78
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY Region 1 5 Post Office Square, Suite 100 BOSTON, MA 02109-3912 CERTIFIED MAILMAI L RETURN RECEIPT REQUESTED APR 16 2ot5 Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 Re: Authorization to discharge under the Remediation General Permit (RGP) - MAG910000. Groveton Wastewater Lagoons site located at 10 Mechanic Street, Groveton, New Hampshire, Coos County; Authorization# NHG910068 Dear Mr. Chapman: Based on the review of a Notice of Intent (NOI) submitted by Sylvia Clark from Stonecipher & Clark Environmental Solutions, LLC, on your behalf for the site referenced above, the U.S. Environmental Protection Agency (EPA) hereby authorizes you, as the named Owner to discharge in accordance with the provisions of the RGP at that site. Your authorization number is listed above. The checklist enclosed with this RGP authorization indicates the pollutants which you are required to monitor. Also indicated on the checklist are the effluent limits, test methods and minimum levels (MLs) for each pollutant. Please note that the checklist does not represent the complete requirements of the RGP. Operators must comply with all of the applicable requirements of this permit, including influent and effluent monitoring, narrative water quality standards, record keeping, and reporting requirements, found in Parts I and II, and Appendices I - VIII of the RGP. See EPA's website for the complete RGP and other information at: http://www.epa.gov/regionl/npdes/mass.html#dgp. Please note the enclosed checklist includes the parameters which your consultant has marked "Believed Present". The checklist also includes parameters your consultant has marked "Believed Absent" and did not submitted a justification (laboratory reports) to indicate their presence or absence in the intake water, as required by the RGP regulations. Also, please note that the metals included on the checklist are dilution dependent pollutants and subject to limitations based on selected dilution ranges and technology-

APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

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Page 1: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY Region 1

5 Post Office Square Suite 100 BOSTON MA 02109-3912

CERTIFIED MAILMAI L RETURN RECEIPT REQUESTED

APR 1 6 2ot5

Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan NH 03588

Re Authorization to discharge under the Remediation General Permit (RGP) shyMAG910000 Groveton Wastewater Lagoons site located at 10 Mechanic Street Groveton New Hampshire Coos County Authorization NHG910068

Dear Mr Chapman

Based on the review of a Notice of Intent (NO I) submitted by Sylvia Clark from Stonecipher amp Clark Environmental Solutions LLC on your behalffor the site referenced above the US Environmental Protection Agency (EPA) hereby authorizes you as the named Owner to discharge in accordance with the provisions of the RGP at that site Your authorization number is listed above

The checklist enclosed with this RGP authorization indicates the pollutants which you are required to monitor Also indicated on the checklist are the effluent limits test methods and minimum levels (MLs) for each pollutant Please note that the checklist does not represent the complete requirements of the RGP Operators must comply with all of the applicable requirements of this permit including influent and effluent monitoring narrative water quality standards record keeping and reporting requirements found in Parts I and II and Appendices I - VIII ofthe RGP See EPAs website for the complete RGP and other information at httpwwwepagovregionlnpdesmasshtmldgp

Please note the enclosed checklist includes the parameters which your consultant has marked Believed Present

The checklist also includes parameters your consultant has marked Believed Absent and did not submitted a justification (laboratory reports) to indicate their presence or absence in the intake water as required by the RGP regulations

Also please note that the metals included on the checklist are dilution dependent pollutants and subject to limitations based on selected dilution ranges and technologyshy

based ceiling limitations For each parameter the dilution factor 679 for this site is within a dilution range greater than fifty to one hundred (gt50-100) established in the RGP (See the RGP Appendix IV for Hew Hampshire facilities) Therefore the limits for antimony of 141 ugL arsenic of 500 ugL cadmium of 16 ugL trivalent chromium of 1385 ugL hexavalent chromium of 570 ugL copper of 142 ugL nickel of807 ugL zinc of 1480 ugL and iron of 5000 ugL are required to achieve permit compliance at your site

Finally please note the checklist ofpollutants attached to this authorization is subject to a recertification ifthe operations at the site result in a discharge lasting longer than six months A recertification can be submitted to EPA within six (6) to twelve (12) months of operations in accordance with the 2010 RGP regulations

This general permit and authorization to discharge will expire on September 9 2015 You have reported that this project will terminate on December 1 2015 Please note you may be required to reapply for a new authorization should the clean- up completion lasts longer than the projected termination date Also regardless of the termination date you are required to submit a Notice of Termination (NOT) to the attention of the contact person indicated below within 30 days of project completion

Thank you in advance for your cooperation in this matter Please contact Victor Alvarez at 617shy918-1572 or AlvarezVictorepagov if you have any questions

Sincerely

)Un-A~ Thelma Murphy Chief Storm Water and Construction Permits Section

Enclosure

cc Jeffrey Andrews NHDES Sylvia Clark SampC

2

2010 Remediation General Permit Summary of Monitoring ParametersW

NPDES Authorization Number NHG910068

Authorization Issued April 2015 FacilitySite Name Groveton Wastewater Lagoons FacilitySite Address 10 Mechanic Street Groveton NH 03582 Coos County

Email address of owner chaomanscra_p_ah_o_ocom LegaI Name of Operator Mikel Douglas Stirling Jr

Operator contact name title and Address

Mike Sterling General Manager Ph6025248312 180 Lancaster Street Gorham NH 03581 Emailmdstirlinggmailcom

Estimated date of The Project IDecember 1 2015Completion

Category and Sub-Category

Category Subcategory

Category III Contaminated Construction Dewatering Subshycategory B Known Contaminated Sites

RGP Termination Date September 2015 Receiving Water

Connecticut River

Monitoring 8t Limits are applicable if checked All samples are to be collected as grab samples middot

Parameter

Effluent LimitLMethodLML (All Effluent Limits are shown as Daily

Maximum Limit unless denoted by a in that case it will be a Monthly Average

Limit)

v 1 Total Suspended Solids (TSS)

30 milligramsliter (mgL) SO mgL for hydrostatic testing Me1602ML5ugL

2 Total Residual Chlorine (TRC) 1

Freshwater= 11 ugL Saltwater= 7 5 ugL Me3305ML 20ugL

3 Total Petroleum Hydrocarbons (TPH)

50 JTlgL Me 1664AML 50mgL

4 Cyanide (CN) 2bull 3 Freshwater= 52 ug1 Saltwater= 10 uQL Me3354ML 10ugL

5 Benzene (B) 5ugL 500 ugL for hydrostatic testing only Me8260CML 2 ugL

6 Toluene (T) (limited as ugL total BTEX) Me8260C ML 2UQL

7 Ethylbenzene (E) (limited as ugL total BTEX) Me8260C ML 2ugL

3

Parameter

Effluent LimitlMethodLML (All Effluent Limits are shown as Daily

Maximum Limit unless denoted by a in that case it will be a Monthly Average

Limit)

8 (mpo) Xylenes (X) (limited as ugL total BTEX) Me8260C ML 2ugL

9 Total Benzene Toluene Ethyl Benzene and Xylenes (BTEX) 4

100 ugL Memiddot8260C ML 2ugL

10 Ethylene Dibromide (EDB) ( 12- Dibromoethane) 005 ug1 Me8260C ML 10ugL

11 Methyl-tert-Butyl Ether (MtBE) 700 ugIMe8260CML 10ugL

12tert-Butyl Alcohol (TBA) (TertiaryButanol)

Monitor Only (ugL)Me 8260C ML 10ugL

13 tert-Amyl Methyl Ether (TAME) Monitor Only(ugL)Me8260CML 10ugL

14 Naphthalene s 20 ugL Me8260CML 2ugL 15 Carbon Tetrachloride 44 ugL Me 8260C ML SugL 16 12 Dichlorobenzene (o-DCB)

600 ugL Me8260C ML 5ugL

17 13 Dichlorobenzene (m-DCB)

320 ugL Me8260C ML 5ugL

18 14 Dichlorobenzene (p-DCB)

50 ugL Me8260C ML 5ugL

18a Total dichlorobenzene 763 ugL shy NH onlyMe 8260C ML 5ugL 19 1 1 Dichloroethane (DCA) 70 ugL Me8260C ML 5ugL 20 1 2 Dichloroethane (DCA) 50 ugL Me8260C ML 5ugL 21 11 Dichloroethene (DCE) 3 2 ugLMe 8260C ML 5ugL 22 cis-12 Dichloroethene (DCE) 70 ugLMe8260C ML 5ugL

23 Methylene Chloride 46 ugLMe8260C ML 5ugjl 24 Tetrachloroethene JPCE) 50 ugLMe8260C ML 5ugL 25 111 Trichloro-ethane (TCA) 200 ugLMe8260C ML 5ugL

26 112 Trichloro-et hane (TCA) 50 ugL Me8260C ML 5ugL

27 Trichloroethene (TCE) 50 ugL Me8260C ML 5ugL 28 Vinyl Chloride (Chloroethene) 20 ugL Me8260C ML 5ugL

29 Acetone Monitor Only(ugL)Me 8260CML 50ugL 30 14 Dioxane Monitor Only Me1624CML 50ugL

31 Total Phenols 300 ugL Me 4201amp4202ML 2 ugL Me 4204 ML 50ugL

32 Pentachlorophenol (PCP) 10 ugL Me8270DML 5ugLMe604 amp625ML 10u_gil

33 Total Phthalates _(Phthalate estersJ 6

30 ugL Me8270DML 5ugL Me606ML 10uqLamp Me 625ML 5uqL

4

Effluent LimitlMethodlML (All Effluent Limits are shown as Daily

Parameter Maximum Limit unless denoted by a in that case it will be a Monthly Average

Limit) 34 Bis (2-Ethylhexyl) 60 ugL Me8270DML Phthalate [Di- (ethylhexyl) SugLMe606ML lOugL amp Me625ML Phthalat~l SuqL 35 Total Group I Polycycl ic v 100 ugLAromatic Hydrocarbons ( PAH)

00038 ugL Me8270D ML SugL v a Benzo(a) Anthracene 7 Me610ML Suqjlamp Me625ML SugL 00038 ugL Me8270D ML SugL v b Benzo(a) Pyrene 7 Me610ML SugLamp Me625ML SuqL 00038 ugL Me8270D ML SugLv c Benzo(b)Fiuoranthene 7 Me610ML SugLamp Me625ML SuqL 00038 ugL Me8270D ML SugLv d Benzo(k)Fiuoranthene 7 Me610ML SugLamp Me625ML SugL 0 0038 ugL Me8270DML Sug L v e Chrysene 7 Me610ML SugLamp Me625ML Sugjl 00038 ugL Me8270DML SugLv f Dibenzo(ah)anthracene 7 Me610ML SugLamp Me625ML SugL 00038 ugL Me8270DML SugLv g Indeno(123-cd) Pyrene 7

Me610ML SugLamp Me625ML5ugL 36 Total Group II Polycyclic

100 ugLAromatic Hydrocarbons (PAH)

XMe8270DML 5ugLMe610 ML h Acenaphthene

SuCJL amp Me625ML SugL XMe 8270DML 5ugLMe610 ML

i Acenaphthylene SugL amp Me625ML SugL XMe8270DML 5ugLMe610ML

j Anthracene SugL amp Me625ML SugL XMe8270DML 5ugLMe610ML

k Benzo(ghi) Perylene SugL amp Me625ML SLJg[L XMe8270DML 5ugLMe610MLv I Fluoranthene SugL amp Me625ML SLJgL XMe8270DML 5ugLMe610ML

m Fluorene SugL amp Me625ML Sugl 20 ug1 Me8270ML SugL Me610 ML

n Naphthalene 5 Sugl amp Me625ML Sug L XMe8270DML 5uglMe610Ml

o Phenanthrene SugL amp Me625ML Su_gfl XMe8270DML5uglMe610ML SugL v p Pyrene amp Me6251ML SugL

37 Total Polychlorinated 0000064 uglMe 608 Ml 05 ugLBiphenyls (PCBs) 8bull 9

v Monitor onlyMe 3000 Ml 100 ugl38 Chloride

5

Metal parameter

Total Recoverable NH[Metal Limit H 10 =25 mgll

CaC03 Units = ugll 1lLlU

Minimum levei=ML

Freshwater Limits

2206 dilution

39 Antimony 141 ML 10

40 Arsenic 500 ML 20

41 Cadmium 16 ML 10

42 Chromium III (trivalent) 1385 ML 15

43 Chromium VI (hexavalent) 570 ML 10

44 Copper 142 ML 15 45 Lead 05 ML 20 46 Mercury 09 ML 02

47 Nickel 807 ML 20 48 Selenium 5 ML 20 49 Silver 04 ML 10

so Zinc 1480 ML 15

51 Iron 5 000 ML 20

Other Parameters Jml

52 Instantaneous Flow Site specific in CFS

53 Total Flow Site specific in CFS

54 pH Range for Class B Waters in NH 65-83 1MonthGrab13

55 pH Range for Class SB Waters in NH 65-8 1MonthGrab13

56 57 Daily maximum temperature shy Warm water fisheries

83 oF 1MonthGrab1 4

58 Daily maximum temperature - Cold water fisheries 68degF 1MonthGrab14

59 60 Maximum Change in Temperature in NH- Any Class B water body- Warm Water

5deg F 1MonthGrab14

61 Maximum Change in Temperature in NH- Any Class B water body shy Cold water and LakesPonds

3oF 1MonthGrab14

Footnotes

1 Although t he maximum values for TRC are 11ugl and 75 ug1 for freshwater and saltwater respectively the compliance limits are equal to the minimum level ( ML) of the test method used as listed in Appendix VI (ie Method 3305 20 ug1) 2 Limits for cyanide are based on EPAs water quality criteria expressed as micrograms per liter There is currently no EPA approved t est method for free cyanide Therefore total cyanide must be reported

6

3 Although the maximum values for cyanide are 52 ug1 and 10 ug1 for freshwater and saltwater respectively the compliance limits are equal to the minimum level (ML) of the Method 335 4 as listed in Appendix VI (ie 10 ug1) 4 BTEX = sum of Benzene Toluene Ethylbenzene and total Xylenes 5 Naphthalene can be reported as both a purgeable (VOC) and extractable (SVOC) organic compound If both VOC and SVOC are analyzed the highest value must be used unless the QC criteria for one of the analyses is not met In such cases the value from the analysis meeting the QC criteria must be used 6 The sum of individual phthalate compounds(not including the 34 Sis (2shyEthylhexyl) Phthalate The compliance limits are equal to the minimum level (ML) of the test method used as listed in Appendix VI Total values calculated for reporting on NOis and discharge monitoring reports shall be calculated by adding the measured concentration of each constituent If the measurement ofa constituent is less than the ML the permittee shall use a value of zero for that constituent For each test the permittee shall also attach the raw data for each constituent to the discharge monitoring report including the minimum level and minimum detection level for the analysis 7 Although the maximum value for the individual PAH compounds is 00038 ug1 the compliance limits are equal to the minimum level (ML) of the test method used as listed in Appendix VI 8 In the November 2002 WQC EPA has revised the definition of Total PCBs for aquatic life as total PCBs is the sum of all homologue all isomer all congener or all Oroclor analysesTotal values calculated for reporting on NOis and discharge monitoring reports shall be calculated by adding the measured concentration of each constituent If the measure of a constituent is less than the ML the permittee shall use a value of zero for that constituent For each test the permittee shall also attach the raw data for each constituent to the discharge monitoring report including the minimum level and minimum detection level for the analysis 9Aithough the maximum valuemiddot for total PCBs is 0000064 ug1 the compliance limit is equal to the minimum level (ML) of the test method used as listed in Appendix VI (ie 05 ug1 for Method 608 or 000005 ug1 when Method 1668a is approved) 10 Hardness Cadmium Chromium III Copper Lead Nickel Silver and Zinc are Hardness Dependent 11 For a Dilution Factor (DF) from 1 to 5 metals limits are calculated using DF times the base limit for the metal See Appendix IV For example iron limits are calculated using DF x 1000ugL (the iron base limit) Therefore DF is 15 the iron limit will be 1500 ugL DF 2 then iron limit =1000 x 2 =2000 ugL etc not to exceed the DF=5 12

Minimum Level (ML is the lowest level at which the analytical system gives a recognizable signal and acceptable calibration point for the analyte The ML represents the lowest-concentration at which an analyte can b~ measured with a known level of confidence The ML is calculated by multiplying the laboratoryshydetermined method detection limit by 318 (see 40 CFR Part 136 Appendix 8) 13

pH sampling for compliance with permit limits may be performed using field methods as provided for in EPA test Method 1501 14

Temperature sampling per Method 1701

7

January 31 2015

United States Environmental Protection Agency 5 Post Office Square Suite 100 Boston Massachusetts 02109-3912 Attn Remediation General Permit NOI Processing

Subject Notice of Intent for Remediation General Permit Groveton Wastewater Lagoons 10 Mechanic Street Groveton New Hampshire

Mr Alvarez

Stonecipher amp Clark Environmental Solutions LLC (SampC) is submitting the attached Remediation General Permit Notice of Intent for the above-referenced location (the ldquoSiterdquo) on behalf of Mr Bob Chapman Please find the NOI form under Attachment A The Site is the former Wausau Paper Mill and is located on two parcels located in Groveton NH along the Upper Ammonoosuc River Please refer to the enclosed locus map (Figure 1) The Site consists of three clarifiers on the 95 acre parcel located adjacent to the Upper Ammonoosuc River and the wastewater lagoonpolishing ponds are located on the 53 acre parcel also adjacent to the Ammonoosuc River

General Site Information

All processes pertaining to the paper mill have ceased and reportedly the lagoons were discharged and cleaned in 2008 under an individual NPDES permit (Permit No NH0001562) This permit expired in 2011 The lagoons have reportedly received no additional wastewater since then Water currently in the open-topped lagoon area and clarifiers is a result of stormwater collection (supernatant) over the past few years The RGP is being sought in order to discharge the remaining supernatant water as part of a final dewatering in order to install drain-holes and maintain the lagoons in an empty state as well as eventual demolition of the clarifiers

Discharge Information

The expired NPDES Individual Permit allowed discharge via Outfall 017 which discharges approximately 05 miles west into the Connecticut River Please see Attachment A for a aerial view of the Site including the approximate outfall locationThis RGP application seeks to maintain the the Outfall 017 discharge point

STON

ECIPH

ER amp C

LARK EN

VIRON

MEN

TAL SO

LUTIO

NS LLC

111 Saranac Street Stu

dio 8 L

ittleton N

H 03561 6035755154

ww

wston

eciph

erand

clarkcom

In December 2013 John King of EPA approved the Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire report prepared and submitted by Horizons Engineering Inc Please find this report under Attachment B This report outlined the results of the sampling plan completed in October 2013 which included samples from 9 locations the four quadrants of the main lagoon the two polishing ponds (lagoons) and the three clarifiers Three samples were taken at each of the nine sampling locations one grab sample from mid-depth between the supernatantsludge interface and the surface one grab sample from the supernatant interface and one sludge sample from the bottom The laboratory results are included in the decommissioning plan report and indicate that detected parameter concentrations in the samples obtained from mid-depth between the supernatant interface and the water surface were all within the former NPDES permit standards with the exception of the sample from Clarifier 1 for which we are NOT seeking coverage under the RGP NOI

The recommendation of the approved decommissioning report was to pump each lagoon and clarifier down to the supernatant interface individually into Outfall 017 (which discharges directly to the Connecticut River) Pumping rates were specified in the report based on BOD and TSS and turbidity monitoring was recommended in order to determine when interface was reached

In November 2014 SampC oversaw discharge of the supernatant from the lagoon area as specified in the approved decommissioning report The pumping rate was greatly reduced from the allowable rate in the plan due to availability of pumping equipment as well as field conditions Turbidity was closely monitored Field observations indicated that the line between the supernatant and the interface was quite sharply defined Close monitoring allowed SampC to be confident in the discharge of only supernatant

Contaminant Information

For the purposes of this permit application it is assumed that the Site falls under Category III subcategory B Upon reviewing Appendix III regarding Effluent Limits and Monitoring Requirements it appears that the supernatant laboratory results for all sampled locations with the exception of Clarifier 1 average 19 mgl TSS which is well below the specified TSS effluent limit of 30 mgl TSS (monthly average) Laboratory results from supernatant collected from Clarifier 3 yielded a TSS value of 45 mgl Please note that using this TSS value as a maximum daily TSS value in the NOI application under Appendix III will therefore skew the actual amount of daily TSS as the dewatering of Clarifier 3 is anticipated at a lesser rate than the 1000 gpm maximum In addition the volume of water in Clarifier 3 (reportedly 9 feet) will be discharged prior to achieving a 24-hr time period

Group I PAHs and Group II PAHs fall below the respective 100 ugl and 1000 ugl daily limits

SampC collected and submitted to the laboratory a confirmatory sample of the lagoon supernatant on December 3 2014 This sample was tested for Volatile Organic Compounds (VOCs) Group I PAHs Group II PAHs and all required metals to be tested under Appendix III Category III subcategory B with the exception of antimony copper nickel zinc and iron

Once the supernatantsludge interface has been reached the plan is to dewater the remaining water overland via NHDES Temporary Groundwater Discharge Permit This will NOT be released to any surface waters

Treatment System Information

No treatment is proposed during dewatering The pumping discharge rate is proposed to be a maximum of 1000 gpm

Receiving Surface Water(s) Information

Discharge will occur approximately 05 miles away to Outfall 017 via underground 32rdquo pipe into the Connecticut River

Endangered Species Act amp National Historic Preservation Act Reviews

SampC has received verbal response from United States Fish and Wildlife Service that the discharge activities are ldquounlikely to adversely affectrdquo listed species or critical habitat When official sign-off is received SampC will forward that response

Under Attachment D please find the correspondence with New Hampshire Division of Historical Resources indicating that findings for this project considered ldquoNo Historic Properties Affectedrdquo

Please contact the undersigned if you have any questions or require additional information

Sincerely

Sylvia A Clark Co-OwnerProject Manager Stonecipher amp Clark Environmental Solutions LLC Office 6035755154 Cell 8027341403 sclarkstonecipherandclarkcom

Attachments Figure 1 ndash Site Aerial Map Figure 2 ndash Treatment System Flow Diagram Attachment A ndash Notice of Intent Form Attachment B ndash EPA Approved Decommissioning Plan Attachment C ndash December 3 2014 Laboratory Results Attachment D ndash NH DHR Correspondence Attachment E - US FWS Correspondence (To be forwarded)

cc Jeff Andrews NHDES

Sylvia
Stamp

Figure 1

Lagoon

Clarifiers

Outfall 017

Stonecipheramp Clark Environmental Solutions LLC 111 Saranac Street Studio 8

Littleton New Hampshire 03561

6035755154

Groveton Wastewater Lagoons amp Clarifiers Groveton NH

SampC Project 2014-062

Aerial Map

Figure 2

LAGOON AREA

CLARIFIER 2

CLARIFIER 1

CLARIFIER 3

UPPER AMMONOOSUC RIVER

MONITORING

CHAMBER

32 PIPE DISCHARGES

APPROX 05 MILES WEST

INTO THE CONNECTICUT

RIVER (OUTFALL 017)

STONECIPHER amp CLARK

ENVIRONMENTAL SOLUTIONS LLC

111 SARANAC STREET STUDIO 8

LITTLETON NEW HAMPSHIRE 03561

6035755154

GROVETON WASTEWATER LAGOONS

GROVETON NEW HAMPSHIRE

FLOW SCHEMATIC

Attachment A

NPDES Permit No MAG910000 NPDES Permit No NHG910000

B Suggested Form for Notice of Intent (NOI) for the Remediation General Permit

1 General facilitysite information Please provide the following information about the site

a) Name of facilitysite Facilitysite mailing address

Location of facilitysite

longitude_______________ latitude_______________

Facility SIC code(s)

Street

b) Name of facilitysite owner Town

Email address of facilitysite owner State Zip County

Telephone no of facilitysite owner

Fax no of facilitysite owner Owner is (check one) 1 Federal____ 2 StateTribal____ 3 Private____ 4 Other ____ if so describe

Address of owner (if different from site)

Street

Town State Zip County

c) Legal name of operator Operator telephone no

Operator fax no Operator email

Operator contact name and title

Address of operator (if different from owner)

Street

Town State Zip County

Remediation General Permit Page 10 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

d) Check Y for Ayes or N for Ano for the following 1 Has a prior NPDES permit exclusion been granted for the discharge Y___ N___ if Y number_________________ 2 Has a prior NPDES application (Form 1 amp 2C) ever been filed for the discharge Y___ N___ if Y date and tracking __________________________________________________________________ 3 Is the discharge a ldquonew dischargerdquo as defined by 40 CFR 1222 Y___ N___ 4 For sites in Massachusetts is the discharge covered under the Massachusetts Contingency Plan (MCP) and exempt from state permitting Y___ N___

e) Is sitefacility subject to any State permitting license f) Is the sitefacility covered by any other EPA permit including or other action which is causing the generation of 1 Multi-Sector General Permit Y___ N___ discharge Y___ N___ if Y number_______________ If Y please list 2 Final Dewatering General Permit Y___ N___ 1 site identification assigned by the state of NH or if Y number________________ MA_________________________________________ 3 EPA Construction General Permit Y___ N___ 2 permit or license assigned____________________ if Y number _______________ 3 state agency contact information name location and 4 Individual NPDES permit Y___ N___ telephone number if Y number_____________

5 any other water quality related individual or general permit Y___ N___ if Y number______________

g) Is the sitefacility located within or does it discharge to an Area of Critical Environmental Concern (ACEC) Y____ N____

h) Based on the facilitysite information and any historical sampling data identify the sub-category into which the potential discharge falls Activity Category Activity Sub-Category I - Petroleum Related Site Remediation A Gasoline Only Sites ____

B Fuel Oils and Other Oil Sites (including Residential Non-Business Remediation Discharges) ____ C Petroleum Sites with Additional Contamination ____

II - Non Petroleum Site Remediation A Volatile Organic Compound (VOC) Only Sites _____ B VOC Sites with Additional Contamination ____ C Primarily Heavy Metal Sites ____

III - Contaminated Construction Dewatering A General Urban Fill Sites ____ B Known Contaminated Sites ____

Remediation General Permit Page 11 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

IV - Miscellaneous Related Discharges A Aquifer Pump Testing to Evaluate Formerly Contaminated Sites ____ B Well DevelopmentRehabilitation at ContaminatedFormerly Contaminated Sites ____ C Hydrostatic Testing of Pipelines and Tanks ____ D Long-Term Remediation of Contaminated Sumps and Dikes ____ E Short-term Contaminated Dredging Drain Back Waters (if not covered by 401404 permit) ____

2 Discharge information Please provide information about the discharge (attaching additional sheets as necessary) including

a) Describe the discharge activities for which the ownerapplicant is seeking coverage

b) Provide the following information about each discharge

1) Number of discharge points

2) What is the maximum and average flow rate of discharge (in cubic feet per second ft3s) Max flow____________ Is maximum flow a design value Y___ N____ Average flow (include units) __________ Is average flow a design value or estimate _________

3) Latitude and longitude of each discharge within 100 feet pt1 lat_____________ long_____________ pt2 lat_____________ long_____________ pt3 lat_____________ long_____________ pt4 lat_____________ long_____________ pt5 lat_____________ long_____________ pt6 lat_____________ long_____________ pt7 lat_____________ long_____________ pt8 lat_____________ long_____________ etc

4) If hydrostatic testing total volume of the discharge (gals)_________

5) Is the discharge intermittent ____ or seasonal____ Is discharge ongoing Y ____ N______

c) Expected dates of discharge (mmddyy) start_____________ end_________________ d) Please attach a line drawing or flow schematic showing water flow through the facility including 1 sources of intake water 2 contributing flow from the operation 3 treatment units and 4 discharge points and receiving waters(s)

Remediation General Permit Page 12 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

3 Contaminant information a) Based on the sub-category selected (see Appendix III) indicate whether each listed chemical is believed present or believed absent in the potential discharge Attach additional sheets as needed

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

1 Total Suspended Solids (TSS) 2 Total Residual Chlorine (TRC) 3 Total Petroleum Hydrocarbons (TPH) 4 Cyanide (CN) 57125 5 Benzene (B) 71432 6 Toluene (T) 108883 7 Ethylbenzene (E) 100414 8 (mpo) Xylenes (X) 108883

106423 95476

1330207

9 Total BTEX 2 na 10 Ethylene Dibromide (EDB) (12- Dibromoethane) 3

106934

11 Methyl-tert-Butyl Ether (MtBE)

1634044

12 tert-Butyl Alcohol (TBA) (Tertiary-Butanol)

75650

Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI 2 BTEX = Sum of Benzene Toluene Ethylbenzene total Xylenes 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England

Remediation General Permit Page 13 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
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                  5. TextField38[0] estimate
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                  8. DateTimeField1[0] 312015
                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
                                          11. TextField59[0] Class B
                                          12. TextField60[0] 216
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Page 2: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

based ceiling limitations For each parameter the dilution factor 679 for this site is within a dilution range greater than fifty to one hundred (gt50-100) established in the RGP (See the RGP Appendix IV for Hew Hampshire facilities) Therefore the limits for antimony of 141 ugL arsenic of 500 ugL cadmium of 16 ugL trivalent chromium of 1385 ugL hexavalent chromium of 570 ugL copper of 142 ugL nickel of807 ugL zinc of 1480 ugL and iron of 5000 ugL are required to achieve permit compliance at your site

Finally please note the checklist ofpollutants attached to this authorization is subject to a recertification ifthe operations at the site result in a discharge lasting longer than six months A recertification can be submitted to EPA within six (6) to twelve (12) months of operations in accordance with the 2010 RGP regulations

This general permit and authorization to discharge will expire on September 9 2015 You have reported that this project will terminate on December 1 2015 Please note you may be required to reapply for a new authorization should the clean- up completion lasts longer than the projected termination date Also regardless of the termination date you are required to submit a Notice of Termination (NOT) to the attention of the contact person indicated below within 30 days of project completion

Thank you in advance for your cooperation in this matter Please contact Victor Alvarez at 617shy918-1572 or AlvarezVictorepagov if you have any questions

Sincerely

)Un-A~ Thelma Murphy Chief Storm Water and Construction Permits Section

Enclosure

cc Jeffrey Andrews NHDES Sylvia Clark SampC

2

2010 Remediation General Permit Summary of Monitoring ParametersW

NPDES Authorization Number NHG910068

Authorization Issued April 2015 FacilitySite Name Groveton Wastewater Lagoons FacilitySite Address 10 Mechanic Street Groveton NH 03582 Coos County

Email address of owner chaomanscra_p_ah_o_ocom LegaI Name of Operator Mikel Douglas Stirling Jr

Operator contact name title and Address

Mike Sterling General Manager Ph6025248312 180 Lancaster Street Gorham NH 03581 Emailmdstirlinggmailcom

Estimated date of The Project IDecember 1 2015Completion

Category and Sub-Category

Category Subcategory

Category III Contaminated Construction Dewatering Subshycategory B Known Contaminated Sites

RGP Termination Date September 2015 Receiving Water

Connecticut River

Monitoring 8t Limits are applicable if checked All samples are to be collected as grab samples middot

Parameter

Effluent LimitLMethodLML (All Effluent Limits are shown as Daily

Maximum Limit unless denoted by a in that case it will be a Monthly Average

Limit)

v 1 Total Suspended Solids (TSS)

30 milligramsliter (mgL) SO mgL for hydrostatic testing Me1602ML5ugL

2 Total Residual Chlorine (TRC) 1

Freshwater= 11 ugL Saltwater= 7 5 ugL Me3305ML 20ugL

3 Total Petroleum Hydrocarbons (TPH)

50 JTlgL Me 1664AML 50mgL

4 Cyanide (CN) 2bull 3 Freshwater= 52 ug1 Saltwater= 10 uQL Me3354ML 10ugL

5 Benzene (B) 5ugL 500 ugL for hydrostatic testing only Me8260CML 2 ugL

6 Toluene (T) (limited as ugL total BTEX) Me8260C ML 2UQL

7 Ethylbenzene (E) (limited as ugL total BTEX) Me8260C ML 2ugL

3

Parameter

Effluent LimitlMethodLML (All Effluent Limits are shown as Daily

Maximum Limit unless denoted by a in that case it will be a Monthly Average

Limit)

8 (mpo) Xylenes (X) (limited as ugL total BTEX) Me8260C ML 2ugL

9 Total Benzene Toluene Ethyl Benzene and Xylenes (BTEX) 4

100 ugL Memiddot8260C ML 2ugL

10 Ethylene Dibromide (EDB) ( 12- Dibromoethane) 005 ug1 Me8260C ML 10ugL

11 Methyl-tert-Butyl Ether (MtBE) 700 ugIMe8260CML 10ugL

12tert-Butyl Alcohol (TBA) (TertiaryButanol)

Monitor Only (ugL)Me 8260C ML 10ugL

13 tert-Amyl Methyl Ether (TAME) Monitor Only(ugL)Me8260CML 10ugL

14 Naphthalene s 20 ugL Me8260CML 2ugL 15 Carbon Tetrachloride 44 ugL Me 8260C ML SugL 16 12 Dichlorobenzene (o-DCB)

600 ugL Me8260C ML 5ugL

17 13 Dichlorobenzene (m-DCB)

320 ugL Me8260C ML 5ugL

18 14 Dichlorobenzene (p-DCB)

50 ugL Me8260C ML 5ugL

18a Total dichlorobenzene 763 ugL shy NH onlyMe 8260C ML 5ugL 19 1 1 Dichloroethane (DCA) 70 ugL Me8260C ML 5ugL 20 1 2 Dichloroethane (DCA) 50 ugL Me8260C ML 5ugL 21 11 Dichloroethene (DCE) 3 2 ugLMe 8260C ML 5ugL 22 cis-12 Dichloroethene (DCE) 70 ugLMe8260C ML 5ugL

23 Methylene Chloride 46 ugLMe8260C ML 5ugjl 24 Tetrachloroethene JPCE) 50 ugLMe8260C ML 5ugL 25 111 Trichloro-ethane (TCA) 200 ugLMe8260C ML 5ugL

26 112 Trichloro-et hane (TCA) 50 ugL Me8260C ML 5ugL

27 Trichloroethene (TCE) 50 ugL Me8260C ML 5ugL 28 Vinyl Chloride (Chloroethene) 20 ugL Me8260C ML 5ugL

29 Acetone Monitor Only(ugL)Me 8260CML 50ugL 30 14 Dioxane Monitor Only Me1624CML 50ugL

31 Total Phenols 300 ugL Me 4201amp4202ML 2 ugL Me 4204 ML 50ugL

32 Pentachlorophenol (PCP) 10 ugL Me8270DML 5ugLMe604 amp625ML 10u_gil

33 Total Phthalates _(Phthalate estersJ 6

30 ugL Me8270DML 5ugL Me606ML 10uqLamp Me 625ML 5uqL

4

Effluent LimitlMethodlML (All Effluent Limits are shown as Daily

Parameter Maximum Limit unless denoted by a in that case it will be a Monthly Average

Limit) 34 Bis (2-Ethylhexyl) 60 ugL Me8270DML Phthalate [Di- (ethylhexyl) SugLMe606ML lOugL amp Me625ML Phthalat~l SuqL 35 Total Group I Polycycl ic v 100 ugLAromatic Hydrocarbons ( PAH)

00038 ugL Me8270D ML SugL v a Benzo(a) Anthracene 7 Me610ML Suqjlamp Me625ML SugL 00038 ugL Me8270D ML SugL v b Benzo(a) Pyrene 7 Me610ML SugLamp Me625ML SuqL 00038 ugL Me8270D ML SugLv c Benzo(b)Fiuoranthene 7 Me610ML SugLamp Me625ML SuqL 00038 ugL Me8270D ML SugLv d Benzo(k)Fiuoranthene 7 Me610ML SugLamp Me625ML SugL 0 0038 ugL Me8270DML Sug L v e Chrysene 7 Me610ML SugLamp Me625ML Sugjl 00038 ugL Me8270DML SugLv f Dibenzo(ah)anthracene 7 Me610ML SugLamp Me625ML SugL 00038 ugL Me8270DML SugLv g Indeno(123-cd) Pyrene 7

Me610ML SugLamp Me625ML5ugL 36 Total Group II Polycyclic

100 ugLAromatic Hydrocarbons (PAH)

XMe8270DML 5ugLMe610 ML h Acenaphthene

SuCJL amp Me625ML SugL XMe 8270DML 5ugLMe610 ML

i Acenaphthylene SugL amp Me625ML SugL XMe8270DML 5ugLMe610ML

j Anthracene SugL amp Me625ML SugL XMe8270DML 5ugLMe610ML

k Benzo(ghi) Perylene SugL amp Me625ML SLJg[L XMe8270DML 5ugLMe610MLv I Fluoranthene SugL amp Me625ML SLJgL XMe8270DML 5ugLMe610ML

m Fluorene SugL amp Me625ML Sugl 20 ug1 Me8270ML SugL Me610 ML

n Naphthalene 5 Sugl amp Me625ML Sug L XMe8270DML 5uglMe610Ml

o Phenanthrene SugL amp Me625ML Su_gfl XMe8270DML5uglMe610ML SugL v p Pyrene amp Me6251ML SugL

37 Total Polychlorinated 0000064 uglMe 608 Ml 05 ugLBiphenyls (PCBs) 8bull 9

v Monitor onlyMe 3000 Ml 100 ugl38 Chloride

5

Metal parameter

Total Recoverable NH[Metal Limit H 10 =25 mgll

CaC03 Units = ugll 1lLlU

Minimum levei=ML

Freshwater Limits

2206 dilution

39 Antimony 141 ML 10

40 Arsenic 500 ML 20

41 Cadmium 16 ML 10

42 Chromium III (trivalent) 1385 ML 15

43 Chromium VI (hexavalent) 570 ML 10

44 Copper 142 ML 15 45 Lead 05 ML 20 46 Mercury 09 ML 02

47 Nickel 807 ML 20 48 Selenium 5 ML 20 49 Silver 04 ML 10

so Zinc 1480 ML 15

51 Iron 5 000 ML 20

Other Parameters Jml

52 Instantaneous Flow Site specific in CFS

53 Total Flow Site specific in CFS

54 pH Range for Class B Waters in NH 65-83 1MonthGrab13

55 pH Range for Class SB Waters in NH 65-8 1MonthGrab13

56 57 Daily maximum temperature shy Warm water fisheries

83 oF 1MonthGrab1 4

58 Daily maximum temperature - Cold water fisheries 68degF 1MonthGrab14

59 60 Maximum Change in Temperature in NH- Any Class B water body- Warm Water

5deg F 1MonthGrab14

61 Maximum Change in Temperature in NH- Any Class B water body shy Cold water and LakesPonds

3oF 1MonthGrab14

Footnotes

1 Although t he maximum values for TRC are 11ugl and 75 ug1 for freshwater and saltwater respectively the compliance limits are equal to the minimum level ( ML) of the test method used as listed in Appendix VI (ie Method 3305 20 ug1) 2 Limits for cyanide are based on EPAs water quality criteria expressed as micrograms per liter There is currently no EPA approved t est method for free cyanide Therefore total cyanide must be reported

6

3 Although the maximum values for cyanide are 52 ug1 and 10 ug1 for freshwater and saltwater respectively the compliance limits are equal to the minimum level (ML) of the Method 335 4 as listed in Appendix VI (ie 10 ug1) 4 BTEX = sum of Benzene Toluene Ethylbenzene and total Xylenes 5 Naphthalene can be reported as both a purgeable (VOC) and extractable (SVOC) organic compound If both VOC and SVOC are analyzed the highest value must be used unless the QC criteria for one of the analyses is not met In such cases the value from the analysis meeting the QC criteria must be used 6 The sum of individual phthalate compounds(not including the 34 Sis (2shyEthylhexyl) Phthalate The compliance limits are equal to the minimum level (ML) of the test method used as listed in Appendix VI Total values calculated for reporting on NOis and discharge monitoring reports shall be calculated by adding the measured concentration of each constituent If the measurement ofa constituent is less than the ML the permittee shall use a value of zero for that constituent For each test the permittee shall also attach the raw data for each constituent to the discharge monitoring report including the minimum level and minimum detection level for the analysis 7 Although the maximum value for the individual PAH compounds is 00038 ug1 the compliance limits are equal to the minimum level (ML) of the test method used as listed in Appendix VI 8 In the November 2002 WQC EPA has revised the definition of Total PCBs for aquatic life as total PCBs is the sum of all homologue all isomer all congener or all Oroclor analysesTotal values calculated for reporting on NOis and discharge monitoring reports shall be calculated by adding the measured concentration of each constituent If the measure of a constituent is less than the ML the permittee shall use a value of zero for that constituent For each test the permittee shall also attach the raw data for each constituent to the discharge monitoring report including the minimum level and minimum detection level for the analysis 9Aithough the maximum valuemiddot for total PCBs is 0000064 ug1 the compliance limit is equal to the minimum level (ML) of the test method used as listed in Appendix VI (ie 05 ug1 for Method 608 or 000005 ug1 when Method 1668a is approved) 10 Hardness Cadmium Chromium III Copper Lead Nickel Silver and Zinc are Hardness Dependent 11 For a Dilution Factor (DF) from 1 to 5 metals limits are calculated using DF times the base limit for the metal See Appendix IV For example iron limits are calculated using DF x 1000ugL (the iron base limit) Therefore DF is 15 the iron limit will be 1500 ugL DF 2 then iron limit =1000 x 2 =2000 ugL etc not to exceed the DF=5 12

Minimum Level (ML is the lowest level at which the analytical system gives a recognizable signal and acceptable calibration point for the analyte The ML represents the lowest-concentration at which an analyte can b~ measured with a known level of confidence The ML is calculated by multiplying the laboratoryshydetermined method detection limit by 318 (see 40 CFR Part 136 Appendix 8) 13

pH sampling for compliance with permit limits may be performed using field methods as provided for in EPA test Method 1501 14

Temperature sampling per Method 1701

7

January 31 2015

United States Environmental Protection Agency 5 Post Office Square Suite 100 Boston Massachusetts 02109-3912 Attn Remediation General Permit NOI Processing

Subject Notice of Intent for Remediation General Permit Groveton Wastewater Lagoons 10 Mechanic Street Groveton New Hampshire

Mr Alvarez

Stonecipher amp Clark Environmental Solutions LLC (SampC) is submitting the attached Remediation General Permit Notice of Intent for the above-referenced location (the ldquoSiterdquo) on behalf of Mr Bob Chapman Please find the NOI form under Attachment A The Site is the former Wausau Paper Mill and is located on two parcels located in Groveton NH along the Upper Ammonoosuc River Please refer to the enclosed locus map (Figure 1) The Site consists of three clarifiers on the 95 acre parcel located adjacent to the Upper Ammonoosuc River and the wastewater lagoonpolishing ponds are located on the 53 acre parcel also adjacent to the Ammonoosuc River

General Site Information

All processes pertaining to the paper mill have ceased and reportedly the lagoons were discharged and cleaned in 2008 under an individual NPDES permit (Permit No NH0001562) This permit expired in 2011 The lagoons have reportedly received no additional wastewater since then Water currently in the open-topped lagoon area and clarifiers is a result of stormwater collection (supernatant) over the past few years The RGP is being sought in order to discharge the remaining supernatant water as part of a final dewatering in order to install drain-holes and maintain the lagoons in an empty state as well as eventual demolition of the clarifiers

Discharge Information

The expired NPDES Individual Permit allowed discharge via Outfall 017 which discharges approximately 05 miles west into the Connecticut River Please see Attachment A for a aerial view of the Site including the approximate outfall locationThis RGP application seeks to maintain the the Outfall 017 discharge point

STON

ECIPH

ER amp C

LARK EN

VIRON

MEN

TAL SO

LUTIO

NS LLC

111 Saranac Street Stu

dio 8 L

ittleton N

H 03561 6035755154

ww

wston

eciph

erand

clarkcom

In December 2013 John King of EPA approved the Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire report prepared and submitted by Horizons Engineering Inc Please find this report under Attachment B This report outlined the results of the sampling plan completed in October 2013 which included samples from 9 locations the four quadrants of the main lagoon the two polishing ponds (lagoons) and the three clarifiers Three samples were taken at each of the nine sampling locations one grab sample from mid-depth between the supernatantsludge interface and the surface one grab sample from the supernatant interface and one sludge sample from the bottom The laboratory results are included in the decommissioning plan report and indicate that detected parameter concentrations in the samples obtained from mid-depth between the supernatant interface and the water surface were all within the former NPDES permit standards with the exception of the sample from Clarifier 1 for which we are NOT seeking coverage under the RGP NOI

The recommendation of the approved decommissioning report was to pump each lagoon and clarifier down to the supernatant interface individually into Outfall 017 (which discharges directly to the Connecticut River) Pumping rates were specified in the report based on BOD and TSS and turbidity monitoring was recommended in order to determine when interface was reached

In November 2014 SampC oversaw discharge of the supernatant from the lagoon area as specified in the approved decommissioning report The pumping rate was greatly reduced from the allowable rate in the plan due to availability of pumping equipment as well as field conditions Turbidity was closely monitored Field observations indicated that the line between the supernatant and the interface was quite sharply defined Close monitoring allowed SampC to be confident in the discharge of only supernatant

Contaminant Information

For the purposes of this permit application it is assumed that the Site falls under Category III subcategory B Upon reviewing Appendix III regarding Effluent Limits and Monitoring Requirements it appears that the supernatant laboratory results for all sampled locations with the exception of Clarifier 1 average 19 mgl TSS which is well below the specified TSS effluent limit of 30 mgl TSS (monthly average) Laboratory results from supernatant collected from Clarifier 3 yielded a TSS value of 45 mgl Please note that using this TSS value as a maximum daily TSS value in the NOI application under Appendix III will therefore skew the actual amount of daily TSS as the dewatering of Clarifier 3 is anticipated at a lesser rate than the 1000 gpm maximum In addition the volume of water in Clarifier 3 (reportedly 9 feet) will be discharged prior to achieving a 24-hr time period

Group I PAHs and Group II PAHs fall below the respective 100 ugl and 1000 ugl daily limits

SampC collected and submitted to the laboratory a confirmatory sample of the lagoon supernatant on December 3 2014 This sample was tested for Volatile Organic Compounds (VOCs) Group I PAHs Group II PAHs and all required metals to be tested under Appendix III Category III subcategory B with the exception of antimony copper nickel zinc and iron

Once the supernatantsludge interface has been reached the plan is to dewater the remaining water overland via NHDES Temporary Groundwater Discharge Permit This will NOT be released to any surface waters

Treatment System Information

No treatment is proposed during dewatering The pumping discharge rate is proposed to be a maximum of 1000 gpm

Receiving Surface Water(s) Information

Discharge will occur approximately 05 miles away to Outfall 017 via underground 32rdquo pipe into the Connecticut River

Endangered Species Act amp National Historic Preservation Act Reviews

SampC has received verbal response from United States Fish and Wildlife Service that the discharge activities are ldquounlikely to adversely affectrdquo listed species or critical habitat When official sign-off is received SampC will forward that response

Under Attachment D please find the correspondence with New Hampshire Division of Historical Resources indicating that findings for this project considered ldquoNo Historic Properties Affectedrdquo

Please contact the undersigned if you have any questions or require additional information

Sincerely

Sylvia A Clark Co-OwnerProject Manager Stonecipher amp Clark Environmental Solutions LLC Office 6035755154 Cell 8027341403 sclarkstonecipherandclarkcom

Attachments Figure 1 ndash Site Aerial Map Figure 2 ndash Treatment System Flow Diagram Attachment A ndash Notice of Intent Form Attachment B ndash EPA Approved Decommissioning Plan Attachment C ndash December 3 2014 Laboratory Results Attachment D ndash NH DHR Correspondence Attachment E - US FWS Correspondence (To be forwarded)

cc Jeff Andrews NHDES

Sylvia
Stamp

Figure 1

Lagoon

Clarifiers

Outfall 017

Stonecipheramp Clark Environmental Solutions LLC 111 Saranac Street Studio 8

Littleton New Hampshire 03561

6035755154

Groveton Wastewater Lagoons amp Clarifiers Groveton NH

SampC Project 2014-062

Aerial Map

Figure 2

LAGOON AREA

CLARIFIER 2

CLARIFIER 1

CLARIFIER 3

UPPER AMMONOOSUC RIVER

MONITORING

CHAMBER

32 PIPE DISCHARGES

APPROX 05 MILES WEST

INTO THE CONNECTICUT

RIVER (OUTFALL 017)

STONECIPHER amp CLARK

ENVIRONMENTAL SOLUTIONS LLC

111 SARANAC STREET STUDIO 8

LITTLETON NEW HAMPSHIRE 03561

6035755154

GROVETON WASTEWATER LAGOONS

GROVETON NEW HAMPSHIRE

FLOW SCHEMATIC

Attachment A

NPDES Permit No MAG910000 NPDES Permit No NHG910000

B Suggested Form for Notice of Intent (NOI) for the Remediation General Permit

1 General facilitysite information Please provide the following information about the site

a) Name of facilitysite Facilitysite mailing address

Location of facilitysite

longitude_______________ latitude_______________

Facility SIC code(s)

Street

b) Name of facilitysite owner Town

Email address of facilitysite owner State Zip County

Telephone no of facilitysite owner

Fax no of facilitysite owner Owner is (check one) 1 Federal____ 2 StateTribal____ 3 Private____ 4 Other ____ if so describe

Address of owner (if different from site)

Street

Town State Zip County

c) Legal name of operator Operator telephone no

Operator fax no Operator email

Operator contact name and title

Address of operator (if different from owner)

Street

Town State Zip County

Remediation General Permit Page 10 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

d) Check Y for Ayes or N for Ano for the following 1 Has a prior NPDES permit exclusion been granted for the discharge Y___ N___ if Y number_________________ 2 Has a prior NPDES application (Form 1 amp 2C) ever been filed for the discharge Y___ N___ if Y date and tracking __________________________________________________________________ 3 Is the discharge a ldquonew dischargerdquo as defined by 40 CFR 1222 Y___ N___ 4 For sites in Massachusetts is the discharge covered under the Massachusetts Contingency Plan (MCP) and exempt from state permitting Y___ N___

e) Is sitefacility subject to any State permitting license f) Is the sitefacility covered by any other EPA permit including or other action which is causing the generation of 1 Multi-Sector General Permit Y___ N___ discharge Y___ N___ if Y number_______________ If Y please list 2 Final Dewatering General Permit Y___ N___ 1 site identification assigned by the state of NH or if Y number________________ MA_________________________________________ 3 EPA Construction General Permit Y___ N___ 2 permit or license assigned____________________ if Y number _______________ 3 state agency contact information name location and 4 Individual NPDES permit Y___ N___ telephone number if Y number_____________

5 any other water quality related individual or general permit Y___ N___ if Y number______________

g) Is the sitefacility located within or does it discharge to an Area of Critical Environmental Concern (ACEC) Y____ N____

h) Based on the facilitysite information and any historical sampling data identify the sub-category into which the potential discharge falls Activity Category Activity Sub-Category I - Petroleum Related Site Remediation A Gasoline Only Sites ____

B Fuel Oils and Other Oil Sites (including Residential Non-Business Remediation Discharges) ____ C Petroleum Sites with Additional Contamination ____

II - Non Petroleum Site Remediation A Volatile Organic Compound (VOC) Only Sites _____ B VOC Sites with Additional Contamination ____ C Primarily Heavy Metal Sites ____

III - Contaminated Construction Dewatering A General Urban Fill Sites ____ B Known Contaminated Sites ____

Remediation General Permit Page 11 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

IV - Miscellaneous Related Discharges A Aquifer Pump Testing to Evaluate Formerly Contaminated Sites ____ B Well DevelopmentRehabilitation at ContaminatedFormerly Contaminated Sites ____ C Hydrostatic Testing of Pipelines and Tanks ____ D Long-Term Remediation of Contaminated Sumps and Dikes ____ E Short-term Contaminated Dredging Drain Back Waters (if not covered by 401404 permit) ____

2 Discharge information Please provide information about the discharge (attaching additional sheets as necessary) including

a) Describe the discharge activities for which the ownerapplicant is seeking coverage

b) Provide the following information about each discharge

1) Number of discharge points

2) What is the maximum and average flow rate of discharge (in cubic feet per second ft3s) Max flow____________ Is maximum flow a design value Y___ N____ Average flow (include units) __________ Is average flow a design value or estimate _________

3) Latitude and longitude of each discharge within 100 feet pt1 lat_____________ long_____________ pt2 lat_____________ long_____________ pt3 lat_____________ long_____________ pt4 lat_____________ long_____________ pt5 lat_____________ long_____________ pt6 lat_____________ long_____________ pt7 lat_____________ long_____________ pt8 lat_____________ long_____________ etc

4) If hydrostatic testing total volume of the discharge (gals)_________

5) Is the discharge intermittent ____ or seasonal____ Is discharge ongoing Y ____ N______

c) Expected dates of discharge (mmddyy) start_____________ end_________________ d) Please attach a line drawing or flow schematic showing water flow through the facility including 1 sources of intake water 2 contributing flow from the operation 3 treatment units and 4 discharge points and receiving waters(s)

Remediation General Permit Page 12 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

3 Contaminant information a) Based on the sub-category selected (see Appendix III) indicate whether each listed chemical is believed present or believed absent in the potential discharge Attach additional sheets as needed

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

1 Total Suspended Solids (TSS) 2 Total Residual Chlorine (TRC) 3 Total Petroleum Hydrocarbons (TPH) 4 Cyanide (CN) 57125 5 Benzene (B) 71432 6 Toluene (T) 108883 7 Ethylbenzene (E) 100414 8 (mpo) Xylenes (X) 108883

106423 95476

1330207

9 Total BTEX 2 na 10 Ethylene Dibromide (EDB) (12- Dibromoethane) 3

106934

11 Methyl-tert-Butyl Ether (MtBE)

1634044

12 tert-Butyl Alcohol (TBA) (Tertiary-Butanol)

75650

Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI 2 BTEX = Sum of Benzene Toluene Ethylbenzene total Xylenes 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England

Remediation General Permit Page 13 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
            1. Page11[0]
              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
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                  5. TextField38[0] estimate
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                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
                                          11. TextField59[0] Class B
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Page 3: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

2010 Remediation General Permit Summary of Monitoring ParametersW

NPDES Authorization Number NHG910068

Authorization Issued April 2015 FacilitySite Name Groveton Wastewater Lagoons FacilitySite Address 10 Mechanic Street Groveton NH 03582 Coos County

Email address of owner chaomanscra_p_ah_o_ocom LegaI Name of Operator Mikel Douglas Stirling Jr

Operator contact name title and Address

Mike Sterling General Manager Ph6025248312 180 Lancaster Street Gorham NH 03581 Emailmdstirlinggmailcom

Estimated date of The Project IDecember 1 2015Completion

Category and Sub-Category

Category Subcategory

Category III Contaminated Construction Dewatering Subshycategory B Known Contaminated Sites

RGP Termination Date September 2015 Receiving Water

Connecticut River

Monitoring 8t Limits are applicable if checked All samples are to be collected as grab samples middot

Parameter

Effluent LimitLMethodLML (All Effluent Limits are shown as Daily

Maximum Limit unless denoted by a in that case it will be a Monthly Average

Limit)

v 1 Total Suspended Solids (TSS)

30 milligramsliter (mgL) SO mgL for hydrostatic testing Me1602ML5ugL

2 Total Residual Chlorine (TRC) 1

Freshwater= 11 ugL Saltwater= 7 5 ugL Me3305ML 20ugL

3 Total Petroleum Hydrocarbons (TPH)

50 JTlgL Me 1664AML 50mgL

4 Cyanide (CN) 2bull 3 Freshwater= 52 ug1 Saltwater= 10 uQL Me3354ML 10ugL

5 Benzene (B) 5ugL 500 ugL for hydrostatic testing only Me8260CML 2 ugL

6 Toluene (T) (limited as ugL total BTEX) Me8260C ML 2UQL

7 Ethylbenzene (E) (limited as ugL total BTEX) Me8260C ML 2ugL

3

Parameter

Effluent LimitlMethodLML (All Effluent Limits are shown as Daily

Maximum Limit unless denoted by a in that case it will be a Monthly Average

Limit)

8 (mpo) Xylenes (X) (limited as ugL total BTEX) Me8260C ML 2ugL

9 Total Benzene Toluene Ethyl Benzene and Xylenes (BTEX) 4

100 ugL Memiddot8260C ML 2ugL

10 Ethylene Dibromide (EDB) ( 12- Dibromoethane) 005 ug1 Me8260C ML 10ugL

11 Methyl-tert-Butyl Ether (MtBE) 700 ugIMe8260CML 10ugL

12tert-Butyl Alcohol (TBA) (TertiaryButanol)

Monitor Only (ugL)Me 8260C ML 10ugL

13 tert-Amyl Methyl Ether (TAME) Monitor Only(ugL)Me8260CML 10ugL

14 Naphthalene s 20 ugL Me8260CML 2ugL 15 Carbon Tetrachloride 44 ugL Me 8260C ML SugL 16 12 Dichlorobenzene (o-DCB)

600 ugL Me8260C ML 5ugL

17 13 Dichlorobenzene (m-DCB)

320 ugL Me8260C ML 5ugL

18 14 Dichlorobenzene (p-DCB)

50 ugL Me8260C ML 5ugL

18a Total dichlorobenzene 763 ugL shy NH onlyMe 8260C ML 5ugL 19 1 1 Dichloroethane (DCA) 70 ugL Me8260C ML 5ugL 20 1 2 Dichloroethane (DCA) 50 ugL Me8260C ML 5ugL 21 11 Dichloroethene (DCE) 3 2 ugLMe 8260C ML 5ugL 22 cis-12 Dichloroethene (DCE) 70 ugLMe8260C ML 5ugL

23 Methylene Chloride 46 ugLMe8260C ML 5ugjl 24 Tetrachloroethene JPCE) 50 ugLMe8260C ML 5ugL 25 111 Trichloro-ethane (TCA) 200 ugLMe8260C ML 5ugL

26 112 Trichloro-et hane (TCA) 50 ugL Me8260C ML 5ugL

27 Trichloroethene (TCE) 50 ugL Me8260C ML 5ugL 28 Vinyl Chloride (Chloroethene) 20 ugL Me8260C ML 5ugL

29 Acetone Monitor Only(ugL)Me 8260CML 50ugL 30 14 Dioxane Monitor Only Me1624CML 50ugL

31 Total Phenols 300 ugL Me 4201amp4202ML 2 ugL Me 4204 ML 50ugL

32 Pentachlorophenol (PCP) 10 ugL Me8270DML 5ugLMe604 amp625ML 10u_gil

33 Total Phthalates _(Phthalate estersJ 6

30 ugL Me8270DML 5ugL Me606ML 10uqLamp Me 625ML 5uqL

4

Effluent LimitlMethodlML (All Effluent Limits are shown as Daily

Parameter Maximum Limit unless denoted by a in that case it will be a Monthly Average

Limit) 34 Bis (2-Ethylhexyl) 60 ugL Me8270DML Phthalate [Di- (ethylhexyl) SugLMe606ML lOugL amp Me625ML Phthalat~l SuqL 35 Total Group I Polycycl ic v 100 ugLAromatic Hydrocarbons ( PAH)

00038 ugL Me8270D ML SugL v a Benzo(a) Anthracene 7 Me610ML Suqjlamp Me625ML SugL 00038 ugL Me8270D ML SugL v b Benzo(a) Pyrene 7 Me610ML SugLamp Me625ML SuqL 00038 ugL Me8270D ML SugLv c Benzo(b)Fiuoranthene 7 Me610ML SugLamp Me625ML SuqL 00038 ugL Me8270D ML SugLv d Benzo(k)Fiuoranthene 7 Me610ML SugLamp Me625ML SugL 0 0038 ugL Me8270DML Sug L v e Chrysene 7 Me610ML SugLamp Me625ML Sugjl 00038 ugL Me8270DML SugLv f Dibenzo(ah)anthracene 7 Me610ML SugLamp Me625ML SugL 00038 ugL Me8270DML SugLv g Indeno(123-cd) Pyrene 7

Me610ML SugLamp Me625ML5ugL 36 Total Group II Polycyclic

100 ugLAromatic Hydrocarbons (PAH)

XMe8270DML 5ugLMe610 ML h Acenaphthene

SuCJL amp Me625ML SugL XMe 8270DML 5ugLMe610 ML

i Acenaphthylene SugL amp Me625ML SugL XMe8270DML 5ugLMe610ML

j Anthracene SugL amp Me625ML SugL XMe8270DML 5ugLMe610ML

k Benzo(ghi) Perylene SugL amp Me625ML SLJg[L XMe8270DML 5ugLMe610MLv I Fluoranthene SugL amp Me625ML SLJgL XMe8270DML 5ugLMe610ML

m Fluorene SugL amp Me625ML Sugl 20 ug1 Me8270ML SugL Me610 ML

n Naphthalene 5 Sugl amp Me625ML Sug L XMe8270DML 5uglMe610Ml

o Phenanthrene SugL amp Me625ML Su_gfl XMe8270DML5uglMe610ML SugL v p Pyrene amp Me6251ML SugL

37 Total Polychlorinated 0000064 uglMe 608 Ml 05 ugLBiphenyls (PCBs) 8bull 9

v Monitor onlyMe 3000 Ml 100 ugl38 Chloride

5

Metal parameter

Total Recoverable NH[Metal Limit H 10 =25 mgll

CaC03 Units = ugll 1lLlU

Minimum levei=ML

Freshwater Limits

2206 dilution

39 Antimony 141 ML 10

40 Arsenic 500 ML 20

41 Cadmium 16 ML 10

42 Chromium III (trivalent) 1385 ML 15

43 Chromium VI (hexavalent) 570 ML 10

44 Copper 142 ML 15 45 Lead 05 ML 20 46 Mercury 09 ML 02

47 Nickel 807 ML 20 48 Selenium 5 ML 20 49 Silver 04 ML 10

so Zinc 1480 ML 15

51 Iron 5 000 ML 20

Other Parameters Jml

52 Instantaneous Flow Site specific in CFS

53 Total Flow Site specific in CFS

54 pH Range for Class B Waters in NH 65-83 1MonthGrab13

55 pH Range for Class SB Waters in NH 65-8 1MonthGrab13

56 57 Daily maximum temperature shy Warm water fisheries

83 oF 1MonthGrab1 4

58 Daily maximum temperature - Cold water fisheries 68degF 1MonthGrab14

59 60 Maximum Change in Temperature in NH- Any Class B water body- Warm Water

5deg F 1MonthGrab14

61 Maximum Change in Temperature in NH- Any Class B water body shy Cold water and LakesPonds

3oF 1MonthGrab14

Footnotes

1 Although t he maximum values for TRC are 11ugl and 75 ug1 for freshwater and saltwater respectively the compliance limits are equal to the minimum level ( ML) of the test method used as listed in Appendix VI (ie Method 3305 20 ug1) 2 Limits for cyanide are based on EPAs water quality criteria expressed as micrograms per liter There is currently no EPA approved t est method for free cyanide Therefore total cyanide must be reported

6

3 Although the maximum values for cyanide are 52 ug1 and 10 ug1 for freshwater and saltwater respectively the compliance limits are equal to the minimum level (ML) of the Method 335 4 as listed in Appendix VI (ie 10 ug1) 4 BTEX = sum of Benzene Toluene Ethylbenzene and total Xylenes 5 Naphthalene can be reported as both a purgeable (VOC) and extractable (SVOC) organic compound If both VOC and SVOC are analyzed the highest value must be used unless the QC criteria for one of the analyses is not met In such cases the value from the analysis meeting the QC criteria must be used 6 The sum of individual phthalate compounds(not including the 34 Sis (2shyEthylhexyl) Phthalate The compliance limits are equal to the minimum level (ML) of the test method used as listed in Appendix VI Total values calculated for reporting on NOis and discharge monitoring reports shall be calculated by adding the measured concentration of each constituent If the measurement ofa constituent is less than the ML the permittee shall use a value of zero for that constituent For each test the permittee shall also attach the raw data for each constituent to the discharge monitoring report including the minimum level and minimum detection level for the analysis 7 Although the maximum value for the individual PAH compounds is 00038 ug1 the compliance limits are equal to the minimum level (ML) of the test method used as listed in Appendix VI 8 In the November 2002 WQC EPA has revised the definition of Total PCBs for aquatic life as total PCBs is the sum of all homologue all isomer all congener or all Oroclor analysesTotal values calculated for reporting on NOis and discharge monitoring reports shall be calculated by adding the measured concentration of each constituent If the measure of a constituent is less than the ML the permittee shall use a value of zero for that constituent For each test the permittee shall also attach the raw data for each constituent to the discharge monitoring report including the minimum level and minimum detection level for the analysis 9Aithough the maximum valuemiddot for total PCBs is 0000064 ug1 the compliance limit is equal to the minimum level (ML) of the test method used as listed in Appendix VI (ie 05 ug1 for Method 608 or 000005 ug1 when Method 1668a is approved) 10 Hardness Cadmium Chromium III Copper Lead Nickel Silver and Zinc are Hardness Dependent 11 For a Dilution Factor (DF) from 1 to 5 metals limits are calculated using DF times the base limit for the metal See Appendix IV For example iron limits are calculated using DF x 1000ugL (the iron base limit) Therefore DF is 15 the iron limit will be 1500 ugL DF 2 then iron limit =1000 x 2 =2000 ugL etc not to exceed the DF=5 12

Minimum Level (ML is the lowest level at which the analytical system gives a recognizable signal and acceptable calibration point for the analyte The ML represents the lowest-concentration at which an analyte can b~ measured with a known level of confidence The ML is calculated by multiplying the laboratoryshydetermined method detection limit by 318 (see 40 CFR Part 136 Appendix 8) 13

pH sampling for compliance with permit limits may be performed using field methods as provided for in EPA test Method 1501 14

Temperature sampling per Method 1701

7

January 31 2015

United States Environmental Protection Agency 5 Post Office Square Suite 100 Boston Massachusetts 02109-3912 Attn Remediation General Permit NOI Processing

Subject Notice of Intent for Remediation General Permit Groveton Wastewater Lagoons 10 Mechanic Street Groveton New Hampshire

Mr Alvarez

Stonecipher amp Clark Environmental Solutions LLC (SampC) is submitting the attached Remediation General Permit Notice of Intent for the above-referenced location (the ldquoSiterdquo) on behalf of Mr Bob Chapman Please find the NOI form under Attachment A The Site is the former Wausau Paper Mill and is located on two parcels located in Groveton NH along the Upper Ammonoosuc River Please refer to the enclosed locus map (Figure 1) The Site consists of three clarifiers on the 95 acre parcel located adjacent to the Upper Ammonoosuc River and the wastewater lagoonpolishing ponds are located on the 53 acre parcel also adjacent to the Ammonoosuc River

General Site Information

All processes pertaining to the paper mill have ceased and reportedly the lagoons were discharged and cleaned in 2008 under an individual NPDES permit (Permit No NH0001562) This permit expired in 2011 The lagoons have reportedly received no additional wastewater since then Water currently in the open-topped lagoon area and clarifiers is a result of stormwater collection (supernatant) over the past few years The RGP is being sought in order to discharge the remaining supernatant water as part of a final dewatering in order to install drain-holes and maintain the lagoons in an empty state as well as eventual demolition of the clarifiers

Discharge Information

The expired NPDES Individual Permit allowed discharge via Outfall 017 which discharges approximately 05 miles west into the Connecticut River Please see Attachment A for a aerial view of the Site including the approximate outfall locationThis RGP application seeks to maintain the the Outfall 017 discharge point

STON

ECIPH

ER amp C

LARK EN

VIRON

MEN

TAL SO

LUTIO

NS LLC

111 Saranac Street Stu

dio 8 L

ittleton N

H 03561 6035755154

ww

wston

eciph

erand

clarkcom

In December 2013 John King of EPA approved the Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire report prepared and submitted by Horizons Engineering Inc Please find this report under Attachment B This report outlined the results of the sampling plan completed in October 2013 which included samples from 9 locations the four quadrants of the main lagoon the two polishing ponds (lagoons) and the three clarifiers Three samples were taken at each of the nine sampling locations one grab sample from mid-depth between the supernatantsludge interface and the surface one grab sample from the supernatant interface and one sludge sample from the bottom The laboratory results are included in the decommissioning plan report and indicate that detected parameter concentrations in the samples obtained from mid-depth between the supernatant interface and the water surface were all within the former NPDES permit standards with the exception of the sample from Clarifier 1 for which we are NOT seeking coverage under the RGP NOI

The recommendation of the approved decommissioning report was to pump each lagoon and clarifier down to the supernatant interface individually into Outfall 017 (which discharges directly to the Connecticut River) Pumping rates were specified in the report based on BOD and TSS and turbidity monitoring was recommended in order to determine when interface was reached

In November 2014 SampC oversaw discharge of the supernatant from the lagoon area as specified in the approved decommissioning report The pumping rate was greatly reduced from the allowable rate in the plan due to availability of pumping equipment as well as field conditions Turbidity was closely monitored Field observations indicated that the line between the supernatant and the interface was quite sharply defined Close monitoring allowed SampC to be confident in the discharge of only supernatant

Contaminant Information

For the purposes of this permit application it is assumed that the Site falls under Category III subcategory B Upon reviewing Appendix III regarding Effluent Limits and Monitoring Requirements it appears that the supernatant laboratory results for all sampled locations with the exception of Clarifier 1 average 19 mgl TSS which is well below the specified TSS effluent limit of 30 mgl TSS (monthly average) Laboratory results from supernatant collected from Clarifier 3 yielded a TSS value of 45 mgl Please note that using this TSS value as a maximum daily TSS value in the NOI application under Appendix III will therefore skew the actual amount of daily TSS as the dewatering of Clarifier 3 is anticipated at a lesser rate than the 1000 gpm maximum In addition the volume of water in Clarifier 3 (reportedly 9 feet) will be discharged prior to achieving a 24-hr time period

Group I PAHs and Group II PAHs fall below the respective 100 ugl and 1000 ugl daily limits

SampC collected and submitted to the laboratory a confirmatory sample of the lagoon supernatant on December 3 2014 This sample was tested for Volatile Organic Compounds (VOCs) Group I PAHs Group II PAHs and all required metals to be tested under Appendix III Category III subcategory B with the exception of antimony copper nickel zinc and iron

Once the supernatantsludge interface has been reached the plan is to dewater the remaining water overland via NHDES Temporary Groundwater Discharge Permit This will NOT be released to any surface waters

Treatment System Information

No treatment is proposed during dewatering The pumping discharge rate is proposed to be a maximum of 1000 gpm

Receiving Surface Water(s) Information

Discharge will occur approximately 05 miles away to Outfall 017 via underground 32rdquo pipe into the Connecticut River

Endangered Species Act amp National Historic Preservation Act Reviews

SampC has received verbal response from United States Fish and Wildlife Service that the discharge activities are ldquounlikely to adversely affectrdquo listed species or critical habitat When official sign-off is received SampC will forward that response

Under Attachment D please find the correspondence with New Hampshire Division of Historical Resources indicating that findings for this project considered ldquoNo Historic Properties Affectedrdquo

Please contact the undersigned if you have any questions or require additional information

Sincerely

Sylvia A Clark Co-OwnerProject Manager Stonecipher amp Clark Environmental Solutions LLC Office 6035755154 Cell 8027341403 sclarkstonecipherandclarkcom

Attachments Figure 1 ndash Site Aerial Map Figure 2 ndash Treatment System Flow Diagram Attachment A ndash Notice of Intent Form Attachment B ndash EPA Approved Decommissioning Plan Attachment C ndash December 3 2014 Laboratory Results Attachment D ndash NH DHR Correspondence Attachment E - US FWS Correspondence (To be forwarded)

cc Jeff Andrews NHDES

Sylvia
Stamp

Figure 1

Lagoon

Clarifiers

Outfall 017

Stonecipheramp Clark Environmental Solutions LLC 111 Saranac Street Studio 8

Littleton New Hampshire 03561

6035755154

Groveton Wastewater Lagoons amp Clarifiers Groveton NH

SampC Project 2014-062

Aerial Map

Figure 2

LAGOON AREA

CLARIFIER 2

CLARIFIER 1

CLARIFIER 3

UPPER AMMONOOSUC RIVER

MONITORING

CHAMBER

32 PIPE DISCHARGES

APPROX 05 MILES WEST

INTO THE CONNECTICUT

RIVER (OUTFALL 017)

STONECIPHER amp CLARK

ENVIRONMENTAL SOLUTIONS LLC

111 SARANAC STREET STUDIO 8

LITTLETON NEW HAMPSHIRE 03561

6035755154

GROVETON WASTEWATER LAGOONS

GROVETON NEW HAMPSHIRE

FLOW SCHEMATIC

Attachment A

NPDES Permit No MAG910000 NPDES Permit No NHG910000

B Suggested Form for Notice of Intent (NOI) for the Remediation General Permit

1 General facilitysite information Please provide the following information about the site

a) Name of facilitysite Facilitysite mailing address

Location of facilitysite

longitude_______________ latitude_______________

Facility SIC code(s)

Street

b) Name of facilitysite owner Town

Email address of facilitysite owner State Zip County

Telephone no of facilitysite owner

Fax no of facilitysite owner Owner is (check one) 1 Federal____ 2 StateTribal____ 3 Private____ 4 Other ____ if so describe

Address of owner (if different from site)

Street

Town State Zip County

c) Legal name of operator Operator telephone no

Operator fax no Operator email

Operator contact name and title

Address of operator (if different from owner)

Street

Town State Zip County

Remediation General Permit Page 10 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

d) Check Y for Ayes or N for Ano for the following 1 Has a prior NPDES permit exclusion been granted for the discharge Y___ N___ if Y number_________________ 2 Has a prior NPDES application (Form 1 amp 2C) ever been filed for the discharge Y___ N___ if Y date and tracking __________________________________________________________________ 3 Is the discharge a ldquonew dischargerdquo as defined by 40 CFR 1222 Y___ N___ 4 For sites in Massachusetts is the discharge covered under the Massachusetts Contingency Plan (MCP) and exempt from state permitting Y___ N___

e) Is sitefacility subject to any State permitting license f) Is the sitefacility covered by any other EPA permit including or other action which is causing the generation of 1 Multi-Sector General Permit Y___ N___ discharge Y___ N___ if Y number_______________ If Y please list 2 Final Dewatering General Permit Y___ N___ 1 site identification assigned by the state of NH or if Y number________________ MA_________________________________________ 3 EPA Construction General Permit Y___ N___ 2 permit or license assigned____________________ if Y number _______________ 3 state agency contact information name location and 4 Individual NPDES permit Y___ N___ telephone number if Y number_____________

5 any other water quality related individual or general permit Y___ N___ if Y number______________

g) Is the sitefacility located within or does it discharge to an Area of Critical Environmental Concern (ACEC) Y____ N____

h) Based on the facilitysite information and any historical sampling data identify the sub-category into which the potential discharge falls Activity Category Activity Sub-Category I - Petroleum Related Site Remediation A Gasoline Only Sites ____

B Fuel Oils and Other Oil Sites (including Residential Non-Business Remediation Discharges) ____ C Petroleum Sites with Additional Contamination ____

II - Non Petroleum Site Remediation A Volatile Organic Compound (VOC) Only Sites _____ B VOC Sites with Additional Contamination ____ C Primarily Heavy Metal Sites ____

III - Contaminated Construction Dewatering A General Urban Fill Sites ____ B Known Contaminated Sites ____

Remediation General Permit Page 11 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

IV - Miscellaneous Related Discharges A Aquifer Pump Testing to Evaluate Formerly Contaminated Sites ____ B Well DevelopmentRehabilitation at ContaminatedFormerly Contaminated Sites ____ C Hydrostatic Testing of Pipelines and Tanks ____ D Long-Term Remediation of Contaminated Sumps and Dikes ____ E Short-term Contaminated Dredging Drain Back Waters (if not covered by 401404 permit) ____

2 Discharge information Please provide information about the discharge (attaching additional sheets as necessary) including

a) Describe the discharge activities for which the ownerapplicant is seeking coverage

b) Provide the following information about each discharge

1) Number of discharge points

2) What is the maximum and average flow rate of discharge (in cubic feet per second ft3s) Max flow____________ Is maximum flow a design value Y___ N____ Average flow (include units) __________ Is average flow a design value or estimate _________

3) Latitude and longitude of each discharge within 100 feet pt1 lat_____________ long_____________ pt2 lat_____________ long_____________ pt3 lat_____________ long_____________ pt4 lat_____________ long_____________ pt5 lat_____________ long_____________ pt6 lat_____________ long_____________ pt7 lat_____________ long_____________ pt8 lat_____________ long_____________ etc

4) If hydrostatic testing total volume of the discharge (gals)_________

5) Is the discharge intermittent ____ or seasonal____ Is discharge ongoing Y ____ N______

c) Expected dates of discharge (mmddyy) start_____________ end_________________ d) Please attach a line drawing or flow schematic showing water flow through the facility including 1 sources of intake water 2 contributing flow from the operation 3 treatment units and 4 discharge points and receiving waters(s)

Remediation General Permit Page 12 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

3 Contaminant information a) Based on the sub-category selected (see Appendix III) indicate whether each listed chemical is believed present or believed absent in the potential discharge Attach additional sheets as needed

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

1 Total Suspended Solids (TSS) 2 Total Residual Chlorine (TRC) 3 Total Petroleum Hydrocarbons (TPH) 4 Cyanide (CN) 57125 5 Benzene (B) 71432 6 Toluene (T) 108883 7 Ethylbenzene (E) 100414 8 (mpo) Xylenes (X) 108883

106423 95476

1330207

9 Total BTEX 2 na 10 Ethylene Dibromide (EDB) (12- Dibromoethane) 3

106934

11 Methyl-tert-Butyl Ether (MtBE)

1634044

12 tert-Butyl Alcohol (TBA) (Tertiary-Butanol)

75650

Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI 2 BTEX = Sum of Benzene Toluene Ethylbenzene total Xylenes 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England

Remediation General Permit Page 13 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
          13. RadioButtonList[0] 3
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
                  3. TextField36[0] 29
                  4. TextField37[0] 22
                  5. TextField38[0] estimate
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                  8. DateTimeField1[0] 312015
                  9. DateTimeField2[0] 1212015
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                  11. TextField44[0] NA
                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
                                          11. TextField59[0] Class B
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Page 4: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Parameter

Effluent LimitlMethodLML (All Effluent Limits are shown as Daily

Maximum Limit unless denoted by a in that case it will be a Monthly Average

Limit)

8 (mpo) Xylenes (X) (limited as ugL total BTEX) Me8260C ML 2ugL

9 Total Benzene Toluene Ethyl Benzene and Xylenes (BTEX) 4

100 ugL Memiddot8260C ML 2ugL

10 Ethylene Dibromide (EDB) ( 12- Dibromoethane) 005 ug1 Me8260C ML 10ugL

11 Methyl-tert-Butyl Ether (MtBE) 700 ugIMe8260CML 10ugL

12tert-Butyl Alcohol (TBA) (TertiaryButanol)

Monitor Only (ugL)Me 8260C ML 10ugL

13 tert-Amyl Methyl Ether (TAME) Monitor Only(ugL)Me8260CML 10ugL

14 Naphthalene s 20 ugL Me8260CML 2ugL 15 Carbon Tetrachloride 44 ugL Me 8260C ML SugL 16 12 Dichlorobenzene (o-DCB)

600 ugL Me8260C ML 5ugL

17 13 Dichlorobenzene (m-DCB)

320 ugL Me8260C ML 5ugL

18 14 Dichlorobenzene (p-DCB)

50 ugL Me8260C ML 5ugL

18a Total dichlorobenzene 763 ugL shy NH onlyMe 8260C ML 5ugL 19 1 1 Dichloroethane (DCA) 70 ugL Me8260C ML 5ugL 20 1 2 Dichloroethane (DCA) 50 ugL Me8260C ML 5ugL 21 11 Dichloroethene (DCE) 3 2 ugLMe 8260C ML 5ugL 22 cis-12 Dichloroethene (DCE) 70 ugLMe8260C ML 5ugL

23 Methylene Chloride 46 ugLMe8260C ML 5ugjl 24 Tetrachloroethene JPCE) 50 ugLMe8260C ML 5ugL 25 111 Trichloro-ethane (TCA) 200 ugLMe8260C ML 5ugL

26 112 Trichloro-et hane (TCA) 50 ugL Me8260C ML 5ugL

27 Trichloroethene (TCE) 50 ugL Me8260C ML 5ugL 28 Vinyl Chloride (Chloroethene) 20 ugL Me8260C ML 5ugL

29 Acetone Monitor Only(ugL)Me 8260CML 50ugL 30 14 Dioxane Monitor Only Me1624CML 50ugL

31 Total Phenols 300 ugL Me 4201amp4202ML 2 ugL Me 4204 ML 50ugL

32 Pentachlorophenol (PCP) 10 ugL Me8270DML 5ugLMe604 amp625ML 10u_gil

33 Total Phthalates _(Phthalate estersJ 6

30 ugL Me8270DML 5ugL Me606ML 10uqLamp Me 625ML 5uqL

4

Effluent LimitlMethodlML (All Effluent Limits are shown as Daily

Parameter Maximum Limit unless denoted by a in that case it will be a Monthly Average

Limit) 34 Bis (2-Ethylhexyl) 60 ugL Me8270DML Phthalate [Di- (ethylhexyl) SugLMe606ML lOugL amp Me625ML Phthalat~l SuqL 35 Total Group I Polycycl ic v 100 ugLAromatic Hydrocarbons ( PAH)

00038 ugL Me8270D ML SugL v a Benzo(a) Anthracene 7 Me610ML Suqjlamp Me625ML SugL 00038 ugL Me8270D ML SugL v b Benzo(a) Pyrene 7 Me610ML SugLamp Me625ML SuqL 00038 ugL Me8270D ML SugLv c Benzo(b)Fiuoranthene 7 Me610ML SugLamp Me625ML SuqL 00038 ugL Me8270D ML SugLv d Benzo(k)Fiuoranthene 7 Me610ML SugLamp Me625ML SugL 0 0038 ugL Me8270DML Sug L v e Chrysene 7 Me610ML SugLamp Me625ML Sugjl 00038 ugL Me8270DML SugLv f Dibenzo(ah)anthracene 7 Me610ML SugLamp Me625ML SugL 00038 ugL Me8270DML SugLv g Indeno(123-cd) Pyrene 7

Me610ML SugLamp Me625ML5ugL 36 Total Group II Polycyclic

100 ugLAromatic Hydrocarbons (PAH)

XMe8270DML 5ugLMe610 ML h Acenaphthene

SuCJL amp Me625ML SugL XMe 8270DML 5ugLMe610 ML

i Acenaphthylene SugL amp Me625ML SugL XMe8270DML 5ugLMe610ML

j Anthracene SugL amp Me625ML SugL XMe8270DML 5ugLMe610ML

k Benzo(ghi) Perylene SugL amp Me625ML SLJg[L XMe8270DML 5ugLMe610MLv I Fluoranthene SugL amp Me625ML SLJgL XMe8270DML 5ugLMe610ML

m Fluorene SugL amp Me625ML Sugl 20 ug1 Me8270ML SugL Me610 ML

n Naphthalene 5 Sugl amp Me625ML Sug L XMe8270DML 5uglMe610Ml

o Phenanthrene SugL amp Me625ML Su_gfl XMe8270DML5uglMe610ML SugL v p Pyrene amp Me6251ML SugL

37 Total Polychlorinated 0000064 uglMe 608 Ml 05 ugLBiphenyls (PCBs) 8bull 9

v Monitor onlyMe 3000 Ml 100 ugl38 Chloride

5

Metal parameter

Total Recoverable NH[Metal Limit H 10 =25 mgll

CaC03 Units = ugll 1lLlU

Minimum levei=ML

Freshwater Limits

2206 dilution

39 Antimony 141 ML 10

40 Arsenic 500 ML 20

41 Cadmium 16 ML 10

42 Chromium III (trivalent) 1385 ML 15

43 Chromium VI (hexavalent) 570 ML 10

44 Copper 142 ML 15 45 Lead 05 ML 20 46 Mercury 09 ML 02

47 Nickel 807 ML 20 48 Selenium 5 ML 20 49 Silver 04 ML 10

so Zinc 1480 ML 15

51 Iron 5 000 ML 20

Other Parameters Jml

52 Instantaneous Flow Site specific in CFS

53 Total Flow Site specific in CFS

54 pH Range for Class B Waters in NH 65-83 1MonthGrab13

55 pH Range for Class SB Waters in NH 65-8 1MonthGrab13

56 57 Daily maximum temperature shy Warm water fisheries

83 oF 1MonthGrab1 4

58 Daily maximum temperature - Cold water fisheries 68degF 1MonthGrab14

59 60 Maximum Change in Temperature in NH- Any Class B water body- Warm Water

5deg F 1MonthGrab14

61 Maximum Change in Temperature in NH- Any Class B water body shy Cold water and LakesPonds

3oF 1MonthGrab14

Footnotes

1 Although t he maximum values for TRC are 11ugl and 75 ug1 for freshwater and saltwater respectively the compliance limits are equal to the minimum level ( ML) of the test method used as listed in Appendix VI (ie Method 3305 20 ug1) 2 Limits for cyanide are based on EPAs water quality criteria expressed as micrograms per liter There is currently no EPA approved t est method for free cyanide Therefore total cyanide must be reported

6

3 Although the maximum values for cyanide are 52 ug1 and 10 ug1 for freshwater and saltwater respectively the compliance limits are equal to the minimum level (ML) of the Method 335 4 as listed in Appendix VI (ie 10 ug1) 4 BTEX = sum of Benzene Toluene Ethylbenzene and total Xylenes 5 Naphthalene can be reported as both a purgeable (VOC) and extractable (SVOC) organic compound If both VOC and SVOC are analyzed the highest value must be used unless the QC criteria for one of the analyses is not met In such cases the value from the analysis meeting the QC criteria must be used 6 The sum of individual phthalate compounds(not including the 34 Sis (2shyEthylhexyl) Phthalate The compliance limits are equal to the minimum level (ML) of the test method used as listed in Appendix VI Total values calculated for reporting on NOis and discharge monitoring reports shall be calculated by adding the measured concentration of each constituent If the measurement ofa constituent is less than the ML the permittee shall use a value of zero for that constituent For each test the permittee shall also attach the raw data for each constituent to the discharge monitoring report including the minimum level and minimum detection level for the analysis 7 Although the maximum value for the individual PAH compounds is 00038 ug1 the compliance limits are equal to the minimum level (ML) of the test method used as listed in Appendix VI 8 In the November 2002 WQC EPA has revised the definition of Total PCBs for aquatic life as total PCBs is the sum of all homologue all isomer all congener or all Oroclor analysesTotal values calculated for reporting on NOis and discharge monitoring reports shall be calculated by adding the measured concentration of each constituent If the measure of a constituent is less than the ML the permittee shall use a value of zero for that constituent For each test the permittee shall also attach the raw data for each constituent to the discharge monitoring report including the minimum level and minimum detection level for the analysis 9Aithough the maximum valuemiddot for total PCBs is 0000064 ug1 the compliance limit is equal to the minimum level (ML) of the test method used as listed in Appendix VI (ie 05 ug1 for Method 608 or 000005 ug1 when Method 1668a is approved) 10 Hardness Cadmium Chromium III Copper Lead Nickel Silver and Zinc are Hardness Dependent 11 For a Dilution Factor (DF) from 1 to 5 metals limits are calculated using DF times the base limit for the metal See Appendix IV For example iron limits are calculated using DF x 1000ugL (the iron base limit) Therefore DF is 15 the iron limit will be 1500 ugL DF 2 then iron limit =1000 x 2 =2000 ugL etc not to exceed the DF=5 12

Minimum Level (ML is the lowest level at which the analytical system gives a recognizable signal and acceptable calibration point for the analyte The ML represents the lowest-concentration at which an analyte can b~ measured with a known level of confidence The ML is calculated by multiplying the laboratoryshydetermined method detection limit by 318 (see 40 CFR Part 136 Appendix 8) 13

pH sampling for compliance with permit limits may be performed using field methods as provided for in EPA test Method 1501 14

Temperature sampling per Method 1701

7

January 31 2015

United States Environmental Protection Agency 5 Post Office Square Suite 100 Boston Massachusetts 02109-3912 Attn Remediation General Permit NOI Processing

Subject Notice of Intent for Remediation General Permit Groveton Wastewater Lagoons 10 Mechanic Street Groveton New Hampshire

Mr Alvarez

Stonecipher amp Clark Environmental Solutions LLC (SampC) is submitting the attached Remediation General Permit Notice of Intent for the above-referenced location (the ldquoSiterdquo) on behalf of Mr Bob Chapman Please find the NOI form under Attachment A The Site is the former Wausau Paper Mill and is located on two parcels located in Groveton NH along the Upper Ammonoosuc River Please refer to the enclosed locus map (Figure 1) The Site consists of three clarifiers on the 95 acre parcel located adjacent to the Upper Ammonoosuc River and the wastewater lagoonpolishing ponds are located on the 53 acre parcel also adjacent to the Ammonoosuc River

General Site Information

All processes pertaining to the paper mill have ceased and reportedly the lagoons were discharged and cleaned in 2008 under an individual NPDES permit (Permit No NH0001562) This permit expired in 2011 The lagoons have reportedly received no additional wastewater since then Water currently in the open-topped lagoon area and clarifiers is a result of stormwater collection (supernatant) over the past few years The RGP is being sought in order to discharge the remaining supernatant water as part of a final dewatering in order to install drain-holes and maintain the lagoons in an empty state as well as eventual demolition of the clarifiers

Discharge Information

The expired NPDES Individual Permit allowed discharge via Outfall 017 which discharges approximately 05 miles west into the Connecticut River Please see Attachment A for a aerial view of the Site including the approximate outfall locationThis RGP application seeks to maintain the the Outfall 017 discharge point

STON

ECIPH

ER amp C

LARK EN

VIRON

MEN

TAL SO

LUTIO

NS LLC

111 Saranac Street Stu

dio 8 L

ittleton N

H 03561 6035755154

ww

wston

eciph

erand

clarkcom

In December 2013 John King of EPA approved the Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire report prepared and submitted by Horizons Engineering Inc Please find this report under Attachment B This report outlined the results of the sampling plan completed in October 2013 which included samples from 9 locations the four quadrants of the main lagoon the two polishing ponds (lagoons) and the three clarifiers Three samples were taken at each of the nine sampling locations one grab sample from mid-depth between the supernatantsludge interface and the surface one grab sample from the supernatant interface and one sludge sample from the bottom The laboratory results are included in the decommissioning plan report and indicate that detected parameter concentrations in the samples obtained from mid-depth between the supernatant interface and the water surface were all within the former NPDES permit standards with the exception of the sample from Clarifier 1 for which we are NOT seeking coverage under the RGP NOI

The recommendation of the approved decommissioning report was to pump each lagoon and clarifier down to the supernatant interface individually into Outfall 017 (which discharges directly to the Connecticut River) Pumping rates were specified in the report based on BOD and TSS and turbidity monitoring was recommended in order to determine when interface was reached

In November 2014 SampC oversaw discharge of the supernatant from the lagoon area as specified in the approved decommissioning report The pumping rate was greatly reduced from the allowable rate in the plan due to availability of pumping equipment as well as field conditions Turbidity was closely monitored Field observations indicated that the line between the supernatant and the interface was quite sharply defined Close monitoring allowed SampC to be confident in the discharge of only supernatant

Contaminant Information

For the purposes of this permit application it is assumed that the Site falls under Category III subcategory B Upon reviewing Appendix III regarding Effluent Limits and Monitoring Requirements it appears that the supernatant laboratory results for all sampled locations with the exception of Clarifier 1 average 19 mgl TSS which is well below the specified TSS effluent limit of 30 mgl TSS (monthly average) Laboratory results from supernatant collected from Clarifier 3 yielded a TSS value of 45 mgl Please note that using this TSS value as a maximum daily TSS value in the NOI application under Appendix III will therefore skew the actual amount of daily TSS as the dewatering of Clarifier 3 is anticipated at a lesser rate than the 1000 gpm maximum In addition the volume of water in Clarifier 3 (reportedly 9 feet) will be discharged prior to achieving a 24-hr time period

Group I PAHs and Group II PAHs fall below the respective 100 ugl and 1000 ugl daily limits

SampC collected and submitted to the laboratory a confirmatory sample of the lagoon supernatant on December 3 2014 This sample was tested for Volatile Organic Compounds (VOCs) Group I PAHs Group II PAHs and all required metals to be tested under Appendix III Category III subcategory B with the exception of antimony copper nickel zinc and iron

Once the supernatantsludge interface has been reached the plan is to dewater the remaining water overland via NHDES Temporary Groundwater Discharge Permit This will NOT be released to any surface waters

Treatment System Information

No treatment is proposed during dewatering The pumping discharge rate is proposed to be a maximum of 1000 gpm

Receiving Surface Water(s) Information

Discharge will occur approximately 05 miles away to Outfall 017 via underground 32rdquo pipe into the Connecticut River

Endangered Species Act amp National Historic Preservation Act Reviews

SampC has received verbal response from United States Fish and Wildlife Service that the discharge activities are ldquounlikely to adversely affectrdquo listed species or critical habitat When official sign-off is received SampC will forward that response

Under Attachment D please find the correspondence with New Hampshire Division of Historical Resources indicating that findings for this project considered ldquoNo Historic Properties Affectedrdquo

Please contact the undersigned if you have any questions or require additional information

Sincerely

Sylvia A Clark Co-OwnerProject Manager Stonecipher amp Clark Environmental Solutions LLC Office 6035755154 Cell 8027341403 sclarkstonecipherandclarkcom

Attachments Figure 1 ndash Site Aerial Map Figure 2 ndash Treatment System Flow Diagram Attachment A ndash Notice of Intent Form Attachment B ndash EPA Approved Decommissioning Plan Attachment C ndash December 3 2014 Laboratory Results Attachment D ndash NH DHR Correspondence Attachment E - US FWS Correspondence (To be forwarded)

cc Jeff Andrews NHDES

Sylvia
Stamp

Figure 1

Lagoon

Clarifiers

Outfall 017

Stonecipheramp Clark Environmental Solutions LLC 111 Saranac Street Studio 8

Littleton New Hampshire 03561

6035755154

Groveton Wastewater Lagoons amp Clarifiers Groveton NH

SampC Project 2014-062

Aerial Map

Figure 2

LAGOON AREA

CLARIFIER 2

CLARIFIER 1

CLARIFIER 3

UPPER AMMONOOSUC RIVER

MONITORING

CHAMBER

32 PIPE DISCHARGES

APPROX 05 MILES WEST

INTO THE CONNECTICUT

RIVER (OUTFALL 017)

STONECIPHER amp CLARK

ENVIRONMENTAL SOLUTIONS LLC

111 SARANAC STREET STUDIO 8

LITTLETON NEW HAMPSHIRE 03561

6035755154

GROVETON WASTEWATER LAGOONS

GROVETON NEW HAMPSHIRE

FLOW SCHEMATIC

Attachment A

NPDES Permit No MAG910000 NPDES Permit No NHG910000

B Suggested Form for Notice of Intent (NOI) for the Remediation General Permit

1 General facilitysite information Please provide the following information about the site

a) Name of facilitysite Facilitysite mailing address

Location of facilitysite

longitude_______________ latitude_______________

Facility SIC code(s)

Street

b) Name of facilitysite owner Town

Email address of facilitysite owner State Zip County

Telephone no of facilitysite owner

Fax no of facilitysite owner Owner is (check one) 1 Federal____ 2 StateTribal____ 3 Private____ 4 Other ____ if so describe

Address of owner (if different from site)

Street

Town State Zip County

c) Legal name of operator Operator telephone no

Operator fax no Operator email

Operator contact name and title

Address of operator (if different from owner)

Street

Town State Zip County

Remediation General Permit Page 10 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

d) Check Y for Ayes or N for Ano for the following 1 Has a prior NPDES permit exclusion been granted for the discharge Y___ N___ if Y number_________________ 2 Has a prior NPDES application (Form 1 amp 2C) ever been filed for the discharge Y___ N___ if Y date and tracking __________________________________________________________________ 3 Is the discharge a ldquonew dischargerdquo as defined by 40 CFR 1222 Y___ N___ 4 For sites in Massachusetts is the discharge covered under the Massachusetts Contingency Plan (MCP) and exempt from state permitting Y___ N___

e) Is sitefacility subject to any State permitting license f) Is the sitefacility covered by any other EPA permit including or other action which is causing the generation of 1 Multi-Sector General Permit Y___ N___ discharge Y___ N___ if Y number_______________ If Y please list 2 Final Dewatering General Permit Y___ N___ 1 site identification assigned by the state of NH or if Y number________________ MA_________________________________________ 3 EPA Construction General Permit Y___ N___ 2 permit or license assigned____________________ if Y number _______________ 3 state agency contact information name location and 4 Individual NPDES permit Y___ N___ telephone number if Y number_____________

5 any other water quality related individual or general permit Y___ N___ if Y number______________

g) Is the sitefacility located within or does it discharge to an Area of Critical Environmental Concern (ACEC) Y____ N____

h) Based on the facilitysite information and any historical sampling data identify the sub-category into which the potential discharge falls Activity Category Activity Sub-Category I - Petroleum Related Site Remediation A Gasoline Only Sites ____

B Fuel Oils and Other Oil Sites (including Residential Non-Business Remediation Discharges) ____ C Petroleum Sites with Additional Contamination ____

II - Non Petroleum Site Remediation A Volatile Organic Compound (VOC) Only Sites _____ B VOC Sites with Additional Contamination ____ C Primarily Heavy Metal Sites ____

III - Contaminated Construction Dewatering A General Urban Fill Sites ____ B Known Contaminated Sites ____

Remediation General Permit Page 11 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

IV - Miscellaneous Related Discharges A Aquifer Pump Testing to Evaluate Formerly Contaminated Sites ____ B Well DevelopmentRehabilitation at ContaminatedFormerly Contaminated Sites ____ C Hydrostatic Testing of Pipelines and Tanks ____ D Long-Term Remediation of Contaminated Sumps and Dikes ____ E Short-term Contaminated Dredging Drain Back Waters (if not covered by 401404 permit) ____

2 Discharge information Please provide information about the discharge (attaching additional sheets as necessary) including

a) Describe the discharge activities for which the ownerapplicant is seeking coverage

b) Provide the following information about each discharge

1) Number of discharge points

2) What is the maximum and average flow rate of discharge (in cubic feet per second ft3s) Max flow____________ Is maximum flow a design value Y___ N____ Average flow (include units) __________ Is average flow a design value or estimate _________

3) Latitude and longitude of each discharge within 100 feet pt1 lat_____________ long_____________ pt2 lat_____________ long_____________ pt3 lat_____________ long_____________ pt4 lat_____________ long_____________ pt5 lat_____________ long_____________ pt6 lat_____________ long_____________ pt7 lat_____________ long_____________ pt8 lat_____________ long_____________ etc

4) If hydrostatic testing total volume of the discharge (gals)_________

5) Is the discharge intermittent ____ or seasonal____ Is discharge ongoing Y ____ N______

c) Expected dates of discharge (mmddyy) start_____________ end_________________ d) Please attach a line drawing or flow schematic showing water flow through the facility including 1 sources of intake water 2 contributing flow from the operation 3 treatment units and 4 discharge points and receiving waters(s)

Remediation General Permit Page 12 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

3 Contaminant information a) Based on the sub-category selected (see Appendix III) indicate whether each listed chemical is believed present or believed absent in the potential discharge Attach additional sheets as needed

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

1 Total Suspended Solids (TSS) 2 Total Residual Chlorine (TRC) 3 Total Petroleum Hydrocarbons (TPH) 4 Cyanide (CN) 57125 5 Benzene (B) 71432 6 Toluene (T) 108883 7 Ethylbenzene (E) 100414 8 (mpo) Xylenes (X) 108883

106423 95476

1330207

9 Total BTEX 2 na 10 Ethylene Dibromide (EDB) (12- Dibromoethane) 3

106934

11 Methyl-tert-Butyl Ether (MtBE)

1634044

12 tert-Butyl Alcohol (TBA) (Tertiary-Butanol)

75650

Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI 2 BTEX = Sum of Benzene Toluene Ethylbenzene total Xylenes 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England

Remediation General Permit Page 13 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
            1. Page11[0]
              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
                  3. TextField36[0] 29
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                  5. TextField38[0] estimate
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                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
                                          11. TextField59[0] Class B
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Page 5: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Effluent LimitlMethodlML (All Effluent Limits are shown as Daily

Parameter Maximum Limit unless denoted by a in that case it will be a Monthly Average

Limit) 34 Bis (2-Ethylhexyl) 60 ugL Me8270DML Phthalate [Di- (ethylhexyl) SugLMe606ML lOugL amp Me625ML Phthalat~l SuqL 35 Total Group I Polycycl ic v 100 ugLAromatic Hydrocarbons ( PAH)

00038 ugL Me8270D ML SugL v a Benzo(a) Anthracene 7 Me610ML Suqjlamp Me625ML SugL 00038 ugL Me8270D ML SugL v b Benzo(a) Pyrene 7 Me610ML SugLamp Me625ML SuqL 00038 ugL Me8270D ML SugLv c Benzo(b)Fiuoranthene 7 Me610ML SugLamp Me625ML SuqL 00038 ugL Me8270D ML SugLv d Benzo(k)Fiuoranthene 7 Me610ML SugLamp Me625ML SugL 0 0038 ugL Me8270DML Sug L v e Chrysene 7 Me610ML SugLamp Me625ML Sugjl 00038 ugL Me8270DML SugLv f Dibenzo(ah)anthracene 7 Me610ML SugLamp Me625ML SugL 00038 ugL Me8270DML SugLv g Indeno(123-cd) Pyrene 7

Me610ML SugLamp Me625ML5ugL 36 Total Group II Polycyclic

100 ugLAromatic Hydrocarbons (PAH)

XMe8270DML 5ugLMe610 ML h Acenaphthene

SuCJL amp Me625ML SugL XMe 8270DML 5ugLMe610 ML

i Acenaphthylene SugL amp Me625ML SugL XMe8270DML 5ugLMe610ML

j Anthracene SugL amp Me625ML SugL XMe8270DML 5ugLMe610ML

k Benzo(ghi) Perylene SugL amp Me625ML SLJg[L XMe8270DML 5ugLMe610MLv I Fluoranthene SugL amp Me625ML SLJgL XMe8270DML 5ugLMe610ML

m Fluorene SugL amp Me625ML Sugl 20 ug1 Me8270ML SugL Me610 ML

n Naphthalene 5 Sugl amp Me625ML Sug L XMe8270DML 5uglMe610Ml

o Phenanthrene SugL amp Me625ML Su_gfl XMe8270DML5uglMe610ML SugL v p Pyrene amp Me6251ML SugL

37 Total Polychlorinated 0000064 uglMe 608 Ml 05 ugLBiphenyls (PCBs) 8bull 9

v Monitor onlyMe 3000 Ml 100 ugl38 Chloride

5

Metal parameter

Total Recoverable NH[Metal Limit H 10 =25 mgll

CaC03 Units = ugll 1lLlU

Minimum levei=ML

Freshwater Limits

2206 dilution

39 Antimony 141 ML 10

40 Arsenic 500 ML 20

41 Cadmium 16 ML 10

42 Chromium III (trivalent) 1385 ML 15

43 Chromium VI (hexavalent) 570 ML 10

44 Copper 142 ML 15 45 Lead 05 ML 20 46 Mercury 09 ML 02

47 Nickel 807 ML 20 48 Selenium 5 ML 20 49 Silver 04 ML 10

so Zinc 1480 ML 15

51 Iron 5 000 ML 20

Other Parameters Jml

52 Instantaneous Flow Site specific in CFS

53 Total Flow Site specific in CFS

54 pH Range for Class B Waters in NH 65-83 1MonthGrab13

55 pH Range for Class SB Waters in NH 65-8 1MonthGrab13

56 57 Daily maximum temperature shy Warm water fisheries

83 oF 1MonthGrab1 4

58 Daily maximum temperature - Cold water fisheries 68degF 1MonthGrab14

59 60 Maximum Change in Temperature in NH- Any Class B water body- Warm Water

5deg F 1MonthGrab14

61 Maximum Change in Temperature in NH- Any Class B water body shy Cold water and LakesPonds

3oF 1MonthGrab14

Footnotes

1 Although t he maximum values for TRC are 11ugl and 75 ug1 for freshwater and saltwater respectively the compliance limits are equal to the minimum level ( ML) of the test method used as listed in Appendix VI (ie Method 3305 20 ug1) 2 Limits for cyanide are based on EPAs water quality criteria expressed as micrograms per liter There is currently no EPA approved t est method for free cyanide Therefore total cyanide must be reported

6

3 Although the maximum values for cyanide are 52 ug1 and 10 ug1 for freshwater and saltwater respectively the compliance limits are equal to the minimum level (ML) of the Method 335 4 as listed in Appendix VI (ie 10 ug1) 4 BTEX = sum of Benzene Toluene Ethylbenzene and total Xylenes 5 Naphthalene can be reported as both a purgeable (VOC) and extractable (SVOC) organic compound If both VOC and SVOC are analyzed the highest value must be used unless the QC criteria for one of the analyses is not met In such cases the value from the analysis meeting the QC criteria must be used 6 The sum of individual phthalate compounds(not including the 34 Sis (2shyEthylhexyl) Phthalate The compliance limits are equal to the minimum level (ML) of the test method used as listed in Appendix VI Total values calculated for reporting on NOis and discharge monitoring reports shall be calculated by adding the measured concentration of each constituent If the measurement ofa constituent is less than the ML the permittee shall use a value of zero for that constituent For each test the permittee shall also attach the raw data for each constituent to the discharge monitoring report including the minimum level and minimum detection level for the analysis 7 Although the maximum value for the individual PAH compounds is 00038 ug1 the compliance limits are equal to the minimum level (ML) of the test method used as listed in Appendix VI 8 In the November 2002 WQC EPA has revised the definition of Total PCBs for aquatic life as total PCBs is the sum of all homologue all isomer all congener or all Oroclor analysesTotal values calculated for reporting on NOis and discharge monitoring reports shall be calculated by adding the measured concentration of each constituent If the measure of a constituent is less than the ML the permittee shall use a value of zero for that constituent For each test the permittee shall also attach the raw data for each constituent to the discharge monitoring report including the minimum level and minimum detection level for the analysis 9Aithough the maximum valuemiddot for total PCBs is 0000064 ug1 the compliance limit is equal to the minimum level (ML) of the test method used as listed in Appendix VI (ie 05 ug1 for Method 608 or 000005 ug1 when Method 1668a is approved) 10 Hardness Cadmium Chromium III Copper Lead Nickel Silver and Zinc are Hardness Dependent 11 For a Dilution Factor (DF) from 1 to 5 metals limits are calculated using DF times the base limit for the metal See Appendix IV For example iron limits are calculated using DF x 1000ugL (the iron base limit) Therefore DF is 15 the iron limit will be 1500 ugL DF 2 then iron limit =1000 x 2 =2000 ugL etc not to exceed the DF=5 12

Minimum Level (ML is the lowest level at which the analytical system gives a recognizable signal and acceptable calibration point for the analyte The ML represents the lowest-concentration at which an analyte can b~ measured with a known level of confidence The ML is calculated by multiplying the laboratoryshydetermined method detection limit by 318 (see 40 CFR Part 136 Appendix 8) 13

pH sampling for compliance with permit limits may be performed using field methods as provided for in EPA test Method 1501 14

Temperature sampling per Method 1701

7

January 31 2015

United States Environmental Protection Agency 5 Post Office Square Suite 100 Boston Massachusetts 02109-3912 Attn Remediation General Permit NOI Processing

Subject Notice of Intent for Remediation General Permit Groveton Wastewater Lagoons 10 Mechanic Street Groveton New Hampshire

Mr Alvarez

Stonecipher amp Clark Environmental Solutions LLC (SampC) is submitting the attached Remediation General Permit Notice of Intent for the above-referenced location (the ldquoSiterdquo) on behalf of Mr Bob Chapman Please find the NOI form under Attachment A The Site is the former Wausau Paper Mill and is located on two parcels located in Groveton NH along the Upper Ammonoosuc River Please refer to the enclosed locus map (Figure 1) The Site consists of three clarifiers on the 95 acre parcel located adjacent to the Upper Ammonoosuc River and the wastewater lagoonpolishing ponds are located on the 53 acre parcel also adjacent to the Ammonoosuc River

General Site Information

All processes pertaining to the paper mill have ceased and reportedly the lagoons were discharged and cleaned in 2008 under an individual NPDES permit (Permit No NH0001562) This permit expired in 2011 The lagoons have reportedly received no additional wastewater since then Water currently in the open-topped lagoon area and clarifiers is a result of stormwater collection (supernatant) over the past few years The RGP is being sought in order to discharge the remaining supernatant water as part of a final dewatering in order to install drain-holes and maintain the lagoons in an empty state as well as eventual demolition of the clarifiers

Discharge Information

The expired NPDES Individual Permit allowed discharge via Outfall 017 which discharges approximately 05 miles west into the Connecticut River Please see Attachment A for a aerial view of the Site including the approximate outfall locationThis RGP application seeks to maintain the the Outfall 017 discharge point

STON

ECIPH

ER amp C

LARK EN

VIRON

MEN

TAL SO

LUTIO

NS LLC

111 Saranac Street Stu

dio 8 L

ittleton N

H 03561 6035755154

ww

wston

eciph

erand

clarkcom

In December 2013 John King of EPA approved the Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire report prepared and submitted by Horizons Engineering Inc Please find this report under Attachment B This report outlined the results of the sampling plan completed in October 2013 which included samples from 9 locations the four quadrants of the main lagoon the two polishing ponds (lagoons) and the three clarifiers Three samples were taken at each of the nine sampling locations one grab sample from mid-depth between the supernatantsludge interface and the surface one grab sample from the supernatant interface and one sludge sample from the bottom The laboratory results are included in the decommissioning plan report and indicate that detected parameter concentrations in the samples obtained from mid-depth between the supernatant interface and the water surface were all within the former NPDES permit standards with the exception of the sample from Clarifier 1 for which we are NOT seeking coverage under the RGP NOI

The recommendation of the approved decommissioning report was to pump each lagoon and clarifier down to the supernatant interface individually into Outfall 017 (which discharges directly to the Connecticut River) Pumping rates were specified in the report based on BOD and TSS and turbidity monitoring was recommended in order to determine when interface was reached

In November 2014 SampC oversaw discharge of the supernatant from the lagoon area as specified in the approved decommissioning report The pumping rate was greatly reduced from the allowable rate in the plan due to availability of pumping equipment as well as field conditions Turbidity was closely monitored Field observations indicated that the line between the supernatant and the interface was quite sharply defined Close monitoring allowed SampC to be confident in the discharge of only supernatant

Contaminant Information

For the purposes of this permit application it is assumed that the Site falls under Category III subcategory B Upon reviewing Appendix III regarding Effluent Limits and Monitoring Requirements it appears that the supernatant laboratory results for all sampled locations with the exception of Clarifier 1 average 19 mgl TSS which is well below the specified TSS effluent limit of 30 mgl TSS (monthly average) Laboratory results from supernatant collected from Clarifier 3 yielded a TSS value of 45 mgl Please note that using this TSS value as a maximum daily TSS value in the NOI application under Appendix III will therefore skew the actual amount of daily TSS as the dewatering of Clarifier 3 is anticipated at a lesser rate than the 1000 gpm maximum In addition the volume of water in Clarifier 3 (reportedly 9 feet) will be discharged prior to achieving a 24-hr time period

Group I PAHs and Group II PAHs fall below the respective 100 ugl and 1000 ugl daily limits

SampC collected and submitted to the laboratory a confirmatory sample of the lagoon supernatant on December 3 2014 This sample was tested for Volatile Organic Compounds (VOCs) Group I PAHs Group II PAHs and all required metals to be tested under Appendix III Category III subcategory B with the exception of antimony copper nickel zinc and iron

Once the supernatantsludge interface has been reached the plan is to dewater the remaining water overland via NHDES Temporary Groundwater Discharge Permit This will NOT be released to any surface waters

Treatment System Information

No treatment is proposed during dewatering The pumping discharge rate is proposed to be a maximum of 1000 gpm

Receiving Surface Water(s) Information

Discharge will occur approximately 05 miles away to Outfall 017 via underground 32rdquo pipe into the Connecticut River

Endangered Species Act amp National Historic Preservation Act Reviews

SampC has received verbal response from United States Fish and Wildlife Service that the discharge activities are ldquounlikely to adversely affectrdquo listed species or critical habitat When official sign-off is received SampC will forward that response

Under Attachment D please find the correspondence with New Hampshire Division of Historical Resources indicating that findings for this project considered ldquoNo Historic Properties Affectedrdquo

Please contact the undersigned if you have any questions or require additional information

Sincerely

Sylvia A Clark Co-OwnerProject Manager Stonecipher amp Clark Environmental Solutions LLC Office 6035755154 Cell 8027341403 sclarkstonecipherandclarkcom

Attachments Figure 1 ndash Site Aerial Map Figure 2 ndash Treatment System Flow Diagram Attachment A ndash Notice of Intent Form Attachment B ndash EPA Approved Decommissioning Plan Attachment C ndash December 3 2014 Laboratory Results Attachment D ndash NH DHR Correspondence Attachment E - US FWS Correspondence (To be forwarded)

cc Jeff Andrews NHDES

Sylvia
Stamp

Figure 1

Lagoon

Clarifiers

Outfall 017

Stonecipheramp Clark Environmental Solutions LLC 111 Saranac Street Studio 8

Littleton New Hampshire 03561

6035755154

Groveton Wastewater Lagoons amp Clarifiers Groveton NH

SampC Project 2014-062

Aerial Map

Figure 2

LAGOON AREA

CLARIFIER 2

CLARIFIER 1

CLARIFIER 3

UPPER AMMONOOSUC RIVER

MONITORING

CHAMBER

32 PIPE DISCHARGES

APPROX 05 MILES WEST

INTO THE CONNECTICUT

RIVER (OUTFALL 017)

STONECIPHER amp CLARK

ENVIRONMENTAL SOLUTIONS LLC

111 SARANAC STREET STUDIO 8

LITTLETON NEW HAMPSHIRE 03561

6035755154

GROVETON WASTEWATER LAGOONS

GROVETON NEW HAMPSHIRE

FLOW SCHEMATIC

Attachment A

NPDES Permit No MAG910000 NPDES Permit No NHG910000

B Suggested Form for Notice of Intent (NOI) for the Remediation General Permit

1 General facilitysite information Please provide the following information about the site

a) Name of facilitysite Facilitysite mailing address

Location of facilitysite

longitude_______________ latitude_______________

Facility SIC code(s)

Street

b) Name of facilitysite owner Town

Email address of facilitysite owner State Zip County

Telephone no of facilitysite owner

Fax no of facilitysite owner Owner is (check one) 1 Federal____ 2 StateTribal____ 3 Private____ 4 Other ____ if so describe

Address of owner (if different from site)

Street

Town State Zip County

c) Legal name of operator Operator telephone no

Operator fax no Operator email

Operator contact name and title

Address of operator (if different from owner)

Street

Town State Zip County

Remediation General Permit Page 10 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

d) Check Y for Ayes or N for Ano for the following 1 Has a prior NPDES permit exclusion been granted for the discharge Y___ N___ if Y number_________________ 2 Has a prior NPDES application (Form 1 amp 2C) ever been filed for the discharge Y___ N___ if Y date and tracking __________________________________________________________________ 3 Is the discharge a ldquonew dischargerdquo as defined by 40 CFR 1222 Y___ N___ 4 For sites in Massachusetts is the discharge covered under the Massachusetts Contingency Plan (MCP) and exempt from state permitting Y___ N___

e) Is sitefacility subject to any State permitting license f) Is the sitefacility covered by any other EPA permit including or other action which is causing the generation of 1 Multi-Sector General Permit Y___ N___ discharge Y___ N___ if Y number_______________ If Y please list 2 Final Dewatering General Permit Y___ N___ 1 site identification assigned by the state of NH or if Y number________________ MA_________________________________________ 3 EPA Construction General Permit Y___ N___ 2 permit or license assigned____________________ if Y number _______________ 3 state agency contact information name location and 4 Individual NPDES permit Y___ N___ telephone number if Y number_____________

5 any other water quality related individual or general permit Y___ N___ if Y number______________

g) Is the sitefacility located within or does it discharge to an Area of Critical Environmental Concern (ACEC) Y____ N____

h) Based on the facilitysite information and any historical sampling data identify the sub-category into which the potential discharge falls Activity Category Activity Sub-Category I - Petroleum Related Site Remediation A Gasoline Only Sites ____

B Fuel Oils and Other Oil Sites (including Residential Non-Business Remediation Discharges) ____ C Petroleum Sites with Additional Contamination ____

II - Non Petroleum Site Remediation A Volatile Organic Compound (VOC) Only Sites _____ B VOC Sites with Additional Contamination ____ C Primarily Heavy Metal Sites ____

III - Contaminated Construction Dewatering A General Urban Fill Sites ____ B Known Contaminated Sites ____

Remediation General Permit Page 11 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

IV - Miscellaneous Related Discharges A Aquifer Pump Testing to Evaluate Formerly Contaminated Sites ____ B Well DevelopmentRehabilitation at ContaminatedFormerly Contaminated Sites ____ C Hydrostatic Testing of Pipelines and Tanks ____ D Long-Term Remediation of Contaminated Sumps and Dikes ____ E Short-term Contaminated Dredging Drain Back Waters (if not covered by 401404 permit) ____

2 Discharge information Please provide information about the discharge (attaching additional sheets as necessary) including

a) Describe the discharge activities for which the ownerapplicant is seeking coverage

b) Provide the following information about each discharge

1) Number of discharge points

2) What is the maximum and average flow rate of discharge (in cubic feet per second ft3s) Max flow____________ Is maximum flow a design value Y___ N____ Average flow (include units) __________ Is average flow a design value or estimate _________

3) Latitude and longitude of each discharge within 100 feet pt1 lat_____________ long_____________ pt2 lat_____________ long_____________ pt3 lat_____________ long_____________ pt4 lat_____________ long_____________ pt5 lat_____________ long_____________ pt6 lat_____________ long_____________ pt7 lat_____________ long_____________ pt8 lat_____________ long_____________ etc

4) If hydrostatic testing total volume of the discharge (gals)_________

5) Is the discharge intermittent ____ or seasonal____ Is discharge ongoing Y ____ N______

c) Expected dates of discharge (mmddyy) start_____________ end_________________ d) Please attach a line drawing or flow schematic showing water flow through the facility including 1 sources of intake water 2 contributing flow from the operation 3 treatment units and 4 discharge points and receiving waters(s)

Remediation General Permit Page 12 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

3 Contaminant information a) Based on the sub-category selected (see Appendix III) indicate whether each listed chemical is believed present or believed absent in the potential discharge Attach additional sheets as needed

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

1 Total Suspended Solids (TSS) 2 Total Residual Chlorine (TRC) 3 Total Petroleum Hydrocarbons (TPH) 4 Cyanide (CN) 57125 5 Benzene (B) 71432 6 Toluene (T) 108883 7 Ethylbenzene (E) 100414 8 (mpo) Xylenes (X) 108883

106423 95476

1330207

9 Total BTEX 2 na 10 Ethylene Dibromide (EDB) (12- Dibromoethane) 3

106934

11 Methyl-tert-Butyl Ether (MtBE)

1634044

12 tert-Butyl Alcohol (TBA) (Tertiary-Butanol)

75650

Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI 2 BTEX = Sum of Benzene Toluene Ethylbenzene total Xylenes 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England

Remediation General Permit Page 13 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
            1. Page11[0]
              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
                  3. TextField36[0] 29
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                  5. TextField38[0] estimate
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                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
                                          11. TextField59[0] Class B
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Page 6: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Metal parameter

Total Recoverable NH[Metal Limit H 10 =25 mgll

CaC03 Units = ugll 1lLlU

Minimum levei=ML

Freshwater Limits

2206 dilution

39 Antimony 141 ML 10

40 Arsenic 500 ML 20

41 Cadmium 16 ML 10

42 Chromium III (trivalent) 1385 ML 15

43 Chromium VI (hexavalent) 570 ML 10

44 Copper 142 ML 15 45 Lead 05 ML 20 46 Mercury 09 ML 02

47 Nickel 807 ML 20 48 Selenium 5 ML 20 49 Silver 04 ML 10

so Zinc 1480 ML 15

51 Iron 5 000 ML 20

Other Parameters Jml

52 Instantaneous Flow Site specific in CFS

53 Total Flow Site specific in CFS

54 pH Range for Class B Waters in NH 65-83 1MonthGrab13

55 pH Range for Class SB Waters in NH 65-8 1MonthGrab13

56 57 Daily maximum temperature shy Warm water fisheries

83 oF 1MonthGrab1 4

58 Daily maximum temperature - Cold water fisheries 68degF 1MonthGrab14

59 60 Maximum Change in Temperature in NH- Any Class B water body- Warm Water

5deg F 1MonthGrab14

61 Maximum Change in Temperature in NH- Any Class B water body shy Cold water and LakesPonds

3oF 1MonthGrab14

Footnotes

1 Although t he maximum values for TRC are 11ugl and 75 ug1 for freshwater and saltwater respectively the compliance limits are equal to the minimum level ( ML) of the test method used as listed in Appendix VI (ie Method 3305 20 ug1) 2 Limits for cyanide are based on EPAs water quality criteria expressed as micrograms per liter There is currently no EPA approved t est method for free cyanide Therefore total cyanide must be reported

6

3 Although the maximum values for cyanide are 52 ug1 and 10 ug1 for freshwater and saltwater respectively the compliance limits are equal to the minimum level (ML) of the Method 335 4 as listed in Appendix VI (ie 10 ug1) 4 BTEX = sum of Benzene Toluene Ethylbenzene and total Xylenes 5 Naphthalene can be reported as both a purgeable (VOC) and extractable (SVOC) organic compound If both VOC and SVOC are analyzed the highest value must be used unless the QC criteria for one of the analyses is not met In such cases the value from the analysis meeting the QC criteria must be used 6 The sum of individual phthalate compounds(not including the 34 Sis (2shyEthylhexyl) Phthalate The compliance limits are equal to the minimum level (ML) of the test method used as listed in Appendix VI Total values calculated for reporting on NOis and discharge monitoring reports shall be calculated by adding the measured concentration of each constituent If the measurement ofa constituent is less than the ML the permittee shall use a value of zero for that constituent For each test the permittee shall also attach the raw data for each constituent to the discharge monitoring report including the minimum level and minimum detection level for the analysis 7 Although the maximum value for the individual PAH compounds is 00038 ug1 the compliance limits are equal to the minimum level (ML) of the test method used as listed in Appendix VI 8 In the November 2002 WQC EPA has revised the definition of Total PCBs for aquatic life as total PCBs is the sum of all homologue all isomer all congener or all Oroclor analysesTotal values calculated for reporting on NOis and discharge monitoring reports shall be calculated by adding the measured concentration of each constituent If the measure of a constituent is less than the ML the permittee shall use a value of zero for that constituent For each test the permittee shall also attach the raw data for each constituent to the discharge monitoring report including the minimum level and minimum detection level for the analysis 9Aithough the maximum valuemiddot for total PCBs is 0000064 ug1 the compliance limit is equal to the minimum level (ML) of the test method used as listed in Appendix VI (ie 05 ug1 for Method 608 or 000005 ug1 when Method 1668a is approved) 10 Hardness Cadmium Chromium III Copper Lead Nickel Silver and Zinc are Hardness Dependent 11 For a Dilution Factor (DF) from 1 to 5 metals limits are calculated using DF times the base limit for the metal See Appendix IV For example iron limits are calculated using DF x 1000ugL (the iron base limit) Therefore DF is 15 the iron limit will be 1500 ugL DF 2 then iron limit =1000 x 2 =2000 ugL etc not to exceed the DF=5 12

Minimum Level (ML is the lowest level at which the analytical system gives a recognizable signal and acceptable calibration point for the analyte The ML represents the lowest-concentration at which an analyte can b~ measured with a known level of confidence The ML is calculated by multiplying the laboratoryshydetermined method detection limit by 318 (see 40 CFR Part 136 Appendix 8) 13

pH sampling for compliance with permit limits may be performed using field methods as provided for in EPA test Method 1501 14

Temperature sampling per Method 1701

7

January 31 2015

United States Environmental Protection Agency 5 Post Office Square Suite 100 Boston Massachusetts 02109-3912 Attn Remediation General Permit NOI Processing

Subject Notice of Intent for Remediation General Permit Groveton Wastewater Lagoons 10 Mechanic Street Groveton New Hampshire

Mr Alvarez

Stonecipher amp Clark Environmental Solutions LLC (SampC) is submitting the attached Remediation General Permit Notice of Intent for the above-referenced location (the ldquoSiterdquo) on behalf of Mr Bob Chapman Please find the NOI form under Attachment A The Site is the former Wausau Paper Mill and is located on two parcels located in Groveton NH along the Upper Ammonoosuc River Please refer to the enclosed locus map (Figure 1) The Site consists of three clarifiers on the 95 acre parcel located adjacent to the Upper Ammonoosuc River and the wastewater lagoonpolishing ponds are located on the 53 acre parcel also adjacent to the Ammonoosuc River

General Site Information

All processes pertaining to the paper mill have ceased and reportedly the lagoons were discharged and cleaned in 2008 under an individual NPDES permit (Permit No NH0001562) This permit expired in 2011 The lagoons have reportedly received no additional wastewater since then Water currently in the open-topped lagoon area and clarifiers is a result of stormwater collection (supernatant) over the past few years The RGP is being sought in order to discharge the remaining supernatant water as part of a final dewatering in order to install drain-holes and maintain the lagoons in an empty state as well as eventual demolition of the clarifiers

Discharge Information

The expired NPDES Individual Permit allowed discharge via Outfall 017 which discharges approximately 05 miles west into the Connecticut River Please see Attachment A for a aerial view of the Site including the approximate outfall locationThis RGP application seeks to maintain the the Outfall 017 discharge point

STON

ECIPH

ER amp C

LARK EN

VIRON

MEN

TAL SO

LUTIO

NS LLC

111 Saranac Street Stu

dio 8 L

ittleton N

H 03561 6035755154

ww

wston

eciph

erand

clarkcom

In December 2013 John King of EPA approved the Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire report prepared and submitted by Horizons Engineering Inc Please find this report under Attachment B This report outlined the results of the sampling plan completed in October 2013 which included samples from 9 locations the four quadrants of the main lagoon the two polishing ponds (lagoons) and the three clarifiers Three samples were taken at each of the nine sampling locations one grab sample from mid-depth between the supernatantsludge interface and the surface one grab sample from the supernatant interface and one sludge sample from the bottom The laboratory results are included in the decommissioning plan report and indicate that detected parameter concentrations in the samples obtained from mid-depth between the supernatant interface and the water surface were all within the former NPDES permit standards with the exception of the sample from Clarifier 1 for which we are NOT seeking coverage under the RGP NOI

The recommendation of the approved decommissioning report was to pump each lagoon and clarifier down to the supernatant interface individually into Outfall 017 (which discharges directly to the Connecticut River) Pumping rates were specified in the report based on BOD and TSS and turbidity monitoring was recommended in order to determine when interface was reached

In November 2014 SampC oversaw discharge of the supernatant from the lagoon area as specified in the approved decommissioning report The pumping rate was greatly reduced from the allowable rate in the plan due to availability of pumping equipment as well as field conditions Turbidity was closely monitored Field observations indicated that the line between the supernatant and the interface was quite sharply defined Close monitoring allowed SampC to be confident in the discharge of only supernatant

Contaminant Information

For the purposes of this permit application it is assumed that the Site falls under Category III subcategory B Upon reviewing Appendix III regarding Effluent Limits and Monitoring Requirements it appears that the supernatant laboratory results for all sampled locations with the exception of Clarifier 1 average 19 mgl TSS which is well below the specified TSS effluent limit of 30 mgl TSS (monthly average) Laboratory results from supernatant collected from Clarifier 3 yielded a TSS value of 45 mgl Please note that using this TSS value as a maximum daily TSS value in the NOI application under Appendix III will therefore skew the actual amount of daily TSS as the dewatering of Clarifier 3 is anticipated at a lesser rate than the 1000 gpm maximum In addition the volume of water in Clarifier 3 (reportedly 9 feet) will be discharged prior to achieving a 24-hr time period

Group I PAHs and Group II PAHs fall below the respective 100 ugl and 1000 ugl daily limits

SampC collected and submitted to the laboratory a confirmatory sample of the lagoon supernatant on December 3 2014 This sample was tested for Volatile Organic Compounds (VOCs) Group I PAHs Group II PAHs and all required metals to be tested under Appendix III Category III subcategory B with the exception of antimony copper nickel zinc and iron

Once the supernatantsludge interface has been reached the plan is to dewater the remaining water overland via NHDES Temporary Groundwater Discharge Permit This will NOT be released to any surface waters

Treatment System Information

No treatment is proposed during dewatering The pumping discharge rate is proposed to be a maximum of 1000 gpm

Receiving Surface Water(s) Information

Discharge will occur approximately 05 miles away to Outfall 017 via underground 32rdquo pipe into the Connecticut River

Endangered Species Act amp National Historic Preservation Act Reviews

SampC has received verbal response from United States Fish and Wildlife Service that the discharge activities are ldquounlikely to adversely affectrdquo listed species or critical habitat When official sign-off is received SampC will forward that response

Under Attachment D please find the correspondence with New Hampshire Division of Historical Resources indicating that findings for this project considered ldquoNo Historic Properties Affectedrdquo

Please contact the undersigned if you have any questions or require additional information

Sincerely

Sylvia A Clark Co-OwnerProject Manager Stonecipher amp Clark Environmental Solutions LLC Office 6035755154 Cell 8027341403 sclarkstonecipherandclarkcom

Attachments Figure 1 ndash Site Aerial Map Figure 2 ndash Treatment System Flow Diagram Attachment A ndash Notice of Intent Form Attachment B ndash EPA Approved Decommissioning Plan Attachment C ndash December 3 2014 Laboratory Results Attachment D ndash NH DHR Correspondence Attachment E - US FWS Correspondence (To be forwarded)

cc Jeff Andrews NHDES

Sylvia
Stamp

Figure 1

Lagoon

Clarifiers

Outfall 017

Stonecipheramp Clark Environmental Solutions LLC 111 Saranac Street Studio 8

Littleton New Hampshire 03561

6035755154

Groveton Wastewater Lagoons amp Clarifiers Groveton NH

SampC Project 2014-062

Aerial Map

Figure 2

LAGOON AREA

CLARIFIER 2

CLARIFIER 1

CLARIFIER 3

UPPER AMMONOOSUC RIVER

MONITORING

CHAMBER

32 PIPE DISCHARGES

APPROX 05 MILES WEST

INTO THE CONNECTICUT

RIVER (OUTFALL 017)

STONECIPHER amp CLARK

ENVIRONMENTAL SOLUTIONS LLC

111 SARANAC STREET STUDIO 8

LITTLETON NEW HAMPSHIRE 03561

6035755154

GROVETON WASTEWATER LAGOONS

GROVETON NEW HAMPSHIRE

FLOW SCHEMATIC

Attachment A

NPDES Permit No MAG910000 NPDES Permit No NHG910000

B Suggested Form for Notice of Intent (NOI) for the Remediation General Permit

1 General facilitysite information Please provide the following information about the site

a) Name of facilitysite Facilitysite mailing address

Location of facilitysite

longitude_______________ latitude_______________

Facility SIC code(s)

Street

b) Name of facilitysite owner Town

Email address of facilitysite owner State Zip County

Telephone no of facilitysite owner

Fax no of facilitysite owner Owner is (check one) 1 Federal____ 2 StateTribal____ 3 Private____ 4 Other ____ if so describe

Address of owner (if different from site)

Street

Town State Zip County

c) Legal name of operator Operator telephone no

Operator fax no Operator email

Operator contact name and title

Address of operator (if different from owner)

Street

Town State Zip County

Remediation General Permit Page 10 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

d) Check Y for Ayes or N for Ano for the following 1 Has a prior NPDES permit exclusion been granted for the discharge Y___ N___ if Y number_________________ 2 Has a prior NPDES application (Form 1 amp 2C) ever been filed for the discharge Y___ N___ if Y date and tracking __________________________________________________________________ 3 Is the discharge a ldquonew dischargerdquo as defined by 40 CFR 1222 Y___ N___ 4 For sites in Massachusetts is the discharge covered under the Massachusetts Contingency Plan (MCP) and exempt from state permitting Y___ N___

e) Is sitefacility subject to any State permitting license f) Is the sitefacility covered by any other EPA permit including or other action which is causing the generation of 1 Multi-Sector General Permit Y___ N___ discharge Y___ N___ if Y number_______________ If Y please list 2 Final Dewatering General Permit Y___ N___ 1 site identification assigned by the state of NH or if Y number________________ MA_________________________________________ 3 EPA Construction General Permit Y___ N___ 2 permit or license assigned____________________ if Y number _______________ 3 state agency contact information name location and 4 Individual NPDES permit Y___ N___ telephone number if Y number_____________

5 any other water quality related individual or general permit Y___ N___ if Y number______________

g) Is the sitefacility located within or does it discharge to an Area of Critical Environmental Concern (ACEC) Y____ N____

h) Based on the facilitysite information and any historical sampling data identify the sub-category into which the potential discharge falls Activity Category Activity Sub-Category I - Petroleum Related Site Remediation A Gasoline Only Sites ____

B Fuel Oils and Other Oil Sites (including Residential Non-Business Remediation Discharges) ____ C Petroleum Sites with Additional Contamination ____

II - Non Petroleum Site Remediation A Volatile Organic Compound (VOC) Only Sites _____ B VOC Sites with Additional Contamination ____ C Primarily Heavy Metal Sites ____

III - Contaminated Construction Dewatering A General Urban Fill Sites ____ B Known Contaminated Sites ____

Remediation General Permit Page 11 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

IV - Miscellaneous Related Discharges A Aquifer Pump Testing to Evaluate Formerly Contaminated Sites ____ B Well DevelopmentRehabilitation at ContaminatedFormerly Contaminated Sites ____ C Hydrostatic Testing of Pipelines and Tanks ____ D Long-Term Remediation of Contaminated Sumps and Dikes ____ E Short-term Contaminated Dredging Drain Back Waters (if not covered by 401404 permit) ____

2 Discharge information Please provide information about the discharge (attaching additional sheets as necessary) including

a) Describe the discharge activities for which the ownerapplicant is seeking coverage

b) Provide the following information about each discharge

1) Number of discharge points

2) What is the maximum and average flow rate of discharge (in cubic feet per second ft3s) Max flow____________ Is maximum flow a design value Y___ N____ Average flow (include units) __________ Is average flow a design value or estimate _________

3) Latitude and longitude of each discharge within 100 feet pt1 lat_____________ long_____________ pt2 lat_____________ long_____________ pt3 lat_____________ long_____________ pt4 lat_____________ long_____________ pt5 lat_____________ long_____________ pt6 lat_____________ long_____________ pt7 lat_____________ long_____________ pt8 lat_____________ long_____________ etc

4) If hydrostatic testing total volume of the discharge (gals)_________

5) Is the discharge intermittent ____ or seasonal____ Is discharge ongoing Y ____ N______

c) Expected dates of discharge (mmddyy) start_____________ end_________________ d) Please attach a line drawing or flow schematic showing water flow through the facility including 1 sources of intake water 2 contributing flow from the operation 3 treatment units and 4 discharge points and receiving waters(s)

Remediation General Permit Page 12 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

3 Contaminant information a) Based on the sub-category selected (see Appendix III) indicate whether each listed chemical is believed present or believed absent in the potential discharge Attach additional sheets as needed

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

1 Total Suspended Solids (TSS) 2 Total Residual Chlorine (TRC) 3 Total Petroleum Hydrocarbons (TPH) 4 Cyanide (CN) 57125 5 Benzene (B) 71432 6 Toluene (T) 108883 7 Ethylbenzene (E) 100414 8 (mpo) Xylenes (X) 108883

106423 95476

1330207

9 Total BTEX 2 na 10 Ethylene Dibromide (EDB) (12- Dibromoethane) 3

106934

11 Methyl-tert-Butyl Ether (MtBE)

1634044

12 tert-Butyl Alcohol (TBA) (Tertiary-Butanol)

75650

Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI 2 BTEX = Sum of Benzene Toluene Ethylbenzene total Xylenes 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England

Remediation General Permit Page 13 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
          13. RadioButtonList[0] 3
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
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                  4. TextField37[0] 22
                  5. TextField38[0] estimate
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                  8. DateTimeField1[0] 312015
                  9. DateTimeField2[0] 1212015
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                  11. TextField44[0] NA
                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                      26. TextField89[1] GRAB
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
                                          11. TextField59[0] Class B
                                          12. TextField60[0] 216
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Page 7: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

3 Although the maximum values for cyanide are 52 ug1 and 10 ug1 for freshwater and saltwater respectively the compliance limits are equal to the minimum level (ML) of the Method 335 4 as listed in Appendix VI (ie 10 ug1) 4 BTEX = sum of Benzene Toluene Ethylbenzene and total Xylenes 5 Naphthalene can be reported as both a purgeable (VOC) and extractable (SVOC) organic compound If both VOC and SVOC are analyzed the highest value must be used unless the QC criteria for one of the analyses is not met In such cases the value from the analysis meeting the QC criteria must be used 6 The sum of individual phthalate compounds(not including the 34 Sis (2shyEthylhexyl) Phthalate The compliance limits are equal to the minimum level (ML) of the test method used as listed in Appendix VI Total values calculated for reporting on NOis and discharge monitoring reports shall be calculated by adding the measured concentration of each constituent If the measurement ofa constituent is less than the ML the permittee shall use a value of zero for that constituent For each test the permittee shall also attach the raw data for each constituent to the discharge monitoring report including the minimum level and minimum detection level for the analysis 7 Although the maximum value for the individual PAH compounds is 00038 ug1 the compliance limits are equal to the minimum level (ML) of the test method used as listed in Appendix VI 8 In the November 2002 WQC EPA has revised the definition of Total PCBs for aquatic life as total PCBs is the sum of all homologue all isomer all congener or all Oroclor analysesTotal values calculated for reporting on NOis and discharge monitoring reports shall be calculated by adding the measured concentration of each constituent If the measure of a constituent is less than the ML the permittee shall use a value of zero for that constituent For each test the permittee shall also attach the raw data for each constituent to the discharge monitoring report including the minimum level and minimum detection level for the analysis 9Aithough the maximum valuemiddot for total PCBs is 0000064 ug1 the compliance limit is equal to the minimum level (ML) of the test method used as listed in Appendix VI (ie 05 ug1 for Method 608 or 000005 ug1 when Method 1668a is approved) 10 Hardness Cadmium Chromium III Copper Lead Nickel Silver and Zinc are Hardness Dependent 11 For a Dilution Factor (DF) from 1 to 5 metals limits are calculated using DF times the base limit for the metal See Appendix IV For example iron limits are calculated using DF x 1000ugL (the iron base limit) Therefore DF is 15 the iron limit will be 1500 ugL DF 2 then iron limit =1000 x 2 =2000 ugL etc not to exceed the DF=5 12

Minimum Level (ML is the lowest level at which the analytical system gives a recognizable signal and acceptable calibration point for the analyte The ML represents the lowest-concentration at which an analyte can b~ measured with a known level of confidence The ML is calculated by multiplying the laboratoryshydetermined method detection limit by 318 (see 40 CFR Part 136 Appendix 8) 13

pH sampling for compliance with permit limits may be performed using field methods as provided for in EPA test Method 1501 14

Temperature sampling per Method 1701

7

January 31 2015

United States Environmental Protection Agency 5 Post Office Square Suite 100 Boston Massachusetts 02109-3912 Attn Remediation General Permit NOI Processing

Subject Notice of Intent for Remediation General Permit Groveton Wastewater Lagoons 10 Mechanic Street Groveton New Hampshire

Mr Alvarez

Stonecipher amp Clark Environmental Solutions LLC (SampC) is submitting the attached Remediation General Permit Notice of Intent for the above-referenced location (the ldquoSiterdquo) on behalf of Mr Bob Chapman Please find the NOI form under Attachment A The Site is the former Wausau Paper Mill and is located on two parcels located in Groveton NH along the Upper Ammonoosuc River Please refer to the enclosed locus map (Figure 1) The Site consists of three clarifiers on the 95 acre parcel located adjacent to the Upper Ammonoosuc River and the wastewater lagoonpolishing ponds are located on the 53 acre parcel also adjacent to the Ammonoosuc River

General Site Information

All processes pertaining to the paper mill have ceased and reportedly the lagoons were discharged and cleaned in 2008 under an individual NPDES permit (Permit No NH0001562) This permit expired in 2011 The lagoons have reportedly received no additional wastewater since then Water currently in the open-topped lagoon area and clarifiers is a result of stormwater collection (supernatant) over the past few years The RGP is being sought in order to discharge the remaining supernatant water as part of a final dewatering in order to install drain-holes and maintain the lagoons in an empty state as well as eventual demolition of the clarifiers

Discharge Information

The expired NPDES Individual Permit allowed discharge via Outfall 017 which discharges approximately 05 miles west into the Connecticut River Please see Attachment A for a aerial view of the Site including the approximate outfall locationThis RGP application seeks to maintain the the Outfall 017 discharge point

STON

ECIPH

ER amp C

LARK EN

VIRON

MEN

TAL SO

LUTIO

NS LLC

111 Saranac Street Stu

dio 8 L

ittleton N

H 03561 6035755154

ww

wston

eciph

erand

clarkcom

In December 2013 John King of EPA approved the Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire report prepared and submitted by Horizons Engineering Inc Please find this report under Attachment B This report outlined the results of the sampling plan completed in October 2013 which included samples from 9 locations the four quadrants of the main lagoon the two polishing ponds (lagoons) and the three clarifiers Three samples were taken at each of the nine sampling locations one grab sample from mid-depth between the supernatantsludge interface and the surface one grab sample from the supernatant interface and one sludge sample from the bottom The laboratory results are included in the decommissioning plan report and indicate that detected parameter concentrations in the samples obtained from mid-depth between the supernatant interface and the water surface were all within the former NPDES permit standards with the exception of the sample from Clarifier 1 for which we are NOT seeking coverage under the RGP NOI

The recommendation of the approved decommissioning report was to pump each lagoon and clarifier down to the supernatant interface individually into Outfall 017 (which discharges directly to the Connecticut River) Pumping rates were specified in the report based on BOD and TSS and turbidity monitoring was recommended in order to determine when interface was reached

In November 2014 SampC oversaw discharge of the supernatant from the lagoon area as specified in the approved decommissioning report The pumping rate was greatly reduced from the allowable rate in the plan due to availability of pumping equipment as well as field conditions Turbidity was closely monitored Field observations indicated that the line between the supernatant and the interface was quite sharply defined Close monitoring allowed SampC to be confident in the discharge of only supernatant

Contaminant Information

For the purposes of this permit application it is assumed that the Site falls under Category III subcategory B Upon reviewing Appendix III regarding Effluent Limits and Monitoring Requirements it appears that the supernatant laboratory results for all sampled locations with the exception of Clarifier 1 average 19 mgl TSS which is well below the specified TSS effluent limit of 30 mgl TSS (monthly average) Laboratory results from supernatant collected from Clarifier 3 yielded a TSS value of 45 mgl Please note that using this TSS value as a maximum daily TSS value in the NOI application under Appendix III will therefore skew the actual amount of daily TSS as the dewatering of Clarifier 3 is anticipated at a lesser rate than the 1000 gpm maximum In addition the volume of water in Clarifier 3 (reportedly 9 feet) will be discharged prior to achieving a 24-hr time period

Group I PAHs and Group II PAHs fall below the respective 100 ugl and 1000 ugl daily limits

SampC collected and submitted to the laboratory a confirmatory sample of the lagoon supernatant on December 3 2014 This sample was tested for Volatile Organic Compounds (VOCs) Group I PAHs Group II PAHs and all required metals to be tested under Appendix III Category III subcategory B with the exception of antimony copper nickel zinc and iron

Once the supernatantsludge interface has been reached the plan is to dewater the remaining water overland via NHDES Temporary Groundwater Discharge Permit This will NOT be released to any surface waters

Treatment System Information

No treatment is proposed during dewatering The pumping discharge rate is proposed to be a maximum of 1000 gpm

Receiving Surface Water(s) Information

Discharge will occur approximately 05 miles away to Outfall 017 via underground 32rdquo pipe into the Connecticut River

Endangered Species Act amp National Historic Preservation Act Reviews

SampC has received verbal response from United States Fish and Wildlife Service that the discharge activities are ldquounlikely to adversely affectrdquo listed species or critical habitat When official sign-off is received SampC will forward that response

Under Attachment D please find the correspondence with New Hampshire Division of Historical Resources indicating that findings for this project considered ldquoNo Historic Properties Affectedrdquo

Please contact the undersigned if you have any questions or require additional information

Sincerely

Sylvia A Clark Co-OwnerProject Manager Stonecipher amp Clark Environmental Solutions LLC Office 6035755154 Cell 8027341403 sclarkstonecipherandclarkcom

Attachments Figure 1 ndash Site Aerial Map Figure 2 ndash Treatment System Flow Diagram Attachment A ndash Notice of Intent Form Attachment B ndash EPA Approved Decommissioning Plan Attachment C ndash December 3 2014 Laboratory Results Attachment D ndash NH DHR Correspondence Attachment E - US FWS Correspondence (To be forwarded)

cc Jeff Andrews NHDES

Sylvia
Stamp

Figure 1

Lagoon

Clarifiers

Outfall 017

Stonecipheramp Clark Environmental Solutions LLC 111 Saranac Street Studio 8

Littleton New Hampshire 03561

6035755154

Groveton Wastewater Lagoons amp Clarifiers Groveton NH

SampC Project 2014-062

Aerial Map

Figure 2

LAGOON AREA

CLARIFIER 2

CLARIFIER 1

CLARIFIER 3

UPPER AMMONOOSUC RIVER

MONITORING

CHAMBER

32 PIPE DISCHARGES

APPROX 05 MILES WEST

INTO THE CONNECTICUT

RIVER (OUTFALL 017)

STONECIPHER amp CLARK

ENVIRONMENTAL SOLUTIONS LLC

111 SARANAC STREET STUDIO 8

LITTLETON NEW HAMPSHIRE 03561

6035755154

GROVETON WASTEWATER LAGOONS

GROVETON NEW HAMPSHIRE

FLOW SCHEMATIC

Attachment A

NPDES Permit No MAG910000 NPDES Permit No NHG910000

B Suggested Form for Notice of Intent (NOI) for the Remediation General Permit

1 General facilitysite information Please provide the following information about the site

a) Name of facilitysite Facilitysite mailing address

Location of facilitysite

longitude_______________ latitude_______________

Facility SIC code(s)

Street

b) Name of facilitysite owner Town

Email address of facilitysite owner State Zip County

Telephone no of facilitysite owner

Fax no of facilitysite owner Owner is (check one) 1 Federal____ 2 StateTribal____ 3 Private____ 4 Other ____ if so describe

Address of owner (if different from site)

Street

Town State Zip County

c) Legal name of operator Operator telephone no

Operator fax no Operator email

Operator contact name and title

Address of operator (if different from owner)

Street

Town State Zip County

Remediation General Permit Page 10 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

d) Check Y for Ayes or N for Ano for the following 1 Has a prior NPDES permit exclusion been granted for the discharge Y___ N___ if Y number_________________ 2 Has a prior NPDES application (Form 1 amp 2C) ever been filed for the discharge Y___ N___ if Y date and tracking __________________________________________________________________ 3 Is the discharge a ldquonew dischargerdquo as defined by 40 CFR 1222 Y___ N___ 4 For sites in Massachusetts is the discharge covered under the Massachusetts Contingency Plan (MCP) and exempt from state permitting Y___ N___

e) Is sitefacility subject to any State permitting license f) Is the sitefacility covered by any other EPA permit including or other action which is causing the generation of 1 Multi-Sector General Permit Y___ N___ discharge Y___ N___ if Y number_______________ If Y please list 2 Final Dewatering General Permit Y___ N___ 1 site identification assigned by the state of NH or if Y number________________ MA_________________________________________ 3 EPA Construction General Permit Y___ N___ 2 permit or license assigned____________________ if Y number _______________ 3 state agency contact information name location and 4 Individual NPDES permit Y___ N___ telephone number if Y number_____________

5 any other water quality related individual or general permit Y___ N___ if Y number______________

g) Is the sitefacility located within or does it discharge to an Area of Critical Environmental Concern (ACEC) Y____ N____

h) Based on the facilitysite information and any historical sampling data identify the sub-category into which the potential discharge falls Activity Category Activity Sub-Category I - Petroleum Related Site Remediation A Gasoline Only Sites ____

B Fuel Oils and Other Oil Sites (including Residential Non-Business Remediation Discharges) ____ C Petroleum Sites with Additional Contamination ____

II - Non Petroleum Site Remediation A Volatile Organic Compound (VOC) Only Sites _____ B VOC Sites with Additional Contamination ____ C Primarily Heavy Metal Sites ____

III - Contaminated Construction Dewatering A General Urban Fill Sites ____ B Known Contaminated Sites ____

Remediation General Permit Page 11 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

IV - Miscellaneous Related Discharges A Aquifer Pump Testing to Evaluate Formerly Contaminated Sites ____ B Well DevelopmentRehabilitation at ContaminatedFormerly Contaminated Sites ____ C Hydrostatic Testing of Pipelines and Tanks ____ D Long-Term Remediation of Contaminated Sumps and Dikes ____ E Short-term Contaminated Dredging Drain Back Waters (if not covered by 401404 permit) ____

2 Discharge information Please provide information about the discharge (attaching additional sheets as necessary) including

a) Describe the discharge activities for which the ownerapplicant is seeking coverage

b) Provide the following information about each discharge

1) Number of discharge points

2) What is the maximum and average flow rate of discharge (in cubic feet per second ft3s) Max flow____________ Is maximum flow a design value Y___ N____ Average flow (include units) __________ Is average flow a design value or estimate _________

3) Latitude and longitude of each discharge within 100 feet pt1 lat_____________ long_____________ pt2 lat_____________ long_____________ pt3 lat_____________ long_____________ pt4 lat_____________ long_____________ pt5 lat_____________ long_____________ pt6 lat_____________ long_____________ pt7 lat_____________ long_____________ pt8 lat_____________ long_____________ etc

4) If hydrostatic testing total volume of the discharge (gals)_________

5) Is the discharge intermittent ____ or seasonal____ Is discharge ongoing Y ____ N______

c) Expected dates of discharge (mmddyy) start_____________ end_________________ d) Please attach a line drawing or flow schematic showing water flow through the facility including 1 sources of intake water 2 contributing flow from the operation 3 treatment units and 4 discharge points and receiving waters(s)

Remediation General Permit Page 12 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

3 Contaminant information a) Based on the sub-category selected (see Appendix III) indicate whether each listed chemical is believed present or believed absent in the potential discharge Attach additional sheets as needed

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

1 Total Suspended Solids (TSS) 2 Total Residual Chlorine (TRC) 3 Total Petroleum Hydrocarbons (TPH) 4 Cyanide (CN) 57125 5 Benzene (B) 71432 6 Toluene (T) 108883 7 Ethylbenzene (E) 100414 8 (mpo) Xylenes (X) 108883

106423 95476

1330207

9 Total BTEX 2 na 10 Ethylene Dibromide (EDB) (12- Dibromoethane) 3

106934

11 Methyl-tert-Butyl Ether (MtBE)

1634044

12 tert-Butyl Alcohol (TBA) (Tertiary-Butanol)

75650

Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI 2 BTEX = Sum of Benzene Toluene Ethylbenzene total Xylenes 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England

Remediation General Permit Page 13 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
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                  5. TextField38[0] estimate
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                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                                      4. TextField50[0]
                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
                                          11. TextField59[0] Class B
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Page 8: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

January 31 2015

United States Environmental Protection Agency 5 Post Office Square Suite 100 Boston Massachusetts 02109-3912 Attn Remediation General Permit NOI Processing

Subject Notice of Intent for Remediation General Permit Groveton Wastewater Lagoons 10 Mechanic Street Groveton New Hampshire

Mr Alvarez

Stonecipher amp Clark Environmental Solutions LLC (SampC) is submitting the attached Remediation General Permit Notice of Intent for the above-referenced location (the ldquoSiterdquo) on behalf of Mr Bob Chapman Please find the NOI form under Attachment A The Site is the former Wausau Paper Mill and is located on two parcels located in Groveton NH along the Upper Ammonoosuc River Please refer to the enclosed locus map (Figure 1) The Site consists of three clarifiers on the 95 acre parcel located adjacent to the Upper Ammonoosuc River and the wastewater lagoonpolishing ponds are located on the 53 acre parcel also adjacent to the Ammonoosuc River

General Site Information

All processes pertaining to the paper mill have ceased and reportedly the lagoons were discharged and cleaned in 2008 under an individual NPDES permit (Permit No NH0001562) This permit expired in 2011 The lagoons have reportedly received no additional wastewater since then Water currently in the open-topped lagoon area and clarifiers is a result of stormwater collection (supernatant) over the past few years The RGP is being sought in order to discharge the remaining supernatant water as part of a final dewatering in order to install drain-holes and maintain the lagoons in an empty state as well as eventual demolition of the clarifiers

Discharge Information

The expired NPDES Individual Permit allowed discharge via Outfall 017 which discharges approximately 05 miles west into the Connecticut River Please see Attachment A for a aerial view of the Site including the approximate outfall locationThis RGP application seeks to maintain the the Outfall 017 discharge point

STON

ECIPH

ER amp C

LARK EN

VIRON

MEN

TAL SO

LUTIO

NS LLC

111 Saranac Street Stu

dio 8 L

ittleton N

H 03561 6035755154

ww

wston

eciph

erand

clarkcom

In December 2013 John King of EPA approved the Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire report prepared and submitted by Horizons Engineering Inc Please find this report under Attachment B This report outlined the results of the sampling plan completed in October 2013 which included samples from 9 locations the four quadrants of the main lagoon the two polishing ponds (lagoons) and the three clarifiers Three samples were taken at each of the nine sampling locations one grab sample from mid-depth between the supernatantsludge interface and the surface one grab sample from the supernatant interface and one sludge sample from the bottom The laboratory results are included in the decommissioning plan report and indicate that detected parameter concentrations in the samples obtained from mid-depth between the supernatant interface and the water surface were all within the former NPDES permit standards with the exception of the sample from Clarifier 1 for which we are NOT seeking coverage under the RGP NOI

The recommendation of the approved decommissioning report was to pump each lagoon and clarifier down to the supernatant interface individually into Outfall 017 (which discharges directly to the Connecticut River) Pumping rates were specified in the report based on BOD and TSS and turbidity monitoring was recommended in order to determine when interface was reached

In November 2014 SampC oversaw discharge of the supernatant from the lagoon area as specified in the approved decommissioning report The pumping rate was greatly reduced from the allowable rate in the plan due to availability of pumping equipment as well as field conditions Turbidity was closely monitored Field observations indicated that the line between the supernatant and the interface was quite sharply defined Close monitoring allowed SampC to be confident in the discharge of only supernatant

Contaminant Information

For the purposes of this permit application it is assumed that the Site falls under Category III subcategory B Upon reviewing Appendix III regarding Effluent Limits and Monitoring Requirements it appears that the supernatant laboratory results for all sampled locations with the exception of Clarifier 1 average 19 mgl TSS which is well below the specified TSS effluent limit of 30 mgl TSS (monthly average) Laboratory results from supernatant collected from Clarifier 3 yielded a TSS value of 45 mgl Please note that using this TSS value as a maximum daily TSS value in the NOI application under Appendix III will therefore skew the actual amount of daily TSS as the dewatering of Clarifier 3 is anticipated at a lesser rate than the 1000 gpm maximum In addition the volume of water in Clarifier 3 (reportedly 9 feet) will be discharged prior to achieving a 24-hr time period

Group I PAHs and Group II PAHs fall below the respective 100 ugl and 1000 ugl daily limits

SampC collected and submitted to the laboratory a confirmatory sample of the lagoon supernatant on December 3 2014 This sample was tested for Volatile Organic Compounds (VOCs) Group I PAHs Group II PAHs and all required metals to be tested under Appendix III Category III subcategory B with the exception of antimony copper nickel zinc and iron

Once the supernatantsludge interface has been reached the plan is to dewater the remaining water overland via NHDES Temporary Groundwater Discharge Permit This will NOT be released to any surface waters

Treatment System Information

No treatment is proposed during dewatering The pumping discharge rate is proposed to be a maximum of 1000 gpm

Receiving Surface Water(s) Information

Discharge will occur approximately 05 miles away to Outfall 017 via underground 32rdquo pipe into the Connecticut River

Endangered Species Act amp National Historic Preservation Act Reviews

SampC has received verbal response from United States Fish and Wildlife Service that the discharge activities are ldquounlikely to adversely affectrdquo listed species or critical habitat When official sign-off is received SampC will forward that response

Under Attachment D please find the correspondence with New Hampshire Division of Historical Resources indicating that findings for this project considered ldquoNo Historic Properties Affectedrdquo

Please contact the undersigned if you have any questions or require additional information

Sincerely

Sylvia A Clark Co-OwnerProject Manager Stonecipher amp Clark Environmental Solutions LLC Office 6035755154 Cell 8027341403 sclarkstonecipherandclarkcom

Attachments Figure 1 ndash Site Aerial Map Figure 2 ndash Treatment System Flow Diagram Attachment A ndash Notice of Intent Form Attachment B ndash EPA Approved Decommissioning Plan Attachment C ndash December 3 2014 Laboratory Results Attachment D ndash NH DHR Correspondence Attachment E - US FWS Correspondence (To be forwarded)

cc Jeff Andrews NHDES

Sylvia
Stamp

Figure 1

Lagoon

Clarifiers

Outfall 017

Stonecipheramp Clark Environmental Solutions LLC 111 Saranac Street Studio 8

Littleton New Hampshire 03561

6035755154

Groveton Wastewater Lagoons amp Clarifiers Groveton NH

SampC Project 2014-062

Aerial Map

Figure 2

LAGOON AREA

CLARIFIER 2

CLARIFIER 1

CLARIFIER 3

UPPER AMMONOOSUC RIVER

MONITORING

CHAMBER

32 PIPE DISCHARGES

APPROX 05 MILES WEST

INTO THE CONNECTICUT

RIVER (OUTFALL 017)

STONECIPHER amp CLARK

ENVIRONMENTAL SOLUTIONS LLC

111 SARANAC STREET STUDIO 8

LITTLETON NEW HAMPSHIRE 03561

6035755154

GROVETON WASTEWATER LAGOONS

GROVETON NEW HAMPSHIRE

FLOW SCHEMATIC

Attachment A

NPDES Permit No MAG910000 NPDES Permit No NHG910000

B Suggested Form for Notice of Intent (NOI) for the Remediation General Permit

1 General facilitysite information Please provide the following information about the site

a) Name of facilitysite Facilitysite mailing address

Location of facilitysite

longitude_______________ latitude_______________

Facility SIC code(s)

Street

b) Name of facilitysite owner Town

Email address of facilitysite owner State Zip County

Telephone no of facilitysite owner

Fax no of facilitysite owner Owner is (check one) 1 Federal____ 2 StateTribal____ 3 Private____ 4 Other ____ if so describe

Address of owner (if different from site)

Street

Town State Zip County

c) Legal name of operator Operator telephone no

Operator fax no Operator email

Operator contact name and title

Address of operator (if different from owner)

Street

Town State Zip County

Remediation General Permit Page 10 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

d) Check Y for Ayes or N for Ano for the following 1 Has a prior NPDES permit exclusion been granted for the discharge Y___ N___ if Y number_________________ 2 Has a prior NPDES application (Form 1 amp 2C) ever been filed for the discharge Y___ N___ if Y date and tracking __________________________________________________________________ 3 Is the discharge a ldquonew dischargerdquo as defined by 40 CFR 1222 Y___ N___ 4 For sites in Massachusetts is the discharge covered under the Massachusetts Contingency Plan (MCP) and exempt from state permitting Y___ N___

e) Is sitefacility subject to any State permitting license f) Is the sitefacility covered by any other EPA permit including or other action which is causing the generation of 1 Multi-Sector General Permit Y___ N___ discharge Y___ N___ if Y number_______________ If Y please list 2 Final Dewatering General Permit Y___ N___ 1 site identification assigned by the state of NH or if Y number________________ MA_________________________________________ 3 EPA Construction General Permit Y___ N___ 2 permit or license assigned____________________ if Y number _______________ 3 state agency contact information name location and 4 Individual NPDES permit Y___ N___ telephone number if Y number_____________

5 any other water quality related individual or general permit Y___ N___ if Y number______________

g) Is the sitefacility located within or does it discharge to an Area of Critical Environmental Concern (ACEC) Y____ N____

h) Based on the facilitysite information and any historical sampling data identify the sub-category into which the potential discharge falls Activity Category Activity Sub-Category I - Petroleum Related Site Remediation A Gasoline Only Sites ____

B Fuel Oils and Other Oil Sites (including Residential Non-Business Remediation Discharges) ____ C Petroleum Sites with Additional Contamination ____

II - Non Petroleum Site Remediation A Volatile Organic Compound (VOC) Only Sites _____ B VOC Sites with Additional Contamination ____ C Primarily Heavy Metal Sites ____

III - Contaminated Construction Dewatering A General Urban Fill Sites ____ B Known Contaminated Sites ____

Remediation General Permit Page 11 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

IV - Miscellaneous Related Discharges A Aquifer Pump Testing to Evaluate Formerly Contaminated Sites ____ B Well DevelopmentRehabilitation at ContaminatedFormerly Contaminated Sites ____ C Hydrostatic Testing of Pipelines and Tanks ____ D Long-Term Remediation of Contaminated Sumps and Dikes ____ E Short-term Contaminated Dredging Drain Back Waters (if not covered by 401404 permit) ____

2 Discharge information Please provide information about the discharge (attaching additional sheets as necessary) including

a) Describe the discharge activities for which the ownerapplicant is seeking coverage

b) Provide the following information about each discharge

1) Number of discharge points

2) What is the maximum and average flow rate of discharge (in cubic feet per second ft3s) Max flow____________ Is maximum flow a design value Y___ N____ Average flow (include units) __________ Is average flow a design value or estimate _________

3) Latitude and longitude of each discharge within 100 feet pt1 lat_____________ long_____________ pt2 lat_____________ long_____________ pt3 lat_____________ long_____________ pt4 lat_____________ long_____________ pt5 lat_____________ long_____________ pt6 lat_____________ long_____________ pt7 lat_____________ long_____________ pt8 lat_____________ long_____________ etc

4) If hydrostatic testing total volume of the discharge (gals)_________

5) Is the discharge intermittent ____ or seasonal____ Is discharge ongoing Y ____ N______

c) Expected dates of discharge (mmddyy) start_____________ end_________________ d) Please attach a line drawing or flow schematic showing water flow through the facility including 1 sources of intake water 2 contributing flow from the operation 3 treatment units and 4 discharge points and receiving waters(s)

Remediation General Permit Page 12 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

3 Contaminant information a) Based on the sub-category selected (see Appendix III) indicate whether each listed chemical is believed present or believed absent in the potential discharge Attach additional sheets as needed

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

1 Total Suspended Solids (TSS) 2 Total Residual Chlorine (TRC) 3 Total Petroleum Hydrocarbons (TPH) 4 Cyanide (CN) 57125 5 Benzene (B) 71432 6 Toluene (T) 108883 7 Ethylbenzene (E) 100414 8 (mpo) Xylenes (X) 108883

106423 95476

1330207

9 Total BTEX 2 na 10 Ethylene Dibromide (EDB) (12- Dibromoethane) 3

106934

11 Methyl-tert-Butyl Ether (MtBE)

1634044

12 tert-Butyl Alcohol (TBA) (Tertiary-Butanol)

75650

Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI 2 BTEX = Sum of Benzene Toluene Ethylbenzene total Xylenes 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England

Remediation General Permit Page 13 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
            1. Page11[0]
              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
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                  5. TextField38[0] estimate
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                  8. DateTimeField1[0] 312015
                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
                                          11. TextField59[0] Class B
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Page 9: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

In December 2013 John King of EPA approved the Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire report prepared and submitted by Horizons Engineering Inc Please find this report under Attachment B This report outlined the results of the sampling plan completed in October 2013 which included samples from 9 locations the four quadrants of the main lagoon the two polishing ponds (lagoons) and the three clarifiers Three samples were taken at each of the nine sampling locations one grab sample from mid-depth between the supernatantsludge interface and the surface one grab sample from the supernatant interface and one sludge sample from the bottom The laboratory results are included in the decommissioning plan report and indicate that detected parameter concentrations in the samples obtained from mid-depth between the supernatant interface and the water surface were all within the former NPDES permit standards with the exception of the sample from Clarifier 1 for which we are NOT seeking coverage under the RGP NOI

The recommendation of the approved decommissioning report was to pump each lagoon and clarifier down to the supernatant interface individually into Outfall 017 (which discharges directly to the Connecticut River) Pumping rates were specified in the report based on BOD and TSS and turbidity monitoring was recommended in order to determine when interface was reached

In November 2014 SampC oversaw discharge of the supernatant from the lagoon area as specified in the approved decommissioning report The pumping rate was greatly reduced from the allowable rate in the plan due to availability of pumping equipment as well as field conditions Turbidity was closely monitored Field observations indicated that the line between the supernatant and the interface was quite sharply defined Close monitoring allowed SampC to be confident in the discharge of only supernatant

Contaminant Information

For the purposes of this permit application it is assumed that the Site falls under Category III subcategory B Upon reviewing Appendix III regarding Effluent Limits and Monitoring Requirements it appears that the supernatant laboratory results for all sampled locations with the exception of Clarifier 1 average 19 mgl TSS which is well below the specified TSS effluent limit of 30 mgl TSS (monthly average) Laboratory results from supernatant collected from Clarifier 3 yielded a TSS value of 45 mgl Please note that using this TSS value as a maximum daily TSS value in the NOI application under Appendix III will therefore skew the actual amount of daily TSS as the dewatering of Clarifier 3 is anticipated at a lesser rate than the 1000 gpm maximum In addition the volume of water in Clarifier 3 (reportedly 9 feet) will be discharged prior to achieving a 24-hr time period

Group I PAHs and Group II PAHs fall below the respective 100 ugl and 1000 ugl daily limits

SampC collected and submitted to the laboratory a confirmatory sample of the lagoon supernatant on December 3 2014 This sample was tested for Volatile Organic Compounds (VOCs) Group I PAHs Group II PAHs and all required metals to be tested under Appendix III Category III subcategory B with the exception of antimony copper nickel zinc and iron

Once the supernatantsludge interface has been reached the plan is to dewater the remaining water overland via NHDES Temporary Groundwater Discharge Permit This will NOT be released to any surface waters

Treatment System Information

No treatment is proposed during dewatering The pumping discharge rate is proposed to be a maximum of 1000 gpm

Receiving Surface Water(s) Information

Discharge will occur approximately 05 miles away to Outfall 017 via underground 32rdquo pipe into the Connecticut River

Endangered Species Act amp National Historic Preservation Act Reviews

SampC has received verbal response from United States Fish and Wildlife Service that the discharge activities are ldquounlikely to adversely affectrdquo listed species or critical habitat When official sign-off is received SampC will forward that response

Under Attachment D please find the correspondence with New Hampshire Division of Historical Resources indicating that findings for this project considered ldquoNo Historic Properties Affectedrdquo

Please contact the undersigned if you have any questions or require additional information

Sincerely

Sylvia A Clark Co-OwnerProject Manager Stonecipher amp Clark Environmental Solutions LLC Office 6035755154 Cell 8027341403 sclarkstonecipherandclarkcom

Attachments Figure 1 ndash Site Aerial Map Figure 2 ndash Treatment System Flow Diagram Attachment A ndash Notice of Intent Form Attachment B ndash EPA Approved Decommissioning Plan Attachment C ndash December 3 2014 Laboratory Results Attachment D ndash NH DHR Correspondence Attachment E - US FWS Correspondence (To be forwarded)

cc Jeff Andrews NHDES

Sylvia
Stamp

Figure 1

Lagoon

Clarifiers

Outfall 017

Stonecipheramp Clark Environmental Solutions LLC 111 Saranac Street Studio 8

Littleton New Hampshire 03561

6035755154

Groveton Wastewater Lagoons amp Clarifiers Groveton NH

SampC Project 2014-062

Aerial Map

Figure 2

LAGOON AREA

CLARIFIER 2

CLARIFIER 1

CLARIFIER 3

UPPER AMMONOOSUC RIVER

MONITORING

CHAMBER

32 PIPE DISCHARGES

APPROX 05 MILES WEST

INTO THE CONNECTICUT

RIVER (OUTFALL 017)

STONECIPHER amp CLARK

ENVIRONMENTAL SOLUTIONS LLC

111 SARANAC STREET STUDIO 8

LITTLETON NEW HAMPSHIRE 03561

6035755154

GROVETON WASTEWATER LAGOONS

GROVETON NEW HAMPSHIRE

FLOW SCHEMATIC

Attachment A

NPDES Permit No MAG910000 NPDES Permit No NHG910000

B Suggested Form for Notice of Intent (NOI) for the Remediation General Permit

1 General facilitysite information Please provide the following information about the site

a) Name of facilitysite Facilitysite mailing address

Location of facilitysite

longitude_______________ latitude_______________

Facility SIC code(s)

Street

b) Name of facilitysite owner Town

Email address of facilitysite owner State Zip County

Telephone no of facilitysite owner

Fax no of facilitysite owner Owner is (check one) 1 Federal____ 2 StateTribal____ 3 Private____ 4 Other ____ if so describe

Address of owner (if different from site)

Street

Town State Zip County

c) Legal name of operator Operator telephone no

Operator fax no Operator email

Operator contact name and title

Address of operator (if different from owner)

Street

Town State Zip County

Remediation General Permit Page 10 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

d) Check Y for Ayes or N for Ano for the following 1 Has a prior NPDES permit exclusion been granted for the discharge Y___ N___ if Y number_________________ 2 Has a prior NPDES application (Form 1 amp 2C) ever been filed for the discharge Y___ N___ if Y date and tracking __________________________________________________________________ 3 Is the discharge a ldquonew dischargerdquo as defined by 40 CFR 1222 Y___ N___ 4 For sites in Massachusetts is the discharge covered under the Massachusetts Contingency Plan (MCP) and exempt from state permitting Y___ N___

e) Is sitefacility subject to any State permitting license f) Is the sitefacility covered by any other EPA permit including or other action which is causing the generation of 1 Multi-Sector General Permit Y___ N___ discharge Y___ N___ if Y number_______________ If Y please list 2 Final Dewatering General Permit Y___ N___ 1 site identification assigned by the state of NH or if Y number________________ MA_________________________________________ 3 EPA Construction General Permit Y___ N___ 2 permit or license assigned____________________ if Y number _______________ 3 state agency contact information name location and 4 Individual NPDES permit Y___ N___ telephone number if Y number_____________

5 any other water quality related individual or general permit Y___ N___ if Y number______________

g) Is the sitefacility located within or does it discharge to an Area of Critical Environmental Concern (ACEC) Y____ N____

h) Based on the facilitysite information and any historical sampling data identify the sub-category into which the potential discharge falls Activity Category Activity Sub-Category I - Petroleum Related Site Remediation A Gasoline Only Sites ____

B Fuel Oils and Other Oil Sites (including Residential Non-Business Remediation Discharges) ____ C Petroleum Sites with Additional Contamination ____

II - Non Petroleum Site Remediation A Volatile Organic Compound (VOC) Only Sites _____ B VOC Sites with Additional Contamination ____ C Primarily Heavy Metal Sites ____

III - Contaminated Construction Dewatering A General Urban Fill Sites ____ B Known Contaminated Sites ____

Remediation General Permit Page 11 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

IV - Miscellaneous Related Discharges A Aquifer Pump Testing to Evaluate Formerly Contaminated Sites ____ B Well DevelopmentRehabilitation at ContaminatedFormerly Contaminated Sites ____ C Hydrostatic Testing of Pipelines and Tanks ____ D Long-Term Remediation of Contaminated Sumps and Dikes ____ E Short-term Contaminated Dredging Drain Back Waters (if not covered by 401404 permit) ____

2 Discharge information Please provide information about the discharge (attaching additional sheets as necessary) including

a) Describe the discharge activities for which the ownerapplicant is seeking coverage

b) Provide the following information about each discharge

1) Number of discharge points

2) What is the maximum and average flow rate of discharge (in cubic feet per second ft3s) Max flow____________ Is maximum flow a design value Y___ N____ Average flow (include units) __________ Is average flow a design value or estimate _________

3) Latitude and longitude of each discharge within 100 feet pt1 lat_____________ long_____________ pt2 lat_____________ long_____________ pt3 lat_____________ long_____________ pt4 lat_____________ long_____________ pt5 lat_____________ long_____________ pt6 lat_____________ long_____________ pt7 lat_____________ long_____________ pt8 lat_____________ long_____________ etc

4) If hydrostatic testing total volume of the discharge (gals)_________

5) Is the discharge intermittent ____ or seasonal____ Is discharge ongoing Y ____ N______

c) Expected dates of discharge (mmddyy) start_____________ end_________________ d) Please attach a line drawing or flow schematic showing water flow through the facility including 1 sources of intake water 2 contributing flow from the operation 3 treatment units and 4 discharge points and receiving waters(s)

Remediation General Permit Page 12 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

3 Contaminant information a) Based on the sub-category selected (see Appendix III) indicate whether each listed chemical is believed present or believed absent in the potential discharge Attach additional sheets as needed

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

1 Total Suspended Solids (TSS) 2 Total Residual Chlorine (TRC) 3 Total Petroleum Hydrocarbons (TPH) 4 Cyanide (CN) 57125 5 Benzene (B) 71432 6 Toluene (T) 108883 7 Ethylbenzene (E) 100414 8 (mpo) Xylenes (X) 108883

106423 95476

1330207

9 Total BTEX 2 na 10 Ethylene Dibromide (EDB) (12- Dibromoethane) 3

106934

11 Methyl-tert-Butyl Ether (MtBE)

1634044

12 tert-Butyl Alcohol (TBA) (Tertiary-Butanol)

75650

Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI 2 BTEX = Sum of Benzene Toluene Ethylbenzene total Xylenes 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England

Remediation General Permit Page 13 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
                  3. TextField36[0] 29
                  4. TextField37[0] 22
                  5. TextField38[0] estimate
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                  8. DateTimeField1[0] 312015
                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                      26. TextField89[1] GRAB
                      27. TextField89[2] 2540D-97
                      28. TextField89[3] 5 mgl
                      29. TextField89[4] 45000
                      30. TextField89[5] 245
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Page 10: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Once the supernatantsludge interface has been reached the plan is to dewater the remaining water overland via NHDES Temporary Groundwater Discharge Permit This will NOT be released to any surface waters

Treatment System Information

No treatment is proposed during dewatering The pumping discharge rate is proposed to be a maximum of 1000 gpm

Receiving Surface Water(s) Information

Discharge will occur approximately 05 miles away to Outfall 017 via underground 32rdquo pipe into the Connecticut River

Endangered Species Act amp National Historic Preservation Act Reviews

SampC has received verbal response from United States Fish and Wildlife Service that the discharge activities are ldquounlikely to adversely affectrdquo listed species or critical habitat When official sign-off is received SampC will forward that response

Under Attachment D please find the correspondence with New Hampshire Division of Historical Resources indicating that findings for this project considered ldquoNo Historic Properties Affectedrdquo

Please contact the undersigned if you have any questions or require additional information

Sincerely

Sylvia A Clark Co-OwnerProject Manager Stonecipher amp Clark Environmental Solutions LLC Office 6035755154 Cell 8027341403 sclarkstonecipherandclarkcom

Attachments Figure 1 ndash Site Aerial Map Figure 2 ndash Treatment System Flow Diagram Attachment A ndash Notice of Intent Form Attachment B ndash EPA Approved Decommissioning Plan Attachment C ndash December 3 2014 Laboratory Results Attachment D ndash NH DHR Correspondence Attachment E - US FWS Correspondence (To be forwarded)

cc Jeff Andrews NHDES

Sylvia
Stamp

Figure 1

Lagoon

Clarifiers

Outfall 017

Stonecipheramp Clark Environmental Solutions LLC 111 Saranac Street Studio 8

Littleton New Hampshire 03561

6035755154

Groveton Wastewater Lagoons amp Clarifiers Groveton NH

SampC Project 2014-062

Aerial Map

Figure 2

LAGOON AREA

CLARIFIER 2

CLARIFIER 1

CLARIFIER 3

UPPER AMMONOOSUC RIVER

MONITORING

CHAMBER

32 PIPE DISCHARGES

APPROX 05 MILES WEST

INTO THE CONNECTICUT

RIVER (OUTFALL 017)

STONECIPHER amp CLARK

ENVIRONMENTAL SOLUTIONS LLC

111 SARANAC STREET STUDIO 8

LITTLETON NEW HAMPSHIRE 03561

6035755154

GROVETON WASTEWATER LAGOONS

GROVETON NEW HAMPSHIRE

FLOW SCHEMATIC

Attachment A

NPDES Permit No MAG910000 NPDES Permit No NHG910000

B Suggested Form for Notice of Intent (NOI) for the Remediation General Permit

1 General facilitysite information Please provide the following information about the site

a) Name of facilitysite Facilitysite mailing address

Location of facilitysite

longitude_______________ latitude_______________

Facility SIC code(s)

Street

b) Name of facilitysite owner Town

Email address of facilitysite owner State Zip County

Telephone no of facilitysite owner

Fax no of facilitysite owner Owner is (check one) 1 Federal____ 2 StateTribal____ 3 Private____ 4 Other ____ if so describe

Address of owner (if different from site)

Street

Town State Zip County

c) Legal name of operator Operator telephone no

Operator fax no Operator email

Operator contact name and title

Address of operator (if different from owner)

Street

Town State Zip County

Remediation General Permit Page 10 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

d) Check Y for Ayes or N for Ano for the following 1 Has a prior NPDES permit exclusion been granted for the discharge Y___ N___ if Y number_________________ 2 Has a prior NPDES application (Form 1 amp 2C) ever been filed for the discharge Y___ N___ if Y date and tracking __________________________________________________________________ 3 Is the discharge a ldquonew dischargerdquo as defined by 40 CFR 1222 Y___ N___ 4 For sites in Massachusetts is the discharge covered under the Massachusetts Contingency Plan (MCP) and exempt from state permitting Y___ N___

e) Is sitefacility subject to any State permitting license f) Is the sitefacility covered by any other EPA permit including or other action which is causing the generation of 1 Multi-Sector General Permit Y___ N___ discharge Y___ N___ if Y number_______________ If Y please list 2 Final Dewatering General Permit Y___ N___ 1 site identification assigned by the state of NH or if Y number________________ MA_________________________________________ 3 EPA Construction General Permit Y___ N___ 2 permit or license assigned____________________ if Y number _______________ 3 state agency contact information name location and 4 Individual NPDES permit Y___ N___ telephone number if Y number_____________

5 any other water quality related individual or general permit Y___ N___ if Y number______________

g) Is the sitefacility located within or does it discharge to an Area of Critical Environmental Concern (ACEC) Y____ N____

h) Based on the facilitysite information and any historical sampling data identify the sub-category into which the potential discharge falls Activity Category Activity Sub-Category I - Petroleum Related Site Remediation A Gasoline Only Sites ____

B Fuel Oils and Other Oil Sites (including Residential Non-Business Remediation Discharges) ____ C Petroleum Sites with Additional Contamination ____

II - Non Petroleum Site Remediation A Volatile Organic Compound (VOC) Only Sites _____ B VOC Sites with Additional Contamination ____ C Primarily Heavy Metal Sites ____

III - Contaminated Construction Dewatering A General Urban Fill Sites ____ B Known Contaminated Sites ____

Remediation General Permit Page 11 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

IV - Miscellaneous Related Discharges A Aquifer Pump Testing to Evaluate Formerly Contaminated Sites ____ B Well DevelopmentRehabilitation at ContaminatedFormerly Contaminated Sites ____ C Hydrostatic Testing of Pipelines and Tanks ____ D Long-Term Remediation of Contaminated Sumps and Dikes ____ E Short-term Contaminated Dredging Drain Back Waters (if not covered by 401404 permit) ____

2 Discharge information Please provide information about the discharge (attaching additional sheets as necessary) including

a) Describe the discharge activities for which the ownerapplicant is seeking coverage

b) Provide the following information about each discharge

1) Number of discharge points

2) What is the maximum and average flow rate of discharge (in cubic feet per second ft3s) Max flow____________ Is maximum flow a design value Y___ N____ Average flow (include units) __________ Is average flow a design value or estimate _________

3) Latitude and longitude of each discharge within 100 feet pt1 lat_____________ long_____________ pt2 lat_____________ long_____________ pt3 lat_____________ long_____________ pt4 lat_____________ long_____________ pt5 lat_____________ long_____________ pt6 lat_____________ long_____________ pt7 lat_____________ long_____________ pt8 lat_____________ long_____________ etc

4) If hydrostatic testing total volume of the discharge (gals)_________

5) Is the discharge intermittent ____ or seasonal____ Is discharge ongoing Y ____ N______

c) Expected dates of discharge (mmddyy) start_____________ end_________________ d) Please attach a line drawing or flow schematic showing water flow through the facility including 1 sources of intake water 2 contributing flow from the operation 3 treatment units and 4 discharge points and receiving waters(s)

Remediation General Permit Page 12 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

3 Contaminant information a) Based on the sub-category selected (see Appendix III) indicate whether each listed chemical is believed present or believed absent in the potential discharge Attach additional sheets as needed

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

1 Total Suspended Solids (TSS) 2 Total Residual Chlorine (TRC) 3 Total Petroleum Hydrocarbons (TPH) 4 Cyanide (CN) 57125 5 Benzene (B) 71432 6 Toluene (T) 108883 7 Ethylbenzene (E) 100414 8 (mpo) Xylenes (X) 108883

106423 95476

1330207

9 Total BTEX 2 na 10 Ethylene Dibromide (EDB) (12- Dibromoethane) 3

106934

11 Methyl-tert-Butyl Ether (MtBE)

1634044

12 tert-Butyl Alcohol (TBA) (Tertiary-Butanol)

75650

Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI 2 BTEX = Sum of Benzene Toluene Ethylbenzene total Xylenes 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England

Remediation General Permit Page 13 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
                  3. TextField36[0] 29
                  4. TextField37[0] 22
                  5. TextField38[0] estimate
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                  8. DateTimeField1[0] 312015
                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
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Page 11: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Figure 1

Lagoon

Clarifiers

Outfall 017

Stonecipheramp Clark Environmental Solutions LLC 111 Saranac Street Studio 8

Littleton New Hampshire 03561

6035755154

Groveton Wastewater Lagoons amp Clarifiers Groveton NH

SampC Project 2014-062

Aerial Map

Figure 2

LAGOON AREA

CLARIFIER 2

CLARIFIER 1

CLARIFIER 3

UPPER AMMONOOSUC RIVER

MONITORING

CHAMBER

32 PIPE DISCHARGES

APPROX 05 MILES WEST

INTO THE CONNECTICUT

RIVER (OUTFALL 017)

STONECIPHER amp CLARK

ENVIRONMENTAL SOLUTIONS LLC

111 SARANAC STREET STUDIO 8

LITTLETON NEW HAMPSHIRE 03561

6035755154

GROVETON WASTEWATER LAGOONS

GROVETON NEW HAMPSHIRE

FLOW SCHEMATIC

Attachment A

NPDES Permit No MAG910000 NPDES Permit No NHG910000

B Suggested Form for Notice of Intent (NOI) for the Remediation General Permit

1 General facilitysite information Please provide the following information about the site

a) Name of facilitysite Facilitysite mailing address

Location of facilitysite

longitude_______________ latitude_______________

Facility SIC code(s)

Street

b) Name of facilitysite owner Town

Email address of facilitysite owner State Zip County

Telephone no of facilitysite owner

Fax no of facilitysite owner Owner is (check one) 1 Federal____ 2 StateTribal____ 3 Private____ 4 Other ____ if so describe

Address of owner (if different from site)

Street

Town State Zip County

c) Legal name of operator Operator telephone no

Operator fax no Operator email

Operator contact name and title

Address of operator (if different from owner)

Street

Town State Zip County

Remediation General Permit Page 10 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

d) Check Y for Ayes or N for Ano for the following 1 Has a prior NPDES permit exclusion been granted for the discharge Y___ N___ if Y number_________________ 2 Has a prior NPDES application (Form 1 amp 2C) ever been filed for the discharge Y___ N___ if Y date and tracking __________________________________________________________________ 3 Is the discharge a ldquonew dischargerdquo as defined by 40 CFR 1222 Y___ N___ 4 For sites in Massachusetts is the discharge covered under the Massachusetts Contingency Plan (MCP) and exempt from state permitting Y___ N___

e) Is sitefacility subject to any State permitting license f) Is the sitefacility covered by any other EPA permit including or other action which is causing the generation of 1 Multi-Sector General Permit Y___ N___ discharge Y___ N___ if Y number_______________ If Y please list 2 Final Dewatering General Permit Y___ N___ 1 site identification assigned by the state of NH or if Y number________________ MA_________________________________________ 3 EPA Construction General Permit Y___ N___ 2 permit or license assigned____________________ if Y number _______________ 3 state agency contact information name location and 4 Individual NPDES permit Y___ N___ telephone number if Y number_____________

5 any other water quality related individual or general permit Y___ N___ if Y number______________

g) Is the sitefacility located within or does it discharge to an Area of Critical Environmental Concern (ACEC) Y____ N____

h) Based on the facilitysite information and any historical sampling data identify the sub-category into which the potential discharge falls Activity Category Activity Sub-Category I - Petroleum Related Site Remediation A Gasoline Only Sites ____

B Fuel Oils and Other Oil Sites (including Residential Non-Business Remediation Discharges) ____ C Petroleum Sites with Additional Contamination ____

II - Non Petroleum Site Remediation A Volatile Organic Compound (VOC) Only Sites _____ B VOC Sites with Additional Contamination ____ C Primarily Heavy Metal Sites ____

III - Contaminated Construction Dewatering A General Urban Fill Sites ____ B Known Contaminated Sites ____

Remediation General Permit Page 11 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

IV - Miscellaneous Related Discharges A Aquifer Pump Testing to Evaluate Formerly Contaminated Sites ____ B Well DevelopmentRehabilitation at ContaminatedFormerly Contaminated Sites ____ C Hydrostatic Testing of Pipelines and Tanks ____ D Long-Term Remediation of Contaminated Sumps and Dikes ____ E Short-term Contaminated Dredging Drain Back Waters (if not covered by 401404 permit) ____

2 Discharge information Please provide information about the discharge (attaching additional sheets as necessary) including

a) Describe the discharge activities for which the ownerapplicant is seeking coverage

b) Provide the following information about each discharge

1) Number of discharge points

2) What is the maximum and average flow rate of discharge (in cubic feet per second ft3s) Max flow____________ Is maximum flow a design value Y___ N____ Average flow (include units) __________ Is average flow a design value or estimate _________

3) Latitude and longitude of each discharge within 100 feet pt1 lat_____________ long_____________ pt2 lat_____________ long_____________ pt3 lat_____________ long_____________ pt4 lat_____________ long_____________ pt5 lat_____________ long_____________ pt6 lat_____________ long_____________ pt7 lat_____________ long_____________ pt8 lat_____________ long_____________ etc

4) If hydrostatic testing total volume of the discharge (gals)_________

5) Is the discharge intermittent ____ or seasonal____ Is discharge ongoing Y ____ N______

c) Expected dates of discharge (mmddyy) start_____________ end_________________ d) Please attach a line drawing or flow schematic showing water flow through the facility including 1 sources of intake water 2 contributing flow from the operation 3 treatment units and 4 discharge points and receiving waters(s)

Remediation General Permit Page 12 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

3 Contaminant information a) Based on the sub-category selected (see Appendix III) indicate whether each listed chemical is believed present or believed absent in the potential discharge Attach additional sheets as needed

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

1 Total Suspended Solids (TSS) 2 Total Residual Chlorine (TRC) 3 Total Petroleum Hydrocarbons (TPH) 4 Cyanide (CN) 57125 5 Benzene (B) 71432 6 Toluene (T) 108883 7 Ethylbenzene (E) 100414 8 (mpo) Xylenes (X) 108883

106423 95476

1330207

9 Total BTEX 2 na 10 Ethylene Dibromide (EDB) (12- Dibromoethane) 3

106934

11 Methyl-tert-Butyl Ether (MtBE)

1634044

12 tert-Butyl Alcohol (TBA) (Tertiary-Butanol)

75650

Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI 2 BTEX = Sum of Benzene Toluene Ethylbenzene total Xylenes 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England

Remediation General Permit Page 13 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
      1. topmostSubform[0]
        1. Page10[0]
          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
          13. RadioButtonList[0] 3
          14. TextField13[0]
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          16. TextField15[0]
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          18. TextField17[0]
          19. TextField18[0]
          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
            1. Page11[0]
              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              10. TextField41[0]
              11. TextField42[0] Permit expired in 2011
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
                                          11. TextField59[0] Class B
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Page 12: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Lagoon

Clarifiers

Outfall 017

Stonecipheramp Clark Environmental Solutions LLC 111 Saranac Street Studio 8

Littleton New Hampshire 03561

6035755154

Groveton Wastewater Lagoons amp Clarifiers Groveton NH

SampC Project 2014-062

Aerial Map

Figure 2

LAGOON AREA

CLARIFIER 2

CLARIFIER 1

CLARIFIER 3

UPPER AMMONOOSUC RIVER

MONITORING

CHAMBER

32 PIPE DISCHARGES

APPROX 05 MILES WEST

INTO THE CONNECTICUT

RIVER (OUTFALL 017)

STONECIPHER amp CLARK

ENVIRONMENTAL SOLUTIONS LLC

111 SARANAC STREET STUDIO 8

LITTLETON NEW HAMPSHIRE 03561

6035755154

GROVETON WASTEWATER LAGOONS

GROVETON NEW HAMPSHIRE

FLOW SCHEMATIC

Attachment A

NPDES Permit No MAG910000 NPDES Permit No NHG910000

B Suggested Form for Notice of Intent (NOI) for the Remediation General Permit

1 General facilitysite information Please provide the following information about the site

a) Name of facilitysite Facilitysite mailing address

Location of facilitysite

longitude_______________ latitude_______________

Facility SIC code(s)

Street

b) Name of facilitysite owner Town

Email address of facilitysite owner State Zip County

Telephone no of facilitysite owner

Fax no of facilitysite owner Owner is (check one) 1 Federal____ 2 StateTribal____ 3 Private____ 4 Other ____ if so describe

Address of owner (if different from site)

Street

Town State Zip County

c) Legal name of operator Operator telephone no

Operator fax no Operator email

Operator contact name and title

Address of operator (if different from owner)

Street

Town State Zip County

Remediation General Permit Page 10 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

d) Check Y for Ayes or N for Ano for the following 1 Has a prior NPDES permit exclusion been granted for the discharge Y___ N___ if Y number_________________ 2 Has a prior NPDES application (Form 1 amp 2C) ever been filed for the discharge Y___ N___ if Y date and tracking __________________________________________________________________ 3 Is the discharge a ldquonew dischargerdquo as defined by 40 CFR 1222 Y___ N___ 4 For sites in Massachusetts is the discharge covered under the Massachusetts Contingency Plan (MCP) and exempt from state permitting Y___ N___

e) Is sitefacility subject to any State permitting license f) Is the sitefacility covered by any other EPA permit including or other action which is causing the generation of 1 Multi-Sector General Permit Y___ N___ discharge Y___ N___ if Y number_______________ If Y please list 2 Final Dewatering General Permit Y___ N___ 1 site identification assigned by the state of NH or if Y number________________ MA_________________________________________ 3 EPA Construction General Permit Y___ N___ 2 permit or license assigned____________________ if Y number _______________ 3 state agency contact information name location and 4 Individual NPDES permit Y___ N___ telephone number if Y number_____________

5 any other water quality related individual or general permit Y___ N___ if Y number______________

g) Is the sitefacility located within or does it discharge to an Area of Critical Environmental Concern (ACEC) Y____ N____

h) Based on the facilitysite information and any historical sampling data identify the sub-category into which the potential discharge falls Activity Category Activity Sub-Category I - Petroleum Related Site Remediation A Gasoline Only Sites ____

B Fuel Oils and Other Oil Sites (including Residential Non-Business Remediation Discharges) ____ C Petroleum Sites with Additional Contamination ____

II - Non Petroleum Site Remediation A Volatile Organic Compound (VOC) Only Sites _____ B VOC Sites with Additional Contamination ____ C Primarily Heavy Metal Sites ____

III - Contaminated Construction Dewatering A General Urban Fill Sites ____ B Known Contaminated Sites ____

Remediation General Permit Page 11 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

IV - Miscellaneous Related Discharges A Aquifer Pump Testing to Evaluate Formerly Contaminated Sites ____ B Well DevelopmentRehabilitation at ContaminatedFormerly Contaminated Sites ____ C Hydrostatic Testing of Pipelines and Tanks ____ D Long-Term Remediation of Contaminated Sumps and Dikes ____ E Short-term Contaminated Dredging Drain Back Waters (if not covered by 401404 permit) ____

2 Discharge information Please provide information about the discharge (attaching additional sheets as necessary) including

a) Describe the discharge activities for which the ownerapplicant is seeking coverage

b) Provide the following information about each discharge

1) Number of discharge points

2) What is the maximum and average flow rate of discharge (in cubic feet per second ft3s) Max flow____________ Is maximum flow a design value Y___ N____ Average flow (include units) __________ Is average flow a design value or estimate _________

3) Latitude and longitude of each discharge within 100 feet pt1 lat_____________ long_____________ pt2 lat_____________ long_____________ pt3 lat_____________ long_____________ pt4 lat_____________ long_____________ pt5 lat_____________ long_____________ pt6 lat_____________ long_____________ pt7 lat_____________ long_____________ pt8 lat_____________ long_____________ etc

4) If hydrostatic testing total volume of the discharge (gals)_________

5) Is the discharge intermittent ____ or seasonal____ Is discharge ongoing Y ____ N______

c) Expected dates of discharge (mmddyy) start_____________ end_________________ d) Please attach a line drawing or flow schematic showing water flow through the facility including 1 sources of intake water 2 contributing flow from the operation 3 treatment units and 4 discharge points and receiving waters(s)

Remediation General Permit Page 12 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

3 Contaminant information a) Based on the sub-category selected (see Appendix III) indicate whether each listed chemical is believed present or believed absent in the potential discharge Attach additional sheets as needed

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

1 Total Suspended Solids (TSS) 2 Total Residual Chlorine (TRC) 3 Total Petroleum Hydrocarbons (TPH) 4 Cyanide (CN) 57125 5 Benzene (B) 71432 6 Toluene (T) 108883 7 Ethylbenzene (E) 100414 8 (mpo) Xylenes (X) 108883

106423 95476

1330207

9 Total BTEX 2 na 10 Ethylene Dibromide (EDB) (12- Dibromoethane) 3

106934

11 Methyl-tert-Butyl Ether (MtBE)

1634044

12 tert-Butyl Alcohol (TBA) (Tertiary-Butanol)

75650

Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI 2 BTEX = Sum of Benzene Toluene Ethylbenzene total Xylenes 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England

Remediation General Permit Page 13 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
            1. Page11[0]
              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
              3. RadioButtonList[0] 2
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
                  3. TextField36[0] 29
                  4. TextField37[0] 22
                  5. TextField38[0] estimate
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                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
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Page 13: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Figure 2

LAGOON AREA

CLARIFIER 2

CLARIFIER 1

CLARIFIER 3

UPPER AMMONOOSUC RIVER

MONITORING

CHAMBER

32 PIPE DISCHARGES

APPROX 05 MILES WEST

INTO THE CONNECTICUT

RIVER (OUTFALL 017)

STONECIPHER amp CLARK

ENVIRONMENTAL SOLUTIONS LLC

111 SARANAC STREET STUDIO 8

LITTLETON NEW HAMPSHIRE 03561

6035755154

GROVETON WASTEWATER LAGOONS

GROVETON NEW HAMPSHIRE

FLOW SCHEMATIC

Attachment A

NPDES Permit No MAG910000 NPDES Permit No NHG910000

B Suggested Form for Notice of Intent (NOI) for the Remediation General Permit

1 General facilitysite information Please provide the following information about the site

a) Name of facilitysite Facilitysite mailing address

Location of facilitysite

longitude_______________ latitude_______________

Facility SIC code(s)

Street

b) Name of facilitysite owner Town

Email address of facilitysite owner State Zip County

Telephone no of facilitysite owner

Fax no of facilitysite owner Owner is (check one) 1 Federal____ 2 StateTribal____ 3 Private____ 4 Other ____ if so describe

Address of owner (if different from site)

Street

Town State Zip County

c) Legal name of operator Operator telephone no

Operator fax no Operator email

Operator contact name and title

Address of operator (if different from owner)

Street

Town State Zip County

Remediation General Permit Page 10 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

d) Check Y for Ayes or N for Ano for the following 1 Has a prior NPDES permit exclusion been granted for the discharge Y___ N___ if Y number_________________ 2 Has a prior NPDES application (Form 1 amp 2C) ever been filed for the discharge Y___ N___ if Y date and tracking __________________________________________________________________ 3 Is the discharge a ldquonew dischargerdquo as defined by 40 CFR 1222 Y___ N___ 4 For sites in Massachusetts is the discharge covered under the Massachusetts Contingency Plan (MCP) and exempt from state permitting Y___ N___

e) Is sitefacility subject to any State permitting license f) Is the sitefacility covered by any other EPA permit including or other action which is causing the generation of 1 Multi-Sector General Permit Y___ N___ discharge Y___ N___ if Y number_______________ If Y please list 2 Final Dewatering General Permit Y___ N___ 1 site identification assigned by the state of NH or if Y number________________ MA_________________________________________ 3 EPA Construction General Permit Y___ N___ 2 permit or license assigned____________________ if Y number _______________ 3 state agency contact information name location and 4 Individual NPDES permit Y___ N___ telephone number if Y number_____________

5 any other water quality related individual or general permit Y___ N___ if Y number______________

g) Is the sitefacility located within or does it discharge to an Area of Critical Environmental Concern (ACEC) Y____ N____

h) Based on the facilitysite information and any historical sampling data identify the sub-category into which the potential discharge falls Activity Category Activity Sub-Category I - Petroleum Related Site Remediation A Gasoline Only Sites ____

B Fuel Oils and Other Oil Sites (including Residential Non-Business Remediation Discharges) ____ C Petroleum Sites with Additional Contamination ____

II - Non Petroleum Site Remediation A Volatile Organic Compound (VOC) Only Sites _____ B VOC Sites with Additional Contamination ____ C Primarily Heavy Metal Sites ____

III - Contaminated Construction Dewatering A General Urban Fill Sites ____ B Known Contaminated Sites ____

Remediation General Permit Page 11 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

IV - Miscellaneous Related Discharges A Aquifer Pump Testing to Evaluate Formerly Contaminated Sites ____ B Well DevelopmentRehabilitation at ContaminatedFormerly Contaminated Sites ____ C Hydrostatic Testing of Pipelines and Tanks ____ D Long-Term Remediation of Contaminated Sumps and Dikes ____ E Short-term Contaminated Dredging Drain Back Waters (if not covered by 401404 permit) ____

2 Discharge information Please provide information about the discharge (attaching additional sheets as necessary) including

a) Describe the discharge activities for which the ownerapplicant is seeking coverage

b) Provide the following information about each discharge

1) Number of discharge points

2) What is the maximum and average flow rate of discharge (in cubic feet per second ft3s) Max flow____________ Is maximum flow a design value Y___ N____ Average flow (include units) __________ Is average flow a design value or estimate _________

3) Latitude and longitude of each discharge within 100 feet pt1 lat_____________ long_____________ pt2 lat_____________ long_____________ pt3 lat_____________ long_____________ pt4 lat_____________ long_____________ pt5 lat_____________ long_____________ pt6 lat_____________ long_____________ pt7 lat_____________ long_____________ pt8 lat_____________ long_____________ etc

4) If hydrostatic testing total volume of the discharge (gals)_________

5) Is the discharge intermittent ____ or seasonal____ Is discharge ongoing Y ____ N______

c) Expected dates of discharge (mmddyy) start_____________ end_________________ d) Please attach a line drawing or flow schematic showing water flow through the facility including 1 sources of intake water 2 contributing flow from the operation 3 treatment units and 4 discharge points and receiving waters(s)

Remediation General Permit Page 12 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

3 Contaminant information a) Based on the sub-category selected (see Appendix III) indicate whether each listed chemical is believed present or believed absent in the potential discharge Attach additional sheets as needed

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

1 Total Suspended Solids (TSS) 2 Total Residual Chlorine (TRC) 3 Total Petroleum Hydrocarbons (TPH) 4 Cyanide (CN) 57125 5 Benzene (B) 71432 6 Toluene (T) 108883 7 Ethylbenzene (E) 100414 8 (mpo) Xylenes (X) 108883

106423 95476

1330207

9 Total BTEX 2 na 10 Ethylene Dibromide (EDB) (12- Dibromoethane) 3

106934

11 Methyl-tert-Butyl Ether (MtBE)

1634044

12 tert-Butyl Alcohol (TBA) (Tertiary-Butanol)

75650

Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI 2 BTEX = Sum of Benzene Toluene Ethylbenzene total Xylenes 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England

Remediation General Permit Page 13 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
            1. Page11[0]
              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
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                  5. TextField38[0] estimate
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                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                                  91. TextField89[40] 024
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                                  94. TextField89[43] GRAB
                                  95. TextField89[44] 8270D
                                  96. TextField89[45] 01
                                  97. TextField89[46] 034
                                  98. TextField89[47] 0002
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                                  123. TextField89[72] 027
                                  124. TextField89[73] 00014
                                  125. TextField89[74] 2
                                  126. TextField89[75] GRAB
                                  127. TextField89[76] 8270D
                                  128. TextField89[77] 01
                                  129. TextField89[78] 030
                                  130. TextField89[79] 0002
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
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Page 14: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

LAGOON AREA

CLARIFIER 2

CLARIFIER 1

CLARIFIER 3

UPPER AMMONOOSUC RIVER

MONITORING

CHAMBER

32 PIPE DISCHARGES

APPROX 05 MILES WEST

INTO THE CONNECTICUT

RIVER (OUTFALL 017)

STONECIPHER amp CLARK

ENVIRONMENTAL SOLUTIONS LLC

111 SARANAC STREET STUDIO 8

LITTLETON NEW HAMPSHIRE 03561

6035755154

GROVETON WASTEWATER LAGOONS

GROVETON NEW HAMPSHIRE

FLOW SCHEMATIC

Attachment A

NPDES Permit No MAG910000 NPDES Permit No NHG910000

B Suggested Form for Notice of Intent (NOI) for the Remediation General Permit

1 General facilitysite information Please provide the following information about the site

a) Name of facilitysite Facilitysite mailing address

Location of facilitysite

longitude_______________ latitude_______________

Facility SIC code(s)

Street

b) Name of facilitysite owner Town

Email address of facilitysite owner State Zip County

Telephone no of facilitysite owner

Fax no of facilitysite owner Owner is (check one) 1 Federal____ 2 StateTribal____ 3 Private____ 4 Other ____ if so describe

Address of owner (if different from site)

Street

Town State Zip County

c) Legal name of operator Operator telephone no

Operator fax no Operator email

Operator contact name and title

Address of operator (if different from owner)

Street

Town State Zip County

Remediation General Permit Page 10 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

d) Check Y for Ayes or N for Ano for the following 1 Has a prior NPDES permit exclusion been granted for the discharge Y___ N___ if Y number_________________ 2 Has a prior NPDES application (Form 1 amp 2C) ever been filed for the discharge Y___ N___ if Y date and tracking __________________________________________________________________ 3 Is the discharge a ldquonew dischargerdquo as defined by 40 CFR 1222 Y___ N___ 4 For sites in Massachusetts is the discharge covered under the Massachusetts Contingency Plan (MCP) and exempt from state permitting Y___ N___

e) Is sitefacility subject to any State permitting license f) Is the sitefacility covered by any other EPA permit including or other action which is causing the generation of 1 Multi-Sector General Permit Y___ N___ discharge Y___ N___ if Y number_______________ If Y please list 2 Final Dewatering General Permit Y___ N___ 1 site identification assigned by the state of NH or if Y number________________ MA_________________________________________ 3 EPA Construction General Permit Y___ N___ 2 permit or license assigned____________________ if Y number _______________ 3 state agency contact information name location and 4 Individual NPDES permit Y___ N___ telephone number if Y number_____________

5 any other water quality related individual or general permit Y___ N___ if Y number______________

g) Is the sitefacility located within or does it discharge to an Area of Critical Environmental Concern (ACEC) Y____ N____

h) Based on the facilitysite information and any historical sampling data identify the sub-category into which the potential discharge falls Activity Category Activity Sub-Category I - Petroleum Related Site Remediation A Gasoline Only Sites ____

B Fuel Oils and Other Oil Sites (including Residential Non-Business Remediation Discharges) ____ C Petroleum Sites with Additional Contamination ____

II - Non Petroleum Site Remediation A Volatile Organic Compound (VOC) Only Sites _____ B VOC Sites with Additional Contamination ____ C Primarily Heavy Metal Sites ____

III - Contaminated Construction Dewatering A General Urban Fill Sites ____ B Known Contaminated Sites ____

Remediation General Permit Page 11 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

IV - Miscellaneous Related Discharges A Aquifer Pump Testing to Evaluate Formerly Contaminated Sites ____ B Well DevelopmentRehabilitation at ContaminatedFormerly Contaminated Sites ____ C Hydrostatic Testing of Pipelines and Tanks ____ D Long-Term Remediation of Contaminated Sumps and Dikes ____ E Short-term Contaminated Dredging Drain Back Waters (if not covered by 401404 permit) ____

2 Discharge information Please provide information about the discharge (attaching additional sheets as necessary) including

a) Describe the discharge activities for which the ownerapplicant is seeking coverage

b) Provide the following information about each discharge

1) Number of discharge points

2) What is the maximum and average flow rate of discharge (in cubic feet per second ft3s) Max flow____________ Is maximum flow a design value Y___ N____ Average flow (include units) __________ Is average flow a design value or estimate _________

3) Latitude and longitude of each discharge within 100 feet pt1 lat_____________ long_____________ pt2 lat_____________ long_____________ pt3 lat_____________ long_____________ pt4 lat_____________ long_____________ pt5 lat_____________ long_____________ pt6 lat_____________ long_____________ pt7 lat_____________ long_____________ pt8 lat_____________ long_____________ etc

4) If hydrostatic testing total volume of the discharge (gals)_________

5) Is the discharge intermittent ____ or seasonal____ Is discharge ongoing Y ____ N______

c) Expected dates of discharge (mmddyy) start_____________ end_________________ d) Please attach a line drawing or flow schematic showing water flow through the facility including 1 sources of intake water 2 contributing flow from the operation 3 treatment units and 4 discharge points and receiving waters(s)

Remediation General Permit Page 12 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

3 Contaminant information a) Based on the sub-category selected (see Appendix III) indicate whether each listed chemical is believed present or believed absent in the potential discharge Attach additional sheets as needed

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

1 Total Suspended Solids (TSS) 2 Total Residual Chlorine (TRC) 3 Total Petroleum Hydrocarbons (TPH) 4 Cyanide (CN) 57125 5 Benzene (B) 71432 6 Toluene (T) 108883 7 Ethylbenzene (E) 100414 8 (mpo) Xylenes (X) 108883

106423 95476

1330207

9 Total BTEX 2 na 10 Ethylene Dibromide (EDB) (12- Dibromoethane) 3

106934

11 Methyl-tert-Butyl Ether (MtBE)

1634044

12 tert-Butyl Alcohol (TBA) (Tertiary-Butanol)

75650

Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI 2 BTEX = Sum of Benzene Toluene Ethylbenzene total Xylenes 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England

Remediation General Permit Page 13 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
                  3. TextField36[0] 29
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                  5. TextField38[0] estimate
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                  8. DateTimeField1[0] 312015
                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
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Page 15: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Attachment A

NPDES Permit No MAG910000 NPDES Permit No NHG910000

B Suggested Form for Notice of Intent (NOI) for the Remediation General Permit

1 General facilitysite information Please provide the following information about the site

a) Name of facilitysite Facilitysite mailing address

Location of facilitysite

longitude_______________ latitude_______________

Facility SIC code(s)

Street

b) Name of facilitysite owner Town

Email address of facilitysite owner State Zip County

Telephone no of facilitysite owner

Fax no of facilitysite owner Owner is (check one) 1 Federal____ 2 StateTribal____ 3 Private____ 4 Other ____ if so describe

Address of owner (if different from site)

Street

Town State Zip County

c) Legal name of operator Operator telephone no

Operator fax no Operator email

Operator contact name and title

Address of operator (if different from owner)

Street

Town State Zip County

Remediation General Permit Page 10 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

d) Check Y for Ayes or N for Ano for the following 1 Has a prior NPDES permit exclusion been granted for the discharge Y___ N___ if Y number_________________ 2 Has a prior NPDES application (Form 1 amp 2C) ever been filed for the discharge Y___ N___ if Y date and tracking __________________________________________________________________ 3 Is the discharge a ldquonew dischargerdquo as defined by 40 CFR 1222 Y___ N___ 4 For sites in Massachusetts is the discharge covered under the Massachusetts Contingency Plan (MCP) and exempt from state permitting Y___ N___

e) Is sitefacility subject to any State permitting license f) Is the sitefacility covered by any other EPA permit including or other action which is causing the generation of 1 Multi-Sector General Permit Y___ N___ discharge Y___ N___ if Y number_______________ If Y please list 2 Final Dewatering General Permit Y___ N___ 1 site identification assigned by the state of NH or if Y number________________ MA_________________________________________ 3 EPA Construction General Permit Y___ N___ 2 permit or license assigned____________________ if Y number _______________ 3 state agency contact information name location and 4 Individual NPDES permit Y___ N___ telephone number if Y number_____________

5 any other water quality related individual or general permit Y___ N___ if Y number______________

g) Is the sitefacility located within or does it discharge to an Area of Critical Environmental Concern (ACEC) Y____ N____

h) Based on the facilitysite information and any historical sampling data identify the sub-category into which the potential discharge falls Activity Category Activity Sub-Category I - Petroleum Related Site Remediation A Gasoline Only Sites ____

B Fuel Oils and Other Oil Sites (including Residential Non-Business Remediation Discharges) ____ C Petroleum Sites with Additional Contamination ____

II - Non Petroleum Site Remediation A Volatile Organic Compound (VOC) Only Sites _____ B VOC Sites with Additional Contamination ____ C Primarily Heavy Metal Sites ____

III - Contaminated Construction Dewatering A General Urban Fill Sites ____ B Known Contaminated Sites ____

Remediation General Permit Page 11 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

IV - Miscellaneous Related Discharges A Aquifer Pump Testing to Evaluate Formerly Contaminated Sites ____ B Well DevelopmentRehabilitation at ContaminatedFormerly Contaminated Sites ____ C Hydrostatic Testing of Pipelines and Tanks ____ D Long-Term Remediation of Contaminated Sumps and Dikes ____ E Short-term Contaminated Dredging Drain Back Waters (if not covered by 401404 permit) ____

2 Discharge information Please provide information about the discharge (attaching additional sheets as necessary) including

a) Describe the discharge activities for which the ownerapplicant is seeking coverage

b) Provide the following information about each discharge

1) Number of discharge points

2) What is the maximum and average flow rate of discharge (in cubic feet per second ft3s) Max flow____________ Is maximum flow a design value Y___ N____ Average flow (include units) __________ Is average flow a design value or estimate _________

3) Latitude and longitude of each discharge within 100 feet pt1 lat_____________ long_____________ pt2 lat_____________ long_____________ pt3 lat_____________ long_____________ pt4 lat_____________ long_____________ pt5 lat_____________ long_____________ pt6 lat_____________ long_____________ pt7 lat_____________ long_____________ pt8 lat_____________ long_____________ etc

4) If hydrostatic testing total volume of the discharge (gals)_________

5) Is the discharge intermittent ____ or seasonal____ Is discharge ongoing Y ____ N______

c) Expected dates of discharge (mmddyy) start_____________ end_________________ d) Please attach a line drawing or flow schematic showing water flow through the facility including 1 sources of intake water 2 contributing flow from the operation 3 treatment units and 4 discharge points and receiving waters(s)

Remediation General Permit Page 12 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

3 Contaminant information a) Based on the sub-category selected (see Appendix III) indicate whether each listed chemical is believed present or believed absent in the potential discharge Attach additional sheets as needed

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

1 Total Suspended Solids (TSS) 2 Total Residual Chlorine (TRC) 3 Total Petroleum Hydrocarbons (TPH) 4 Cyanide (CN) 57125 5 Benzene (B) 71432 6 Toluene (T) 108883 7 Ethylbenzene (E) 100414 8 (mpo) Xylenes (X) 108883

106423 95476

1330207

9 Total BTEX 2 na 10 Ethylene Dibromide (EDB) (12- Dibromoethane) 3

106934

11 Methyl-tert-Butyl Ether (MtBE)

1634044

12 tert-Butyl Alcohol (TBA) (Tertiary-Butanol)

75650

Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI 2 BTEX = Sum of Benzene Toluene Ethylbenzene total Xylenes 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England

Remediation General Permit Page 13 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
            1. Page11[0]
              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
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                  5. TextField38[0] estimate
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
                                          11. TextField59[0] Class B
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Page 16: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

NPDES Permit No MAG910000 NPDES Permit No NHG910000

B Suggested Form for Notice of Intent (NOI) for the Remediation General Permit

1 General facilitysite information Please provide the following information about the site

a) Name of facilitysite Facilitysite mailing address

Location of facilitysite

longitude_______________ latitude_______________

Facility SIC code(s)

Street

b) Name of facilitysite owner Town

Email address of facilitysite owner State Zip County

Telephone no of facilitysite owner

Fax no of facilitysite owner Owner is (check one) 1 Federal____ 2 StateTribal____ 3 Private____ 4 Other ____ if so describe

Address of owner (if different from site)

Street

Town State Zip County

c) Legal name of operator Operator telephone no

Operator fax no Operator email

Operator contact name and title

Address of operator (if different from owner)

Street

Town State Zip County

Remediation General Permit Page 10 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

d) Check Y for Ayes or N for Ano for the following 1 Has a prior NPDES permit exclusion been granted for the discharge Y___ N___ if Y number_________________ 2 Has a prior NPDES application (Form 1 amp 2C) ever been filed for the discharge Y___ N___ if Y date and tracking __________________________________________________________________ 3 Is the discharge a ldquonew dischargerdquo as defined by 40 CFR 1222 Y___ N___ 4 For sites in Massachusetts is the discharge covered under the Massachusetts Contingency Plan (MCP) and exempt from state permitting Y___ N___

e) Is sitefacility subject to any State permitting license f) Is the sitefacility covered by any other EPA permit including or other action which is causing the generation of 1 Multi-Sector General Permit Y___ N___ discharge Y___ N___ if Y number_______________ If Y please list 2 Final Dewatering General Permit Y___ N___ 1 site identification assigned by the state of NH or if Y number________________ MA_________________________________________ 3 EPA Construction General Permit Y___ N___ 2 permit or license assigned____________________ if Y number _______________ 3 state agency contact information name location and 4 Individual NPDES permit Y___ N___ telephone number if Y number_____________

5 any other water quality related individual or general permit Y___ N___ if Y number______________

g) Is the sitefacility located within or does it discharge to an Area of Critical Environmental Concern (ACEC) Y____ N____

h) Based on the facilitysite information and any historical sampling data identify the sub-category into which the potential discharge falls Activity Category Activity Sub-Category I - Petroleum Related Site Remediation A Gasoline Only Sites ____

B Fuel Oils and Other Oil Sites (including Residential Non-Business Remediation Discharges) ____ C Petroleum Sites with Additional Contamination ____

II - Non Petroleum Site Remediation A Volatile Organic Compound (VOC) Only Sites _____ B VOC Sites with Additional Contamination ____ C Primarily Heavy Metal Sites ____

III - Contaminated Construction Dewatering A General Urban Fill Sites ____ B Known Contaminated Sites ____

Remediation General Permit Page 11 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

IV - Miscellaneous Related Discharges A Aquifer Pump Testing to Evaluate Formerly Contaminated Sites ____ B Well DevelopmentRehabilitation at ContaminatedFormerly Contaminated Sites ____ C Hydrostatic Testing of Pipelines and Tanks ____ D Long-Term Remediation of Contaminated Sumps and Dikes ____ E Short-term Contaminated Dredging Drain Back Waters (if not covered by 401404 permit) ____

2 Discharge information Please provide information about the discharge (attaching additional sheets as necessary) including

a) Describe the discharge activities for which the ownerapplicant is seeking coverage

b) Provide the following information about each discharge

1) Number of discharge points

2) What is the maximum and average flow rate of discharge (in cubic feet per second ft3s) Max flow____________ Is maximum flow a design value Y___ N____ Average flow (include units) __________ Is average flow a design value or estimate _________

3) Latitude and longitude of each discharge within 100 feet pt1 lat_____________ long_____________ pt2 lat_____________ long_____________ pt3 lat_____________ long_____________ pt4 lat_____________ long_____________ pt5 lat_____________ long_____________ pt6 lat_____________ long_____________ pt7 lat_____________ long_____________ pt8 lat_____________ long_____________ etc

4) If hydrostatic testing total volume of the discharge (gals)_________

5) Is the discharge intermittent ____ or seasonal____ Is discharge ongoing Y ____ N______

c) Expected dates of discharge (mmddyy) start_____________ end_________________ d) Please attach a line drawing or flow schematic showing water flow through the facility including 1 sources of intake water 2 contributing flow from the operation 3 treatment units and 4 discharge points and receiving waters(s)

Remediation General Permit Page 12 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

3 Contaminant information a) Based on the sub-category selected (see Appendix III) indicate whether each listed chemical is believed present or believed absent in the potential discharge Attach additional sheets as needed

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

1 Total Suspended Solids (TSS) 2 Total Residual Chlorine (TRC) 3 Total Petroleum Hydrocarbons (TPH) 4 Cyanide (CN) 57125 5 Benzene (B) 71432 6 Toluene (T) 108883 7 Ethylbenzene (E) 100414 8 (mpo) Xylenes (X) 108883

106423 95476

1330207

9 Total BTEX 2 na 10 Ethylene Dibromide (EDB) (12- Dibromoethane) 3

106934

11 Methyl-tert-Butyl Ether (MtBE)

1634044

12 tert-Butyl Alcohol (TBA) (Tertiary-Butanol)

75650

Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI 2 BTEX = Sum of Benzene Toluene Ethylbenzene total Xylenes 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England

Remediation General Permit Page 13 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
      1. topmostSubform[0]
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
                  3. TextField36[0] 29
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                  5. TextField38[0] estimate
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                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                      26. TextField89[1] GRAB
                      27. TextField89[2] 2540D-97
                      28. TextField89[3] 5 mgl
                      29. TextField89[4] 45000
                      30. TextField89[5] 245
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Page 17: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

NPDES Permit No MAG910000 NPDES Permit No NHG910000

d) Check Y for Ayes or N for Ano for the following 1 Has a prior NPDES permit exclusion been granted for the discharge Y___ N___ if Y number_________________ 2 Has a prior NPDES application (Form 1 amp 2C) ever been filed for the discharge Y___ N___ if Y date and tracking __________________________________________________________________ 3 Is the discharge a ldquonew dischargerdquo as defined by 40 CFR 1222 Y___ N___ 4 For sites in Massachusetts is the discharge covered under the Massachusetts Contingency Plan (MCP) and exempt from state permitting Y___ N___

e) Is sitefacility subject to any State permitting license f) Is the sitefacility covered by any other EPA permit including or other action which is causing the generation of 1 Multi-Sector General Permit Y___ N___ discharge Y___ N___ if Y number_______________ If Y please list 2 Final Dewatering General Permit Y___ N___ 1 site identification assigned by the state of NH or if Y number________________ MA_________________________________________ 3 EPA Construction General Permit Y___ N___ 2 permit or license assigned____________________ if Y number _______________ 3 state agency contact information name location and 4 Individual NPDES permit Y___ N___ telephone number if Y number_____________

5 any other water quality related individual or general permit Y___ N___ if Y number______________

g) Is the sitefacility located within or does it discharge to an Area of Critical Environmental Concern (ACEC) Y____ N____

h) Based on the facilitysite information and any historical sampling data identify the sub-category into which the potential discharge falls Activity Category Activity Sub-Category I - Petroleum Related Site Remediation A Gasoline Only Sites ____

B Fuel Oils and Other Oil Sites (including Residential Non-Business Remediation Discharges) ____ C Petroleum Sites with Additional Contamination ____

II - Non Petroleum Site Remediation A Volatile Organic Compound (VOC) Only Sites _____ B VOC Sites with Additional Contamination ____ C Primarily Heavy Metal Sites ____

III - Contaminated Construction Dewatering A General Urban Fill Sites ____ B Known Contaminated Sites ____

Remediation General Permit Page 11 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

IV - Miscellaneous Related Discharges A Aquifer Pump Testing to Evaluate Formerly Contaminated Sites ____ B Well DevelopmentRehabilitation at ContaminatedFormerly Contaminated Sites ____ C Hydrostatic Testing of Pipelines and Tanks ____ D Long-Term Remediation of Contaminated Sumps and Dikes ____ E Short-term Contaminated Dredging Drain Back Waters (if not covered by 401404 permit) ____

2 Discharge information Please provide information about the discharge (attaching additional sheets as necessary) including

a) Describe the discharge activities for which the ownerapplicant is seeking coverage

b) Provide the following information about each discharge

1) Number of discharge points

2) What is the maximum and average flow rate of discharge (in cubic feet per second ft3s) Max flow____________ Is maximum flow a design value Y___ N____ Average flow (include units) __________ Is average flow a design value or estimate _________

3) Latitude and longitude of each discharge within 100 feet pt1 lat_____________ long_____________ pt2 lat_____________ long_____________ pt3 lat_____________ long_____________ pt4 lat_____________ long_____________ pt5 lat_____________ long_____________ pt6 lat_____________ long_____________ pt7 lat_____________ long_____________ pt8 lat_____________ long_____________ etc

4) If hydrostatic testing total volume of the discharge (gals)_________

5) Is the discharge intermittent ____ or seasonal____ Is discharge ongoing Y ____ N______

c) Expected dates of discharge (mmddyy) start_____________ end_________________ d) Please attach a line drawing or flow schematic showing water flow through the facility including 1 sources of intake water 2 contributing flow from the operation 3 treatment units and 4 discharge points and receiving waters(s)

Remediation General Permit Page 12 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

3 Contaminant information a) Based on the sub-category selected (see Appendix III) indicate whether each listed chemical is believed present or believed absent in the potential discharge Attach additional sheets as needed

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

1 Total Suspended Solids (TSS) 2 Total Residual Chlorine (TRC) 3 Total Petroleum Hydrocarbons (TPH) 4 Cyanide (CN) 57125 5 Benzene (B) 71432 6 Toluene (T) 108883 7 Ethylbenzene (E) 100414 8 (mpo) Xylenes (X) 108883

106423 95476

1330207

9 Total BTEX 2 na 10 Ethylene Dibromide (EDB) (12- Dibromoethane) 3

106934

11 Methyl-tert-Butyl Ether (MtBE)

1634044

12 tert-Butyl Alcohol (TBA) (Tertiary-Butanol)

75650

Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI 2 BTEX = Sum of Benzene Toluene Ethylbenzene total Xylenes 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England

Remediation General Permit Page 13 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
            1. Page11[0]
              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
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                  4. TextField37[0] 22
                  5. TextField38[0] estimate
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                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
                                          11. TextField59[0] Class B
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Page 18: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

NPDES Permit No MAG910000 NPDES Permit No NHG910000

IV - Miscellaneous Related Discharges A Aquifer Pump Testing to Evaluate Formerly Contaminated Sites ____ B Well DevelopmentRehabilitation at ContaminatedFormerly Contaminated Sites ____ C Hydrostatic Testing of Pipelines and Tanks ____ D Long-Term Remediation of Contaminated Sumps and Dikes ____ E Short-term Contaminated Dredging Drain Back Waters (if not covered by 401404 permit) ____

2 Discharge information Please provide information about the discharge (attaching additional sheets as necessary) including

a) Describe the discharge activities for which the ownerapplicant is seeking coverage

b) Provide the following information about each discharge

1) Number of discharge points

2) What is the maximum and average flow rate of discharge (in cubic feet per second ft3s) Max flow____________ Is maximum flow a design value Y___ N____ Average flow (include units) __________ Is average flow a design value or estimate _________

3) Latitude and longitude of each discharge within 100 feet pt1 lat_____________ long_____________ pt2 lat_____________ long_____________ pt3 lat_____________ long_____________ pt4 lat_____________ long_____________ pt5 lat_____________ long_____________ pt6 lat_____________ long_____________ pt7 lat_____________ long_____________ pt8 lat_____________ long_____________ etc

4) If hydrostatic testing total volume of the discharge (gals)_________

5) Is the discharge intermittent ____ or seasonal____ Is discharge ongoing Y ____ N______

c) Expected dates of discharge (mmddyy) start_____________ end_________________ d) Please attach a line drawing or flow schematic showing water flow through the facility including 1 sources of intake water 2 contributing flow from the operation 3 treatment units and 4 discharge points and receiving waters(s)

Remediation General Permit Page 12 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

3 Contaminant information a) Based on the sub-category selected (see Appendix III) indicate whether each listed chemical is believed present or believed absent in the potential discharge Attach additional sheets as needed

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

1 Total Suspended Solids (TSS) 2 Total Residual Chlorine (TRC) 3 Total Petroleum Hydrocarbons (TPH) 4 Cyanide (CN) 57125 5 Benzene (B) 71432 6 Toluene (T) 108883 7 Ethylbenzene (E) 100414 8 (mpo) Xylenes (X) 108883

106423 95476

1330207

9 Total BTEX 2 na 10 Ethylene Dibromide (EDB) (12- Dibromoethane) 3

106934

11 Methyl-tert-Butyl Ether (MtBE)

1634044

12 tert-Butyl Alcohol (TBA) (Tertiary-Butanol)

75650

Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI 2 BTEX = Sum of Benzene Toluene Ethylbenzene total Xylenes 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England

Remediation General Permit Page 13 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
                  3. TextField36[0] 29
                  4. TextField37[0] 22
                  5. TextField38[0] estimate
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                  8. DateTimeField1[0] 312015
                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                      26. TextField89[1] GRAB
                      27. TextField89[2] 2540D-97
                      28. TextField89[3] 5 mgl
                      29. TextField89[4] 45000
                      30. TextField89[5] 245
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
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Page 19: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

NPDES Permit No MAG910000 NPDES Permit No NHG910000

3 Contaminant information a) Based on the sub-category selected (see Appendix III) indicate whether each listed chemical is believed present or believed absent in the potential discharge Attach additional sheets as needed

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

1 Total Suspended Solids (TSS) 2 Total Residual Chlorine (TRC) 3 Total Petroleum Hydrocarbons (TPH) 4 Cyanide (CN) 57125 5 Benzene (B) 71432 6 Toluene (T) 108883 7 Ethylbenzene (E) 100414 8 (mpo) Xylenes (X) 108883

106423 95476

1330207

9 Total BTEX 2 na 10 Ethylene Dibromide (EDB) (12- Dibromoethane) 3

106934

11 Methyl-tert-Butyl Ether (MtBE)

1634044

12 tert-Butyl Alcohol (TBA) (Tertiary-Butanol)

75650

Numbering system is provided to allow cross-referencing to Effluent Limits and Monitoring Requirements by Sub-Category included in Appendix III as well as the Test Methods and Minimum Levels associated with each parameter provided in Appendix VI 2 BTEX = Sum of Benzene Toluene Ethylbenzene total Xylenes 3 EDB is a groundwater contaminant at fuel spill and pesticide application sites in New England

Remediation General Permit Page 13 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
            1. Page11[0]
              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
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                  5. TextField38[0] estimate
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                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                                      1. RadioButtonList[0] 2
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                                      4. TextField50[0]
                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
                                          11. TextField59[0] Class B
                                          12. TextField60[0] 216
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Page 20: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

13 tert-Amyl Methyl Ether (TAME)

9940508

14 Naphthalene 91203 15 Carbon Tetrachloride 56235

16 12 Dichlorobenzene (o-DCB)

95501

17 13 Dichlorobenzene (m-DCB)

541731

18 14 Dichlorobenzene (p-DCB)

106467

18a Total dichlorobenzene 19 11 Dichloroethane (DCA)

75343

20 12 Dichloroethane (DCA)

107062

21 11 Dichloroethene (DCE)

75354

22 cis-12 Dichloroethene (DCE)

156592

23 Methylene Chloride 75092 24 Tetrachloroethene (PCE)

127184

25 111 Trichloro-ethane (TCA)

71556

26 112 Trichloro-ethane (TCA)

79005

27 Trichloroethene (TCE)

79016

Remediation General Permit Page 14 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
            1. Page11[0]
              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
              3. RadioButtonList[0] 2
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
                  3. TextField36[0] 29
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                  5. TextField38[0] estimate
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                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
                                          11. TextField59[0] Class B
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Page 21: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

28 Vinyl Chloride (Chloroethene)

75014

29 Acetone 67641 30 14 Dioxane 123911 31 Total Phenols 108952 32 Pentachlorophenol (PCP)

87865

33 Total Phthalates (Phthalate esters) 4

34 Bis (2-Ethylhexyl) Phthalate [Di-(ethylhexyl) Phthalate]

117817

35 Total Group I Polycyclic Aromatic Hydrocarbons (PAH) a Benzo(a) Anthracene 56553 b Benzo(a) Pyrene 50328 c Benzo(b)Fluoranthene 205992

d Benzo(k)Fluoranthene 207089

e Chrysene 21801 f Dibenzo(ah)anthracene 53703

g Indeno(123-cd) Pyrene

193395

36 Total Group II Polycyclic Aromatic Hydrocarbons (PAH)

4 The sum of individual phthalate compounds

Remediation General Permit Page 15 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
      1. topmostSubform[0]
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
          13. RadioButtonList[0] 3
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          19. TextField18[0]
          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              10. TextField41[0]
              11. TextField42[0] Permit expired in 2011
              12. TextField43[0]
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
                  3. TextField36[0] 29
                  4. TextField37[0] 22
                  5. TextField38[0] estimate
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                  8. DateTimeField1[0] 312015
                  9. DateTimeField2[0] 1212015
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                  11. TextField44[0] NA
                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                      26. TextField89[1] GRAB
                      27. TextField89[2] 2540D-97
                      28. TextField89[3] 5 mgl
                      29. TextField89[4] 45000
                      30. TextField89[5] 245
                      31. TextField89[6] 19000
                      32. TextField89[7] 103
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Page 22: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

h Acenaphthene 83329 i Acenaphthylene 208968 j Anthracene 120127 k Benzo(ghi) Perylene 191242 l Fluoranthene 206440 m Fluorene 86737 n Naphthalene 91203 o Phenanthrene 85018 p Pyrene 129000

37 Total Polychlorinated Biphenyls (PCBs)

85687 84742 117840 84662 131113 117817

38 Chloride 16887006 39 Antimony 7440360 40 Arsenic 7440382 41 Cadmium 7440439 42 Chromium III (trivalent) 16065831 43 Chromium VI (hexavalent) 18540299 44 Copper 7440508 45 Lead 7439921 46 Mercury 7439976 47 Nickel 7440020 48 Selenium 7782492 49 Silver 7440224 50 Zinc 7440666 51 Iron 7439896 Other (describe)

Remediation General Permit Page 16 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
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                  13. TextField46[0] 71 deg 31 20 W
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
                                          11. TextField59[0] Class B
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Page 23: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

NPDES Permit No MAG910000 NPDES Permit No NHG910000

Parameter CAS Number

Believed Absent

Believed Present

of Samples

Sample Type (eg grab)

Analytical Method

Used (method )

Minimum Level

(ML) of Test

Method

Maximum daily value Average daily value

concentration (ugl)

mass (kg)

concentration (ugl)

mass (kg)

b) For discharges where metals are believed present please fill out the following (attach results of any calculations)

Step 1 Do any of the metals in the influent exceed the effluent limits in Appendix III (ie the limits set at zero dilution) Y____ N____

If yes which metals

Step 2 For any metals which exceed the Appendix III limits calculate the dilution factor (DF) using the formula in Part IA3c (step 2) of the NOI instructions or as determined by the State prior to the submission of this NOI What is the dilution factor for applicable metals Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Metal_____________________DF______ Etc

Look up the limit calculated at the corresponding dilution factor in Appendix IV Do any of the metals in the influent have the potential to exceed the corresponding effluent limits in Appendix IV (ie is the influent concentration above the limit set at the calculated dilution factor) Y____ N____ If Y list which metals

4 Treatment system information Please describe the treatment system using separate sheets as necessary including

a) A description of the treatment system including a schematic of the proposed or existing treatment system

b) Identify each applicable treatment unit (check all that apply)

Frac tank Air stripper Oilwater separator Equalization tanks Bag filter GAC filter

Chlorination De-chlorination

Other (please describe)

Remediation General Permit Page 17 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
            1. Page11[0]
              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
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                  5. TextField38[0] estimate
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                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                                      4. TextField50[0]
                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
                                          11. TextField59[0] Class B
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Page 24: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

NPDES Permit No MAG910000 NPDES Permit No NHG910000

c) Proposed average and maximum flow rates (gallons per minute) for the discharge and the design flow rate(s) (gallons per minute) of the treatment system Average flow rate of discharge__________ gpm Maximum flow rate of treatment system ___________ gpm Design flow rate of treatment system ___________ gpm

d) A description of chemical additives being used or planned to be used (attach MSDS sheets)

5 Receiving surface water(s) Please provide information about the receiving water(s) using separate sheets as necessary

a) Identify the discharge pathway Direct to receiving water_____

Within facility (sewer) ____

Storm drain____

Wetlands ____ Other (describe) __________________________

b) Provide a narrative description of the discharge pathway including the name(s) of the receiving waters

c) Attach a detailed map(s) indicating the site location and location of the outfall to the receiving water 1 For multiple discharges number the discharges sequentially 2 For indirect dischargers indicate the location of the discharge to the indirect conveyance and the discharge to surface water The map should also include the location and distance to the nearest sanitary sewer as well as the locus of nearby sensitive receptors (based on USGS topographical mapping) such as surface waters drinking water supplies and wetland areas

d) Provide the state water quality classification of the receiving water_______

e) Provide the reported or calculated seven day-ten year low flow (7Q10) of the receiving water _________________________cfs Please attach any calculation sheets used to support stream flow and dilution calculations

f) Is the receiving water a listed 303(d) water quality impaired or limited water Y____ N____ If yes for which pollutant(s) ______________________________________________________________________________________________________________ Is there a final TMDL Y____ N____ If yes for which pollutant(s) ______________________________________________________

pH and E Coli

Remediation General Permit Page 18 of 22 Appendix V - NOI

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
          13. RadioButtonList[0] 3
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
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                  5. TextField38[0] estimate
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                  8. DateTimeField1[0] 312015
                  9. DateTimeField2[0] 1212015
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                  11. TextField44[0] NA
                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                      26. TextField89[1] GRAB
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                                      3. RadioButtonList[1] Off
                                      4. TextField50[0]
                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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Page 25: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

NPDES Permit No MAG910000 NPDES Permit No NHG910000

6 ESA and NHPA Eligibility Please provide the following information according to requirements of Permit Parts IA4 and IA5 Appendices II and VII

a) Using the instructions in Appendix VII and information on Appendix II under which criterion listed in Part IC are you eligible for coverage under this general permit A ____ B ____ C ____ D ____ E ____ F ____ b) If you selected Criterion D or F has consultation with the federal services been completed Y____ N____ Underway____

c) If consultation with US Fish and Wildlife Service andor NOAA Fisheries Service was completed was a written concurrence finding that the discharge is ldquonot likely to adversely affectrdquo listed species or critical habitat received Y____ N____

d) Attach documentation of ESA eligibility as described in the NOI instructions and required by Appendix VII Part IC Step 4

e) Using the instructions in Appendix VII under which criterion listed in Part IIC are you eligible for coverage under this general permit 1 ____ 2 ____ 3 ____ f) If Criterion 3 was selected attach all written correspondence with the State or Tribal historic preservation officers including any terms and conditions that outline measures the applicant must follow to mitigate or prevent adverse effects due to activities regulated by the RGP

7 Supplemental information

Please provide any supplemental information Attach any analytical data used to support the application Attach any certification(s) required by the general permit

Remediation General Permit Page 19 of 22 Appendix V - NOI

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
            1. Page11[0]
              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
              3. RadioButtonList[0] 2
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
                  3. TextField36[0] 29
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                  5. TextField38[0] estimate
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                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
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Page 26: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Groveton Wastewater Lagoons

Robert Chapman Owner

January 31 2015

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
            1. Page11[0]
              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
                  3. TextField36[0] 29
                  4. TextField37[0] 22
                  5. TextField38[0] estimate
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                  8. DateTimeField1[0] 312015
                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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Page 27: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Attachment B ndash Decommissioning Plan

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
                  3. TextField36[0] 29
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                  5. TextField38[0] estimate
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                  8. DateTimeField1[0] 312015
                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
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Page 28: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

34 SCHOOL STREET bullbullbullbull LITTLETON NH 03561 bullbullbullbull PHONE 603-444-4111 bullbullbullbull FAX 603-444-1343 bullbullbullbull wwwhorizonsengineeringcom

Project No 13087

November 26 2013

Mr Jeffery G Andrews PE

Wastewater Engineering Bureau

New Hampshire Department of Environmental Services

29 Hazen Drive PO Box 95

Concord NH 03302-0095

Subject Wastewater Facility Decommissioning Groveton Mill Groveton New Hampshire

Dear Mr Andrews

At the request of Green Steel (ldquoClientrdquo) Horizons Engineering Inc (ldquoHorizonsrdquo) has completed a

proposed sampling plan to characterize the wastewater lagoon polishing ponds and clarifiers

The treatment facility in question is located in Groveton NH (ldquoSiterdquo)

Horizons representative Michael Czok was onsite on October 22nd

to obtain water samples from

the four (4) quadrants of the main lagoon two (2) polishing ponds and three (3) clarifiers

Samples from the clarifier and polishing lagoons were obtained from catwalks which extended

into the sampling area The four (4) quadrants of the lagoons were sampled via boat Two

sampling depths were collected per sampling location These depths consisted of a grab sample

from mid-depth between the supernatant interface and the surface The second consisted of a

grab sample from the supernatant interface A sludge sample was also obtained from each

sampling area for analysis Total depth of water was recorded as well as sludge depth for each

sampling area These are summarized in attached Table 1

Grab samples of water and sludge were obtained and placed on ice and transported to Eastern

Analytical Inc under proper chain of custody documentation Water samples were analyzed for

total phosphorus pH e Coli polycyclic aromatic hydrocarbons (PAHs) total nitrogen nitrate

nitrite total kjeldahl nitrogen (TKN) aluminum biochemical oxygen demand (BOD) total

suspended solids (TSS) and turbidity Sludge samples were analyzed for total metals and

volatile organic compounds (VOCs) Laboratory Analytical results are attached in accordance

with the EPA preapproved sampling plan

Results

Analytical results returned indicated that detected concentrations in the wastewater for the

parameters outlined in the NPDES permit NH0001562 were within the permit standards for

17 Sunset Terrace 34 School Street 35 Railroad Row Suite 204

Newport VT 05855 Littleton NH 03561 White River Junction VT 05001 Ph 802-334-6434 Ph 603-444-4111 Ph 802-296-8300 Fax 802-334-5602 Fax 603-444-1343 Fax 802-296-8301

wwwhorizonsengineeringcom

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
                  3. TextField36[0] 29
                  4. TextField37[0] 22
                  5. TextField38[0] estimate
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                  8. DateTimeField1[0] 312015
                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                      26. TextField89[1] GRAB
                      27. TextField89[2] 2540D-97
                      28. TextField89[3] 5 mgl
                      29. TextField89[4] 45000
                      30. TextField89[5] 245
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Page 29: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

November 26 2013

Page 2 of 5

samples obtained from mid-depth between the supernatant interface and the water surface except in

clarifier 1

Samples obtained from the supernatant interface had detected concentrations of aluminum above the

Secondary Maximum Contaminant Level standard (SMCLs) of 02 mgl Samples ranged in detected

concentration of 008 to 40 mgl Detected concentrations of multiple PAHs were found in the

supernatant interface samples The detected concentrations for each PAH violation are summarized in

the Sample Results Tables attached

Sludge samples taken from each of the nine (9) sampling areas had detected concentrations of metals

below the NHDES soil quality standards No VOCs were detected in any of the samples obtained from

the Site

Results are listed below and correspond to the two depths where water samples were obtained f They

are listed from mid-depth to the interface respectively

Polishing Pond 1 (Polish 1-1 - mid-depth and Polish 1-2 - interface)

bull Total Phosphorous - 032 and 37 mgl

bull pH - 66 and 65 SU

bull E Coli - 703 and 1145 MPN100ml

bull PAHs - Detected in Polish 1-2 see attached Sample Results Tables

bull Total Nitrogen - 37 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 37 and 14 mgl

bull Aluminum - 05 and 15 mgl

bull BOD - 11 and 31 mgl

bull TSS - 18 and 240 mgl

bull Turbidity - 12 and 130 NTU

Polishing Pond 2 (Polish 2-1 -mid-depth and Polish 2-2 - interface)

bull Total Phosphorous - 053 and 81 mgl

bull pH - 64 and 64 SU

bull E Coli - 63 and 16 MPN100ml

bull PAHs - Detected in Polish 2-2 see attached Sample Results Tables

bull Total Nitrogen - 56 and 28 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 56 and 28 mgl

bull Aluminum - 008 and 35 mgl

bull BOD - 15 and 22 mgl

bull TSS - 35 and 300 mgl

bull Turbidity - 17 and 150 NTU

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
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                  3. TextField36[0] 29
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                  5. TextField38[0] estimate
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                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                      28. TextField89[3] 5 mgl
                      29. TextField89[4] 45000
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
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Page 30: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

November 26 2013

Page 3 of 5

Quad 1 (Quad 1-1 - mid-depth and Quad 1-2 - inteface)

bull Total Phosphorous - 18 and 53 mgl

bull pH - 73 and 70 SU

bull E Coli - 31 and 31 MPN100ml

bull PAHs - AGQS violations were detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 14 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93and 14 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 12 and lt30 mgl

bull TSS - 15 and 370 mgl

bull Turbidity - 7 and 150 NTU

Quad 2 (Quad 2-1-mid-depth and Quad 2-2-interface)

bull Total Phosphorous - 18 and 49 mgl

bull pH - 72 and 71 SU

bull E Coli - 41 and lt1 MPN100ml

bull PAHs - Detected in Quad 2-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 17 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 17 mgl

bull Aluminum - lt005 and 42 mgl

bull BOD - 17 and 69 mgl

bull TSS - 16 and 480 mgl

bull Turbidity - 7 and 33 NTU

Quad 3 (Quad 3-1-mid-depth and Quad 3-2-interface)

bull Total Phosphorous - 19 and 15 mgl

bull pH - 73 and 70SU

bull E Coli - 20 and 119 MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 95 and 56 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 95 and 56 mgl

bull Aluminum - lt005 and 40 mgl

bull BOD - 13 and 71 mgl

bull TSS - 14 and 1400 mgl

bull Turbidity - 7 and 650 NTU

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
            1. Page11[0]
              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
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                  5. TextField38[0] estimate
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                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
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Page 31: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

November 26 2013

Page 4 of 5

Quad 4 (Quad 4-1-mid-depth and Quad 4-2-interface)

bull Total Phosphorous - 19 and 10 mgl

bull pH - 73 and 71 SU

bull E Coli - 31 and 1MPN100ml

bull PAHs - Detected in Quad 1-2 see attached Sample Results Tables

bull Total Nitrogen - 93 and 35 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 93 and 35 mgl

bull Aluminum - lt005 and 65 mgl

bull BOD - 11 and 24 mgl

bull TSS - 15 and 400 mgl

bull Turbidity - 9 and 110 NTU

Clarifier 1 (Clarifier 1-1-mid-depth and Clarifier 1-2-interface)

bull Total Phosphorous - 91 and 17 mgl

bull pH - 73 and 71 SU

bull E Coli - 906 and 1529 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 60 and 120 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 60 and 120 mgl

bull Aluminum - 27 and 23 mgl

bull BOD - 42 and 100 mgl

bull TSS - 990 and 3300 mgl

bull Turbidity - 670 and 1300 NTU

Clarifier 2 (Clarifier 2-1-mid-depth Clarifier 2-2-interface)

bull Total Phosphorous - 002 and 37 mgl

bull pH - 82 and 72 SU

bull E Coli - lt1 and lt1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - lt05 and 16 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - lt05 and 16 mgl

bull Aluminum - lt005 and 86 mgl

bull BOD - lt6 and 40 mgl

bull TSS - lt5 and 990 mgl

bull Turbidity - 1 and 340 NTU

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
            1. Page11[0]
              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
              3. RadioButtonList[0] 2
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
                  3. TextField36[0] 29
                  4. TextField37[0] 22
                  5. TextField38[0] estimate
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                  8. DateTimeField1[0] 312015
                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                      26. TextField89[1] GRAB
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
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Page 32: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

November 26 2013

Page 5 of 5

Clarifier 3 (Clarifier 3-1-mid-depth and Clarifier 3-2-interface)

bull Total Phosphorous - 008 and 11 mgl

bull pH - 72 and 71 SU

bull E Coli - lt1 and 1 MPN100ml

bull PAHs - Detected in Clarifier 1-2 see attached Sample Results Tables

bull Total Nitrogen - 1 and 26 mgl

bull Nitrate - lt05 and lt05 mgl

bull Nitrite - lt05 and lt05 mgl

bull TKN - 1 and 26 mgl

bull Aluminum - lt005 and 38 mgl

bull BOD - 9 and 47 mgl

bull TSS - 45 and 750 mgl

bull Turbidity - 5 and 1 NTU

Recommendations

Based on the Analytical Results completed by Eastern Analytical Inc Horizons Engineering Inc

recommends pumping each lagoon and clarifier down to the supernatant interface individually and

discharging to the nearby Upper Ammonoonsuc River in fallwinter 2013 Allowable pumping rates will

be established based on BOD and TSS to meet the permit conditions while discharging Horizons

proposes that turbidity be monitored during the discharge to determine when the wastewater has reached

the supernatant interface An established allowable amount of turbidity will be determined based on the

relationship between turbidity and total suspended solids detected in the samples obtained (see to TSS

vs Turbidity Graph)

Once initial dewatering is completed Horizons proposes in the spring of 2014 that the remaining sludge

and supernatant water within the lagoons and clarifiers be pumped dewatered and disposed of at the

proper facility Water removed from sludge will be run through a bag filter and discharged to the outfall

of the treatment facility and to the nearby Upper Ammonoosuc River

Michael Czok Project Engineer

Horizons Engineering Inc

Attachments Analytical Results

Sample Results Tables

TSS vs Turbidity Graph Table 1

Sampling Location Site Plan

cc Mike Stirling Green Steel

P13087 Green Steel - Groveton MillDOCSREPORTSLead SamplingProposed Sampling for Grovetondoc

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
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                  5. TextField38[0] estimate
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                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
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Page 33: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Polish Pond 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 1-1 (Mid-Depth) 11 18 20803 20665 Polish 1-2 (Mid-Depth) 31 240 7382 1550

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 38 Interface Benzo(k)fluoranthene 093 Interface

Benzo(a)pyrene 28 Interface Indeno(123-cd)pyrene 29 Interface Dibenz(ah)anthracene 049 Interface

Aluminum Results Samples mgl Sample Depth

Polish 1-1 015 Mid-Depth Polish 1-2 15 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
          13. RadioButtonList[0] 3
          14. TextField13[0]
          15. TextField14[0]
          16. TextField15[0]
          17. TextField16[0]
          18. TextField17[0]
          19. TextField18[0]
          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
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Page 34: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Polish Pond 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Polish 2-1 (Mid-Depth) 15 35 15256 10627 Polish 2-2 (Interface) 22 300 10402 1240

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Polish 2-1 008 Mid-Depth Polish 2-2 35 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
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Page 35: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Quad 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 1-1 12 15 19070 24797 Quad 1-2 1 370 228835 1005

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 031 Interface Benzo(b)fluoranthene 07 Interface

Benzo(a)pyrene 048 Interface Indeno(123-cd)pyrene 056 Interface

Aluminum Results Samples mgl Sample Depth

Quad 1-1 lt005 Mid-Depth Quad 1-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
            1. Page11[0]
              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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              11. TextField42[0] Permit expired in 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
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                  5. TextField38[0] estimate
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                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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Page 36: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Quad 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 2-1 (Mid-Depth) 17 16 13461 23248 Quad 2-2 (Interface) 69 480 3316 775

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 054 Interface Benzo(b)fluoranthene 12 Interface

Benzo(a)pyrene 083 Interface Indeno(123-cd)pyrene 1 Interface Dibenz(ah)anthracene 017 Interface

Aluminum Results Samples mgl Sample Depth

Quad 2-1 lt005 Mid-Depth Quad 2-2 42 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
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                  5. TextField38[0] estimate
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                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
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Page 37: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Quad 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 3-1 (Mid-Depth) 13 14 17603 26569 Quad 3-2 (Interface) 71 1400 3223 266

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 27 Interface Benzo(b)fluoranthene 54 Interface Benzo(k)fluoranthene 14 Interface

Benzo(a)pyrene 44 Interface Indeno(123-cd)pyrene 47 Interface Dibenz(ah)anthracene 078 Interface

Aluminum Results Samples mgl Sample Depth

Quad 3-1 lt005 Mid-Depth Quad 3-2 40 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
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Page 38: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Quad 4 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Quad 4-1 (Mid-Depth) 11 15 20803 24797 Quad 4-2 (Interface) 24 400 9535 930

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 19 Interface Benzo(b)fluoranthene 37 Interface Benzo(k)fluoranthene 1 Interface

Benzo(a)pyrene 29 Interface Indeno(123-cd)pyrene 33 Interface Dibenz(ah)anthracene 054 Interface

Aluminum Results Samples mgl Sample Depth Quad 4-1 lt005 Mid-Depth Quad 4-2 65 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
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Page 39: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Clarifer 1 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 1-1(Mid-Depth) 42 990 5448 376 Clarifier 1-2(Interface) 100 3300 2288 113

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 16 Interface Chrysene 27 Interface

Benzo(b)fluoranthene 25 Interface Benzo(k)fluoranthene 58 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 18 Interface Dibenz(ah)anthracene 31 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 1-1 27 Mid-Depth Clarifier 1-2 23 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
                                          11. TextField59[0] Class B
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Page 40: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Clarifer 2 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 2-1( Mid-Depth) 1 1 228835 371961 Clarifier 2-2 (Interface) 40 990 5721 376

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 14 Interface Benzo(b)fluoranthene 29 Interface Benzo(k)fluoranthene 08 Interface

Benzo(a)pyrene 21 Interface Indeno(123-cd)pyrene 21 Interface Dibenz(ah)anthracene 038 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 2-1 lt005 Mid Depth Clarifier 2-2 86 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
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Page 41: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Clarifer 3 Sampling Results Date 11182013 Produced MZC

Pumping Rate Determination for Decommission Allowable Gallons Day Liters Day Allowable LBS Day BOD (Per Permit) Allowable Milligrams Day BOD mgL Allowable

7500000 28390575 2750 1247378000 44 Allowable LBS Day TSS (Per Permit) Allowable Milligrams Day TSS

447000 202755624000 71

Sample mgl BOD mgl TSS Allowable Pumping Rates BOD ( Gal Min) Allowable Pumping Rates TSS ( Gal Min)

Clarifier 3-1 (mid depth) 9 45 25426 8266 Clarifier 3-2 (interface) 47 750 4869 496

Polycyclic Aromatic Hydrocarbon PAH microgL (PPB) Sample Depth

Benzo(a)anthracene 35 Interface Chrysene 63 Interface

Benzo(b)fluoranthene 61 Interface Benzo(k)fluoranthene 17 Interface

Benzo(a)pyrene 48 Interface Indeno(123-cd)pyrene 4 Interface Dibenz(ah)anthracene 076 Interface

Aluminum Results Samples mgl Sample Depth

Clarifier 3-1 lt005 Mid Depth Clarifier 3-2 38 Interface

Notes

Mid-Depth refers to midway between the surface and supernant interface This was determined in the field visually a with a sludge judge Interface refered to the depth at which the supernant interface was determined This was determined in the field visually with a sludge judge

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
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          9. TextField9[0] 03588
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
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              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
                                          11. TextField59[0] Class B
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Page 42: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Total Suspended Solids vs Turbidity

1

10

100

1000

Tu

rbid

ity m

gl

TSS vs Turbidity

Power (TSS vs Turbidity)

1 10 100 1000 10000

Total Suspended Solids mgl

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
                                          11. TextField59[0] Class B
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Page 43: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Groveton Wastewater DecommisioningTable 1

Sample Location Sludge Depth (ft) Total Depth (ft) Polish 1 25 65 Polish 2 3 75 Lagoon Quad 1 175 7 Lagoon Quad 2 2 7 Lagoon Quad 3 2 7 Lagoon Quad 4 2 7 Clarifier 1 2 3 Clarifier 2 1 10 Clarifier 3 2 11

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
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          9. TextField9[0] 03588
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          11. TextField11[0] 603-466-9966
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
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Page 44: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Attachment C ndash December 3 2014 Laboratory Results

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
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              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
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                  28. TextField86[0] Please see attached
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
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Page 45: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Attachment D ndash NHDHR Correspondence

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
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                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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                                      5. TextField51[0] As the lagoons and clarifiers have only accepted stormwater in recent years treatment occurs only in the form of settling All other processes at the plant are discontinued
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                                          10. TextField58[0] 32 Effluent Pipe that discharges approx 05 mile westerly into the Connecticut River
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Page 46: APR 1 6 2ot5 · 2015-04-16 · APR 1 6 2ot5 . Robert Chapman Owner Groveton Wastewater Lagoons PO Box 64 Milan, NH 03588 . Re: Authorization to discharge under the Remediation General

Attachment E ndash US FWS Correspondence

To be forwardedhellip

  • Authorization Letter13
  • Letter
  • Figure 1 - Aerial
  • Figure 2 - Flow Shematic
  • NOI Form
  • Decommissioning Plan
  • December 3 Additional Sampling Laboratory Results
  • NH DHR Correspondence
  • US FWS Correspondence
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          1. TextField1[0] Groveton Wastewater Lagoons
          2. TextField2[0] PO Box 64
          3. TextField3[0] 2621 Paper Mill
          4. TextField4[0] 71 deg 31 19 W
          5. TextField5[0] 44 deg 35 31 N
          6. TextField6[0] Milan
          7. TextField7[0] Owner Bob Chapman email chapmanscrapyahoocom
          8. TextField8[0] NH
          9. TextField9[0] 03588
          10. TextField10[0] USA
          11. TextField11[0] 603-466-9966
          12. TextField12[0] 603-466-9960
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          20. TextField19[0] Michael Douglas Stirling Jr
          21. TextField20[0] 602-524-8312
          22. TextField21[0] 603-466-9960
          23. TextField22[0] mdstirlinggmailcom
          24. TextField23[0] Mike Stirling General Manager
          25. TextField24[0] 180 Lancaster Street
          26. TextField25[0] Gorham
          27. TextField26[0] NH
          28. TextField27[0] 03581
          29. TextField28[0] USA
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              1. TextField29[0]
              2. TextField30[0] The Site formerly held individual NPDES Permit No NH0001562 issued September 2006 and expired May 2011
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                  1. TextField34[0] The lagoon amp clarifiers have remained dormant for several years and as a result have only accepted stormwater Reportedly the lagoon was cleaned in 2008 Owner is seeking permit in order to dewater the lagoon amp clarifier supernatantstormwater
                  2. TextField35[0] 1
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                  5. TextField38[0] estimate
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                  8. DateTimeField1[0] 312015
                  9. DateTimeField2[0] 1212015
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                  12. TextField45[0] 44 deg 35 31 N
                  13. TextField46[0] 71 deg 31 20 W
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                  28. TextField86[0] Please see attached
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