ENGINEERING INVESTIGATIONS AT INACTIVE

ENGINEERING INVESTIGATIONS AT INACTIVE HAZARDOUS WASTE SITES

IN THE

PHASE II . I -

Golden Road Disposal Sit siteSNo. 828021

~own'of ~fiill, Monroe Coun I

t - March 1992

t

, .. .u

Prepared for:

New York State Department of Environmental Conservation

50 Wolf Road, Albany, New York 12233 Thomas C. Jotling, Commissioner

Division of Hazardous Waste Remediation Michael J. 07oole, Jr., P.E., Director

Prepared by:

Ecology and Environment Engineering, PC.

> .

TABLE OF C ( T m .: -.,

Sect ion

1 EXECUTIVE SUMMARY ...................................... 1 . 1 SITE DESCRIPTION AND BACKGROUND .................. 1 . 2 PHASE I1 INVESTIGATION ....-.....,. ;............... 1 . 3 SITE ASSESSMENT .....................,......:...:. 1 . 4 HAZARD RANKING SYSTEM SCORE ....,...,..........-... 1 . 5 ADDITIONS/CHANGES TO REGISTRY' OF IlWC"MVE

HAZARDOUS WASTE DISPOSAL SITES ...................

2 OBJECTIVE ............:.......................-......... L , 2-1'

3 SCOPE OF WORK ................. L.... . . . . . . . .c.. . . . . . . . 3-2

3 .1 INTRODUCTION ............... L...................... 3-1 3 . 2 PHASE I1 SITE INVESTIGATION ............... ....... . 3-2

3 . 2 . 1 Records SearchIData Compilatio~ ........... 3-2

3 . 2 . 2 Site Reconnaissance and Site Safety ... :... 3-2

3 . 2 . 3 Geophysical Survey ......................... 3-3

3 . 2 . 4 - doni t ~ r i n g V & l ~ + ~ ~ , ~ & ~ & ~ ~ , . . . . . . . ; . , ? - 3 3 . 2 . 5 ~ ~ b ~ . < ~ ' f f i ~ & , @ i ~ ' ; ~ l ~ ~ . ~ ~ ~ k ~ ~ ~ ~ : ~ . , r;; $-m4

"2 .? , . . . . -- 3 . 2 . 6 ~io~ndvater:-81r'm.pl~i~~~~'~~h.1~si~s * . . ., ., . . . . 3 . ~ 5

3 . 2 . 7 Surface ~&te&ebhWnt ~ d h f i ~ : ~ ~ and Analysis . ., . . ; . . . . . . . .~s+,,~ . . . . i . .. . . . . .

3 . 2 . 8 Surface Soil Sampling and Analysis . . , . . . , * .?-"4 3 . 2 . 9 Waste Sampling aqd Analysis ...:....... .., 3-6

3 .2 .10 Leachate Sampling and Analy9is ..... ;..,? 3 - i 7

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Table of Contents (Cont.)

Sect ion Page

4 SITE ASSESSMENT ....................................... ..................................... 4.1 SITE HISTORY

................................. 4.2 REGIONAL SETTING

4.2.1 Regional Geology and Hydrology of Monroe County .............................

................................... 4.3 SITE GEOGRAPHY

4.3.1 Topography ................................ ..................................... 4.3.2 Soils

................................ 4.4 SITE HYDROGEOLOGY

4.4.1 Geology ................................... ................................. 4.4.2 Hydrology

.................... 4.5 SITE CONTAMINATION ASSESSMENT

4.5.1 Subsurface Soil from Well Borings ......... 4.5.2 Groundwater ............................... 4.5.3 Surface Water/Sediment ....................

.............................. 4.5.4 Surface Soil

4.5.5 Waste ..................................... 4.5.6 Leachate .................................. 4.5.7 Contamination Assessment Summary ..........

4.6 RECOMMENDATIONS ..................................

5 FINAL APPLICATION OF HAZARD RANKING SYSTEM ............ 5-1

5.1 NARRATIVE SUMMARY ................................ 5-1

5.2 LOCATION (MAP) ................................... 5-3

5.3 HRS WORKSHEETS ................................... 5-4

5 .4 HRS DOCUMENTATION RECORDS (PHASE I AND 11) ....... 5-11

5.5 EPA FORM 2070-13 SITE INSPECTION REPORT .......... 5-71

6 REFERENCES ............................................ 6-1

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Table of Contents (Cont.)

Appendix Page

A SITE-SPECIFIC HEALTH AND SAFETY PLAN AND DRILLING SITE SAFETY CHECKLIST ................................. A-1

B PHOTOGRAPHIC LOG ...................................... B-1

C GEOPHYSICAL SURVEY .................................... C-1

........ D DRILLING LOGS FOR GROUNDWATER MONITORING WELLS D-1

E GEOTECHNICAL ANALYSES ................................. E-1

F RAW ANALYTICAL DATA SUMMARIES ......................... F-1

G SUBSURFACE SOIL. GROUNDWATER. SURFACE SOIL. SURFACE WATER/SEDIMENT. AND LEACHATE SAMPLING PROCEDURES ............................................ G-1

H SITE SURVEY MAP ....................................... H-1

I SITE FIELD LOGBOOKS ................................... 1.1.

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LIST OF TABLES

Table Page

3-1 Sources Contacted for the NYSDEC Phase I1 Investigation at the Golden Road Disposal Site ........................ 3-8

3-2 Water Level Data ........................................ 3-10

3-3 Surface Water and Sediment Sampling Locations ........... 3-11

......................... 3-4 Surface Soil Sampling Locations 3-12

................... 3-5 Waste and Leachate Sampling Locations 3-13

4-1 Summary of Geotechnical Analyses ........................ 4-22 *L-

4-2 Drilling Log Information of New Wells ................... 4-23

4-3 Monitoring Well Construction Data ....................... 4-24

........................................ 4-4 Water Level Data 4-25

4-5 Subsurface and Surface Soils. Sediment. Leachate- Stained SoiUSediment. and Waste Organic Analyses Summary ............................................... 4-26

4-6 Subsurface and Surface Soils. Sediment. Leachate- Stained Soil/Sedirnent. and Waste Inorganic Analyses Summary ................................................ 4-29

4-7 Field Measurements of Groundwater Chemical Parameters Taken During Well Sampling ................... 4-32

.... 4-8 Groundwater and Drill Water Organic Analyses Summary 4-33

4-9 Groundwater Inorganic Analyses Summary .................. 4-34

4-10 Surface Water and Leachate Organic Analyses Summary ..... 4-37

4-11 Surface Water and Leachate Inorganic Analyses Summary ... 4-38

b 4-12 Waste Inorganic Analyses Summary ........................ 4-42

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LIST OF ILLUSTRATIONS

Figure Page

1-1 Location Map: Golden Road Disposal Site ............... 1-8

1-2 Site Sketch of the Golden Road Disposal Site ........... 1-9

3-1 Geophysical Survey and Proposed Groundwater Monitoring Well Locations .............................. 3-14

3-2 Monitoring Well, Groundwater, Surface Water/Sediment, Surface Soil, Waste, and Leachate Sampling Locations ... 3-15

4-1 Bedrock Units of Northern Monroe County ................ 4-43

4-2 Ground Surface Contour Map ............................. 4-44

4-3 Overburden Groundwater Contour Map ..................... 4-45

5-1 Location Map: Golden Road Disposal Site ............... 5-3

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1. EXECUTIVE SUnllARY

1.1 SITE DESCRIPTION AND BACKGROUND

The Golden Road Disposal Site (Golden Road site) is located in the

Town of Chili, Monroe County, New York (see Figures 1-1 and 1-2). The

8-acre inactive site is located adjacent to Route 490 in a once-rural

area of the Town of Chili. Access to the site is obtained from Golden

Road. Conrail railroad tracks divide the site into two separate areas,

both of which lie immediately adjacent to designated wetlands and are

characterized by poor drainage and a high water table. The access road

to the area south of the railroad tracks is blocked off by a locking

gate. Access to the area north of the railroad tracks is through the

Fitzsimons residence driveway.

The site owner, Mr. Howard Fitzsimons, Jr., has been associated

with the Golden Road site throughout its use as a disposal site. Most

of the fill and drums were brought onto the site with the owner's per-

mission; however, Mr. Fitzsimons himself trucked foundry sand from Abex

Corporation to the site (Fitzsimons 1991). The drums originated from

the U.S. Army Reserve Unit, Chevron Oil, and unknown illegal dumping.

The poorly covered site was active from 1955 through 1976, receiving a

wide variety of waste types including U.S. Army artillery shell casings

from the 98th Division Reserve Unit (Fitzsimons 1991), 55-gallon drums

of unknown wastes, household refuse, metal slag, fly ash, and junked

vehicles. The filling of the site was largely accomplished using

foundry sand. A great deal of structural steel, fuel tanks, and

partially buried drums presently lie about the site. A portion of the

wetland area to the west and south was filled during the operation of

the site. There are no records concerning the volume of wastes that

entered the site.

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In early 1982, prior to the Phase I investigation, the Monroe

County Health Department and the New York State Department of Environ-

mental Conservation (NYSDEC) began taking samples of the surface waters,

sediments, drum contents, and well water from wells in close proximity

to the site. Results of groundwater testing indicated levels of cadmium

and lead exceeding New York State drinking water standards. Surface

water contained elevated levels of cadmium, benzene, and toluene. These

results were reported in the Phase I investigation report submitted by

Recra Research, Inc. in November 1983.

During 1985, an emergency drum removal project was carried out by a

United States Environmental Protection Agency (EPA) contractor. Approx-

imately 560 drums were removed from the land surface. Environmental

testing revealed the presence of chlorinated and nonchlorinated sol-

vents, high total organic carbon, organic solids with low flash points,

polychlorinated biphenyls (PCBs), and waste oils. Partially buried

drums are still visible on site.

1.2 PEIASE I1 INVESTIGATION

As part of the Phase I1 Investigation, Ecology and Environment

Engineering, P.C. (E & E) performed an initial site reconnaissance on

April 26, 1989, and a geophysical survey on May 17, 1989. Along with a

visual inspection, the site reconnaissance included a continuous air

monitoring survey using an HNu photoionization detector to determine the

presence of organic vapors. The geophysical investigation consisted of

a ground conductivity survey and a total earth's magnetic field survey

to locate any buried metallic materials and determine the presence of

contaminant plumes.

On June 15, 1989, Om P. Popli, P.E. Engineers (Om Popli), under

subcontract to E & E, collected 11 surface soil samples, two waste sam-

ples, and one leachate sample to characterize the chemical composition

of the soils throughout the site. A third waste sample was collected on

August 2, 1989, as requested by NYSDEC. Five monitoring wells were

drilled and installed between August 22 and 28, 1989, by Empire Soils

under the supervision of Om Popli. Subsurface soil samples from three

borings were collected for geotechnical analysis and one sample from

'w well GW-7 was collected for chemical analyses. Groundwater samples were


collected on February 6 and 7, 1990, and surface water samples were col-

lected on February 6, 8, 9, and 12, 1990. All sampling was performed

by Om Popli, as was the site survey, which was performed on February 12,

1990. All analyses were performed by E & E's Analytical Services Center

(ASC) .

1.3 SITE ASSESSIIENT.

The continuous air monitoring survey during the site reconnaissance

using the HNu photoionization detector indicated no organic vapors above

background levels from any areas on site. The geophysical surveys pro-

vided information to characterize the subsurface and locate potential

areas of buried metallic materials. Surface interference from metallic

objects (i.e., junked vehicles, steel structures, electric fences, etc.)

was encountered in several areas, however, six of the seven survey grids

contained enough area free from subsurface metallic debris to drill the

monitoring wells without any obstructions. The survey grid for moni-

toring well GW-7 was not designated free from subsurface metallic debris

due to the presence of junked vehicles within the survey grid. This

well location was moved to a more suitable area. The subsurface strati-

graphy, as confirmed by the installation of the groundwater monitoring

wells, indicated an average of 3 feet of fill material (foundry sand,

wood fragments, etc.) and possibly 18 feet in some locations (i.e.,

GW-5). The fill was underlain by silt and clay with rock fragments. In

areas where fill material was absent, the soils consisted of various

layers of silt, clay, sand, and gravel. Bedrock varied in depth between

11.2 feet to 25.4 feet below ground surface and the top of bedrock

generally dipped to the southwest.

Water levels varied between 2.1 feet above ground surface to 5.2

feet below ground surface. Water levels rising above ground surface

may indicate artesian conditions, enhanced by a mounding effect within

the fill areas, causing a high piezometric surface in the southern and

northwestern portions of the site. The groundwater in Monroe County

generally flows to the Genesee River or to Irondequoit Bay, which both

flow northerly to northeasterly into Lake Ontario (Sweet -- et al. 1938).

Regional groundwater in the vicinity of the site likely flows east

toward the Genesee River or north to northwesterly toward the lake.

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However, groundwater beneath the site is likely to be mounded in the

fill areas. Hounding occurs as water flows through the fill areas,

which are composed of coarser materials and have a high hydraulic con-

ductivity, to the underlying finer, undisturbed overburden, which has a

lower hydraulic conductivity. Those differences in hydraulic conduc-

tivity cause groundwater within the fill to flow radially outward to the

surrounding wetlands and ditches. Groundwater flow in the underlying

overburden appears to be to the east as indicated by the water levels

measured in the monitoring wells.

One subsurface soil sample was collected and analyzed for Target

Compound List (TCL) organics including volatile organics, base/neutral

and acid extractables (BNAs), and PCBs/pesticides. In addition, this

sample was analyzed for the inorganic portion of the TCL list including

23 metals and cyanide. The sample was collected from the GW-7 well bore

at a depth of 17 to 19 feet. No organic compounds or cyanide were

detected, however, magnesium was detected slightly above the common

range for soils in the Eastern United States.

Seven groundwater samples and one drill water sample were collected

and analyzed for TCL organics and inorganics. Several organic compounds

were detected in both up- and downgradient newly installed groundwater

monitoring wells and in the drill rig water. The drill rig water was

taken from a local fire hydrant on Golden Road and placed in the drill

rig water tank. Contamination detected in the drill rig water sample

was the result of laboratory artifacts and is not of concern. Most of

the compounds detected in the groundwater were in very low concentra-

tions (i.e., below sample quantitation limits). Some also may have been

laboratory artifacts. Benzene in GW-1 and GW-6, ethylbenzene in GW-1,

and vinyl chloride, chloroethane, 1,l-dichloroethane, and total 1,2-

dichloroethene in GW-7 exceeded New York State Class GA drinking water

standards. Several metals also exceeded New York State Class GA drink-

ing water standards in both unfiltered and filtered samples from all the

newly installed wells. Some of the samples contained metals (i.e.,

arsenic, barium, cadmium, chromium, copper, iron, lead, manganese, and

zinc) in unfiltered portions that were not detected in the filtered

portions. No PCBs, pesticides, or cyanide were detected in any of the

groundwater samples tested.

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Twenty-three surface waterlsediment samples were collected on and

adjacent to the Golden Road site. Fourteen on-site samples were ana-

lyzed for TCL organics and inorganics and eight off-site samples from

the railroad drainage ditch were analyzed only for PCBs/pesticides.

Proposed sample SW-13/SED-13 was not collected due to dry conditions.

Several organic compounds were detected in five of the 14 surface water

samples tested (SW-1, SW-7, SW-9, SW-11, and SW-12). All of the com-

pounds detected were in very low concentrations (i.e., below sample

quantitation limits) and did not exceed Class C surface water standards.

Several metals were detected in almost all the surface water samples

tested at concentrations exceeding Class C surface water standards for

the protection of aquatic life. The metals detected included aluminum,

cadmium, copper, cobalt, iron, lead, nickel, selenium, vanadium, and

zinc. No PCBs, pesticides, or cyanide were detected in any of the sur-

face water samples tested.

Several organic compounds were detected in 11 of the 14 sediment

samples tested (SED-1, SED-3, SED-4 through SED-11, and SED-14). Most

of these compounds were detected in very low concentrations (below sam-

ple quantitation limits) and some may have been laboratory artifacts

(i.e., carbon disulfide). In SED-8, one PCB compound (Aroclor-1254) was

detected at a very low concentration (i.e., below sample quantitation

limits), and two metals (chromium and nickel) exceeded the common range

for metals in soils of the Eastern United States. No pesticides or

cyanide were detected in any of the samples tested.

Eleven surface soil samples were collected and analyzed for TCL

organics and inorganics. Several organic compounds were detected in all

of the surface soils tested. Most of the compounds were in very low

concentrations (i.e., below sample quantitation limits) and some may

have been laboratory artifacts (i.e., chloroform, phthalates). One PCB

compound (Aroclor-1260) was also detected in very low concentrations in

samples S-1, S-2, and S-8. Neither metals nor cyanide were detected in

excess of common ranges of metals in soils of the Eastern United States,

and no pesticides were detected in any of samples tested.

Three waste samples and two leachate samples from apparent out-

breaks were collected and also analyzed for TCL organics and inorganics.

b Two of the waste samples (W-1 and W-2) consisted of foundry sand and one


sample (V-3) was a resin-like substance from a partially buried drum.

One of the leachate samples (L-1) was aqueous and the other was stained

soil/sediment. Several organic compounds were detected in all of the

waste and leachate samples tested. Most of the compounds were in very

low concentrations (i.e., below sample quantitation limits) and some may

have been laboratory artifacts (i.e., chloroform). The concentrations

of several metals such as cobalt, iron, manganese, and lead in the

resin-like waste sample (V-3) and aluminum, cadmium, cobalt, iron, lead,

nickel, vanadium, and zinc in the aqueous leachate sample (L-1) were

noticeably high, and exceeded New York State standards for the protec-

tion of aquatic life in Class C surface water. The lead concentration

in W-3 was noticeably high at 3,430 micrograms per liter (pg/L). No

metals were detected in excess of common ranges of metals in soils in

the Eastern United States for the foundry sand (W-1 and W-2) and

leachate-stained soil/sediment (L-2). No PCBs/pesticides or cyanide

were detected in any of the waste or leachate samples.

1.4 EAZARD RANKING SYSTEM SCORE

The Hazard Ranking System (HRS) score was compiled to evaluate

risks associated with the site. The HRS is applied to in'active hazard-

ous waste sites in New York State to prioritize those needing additional

investigation and remediation. The system evaluates site character-

istics, containment measures, waste types, and potential contaminant

receptors.

Under the HRS, three numerical scores are computed to express the

site's relative risk to or damage done to the surrounding population and

the environment. The three scores are described below:

o SH reflects the potential for harm to humans or the environment from migration of a hazardous substance away from the facility via groundwater, surface water, or air. It is a composite of separate scores for each of the three routes (S = groundwater route score, Ssw = surface water route sc@e, and Sa = air route score).

o SFE reflects the potential for harm from substances that can explode or cause fires.

o S reflects the potential for harm from direct contact wyfh hazardous substances at the facility (i.e., no migration need be involved).

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Based on t h e r e s u l t s of t h i s and p r e v i o u s s t u d i e s , t h e HRS s c o r e s

f o r t h e Golden Road s i t e have been c a l c u l a t e d as f o l l o w s :

SH = 28.06 ' sgw = 44.89; Ss, = 18.46; Sa = 0 )

sFE = Not s c o r e d

SDC = 50

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- - -- -

47-15-25 (11/90)-9d Original-BHSC NEW YORK STATE DEPARTMENT OF ENVIRONMENTAL CONSERVATION Copy-REGION

DIVISION OF HAZARDOUS WASTE REMEDIATION Copy-DEE Copy-DOH

A D D I T I O I I S / ~ E S m REGISTRY OF IMCTIVE ~AZABDOUS WASTE DISPOSAL SITES Copy-PREPARER

I -

9.3. Briefly describe the site (attach site plan showing disposal/sampling locations) The site, which is approximately 8 acres in size, is divided into two sections (north and south) by Conrail tracks. The northern section is primarily used for residences and cow pasture, with a large area of junked vehicles. The southern section is inactive, partially wooded, and contains various I areas of foundry sand and other surface debris. Wetlands are present to the north, west, and south

I of the site. Figure 1-2 of the Phase I1 Investigation report shows the site plan.

b. Area 8 acres c. EPA ID number d. PA/SI [ ] Y e s I ] N O

1. Site Name Golden Road Disposal Site

e. Completed: [XI Phase I [XI Phase I1 [ 1 PSA [XI Sampling

3. Town Chili

2. Site Number 828021

- -

10. Briefly list the type and quantity of the hazardous waste and the dates that it was disposed of at this site. The site was active from 1955 to 1976, receiving a wide variety of waste types, including: U.S. Army artillery shells, 55-gallon drums of unknown wastes, household refuse, metal slag, fly ash, and junked vehicles.

4. County Monroe

lla. Summarized sampling data attached I

7. Activity I I Add [ 1 Reclassify [ 1 Delist [ ] Modify

5. Region 9

1 [ ] Air [XI Groundwater [XI Surface Water [XI Soil [XI Waste [ ] EP Tox I

8.. Describe location of site (attach USGS topographic map showing site location). The Golden Road Disposal Site is located in the Town of Chili, Monroe County, New York, adjacent to Interstate 490. Site access is from Golden Road. Figure 1-1 of the Phase I1 Investigation Report shows the site location on the USGS topographic quadrangle.

132.16,132.20,133.13 b. Quadrangle Clifton, NY c. Site latitude 40°07'15" Longitude 77O45'30" d. Tax Map Number 133.17

6. Classification current 2 /Proposed

b. List contravened parameters and values

1 Groundwater: Surface Water: I Arsenic to 29.4 pg/l Aluminum to 18,700 pg/l Barium to 1,230 pg/l Cadmium to 38.4 pg/l Cadmium to 38 pg/l. Copper to 182 pg/l Chromium to 217 pg/l Iron to 326,000 pg/l Copper to 260 pg/l Lead to 193 pg/l Iron to 265,000 pg/l Nickel to 666 pg/l Lead to 364 pg/l Vanadium to 107 pg/l Magnesium to 840,000 pg/l Zinc to 803 pg/l Manganese to 1,030 pg/l sodium to 71,600 pg/l Zinc to 1,320 pg/l Chloroethane to 17 pg/l 1,l.-Dichloroethane to 36 pg/l Total-1.2,-dichloroethene to 8 pg/l Beneene to 36 pg/l Ethylbenzene to 6 pg/l

02[UZ]YN408O:D2833/6638


I 12. Site impact data

I I a. Nearest surface water: Distance 0 ft. Direction west, south Classification C I b. Nearost groundwater: Depth 2.1 feet Flow Direction: northeast [ ] Source [XIPrimary [ ] principal

above ground surface to 5.2 foot below tho surf ace.

c. Nearest water supply: Distance 0 ft. Direction east Active [XI Yes [ ] No

1 d. Nearest building: Distance 0 it. Direction east Use res idence

a. Crops/livestock on site? [XI Yes [ 1 No j. Within a State Economic Development Zone? [ ] Yes [ 1 No

f. Exposed hazardous wasto? [XI Yes [ I No k. For Class 2A: Code Health model score I

g. Controlled site access? [ I Yes [XI No 1. For Class 2: Priority category

h. Docurnonted fish or wildlife m. HRS Score 28.06 mortality? [ 1 Yes [XI No

i. Impact on special status fish or n. Significant threat [XI Yes I I No wildlife resource? [ 1 Yes [XI No [ I Unknown

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15. Telephone Number (716) 594-2335

13. Site owner's name Howard Fitzsimons, Jr.

16. Prepares James D. Griffis, CHUM Ecology and Environment Engineering, P.C.

Nama, title, and organization

-.;%& .' . ( O L ' , 2,;- , (/A /? /' Signature

17. Approved

Name, title, and organization

Date Signature

14. Address 227 Golden Road, Chili, NY

ipencerport. NY, 1971; All (~hotorevi;ed-1978). SCALE 124.000

Figure 1-1 LOCATION MAP: GOLDEN ROAD DISPOSAL SITE

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2. OBJECTIVE

This Phase I1 investigation was conducted under contract to the

NYSDEC Division of Hazardous Waste Remediation, Bureau of Hazardous Site

Control. The objective of the Phase I1 investigation was to determine

if hazardous wastes have been disposed of at the site, if contaminants

exist in the various media (air, groundwater, and soils), and whether

threats to human health and the environment exist. Information gathered

relative to the above will allow NYSDEC to reclassify the site or, if

warranted, delist it.

The Phase I1 investigation was designed to supplement existing data

for the Golden Road Disposal site and update the HRS score. Previous

investigations conducted by Recra Research, Inc. in November 1983 have

shown levels of cadmium and lead in private groundwater wells that

exceed New York State drinking water standards. Also, cadmium, benzene,

and toluene were found in the surface water on site. No surface or

subsurface soil data for the site were available prior to the Phase I1

study.

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3. SCOPE OF VORR

3.1 INTRODUCTION

Field work for the Phase I1 investigation at the Golden Road site

was based on a work plan prepared by NYSDEC; the work began in June 1989

and was completed in February 1990. A site-specific health and safety

plan (HSP) was submitted for review, and a quality assurance project

plan (QAPP) was submitted to NYSDEC for approval prior to the start of

field work. The work plan called for the installation of seven ground-

water monitoring wells and the collection of groundwater samples from

each monitoring well, as well as the collection of 15 surface water/-

sediment samples, 11 surface soil samples, two waste samples, and two

leachate samples. Based on the findings of the geophysical survey, two

proposed well locations (GW-5 and GW-7) were moved due to significant

electrical or magnetic anomalies and on-site access problems. Proposed

monitoring well GW-5 was moved onto the fill area because of a steep

grade and standing water at the originally proposed location, and GW-7

was moved 125 feet southwest of the original location due to the pre-

sence of surface interference to geophysical instruments caused by

junked vehicles surrounding the proposed well location.

At the request of the on-site NYSDEC representative, one additional

waste sample was collected from a partially buried drum containing a

resin-like substance and eight additional surface waterlsediment samples

were collected along the railroad drainage ditch. The sample from the

drum was submitted for full TCL analysis while the samples from the

drainage ditch were analyzed for PCBs/pesticides only.

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3.2 PEASE I1 SITE INVESTIGATION

3.2.1 Records Search/Data Compilation

Available information from state, county, municipal, and private

files were collected and reviewed prior to the initiation of field work.

Records from local and state agency files were reviewed to supplement

the Phase I report prepared by Recra Research, Inc. in November 1983.

The data review facilitated completion of the field investigation and

site assessment and calculation of the final HRS score. Specific con-

tacts are listed in Table 3-1.

3.2.2 Site Reconnaissance and Site Safety

At the beginning of each day of field activities, a site safety

meeting was conducted by the site safety officer or the team leader. 9

Discussions included the contaminants found on site, routes of exposure,

the route to the hospital, location of the nearest phone, and the use of

the air monitoring instruments. Also, a general plan of the site activ-

ities for the day was discussed. Each person on site was requested to

sign the attendance sheet from these meetings. A site specific HSP was

L available to all personnel at all times (see Appendix A).

On May 9, 1989, E & E personnel conducted a site reconnaissance.

The purposes of the site visit were to:

o Identify access problems;

o Identify tentative locations for borings and wells, surface soil, surface waterlsediment, waste, and leachate samples;

o Visually inspect well locations and contact utility companies to determine if underground or aboveground utilities may impact drilling.

o Identify a water supply source for drilling purposes;

o Conduct a limited air monitoring study using an HNu photoionization detector; and

o Photodocument present site conditions.

The air monitoring survey indicated no organic vapor readings above

background from any area tested. The site contained large amounts.of

metal debris on the surface, which caused interference with geophysical

'bf


instrumentation. Access appeared to be limited to GW-1 by power lines

and a drainage ditch, to GW-2 by trees and a sharp change in grade, and

to GW-5 by ponded water and steep grade. Actual site conditions during

the site reconnaissance have been photodocumented and are presented in

Appendix B, and field logbooks are included in Appendix I.

3 .2 .3 Geophysical Survey

Geophysical surveys utilizing an EM31 ground conductivity meter and

a proton precession magnetometer were performed at the Golden Road site

on May 17, 1989. These surveys were conducted at the seven proposed

monitoring well locations within and around the perimeter of the site

(see Figure 3-1). The results were used to determine site geological

conditions, locate buried materials, verify proposed monitoring well

locations, and identify any conductive subsurface plumes. The geophysi-

cal survey methods and results are presented in Appendix C, and field

logbooks are included in Appendix I.

3.2 .4 Monitoring Well Installation

Five shallow overburden wells were installed at the Golden Road

site between August 22 and August 29, 1989 and two on January 9, 1990 by

Empire Soil Investigations, Inc. under the supervision of Om Popli. Two

of the wells were installed in January due to delays incurred in obtain-

ing a permit to drill on New York State Department of Transportation

(NYSDOT) property. The permit was issued by NYSDOT with co-approval of

the United States DOT. The wells monitor shallow groundwater in the

overburden, both up- and downgradient of the site (see Figure 3-2 and

Table 3-2).

The wells were drilled using an Acker AD-2 hollow-stem auger rig

and constructed in accordance with NYSDEC guidelines. Two-foot soil

samples were collected in 5-foot intervals above the water table and

continuously below the water table using a 2-inch outside diameter (OD)

split-spoon sampler driven by a 140-pound safety hammer with a 30-inch

free fall. Additional split-spoon samples were taken where major

changes in lithology occurred. Seven soil samples were collected for

geotechnical analyses along with one sample for chemical analysis (GW-7,

17 to 19 feet). The last sample was collected because of elevated


organic emissions above background levels detected from the split-spoon

sample. No visible contamination was observed.

The boreholes were advanced using 4.25-inch inside diameter (ID)

hollow-stem augers until refusal at top of bedrock. All wells were set

in the overburden, just above bedrock. Well screen consisting of 2-inch

ID 0.010 machine-slot polyvinyl chloride (PVC) was set at the bottom of

each borehole, above the top of bedrock. Screen length varied from 5

feet (GW-1 and GV-2) to 7 feet (GW-6 and GW-7) to 10 feet (GW-3, GW-4,

and GW-5). The screens were followed by threaded, flush-joint PVC riser

of the same diameter as the well screen to approximately 2 feet above

ground surface. The wells were completed with a sand pack extending 1

foot above the top of the well screen in GW-1 and GW-2, and 2 feet in

the other wells, followed by 1 foot of bentonite pellets in GW-1 and

GW-2 and 2 feet in the other wells, followed by bentonite grout. These

differences were the result of differing depths to groundwater and the

need to screen across the water table. A locking protective steel

casing was placed over the PVC and a concrete pad was constructed on the

ground surface around the protective casing.

After completion of the well, but not sooner than 24 hours after

grouting was completed, the well was developed using air surging. Well

development was performed until pH, conductivity, and temperature

remained constant.

A decontamination pad was constructed on site to steam clean the

drill rig, augers, bits, rods, split-spoons, casings, etc. before and

after the installation of each well. Split-spoons were decontaminated

at each drill site between each sample to prevent cross-contamination of

samples. A trisodium phosphate solution, tap water rinse, pesticide-

grade methanol rinse, and triple deionized water rinse were used succes-

sively.

Boring logs are found in Appendix D, geotechnical analyses are

included in Appendix E, and field logbooks are included in Appendix I.

3.2.5 Subsurface Soil Sampling and Analysis

During the installation of the seven monitoring wells (GW-1 through

GW-7), one subsurface soil sample was collected on August 23, 1989 for

k chemical analysis. The sample was collected from GW-7 at a depth of 17

recycled paper ecology end environment

to 19 feet as requested by the NYSDEC site representative due to an

organic odor present from the split-spoon sample. The sample was

analyzed for TCL organics and inorganics by E & E's Analytical Services

Center (ASC). In addition, quality assurance/quality control (QA/QC)

samples consisting of one matrix spike/matrix spike duplicate (MS/MSD)

sample (GW-7HS/GW-7MSD) were analyzed for volatile organic compounds.

Analyses and reporting were performed following the NYSDEC Contract

Laboratory Protocol (CLP) of November 1987.

Seven subsurface soil samples were collected for geotechnical

analyses. Three were analyzed for grain size and four for Atterberg

limits. Each of these samples was chosen because i t lay within the

screened depth of the well.

Field procedures for subsurface. soil sampling are discussed in

Section 3.2.4. Geotechnical analyses are included in Appendix E.

Analytical results are discussed in Section 4.5 and raw data summary

sheets are included in Appendix F.

3.2.6 Groundwater Sampling and Analysis

As part of the Phase I1 investigation of the Golden Road site,

water level measurements and groundwater samples were collected from the

seven newly installed monitoring wells on February 6 and 7, 1990 (see

Figure 3-2 and Table 3-2). The wells were purged of three to five well

volumes of water after recording the water level, then sampled using

dedicated PVC bailers. Although the wells were properly developed and

purged prior to sampling, the groundwater samples were very silty during

sample collection. These samples were analyzed for TCL.0rganic.s and

inorganics by E & E's ASC. In addition, QA/QC samples consisting of a

drill rig water sample were analyzed for the above-mentioned compounds.

MS/MSD samples were analyzed for volatile organics (GW-6MS/GW-6MSD),

BNAs (drill rig MS/drill rig MSD), and PCBs/pesticides (GW-4MS/GW-4MSD

and drill rig MS/drill rig MSD).

Analytical results are discussed in Section 4.5 and raw data

summary sheets are included in Appendix F. Field procedures for ground-

water sampling are presented in Appendix G.

recycled paper ecology and enwironmenc

3.2.7 Surface Vater/Sediment Sampling and Analysis

Twenty-three surface water/sediment samples were collected on

February 6, 8, 9, and 12, 1990 from intermittent streams, wetlands,

ponds, storm sewers, and railroad ditches surrounding the site (see

Figure 3-2 and Table 3-3). Fifteen of the samples were analyzed for TCL

organics and inorganics and eight for PCBs/pesticides only. Surface

waterlsediment location SW-13ISED-13 was not sampled due to dry condi-

tions. All analyses were performed by E & E's ASC. In addition, QA/QC

samples consisting of surface water MS/MSD samples were analyzed for

volatile organics (SW-14MSlSV-14MSD), BNAs (SW-11MS/SW-11MSD and

SW-12MS/SW-12MSD), and PCBs/pesticides (SW-19MS/SU-19MSD). Sediment

MS/MSD samples were analyzed for volatile organics (SED-8MS/SED-8MSD,

SED-lOMS/SED-IOMSD, SED-14MSlSED-14MSD, and SED-15MS/SED-15MSD), BNAs

(SED-11MS/SED-llMSD), and PCBs/pesticides (SED-16MS/SED-16MSD).

Analytical results are discussed in Section 4.5, raw data is pre-

sented in Appendix F, and field procedures used are described in

Appendix G.

3.2.8 Surface Soil Sampling and Analysis w Eleven surface soil samples were collected from various areas

throughout the site on June 15, 1989 (see Figure 3-2 and Table 3-4).

These samples were analyzed for TCL organics and inorganics by E & E's

ASC. In addition, a QA/QC sample consisting of one MS/MSD sample

(S-9MS/S-9MSD) was analyzed for all of the above-mentioned parameters

except BNAs.

Analytical results are discussed in Section 4.5, raw data are

presented in Appendix F, and field procedures are described in Appendix

G.

3.2.9 Vaste Sampling and Analysis

Two waste samples consisting of foundry sand were collected on

June 15 and one of a resin-like substance from a partially buried drum

was collected on August 24, 1989 (see Figure 3-2 and Table 3-5). These

samples were analyzed for TCL organics and inorganics by E L E's ASC.

In addition, a QA/QC sample consisting of one MS/MSD sample

L (W-3MS/W-3MSD) was also analyzed for volatile organics. Analytical


results are discussed in Section 4.5, raw data are presented in

Appendix F, and field procedures are described in Appendix G.

3.2.10 Leachate Sampling and Analysis

Two leachate samples were collected along the northern edge of the

southern portion of the site at apparent outbreaks (see Figure 3-2 and

Table 3-5). One sample, L-1, collected June 15, 1989, was mostly aque-

ous in nature. The second leachate sample, L-2, collected February 8,

1990, contained frozen stained soil/sediment. The samples were analyzed

for TCL organics and inorganics by E & E's ASC. For QA/QC purposes, the

aqueous leachate sample was grouped with the other water samples and the

soil/sediment sample was grouped with the other sediment samples.

Analytical results are discussed in Section 4.5, raw data are pre-

sented in Appendix F, and field procedures are described in Appendix G.

recycled paper ecology and environmen~

SOU1CES CORTA-D FOR IRSDEC P W E I1 I ~ S T I O A T I O U A T THC f3OLDKR ROAD DISPOSAL S I T E

New York State Department of Health Bureau of Environmental Exposure 2 University Place Room 205 Albany, Nev York 12203 Contact: Mary Ketter Telephone Number: 716/847-4551 Date: April 6 . 1989 Information Gathered: rile search for NYSDEC Phase I1 report preparation.

New York State Department of Environmental Conservation 584 Delaware Avenue Buffalo, New York 14202 Contact: Jaspal Singh Walia Telephone Number: 716/847-4585 Date: March 27-28, 1989 Information Gathered: File search for NYSDEC Phase I1 report preparation.

Monroe county Environmental Management Council 65 Broad Street Terminal Building, Room 203 Rochester, New York Contact: Louise Hartshorn Telephone Number: Date: April 13, 1989 Information Gathered: Monroe aerial photos and water service maps of NYSDEC Phasa I1

sites. Monroe County Department of Health was present at this meeting.

county of Monroe Department of Planning 47 South Pitzhugh Street, Suite 200 Rochester. New York Contact: Andy Wheatcraft Telephone Number: 716/428-5335 Date: March 29, 1989 Information Gathered: Land use and census data for Monroe County NYSDEC Phase II

site-.

New York State Department of Environmental Ccnservation Bureau of Hazardous Site Control 50 Wolf Road A!bany, New Pork 12233 Contact: Xlks Ryan and Jane Thapa Telephone Number: 518/457-9538 Date: Aprli 3-4, 1989 Infarmation Gathered: File search f c r additicnal d a t a and :?iSDE? Phase I reports.

sew Ygrk State 3epartment cf Health Bureau cf Environmental Exposure 2 University Place Room 2 0 5 Albany. New York 12203 t c n t a c t : L s n i >. Rafter'; fslephc-n- b:umSer: 518/458-630E >ate: A:r i! 3 - 4 . 1 3 6 5 T z t ~ r ~ b t l ~ n Gathered: Viewed sits lnspecrion r e p z r ? : f c r ?!i'SZE

-. . .- -- ,,: iL , - I . . . , , , , I , . ~ ~ ~ ~ : ~ ~ ~ l j l n 6 ; ; i ; :

recycled paper

Table 3-1 (Cont.)

New York State Department of Environmental Conservation Division of Regulatory Affairs 600 Delaware Avenue Buffalo, NOW York 14202 Contact: Mary Ketter Telephone Number: 716/847-4551 Date: April 6, 1989 Information Gathered: Pile search.

Monroe County Water Authority 475 Noris Drive Rochester, New York Contact: Tom Stein Telephone Number: 716/422-2000 Date: June 16, 1989 Information Gathered: Water use information for NYSDEC Golden Road site.

New York State Department of Environmental Conservation Information Services/Significant Habitat Unit Wildlife Resources Center 700 Troy-Schenectady Road Latham, New York 12110-2400 Contact: John Ozard Telephone Number 518/783-5733 Date: May 2, 1989 Information Gathered: Information on designated critical habitats with respect to

NYSDEC Phase I1 sites.

Monroe County Department of Maps and Surveys 39 West Main Street, Room 304 Rochester, New York Contact: Andies Hrycaj Telephone Number: 716/428-5461 Date: April 3, 1989 Information Gathered: Orthophoto maps of Monroe County NYSDEC Phase I1 site, tax

maps for Golden Road site.

New York State Department of Environmental Conservation, Region 8 Division of Hazardous Waste 6274 East Avon-Lima Road Avon, New York Contact: Todd Caffoe Telephone Number: 716/226-2466 Date: March 28, 1989 Information Gathered: Pile search for NYSDEC Phase I1 reports.

New York State Department of Environmental Conservation Water Division 600 Delaware Avenue Buffalo, New York 14202 Contact: Rebecca Anderson Telephone Number: 716/847-4590 Date: January 24, 1990 Information Gathered: Flood Insurance Rate Maps

Monroe County Economic Development Office 1 West Main Street, Suite 600 Rochester. New York Contact: Melissa Brookmire Telephone Number: 716/428-4504 Date: March 28, 1989 Information Gathered: Population figures for Town of Chili


T a b l e 3-2

WATER LBVEL DATA

R e l a t i v e ~ l e v a t i o n s " ( f e e t

Wa te r L e v e l Below Ground R e l a t i v e R e l a t i v e R e l a t i v e

Da te S u r f a c e E l e v a t i o Grade Water L e v e l E Wel l Measured ( f e e t ) a t T . O . C . levat ti on^ E l e v a t i o n

GW- I 2/7/90 3/8/91

GW-3 2/7/90 + l . 5 347 .65 3/8/91 +1.9 ( f l o w i n g )

GW- 4 2/7/90 + 2 . 1 ( f l o w i n g ) 347 .93 3/8/91 + 2 . 1 ( f l o w i n g )

GW- 5 2/7/90 3/8/91

GW- 6 2/6/90 3/8/91

d ~ l e v a t i o n s a r e n o t t r u e e l e v a t i o n s , b u t a n o n - s i t e r e f e r e n c e p o i n t ( 1 . 0 . . a r a i l r o a d s p i k e i n R o c h e s t e r Gas a n d E l e c t r i c Power P o l e No. 1 3 w i t h a n assumed

b e l e v a t i o n o f 350.00 f e e t above mean s e a l e v e l ) . T . O . C . = Top o f s t e e l c a s i n g .

' ~ r a d e e l e v a t i o n s r e p o r t e d t o t h e t e n t h o f a n i n c h o n l y . +Water l e v e l measu red w i t h i n t h e w e l l c a s i n g a t a n e l e v a t i o n above g round s u r f a c e .

Note: Wa te r l e v e l s were measured t o t h e n e a r e s t 0 .01 f o o t u s i n g a n e l e c t r o n i c a u d i b l e w a t e r l e v e l m e t e r .

recycled paper ccologv and environment

Table 3-3

SURFACE WATER AND S E D I m SAHPLIRG LOCATIORS

Sample Number Location

SW-l/SED-1

SW-Z/SED-2

SW-3/SED-3

SW-4/SED-4

SW-5/S ED-5

SW-6/SED-6

SW-7/SED-7

SW-8/SED-8

SW-9/SED-9

SW-10/SED-10

SW-11/SED-11

SW-12/SED-12

SW-13/SED-13 (not sampled)

SW-14/SED-14

SW-15/SED-15

SW-16/SEb-16

SW-17/SED-17

Wetlands southeast

1-490 intermittent stream

South intermittent stream

Wetlands south

Wetlands southwest

Railroad ditch

Railroad ditch

On-site. pond/south

Railroad ditch

Railroad ditch

Invert of storm sewer

Wetlands north

Wetlands north center

Wetlands west

Wetlands northwest

Off-site railroad ditch

Off-site railroad ditch

SW-18/SED-18 Off-site railroad ditch




SW-22/SED-22 off-site railroad ditch

SW-23/SEb-23 Off-site railroad ditch

02[UZlYN4080:D2833/6649/35

recycled paper rcology and cnvimnrnent

Table 3-4

SURFACE SOIL SAHPLIUG LOCATIOUS

Sample L o c a t i o n

S-1 Along t h e e a s t s i d e of t h e s o u t h e r n f i l l a r e a



S-4 Along t h e s o u t h s i d e of t h e s o u t h e r n f i l l a r e a



S-7 Along t h e n o r t h s i d e of t h e s o u t h e r n f i l l a r e a


S-9 Ad jacen t t o GW-7

S-10 Along t h e west s i d e of t h e n o r t h e r n f i l l a r e a

S-11 Along t h e west s i d e of t h e n o r t h e r n f i l l a r e a

[UZ]YN4080:D2833, 12885, PM = 33


Tablo 3-5

WASTE Am) ISACEATE SAMPLIIIG WCATIOIIS

Sample Location

W- 1 Foundry sand from the northwest end of the southern fill area

Foundry sand from the central portion of the southern fill area

Resin-like substance from a partially buried drum adjacent to GW-5 near the western edge of the southern fill area

L- 1 Along the north edge of the southern fill area (aqueous )

L- 2 Along the north edge of the southern fill area (soil/sediment)

02[UZlYN408O:D2833/2888/25


COW PASTURE

RVEY GRD NO. 2

S U M QRD

H Geophysical Survey Grid

Flgure 3-1 GEOPHYSICAL SURVEY AND PROPOSED GROUNDWATER MONITORING WELL LOCATIONS

Figure 3-2 MONITORING WELL, GROUNDWATER, SURFACE WATER, SURFACE WATER/SEDiMENT, SURFACE SOIL,

WASTE, AND LEACHATE SAMPLING LOCATIONS

4. SITE ASSESSHBNT

4.1 SITE HISTORY

The Golden Road site is an 8-acre, private parcel of land that was

used as a fill area, located in a once-rural area of the Town of Chili,

Monroe County, New York. The site is divided into two separate areas

(north and south) by Conrail railroad tracks. The northern area is pre-

sently occupied by the site owner, Mr. Howard Fitzsimons, Jr.

The Fitzsimons residence is a two-story dwelling set back approxi-

mately 600 feet to the west of Golden Road. The property is bounded by

active Conrail tracks to the south and wooded wetlands to the north and

west. The area is open and currently used as a cow pasture. There are

numerous junked vehicles, several aboveground storage tanks that once i contained fuel oil from Chili Fuels, and a metal storage building along ,

the southern border of this northern section. The storage building t)<\'' ' , belongs to Mr. Fitzsimons and was used for general storage, maintenance, , ,-1'

and repair of equipment. An 18-inch transit sanitary sewer line - +

1') \ \ -

(cement/asbestos) is present north of and parallel to the railroad I _ - j * *

. ,' lines. The sewer line is approximately 12 feet below the ground sur-,,,,/iff

face. The dates of installation and purpose of this sewer line could

not be confirmed.

The southern area of the site is currently inactive. This area is

characterized by areas of fill (foundry sand from Abex Corporation),

surrounded by wooded wetlands to the south and west, Conrail tracks to

the north, and a wooded area to the east. The fill area contains very

large, empty steel storage tanks and scrap metal on the surface, and

partially buried drums on the southern border. Both areas lie immedi-

ately adjacent to Class I1 designated wetlands and are characterized by

poor drainage and a high water table. Extensive landfilling has

recycled paper crology and cnvkrnnlrnt

elevated the site surface approximately 10 feet above the surrounding

terrain.

The Golden Road site was filled from 1955 through 1976 by

Mr. Howard Fitzsimons, Jr., the sole owner. The site received a wide

variety of wastes including U.S. Army artillery shell casings from the

98th Division Reserve Unit (Fitzsimons 1991), household refuse, metal

slag, fly ash, and junked vehicles. No live ammunition was disposed of

on site. Much of the actual filling of the site was accomplished using

foundry sand hauled from Abex Corporation.

Prior to 1985, several hundred rusted, leaking 55-gallon drums were

piled in several places, some of which were lying in the impounded water

of the wetlands to the south of the Conrail tracks. The drums orig-

inated from the U.S. Army Reserve unit, Chevron Oil, and unknown illegal

dumping. In 1985, an emergency drum removal project was completed by an

EPA contractor, and approximately 560 drums were removed from the site.

However, partially buried drums are still visible on site, and addi-

tional buried drums may be present. Environmental testing revealed the

presence of chlorinated and nonchlorinated solvents, high total organic

carbon, organic solids with low flashpoints, PCBs, and waste oils.

A large number of junk vehicles exist on the northern section of

the property behind the Fitzsimons residence and the large metal storage

building. The Fitzsimons residence is served by a private well located

approximately 40 feet to the north of the residence; however, most of

the surrounding area is serviced by public water. Also located on the

site are a great deal of structural steel debris and fuel tanks. There

are no records of the volumes of the various types of waste that entered

the Golden Road site.

4.2 REGIONAL SEITING

4 . 2 . 1 Regional Geology and Bydrology of Monroe County

Monroe County lies within the Central Lowland Physiographic

Province (Eastern Lake Section). The county is primarily mantled by

glacial till and laminated lacustrine clay and silt deposits. The till

consists of unconsolidated, poorly-sorted clay, silt, and/or sand depo-

sits of relatively low permeability (loamy matrix). Till thickness

ranges from 1 to 165 feet. Lacustrine deposits span southward for


nearly 10 miles from the southern shore of Lake Ontario and exhibit mod-

erate bedding-plane permeability. Lacustrine deposits vary up to 165

feet. Eskers, trending southwest, exist in the western part of the

county. The area between Rochester and Syracuse, just east of the site,

has been estimated to include approximately 10,000 drumlins (Broughton

et al. 1973). -- Outcropping of bedrock is sporadic but occurs along the Genesee

River, Sibleyville Gravel Pit, Honeyoe Falls, and State Route 386

(approximately 1 mile south of South Greece). The bedrock in the region

is exclusively sedimentary and nearly flat-lying, dipping south-

southwest approximately 40 feet per mile. Although the bedrock dips

southward, the land surface increases in elevation to the south. There-

fore, the bedrock units are progressively younger from north to south.

This discussion focuses on five distinct bedrock groups that occur

between the southern shore of Lake Ontario and the New York State

Thruway (see Figure 4-1). These sedimentary units are all located

beneath the Golden Road site and act as the primary controls on regional

groundwater flow. The oldest unit, upper Ordovician in age, is the pre-

dominantly red shale of the Queenston Formation. Commonly, thin green

shale beds and green mottling are present. When weathered, these shales

form the sticky red clay of the Lake Ontario Plain. The Queenston is

approximately 700 to 1,100 feet thick.

Groundwater occurs principally within a fractured and weathered

zone at the top of the Queenston Shale. Most wells penetrating the

Queenston draw water from both the Queenston and the overlying deposits

(Johnston 1964).

Overlying the Queenston Formation is the Lower Silurian Grimsby

Formation of the Medina Group. The basal portion of the Grimsby con-

sists of red shales with interbedded red sandstones. The upper Grimsby

is very distinct in that it is green and white mottled with numerous

depositional features such as cross-bedding, ripple marks, and sole

marks. Its thickness is reported to be 70 feet at Medina in neighboring

Orleans Coun ty . The rock units of the Clinton Group, which overlie the Medina

Group, are highly fossiliferous, with lithologies that are more diverse

than any other bedrock group in this report. Rock units of the Clinton

recycled paper crulogy and environment

Group include shale, sandstone, hematite, limestone, and dolostone. The

total thickness of the Clinton Group is more than 170 feet.

Generally, the limestones and sandstones are the water-bearing

units within the Clinton Group. These rock units contain both vertical

and bedding-plane joints. However, the Rochester Shale of the upper

Clinton is relatively impermeable and impedes recharge to the under-

lying, more permeable limestones and sandstones, thus making the Clinton

a less productive aquifer than the Lockport Group which lies above. The

Lockport Group, which underlies the site, is considered a primary source

of groundwater throughout the area. Three types of bedrock openings in

the Lockport Group contain the groundwater: bedding planes, vertical

fractures, and solution cavities.

The bedding planes, which transmit most of the water in the

Lockport Group, and vertical fractures have been widened by up to 1/8

inch by dissolution of the surrounding rock. These fractures extend

several miles, thus constituting effective water conduits.

The vertical joints of the Lockport Group are generally too short

and sparse to account for significant groundwater storage and transmis-

sion, except in the top 10 to 25 feet of bedrock (Oak Orchard Forma-

tion). Furthermore, solution cavities, formed when gypsum is dissolved,

are present, but are not important components of groundwater flow in the

aquifer. Although they increase the porosity of the rock, they are iso-

lated and do not contribute to groundwater transmission.

Overlying the Lockport Group is the upper Silurian Vernon Formation

of the Salina Group. This 300-foot-thick red shale serves as a con-

fining layer for the overlying, more permeable, unconsolidated deposits

found at the site. Interbedded shale and salt formations, the Syracuse

and Camillus, of the Salina Group contain numerous cavities formed by

dissolution of salt and gypsum and are very productive aquifers. These

formations, as well as the Bertie and Akron formations of the Salina

Group, are not present at the site. They can be located, however, in

close proximity to the south. The Akron and Bertie carbonate units

contain water in bedding joints widened by dissolution. Very little

groundwater is found in the Devonian formations above the Salina Group.

These formations, principally shale, are relatively impermeable. Some

water transmission occurs in small fractures in the bedrock, but no


wells of significant yield are found in these units. In central New

York, south of the site, groundwater is obtained mainly from glacial

overburden deposits.

The depth of the Precambrian basement, which underlies all of the

above-mentioned sedimentary units, increases f,rom approximately 2,000

feet at the northern border of Monroe County to nearly 4,000 feet at its

southern border (Broughton - et - al. 1966). There is only one well docu-

mented within the county that reaches the Precambrian.

The only noteworthy structure is a system of vertical to sub-

vertical joints that are pervasive throughout the sedimentary units

described above. In this region, the joints strike in numerous direc-

tions, thereby generally permitting bedrock to transmit groundwater flow

in the direction of the hydraulic gradient.

4.3 SITE GEOGRAPEIY

4.3.1 Topography

The Golden Road site is located in the Central Lowlands (Eastern

Lake section) Physiographic Province of the United States. This section

consists of the plains region, which is covered by a young blanket of

glacial till (Pirkle and Yoho 1977). The glacial deposits in the vicin-

ity of the site are uneven and undulating, resulting in well-developed

hilly areas with elevations up to 900 feet above mean sea level (AMSL)

(Sweet -- et al. 1938). .

The ground surface over the site is uneven, but generally flat-

lying. There are several mounds of foundry sand and other fill, and

several depressions containing ponds and wetlands. The fill areas are

generally 5 to 10 feet above natural grade. The site is located at an

elevation of approximately 560 feet AMSL (United States Geological

Survey [USGS] 1971).

The site is located in Zone C of the Flood Insurance Rate Map

(FIRM). The actual panel (Community Panel No. 3604120010A) prepared by

the Federal Emergency Management Agency (FEMA) for this area is not

printed because Zone C represents areas of minimal flooding.

4.3.2 Soils

Four soil types have been identified surrounding the landfill area

within the boundaries of the property. These soils are represented by

recycled paper ecology and envimnrnent

the Schoharie silty clay loam to the north of the railroad tracks,

Poygan silt loam to the north and south of the railroad tracks, Colwood

loam to the west of the fill areas, and Ontario loam to the north of the

Schoharie silty clay loam (Heffner and Goodman 1973; Sweet -- et al. 1938).

The Schoharie silty clay loam consists of a silty clay loam surface

layer with a dull Indian-red clay subsoil. The substratum consists of

alternating layers of red clay and sandy material. This soil is usually

found in nearly level areas, and exhibits a pH of 6.3 to 7.5 with depth.

The Poygan silt loam is slightly lighter brown in the surface soil

than Poygan silty clay loam, lighter in texture, and better drained.

The Poygan silty clay loam has a very coarse, granular surface soil.

This is underlain by a reddish-brown compact clay, followed by a compact

sandy till. This soil occupies low, less drained areas when associated

with Schoharie soil and exhibits a pH of 6.0 at the surface.

The Colwood loam consists of a granular loam of fine, light texture

at the surface, followed by a light-textured sandy soil. The subsoil

consists of sandy clay to fine sandy loam. The lower subsoil layer

ranges from a sandy clay to a fine sandy loam. These soils usually

occur in poorly-drained areas.

The Ontario loam consists of a friable, fine-textured loam with

some small irregular sandstone gravel at the surface, and is underlain

by a loam of light texture and loose friable consistency, also contain-

ing gravel. The subsoil is composed of a compact, very gravelly mate-

rial consisting of small rock fragments.

Soil borings at the Golden Road site (see Appendix D) generally

indicated the presence of fill material averaging 3 feet in thickness

and possibly as thick as 18 feet in the vicinity of GW-5. However,

recovery during split spooning at GW-5 was insufficient to verify the

depth of fill at that location (see Appendix I). This upper layer was

usually a silty, gravelly sand. The soils underlying the fill consisted

of various layers of silty sand, silty clay, and clay; followed by rock

fragments and silt overlying the bedrock. Geotechnical analyses were

performed on one sample from each well. The results of these analyses

are presented in Table 4-1 and Appendix E.

recycled paper ecology and rn*vnnmenc

4.4 SITE EiYDROGEOLOGY

The information used to develop the discussion in this subsection

includes the Phase I1 geophysical survey, seven monitoring well borings

and installations, USGS topographic maps (see Figure 1-I), geological

survey maps (see Figure 4-I), and regional groundwater reports.

The boring logs are included in Appendix D, and geotechnical

analysis results are presented in Appendix E.

4.4.1 Geology

Bedrock underlying the soils at the olden Road site varied in depth from 11.2 to 25 .4 feet below ground surface. Drill log informa-

tion is summarized in Table 4-2. The top of bedrock was shallowest

along the eastern border of the fill areas, and deepest in the western

portion of the southern section of the site. Top of bedrock dips to the

southwest. The seven boreholes did not penetrate the bedrock.

The bedrock underlying the soils at the Golden Road site is the

Lockport Dolomite of the Lockport Group. The formation is generally

brownish-gray in color, medium to thick bedded, stylolitic dolomite,

exhibiting parting (i.e., separations along planes), mineralized vugs,

and poorly preserved fossils (Tesmer 1981). Throughout its outcrop and

in the subsurface beneath the Devonian rocks, the Lockport maintains a

nearly uniform thickness of 200 feet. It is also known for its diver-

sity of mineral content (i.e., quartz, calcite, selenite and gypsum,

dolomite, sphalerite, galena, pyrite, and flourite). Although none of

the minerals has been used on a commercial scale, the rock itself is

quarried extensively for use as a crushed stone (Broughton -- et al. 1966).

4.4.2 Hydrology

Groundvater

In general, regional groundwater flow in Monroe County is to the

north toward Lake Ontario. The groundwater in Monroe County generally

flows to the Genesee River or to Irondequoit Bay, which both flow

northerly to northeasterly into Lake Ontario (Sweet - et - al. 1938).

Regional groundwater in the vicinity of the site likely flows east

toward the Genesee River or north to northwesterly toward the lake.


The terrain is variable across the site. From northeast to south-

west, the features include a highland area with a maximum elevation

above the landfill of approximately 25 feet, a low swampy area, the

raised northern landfill area containing a pipeline parallel to the

railroad tracks, a low railroad ditch, an elevated railroad track bed, a

low railroad ditch, the southern landfill area, a low swampy area, the

elevated Route 490 highway, a low swampy area, and a highland area with

a maximum elevation above the landfill of approximately 55 feet. Many

of the low areas were described as "wet with standing water" during

field observations. Topographic maps of the area (USGS 1971, 1978)

indicate possible drainage of these swampy areas is to the east and/or

west . The two landfill areas on site are large surface areas with a

maximum elevated relief of 8 feet above the low areas. They are

composed of a mixture of fill materials that include foundry sand

underlain by finer undisturbed overburden material consisting of silt,

clay, and some sand.

Seven groundwater monitoring wells were installed in the overburden

at the Golden Road site. Three wells were installed in the northern

section and four in the southern section. These wells were installed to

establish whether contamination is present and migrating off site. The

well locations are shown in Figure 3-2 and well construction data are

presented in Table 4-3. Appendix D contains the boring logs, and water

level data are shown in Table 4-4.

Groundwater encountered during drilling varied in depth from 7 to

15 feet below ground surface, or a relative site elevation of 340 to 333

feet. The groundwater levels in the completed wells varied in depth

from approximately 2.1 feet above ground surface to 5.2 feet below

ground surface or a relative site elevation of 347.9 to 345.25 feet.

This change in water levels between when the water-bearing zone was

first encountered and after well completion indicates an upward vertical

gradient. This upward gradient is caused by recharge to the aquifer

from an area of higher potential. When a monitoring well intercepts a

groundwater potential with a higher elevation than the elevation at

which water was encountered, groundwater will rise to the elevation of

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the intercepted potential in the well. In addition, a confining layer

may be present. According to the boring logs (see Appendix D), the

overburden materials are composed of predominantly silts and clays.

These fine-grained materials may confine or partially confine the

underlying coarser sandy silt and gravelly weathered bedrock zones in

some locat ions.

Groundwater may mound in the landfill areas due to the differences

in hydraulic conductivity between the fill, which is coarse and more

permeable, and the underlying undisturbed overburden, which is finer and

less permeable. Water flow, though the fill flows radially outwards,

acting as a recharge area, is to the surrounding lower topographic

areas. At this site, the lower areas consist of the swampy low lands

and the railroad bed and ditches. If it can be assumed that the swampy

conditions existed before the railroad bed was constructed, then the

placement of coarser fill on the tighter overburden may have caused the

coarser material to sink into the overburden over time and use. This

would then provide a more permeable east-west channel for the preferen-

tial flow of the groundwater from the fill and the swampy low areas.

This is only a hypothesis since all seven wells were screened below the

tighter overburden layer.

An 18-inch transit sanitary sewer line (cement/asbestos) trending

east-west is present north of and parallel to the railroad tracks (see

Figure 1-2). The sewer line is approximately 12 feet below ground sur-

face at the overburden-bedrock interface (Murphy 1991). The presence of

this line appears to impact groundwater flow in the undisturbed overbur-

den aquifer since a depression in the groundwater table was detected in

the wells in the vicinity of the pipeline. It is possible that hydrau-

lic communication can take place more readily between the fill and lower

overburden due to the disturbance of the overburden from the pipeline's

construction.

Route 490 may act as a small point of recharge to the groundwater

but this is difficult to determine without knowing the drainage systems

utilized or the details of construction. If the road has an impact on

the site, it would be in contributing to the surface water and sediment

samples taken between the south edge of the landfill and Route 490.

In summary, the Golden Road site may have a complex groundwater

flow pattern. The mounding of the upper groundwater flow system within

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4-9 e c ~ l o g y end environment

the fill may flow radially outward to the outer lowland areas, the

railroad bed, and possibly the sewer pipeline. The lower groundwater

system may be partially confined. The monitoring wells that were

screened in the lower groundwater flow system indicate groundwater flow

to the east or northeast, possibly converging in on and possibly

following a preferential flow along the sewer pipeline.

Surface Water

There are several surface water bodies located on the Golden Road

site. Drainage ditches exist on both sides of the Conrail tracks.

However, no flow was observed in these ditches during the field work.

Standing water is located in the central portion and along the western

and southern edges of the southern section of the site. These areas

appeared to be stagnant and swampy and flow direction could not be

determined. Little Black Creek is located approximately 1 mile north of

the site and Black Creek is located 2 miles south of the site.

Little Black Creek is a Class C stream from its mouth to 1,000 feet

above the Chili Avenue bridge, Class B to the Pixley Road bridge, and

Class C to its headwaters. Tributaries to Little Black Creek are both

Class B and C. Black Creek is Class C within a 3-mile radius of the

project area. All tributaries to Black Creek within a 3-mile radius of

the project area are Class C (Department of State 1983).

Best use for Class B waters is for primary contact recreation and

any other use except as a source of water supply for drinking, culinary,

or food processing purposes. The best use for Class C waters is for

fishing and all other uses except as a source of water supply for drink-

ing, culinary or food processing purposes, and primary-contact recrea-

tion (NYSDEC 1986).

4.5 SITE CONTAHINATION ASSESSWENT

Analytical' data for the site contamination assessment are presented

in Appendix F. For TCL organic compounds, all positive reported values

and qualifiers for samples, field QC samples, and laboratory MS/MSD

samples are presented on data summary forms. For TCL inorganics, CLP

Form 1's are included for all samples and field QC samples.

All CLP data packages were reviewed to determine whether qualified

data were acceptable for the intended use. In general, methylene .

recycled paper ecology and envimnrnrnt

chloride, acetone, 2-butanone, and phthalate compounds are considered to

be due to laboratory contamination and not evaluated if levels are less

than five times the detection limit, when the values are qualified with

a "B." In addition, hexane, which is also considered a laboratory con-

taminant, was often found in samples from the unknown compound search.

4.5.1 Subsurface Soil from Vell Borings

Only one subsurface soil sample was collected from one of the moni-

toring well borings (GW-7) and tested for TCL organics and inorganics.

No other samples were collected due to the lack of organic vapor read-

ings above background. Although this sample did not exhibit measurable

organic vapors with the instrumentation, it was collected at a depth

interval of 17 to 19 feet because of a discoloration and organic odor.

No organic compounds, PCBs/pesticides, or cyanide were detected;

however, magnesium was detected slightly above the common range of

metals in soils of the Eastern United States (see Tables 4-5 and 4-6).

4.5.2 Groundvater

Groundwater samples were collected from each of the seven new moni- 'CI. toring wells and analyzed for TCL organics and inorganics. Monitoring

wells GW-3 and GW-4 were considered upgradient and GW-1, GW-2, GW-5,

GW-6, and GW-7 were considered downgradient. Although GW-3 and GW-4 are

upgradient wells, they may be receiving water from the southern landfill

due to a mounding effect. Table 4-7 contains field measurements of

groundwater chemical parameters taken during well sampling.

Portions of the groundwater TCL organic data were qualified as un-

usable due to analytical problems caused by the lack of a re-extraction

during the initial sample analysis or re-extraction performed over 50

days beyond holding times, thus resulting in very low surrogate recov-

eries. The unusable data included the BNA results for GW-4, GW-5, GW-6,

and GW-7, and PCB/pesticide results for GW-2 and GW-6. In addition,

PCB/pesticide results for GW-1, GW-3, GW-5, and GW-7 should be consid-

ered biased low, These analytical results were not used to determine

the extent of contamination, however, the elimination of these results

has no effect on the HRS scoring because the metals results yielded the

maximum possible score. All metals and volatiles data are valid and

usable.

recycled paper rrology and environment

The groundwater and drill rig water results for TCL organic com-

pounds are summarized in Table 4-8. The groundwater contaminants were

generally limited to trace levels of volatile organic compounds detected

in GW-1, GW-6, and GW-7. Benzene detected in GW-1 and GW-6, ethylben-

zene in GW-1, and vinyl chloride, chloroethane, 1,l-dichloroethane, and

total-1,2-dichloroethene in GW-7 exceeded New York State drinking water

standards . Other petroleum-related volatiles such as toluene in GW-6 and total

xylenes in GW-1 and GW-6 were also detected, indicating a potential

petroleum contamination. The potential source of these contaminants in

GW-1 may be activities associated with the storage of Chili Fuels trucks

in the steel building to the west or the aboveground storage tanks

behind that building. Monitoring well GW-6 may be intercepting the same

petroleum plume as GW-1. Significant levels of chlorinated organic sol-

vents such as chloroethane and 1,l-dichloroethane were found in GW-7,

along with very low levels of tetrachloroethene and chlorobenzene in

GW-6.

Drill rig water was taken from a local fire hydrant on Golden Road

and placed in the drill rig water tank. The trihalomethanes detected in

the volatile fraction of the sample analysis are typical of potable

water sources using chlorination processes. The phthalate in the sample

may be a laboratory artifact.

The following metals exceed New York State Class GA groundwater

drinking water standards (see Table 4-9):

o Arsenic in the unfiltered portion of GW-1;

o Barium in the unfiltered portion of GW-2;

o Cadmium and chromium in the unfiltered portion of GW-1, GW-2, and GW-5;

o Copper in the unfiltered portion of GW-1 and GW-2;

o Iron in the. unfiltered portion of GW-4 and GW-5, and both the unfiltered and filtered portions of GW-1, GW-2, GW-3, GW-6, GW-7, and drill-rig water;

o Lead in the unfiltered portion of GW-1, GW-2, GW-5, and GW-6;

o Magnesium in both the unfiltered and filtered portions of GW-1 through GW-7;

recycled paper rrologv end rnvirnnrnent

o Manganese in the unfiltered portions of GW-2, GW-3, GW-5, and GW-6, and both the unfiltered and filtered portions of GV-1 and GI-7;

o Sodium in both the unfiltered and filtered portions of GW-1 through GW-7; and

o Zinc in the unfiltered portions of GW-1, GW-2, and GW-5.

No PCBs/pesticides or cyanide were detected in any of the ground-

water or drill water samples tested.

Groundwater was also sampled from two private drinking water wells

located on Golden Road. The samples were collected by the Monroe County

Department of Health (DOH) on October 30, 1990 and analyzed by the New

York State DOH. The samples were collected from the site owner's

(Fitzsimons) well located at 227 Golden Road and from the Hendrickson

well located at 240 Golden Road (across the street and to the north of

the site). Analytical results of these samples indicated no contami-

nants attributable to the site in the Hendrickson water sample and only

low levels (below the.NYSDEC Class GA drinking water standard) of tri-

chloroethene (TCE) in the Fitzsimons water sample. These sample results

are on file at the State and County DOH offices.

4.5.3 Surface Uater/Sediment

Twenty-two surface water/sediment samples were collected on and

adjacent to the Golden Road site. Fourteen on-site samples were ana-

lyzed for TCL organics and inorganics and eight off-site samples (along

the railroad drainage ditch) were analyzed for PCB/pesticides only.

Sample SW-13/SED-13 in the north central portion of the site was not

collected due to dry conditions.

Portions of the surface water TCL organic data were also qualified

as unusable due to the same analytical problems stated in Section 4.5.2.

The data include the BNA results for SW-1, SW-12, and SW-14, and PCB/-

pesticide results for SV-12. These analytical results cannot be used to

determine the extent of contamination. The elimination of the results

will have no effect on the HRS score because the metals and volatile

results yielded the maximum possible score. All metals and volatiles

data are valid and usable.

recycled paper ~ r o l u g y nnd rnvironment

The surface water results for TCL organic compounds are summarized

in Table 4-10. All surface water samples were free of contamination

with the exception of very low levels (below sample quantitation limits)

of benzene, toluene, and chlorobenzene in SW-7, toluene in SW-11, carbon

disulfide in SW-12, and total polynuclear aromatic hydrocarbons (PAHs)

in SW-1 and SW-9.

The following metals exceeded New York State Class C surface water

regulatory standards for the protection of aquatic life (see Table

4-11):

o Aluminum in SW-1 through SW-12, SW-14, and SW-15;

o Cadmium in SW-1, SW-7, and SW-9;

o Cobalt in SW-3;

o Copper in SW-1, SW-7, SW-9, and SW-10;

o Iron in SW-1 through SW-10, SW-12, SW-14, and SW-15;

o Lead in SW-1, SW-2, and SW-4 through SW-10;

o Nickel in SW-8;

o Selenium in SW-1, SW-2, SW-7, and SW-10;

o Vanadium in SW-I, SW-7, SW-9, and SW-10; and

o Zinc in SW-1, SW-2, SW-4 through SW-10, SW-14, and SW-15.

There are no standards for the protection of human life for Class C

surface waters. No PCBs or pesticides were detected in any of the sur-

face waters tested.

The sediment results for TCL organic compounds are summarized in

Table 4-5. In general, the sediments contained low levels of toluene

and varying levels of PAHs. The highest total PAH concentrations were

found in sediment samples SED-7, SED-8, SED-9, SED-10, and SED-11.

Other volatile organic compounds (i.e., carbon disulfide, chloromethane,

and 2-butanone) detected are possible laboratory artifacts.

Only two metals (chromium and nickel) exceeded the common range for

metals in soils in the Eastern United States in sample SED-8. Cyanide

was detected only in sample SED-2 (see Table 4-6).


No pesticides were detected in any of the sediment samples tested,

but a low level of PCB Aroclor-1254 was found in SED-8.

The eight off-site surface water and sediment samples (SW-16 to

SW-23) were collected at the request of NYSDEC after the site owner

reported that his neighbor may have dumped materials containing PCBs in

the ditches along the railroad tracks. These samples were collected and

analyzed at ASC for pesticides/PCBs. No pesticides/PCBs were detected

in any sample. Laboratory analytical results are presented in

Appendix F.

4.5.4 Surface Soil

Eleven surface soils were collected and analyzed for TCL organics

and inorganics. The surface soil results for TCL organic compounds are

summarized in Table 4-5. Samples S-1, S-7, S-9, and S-11 contained low

levels of chlorinated solvents such as total-1,2-dichloroethene and

tetrachloroethene with the highest concentrations present in S-1 and

- 1 1 Because of the low concentrations present and various minor ana-

lytical problems, the soil volatile results should be considered esti-

mates. Several soil samples also contained varying concentrations of

semivolatile organic compounds including phenol (S-3, S-5, S-8, S-10,

and S-11), n-nitrosodiphenylamine (S-1 and S-2), and PAHs (S-1 through

S-11) The highest concentrations of total PAHs were found in samples

S-2, S-3, and S-5. One PCB compound (Aroclor-1260) was detected at low

concentrations in samples S-1, S-2, and S-8. Most of the compounds

detected were low in concentration, and chloroform, hexane, and

phthalates are probably laboratory artifacts.

No metals exceeded common ranges for metals in soil in the Eastern

United States. Cyanide was detected only in sample S-2 (see Table 4-6).

No pesticides were detected in any of the surface soil samples

tested.

4.5.5 Waste

Three waste samples were collected and analyzed for TCL organics

and inorganics. Two of the waste samples consisted of foundry sand (W-1

and 1-2) and one was a resin-like substance from a partially buried drum

(W-3). The foundry sand contained the following organic compounds: low-

level PAH in W-1 and W-2; total-1,2,-dichloroethene in W-1; toluene in

recycled paper rrolugy and enrirc,nmrnc

W-1; and hexane in W-2. The resin-like substance (W-3) contained the

following organic compounds: total xylenes and total trimethyl-benzede

isomers (see Table 4-5). Host of the above-mentioned compounds are very

low in concentration (i.e., below sample quantitation limits), and some

(methylene chloride and hexane) are probably laboratory artifacts.

Several metals such as cobalt, iron, lead, and manganese in sample

W-3 were noticeably high.

No metals in the foundry sand samples (W-1 and W-2) exceeded the

common range of metals in soils in the Eastern United States (see Table

4-6). Hetals detected from waste sample W-3 are reported in Table 4-12.

Cyanide was not detected in any of the waste samples.

No PCBs or pesticides were detected in any of the waste samples

collected.

4.5.6 Leachate

Two samples were collected from areas of apparent leachate out-

breaks and analyzed for TCL organics and inorganics. One sample was

aqueous (L-1) and the other was stained soil/sediment (L-2). The

aqueous sample contained measurable concentrations of the chlorinated

organic compounds chloroethane and 1,l-dichloroethane. N,n-diethyl-

3-methylbenzamide was also identified to be present at low concentra-

tions (see Table 4-10). Only two organic compounds, chloroform and

dibenzofuran, were detected at very low concentrations in the stained

soil/sediment sample (see Table 4-5). Chloroform may be a laboratory

artifact.

Several inorganic elements in the aqueous sample exceeded New York

State human regulatory limits for surface water: arsenic, barium,

cadmium, iron, lead, magnesium, manganese, and zinc; and those that

exceeded aquatic regulatory limits include aluminum, cobalt, iron,

vanadium, and zinc (see Table 4-11). No inorganic elements exceeded

common ranges for metals in soils in the Eastern United States from the

leachate-stained soil/sediment sample.

No PCBs/pesticides or cyanide were detected in either leachate

sample.

recycled paper ecology and envimnrnen~

4.5.7 Contamination Assessment Summary

. Only one subsurface soil sample (GV-7 at 17 to 19 feet) was

collected at the Golden Road site. Analysis of this sample did not

indicate the presence of any organic contaminants. Only one metal

(manganese) exceeded the common range of metals in soils of the Eastern

United States from this sample.

The groundwater from the upgradient wells contained the following

chemical constituents at significant concentrations:

GW-3 (Background)

o Iron, magnesium, manganese, and sodium above drinking water standards in the unfiltered sample; and

o Iron, magnesium, and sodium in excess of drinking water standards in the filtered sample.

o Iron and sodium above drinking water standards in the unfiltered sample; and

o Sodium above drinking water standards in the filtered sample.

The groundwater from the downgradient wells contained the following

chemical constituents at significant concentrations:

GV- 1

o Benzene and ethylbenzene in excess of drinking water standards;

o Arsenic, cadmium, chromium, copper, iron, lead, magnesium, manganese, sodium, and zinc in excess of drinking water standards in the unfiltered sample; and

o Iron, magnesium, manganese, and sodium in excess of drinking water standards in the filtered sample.

o Barium, cadmium, chromium, copper, iron, lead, magnesium, manganese, sodium, and zinc above drinking water standards in the unfiltered sample; and

o Iron, magnesium, and sodium in excess of drinking water standards in the filtered sample.

recycled paper ecology and enrvonrnen~

o Cadmium, chromium, iron, lead, manganese, sodium, and zinc above drinking water standards in the unfiltered sample; and

o Sodium above drinking water standards in the filtered sample.

o Benzenes in excess of drinking water standards;

o Iron, lead, manganese, and sodium above drinking water standards in the unfiltered sample; and

o Iron and sodium above drinking water standards in the filtered sample.

o Vinyl chloride, chloroethane, 1,l-dichloroethane, and total-1,2-dichloroethane in excess of drinking water standards;

o Manganese and.sodium above drinking water standards in the i unfiltered sample; and . ,

\ o Manganese and sodium above drinking water standards in the

filtered sample. / - - I

Since both upgradient and downgradient wells and the drill water '\ contained iron in excess of drinking water standards, -------I ._ the source of the /

- .- - ---*I ,.iron \--. isprobably - - .- off s i t ~ High concentrations of manganese were also

--. ------5------- detected upgradient (GW-3), thereby indicating an off-site source. Very

low concentrations of 4-methyl-1,2-pentanone were detected in several of

the downgradient wells, along with one of the upgradient wells (GW-4),

thereby indicating a possible upgradient source also. All of the other

organic compounds and metals mentioned above, detected in the downgra-

dient wells, appear to have originated on site.

The surface waters tested were generally free from organic contami-

nants except-for very low concentrations of benzene, toluene, and chlo- ' ---. robenzene in 6 - 7 ; PAHs in SW-1 and SW-9; and toluene in SW-11. Samples

L- SW-7, SW-9, and SW-11 were from the drainage ditch along the south side

of the railroad tracks. All of the surface water samples contained

metals in excess of Class C surface water standards for the protection

recycled paper erolugy and mvironmrn~

of aquatic life. There are no standards for the protection of human

life in Class C surface waters. Aluminum, iron, and zinc are present

both upgradient and downgradient, indicating an off-site source, while

cadmium, cobalt, lead, magnesium, manganese, selenium, and vanadium seem

to be concentrated in the southeast portion of the site.

Organic constituents detected in the sediments associated with the

surface water samples consisted of mainly very low concentrations of

toluene in SED-1, SED-3, SED-4, SED-5, SED-7, SED-9, and SED-10, all in

the area to the south of the railroad tracks. Other organics detected

in this area include dibenzofuran in SED-8, SED-9, and SED-10, and

Aroclor-1254 in SED-8. Chloromethane and 2-butanone were detected near

the west border in the northern portion of the site; however, they are

often associated with background laboratory contamination. Only two

metals (chromium and nickel) exceeded common ranges of metals in soils

for the Eastern United States in sample SED-8. Cyanide was detected in

SED-2; however, there are no guidelines for this constituent.

Surface soil sample S-1, located to the east of the pond in the

southern portion of the site, and S-11, located in the open area in the

northwest portion of the site contained the most organic contaminants:

1,l-dichloroethane; total-1,2-dichloroethene; l,l,l-trichloroethane,

tetrachloroethene, toluene, n-nitro-sodiphenylamine, PAHs, and Aroclor-

1260; and total-1,2-dichloroethene, trichloroethene, tetrachloroethene,

toluene, and phenol, respectively. Phenols were also detected in

samples S-3, S-5, S-8, and S-10; n-nitrosodiphenylamine in S-2; 1,l-

dichloroethane in S-3, total-1,2-dichloroethene in S-7 and S-9; 1,1,1-

trichloroethene in S-3; and Aroclor-1260 in S-8. No metals exceeded the

common range of metals in soils of the Eastern United States. Cyanide

was detected in sample S-2; however, no guidelines exist for this

constituent.

The foundry sand waste samples (W-1 and W-2) contained very low

concentrations of total-1,2-dichloroethene and toluene, and the resin-

like waste (W-3) contained total xylenes and total-trimethyl-benzene

isomers. No metals in the foundry sand samples exceeded common ranges

of metals in soils of the Eastern United States; however, high levels of

iron, lead, and manganese were detected in the resin-like sample.


The aqueous leachate sample, L-1, contained chloroethane, 1,l-

dichloroethane, and very low concentrations of a few BNAs. The

leachate-stained soil/sediment sample, L-2, contained dibenzofuran.

Elevated levels of aluminum, arsenic, barium, cadmium, cobalt, iron,

lead, magnesium, manganese, vanadium, and zinc were detected in the

aqueous sample (L-1); but no metals exceeded common ranges for the

Eastern United States in the leachate-stained soil/sediment sample

(L-2).

In general, the groundwater, surface water, and surface soils

appear to have been contaminated by landfilling activities on both sides

of the railroad tracks. No pesticides were detected in any of the sam-

ples tested; PCBs were detected only in surface soil samples S-1, S-2,

and S-8, and sediment sample SW-8; cyanide was detected only in surface

soil sample S-2 and sediment sample SW-2. No PCBs/pesticides were

detected from the additional surface water/sediment from the railroad

drainage ditch requested by the on-site NYSDEC representative.

4 . 6 RECOHHFNDATIONS

Based upon the analytical results of subsurface soil, groundwater,

surface water/sediment, surface soil, waste, and leachate samples col-

lected at the Golden Road site, contamination of all the above mentioned

media was confirmed. Most of the organic contaminant levels were low;

however, metal concentrations in both the groundwater and surface water

exceeded drinking water standards. It is apparent that the contamina-

tion is originating on site. The question that remains is whether there

are contaminants on site that pose a significant threat to human health

and the environment. Since the drums removed from the site contained

chlorinated and nonchlorinated solvents, high total organic carbon,

organic solids with low flashpoints, PCBs, and waste oils, i t is possi-

ble that a major source of the on-site contaminants have been removed.

The partially buried drums that are still visible may contain additional

contamination and warrant further investigation. The data collected to

date are insufficient to make a definitive determination; thus, addi-

tional investigatory work is recommended for the immediate vicinity of

the buried drums. There is also the potential for buried live artillery

shells on site; therefore, an explosive ordnance specialist should be

recycled paper ecology and envvonmenc

consulted in order to determine the presence or absence of the shells.

The groundwater monitoring wells should also be tested for explosive

constituents. In addition, sampling of all downgradient private wells

in the vicinity of the site (i.e., along Golden Road) is recommended in

order to further determine the extent of groundwater contamination

migration.

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@IOAITORIUG WELL COCJSTRUCTIOU DATA

T h i c k n e s s o f T o t a l Depth S t i c k - u p F e e t o f S c r e e n F e e t o f B e n t o n i t e o f W e l l H e i g h t

Wel l Opening o r Open H o l e R i s e r ( f e e t ) ( f e e t ) ( f e e t )

GW- 1 s c r e e n 5 8 . 5 1 11.5 2

GW- 2 S c r e e n 5 8.0 1 11.0 2

GW- 3 S c r e e n 1 0 10.2 2 18.2 2

GW-4 S c r e e n 1 0 1 3 . 1 2 21.1 2

GW- 5 S c r e e n 1 0 16.5 2 2 4 . 5 2

GW- 6 s c r e e n 7 11.6 2 16.6 2

GW- 7 S c r e e n 7 12.2 2 17.2 2

0 2 [ U Z ] Y N 4 0 8 0 : D 2 8 3 3 / 2 8 9 2 / 1 5


Table 4-4

WATER LKVSL DATA

Relative F.levationsa (feet)

Water Level Below Ground Relative Relative Relative

Date Surf ace Elevatiog Grade Water Level Wall Measured (feet) at T.O.C. levat ti on' Elevation

+ 1 . 5 347.65 +l. 9 ( flowing)

GW- 4 2/7/90 3/8/91

GW- 5 2/7/90 3/8/91

lev at ions are not true elevations, but an on-site reference point (i.0.. a railroad spike in Rochester Gas and Electric Power Pole No. 13 with an assumed

belevation of 350.00 feet above mean sea level). T.O.C. = Top of steel casing.

'~rade elevations reported to the tenth of an inch only. +Water level measured wihin the well casing at an elevation above ground surface.

Note: Water levols ware measured to the nearest 0.01 foot using an electronic audible water level meter.

recycled paper P I . O ~ U ~ V and en-uonrnrnt

Table 4-5

SUBSURFACE SURFACE SOILS, SEDIIIEIUT, LEACHATE-STNKED SOIL/SEDIIQNT, NQD WASTE O R W I C AUALYSES 9-Y

Compound Detected Concentration

( ~ g / k g ) Sample

Volatile Organics

Chloroform

Trichloroethene

Tetrachloroethene

Toluene

Chloromethane 4 5 SED-14 Carbon disulfide 4 J . SED-14 1,l-Dichloroethane 8 4 S-1

5 5 S- 3 Total-1,2-dich1oroeth.n. 2 J S-1

2 J S-7 2 5 S-9 3 J S-9 MS 2 J S-9 MSD 9 s-11 6 5 S-11 RE 3 5 W- 1 2 J S-3 7 5 L- 2

92 SED-14 19 S-1 20 5-3 5 5 S-11 4 5 S-11 RE

12 s-1 3 5 S-11 1 J S-11 RE 2 5 S-1 9 S-11 4 5 S-11 RE 3 5 SED-1 6 5 SED-3 6 5 SED-4 5 5 SED-5 2 5 SED-6

13 SED-7 9 J SED-9 4 5 SED-9 RE 5 5 SED-10 3 5 W- 1

Hexane 5.5 J S-10 11 J S-11 9 J 5-11 RE

8.8 J W-2 RE Total xylenes 820 J W- 3

1,000 J W-3 MS 1,300 J W-3 MSD

Total trimethyl-benzene isomers 13,000 W- 3

0 2 [ U Z l Y N 4 0 8 0 : D 2 8 3 3 / 3 3 3 8 / 3 1

recycled paper

Key at end of table

ecology end rnvironrncnr

Table 4-5 (Cont.)


( r / q / k g ) Sample

Phenol

Dibenzofuran

Diethylphthalate N-Nitrosodiphenylamine

Butylbenzylphthalate

Total PAHs

S- 3 5-5 5-8 5-10 5-11 5ed-8 5ed-9 SED-10 L- 2 5-2 5-1 5-2 5-1 5-2 5-3 5-4 5-5 5-6 5-8 5-9 5-10 5-1 5-2 5-1 5-2 5-3 5-4 5-5 5-6 5-7 5-8 5-9 5-10 5-11 5ed-1 5ed-2 5ed-3 5ed-6 5ed-7 5ed-8 5ed-9 SED-10 SED-11 SED-11 MS SED-11 MSD L- 2 w- 1 w- 2

Key at end of table.

recycled paper ecology and rnvirunmrnt

Table 4-5 (Cont.)


(vg/kg) Sample

Key:

J r Estimated value for tentatively identified compounds or when mass spectral data indicate the presence of a compound that meets the identification criteria, but the result is 1 e s ~ than the sample quantitation limit but greater than zero.

MS = Matrix spike MSD = Matrix spike duplicate RE = Reanalysis due to unacceptable surrogate recoveries and/or

internal area responses.

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Table 4-7

Nephelometric Conductivity Turbidity !nits

Well D a t e Time PH Temperature OC (micromhos/cm) ( NTU I

GW- 1 2/7/90 0900 8.2 8.7 2,300 >1,000

GW-2 2/7/90 1115 7.9 6.5 3,005 >1,000

GW-3 2/7/90 1140 8.0 8.8 3,048 >1,000

GW- 4 2/7/90 1155 7.9 9.0 2,950 >1,000

GW- 5 2/7/90 1045 8.2 8.7 2,300 >1,000

GW- 7 2/6/90 1125 7.1 8.6 2,268 >1,000

[UZIYN408O:D2833/2894/17

he well water was clouded by silt during purging and sampling.

recycled paper eculogy and envimnmrn~

Table 4-8

QRO-TER DRILL WATER OROMIC AMLYSBS 5-Y

Concentration Compound Detected ( u9/L)

NYSDEC Class GA Groundwater s tandardsa

Sample ( u9/L

Volatile Organics

Vinyl chloride 9 J GW- 7 2

Chloroethane 17 GW- 7 5

Carbon disulfide 2 5 GW-6 5ob

1.1-Dichloroethane 3 6 GW- 7 5

1 J GW-6 8 GW- 7

Chloroform 24 Drill rig 100

Bromodichloromethane 11 Drill rig 50

Trichloroethene 2 J GW-6 5.0

Dibromochloromethane 4 5 Drill rig 50

Benzene GW- 1 GW- 6

3 5 GW- 1 3 5 GW-4 4 5 GW-5 7 5 GW-6 2 5 GW-6 MS 5 J GW-6 MSD

7 J GW-6 5 5 GW-6 HSD

Not detectable

Tetrachloroethene 2 5 GW-6 5

Toluene 2 5 GW-6 5

Chlo robenzene 1 J GW- 6 5

Ethylbenzene

Total xylenes

6 GW- 1 1 J GW-6

4 5 GW- 1 1 . 7 GW-6

Drill rig 5ob Drill rig MS Drill rig MSD

"source: NYSDEC, New York State Ambient Water Quality Standards and Guidance Values 1990.

b~~~~~~ Guidance value

Key:

J = Estimated value for tentatively identified compounds or when mass spectral data indicate the presence of a compound that meets the identification criteria, but the result is less than the sample quantitation limit but greater than zero.

HS = matrix spike MSD = matrix spike duplicate

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Table 4-9 (Cont.)

NYSDEC Class GA

Groundwater Inorganics Range in Samples standardsa Detected ( PQ/L) (Pq/L)

Sample Exceeding Standards or Guidance Values (pg/L)

Location Unfiltered Filtered

GW-1 GW- 2 GW- 5 GW-6

No regulatory standard 35,000 guidance value

GW- 1 GW- 2 GW-3 GW- 4 GW- 5 GW- 6 GW-7

Manganese ND - 1,030 300 500 (iron and manganese)

GW- 1 GW-2 GW- 3 GW- 5 GW-6 GW-7

~eccury ND - 0.28

Nickel ND - 205

Potassium 1,280 - 19,700

Sodium 11,800 - 71.600

No regulatory standard

No regulatory standard

20,000 GW- 1 GW- 2 GW- 3 GW- 4 GW- 5 GW-6 GW-7

Key at end of table.

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Compound Detected

NYSDEC class C Samples Concentration Surface Water standardsa Exceeding

(u9/L) Sample (ug/L Standards

Chloroethane 2 3 L- 1 50

Carbon disulfide 1 J SW-12 50

Benzene 1 J SW-7 6

Toluene

Chlorobenzene 1 J SW-7 5

14 J SW- 1 28 J SW- 9

'source: NYSDEC, New York State Ambient Watar Quality Standards and Guidance Values 1990.

b ~ ~ ~ b ~ ~ guidance value

Key:

J = Estimated value for tentatively identified compounds or when mass spectral data indicate the presence of a compound that meets the identification criteria, but the result is less than the sample quantitation limit but greater than zero.

RE = Reanalysis due to unacceptable surrogate recoveries and/or internal area responses.

recycled paper erolugy and rnvuc~nment

Table 4-11

SURFACE UATER AW LEACEATE IUORGMIC AEALYSES S-Y

Inorganic Range in Samples Detected ( Pg/L)

NYSDEC Class C Surface Water standardsa

I Pg/L )

Samples Exceeding Standards

Level Location (rg/L)

Aluminum 113 - 18,700 100 A

Arsenic ND - 164 190 (dissolved form) A

Barium 32.1 - 1,260 No regulatory standard

Beryllium ND - 3.0 B b

11 or 1 , 1 0 0 ~ A

Cadmium ND - 38.4 EXP (0.7852 [ln (ppm hardness)] - 3.490) Range of standard 1.85 - 6.92 A

Calcium 46,900 - 312,000 No regulatory standard

Chromium ND - 43.0 EXP (0,819 [ln (ppm hardness)] + 1.561) Range of standard 345 - 1,360 A

Cobalt ND - 13.1 B 5 A

SW-1 SW- 2 SW- 3 SW- 4 SW-5 SW-6 sw-7 SW-8 sw-9 SW- 10 SW-11 sw-12 SW-14 SW- 15 L-1

SW-1 sw- 7 SW-9 L- 1

Key at end of table

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Table 4-12

Inorganic Waste Detected ( vg/L)

Aluminum

Antimony N D

Arsenic ND

Barium 7.5 B

Beryllium ND

Cadmium ND

Calcium 3,710

Chromium 3 .O

Cobalt 162

Copper 2.4 B

Iron 778

Lead 3,430

Magnesium 1,670

Manganese 9,090

Mercury N D

Nickel N D

Potassium 336 B

selenium N D

Silver ND

sodi urn 1,240

Thallium N D

vanadium N D

Zinc 231

Cyanide N D

[ U Z l Y N 4 0 8 0 : D 2 8 3 3 / 3 3 4 6 / 4 6

Key:

B = Reported value is less than contract required detection limit but greater than the instrument detection limit.

N D = Not detected.

recycled paper ecology and ensironrnrnt

Thidvreaa System S-' (3roup Formation R o d ~ y p e in Feet Deecripllon

Figure 4-1 BEDROCK UNITS OF NORTHERN MONROE COUNTY

recycled paper ecology and rn~uironmrn~

-- __I__

+ Moniblng Well Sample

A Surfaca Soil Sample A S u b Waterlsedlment Sample

waste Sam* Leachatesampfe

-350- RelaUve Ground Surface ContwrIElevaUon (dashed where approximate)

0 75 150(Bet - Figure 4-2

GROUND SURFACE CONTOUR MAP

cow PASTUSE

I Relative Groundwater

Figure 4-3 OVERBURDEN GROUNDWATER CONTOUR MAP, MARCH 1990

5. FINAL APPLICATION OF HAZARD RANKING SYSTEH

5.1 NARRATIVE SCRMARY

The Golden Road disposal site is situated within an 8-acre parcel

of land on Golden Road in the Town of Chili, Monroe County, New York

(see Figure 5-1). The site is located at 227 Golden Road and is

bisected by active Conrail tracks. The site is currently owned by

Howard Fitzsimons, Jr., and was previously owned by Howard Fitzsimons,

Sr.

The site was active from 1955 through 1976, receiving a wide

variety of wastes including U.S. Army artillery shell casings, 55-gallon

drums of unknown wastes, household refuse, metal slag, fly ash, and

junked vehicles. The majority of the material used for fill was foundry

sand. Approximately 560 drums were removed in 1985. The drums con-

tained chlorinated and nonchlorinated solvents, high total organic

carbon, organic solids with low flashpoints, PCBs, and waste oils.

Large pieces of structural steel, fuel tanks, and partially buried drums

currently lie on site.

According to tests conducted by E & E, groundwater, surface water/

sediment, and surface soils are contaminated with low levels of organic

compounds and high levels of metals. No pesticides were detected in any

of the samples tested; however, PCBs were detected in one sediment sam-

ple and three surface soil samples. Cyanide was detected in one sedi-

ment sample and one surface soil sample.

Approximately 5,352 people live within a l-mile radius of the site

and are potentially affected by direct contact due to lack of security

(i.e., fences), especially to the south of the railroad tracks, and

surface water and soil contamination. All residences within a l-mile

radius of the site are within the local municipal water service area;

recycled paper rc.t~logy and m*vonmenc

however, residents (i.e., the site owners) are still known to be using

private groundwater wells as their only source of drinking water. An

exact number of people drinking groundwater within 1 mile of the site

could not be obtained but is suspected to be low.

recycled paper

Spencerport, NY , 1971 ; All ( ~ h o r o r w i d - 1 9 7 8 ) . SCALE 124,04)

0 w - .S 1 Milo - .I

0 .S 1 Klbmtw t+ - - I

recycled paper

Figure 5-1 LOCATION MAP: GOLDEN ROAD DISPOSAL SITE

5-3 ecology and environment

FIGURE 1

H R S C O V E R S H E E T

facility Name: Golden Road Disposal Site

.ocation: 227 Golden Road, Chili, NY 14625

IPA Region:

'ersonls) in Charge of Facility: Howard Fitzsimons, Jr.

ame of Reviewer: G. Florentino Date: 6/26/90

eneral Description of the Facility:

For example: landfill, surface impoundment, pile, container: types of hazardous substances: ocation of the facility; contamination route of major concern: types of information needed for ating: agency action: etc.)

The Golden Road disposal site is an 8-acre, inactive landfill which contains U.S. Army artillery shells, household refuse, metal slag, fly ash, foundry sand, junked vehicles, and partially buried 55-gallon drums which may contain solvents and/or ink wastes. The site is located in a residential area. The soil surface water and groundwater contamination is of major concern.

S = not scored FE

recycled paper 5-4 ecology end entironmeni

FIGURE 2 GROUND WATER ROUTE WORK SHEET

b

Ground Water Route Work Sheet

recycled paper

Ratlng Factor

rcology and environment

Assigned Value (Circle One) pller

Observed Release 0 0 1 4 5 43 3.1

M u . Score

If observed release Is glven a score of 45. proceed to Ilm m. If observed release Is glven a score of 0, proceed to Ilne a. .

Roub Characterlstlcs 3.2 Depth to Aquifer of 0 1 2 0 2 6 0 Concern

Net Preclpltatlon 0 0 2 3 1 1 3 Permeability of the 0 1 0 3 1 2 3 Unsaturated Zone

~ h y s ~ c a ~ State o 1 2 0 1 3 3

Ref. (Section)

Total ~ o b t e Characterlstlcs Score

Contalnment 0 1 2 0 1

11

3

Waste Chancteristlcs - 3.4 T oxlclty IPerslstence 0 3 8 91215@ t 18 18 Hazardous Waste 0 1 2 3 @ 5 8 7 8 1 4 8 Quantlty

I

15

3

Total Wale Chrracterlstlcs Score

3.3

22 29

fargets 3.5- Ground Water Use 0 1 0 3 3 6 9 Dlatance to Nearwt 0 4 6 1 20 40 ) 12 1. 18 Well 1 Populatlon Served 24 30 32 40

I Total Targets Score

E! 11 line is 4s. multlpc x x I f line is 0. multiply x x x

DIvide llne by 57.330 and multiply by 1W sgw- 44.89

26

25 74c

49

57,330 I I

I Surface Water Route Work Sheet

Ratlng Factor Asslgned Value Multl- Max. Ref.

(Circle One) pller r I Observed Release

It observed release Is glven a value of 45. proceed to Ilne m. It observed release Is ~ I v e n a value of 0, proced to Ilne

Route Chancteristlcs 4.2 Faclllty Slope and Intervening 0 1 2 @) Terrain

l-yr. 2Chr. Ralnfall 0 1 0 3 Distance to Nearest Surface 0 1 2 @ Water

~ h y s r u r state o 1 2 0

I I

I - Toxlclty 1 Persistence 0 3 0 9 1 2 1 5 @ 1 18 18 Hazardous Waste 0 1 2 3 @ 5 0 7 8 1 4 a

Total Rcute Chamcterlstlcs Score

a ~ontalnment 0 1 2 0 1

Surface Water Use 0 1 0 3 3 6 9 Distance to a Sensltlve 0 1 2 0 2 6 0 Environment

Population Served1 Olstance 1 0 40 to Water Intake Downstream 24 30 32 35 40

1 4 .

Waste Chancterlstlcs 4.4

3

15

a Total Waste Characterlstlcs Score

- -- 1 Dlvide l i n e - ~ by m . m and multiply 4 im

3

22

Total Targets Score

FIGURE 7 SURFACE WATER ROUTE WORK SHEET

4.3

recycled paper

12

erolugy and r n v k ~ n m e n t

SS

FIGURE 9 AIR ROUTE WORK SHEET

Alr Route Work Sheet

, recycled paper

Ratlng Factor

ecology end mvhnment

Asslgned Value [Circle One) ( pller

Observed Release @ 45 1

Max. Score

0

Met. [Section)

4s 5.1 - Date and Location: PI/ A

Smpllng Protocol: N/ A

If llne Is 0, the S, - 0. Enter on llne . If llne la 45, then proceed to Ilna .

Waste Characterlstlcs 5.2 Reactivity and 0 0 2 3 1 1 3 Incornpatlblllty

Toxlclty 0 0 2 3 3 3 9 Hazardous Waste 0 1 2 3 @ 5 8 7 8 1 4 8 Quantlty

TOW Waste Chancterlstlcs Score 8 20

Targets 5.3 Population Wlthln 0 9 12 15 18 21 30 CMIIe Radlus

Dlstance to Sensltlva 0 1 2 0 2 6 6 Environment

Land Use 0 1 2 0 1 3 3

Total Targets Score

Multlply x x •

Ohlde line by 3S.lW and rnultlply by 100 s a - 0

30

O

39

35.100

Groundwter Route Scnre (SOW)

Sudace Water Route Score (SSw)

Air Route Score (Sa)

/-11-73 S ~ w - S w -

FIGURE 10 WORKSHEET FOR COMPUTING SM

recycled paper ecology end mbironment

FIGURE 11 FIRE AND EXPLOSION WORK SHEET

Fire urd Explosion Work Sheet

recycled paper ecology and environrnen~

Rating Factor Max. score

3

Ref. (~ectlon)

7.1 Containment 1 3 1

Asslgned Value (Clrcle One)

Waste Cham~terlstlcs 7.2 Dlrect Evldence 0 3 1 3 lqnltablllty 0 1 2 3 1 3 Reactivity 0 1 2 3 1 3 lncompatlblllty 0 1 2 3 1 3 Hazardous Waste 0 1 2 3 4 5 6 7 8 1 8 Quantlty

I

Multl- plier

Total Waste Characteriatlca Score 20

fargets 7.3 Dlstance to Nearest 0 1 2 3 4 5 1 S PopulaUon

Dlstawe to Nearest 0 1 2 3 1 . 3 Buildlng

Dlstance to Sensitive . O f 2 3 1 3 Envlronment

Land Use 0 1 2 3 1 3 Population Wlthln 0 1 2 3 4 5 1 S 2-Mile Radlua

Bulldlngs Wlthln 0 1 2 3 4 5 1 S 2-Mlle Radlus

Total Targats Score

Multiply x x

24

1,440

Ohlde llna 4 1.14) and rnultlpfy by 100 SFE - Not scored

- -

FIGURE 12 DIRECT CONTACT WORK SHEET

- Olrect Contact Work Sheet

recycled paper

Rrtlng F d o r

rrt~lopy and rntironrnen~

Ass~gned Value (Circle One) 1 pller

a Observed Incldent @ 45 1

Max. Score

0

Ret. (Jectlon)

"

8.1

If llno a I8 45. proceed to llne a llno Ir 0, proceeci to line

a AccesrIDYlty 0 1 2 0 1

a Containment 0 0 1

Waste Chuacterlsllcr Toxlclty 0 1 2 0 S

3

15

15

l u g e t o 8.5 Populrtlon Wlthln 1 0 1 2 3 0 5 4 16 20 1-MI18 W l u r

D l s l ~ c e to r @ 1 2 3 . 4 0 12 C r l t l d Hrbltrt

3

15

15

Tots Tugetr Score

If llno a ir 45, multlpty a x x a line is 0. multiply r x x @

8.2

8.3

8.4

Divide llno a by 21,600 and multiply by 103 SOC ' 50

-16

..0,800

32

21.600

D O C U M E n T A T I O n R E C O R D S

~nstructions: As briefly as possible summarize the information you used to assign the score for each factor (e.g., "Waste quantity = 4,320 drums plus 80 cubic yards of sludges"). The source of information should be provided for each entry and should be a bibliographic-type reference. Include the location of the document.

Facility Name: Golden Road Disposal Site

Location: 227 Golden Road, Town of chili, NY

Date Scored: 7/3/90

Person Scoring: G . Florentino

Primary Source(s) of Information (e.g., EPA region, state, FIT, etc.):

Ref. 1. 5, 6 . 7

Factors Not Scored Due to Insufficient Information:

Comments or Qualifications:

5-11 recycled paper ecology end envimnrnen~

O R O U R D W A T E R R O U T E

1. OBSERVED RELEASE

Contaminants detected ( 3 maximum):

Total lead, benzene 1,l-dichloroethane Score = 45 Ref. 1

Rationale for attributing the contaminants to the facility:

Groundwater samples collected from on-site wells Ref. 1

2. ROUTE CHARACTERISTICS

Depth to Aquifer of Concern

Name/description of aquifer(s) of concern:

Lockport Group Ref. 2 and 3

Depth(s) from the ground surface to the highest seasonal level of the saturated zone [water table(s) 1 of the aquifer of concern:

The shallowest water level encountered during drilling was 3.0 feet in GW-2. Water levels rose in the completed wells to 2.1 feet above ground surface in GW-4. Ref. 1

Depth from the ground surface to the lowest point of waste disposal/storage:

<20 feet Assigned value = 3

Net Precipitation

Mean annual or seasonal precipitation (list months for seasonal):

32 inches Ref. 4

Mean annual or seasonal evaporation (list months for seasonal):

27 inches Ref. 4

Net precipitation (subtract the above figures):

5 inches Assigned value = 1

recycled paper ecology and mvimnmrn~

Permeability of Unsaturated Zone

Soil type in unsaturated zone:

Silty sand, sometimes silty clay Ref. 2 and 3

Permeability associated with soil type:

0.63 - 2.0 inches per hour Ref. 2 and 3

Physical State

physical state of substances at time of disposal (or at present time for generated gases):

Solids: Artillery shells, foundry sand/fly ash, household refuse Liquids: ,560 55-gallon drums Ref. 5 and 6

3. CONTAINMENT

Containment

Method(s) of waste or leachate containment evaluated:

Landfill - no liner, no cap

Method with highest score:

See above Assigned value = 3 Ref. 5 and 6

*c 4. WASTE CHARACTERISTICS

Toxicity and Persistence

Compound(s) evaluated:

Total lead 1.1-dichloroethane Benzene Ref. 1 and 7

Assigned value = 18 Assigned value = 12 Assigned value = 12

Compound with highest score:

Total lead Note: Dissolved lead was not detected, therefore an alternative score would be 12 Assigned value = 18 for benzene. Ref. 7

Hazardous Waste Quantity

Total quantity of hazardous substances at the facility, excluding those with a containment score of 0. (Give a reasonable estimate even if quantity is above maximum.):

560 drums were removed from the site and several still remained partially, and possibly, buried. (Note: Other waste present on site in unknown quantities) Ref. 5 and 6

Basis of estimating and/or computing waste quantity:

560 drums removed from site (Note: This is a minimal waste value) Ref. 5 and 6


5. TARGETS

Groundwater Use

Use(s) of aquifer(s) of concern within a 3-mile radius of the facility:

Drinking water with municipal water from alternate unthreatened sources presently available. Assigned value = 2 Ref. 5

Distance to Nearest Well

Location of nearest well drawing from aquifer of concern or occupied building not served by a public water supply:

Mr. Howard Fitzsimons 227 Golden Road Ref. 1, 5, and 19

Distance to above well or building:

Adjacent to fill Assigned value = 4 Ref. 1, 5, and 19

Population Served by Groundwater Wells Within a 3-Mile Radius

Identified water-supply well(s) drawing from aquifer(s) of concern within a 3-mile radius and populations served by each:

Average of 14.1 wells per square mile in Town of Chili. 9.4 sq. miles x 14.1 wells/sq. mile x 3.8 people/well = 504 people Ref. 5 and 8

Computation of land area irrigated by supply well(s) drawing from radius, and conversion to population (1.5 people per acre):

300 acres x 1.5 = 450 people Ref. 5

Total population served by groundwater within a 3-mile radius:

504 + 450 = 954 Assigned value = 2

within a 3-mile

recycled paper ecology and en~vonrnent

1. OBSERVED RELEASE

Contaminants detected in surface water at the facility or downhill from it ( 5 maximum):

Cadmium Toluene Lead Manganese Benzene Score = 45 Ref. 1

Rationale for attributing the contaminants to the facility:

Samples collected from on-site or adjacent surface water Ref. 1

2. ROUTE CHARACTERISTICS

Facility Slope and Intervening Terrain

Average slope of facility in percent:

0 - 3% Ref. 1, 5, 10, 11, 12, and 13

Name/description of nearest downslope surface water:

Unnamed pond and wetlands on and adjacent to site Ref. 1 and 5

Average slope of terrain between facility and above-cited surface water body in percent:

0 - 3% Ref. 1, 5, 10, 11, 12, and 13

Is the facility located either totally or partially in surface water?

yes ~ e f . 1, 5, 10, 11, 12, and 13

Is the facility completely surrounded by areas of higher elevation?

NO Assigned value = 3 Ref. 1, 5, 10, 11, 12, and 13

1-Year 24-Hour Rainfall in Inches

2.2 Assigned value = 2 Ref. 14

Distance to Nearest Downslope Surface Water

Adjacent Assigned value = 3

b e Ref. 1 and 5

5-15

recycled paper ecology and rnvironrnrnt

Physical State of Waste

Solids: Artillery shells, foundry sand/fly ash, household refuse Liquids: >560 55-gallon drums Assigned value = 3

b F Ref. 5. and 19

3. CONTAINMENT

Containment

Method(s1 of waste or leachate containment evaluated:

Landfill - no liner, no cap

Method with highest score:

Same as above Assigned value = 3 Ref. 5

4. WASTE CHARACTERISTICS

Toxicity and Persistence

Compoundls) evaluated:

Cadmium Assigned value = 18 Lead Assigned value = 18 Manganese Assigned value = 18 Benzene Assigned value = 12 Toluene Assigned value = 9 Ref. 1 and 7


L Cadmium Assigned value = 18 Ref. 7


Total quantity of hazardous substances at the facility, excluding those with a containment score of 0. (Give a reasonable estimate even if.quantity is above maximum.):

560 drums removed from site. Other drums exist partially or completely buried. Other wastes exist on site in unknown quantities Ref. 6


560 drums were removed (Note: This is a minimal waste value) Assigned value = 4 Ref. 7

t

5 . TARGETS

Surface Water Use

Use(s) of surface watar within 3 miles downstream of the hazardous substance:

unknown, possibly recreation. No intakes in area. Assigned value = 2 Ref. 5 . 10, 11, 12, and 13

recycled paper rculugy end rn-irunmcn~

Is there tidal influence?

NO Ref. 15

Distance to a sensitive Environment

Distance to 5-acre (minimum) coastal wetland, if 2 miles or less:

None Ref. 15

Distance to 5-acre (minimum) fresh-water wetland, if 1 mile or less:

Site adjacent to designated Class I1 wetland Assigned value = 3 Ref. 5

Distance to critical habitat of an endangered species or national wildlife refuge, if 1 mile or 1.6s:

None Assigned value = 0 Ref. 5

Population Served by Surface Water

Location(s) of water-supply intake(s) within 3 miles (free-flowing bodies) or 1 mile (static water bodies) downstream of the hazardous substance and population served by each intake:


Computation of land area irrigated by above-cited intake(s) and conversion to population (1.5 people per acre) :

None Ref. 5

Total population served:

None Ref. 5

Name/description of nearest of above water bodies:

None Ref. 5

Distance to above-cited.intakes, measured in stream miles:

None Ref. 5

5-17 recycled paper rrulogy and envirrmment

A I R R O U T E

-1. OBSERVED RELEASE

Contaminants detected:

Air samples were not collected and tested. The site was screened with an HNu photoionization detector. No contaminants were detected. Assigned value = 0 Ref. 1

Date and location of detection of contaminants:

Methods used to detect the contaminants:

Rationale for attributing the contaminants to the site:


Reactivity and Incompatibility

Most reactive compound:

Not sampled, unknown Assigned value = 1 Ref. 1 and 5

Most incompatible pair of compounds:

Unknown Assigned value = 1 Ref. 7

Toxicity

Most toxic compound:

Unknown Assigned value = 1


Total quantity of hazardous waste:

5 6 0 drums Ref. 6


9 6 0 drums removed (waste quantity is a minimal value because other wastes were disposed on site) Ref. 1, 5 , and 6

recycled paper eculvgy and cnvironmen~

3. TARGETS

Population Within 4-Mile Radius

Circle radius used, give population, and indicate how determined:

0 to 4 mi 0 to 1 mi 0 to 1/2 mi 0 to 1/4 mi 0 0-1 miles 5,352 Assigned value = 21 Ref. 16

Distance to a Sensitive Environment

Distance to 5-acre (minimum) coastal wetland, if 2 miles or less:

None Ref. 15

Distance to 5-acre (minimum) fresh-water wetland, if 1 mile or less:

Site adjacent to designated Class 11 wetland Assigned value = 3 Ref. 5

Distance to critical habitat of an endangered species, if 1 mile or less:


Land Use

Distance to commercial/industrial area, if 1 mile or less:

1 mile Assigned value = 3 Ref. 10, 11, 12, 13, and 17

Distance to national or state park, forest, wildlife reserve, if 2 miles or less:

None Assigned value = 0 Ref. 10, 11, 12, and 13

Distance to residential area, if 2 miles or less:

Adjacent Assigned value = 3 Ref. 10, 11, 12, 13, and 17

Distance to agricultural land in production within past 5 years, if 1 mile or less:

~ 0 . 2 5 mile Assigned value = 3 Ref. 17

Distance to prime agricultural land in production within past 5 years, if 2 miles or less:

~ 0 . 2 5 mile Assigned value = 3 Ref. 17

Is a historic or landmark site (National Register of Historic Places and National Natural Landmarks) within the view of the site?


C

recycled paper rcolugy end rnrin~nment

F I R E A R D E X P L O S I O R

-1. CONTAINMENT

Hazardous substances present:

No fire hazard at site. Ref. 18

Type of containment, if applicable:


Direct Evidence

Type of instrument and measurements:

No readings with 02/explosimeter Assigned value = 0 Ref. 1

Ignitability

Compound used:


Reactivity

~ o s t reactive compound:


Incompatibility

~ o s t incompatible pair of compounds:



Total quantity of hazardous substances at the facility:

560 drums Ref. 6


560 drums removed (Note: Waste quantity is a minimum value due to the disposal of other unknown quantities of waste)

Ref. 5 and 6


3. TARGETS

Distance to Nearest Population

Adjacent Assigned value = 5

'Ir' Ref. 1,' 5, 10, 11, 12, and 13

Distance to Nearest Buildinq

Adjacent Assigned value = 3 Ref. 1, 5 , 10, 11, 12, and 13

Distance to a Sensitive Environment

Distance to wetlands:

Adjacent Assigned value = 3 Ref. 5 , 10, 11, 12, and 13

Distance to critical habitat:


Land Use

Distance to commercial/industrial area, if 1 mile or less:

1.0 mile Assigned value = 3 Ref. 17

Distance to national or state park, forest, or wildlife reserve, if 2 miles or less:

None Assigned value = 0

'Ir. Ref. 10, 11, 12, and 13

Distance to residential area, if 2 miles or less:

Adjacent Assigned value = 3 Ref. 10, 11, 12, 13, and 17

Distance to agricultural land in production within past 5 years, if 1 mile or less:

( 0 . 2 5 miles Assigned value = 3 Ref. 17

Distance to prime agricultural land in production within past 5 years, if 2 miles or less:

t 0 . 2 5 miles Assigned value = 3 Ref. 17

Is a historic or landmark site (National Register of Historic Places and National Natural Landmarks) within the view of the site?


Population Within 2-Mile Radius

19,439 Assigned value = 5 Ref. 16

Buildings Within 2-Nile Radius

'L > 700 Assigned value = 3 Ref. 10, 11, 12, and 13

recycled paper

5- 2 1 crolo(ey and envimnrnent

- - - - - - --

D I R E C T C O U T A C T

OBSERVED INCIDENT

Date, location, and pertinent details of incident:

No incidents on record. Ref. 5

* * * 2. ACCESSIBILITY

Describe type of barrier(s):

Barriers do not completely surround the facility. Assigned value = 3

3. CONTAINMENT

Type of containment, if applicable:

No containment. Foundry sand/fly ash at surface. Assigned value = 15 Ref. 1, 5, and 19


Toxicity

Compounds evaluated:

Benzene Assigned value = 3 Toluene Assigned value a 2 Ref. 1 and 7


Benzene Assigned value = 3 Ref. 7

t t *

5. TARGETS

Population Within One-Mile Radius

5,352 Assigned value = 4 Ref. 16

Distance to Critical Habitat (of endanqered species)


recycled paper ecology and e n \ v o n m e n ~

If the entire reference is not available for public review in the EPA regional files on this site, indicate where the reference may be found.

Reference Number Description Of the Reference

Ecology and Environment Engineering, P.C., April 26, 1989, Site Inspection of the Golden Road Disposal Site, Town of Chili, New York,.performed for the New York State Department of Environmental Conservation, Albany, New York.

Sweet, A.T., W.J. Latimer, C.S. Pearson, C.H. Diebold, W.W. Riete, C.P. Mead, W. Secor, and M. Howard, Jr., 1938, Soil Survey of Monroe County, New York, United States Depart- ment of Agriculture, Soil Conservation Service, Cornell, New York. Document location: Ecology and Environment Engineering, P.C., Buffalo, New York.

Heffner, R.L., S.D. Goodman, 1973, Soil Survey of Monroe County, New York, United States Department of Agriculture, Soil Conservation Service, Cornell, New York. Document location: Ecology and Environment Engineering, P.C., Buffalo, New York.

National Oceanic and Atmospheric Administration, 1983, Climatic Atlas of the United States, Reprinted from United States Department of Commerce, Environmental Science Services Administration, Environmental Data Service, 1968, National Climatic Data Center, Asheville, North Carolina. Document location: Ecology and Environment Engineering, P.C., Buffalo, New York.

New York State Department of Environmental Conservation, November 28, 1983, Golden Road Disposal Site, New York State Superfund Phase I Summary Report, Town of Chili, Monroe County, New York, prepared by Recra Research, Inc. Document location: NYSDEC, Albany, New York.

Jackson, D., July 25, 1983, Sampling Report, Golden Road Disposal Site, Site No. 8-28-021, New York State Department of Environmental Conservation, Division of Solid and Hazardous Waste, Region 8, Albany, New York. Document location: Ecology and Environ- ment Engineering, P.C., Lancaster, New York.

Uncontrolled Hazardous Waste Site Ranking Systems, A Users Manual, National Oil and Hazardous Substances, Contingency Plan, Appendix A (40 CFR) (47 FR 31219), July 16, 1982. Document location: Ecology and Environment Engineering, P.C., Buffalo, New York.

Chudyk, S., July 3, 1990, personal communication, Highway Superintendent, Town of Chili, New York. Document location: Ecology and Environment Engineering, P.C., Buffalo, New York.

National Conference of State Historic Preservation Officers, National Park Service, and American Assoication for State and Local History, 1989, National Register of Historic Places 1966-1988, American Association for State and Local History, Nashville, Tennes- see. Document location: Ecology and Environment Engineering, P.C., Buffalo, New York

United States Geological Survey, 1971, Clifton, New York Quadrangle, Monroe County, New York, 7.5-Minute Series (Topographic), Washington, D.C. Document location: Ecology and Environment Engineering, P.C., Buffalo, New York.


Reference Number Description of the Reference

, 1978, Rochester West, New York Quadrangle, Photorevised from 1971, Monroe County, New York, 7.5-Minute Series (Topographic), Washington, D.C.

, 1978, Spencerport, New York Quadrangle, Photorevised from 1971, Monroe county, New York, 7.5-Minute Series (Topographic), Washington, D.C.

, 1978, West Henrietta, New York Quadrangle, Photorevised from 1971, Monroe County, New York, 7.5-Minute Series (Topographic), Washington, D.C.

Hershfield, D., 1963, Rainfall Frequency from 30 minutes to 24 hours and Return Periods from 1 to 10 years, Technical Paper No. 40, prepared for United States Department of Agriculture, Soil Conservation Service, Washington, D.C. Document location: Ecology and Environment Engineering, P.C., Buffalo, New York.

Kirsch, K., April 11, 1990, personal communication, New York State Department of Environmental Conservaiton, Wetlands Section, Avon, New York. Document location: Ecology and Environment Engineering, P.C., Buffalo, New York.

General Sciences Corporation, 1987, Graphical Exposure Modeling System Users Guide, Volume I: Core Manual, United States Environmental Protection Agency, Washington, D.C.

Monroe County Department of Planning, 1988, Existing Land Use Map 1 Environmental Planning Atlas, Rochester, New York.

Christian, J., July 5, 1990, personal communication, Fire Marshall, Town of Chili, Chili, New York. Document location: Ecology and Environment Engineering, P.C., Buffalo, New York.

19 Pitzsimons, L., January 21, 1991, personal communication, Golden Road Disposal Site owner, Chili, New York. Document location: Ecology and Environment Engineering, P.C., Buffalo, New York.

02[UZlYN48O:D2833/6639


recycled paper ecology and rnvironment

ENGINEERING INVESTIGATIONS AT w INACTIVE HAZARDOUS WASTE SITES

IN THE STATE OF NEW YORK

PHASE II INVESTIGATIONS

Golden Road Disposal Site Site No. 828021

Town of Chili, Monroe County

August 1990 Volume I

Prepared for:


50 Wolf Road, Albany, New York 12233 Thomas C. Jorling, Commissioner

Division of Hazardous Waste Remediation Michael J. O'Toole, Jr., P E., Director

Prepared by:

Ecology and Environment Engineering, P.C. 5-26

recycled paper crology and environment

REFERENCE 2

recycled paper ecology and msimnrnent

. . : . ; .:...;. . - *:;rJ.'.. recycled paper eco1og.y and ~nviron$en~ . ' ",' ' ' ' ' *.

, ,. . . ., .. . . . .. ' *Y . . ,.,,..f:-?j;-; _ . ...a 1 * . - ..

REFERENCE 3


S U R V E Y

Monroe County New York

UNITED STATES DEPARTMENT OF AGRICULTURE Soil Conservation Service

In cooperation with

CORNELL UNIVERSITY AGFUCULTURAL EXPERIMENT STATION Ieued March 1973 d

recycled paper rcolug~ and environment

SOIL SURVEY OF MONROE COUNTY, NEW YORK By ROBERT L. HEFFNER AND SEYhlOUR D. COOD31AS. SOlL CONSERVATION SERVICE

SOILS SURVEYED BY ROBERT L. HEFFNER, SEYBIOVR D. GOODll lAS, BRADFORD A. HIGGINS. AND TROY D. YOAKUBl, SOlL CONSERVATION SERVICE

UNITED STATES DEPARThlENT OF A(;ItICULTURE. SOIL COSSERS.ATION SEIIVIC'E. IN COOPE11ATlON WITH T H E CORNELL UNIVERSITY ACRICCLTCRAL EKPERlllIENT STATION

M ONliOli: COUhT'l'k- is i l l t l ~ e Kr ic-O~~tnr io I ~ l i c l ' l n i~~ 3t:ltc l'i11.1;. ' 1 . 1 1 ~ cor~l~t? O\VIIS nl)l)rosilr~:llcl~ 10,000 acres region of \vestcrn Kt.\\- 1-n1.1~ (fig. 1). I t is nplwosi- of ~ ~ n ~ . l i l : ~ ~ ~ t l . \ v l l i c . l ~ is (list r i l~~ltct l t l~rougl~o~l t , tllc colr~~ty.

mnlclp 25 ~ t ~ i l c s fl.ol11 I I ~ I ~ ~ I to S O I I ~ 11 a11(l 27 111iIcs 11-0111 e:tit I i o i ~ l ~ ( ~ - t ( ~ ~ ~ , I l l ( * (.01111ty wilt, II:IS III:III? I I I ~ I I I I ~ ~ C ~ I I I . ~ I I ~ to \vest. I t 112s n totnl nriln of 4::O,i,"O ncl.es. 01. nl)orrt 67:: f:~cilitita-: 111:lt i111~111tlr i'ootl ~)~,oc~c.s- i~~g, c l o t l ~ i ~ ~ n mrnpl~ic square miles. Rochester, t l ~ c co1111ty scat, is in the ~ ~ o ~ . t h e r ~ ~ :II t.. ~ : I I I I V I . : I ~ . ( . I I ( ~ I I I ~ I . : I ~ ~ . : ~ ~ ~ t o l ~ ~ o t i \ ( h ~):rrts. n11(1 L)ervy Inn- part of t11c coillrty. c l ~ i ~ ~ c tools. 131~t~~lil)01~t, Ilollro!.c I;nlls, I lil(011, X I I C ~ o t l~c r

~ O \ \ - I I S n l ~ o 11nve FIII:III I I I : I I I I I ~ : I C ~ I I I - ~ I I ~ f:~cilities.

Figure I.-Location of Monroe County in Xew York.

SliSl~tly less tllnlr l l n l f tllc rn1111ty is ur;e(l for ~ : I I . I I I ~ I I = . L ) n i r y ~ ~ ~ g is t l ~ c ~)rcdolttinnnt far111 cl~tcrprisc. A s r ~ l ) s t n ~ ~ - tin1 n m o u ~ ~ t of fluid 111ilk is wItl. illso in~pol.t:r~rt n1.e cn5l1- gmin crops slid fruits and vegetables. Gmin cro ,s are gmlm for dairy feed, ns wcll as for ens11 i~leome. :tlso, n consiclerable acreage of t l r j berms is g r o ~ r ~ t in the cor111tj. Nortl~ of U.S. Route 104 nl~tl n1.w in slnnll nrens sor~tll of this I ~ i g l ~ \ ~ n g , an estc~isire ncrcnge is usccl for f t ~ t i t s nntl vegetables. Apples, cl~crrics, pears, prunes, tonlntoes, po- tatoes, cnbbn e, and green I)cnl~s are colnr~lo~~lj- grown. Approsirllntc F y 30 p c r r c ~ ~ t of t,llc totnl rloll:lr \ . ~ I I I c of ~ : I I . I I I products soltl collies from the sale of fruits ant1 vegetnl)le.;.

Only a small pcrcelitngc of tllc countg is used for rrootl- ~cl. Much of t l ~ e acrengc is scattered tl1ro11g11o11t t11c

W u n t j in s~nal l farm ~voocllots. illucli of tllc \vootlln~~tl is omnecl by t,llc Go~?entlnent. T l ~ c Stnte OKI IS In~ltl nln~tg tllc Ontario P a r k m y , tlie Eric Barge Cn~inl, nlid I Inllllin

How This Survey Was Made Soil scirl~ticts lllntlr t l ~ i s ~ I I I , \ . I ~ ? - to 1onr11 ~ v l ~ a t I;i~ltls of

soil n1.r i l l J l o~~ tu , r ('c11111ty. \vllc~.c tllcy nrc locntetl, ntid Iln\v t11e.1. ( ~ 1 1 1 I)(' 1 1 ~ ~ 1 . 1 ' 1 1 ( ~ soil sc.ic~~tists \vcl~t illto t l ~ c C O I I I I ~ , I , 1<11o\vi11y tIl(>,v \vol~! lili(~l>. to 1i11cI I I I ~ I I ~ soils t11ey l1:111 : l l l~~~:l i l )~ - l s ( B l l :1111l ~ ~ ( ~ l ~ l l : l ] ) ~ Goltl(b Ill(~). I1:l~l 11ot. ;Is tIl(1y t l.n\x~lrcl o\.(.I. 1 Ire rorl~lty, t lloy ol)l;c1.1.~(1 1 IIC S ~ ~ C ~ ) I I C S S , Icrlgt 11, all11 clt:~l)c of slol~cls, tllc~ i z c :~rltl sln~cd of strcnn~s, I I n t i )Inl~ts or crolj" t Ilc I<illtls of rovk, and I I I : I I I ~ ~ : I I - I < :11)01lt. t I IP soils. 'l'l~oy (111g I I I : I I I ~ 11oles t.n ex- 1jose wil ~)l .ol i l r~. -1 111.ofi lc is t l ~ e S C ~ ~ I I C ~ I C C of natornl lny- err;? nr 11ol.izon~. in a soil : it estc111tls fl.0111 t l ~ e surface tlo\v~i into t l ~ c 11:11,cnt 111:1tcl-inl tlr;~t II:IS ]lot. I )PPI I c l ~ n ~ ~ g c d I I I ~ I C ~ I

by I c n c l ~ i ~ ~ c or I)! t11e nctint~ of 11ln11t. ro0t.s. ' I I s t i t I I I : I I ~ I I I I I I ~ I I S I I rofilcs

t11e.v stutlicvl. : I I I ( ~ t l~ey c.o111 ):r~,ctl t l l ~ s c j)rofilcs wit 1 those 1 I' i l l ~ ~ I I I I ~ ichs I I (~ : I I .~I .Y n r l t l i l l 1 ) :Icsr.; IIIOI.(\ (11st:111t. 'l 'l~ry clwsi- fietl n r ~ t l I I : I I I I (Y~ tlle soill; : ~ c c . o ~ ~ l i r ~ g lo ~~:~t,iol~n.icle, 1111iform procetl111.es. Tllc snil srl.ies (7 ' ) ' n l ~ t l t l ~ c soil 1)llnse n1.c tllo cntepnrics of .nil rln~sific-ation 111o5t I I W I i l l n locnl sllrvey.

Soils rll:~t I I : I \P ~)~*olilo.s :~lrllost nlilic 111nlic up n soil sc- 1.i11s. 1;s~tq)t for t l i t l ' v~ . (~~~t tvs1111~h i l l tlrc? s11rf:lce I:I~C>I., all 1I1e ~ibils 01, I I I I C ~ s t ~ r i o ~ I I : I V C > I I I : I ~ ~ I , l ~ o ~ ~ i z o ~ ~ ~ tl1:11 :II*O si111i1:ir i l l tlrick~~e.~. ~ I . I , : I I I ~ ~ I I I ~ I I ~ . :III(I ot I I C ~ ~ i1111)ortnltt c11nrncte1.- is t ie . Encll snil sel.iri is I I : I I I I C ( ~ for 3 to\ni or otller geo- g~.nlIl~ic* f ( ~ ~ t n l . e II(YII. 1 11e 1)1:1cc \vllcrc n r;oil of tl~:lt scrics \vn< fir-t o l~- t~ l~vc~l n l l (1 lll:l~~~)C(I. ~'011:1111er nll(l 1Iilto11, for cxnrnl~lc. n1.c tllc rlnlllrs of t \\.o soil s(11-~CP. -111 t l ~ e coils in t l ~ e Vnitrtl Stntcs I ~ n ~ i ~ l g tllc C:IIIIP S P ~ ~ ( > S II:IIIIC are esr;elt- tiillly :~lil<e i l l tl1o.e cl1n1.:1c.tcl.isti1-5 t l ~ : ~ t nlfcct their be- Iln\.ior i l i t ] ~ ( , 1111tIiut111.1)ctl Inltclscnoc.

Soils o f O I I I ~ ~ ~ ~ . i c ~ ~ I - : I I I tlill'c~~. i l l t c * s t ~ ~ ~ . c of t11c s~lrfnco layer n ~ ~ t l i11 slol~p. s t o ~ ~ i l ~ c ~ s ~ . 01. ~ O I I I C n t l ~ r r cllnr:tc*teristic that n l l r c t~ 11-e of t l ~ c ?oils 1)y I I I ~ I I . 0 1 1 t l ~ c ])asis of s11c.11 tlifie~.c~~vrc. n soil ct~~.ir.s is tlivitlrtl illto ~) l rns~s . 'l 'l~c llnllle of n soil 11l1:1sc i~rtlic:ltrs n f c n t ~ ~ r e t11:rt nlfrcts t t ~ n ~ ~ : l g e ~ ~ ~ c t l t .

' I ta l ic ~ i r l u ~ b c r s I I I pnrrrllllcscs rc.1c.r to Lilcrntclre Cited, p. 170.



:ntal Science Services Administration . Environmental Data ! recycled paper 5-33 ecology and envimnmen~

I'

U.S. DEPARTMENT O F COMMERCE C. R. Smith, Secretary

ENVIRONMENTAL SCIENCE SERVICES ADMINISTRATION Robert M. White, Administrator

b~ ENVIRONMENTAL DATA SERVICE W o o d r o w C. Jacobs, Director

JUNE 1968

REPRINTED B Y THE

NATIONAL OCEANIC A N D ATMOSPHERIC ADMINISTRATION

1983

recycled paper ecology end envvonmenl

REFERENCE 5


GOLDEN ROAD DISPOSAL SITE

NEW YORK STATE SUPERFUND PHASE I SUMMARY REPORT

F I NAL

November 28, 1983

Prepared By:

Recra Research, Inc . 4248 Ridge Lea Road

Amherst, New York 14226

F o r :

New York S t a t e Department o f Environmental Conserva t ion 5 0 Wolf Road .

Albany, New York 12233-0001

recycled paper recycled paper


recycled paper

.. .. SAMPLING REPORT

Golden Road Disp.osal S i t e

c h i l i (TI, Monroe (C)

S i t e Code: 8-28-021

P r i o r i t y Code: N

Date Sampled: J u l y 20, 1983

By: Deborah Jackson Sen io r Engineer ing Techn i c i an D iv i s i on of Sol. id and Hazardous Waste Region 8

J u l y 25, 1983

ecolugy end environment

REFERENCE 7


klazardous Waste Sits Ranking System

A Users Manual

Originally Published in the July 16, 1982, Federal Register

United States Environmental Protection Agency

recycled paper I;., t * , - l ~ ? r i papur

erulugy end envirunmen~ ecqilt~gy a11t1 C I ~ V ~ ~ V I ~ I I I C I I I

REFERENCE 8

recycled paper rcology and rnvirt~nment

CONTACT REPORT

Telephone (X) Meeting ( ) Other ( )

AGENCY : Town of Chili

ADDRESS : 3235 Chili Ave. Rochester, N.Y. 14624

PHONE NO.: (716) 889-3550

PERSON CONTACTED: Steven Chudyk

Highway Superintendent

FROM : G. Floren t ino

DATE : 7/3/90

SUBJECT : Water Supply for Town of Chili "Qu

Mr. Chudyk stated that there are residences south of Black Creek in the Town of Chili that are not on Monroe County water and there may also be some residences north of Black Creek on private wells.

Acknowledgment: (See Attached)

Signature: Date: J, 4. / G 90 c 7 4 ' -

Title:

bf GF/kk CR/YN4080 [ENVSHARE)

recycled paper erulugy and environment


N,-\'IIOS:\L C'OWFERENC'E O F STATE HISTORIC PRESER\:AIlON OFFICERS

1 ! i 1 . ~ / / 1 1 / ~ 1 0 1 1 , V.C7.

.A\IERIC'.-\N .ASSC)CIAI'I(IN FOR S.I.-\l E .r\N D LOCAL H 1547-OR>'

. \ ' ~ i . ~ 1 / 1 ~ 1 1 1 L ~ , 7 ~ f / l / c ~ . s . ~ c ~ ' ~

recycled paper r c o l o ~ y and environrnrn~

Copyright c 1989 o l tlic Klrriorlctl R L ' ~ I ' S / L ~ I ~ U / H I . ~ / ~ ~ I(. P I ~ I C C , ~ 1966-1985 front rnnttcr by tlie Anicr-icnrr Acsociatior~ for Statc nnd Local Histol-\. A l l r.iglits rescr.\.ccl. P~.i~it'd in tlic Urritccl States ol America. For i~i lorr i ia t io~i , \ \ I - i t c t Ire* :\riicr-i- can Association lor S ta te arid Local Hirtor-\, 172 Second A\.cnue North, Nash\,ille, Tcnnesscc 37201.

Library of Congress Cataloging-in-Publication Data

National Register of Historic Places. 1966-1988.

Bibliography: p. 1. Historic sites-United States-Directories. I . United States. National

Rrk Service. 11. National Conference of State Ifistoric Presenalion Officers. 111. American Association for State and Local flistoy. E159.N3418 1989 m3'.025 89-15007 ISBN 0-942063-03-3

The cirmirl;~ti\.c list incli~dccl in this ctlit io~l o l t l l c ~h'ii/ro!rtrl Register- of Ili.sror.ic~ P/u(.(~.~ 1966-1988 llns bccri c.onipilc.d. edited, a n d pro\.ided to the American Association for Statc and Local History in magnet ic tape lormi b \ thC tiatiorial Park Ser\.icc.

Front Co\.cr - The Clcbt: i l l A I - l i ~ ~ ~ t o n , C'irpi~iia, has ~ ~ \ o l \ ~ c l to its pl-cscnt condition \ \ - i t11 additions ninclc to i t tlie years. Walter Jones built tlic or.iginal por-tion i l l the cn~ . l \ 1820s with the a r t i s t , C l a d hlills, acldirig tlic octn_ru~inl iL \ \ i ~ i g to the house in tlic IR30s. That nilrg is o n e o l tlic her1

j esnniples o l this mid-19th centur-\. building lorn1 IH- IBS, Jack E. Bolic.ller:)

B;~cli C'cncr - Top: \\:I1 Srt\rlc,t. .It.. \ I i o \ \ 11 1 1 ~ 1 ' uriclc~~.\\a!. at Pitt5I>~rrgli, Pc~ri~i<\ I\;iriia, c.ir.ca Iq-l?, i~ :I ~ t c r . ~ i \ \ ~ I i e c \ r . i \e~. to\ \ lwat dcrigriccl 1 0 i 111~ lc .1 . lo\\ l31.icfgcs. Called a "pc~c~llicrat" and I i ~ ~ i l t i l l 1918 101 C'al licyic Stc.c.1, she to\ \cd bnrgcc cjl c c ~ ; ~ l o r 1 tlic Ollio, hlis<i<<il>pi, aricl hlonongahcla I . ~ \ c % I ' . SIlc i! !lo\\ ;i ~ i i ~ ~ s e i ~ r i i \csqc,l a t tlic Ohio River hlir- S C L I I ~ I iri 31a1 i c , t t ; ~ , O l ~ i u . ( C ' ( I ~ I ~ / C . S \ , o/ 0111o HI '~~(II . I 'CU/ So- tic,/! ) 3licldIc: 711ic ; \ I -cl iculo~ical site- is tlie remains o l Fort Fil~iiorc Tlic ~ ~ I I I . Ileal. I.aq C'r\~c.c*s, Nc.\\ hl~.uic.o. \\ac; n t \1>ic i1I ~ ~ I I I I ~ I \ \ ~ \ I ~ ~ I I ~ ; I I I I I \ . 1 1 0 < 1 0 1 t l ~ c * 1850s. Saricl so011 C ~ \ ~ I L . C I t l ic , f o ~ t nltc.1- i t \ \ ; IS nhalltlo~icd i l l 1862, \\liich Ilcll>~,cl p~ccc . r - \~ . tlic Io\\cr pol- t io~ir ul tllc.n~lol,c \\ails. (k)lltr P Ilrl\o!? ) Bottc1111. Soutlic.r.ri Tc~.r i l i~l ;~l ;111d \ ~ I I - C I I U L I S C His- 1or . i~ L)ist~ict \\a. t l i c \\lic~lc\aliriy c.crrtcr- Inr. tlic tit\ or I ; n o \ \ illc.. Tcri~ic~~-cc., L I I I L I nitrc.li ol t l ~ c * r~~r.r-uuncl i~ig region i r i I I I L . IatC 19th ; I I I L I c a ~ - l \ 20111 L . C I ~ ~ L I I ics. A \al.icst\ of co1rinicrcinI n I c l l i ~ c . c ~ ~ ~ ~ - a I 4 1 \ Ic~s IiiyIiIigIit~ I I I C d i s t r i c t . (G(i11 I G ! I \ ! J ~ I I ~ ! )

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I r.colugy and environment

I NATIONAL REGISTER OF HISTORIC PLACES 1966-1988 NEW YORK 467

Madison County-Continued

' Comstock, Zcphnia, Farmhouse [Ca~enovia Town MRA]. 2363 Nclson St., Curnovia . 11/02/87, A.C, 87001866

Cottage Lawn, 435 hlain St., Oneida. 11/06/80, A,C. 80002650

Crandall Farm Complex [Cucnovia Town hlRA], 2430 Ballina Rd., Cuenovia vicinity, 11/02/87, A,C, 87001867

Evergreen Acres [Ca~ellovia Town hlR.41, Syra- cuse Rd., Cazenovia \~cini ty , 11;0!./87, .A,C, 87001868

First National Bank of hforrisville, hlain St., hlorrisville, 9/12/85, A,C, 85002365

Hamilton \'illage Ilistoric District, Roughly fiendrick Aye., Broad, Payne, Hamillon, Madison, Plcasant and Leivbanon Sts., Ham. ilton, 9/13/84, C, 84002494

House at 107 Stroud Street [Canastota \'illage SlRA], 107 Stroud St., Canastota, 5/23/86, C, 8600 1302

House at I15 South hlain Strcet [Canastota \'illage hlRA], 115 S. hlaln SI.. Canastota. 5/23/86, C, 86001289

House at 205 North .\lain Strcet [Canastota Vil- lage hlR\], 205 N. hlsin St.. Canastota, 5/23/86, C, 86001296

House at 233 James SII-err [Canastota Village h i m ] , 233 James St., Canastota, 5/23/06, C, 86001295

House at 313 North hlain Street [Canastota Vil- lage hlRA1, 313 N. hlain St., Canastota, 5 / 3 / 8 6 , C, 86001298

Housc at 326 Norrh Pctrrboro Streel [Canastota Village hlR41, 326 N. Prtsrboro St., Canas- 1013, 5./23/86, C, 86001299

Houseat 328 North Pclrrboro Srrret [Canastota Village hlR.41, 328 N. Pe~r rboro St., Canas. Iota, 5/23/86, C, 86001301

Lorenzo, Lcdyard St. (U.S. !O), Cazenovia. 2,.'18/71, C, 71000541

hlain-Broad.Crovr Srrects Ilistoric District, Roughly boundtd by hfain. Broad, E. Grove, \Y. Grow, Li'ilbur, Elizabeth. E. \\'alnut. \Y. Walnut, and Stone Sts.. Oneida. 9/15 4 3 , C, 83001705

hlaplcs, The ICazenovia Town hlRh]. 2420 Nel. son Rd.. C a ~ e n o i ia v~cinit)., 11,/02. '87, d,C. 87001876

Meadows Farm Complex [Cazenovia To\vn hlR.A]. Rippletoll Rd., Cazc~~ovia \icinlty. 11/02 '87, A,C, 87001869

hliddle Farmhouse [Cazenovia Town htR.41. 4875 \V. Lake Rd., C a ~ c n o \ i a v~cinity, 11,'021'87, C, 87001870

Niles Farmllouse [Ca~enovia To\\n hlR.41, Rip- pleton Rd.. Cazeno\ia \~c ln i ty , 1 I. 01 '67, A,C, 87001871

Old Biolon Ilsll, Colgate Iln~\crsit!, !lamilton, 9/!0/73. C, 73001 199

Old hladison County Courthouse. E. hlain St., Slorris\~lle, 6 / 1 5 76. ;\,C. 7S0011160

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Oneida Cornmunit!. hlansion House. Sherrill Rd., Onciiia, 10 '15/66, A.B,a, NHL, 66000527

Ps r l e r Farmhouse ICazenovia Town hfRA], 393 1 EajI Rd., Cueno i i a \-iciniry. 11/02/87, .A,C, di001672

Pcterboro Land Oliicr. Pe~erboro Rd., Peter. boro, 9 07 94. .A.C. 84002498

Peterboro Strtr.1 E I ~ . m r n r a q School [Canaslota \'illage .\lR4]. 220 S. Psterboro St., Canas. Iota, 5 ' 2 3 86, C, 86001304

Robcrtj, Judgc Sathan S., House [Canastota \'iL lags .\IR.A], \\'. Ssnsca A\<., Canastota, 5 '23/86. C, 8tW1305

Rolling Ridgs Farm [Cazeno~ia T0ir.n hlRA]. 3937 Kumbsr S ~ n e Rd., Cazenovia vicinity, 11/'0!:87, .LC, 87001873

Smith, Adon, House, 3 Broad St., Hamilton, 5/02,'74, C, 74Nl256

South Peterboro Strest Commercial Hisloric Disrrict [Canastota \ '~llage hlRA], Roughly bounded b ~ . S T 76, Diamond St., Penn Cen- tral RR tracks, and Commerce dve., Canas- Iota, 5,.23: 86, C , 66001287

South Prtcrboro Srrret Residential Historic Dis- trict [Cana~rota \'illagc LIRA], S. Pttrrboro St. bet\\ ccn Tcrrace and Rasbach Sts., Canas- Iota, 5 '23 ' $ 6 , C, 86001288

Si\ecrland F x m h o u x ICazrnovia To\r.n hlRA], Sunibsr S ine Rd., Caz rno i~a vicinity. ll,O! 6 i . C, .$'i001674

Tall Pines [Cazcnoiia T o i m h f M ] , Ridge Rd., Curnov i s I icinity, 11/02/87, C, 87001875

US Post Oll~cr--Canastota [US Post Offices in Kci\ Torl, Stare. 1858.1943, TR], 118 S. Peter. boro St., Canron, 11/17/88, .\,C, 88002467

United Church of Canastota [Canastota Village hlR41, 144 \\'. Center St., Canastota, 5 13 '86. C,a, 65001306

\\'heeler 110uji. Complex, h"i 8, Leonardsville, 9 '22 63, C, 63001706

hionroe County

.\dams-R!an HOUK, 425 \\'ashingon St., Ad. ams Basin. 9 '05'85, ,\,C, 85001957

.Andrc.\rj Strcct Bridge [Inner Loop .\lRA;Stone .Arch Bridgl: TR], .Andrcus St. at Genesee Riv- cr, R o i l ~ c s ~ e r , 1O;I li'84, A,C, 84000182

.Anthony, S u m B., House. 17 hiadison St., Ro ih t i t t r , 10 15 '66, B, SHL, 66000528

Be\ l t r . \ lcmor~al Building, \Vashinpon St., Roihc>~cr , 10 25 73, A.C, 73001201

Bridge Square Hisroric Districl [Inner Loop \IR.4]. R o ~ ~ h l ! bounded by Inner Loop,Cen- tre Park, \<.,hifigon and \V. X l ~ i n Sts., Roihc>l:r, 10 11 84, .A,C. 84330273

Brtiiin. - \ d ~ n i . Bloili [Inner Loop 1lR.A). 480 E. l i lc~~n St. . Rvibsjter, 10/04.;'85. C, 85002857

Build~ng at 551-555 S o n h Goodman Street, j j l - 5 5 S Goodman St.. Rocheslsr, 3 10 So, C, i C W 4 4 8

Carnpbcll-\\ i;~~tl:jc! Hourr , 113 S. FitzhughSt., R ~ ; h c . ~ r i r . ! 16 '71. C, i1000542

Chamber of Commerce [Inner Loop M U ] , 55 Saint Paul SI., Rochester, 10/04/85, C, 85002859

Child, Jonathan, House & Brewster-Burke House Hisloric District, 37 S. Washinpon St. and 130 Spring St., Rochester, 2/18/71, B,C, 71000543

Chili hlillsConservation Area, 1 mi. SW of West Chili off Stuart Rd. along Black Creek, West Chili vicinity, 3/12/75, C,D, 75001 198

City Hall Historic District, S. Fitzhugh St. between Broad and W. hlain Sts., Rochester, 9/17/74, A,C,a, 74001258

Cohen, H. C., Company Building-Andrews Building [Inner Loop hlRA], 216 Andrews Sf., Roches~er, 10/04/85, A,C, 85002853

Coun Exchange Building-National Casket Company [Inner Loop M U ] , 142 Exchange Sf., Rochester, 10/04/85, C, 85002850

Court Street Bridge [Inner Loop h1RA;Stone Arch Bridge TR], Coun St. at Cenesee River, Rochester, 10/11/84, A,C, 84000276

Cox Building [Inner Loop L1RA;Department Store TR], 36-48 St. Paul St., Rochester, 10/11/84, A,C, 84000279

Daisy Flour Mill, Inc.. 1880 Blossom Rd., Roch- ester, 6/26/72, AX, 72000855

DeLand. Henry, House, 99 S. Main St., Fairport, 4/17/80, C, 80004610

Dewey, Chester, School No. 14 [Inner Loop h l U ] , 200 University Ave., Rochester, 10/04/85, C, 85002847

East Avenue Historic District, Irregular pattern along East Ave. from Proben St. to Alexander St., Rochester, 4/17/79, A,C, 79001589

East High School, 410 Alexander St., Rochester, 6/30/83, C, 83001707

Eastman Dental Dispensary, 800 E. Main St.. Rochester, 1/28/83, B,C, 83001708

Eastman, George, House, 900 East Ave., Roches. ter, 11/13/66, B, NHL, 66000529

Edwards Building [Inner Loop h1RA;Depanment Store TR]. 26-34 St. Paul Sf., Rochester, 10/11/84, A,C, 84000287

EIy, Hentey, House, 138 Troup St., Rochester, 8/12/71, C, 71000544

Erie Canal: Second Cenesee Aqueduct. Broad St., Rochester, 9/29/76, A,C, 76001228

Federal Building. N. Fitzhugh and Church Sts., Rochester, 4/13/72, C, 72000856

First National Bank of Rochester--Old Monroe County Savings Bank Building [Inner Loop hfRA], 35 State St., Rochester, 10/04/85, C, 85002861

First Presb)terian Church, 101 S. Plymouth Ave., Rochesrer, 10/25/73, C,a, 73001202

First Universalist Church, SE corner of S. Clin- ton Ave. and Court St., Rochester, 5/27/71, C,a, 71000545

Gannet1 Building [Inner Loop MRA], 55 Ex- change St., Rochester, 10/04/85, A,C, 85002862

Genesee Lighthouse, 70 Lighthouse St., Roches- tcr, 8/13/74, A, 74001259

5-47 ecology and environment

468 NEW YORK

Monroe County--Continued

Granite Building [Inner Loop h1RA;Departrnent g o r e TR], 124 E. Main St., Rochester, 10/11/84, A,C, 84000290

Grove Place Historic Dislrict [Inner Loop MRA], Gibbs, Selden, Grove and Windsor Sts., Rochester, 10/11/84, A,C, 84000299

Hinchey, Franklin. House, 634 Hinchey Rd., Gates, 11/10/83, C, 83004045

House at 235-237 Reynolds Street, 235-237 Reynolds St., Rochester, 9/12/85, C, 85002272

Jewish Young Men's and Women's Association [Inner Loop LIRA], 400 Andrews St., Roches- ter, 10/04/83, C, 85002848

Kirstein Building [lnner Loop MRA], 242 An- d r e w ~ St., Rochester, 10/04/85, A,C, 85002844

Lchigh Valley Railroad Station [Inner Loop M U ] , 99 Court St., Rochester, 10/04/85, A,C, 85002858

Leopold Street Shule, 30 Leopold St., Rochester, 6/07/71, A,C,a, 74001260

Little Theatre [Inner Loop M U ] , 240 East Ave., Rochester, 10/04/85, A,C, 85002860

Lower Mill, N. hlain St., Honeoye Falls, 5/17/73, A,C, 73001200

Madison Square-West Main Street Historic District, Roughly bounded by Silver. Canal, W. Main and Madison Sts., Rochester, 11/03/88, A,C, 88002382

Main Street Bridge [Inner Loop MRA;Stone Arch Bridge TR], Main St. at Genesee River, Rochester, 10/11/84, A,C, 84000303

MichaelsStern Building [Inner Loop hllRA]. 87 N. Clinton Ave., Rochester, 10/01/85, A,C, 85002854

Mr. Hope.Highland Historic District, Bounded roughly by the Clarissa St. Bridge, Genesee River, Grove and Mt. Hope Aves., plus, Roch- ester. 1/21/74, B.C. 74001261

Mud House, I000 Whalen Rd., Penfield. lo/! 1/78, C, 78001862

National Company Building [Inner Loop .kIRA;Department Store TR], 159 E. Main St., Rochester, 10/11/84, A,C, 84000291

Naval Armory--Convention Hall [lnner Loop MRA], 75 Woodbury Blvd.. Rochester, IO/O4/85, A, 85002852

Nazareth House, 94 Averill Ave., Rochester, 4/12/84, A,C,a, 84002734

O'Kanc Market and O'Kane Building, 104-106 Bartlett St. & 239-255 Reynolds St.. Roche5 ter, 9/12/85, C, 85002288

Old Stone Warehouse, I hlt. Hope Ave., Rochec ter, 10/15/73, A,C, 73001 203

Phoenix Building, S. hlain and State Sts., Pitts- ford, 8/07/74, A,C, 73001257

Pittsford Village Historic District, Roughly bounded by the Canal, Jefterspn Ave., Sufh- erland, and South Sts., Pittsford, 9/07/84, C, 84002736

Powers Buildine, W. hlain and State Sts., Roch. ester, 4/03/73, A,C, 73001204

recycled paper

Reynolds Arcade [Inner h p \IR.\], 16 E. )lain St., Rochesler. lO/W,'P', C, $100!95.;

Rich, Samuel, House. 2204 Fi \e \lile Line Rd., Penfield vicinip., l2/30, '8i. -\.B.C, Eii002199

Richardson's Tavern. I474 Slarsh Rd.. Perin~on. 5/06/80. AX, 800026;!

h g a Academy, 3 Riga-\lumford Rd.. Riga, 11/21/80. A,C, 80002633

Rochester Cily School t24, lleics St., Rochester. 9/15/83, C, 83001709

Rochester Fire Departmen1 Headquarters and Shops [Inner Loop hlRl1, 183 North St., Roches~er, 10/21/8l. C,g, 85003361

Rochester Sa\ings Bank, 10 Franklin St., Roch- ester, 3/16/72, .AX, 72000357

Rochester Street Historic District, Both sides of Rochester St.. Scotts\~ille, 10/25/73, C, 73001205

Rundel hlemorial Libra? [Inner Loop h l u ] , l l 5 South A\.e., Rochester, 10/04/85, C, 85002815

Shingleside. 476 Beach Ate.. Rochcster. 9/13/84, C, 84002337

Sibley Triangle Building (lnner Loop XlR41, 20-30 East A\.e., Rochester, 10/041185, C , 83002849

Sible!, Hiram, Homes~cad. 29 Sibley Rd., Sib- le!~illc, 9/12/85, B,C,b. 85CQ!!91

Spring House. 3001 !donroc Xie.. Pittsford vi. cinity, 11/20/75, ,A,C, i5001199

SL. John's Episcopal Church. I 1 Episcopal Ase., Honeoy Falls, 7/0i/8P, C,a. PF001011

St. Joseph RomanCatholicChurch and Rectory, 109 Franklin St., Rochester, 5/29/75, A,C,a, 73001197

St. Paul.North \\'aler Streets tiistoric District [Inner Loop hlRA]. St. Paul, 9. \Vatcr, and Andreivs Sts., Rochcsler, 10/11/84. A,C, 84W398

Slate Street Historic District [Inner Loop blRA], 109-173 Stale St.. Rochester, 10/11/81, A,C, 84W.102

Stone-Tolan House, 2370 E. Aye., Brighton, 7/21/83, i\,C,c, R!001i10

Third \Yard Historic District. Roughly boundcd by .Adams and Peach Sts., 1-490, and both sides of Troup and Firzhugh Sts., Rochester, 7/ 12/74. A.B,C, i4001!6!

Totiakton Site, Addrcss Rcrrricted, Honeoye Falls sirinit!., 9 i ? l / i 8 , D, iS00l861

L'S Post Office-East Rochcster (1's Posl Offices in h'eir. York Stale, 183?-1913, TR]. 206 \\'. Cornmcrcial St. , h s t Rochcstcr, 11/17/88, A,C, 88002J95

Uni\ersit!. Club [Inner Loop \tR-\], 26 Broad- \\a!. Rochester, 10/ Olj'P3. C, 85002851

Vanderbeck House 1205 Lake Aie., Rochester, J*G9/81, C, 81002i39

Karner , H. 11.. Buildln! [lnner Loop IIRA], 72-82 St. Paul SI.. Rochester, 10/01/85, A,C, BiW2846

Mashicgon Street Roahouses [Inner Loop !IIM]. 30-32 N. \'(achingon St., Rochester, 10/04,'8j, C. 8 0 0 2 8 %

5-48 prolc

JGISTER OF HISTORIC PLACES 1966-1988

\Vilbur House. 187 S. hlain St., Fairport. ?,'06:80, C, POOO265l

\\'ilder Building (Inner Loop hlRA], I E. Main St.. Rochester. 10/'04/'85. A,C, 85002863

hlontgornery County

Butler, \\'alter, fiomestead, NE of Fonda on Old Trail Rd., Fonda vicinity, 6/23/76, B, 76001229

Caughnaivaga Indian \:illngc Site, Address Re- slrictcd, Fonda vicinity, 8/26/73, D, 73001207

Ehle House Site, Address Restricted, Nelliston, 6/14/82, A,D, 82004780

Ehle, Peter. House [Nelliston hIRA], E. Main St.. Nelliston, 9/27/00, B,C, 80002655

Erie Canal, 6 mi. \V of Amsterdam on NY 5S, Fort Huntcr sicinit!, 10/15/66, A,C.D, KHL. 66000530

Fort Johnson, Jct. of KI' 531id 67, Fort Johnson, 11/28/72. B.C. KliL, i2000858

Fort Klock, ! mi. E of Sf. Johnsc.ille on NY 5 , Sf. Johnsi,ille. 11./28i72. A. NHL, 72000859

Fort Plain Conscrsation Area, Address Restrict- ed, Fort Plain sicinity, 11/15/79, A.C,D,d, 79001591

Grcene Mansion, 92 Market St., Amsterdam, 12/31/79, B,C. 74001290

Guy Park, \C. hlain St.. Arns~crdam, 2/06/73, B.C, 73001!06

Lashcr-Davis House [Kclliston MRA], U.S. 5, Nelliston, 9/27/80, C, 80002656

Nellis, Jacob. Farmhouse [Nelliston LIRA], Nel- lis St.. Nelliston, 9/27/80, B,C, 80002657

Nelliston fiistoric Districl [Nellis~on h.IRAj. Prospect, Ri\ er, Railroad and Berthoud Sts.. Nclliston. 9/27/80, C, 80002658

Palafir.: Bridge Frcight Iiousc, E or Palatine Bridgc on N Y 5 , Palatine Bridge vicinily, 3/07/'7!, A,C, 73001208

Palatine Church, hloha\\k Tpke., Palatine, 1/25/73, .A.C,n, 73001209

Rcformcd Du~cli Church of Stonc Arabia, E of Nellisron on NY 10, Nelliston vicinity, 9/14/77, A,C,a,d, 77000951

Ricc's \Voods, Address Rcstrictcd. Canajoharie sicinit!., 7/'18,'80. D.d. 80002654

US Post Orlice-Amsterdam [US Post Offices in Nciv I'ork State, 1858-1943, TR], 12-16 Church St., Amsterdam, 1 I / 17/88, A,C, 118002451

US rust Oflicc-4anajohnric [US Post Oflices in Neir York State, 1858.1913, TR], SO.\+'. Main St.. Canajoharie, 11/17/88, A.C, 88002464

Van Alstjne House, hloyer St., Canajoharie, 9.'08/83, .4.C, 8300171 I

Yrooman Asenuc School, Vrooman Ave.. Am- sterdam, 6/30/83, A.C. 83001712

\Yagncr, \Ycbstcr, Housc, E. Grand St., Palatine Bridge, 3/07/73, B,C, 73001210

IYalra~h-Van Hornc House [Nelliston hlRA], W. hlain SI., Nelliston, 9/27/80, A,C, 80002659

REFERENCE 10

recycled paper ecology and rnvirnnrnen~

REFERENCE 11

recycled paper ecology and envirnnnirnt

ROAD CLASSIFICATION I MILE J Primary highway, Light-duty road, hard or

6 0 ~ 7m FEET improved surface - I

hard surface I KILOMETER Secondary highway.

m - hard surface - Un~mproved road = = = = = = =. = -- ( Ilnterstate Route UU. S . Route O ~ t a t e Route

VATER 242.8

* OUADRANCLC LOCATION ROCHESTER WEST, N. Y.

i ~ A R D S R ~ ~ V I \ I I I I I ~ :,IIIILVII 1 1 1 ~II I I I I I I . I 111111i11u11 1111111 ~ 1 ~ ~ 1 1 ~ 1 1 1i1111tn1:1.10115 43077-86-TF-024 I ' I ~ C I I ILJ/b. 7h15 inror l~ ld l~u~l IIuI 11clJ ~ 1 1 c ~ h L ' d

22092 Map ed~ted 1 9 7 8 ABLE ON REQUEST Purple tint lndlcates extension of urban areas 5 - 5 2

recycled paper

REFERENCE 12

recycled paper rrology end rn\uonrnrn~

recycled paper

ROAD CLASSIFICATION '-'%P

Pr~mary htghway. L~ght.duty road, hard or *A ".,+ hard surlace ~mproved surface -- o,,~%

Secondary h~ghway. e-0 " "A. hard surface , ---, Unimproved road = = = = = = = = =. 7,

Interstate Route U S Route State Route

1 ' ,

SPENCERPORT, N .Y. , , , / , .

5-54 N4307.5-W7745/7.5 1 1 b

197 1 PHOTORWJ&C). AM8nvirnnment

AMS 5470 1 1 1 NE-SERIES V821

REFERENCE 13


)---<q N W YORK

QUADRANGLE LOCAIION

recycled paper

ROAD CLASSIFICATION %

Prlrnary highway. L~ght.duty road, hard or "%P hard surface ~rnproved surface

*.,OL

Secondary highway. ?. P - - Unlrnproved road = = =,= =, =. " '.,

hard surface 2

,- -, (-1 Interstate Route ! : U. S Route (3 state Route

WEST HENRIETTA, N. Y. N4300-W7737.5/7.5

5-56 1971 PHOTOREVlS~~,@?Bnd cnviwnmcnt

AMS 5470 11 SW-SERIES V821

REFERENCE 14


recycled paper

REFERENCE 15


SITE N f ' l i i : : Golden Road 1 . U . N U f l U E H :

PERSON ,. DATE: 4/11/89 CONTACTEL): Kathy Kirsch PIIUNE: N U P i U E K : (716)"226-2466 e x t . 346 AFFILIATION: NYSDEC, Region 8 Off i c e , Wetlands SecCUNTACT

ADDRESS: 6274 East Avon - Lima Rd., Avon, ~y 14414 PEKSuH(S): Natasha Snyder and Matt K i r

TYPE OF CONTACT: Meeting

There are no c o a s t a l wetlands wi th in two m i l e s or l e s s o f the s i t e .

There , i s no t i d a l in f luence on surface waters near the s i t e .

ACKNOWLEDGLMENT '

1 have read the above t ranscr ip t and I agree that i t i s an accurate

sumary . of the inforna t i o n verba l ly conveyed t o Ecology and El~virorlrl~el~ t , Inc . interv iewer ( o ) ( a s rev i s ed below, i f necessary) .

Revis ions ( p l e a s e wr i t e i l l any correct io l l s ~ l c e d c d t o above t r a ~ r s c r i p t )

recycled paper ecology and rnvironn~ent

recycled paper rcology and r n v i r o n m e n ~

D m

GRAPKZCAL EXPOSURE mELIffi S Y m

(GENS)

USER'S GUIDE

m-pared for:

U.S. EHvmoM.IENIIAL P m C N F G m OFFICE OF PEsrIcmEs AND m z c SITBS-

F U R E T O N D M S I O N . 'fask No. 3-2. .

Contract No. 68023970 Project Officer: Russell Kinerson

Task bhnager: -en Hall

Prepared by:

GENERAL SCIlzxEs C O R P C ~ O N 6100 Chevy Chase Drive, Suite 200

Laurel, Mryland 20707

REFERENCE 17

recycled paper rcolopy and rnbironrnrn~

SITE NILU:: Golden Road

PERSON . . CONTACTED: Arthur Ormsby

1.1). N U f l U E K :

L)ATE: 3 / 2 9 and 3 / 3 0 / 8 9

PIIUNI.: NUFIUEK: ( 7 1 6)" 428-5461

AFFILIATION: Monroe Co. Department of Planning COIUTACT

ADDKESS: 47 South Fitzhu h St., Suite 200 P E K S U N ( S ) : Natasha Snyder and Matt K i Rochester, New tort- 14614-2299

TYPE OF CONTACT: Meeting

INTERVIEW S U K M R Y

At the Monroe Co. Department of Planning the following information was examined and copied: Census tract maps and population figures; and the Environmental Planning Atlas for Monroe Co.

The Atlas included information on existing land use, contours and elevations, water mains and districts, prime farmland and agricultural districts, historic sites, and NYS freshwater wetlands.

ACKNOWLEDGUlENT

I have r e a d t h e above t r a n s c r i p t and I a g r e e t h a t i t i s a n a c c u r a t e

summary o f t h e i n f o r m a t i o n v e r b a l l y conveyed t o Ecology and E r ~ v i r o ~ ~ ~ l l e ~ l t .

I n c . i n t e r v i e w e r ( 0 ) ( a s r e v i s e d below, i f n e c e s s a r y ) .

R e v i s i o n s ( p l e a s e w r i t e i n any correct i o i l s llcedcd to above transcript)

w

S i g n a t u r e :

recycled paper t-rnlugy and rnvirnnrnent

recycled paper ecology and environmrnc

CONTACT REPORT

Telephone ( X ) Meeting ( ) Other ( )

AGENCY : Town of Chili Town Hall

ADDRESS : 3235 Chili Ave. Rochester, N.Y. 14624

PHONE NO.: (716) 889-3550

PERSON CONTACTED: Jim Christian

TO : YN-4000 File

FROM : G. Florentino

DATE : 7/5/90

SUBJECT : Fire ~azard at Golden Road Site

bf No apparent fire hazard at Golden Road Site (227 Golden Road, Chili, New York).

Acknowledgment: (See ~t tached

Signature: Date: 7 / / 2 / ? 0 Title: d ~ - ~ , d e q

[ ENVSHARE 1

recycled paper rrolugy and rn~uironmenl

REFERENCE 19


ecology and environment, inc. BUFFALO CORPORATE CENTER 368 PLEASANTVIEW DRIVE, LANCASTER, NEW YORK 14086, TEL. 716/684-8060 International Specialists In the Envrronrnent

March 19, 1991

Mrs. H. Fitzsimons 227 Golden Road Rochester, NY 14625

Dear Mrs. Fitzsimons:

Ecology and Environment Engineering, P.C., (E & E) has been contracted by the New York State Department of Environmental Conservation (NYSDEC) to conduct a Phase I1 investigation on your property.

In accordance with NYSDEC requirements on documentation of all reference material pertaining to this investigation, I would ask you to please review the notes of our telephone conversation (see attached) and make any necessary corrections. If the information is accurate, please sign and complete the information requested on each sheet and return to me in the envelope provided. Your assistance in this matter is greatly appreciated. If you have any questions, please call me at 716-684-8060.

Sincerely,

w James J. Richert Project Manager

JJR/smj L/YN-4080 [ ENV] #885

recycled paper recycled paper

rrology end c.n\ironrnent

CONTACT REPORT

Telephone (X) Meeting ( ) Other ( )

SITE :

ADDRESS :

PHONE NO. :

PERSON CONTACTED:

FROM :

DATE :

SUBJECT :

Golden Road Disposal Site

227 Golden Road Rochester, NY 14624

Linda Fitzsimons

Project File: YN-4000

G. Florentino and J. Richert

3-14-91

Disposal History

The Fitzsimons accepted fill material to fill in low-lying areas to the south of the railroad tracks. The fill included:

o U.S. Army artillery shell casings (no live ammunition) from the US Army Reserve 98th Division in Rochester

o Foundry Sand from Abex Corp. in Rochester, NY - trucked by H. Fitzsimmons Jr.

o Drums and assorted debris (south of the railroad tracks) - U.S. Army Reserve 98th Division - Chevron Oil - Unknown dumping

The Fitzsirnons private well is located on the north side of the house, and is approximately 40 ft. in depth. The railroad which divides the property is active--both passenger and freight. The steel building to the south of the Fitzsimons residence o the north side of the railroad '7' tracks has been used by the Fitzsirnons' for general storage/rnainte- nance/repair purpose in conjunction with their now inactive Chili Fuels and Great Western Construction business and their presently active farming business. The building was never considered an official office building. Fuel oil was stored in tanks on the west side of this building.


Contact Report/Fitzsimmons 1/21/91 Page Two

Acknowledgment

I have read the above transcript and I agree that it is an accurate summary of the information verbally conveyed to Ecology and Environment Engineering, P.C. Interviewer(s) as revised* if necessary).

* Revisions (please write in any corrections needed to the above transcript).

Signature: Date:

smj CR/YN-4070 [ ENV] #a54

recycled paper ecology and rnvvonmcnt

11. SITE NAME AND LOCATION I

I P O T E N T I A L H A Z A R D O U S W A S T E S I T E S I T E I N S P E C T I O N R E P O R T

EPA PART 1 - SITE LOCATION AND INSPECTION INPORMATION

01 Site Name (Legal, common, or descriptive 02 Street, Route No., or Specific Location Identifier name of site) I

I. IDENTIPICATION

01 State

NY

Golden Road Disposal Site

03 City

Town of, Chili

I 4 / 26 / 89 [ I Active 1955 I 1976 [ 1 Unknown I Month Day Year [ X I Inactive Beginning Year Ending Year I

02 Site Number

828021

4 3 0 7 0 8 . -- ,, ,--

04 Agency Performing Inspection (Check all that apply) [ 1 A. EPA [ ] 8. EPA Contractor 1 1 C. Municipal

(Name of Firm)

227 Golden Road

I Ecology and Environ- 1

04 state

NY

09 Coordinates Latitude

- 2 2 1-2 32.-

[ 1 D. Municipal [ 1 E. State [XI P. State Contractor ment Engineering P.C. Contractor (Name of Firm)

(Name of Pirm)

. .

[ I D. County [ 1 E. Municipal [ ] F. Other [ 1 G. Unknown

111. INSPECTION INPORMATION

[ 1 G. Other (Specify) I

05 zip Code

14625

Longitude 10 Type of Ownership (Check One)

[XI A. Private [ I 8 . Federal I 1 C. State

03 Years of Operation 01 Date of Inspection

06 County

Monroe

02 Site status

05 Chief Inspector

G. Florentine

09 Other Inspectors

T. Perrara

13 Site Representatives Interviewed

Howard Pitzsinons

07 county Code

28

06 Title

Geologist

10 Title

Geologist

P

recycled paper ecology and envirnnmrnt

08 Cong. Dist.

30

14 Title

0wne r

04 Person Responsible for Site Inspection Form

J. Griffis

07 Organization Ecology and Environ- ment Engineering P.C.

11 Organization Ecology and Environ- ment Engineering P.C.

17 Access Gained by (Check one) Owner Permission

08 Telephone No.

(716) 684-8060

12 Telephone No.

(716) 684-8060

( )

15 Address

227 Golden Road

05 Agency

16 Telephone No.

(716) 594-2335

( )

18 Tine of Inspection 1445

19 Weather Conditions Sunny, 6O0F wind from north 5 mph

IV. INPORMATION AVAIXABLE PROM

06 Organization Ecology and En- viron. Eng. P.C.

01 Contact Walter Demick

07 Telephone No. 08 Date / 27 / 89

(716) 684-8060 I Month Day Year

02 Agency/Organization NYSDEC - Albany

03 Telephone No. (518) 457-9538

P O T E N T I A L H A Z A R D O U S W A S T E S I T E IDENTIFICATION S I T E I N S P E C T I O N R E P O R T

PART 2 - WASTE INPORHATION

, 11. WASTE STATES, QUANTITIES,

01 Physical States (Check all that apply)

[ X I A. Solid [ 1 B. Powder, Fines [ X I C. Sludge [ X I D. Other Artillery shells

(Specify ) [ ] E. Slurry 1x1 P. Liquid [ 1 G. Gas

AND CHARACTERISTICS

02 Waste Quantity at Site (Measure of waste quantities must be independent)

Tons unknown Cubic Yards unknown

No. of Drums ,560

I 03 Waste Characteristics (Check a11 that ' apply)

[ X I A . Toxic [ 1 H. Ignitable 1 I B. Corrosive [ 1 I. Highly volatile [ 1 C. Radioactive [ X I J. Explosive [ X I D. Persistent [ 1 K. Reactive [ X I E. Soluble I I L. Incompatible [ ] F. Infectious [ 1 M. Not applicable 1x1 0 . Flammable

I 111. WASTE TYPE I

BAS I Bases I I I 1

Category

S LU

OLW

SOL

PSD

OCC

I OC

ACD

1 MES I H e a v y M e t a l s 1 unknown 1 1 1 I IV. HAZARDOUS SUBSTANCES (See ~ppendix for most frequently cited CAS Numbers)

Substance Name

Sludge

Oily waste

Solvents

pesticides

Other organic chemicals

Inorganic chemicals

Acids

01 Gross Amount

01 Category

NYSDEC 1983 Phase I Investigation Jackson, D., 1983 Sampling Report

V. PEEDSTOCKS (See Appendix tor CAS Numbers)

- -

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02 Unit of Measure

02 Substance Name

02[Uz]YN408O:D2833/6646

rrology and environrnen~

03 Comments

Category

P DS

PDS

F DS

PDS -

03 CAS Number

I VI. SOURCES OF I N F o m T I o N (Cite specific references, e.g., state files, sample analysis, reports) I

Category

FDS

FDS

F DS

F DS

01 Feedstock Name

04 Storage/Disposal Method

02 CAS Number 01 Feedstock Name 02 CAS Number

05 Concen- tration

06 Measure of Concent ration

T I I . HAZARDOUS CONDITIONS AND INCIDENTS I

P O T E N T I A L H A Z A R D O U S W A S T E S I T E S I T E I N S P E C T I O N R E P O R T

EPA PART 3 - DESCRIPTION OF HAZARWUS CONDITIONS AND INCIDENTS

- - - - -

01 [XI A. Groundwater Contamination Un- 02 1x1 Observed (Date 4/13/82 ) [ 1 Potential 03 Population Potentially Affected known 04 Narrative Description

Mr. Fitzsimmon's on-site drinking water well tested positive (high concentrations of cadmium and lead). It is not known how many private wells are in the area. Most of the residents use municipal water.

Q,

I. IDENTIFICATION

01 [XI 6. Surface Water contamination 02 [XI Observed (Date 5/12/82 ) [ ] Potential [XI Alleged 03 Population Potentially Affected 0 04 Narrative Description:

01 State

NY

No known use of surface water in the area, other than wetlands.

02 Site Number

828021

01 [ ] C. Contamination of Air 02 [ 1 Observed (Date ) [ I Potential I 1 Alleged 03 Population Potentially Affected 04 Narrative Description:

I No record. I - - - - - -

01 [ ] D. Fire/Explosive Conditions 02 [ I Observed (Date ) [ 1 Potential [ 1 Alleged 03 Population Potentially Affected 04 Narrative Description: I

I No record.

01 [XI E . Direct Contact 02 [ 1 Observed (Date 4/26/89 1 [XI Potential [ j Alleged 03 Population Potentially Affected 5,352 04 Narrative Description:

NO fences, easily accessible. Population within 1-mile radius.

01 [XI F. Contamination of Soil 02 [XI Observed (Date 5/12/82 ) [ 1 Potential [XI Alleged 03 Area Potentially Affected 8 acres 04 Narrative Description:

Drums were observed throughout the site: some spilled onto ground, foundry sand, and/or fly ash disposed on site.

01 [ X J G. Drinking Water Contamination 02 [XI Observed (Date 4/13/82 ) [ ] Potential [XI Alleged 03 Population Potentially Affected unknown 04 Narrative Description:

Mr. Fitzsimmon's drinking water well tested positive for high levels of cadmium and lead. Most residents use municipal water: however, private wells may exist in the immediate area.

01 [ ] H. Worker Exposure/Injury 02 I 1 Observed (Date ) I 1 Potential [ ] Alleged 03 Workers Potentially Affected 04 Narrative Description:

No record.

I - - -

01 [ 1 I. Population Exposure/Injury 02 [ J Observed (Date ) I 1 Potential [ J Alleged 03 Population Potentially Affected 04 Narrative Description:

No record.

I I

5-73 02[UZIYN4080:D2833/6646 recycled paper ecology and environment

02[UZ]YN4080:D2833/6646

rrology and environmen~


E PA PART 3 - DESCRIPTION OF HAZARDOUS CONDITIONS AND INCIDENTS (Cont.)

recycled paper

I. IDENTIFICATION

01 State

NY

11. HAZARDOUS CONDITIONS AND INCIDENTS (Cont.)

01 [ 1 J. Damage to Flora 02 1 1 Observed (Date t I 1 Potential I ] Alleged 04 Narrative Description:

No record.

01 [ ] K. Damage to Fauna 02 [ 1 Observed (Date [ I Potential [ 1 Alleged 04 Narrative Description:

No record.

01 [ 1 L. Contamination of Food Chain 02 [ 1 Observed (Date [ 1 Potential [ I Alleged 04 Narrative Description:

No record.

01 [XI M. Unstable Containment of Wastes 02 1x1 Observed (Date 2/23/79 I [ 1 Potential [XI Alleged (spills/Runoff/Standing liquids, Leaking drums)

03 [ 1 Population Potentially Affected 5352 04 Narrative Description:

Several hundred drums observed on site. Population within 1-mile radius.

02 Site Number

828021

\r.

01 [ 1 N. Damage to Offsite Property 02 I 1 Observed (Date ) [ ] Potential [ ] Alleged 04 Narrative Description:

No record.

01 [ ] 0. Contamination of Sewers, Storm/ 02 1 1 Observed (Date ) [ ] Potential [ 1 Alleged Drains, WWTPs

04 Narrative Description:

No record.

01 [XI P. Illegal/Unauthorized Dumping 02 [XI Observed (Date 1979 J [ 1 Potential [XI Alleged 04 Narrative Description:

Fly ash and foundry sand hauled to site by William Statt.

05 Description of Any Other Known, Potential, or Alleged Hazards

111. TOTAL POPULATION POTENTIALLY AFFECTED 5,352 within 1-mile radius

IV. COMMENTS

Landfill appears to once have been part of wetland.

V. SOURCES OF I N P O R ~ ~ T I O N (Cite specific references, e.g., state files, sample analysis, reports)

NYSDEC 1983 Phase I'lnvestigation Jackson, D., 1983 Sampling Report Ecology and Environment ~ngineering P.C. site inspection on 4/26/89 General Sciences corp., 1987, 1980 census information

P O T E N T I A L H A Z A R D O U S W A S T E S I T E S I T E I N S P E C T I O N R E P O R T 1 EPA PART 4 - PERMIT AND DESCRIPTIVE INFORMATION

I [ 1 D. RCRA I I I 1

11, PERMIT INFORMATION

1 1 E. RCRA Interim Status

I ] F. SPCC Plan

I. IDENTIFICATION

[ 1 G. State (Specify)

] H. ~ o c a l (Specify)

I 1 I. Other (Specify)

[XI J. None

01 State

NY

1 111. SITE DESCRIPTION I

02 Site Number

828021

03 Date Issued 01 Type of Permit Issued (Check all apply)

[ 1 A. NPDES N A

04 Expiration Date

I 01 Storage Disposal I 02 Amount 03 Unit of (Check all that apply) I Measure

02 Permit Number 05 Comments

1 I I A. Surface Impoundment I I [ 1 8 . Piles

(XI C. Drums, Above Ground

( I D. Tank, Above Ground

( ] E. Tank, Below Ground

(XI F. Landfill

[ 1 G. Landfarm

I 1 I. other (Specify) I

I I

07 Comments

04 Treatment (Check all that apply)

I ] A. Incineration

I ] 8. Underground Injectior

I I D. Biological

1 E. Waste Oil Processing

[ I F. Solvent Recovery

[ 1 G. Other Recycling Recovery

1x1 H. Other None (specify)

05 Other

1x1 A. Buildings On Site

06 Area of Site

8 Acres

I IV. CONTAINMENT

01 Containment of Wastes (Check one)

1 1 A. Adequate, Secure [ 1 8. Moderate I 1 C. Inadequate, Poor (XI D. Insecure, Unsound, Dangerous

I 02 Description of Drums, Diking, Liners, Barriers, etc. I Drums were scattered on the surface and buried. There are no liners or any means of containment. I

NYSDEC 1983 Phase I Investigation; Jackson, D., 1983 Sampling Report: Ecology and Environment Engineering, P.C. site inspection 4/26/89

k

recycled paper 5-75 ~rulogy and environmpnc

V. ACCESSIBILITY

01 Waste Easily Accessible: (XI Yes [ ] No 02 Comments:

No fences, drums on surface, foundry sand on surface.

VI. SOURCES OF INFORMATION (Cite specific references, e.g., state files, sample analysis, reports)

P O T E N T I A L H A Z A R D O U S W A S T E S I T E S I T E I N S P E C T I O N R E P O R T 1 EPA

PART 5 - WATER, DEMOGRAPHIC, AND ENVIRONMENTAL DATA

IDENTIFICATION

01 State 02 Site Number

11. DRINKING WATER SUPPLY

1 111. GROUNDWATER I

01 Type of Drinking Supply (Check as applicable)

surface We11 Community A. 1x1 B. I 1 on-community C. 1 ] D. [XI

01 Groundwater Use in Vicinity (Check one)

[ ] A. Only Source for [XI 8. Drinking (Other sources I 1 C. Commercial, I ] D. Not Drinking available) industrial, Used,

Commercial, industrial, irrigation Unusable irrigation (No other (Limited other water sources available) sources available)

02 Status

Endangered Affected Monitored A. I I e . I 1 C. 1 I D. 1 1 E. [XI F. I 1

( 02 Population Served by Groundwater Unknown ( 03 ~ i s t a n c e to Nearest ~ r i n k i n g i a t e r we11 On site (mi) 1

03 Distance to Site

A > 3 (mi)

B on site (mi)

I 7 - 15 North I - igpd' I [ ] Yes [ No I

04 Depth to Groundwater

I 0 9 Description of Wells (including usage, depth, and location relative to population and buildings) I Mr. Pitzsimmon's well is on site: 3 other possible wells along Golden Road, depth unknown.

05 Direction of Groundwater Plow

1 [ 1 Yes 1 Comments: Unknown 1 I 1 Yes 1 Comments: Unknown 1

06 Depth to Aquifer of Concern

- 10 Recharge Area

IV. SURFACE WATER

01 Surface Water (Check one)

11 Discharge Area

[ ] A. Reservoir, Recreation, [ 1 B. Irrigation, Economically [ 1 C. Commercial, [XI D. Not Drinking Water Source Important Resources Industrial Currently

Used

07 Potential Yield of Aquifer

I 02 Affected/Potentially Affected Bodies of Water I

08 Sole Source Aquifer Unknown

I Name: Af fected Distance to Site I 1 Adjacent wetlands [XI Adjacent (mil I

I

I I (mi t

V. DEMOGRAPHIC AND PROPERTY INFORMATION

01 Total Population Within 02 Distance to Nearest Population One (1) Mile of Site Two (2) Miles of Site Three (3) Miles of Site 1

5,352 8 . 19,439 C. 29,206 No. of Persons No. of Persons No. of Persons I Ad jacent

-

Within Two (2) Miles of Site 04 Distance to Nearest Off-Site Home

I The area displays village populations. I

1 ,700

recycled paper rcology and rnvironmenc

t0.25 (mi l

05 Population Within Vicinity of Site (Provide narrative description of nature of population within vicinity of site, e.g., rural, village, densely populated urban area)

P O T E N T I A L H A Z A R D O U S W A S T E S I T E IDENTIFICATION S I T E I N S P E C T I O N R E P O R T 1 EPA 01 State 02 Site Number

PART 5 - WATER, DEMOGRAPHIC, AND ENVIRONMENTAL DATA (Cont.) 828021

VI. ENVIRONMENTAL INFORMATION

01 Permeability of Unsaturated Zone (Check one)

-6 -8 - 4 - 6 - 4 - 3 [ J A. 10 - 10 cm/sec [ ] B. 10 - 10 cm/sec [XI C. 10 - 10 cm/sec I 1 D. Greater than

-3 10 cm/sec

02 Permeability of Bedrock (Check one)

[ 1 A. Impermeable I I B. Relatively Impermeablm 1x1 C. Relatively I ] D. Very Permeable - 6 - 4 - 6 Permeable (Greater than

(Less than 10 cm/sec) (10 - 10 cm/sec) -2 - 2 (10 - 10 cm/sec) - 4

10 cm/sec)

06 Net Precipitation

I 11 Distance to Wetlands ( 5 acre minimum) 12 Distance to Critical Habitat (of endangered species)

ESTUARINE NA OTHER None (mi) I -

05 Soil pH

Unknown

03 Depth to Bedrock

11 - 25 (ft)

6.7 (in)

04 Depth of Contaminated Soil Zone

Unknown

07 One Year 24-Hour Rainfall

( Distanceto:

2.0 (in)

A. - (mi B. Adj, (mi)

I RESIDENTIAL AREA: NATIONAL/STATE AGRICULTURAL LANDS COMMERCIAL/INDUSTRIAL PARKS, FORESTS, OR WILDLIFE RESERVES PRIME AG LAND AG LAND

08 Site Slope

09 Flood Potential

Site is in 500 Year Floodplain

Endangered Species:

I A. 1.0 (mi) B. Adj, (mi) C. (.25 (mi) D. <.25 (mi

0 - 1 %

10 I Site is on Barrier Island, Coastal High Hazard Area, Riverine Floodway

13 Land Use in Vicinity

14 Description of Site in Relation to Surrounding Topography

Site is in a relatively flat-lying area that contains several wetlands. Elevation of the site has been raised 3 - 4 feet above wetlands by till material.

Direction of Site Slop.

( VII. SOURCES OF INFORMATION (Cite specific references, e.g., state files, sample analysis, reports) I

Terrain Average Slope

N/A

USGS topographical maps: Spencerport, NY, photo revised 1978 Clifton, NY 1971 West Henrietta, NY, photo revised 1978 Rochester West, NY, photo revised 1978

Ecology and ~nvironment Engineering, P.C. site inspection 4/26/89 NYSDEC Phase I Investigation 1983 Jackson, D., 1983 Sampling Report United States Department of Agriculture, Soil C ~ n s e r ~ a t i ~ n S O ~ V ~ C ~ , Soils of Monroe County General Sciences Corp., 1987, 1980 census information

0 - 3 o

- - -

recycled paper

02[UZ]YN4080:D2833/6646

erology and environment

1 11. SAMPLES TAKEN - No samples taken during S.I. I


PART 6 - SAMPLE AND FIELD INFORMATION

I. IDENTIFICATION

-

Sample Type

Groundwater

Surface Water

( 111. FIELD MEASUREMENTS TAKEN 1

01 State

NY

Waste

Air

Runoff

Spill

Soil

Vegetation

Other

I 01 TYPO 1 02 Comments I

02 Site Number

828021

01 Number of Samplas Taken

None

( organic vapors ( Site screened with HNu photoionizer 1

I IV. PHOTOGRAPHS AND HAPS I

02 Samples Sent to

01 Type [ X I Ground [ 1 Aerial 02 In Custody of Ecology and Environment Engineering, P.C. I (Name of Organization or Individual)

03 Estimated Date Results Available

I

[ X I yes I Ecology and Environment Engineering, P.C. Logbook 1 I I N O I I

- - - -- -

F K L D DATA COLLECTED (Provide narrative description of sampling activities)

03 Maps

VI. SOURCES OF INFORMATION (Cite specific references, e-g., state files, sample analysis, reports)

04 Location of Maps

Ecology and Environment Engineering, P.C. site inspection 4/26/88

recycled paper ecology and m v i r o n m e n ~

I P O T E N T I A L H A Z A R D O U S W A S T E S I T E 1 I. IDENTIFICATION

S I T E I N S P E C T I O N R E P O R T EPA

PART 7 - OWNER INFORFIATION

01 Name 02 D+B Number

11. CURRENT OWNER(S) I PARENT COMPANY (if applicable)

01 State NY

01 Name Howard Fitzsimons

03 Street Address (P.0. Box, RFD t , etc.)

227 Golden Road

08 Name

02 Site Number 828021

02 D+B Number

04 SIC Code

08 Name

10 Street Address (P.O. Box, RFD W , etc. )

03 Street Address (P.O. Box, RFD # , etc.)

09 D+B Number

11 SIC Code

04 SIC Code

05 City Chili

10 Street Address (P.O. Box, RFD W . etc. )

12 City

11 SIC Code I

06 State NY

05 City 06 State 07 Zip Code

07 Zip Code 14625

13 State 14 Zip code

12 City

I I

I 13 State ( 1 4 z i p T



I I

08 Name

11 SIC Code

- I 09 D+B Number

04 SIC Code 10 Street Address (P.O. Box, RFD # , etc.)


I I

07 Zip Code 05 City 12 City

I

03 Street Address (P.O. Box, RPD # , etc.)

08 Name

06 State

04 SIC Code

I

09 D+B Number

13 State 14 Zip Code

07 Zip Code 05 City

I 10 Street Address (P.O. Box, RFD W , etc.)

06 State

11 SIC Code

I


12 City

04 SIC Code

111. PREVIOUS OWNER(S) (List most recent first)

13 State

01 Name

- - -- - - p~

IV. REALTY OWNER(S) (if applicable, most recent first)

14 Zip Code

02 D+B Number 01 Name

03 Street Address (P.O. Box, RFD 0 , etc. )

01 Name

02 D+B Number

04 SIC Code

05 City

I 02 D+B Number 01 Name 02 D+B Number I 06 State

03 Street Address (P.O. Box, RPD # , etc. )

04 SIC Code

07 Zip Code

03 Street Address (P.O. Box. RFD W . etc. )

( 04 SIC Code

05 City

05 City 06 State 07 Zip Code 05 City 06 State. 07 Zip Code

01 Name 02 D+B Number 01 Name 02 D+B Number

I - - -


06 State

04 SIC Code

07 Zip Code

03 Street Address (P.O. Box, RFD W , etc. )

04 SIC Code

I - - - - - - -

V. SOURCES OF INFORMATION (Cite specific references, e.g., state files, sample analysis, reports)

I I

recycled paper 5-79 erology and environment

I I

05 City 05 City 06 State 06 State 07 Zip Code 07 Zip Code

1 11. CURRENT OPERATOR (if diffarent from O W n ~ r l I OPERATOR'S PARENT COMPANY (if applicable)

P O T E N T I A L H A Z A R D O U S W A S T E S I T E S I T E I N S P E C T I O N R E P O R T ( EsA

PART 8 - OPERATOR INFORPIATION - NA

- - - - - -

01 Name Howard Fitzsimons I

-


1

I. IDENTIFICATION

I 11 D+B Numbar

01 Stat.

NY

02 Site Number

828021

13 SIC Code 03 Street Address (P.O. Box, RFD #, etc.)

227 Golden Road

I 05 City Chi 1 i 06 State 07 Zip Code 14 City I NY 1 14625 1

04 SIC Code

I 15 State 16 Zip Code

12 Street Address (P.O. Box, RFD I), etc.)

I I - - -

08 Years of Operation 09 Nama of Owner 1

I 01 Name 111. PREVIOUS OPERAToR(S) (List most recent first:

provide only if different from owner)

I 02 D+B Number I 10 Name I 11 D+B Number PREVIOUS OPERATORS' PARENT COMPANIES (if applicable)


I 02 D+B Number I 10 Name 11 D+B Number I

04 SIC Code

I I

05 City

12 Street Address (P.O. Box, RFD t , etc. )

07 Zip Code 14 City 05 City

08 Years of Operation

03 street Address (P.0. Box, RFD I), etc.)

06 State 07 Zip Code 14 City

. I I I 15 State 16 Zip Code I

13 SIC Code

06 State

09 Nama of Owner During This Period

I I -

08 Years of Operation 09 Name of Owner During This Period

15 State

04 SIC Code

16 Zip Code

-

03 Street Address (P.0. Box, RFD I), etc.)

12 Street Address (P.O. Box, RFD I), etc.)

I

13 SIC Code

1 13 SIC Code


04 SIC Code 12 Street Address (P.O. Box, RFD #, etc. )

02 D+B Numbar

I

02[Uz]YN4080:D2833/6646 5-80

recycled paper ecology and mrin~nment

10 Name

I

08 Years of Operation

I

09 Name of Ownar During This Period

14 City 07 Zip Code 05 City

IV. SOURCES OF INFORMATION (Cite specific references, e.g., state files, sample analysis, reports)

06 State 15 State 16 Zip Code


EPA PART 9 - GENERATOR/TRANSPORTER INPORfUTION

I 11. ON-SITE GENERATOR - NA I

I. IDENTIPICATION

01 State

03 Street Address (P.O. Box, RFD W , etc.1

02 Site Number

01 Name

04 SIC Code

02 D+B Number

( 111. OPP-SITE GENERATOR(S I - NA I

1

02 D+B Number 01 Name 02 D+B Number


03 Street Address (P.O. Box, 04 SIC Code 03 Street Address (P.O. Box, 04 SIC Code RPD 8, etc.) RPD W , etc. )

04 SIC Code

I

- - -

05 City 07 Zip Code 05 City

w

05 City

I

I I

I IV. TRANSPORTER(S) - NA I

03 Street Address (P.O. Box, RPD 8, etc.)

05 City

01 Name

I I

1 01 Name

04 SIC Code

06 State


02 D+B Number I 01 Name

07 Zip Code 06 State

02 D+B Number

02 D+B Number

07 Zip Code

03 Street Address (P.O. Box, RPD W , etc.)

03 Street Address (P.O. Box, RPD 8, etc.)

04 SIC Code

05 City

04 SIC Code 04 SIC Code

03 Street Address (P.O. Box, RPD 8 , etc.)

07 Zip Code 05 City 06 State

03 Street Address (P.O. Box, RPD 8 , etc. )

recycled paper ecology and envuonmn~

04 SIC Code

06 State 07 Zip Code

I 01 Name 01 Name 02 D+B Number

I

02 D+B Number

V. SOURCES OF INFOXUUTION (Cite specific references, e.q., state files, sample analysis, reports)

I

05 City 05 City 06 state 06 State 07 Zip Code 07 Zip Code

11. PAST RESPONSE ACTIVITIES 1


EPA PART 10 - PAST RESPONSE ACTIVITIES

I 01 [ 1 A. Water Supply Closed 04 Description:

02 Date 03 Agency I

I. IDENTIFICATION

None on record I

01 State

NY

01 [ ] B. Temporary Water supply Provided 04 Description:

None on record

02 Site Number

828021

02 Date 03 Agency

01 [ ] C. Permanent Water Supply Provided 04 Description:

None on record

02 Date 03 Agency I 01 I I D. Spilled Material Removod 02 Date 1985 03 Agency EPA 04 Description:

Emergency drum removal (removed 560 drums)

01 [ ] E. Contaminated Soil Removed 04 Description:

None on record

02 Date 03 Agency

01 [ ] P. Waste Repackaged 04 Description:

None on record

02 Date 03 Agency

1 01 [ 1 G. Waste Disposed Elsewhere 02 Date 03 Agency 04 Description:

None on record

01 1 1 H. On-Site Burial 02 Date 03 Agency 04 Description:

None on record

01 I 1 I. In Situ Chemical Treatment 04 Description:

None on record

02 Date 03 Agency

01 1 1 J. In Situ Biological Treatment 04 Description:

None on record

02 Date 03 Agency

-

01 1 ] K. In Situ Physical Treament 04 Description:

None on record

02 Date 03 Agency

01 I 1 L. Encapsulation 04 Description:

None on record

02 Date 03 Agency

I 01 ( 1 M. Emergency Waste Treatment 04 Description:

02 Date 03 Agency I None on record

I 01 [ 1 N. Cutoff Walls 04 ~escription:

02 Date 03 Agency I I None on record

I 01 1 ] 0. Emergency Dikinq/Surface Water 02 Date 03 Agency Diversion I I 04 Description:

None on record

'((CII' 01 [ 1 P. Cutoff Trenches/Sump 02 Date 03 Agency 04 Description:

None on record

02[UZIYN4080:D2833/6646 5-82

recycled paper t-rology and environrnenr

I P O T E N T I A L H A Z A R D O U S W A S T E S I T E S I T E I N S P E C T I O N R E P O R T

PART 10 - PAST RESPONSE ACTIVITIES (Cont.)

I I. IDENTIFICATION I 01 stat. I 02 Sit. Number

I 11. PAST RESPONSE ACTIVITIES (Cont . ) I 01 [ 1 Q. Subsurface Cutoff Wall 02 Date 03 Agency 04 Description:

None on record

01 [ 1 R. Barrier walls Constructed 04 Description:

02 Date 03 Agency

I None on record

01 [ 1 S. Capping/Covering 04 Description:

02 Data 03 Agency

None on record

01 [ 1 T. Bulk Tankage Repaired 04 Description:

None on record

02 Date 03 Agency

01 [ ] U. Grout Curtain Constructed 02 Date 03 Agency 04 Description:

None on record

01 [ 1 V. Bottom Sealed 04 Description:

None on record

02 Date 03 Agency

01 [ 1 W. Gas Control 04 Description:

None on record

- - -

02 Date 03 Agency 1 01 1 X. Fire Control 02 Date 03 Agency 04 Description:

None on record

01 [ 1 Y. Leachate Treatment 04 Description:

None on record

02 Date 03 Agency

01 [ 1 2 . Area Evacuated 04 Description:

None on record

02 Date 03 Agency

01 [ 1 1. Access to Site Restricted 04 Description:

None on record

02 Date 03 Agency i

01 [ ] 2. Population Relocated 04 Description:

None on record

02 Date 03 Agency

~ ~- -

01 [ ] 3. Other Remedial Activities 04 Description:

None on record

02 Date 03 Agency

111. SOURCES OF INFORMATION (Cite specific references, 0.g.. state files, sample analysis, reports)

NYSDEC Phase I Investigation 1983 NYSDEC Files, Bureau of Hazardous Site Control, Albany, New York

I I

02[UZlYN4080:D2833/6646 5-83

recycled paper ~rulogy and envirc~nmrnt

I 11. ENFORCEMENT INFORMATION I


PART 11 - ENFORCEMENT INFORMATION

( 01 Past Regulatory/Enforcement Action I 1 Yes I 1 No I 1 02 D.scription of Federal, State, Local Regulatory/Enforcement Action

I IDENTIFICATION

1 In 1976, NYSDEC Region 8 directed owner to stop dumping in wetland area. I

01 State

NY

On August 12, 1980, the site was added to the hazardous waste site registry by Ms. C. Wittenberg and Mr. G.D. Knowles of NYSDEC.

02 Site Number

828021

NYSDEC Reqion 8 informed owner of violations of 6 NYCRR Part 360 in 1981.

W. Statt cited by NYSDEC for lack of Part 364 permit to haul fly ash in 1981.

In 1982, NYSDEC and Monroe County Health Department sampled the site and found petroleum hydrocarbons in the soil, and toluene, xylene, and organic dyes in the drums.

July 20, 1983, the site was sampled by NYSDEC.

NYSDEC Phase I Investigation 11/28/83.

Remedial action performed (drum and soil removal) between Nov. 13, 1984 and June 27, 1985 under contract to NYSDEC.

Nov. 24, 1984, Howard Fitzsimons, Jr. received a court order from the Erie County Supreme court to provide access and refrain from hindering or interfacing in any way with NYSDEC investigations.

May 1985, the site was sampled by NYSDEC.

111. SOURCES OF INFORMATION (Cite specific references, e.g., state files, sample analysis, reports)

NYSDEC Phase I Investigation 1983 NYSDEC Files, Bureau of Hazardous Site Control

L 1

5-84 02[uz]Y~408O:D2833/6646 recycled paper ecnlogy and en*irnnmcnc

6 . REFERENCES

Broughton, J.G., D.W. Fisher, Y.W. Isacksen, and L.V. Rickard, 1966, Geology of New York: A Short Account, New York State Museum and Science Service, Albany, New York.

Christan, J., July 5, 1990, personal communication, Fire Marshal, Town of Chili, Chili, New York.

Chudyk, S., July 3, 1990, personal communication, Highway Superinten- dent, Town of Chili, New York.

Department of State, State of New York, 1983, Article 9, Part 805 of Title 6, Official Compilation of Codes, Rules, and Regulations of the State of New York, Albany, New York.

Ecology and Environment Engineering, P.C., April 26, 1989, Site Inspection of the Golden Road Disposal Site, Town of Chili, New York, performed for the New York State Department of Environmental Conservation, Albany, New York.

Freeze, R.A., and Cherry, J.A., 1979, Groundwater, Prentice-Hall, Inc., New Jersey.

Fitzsimons, L., January 21, 1991, personal communication, Golden Road Site Owner, Chili, New York.

General Sciences Corporation, 1987, Graphical Exposure Modeling System Users Guide, Volume I: Core Manual, United States Environmental Protection Agency, Washington, D.C.

Heffner, R.L., S.D. Goodman, 1973, Soil Survey of Monroe County, New York, United States Department of Agriculture, Soil Conservation - Service, Cornell, New York.

Hershfield, D., 1963, Rainfall Frequency from 30 Minutes to 24 Hours and Return Periods from 1 to 100 Years, Technical Paper No. 40, prepared for United States Department of Agriculture, Soil Conserva- tion Service, Washington, D.C.

recycled paper rcolcrg? and e.n>ir~,nnle.r~~

Jackson, D., July 25, 1983, Sampling Report, Golden Road Disposal Site, Site No. 8-28-021, New York State Department of Environmental Conservation, Division of Solid and Hazardous Waste, Region 8,

ce Albany, New York.

Johnston, R.H., 1964, Groundwater in the Niagara Falls Area, New York, Bulletin GW-53, New York State Conservation Department, Water Resources Commission.

Kirsch, K., April 11, 1990, personal communication, New York State Department of Environmental Conservation, Wetlands Section, Avon, New York.

Honroe County Department of Planning, 1988, Existing Land Use Hap, Environmental Planning Atlas, Rochester, New York.

Hurphy, Sean P., Harch 14, 1991,Golden Road Disposal Site Haps, Honroe County Pure Waters, Rochester, New York.

National Conference of State Historic Preservation Officers, National Park Service, and American Association for State and Local History, - . 1989, ~ational Register of Historic Places 1966-1988, American Association for State and Local History, Nashville, Tennessee.

National Oceanic and Atmospheric Administration, 1983, Climatic Atlas of the United States, reprinted from United States Department of Commerce, Environmental Science Services Administration, Environmental Data Service, 1968, National Climatic Data Center, Asheville, North Carolina.

New York State Department of Environmental Conservation, November 28, 1983, Golden Road Disposal Site, New York State Superfund Phase I Summary Report, Town of Chili, Honroe County, New York, prepared by Recra Research, Inc., Albany, New York.

, 1986, Water Quality Regulations, New York State Codes, Rules, and Regulations, Title 6, Chapter X , Parts 700-705, Albany, New York.

, September 5, 1990, Ambient Water Quality Standards and Guidance Values, Division of Water Technical and Operational Guidance Series (1.1.1), Division of Water, Albany, New York.

Pirkle, E.C., and U.H. Yoho, 1977, Natural Regions of the United States, 2nd Edition, Kendall/Hunt Publishing Company, Dubuque, Iowa.

Shacklette, H.T., and J.B. Boerngen, 1984, Element Concentrations in Soils and Other Surficial Haterial of the Conterminous United States, United States Geological Survey Professional Paper 1270, Washington, D.C.

Sweet, A.T., W.J. Latimer, C.S. Pearson, C.H. Diebold, W.W. Rietz, C.P. Head, W. Secor, and H. Howard, Jr. , 1938, Soil Survey of Honroe County, New York, United States Department of Agriculture, Soil Conservation Service, Cornell, New York.

recycled paper erolog? and en~imnrnenl

Tesmer, I.H., 1981, Colossal Cataract, State University of New York Press, Albany, New York.

b Uncontrolled Hazardous Waste Site Ranking Systems, A Users Manual, National Oil and Hazardous Substances, Contingency Plan, Appendix A (40 CFR) (47 FR 31219), July 16, 1982.

United States Geological Survey, 1971, Clifton, New York Quadrangle, Monroe County, New York, 7.5-Minute Series (Topographic), Washington, D.C.

, 1978, Rochester West, New York Quadrangle, Photo Revised from 1971, Monroe County, New York, 7.5-Minute Series (Topographic), Vashington, D.C.

, 1978, Spencerport, New York Quadrangle, Photo Revised from 1971, Monroe County, New York, 7.5-Minute Series (Topographic), Washington, D.C.

, 1978, West Henrietta, New York Quadrangle, Photo Revised from 1971, Monroe County, New York, 7.5-Minute Series (Topographic), Vashington, D. C.

recycled paper erolop? and enruonrnrnc

APPENDIX A

SITE-SPECIFIC HEALTEI ANE SA- AND . -*r-

DRILLING SITE SAFETY T


I I

I I 522 ocoloqy and onvironmont, inc.

!- S I T E S A F E T Y P L A E i

Vorsion 988

A. 0- XrnRnA!rXO.

Project Titlo: Ooldon Road Project no.: YN4020

TDD/Pan no.:

Project Managor: Oono rlorontino Project Dir.: J. Griffir I

I Location(r): Town of Chili, Honroo County, AY

Proparod by: Sharon Walck Dato Proparod: 4-21-89

Approval by: C l ? c n +\/s G ~ Q Dato Approved: c I MALI 4-7 I I

sit. safety OffiC.rt.vi.v: I /

Data Reviowod:

Scopo/Objoctivo of Work: Sit. roconnaissanco, qoophysical survoy, and onvironmontal sampling.

Proposod Dato of Tiold Activities: flay - August 1989

Background Info: Comploto: I I

Ovorall Chomical Hazard:

w Ovorall Physical Hazard

Soriour [ ] Low I 1

Serious [ 1 LO w I I

Preliminary (No analytical I 1 data available)

Hodorato I X 1 Unknovn I 1

Uodorato I X I unknown I I

IS. S X T E r n T E CBA1UCXKNSTXCS

/ Liquid 1 x 1 Solid I X 1 Sludgo [ X I Gasflapor [ ]

Tlammablo/ I X 1 Ignitable

Volatilo I X 1 Corrosive I 1 Acutely I 1 Toxic

' 1 Othor:

Physical hazard^:

Ovorhomd [ 1

Puncture [ X I

Confined* [ 1 Bolow 1 Trip/Fall 1 1 Spmco Grad.

Burn I 1 Cut I 1 splash I 1

N O ~ B O I 1 Othor: U.S. Army Artillery shells aro buried at this sit.. Othor hazards

'.quires couplotion of additional form and special approval from tho Corporato Hoalth/Safoty group. Contact

blWftc Or

recycled paver ,.a m r r c l -11- ~TIIIIIIIVII~

c~ology and environment recycled paper

i Site Hintory/Doscription and Ununual Foaturon Is00 Sampling Plan for dotailod description): Dinporal rite I

i divided in tvo by a railroad track, making northern and southern areas. Both aroan are rurroundod by vot-

i I lands. Southorn section is 0 to 10 foot highor duo to larqo quantitior of fill wanton: foundry sand,

' Lartillory rholln, nunicipal rofuso, metal slaq, flyarh, drummed induntrial wanton. 1 Locations of ~homicalsflastos: Buriod vantor, partially buried drumr, junk vohiclor on northern roction,

i I

Cattle may be on-rite. 1

Ertimatod Volumo of Chomicalrflastos: Unknown.

i Site Currently in Operation Yor: I 1 Ro: 1 x 1 1

List Hazards by Task (i.0.. drum rampling, drilling. Otc.) and numbor them. (Tark numborn are crors-roforoncod in Soction D)

Phyrical Hazard Evaluation: 1. Sit. roconnaissanco, 2. Goophysical survoy, 3. Environmontsl sampling - rurfaco roil, rurfaco water, loachato.

Chemical Hazard Evaluation:

\to: Comploto and attach a Hasard Evaluation Shoot for major known contaminant.

Compound

e?lcoppor

Zinc

Fluoride

Toluono

Xy lono

C a b i u m

Bonzono

Load

recycled paper

recycled paper

PEL/mA

0 -1 mg/m cu

lono ostab- linhod

2.5 mq/m cu/ 0.1 ppm

100 ppm

100 ppm

0.5 mq/m cu/ 0.2 mg/m cu

10 PPm

0.05 mq/m cu

ecology and environment

Rout. of Exposuro

Inhalation, skin and .yo contact, ingostion

Eyo and skin contact inhalation

Inhalation, ingortion, .yo and dermal contact

Inhalation, r kin

Inhalation

Inhalation, ingostion

Inhalation

Inhalation, oral

Odor Doscription

--

a

Strong, intonre (choking)

Aromatic

Aromatic

-

Gasolino

-

Acute Symptoms

Skin. .yo. and and nor. irritation

Skin irritation coughing, vomiting, fovor

Irritation of skin, oyos. mucur uoabranos , and lungs

Fatigue, nausoa, dizzinosr

Dizziness, irritation to oyos and respiration

Irritation of nose and throat

Dizziness, .yo, nose, throat irritation

Lasritudo, pal- lor, lors of appotit.

odor Threshold

--

--

0.035 ppm

2.3 ppm

0.5 ppm

-

4-12 ppm

--

D. SITS WETI WORK P L M

Sit. Control: Attach map, us0 back of this pago, or rkotch of rite showing hot rono, contamination toduction, ,

1 . tone, otc.

i (PCIII Porimotor identifiodl [ I I Sit. securod? I a I

Work Aroas oosignatod? [ R 1 Zone(.) of Contamination Idontifiod? [ N 1

Porsonnol Protoction (TLD badges roquirod for a11 tiold porronnol):

Anticipated Lovol of Protoction (Cross-roforonco tank numborr to Soction C):

(Expand if nocossary)

Task 1

Task 2

Task 3

Task 4

nodificationr: Entor sit. in Level C with adoquato air monitoring to oithor upgrad. to Love1 B or downgrade

to Lovol D.

Action Lovolr for Evacuation of Work ton. Pending Roassorsmont of Conditions:

A

o Lovol D: O2 t19.5% or ,251, oxplo ivo atmorphoro ,101 LEL. organic vaporr above background lovolr, particulator ,- mg/m 9 , other

o Lovol C: o2 t19.51 or ,25%, oxplorivo atmosphoro ,251 LEL31California-20%), unknown organic vapor (in breathing tono) > 5 ppm, particulator > mg/m , othor

B

o Lovol B: 0, tl9.51 or ,251, oxplorivo atmosphoro ,25% LEL (Salifornia-lot), unknown organic vaporr (in broathing tono) ,500 ppm, particulator , mg/m , othor

o ~ o v o l A: 0 t19.5% or ,251, oxplorivo atmos horo ,251 LEL (California-ZOI), unknown organic vaporr ,400 ppm, particulator > mg/mq, other

C

X

X

X

Air Uonitoring (daily calibration unless othorviro noted):

D

X

X

X

(Expand if nocorsary)

Decontamination Solutions and Procoduros for Equipmont, Sampling Gear, otc.:

Contaminant of Intorort

Volatilo organicr

Flammables

1. Scrub 4 t h brurhos in trirodium phosphate solution, 2. Rinso with doionizod wator, 3. 101 Nitric acid

4. Rinse with hoxano, 5. Rinso vith acotono, 6. Rinso with doionized water, 7. Air dry.

*Noto: Docon activitior requiring solvont us. necessitate woaring APR w/GUC-H cartridges, as well as impor-

recycled paper

recycled paper

Typo of Samplo (aroa, personal)

Area

Aroa

~ . t . q , l c t ~ ~ 111111 ~ . IBS~TIBI I I I I I . I I~


Honitoring Equipment

Hnu 10.2 ov

Explosimotor

Froquoncy of . Sampling

Continuous

Continuous

Personnel Docon Protocol: Iolloving disposal of oxpondablos, crow will wash handr/faco .map. water, pump

soap, and papor tovols to bo available at hotlino.

' i i v I

-con solution nonitorinq Procoduros, it ~ p l i c a b l o : *,A.

spacial Site Equipront, Iacilitios, or Procoduros (Sanitary tacilitios and Lighting nust noat 29 C ~ R 1910.120):

Site Entry Procoduros and Special Considerations: Ao. Invasivo sampling vithout adoquato assossront of por-

siblo buried drums and/or ordnance. Us. caution if rail line is active.

Work Limitations (tire of day, voathor conditions, otc.1 and Hoat/Cold Str.88 Roquiromonts:

Daylight, no work during thunderstorms.

- - - - - - - - - - - - - - -

Oonoral Spill Control, if applicable: A/A.

'9lrr Invostigation-Derived Hatorial Disposal (1.0 ., oxpondablos, docon wasto, cuttings): To be dotorminod: solid materials to be double bagged: liquids to bo containorizod. Written authorization

rust be obtained to loavo IDHs on-sit. aftor beginning of fioldwork, or plans should bo mad. for otf-sit.

disposal.

- Sample Randlinq Procoduros Including Protoctivo Woar:

APR, rubbor booties and glovos, Tyvok coveralls, safety shoos. Taco shield to bo vorn when sampling liquids.

Surgical glovos for handling sarplos during documontation, labolinq, and packing.

:1 ontrios into exclusion zone roquiro Buddy System us.. All E L C field staff participate in mdical ~nitoring program and have complotod applicablo training per 29 CIR 1910.120. Respiratory protection program %oats roquiromonts of 29 CIR 1910.134. and ANSI 288.2 (1980).

- - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - T,.,Ja8G FtttT ~ ~ ~ s ~ K ~ I E I I G I I - recycled paper

recycled paper A- 5 ecology and environment

.! (Umo mupplomontal shoots, if nocomaary)

J

(Obtain a local tolophono book from your hotel, 12 possible) ! I Ambulance Dial 911

t Roapital Emorgoncy Room 89 Gonoaoo Stroot, 14611 St. Wary's Hospital (716) 464-3000

Poiaon Control Contor Strong Womorial Hoapital, 601 Elmwood Avonuo, Rochoator 14642 (716) 275-5151

Police (include local, county mhoriff, #tat.) Dial 911, Uonroo County Shoriff

- Fir. Dopartmont Dial 911

Airport Rochostor Wonroo County Airport

Agency Contact (EPA, State, Local USCO, otc.)

Local Laboratory E L E ASC

UPS/Fod. Expross

Cliont/EPA Contact

Site Contact

SIZI EESOVBQS

Site Emorqoncy Evacuation Alarm Uothod TBD at site mooting

wator Supply sourc.

&olephone Location, Numbor

Collular Phone, if available

Radio

................. 1. Dr. Raymond Rarbison (Univ. of Florida) (501) 221-0465 or (904) 462-3277, 3281

. . Alachua, Florida (501) 370-8263 (24 hours1

2. Ecology and Environmont, Xnc., Safety Director . Paul Jonnairo .......................................... (716) 684-8060 (office)

(716) 655-1260 (homo)

3. Regional OZZico Contact ................................. (homo ;#

(offic.)

4 FITOH, TATOU, or Offico Uanaqor ......................... (homo )

recycled paper


mmox e a r n

1. Twenty-four hour anawering rorvico: (501) 370-8263

What to roport:

: - State: *thin ir an omo~goncy:*

i - your name, region, and rite. 1 I - Tolophono number to roach you.

i - Your location.

- Namo of person injured or oxporod. ' - Nature of omorgoncy.

- Action taken.

2. A toxicologist, (Drr. Raymond Harbiron or arrociato) will contact you. Ropoat tho information givon to tho anavoring rorvico.

3. If a toxicologist door not return your call within 15 minutor, call tho following porrons in order until contact is mado:

a. 14 hour hotlino - (716) 681-8940 b. Corporato safoty Diroctor - Paul Jonmairo - homo 1 (716) 655-1260 c. Ansirtant Corp. Safety Officor - Stovon Sherman - homo 1 (716) 688-0084

(ROTE: Fimld Team rust Enow Routo(s) Prior to Start of Work)

Dirmctionr to horpital (include map) Goldon Road to Wort Sido Drivo, mako a right on Wort Sido. ~ o l l o w this

'own to Chili Avenue, make a loft on Chili. rollow this a11 tho way to Gonosoo Stroot: horpital is on cornrr.

0

Emorgoncy I3gror.r Routes to Got Off-Site To bo dotorminod and discursod at on-rite safety mooting.

recycled paper

recycled paper

I.~IPII,LI ISIIII V ~ ~ \ ~ ~ ~ I I I I I I . I I ~


P R Q T E c T r n OEAR

I BUTYL APRON 1 1

! L o v o l B

S C B A

S P A R E A I R T A N G

P R O T E C T I V E COVERALL ( T y p o . I

R N A S U I T

I B O O T I E S I I I S U R G I C A L G W V E S I 1

N o .

I GLOVES (Typo I I

L o v o l A

SCBA

S P A R E A I R TANKS

EFICAPSULATINa S U I T ( T y p o 1

S U R G I C A L G W V E S

NEOPRENE SAFETY BOOTS

I 1 G W V E S I T y p o I

A o .

I OUTER WORK CIWVES ( I OUTER WORK GLOVES

I HARD HAT I I I AEOPRENE SAFETY BOOTS I

CASCADE SYSTEM

MAUIFOLD SYSTEM

L o v o l C

ULTRA-TWIN R E S P I R A T O R X

L o v o l D I U L T R A - N A R E S P I R A T O R ( A v a i 1 a b l . I 1 7 1

I POWER A I R P U R I F Y I U a R E S P I R A T O R I I I CARTRIDGES ( T y p o GMC-H)

CARTRIDGES ( T y p o Gl4C-H )

5-MINUTE E S C A P E MASK

P R O T E C T I V E COVERALL (TYPO T y v o k )

I R A I N S U I T I I I NEOPRENE S M E T Y BOOTS I I

X

x 1

5-MIUUTE ESCAPE MASK ( A v a i 1 a b l . I

P R O T E C T I V E COVERALL ( T y p o T y v o k )

R A I N S U I T

I BUTYL APRON. I 1 I B O O T I E S I X I

X

/ S U R G I C A L GLOVES I X I I WORK G W V E S

I GLOVES ( T y p o N o o p r o n o ) I X I 1 HARD HAT WITH FACE S H I E L D I X l 1 OUTER WORK GLOVES I I S M E T Y G L A S S E S

NEOPRENE SAFETY BOOTS

HARD HAT WITH FACE S H I E L D

B O O T I E S

HARDHAT

recycled paper

recycled paper

X

X

I - ~ - ~ ~ I I I c I IBIIII V I U \ ~ ~ ~ I I I I ~ I ~ I I I


I OVA I ( WASH TUBS

. .. 1 PAOTOVAC TIP I I I PRESSURIZED SPRAYER

j

( Blhr (Probe 10.2 lamp) 1 1 ( I DETERGENT (Type SPrmY bottle) I TI

THER~V~L DESORBER

02/EXPLOSIntTER W/CAL. KIT

1 UAGNETOMETER 1 I SOLVENT (Type hexmne/mcetone)

1

( PIPE LOCATOR I 1 I PLASTIC SHEETING I X I I WEATHER STATION I 1 1 TARPS AND POLES I

BUCKETS

SCRUB BRUSHES

( DRAEGER PUMP, TUBES I 1

X

NOISE EQVI PMENT

PERSONAL SAMPLING P W S

T U S H BAGS

TRASH CANS

HASKING TAPE

DUCT TAPE

I PAPER TOWELS 1 x 1

I FACE HASK I I I I 1 ) FACE MASK SANITIZER

I I TOLDTNG CHAIRS

I I I STEP LADDERS

PORTABLE RATEMETER

SCALER/RATEMETER S A H P U R G KQUIPHERT

1 N ~ I probe I 1 I 8 02. BOTTLES

ZnS Probe I 1 I HALT-GALLON BOTTLES ::. I I I , 1 GM Pmncake Probe I 1 I VOA BOTTLES I I

I G M S l d e Window Probe

I PORTABLE EYE WASH I I I I I - BLOOD PRESSURE MONITOR

(CI FIRE EXTINGUISHER 1

. I

.i

, . $ 4 , 1 v v C \ 8etnoI * I I \ ~ I ~ B ~ B ~ I B ~ ~ ~ I

recycled paper

1

-

PUCRO R METER

ION CHAMBER

ALERT DOSIMETER

POCKET DOSIMETER

FIRST AID KQUIPHKRT

FIRST AID KIT

OXYGEN ADMINISTRATOR

STRETCHER


- -

HAND BAILERS

THIEVING RODS WITH BULBS

SPOONS

M I V E S

TILTER PAPER

PERSONAL SAMPLING PUMP SUPPLIES

-

X

X

5 3 1 ~ . * , . I S , ~ . , u t t a I V I B \ I ~ ~ * I ~ I I ~ ~ . I I I

recycled paper

A- 10 eci)logy and environment recycled paper

V M EQVXPIBFT Ro . TOOL KIT 1

RISQLLAllllOUS (Coot.)

LUO WRERCH

lo.

1

TOW CHAIR

VAN CHOCK OUT

016

oi 1

Antifrmere

1

PICK

SHOVEL

CATALYTIC HEATER

PROPANE GAS

BANNER TAPE

SURVEYING HETER STICK

CHAINIRO PINS L RING

TABLES

WEATHER RADIO

BINOCULARS

MOAPHONE

X

CUSTODY SEALS

CHAIR-Or-CUSTODY ? O W

rEDERAL EXPRESS TORRS

CLEAR PACKING TAPE

X

X

X

I TDD/Pan

T ire Job No.

* . - mcology and mnvironmmnt, inc.

I Protoctivo Clothinq/Cquipmont

1 I

Radiation Harards

Addr088

Specific Location

Typo of Work. .

Physical Hazards

Cmorqoncy Procmduros

1 Chocklist

!.

1. , Cmorgmncy information reviewed? and aadm familiar to a11 tmaa nombors? 2. Route to nmarost hospital driven?- and its location known to a11 tmam mombors? 3. .Sit. safmty plan readily availablo.ndit location known to a11 toam rmmbors?

Hospital/Clinic Tmlophonm

Hospital Addross

Special Equipment

Other

I Rooting shall k attondod by all porsonaol rho rill k working within tho exclusion acorn. Daily informal u p d ~ t o motings will k hold d o n sito tasks aad/or conditioas change.

neotinq Conducted by: (Print I (Signsturml

m E E S (Expand on back of shmmt if nocosraryl

1 ( ~ v l c ~ k i m i r p Coordinator ) (T'A'klhR'~fl%F L t * i r ~ ~ ~ ~ m ~ a m e s a

Naao Printed

recycled paper

Signature

rrulogy and environmn~

recycled paper

recycled paper

- A T T I U D I I S (Cont.)

CI.,IJI*CI 111111 VII\I~G~IIIIII.III


Nama Printad

r7

Signature

.. e c o l o g y and e n v i r o n m e n t , I n c .

HAZARD EVALUATIM CF IYWICALS

Chemical #mu (/n,pr oat. '1-2 1 - ti Y DOT Nuns/U.N. Na. Job No. Ljd '/d 1 d C A S N ~ O C 7 Y YO -ri - g

I

References Consul t ed ( c i r c l e 1 r

NIOSH/OSHA --- P o c k s u u i d e Verschwren Hazardline Chris (Val. 11) -

p i c a d Hazardous Safety M A C C I H t h e / k fi f .' . , .- ., , P . c 5 - - I I , .:

Chemical R o p e r t in: (Synonyms: /l J / ) 11 12 1 ChamicalFormula f i j ( n / l * r ~ ? o / C C L H o l e c v l a r W e i q h t ~ c j / , 0 4 /

~ ~ s l s a l s t a t e $.Y$b;PZL s iulubi i i ty ( ~ ~ 0 1 > , 4 1 / h ~ /e s o i l in, point a-s-Y iY Flash Point Vapor Pressure/Dsmity g q Freezing Paint - Spec i f i c Gravity , , Wor/Wor Threshold - Flamable L i m i t s - Incornpatabil i t ies 4 CC)(L ~ ( A J C ,qP S ', / 1 . ? A x . t , , 5 , ,,!. p4~441 2e5(- j . f ! . : ,

V b 1 V I P , . : f.;.

Biuloqical Proper t ies :

TLV-TWA n. a ( Y ~ . ? / I M 3 PZL Wor Charac te r i s t i c - v - TDI: Locn' I m v ' * IRH Human Orl-.j,.rr : .-rq~MAquatic 5, L n , ~ L / L Rat/Mouse - ?:! 5k.,,, ( 1 , ;L- (-,,fit . , - ~ o u t e o r Exposure I tit- -1 j - 4 4 . JN . r fi,or!C ,

11

Carcinogen Teratoqen Hut agen

Handlinq Recommendations r (Personal p ro tec t ive maaurea) 7

>t,.&( J f x P I , : 7 -,. ,! ( , V L C , . nl - I I

Monitorinq Recaamendationa:

Health Hazards and F i r a t Aid!

E r d t C L a m ; / f / , I ( r i I , , 1 ! f . , - 1 . -, 1 ' : - ,

cg//,:,,q,~ 1 bq S ~ / . ~ I L Cd-fL,4 / s ; ; . , F J J ~ / / / ,rr.nl : : 8 r . ,/ : t , ~ :< 1 . T I , :+,I 1~ 1' ,r .+&fish s A, N L, t ~ , S J P P , n,k.2 1,. 4 j / - ICIULIC 4 d l r 4 ~ , i - i $ ~ r . ~ , r , : f i r J ~ . ( g ( A 1 ' - -T . . , . . , .

recycled paper

r-mr

e c o l o g y and e n v i r o n m e n t , I n c .

HAZARD EV&UAlION ff MMICALS

mid ~.lr 7, 'd c Date (2-2 / - t Y WT N.as/U.N. No. (A& I Y 3L Job tb. a h)L (d ; )d CAS Nu&er

u

References b n u l t e d ( c i r c l e r

NIffiH/OSHA Pocket Guide V 8 n c h w r m Merck Index Hatardl i n e Chris (Vof . I I )

TOXIC nd ~ a z a r d o u n sa fe ty nvud ACCXH OW ~ . p - ~ p bp c

~ h a a i c 8 1 ~ w s r t i m : ( sponynar B/b r E-JrJ'lPr , c 15 7 7 9 '/id, 1 21: _ 1

Chemical Fo t~ lu l8 2 /V k l e c o l a r ~ e i g h t / r zqz7 - - c

P(ysicd S t a t r 5/,1, // Sa lub i l i ty (H20) 1 I . . I C ~ o l l i r q point + * - - Flash Point & o u - t ' l P r o o k Vapor P r ~ a u r e / D s m i t y p,,..,f ? Q $ o t- - f reszfnq Point 7?7 '

Specif ic Gravity 7 , / 4 Wor/Cdor lhreshdld Flammable Limits

Incanpa tab i l i t i e s P C I ~ J , S t ! l J f l ; t r y / 1 I , c /, , p . f ~ r . , I _ - (

Bioloqical R o p e r t i s s :

TLV-TWA - Q. $4gy2,,,> ,*-I Odor Charact e r i a t i c

IDLH ,,1,1 :, rf f - . 1 klunmn Aquatic Rat/Houae

Route of Expanure eye , .qk;d ( r r r r+Pc t- zfi,, ,:,-' \ I t I

Carc imgm Terrtoqen Mutrgen

Handlirq Recommdationa r (Personal prot u t i v e measures)

P(P(/T/L( ,cpe,C.-/ (77 , , , 7:- , . f...,, 9: ' . > , p / : /. f ,.. .-, . . r

f o/o,c.s c f&-C~,4<,-!rA~ b ' Y

nonitorinq Recumendat ions r

Health Hazards and F i r s t Aid:

T-r I j c;,-/T + / , ., . I . - ~ L,, +:: ./', 1" ,Cr / f z . - f , ,% *,-

&,FG((,,/ ' i ) J t . p , : I,..! . ! , * , l , W f ' : ; ,, /

'recydld'pllMr

recycled paDer recycled paper .. .

( l t /BY ,DLD) , '

i!l,j :;;;;;;;;;;,;", wc~logr end rnvinvnmrn~

rrology end rnvironrnrnt

"

ecology a n d e n v l t o n m e n t , I n c .

HAZARD EVALUATION CF WMICXLS

memicai N- ~ l ~ ~ ; ~ , / f ( f l f t , . : . , ~ ) oat. Y - 2 ) C Y OOT N ~ / u . H . ~ o . I 0 Y< ~ o b *. Cr /,I tiodd CAS N d e r 7 7 ~ 3 - 41- Y v References Consulted ( c i r c l e ) a

NIOSH/OSHA h c k e t Guide Verschw run erck Index Hazardline

ry/b & o f J : * .. . / J / , / / / J A Z ~ , , / ; . . ; ' p i c d ~ u a r d o u i i - % t ~ s t l >

Chemical R o o e r t iu: (Synonymsa 1

Chemical ~ o r m u l r Holecular Weight 3 9, n ,O

Physical S t a t a 2 4 f , .?Pi

, ' S o l u b i l i t y (HZO) , F ~ c . ~ . : I P Boil i r p Point - J E t 'C

J Flash Point

m u + , Vapor Pressure/Deraity e.,:. . ~c Freezing Point -31 Li' ='/,

Spec i f i c Gravity 1 , I Wor/Wor Threshold 0, 03;-,.- Flonmabls L i m i t s - ~ n c m p a t a b i l i t i e s ~ C C I C ~ ,,, ,U ~ 0 : c g ~ - ' , . / l z 9 1- !*- 7 , , ...,,,.. : /bJl: , :, s -

Bioloqical Prooe r t i e s : 7 11 *

TLV-r*A 0 , I ? , I P 3 , . 7 Ffi 1 &A Wor C h a r a c t e r i s t i c / . b

IDLH (-ad M / m d-bn Til.: xpnAqua t i c Rat/Mouse L C) . a .,, ,. - -

Route of ~x~:avre i N h P /f I 0 $96 C& u ~ , l ~ * f i ~ i

v I ,

Carcinogen Teratoqen kt agen

Hendl inq Recommendation8 t (Personal prot c t t i v s m e s u r e s )

~ h c f l . ( , 1 / r ~ - <,PC( , I / c(o#~ / , I 5 €515 . !-. ,v - r ' . l V . I I L

C

Monitorinq Recunmenda t ions:

Disposal/Waste Treatment:

$ 4 , , 2 , I - , : : , ; - 1 , . r . . ,,-.- L / ; , . - & , * I . . ;

. / ( / c t w . : c ; y 'AAJ , , / , - I ~ P [ f f f , , : , P I - , c , r /A,J,I T I , - ? ,: -,, P , ~ , . . v : ~ , ~ ,,/ / ~L . .J , , : $14, ;Ie. v

Health Hezards and F i r s t Aid r

~ o o , ~ / (,j,,+nL t , & I ! f i r , , , p ,c. , m,.,q , i,.:,

Svmotas t Acuter r n 7 . k . f Ih 9 '-lf.~- Ivl trnal~r* ' +LL+ / ; J ; v

~- - - -

m r o n i c r ~ : ~ k r ~ I : r J I ~ J , A N 1 . h rod( h ~ y -,a c r~ . I

c , n / ~ f b ~ J n s n ~ t r r , l r , ~ . > , A /LO Gncjt . I , & ~ l p , ~ l '- . ./ . r . . . v

. , , b I * < ! ! . , ! , ,# I ,,,\il,,,,, ,, 375103

r ~ r y c l r v l v.71 01 t i ' f / a 3 , o ~ o ) recycled paper A- 15 I . v . . ~ ~ , . ! , ,,II,I ,.l lrir,~,~~,,l .,,,

r - m , e c 0 k 9 ~ ~ r l n d u ~ r 4 W e ~ ~ ~ ~ r n ~

ecology a n d e n v i r o n m e n t , i n c .

HAZARD EVALUAlION OF U i M I C A L S

C- - . Chemical Name 104 -L?€NE Date - , - ~ C , , ] q - L / . k q O O f N~IIIo/U.N~ Noo 24 Y Job Fb.

r, CAS N&er

References Consul ttd ( c i r c l e r

Hazardl ine

Toxic and Hazardous Sa fe ty Harxjal ACCI H Other:

Chemical R o p e r t ies: (Synanyma: M E ~ I ~ L E m €E13E 1.i-1 , . r . i . 1 I

Chemical Formula C.7 C ~ P Holecv l a r Weight 7 2 CuLr ~ ~ 2 5 ' ;

P h y s i c a l f t a t e LI.*D' " S t ~ l u b i l i t y ( H 2 O ) c . ~ ~ ~ , / , s ~ , ~ ~ ~ o i l i q P 0 i n t 771° 1' I

Flaah Po in t 4 0- F Vapor P re s su re /Dsmi t y 3 . A f r e e z i n g Poin t - (3C/'U~0 wHc. .,-,- 1 1 . 1 ' . t . > d

S p e c i f i c Grav i ty 0. ki,-(,.7 Odor/Odor Threshold JI~..I - f lammeble L i m i t s I.')'%. - ? ' I %

Bio l oq i ca l Prooer t i e s : ( ~ I L I ~ L 1

TU-TWA ;co ( T C P* PEL Wor C h a r a c t e r r s t l c - 3 ~ ~ . c r - < ! - L\ k t

IDLH ~ . C C ' @ ,,lvy Human I H L - 2 d f i % q u a t l c Rat/Hause 1 ,I

Route of Exposurs u r i n U 4 ncr3 . 5 ~ \ d

Carcinogen € X E P , ~ ~ F ~ ~ T A ~ . Teratoqen Hut agen

Hand1 inq Recommendations : (Pe r sona l p r o t e c t i v e m a s u r e s ) 41-1 c.1< -

I m p ~ e v , ~ ? ~ ' ; CLL~TH I,& E \ t I i . ~ ? P , , > I PIA-IC.?

ceGf\1a\c V A Q C Q /

( ' n p ~ p , y$,q u .,., > 1 c : r . o ,-,-,.-, 5 Y 1 6 A I

Honi tor inq Recamcndat ions , :

Disoosal/Waste Treatment:

~ M E G I T M E . D *. \NCIKIEIZ~~TIC~ '. I T QI',('~~OF(:.F- -rr, I ~ , _ ~ , ~ . ~ , C . I ~ R -. Sfi,dcc p p ,mnp r T ? . E ~ T I ~ E ~ \ ) T , i c ( ' ~ h > F I Z i r T i c . d f i r g 1) t c

c (.'.,-,rJ ,C ,'\ I g 'I L 2 .i_

Heal th Hazards and F i r s t Aid:

FLC~,H APE^ ~3 I.TI+ 4- . t I I i i , t I . I < \ <';:;I \ /

1-1 rV 11- @ ~ ~ i ] S l l ~ i > : 1 L C k! i- I . L':.. 1 I T r i d ( . .

~vmotoms: Acute: Cr\S 3 &b~zs7 , \ c~ . f % r l ~ - ~ ~ 2 . blttua2~ 1-1 I I

- e c o l o g y a n d e n v i r o n m e n t , i n c .

HAZARD EVALUATION OF CHCHICALS

>< YLEh3L Chemical Name Date l / -J 1 - 2 9 +

DOT N ~ I ~ / u . N . ~ o . 1'30 7- J O ~ ~ o . vw-= , . . ~ d 9'32-j CAS Nunbet

Ref erencea-Eonsu&&i r c l l ) : . \ . ;G:' ~erschvcrmn & r _ a Hazardline < ~ h r l s ( V O J . _ _ 11) \.

Toxic and Hazardous Safe ty Manual ACClH Other:

Chemical P r o p e t t i c s : (Synonyms: 3 1 n ~ ~ ~ ~ ~ t ) r ; ~ e & ~ ~ d ~ . X y l r \ L - 1

Chemical Formule C Y /-lro 1

k l e c u l a r Weight \c(,- cc L A Y L L S L

Physical S t a t e ~ p . ~ \ n S o l u b i l i t y (HZO) O.cCx-r3 j K Bail i r q Point ,*?'f.? 'F Flash Point 7 7 O Vapor Pressure /Demity 3 Freezing Point - 1 zL' S p e c i f i c Gravity O %L Odor/Wor Threshold 0 fFc.b?.- Flammable L imi t s \ . / I ' / , : - T.c)'& Incornpatabi l i t ies ~ T K L ~ ~ < ( - O % I D l Z F P s 3.i G ~ r 3 ( . - t \ ( ' t \\I=o.T, ,: I - i ' O ~ l ~ 1 :

/

B i n loqica l P roper t i e s :

TLV-TYA 100 p ~ t r b PEL Wor C h a r a c t e r i s t i c I - \ I < C ~ ~ ~ ~ ~ ~ - T I ( : ,

IDLH \ c ? , ~ : ( . r c~,v\ Humeni H i T C ~ - 2 a ' P A q u a t i c Rat/Houge 7 t rc O:C Tcs' ,+""/ > I -

Routs of Exposure ~d iraCE , SKI^

Carcinogen E X c ~ ~ \rc,~-d~r.\( , Teratogen Hut aqen

Hendl inq Recornmendat iona : (Personal p r o t e c t i v e m a s u r e s )

lmpgcvlcc.; C L C : ~ . I , , " ( - ' L C E i \ E L - , I \ V ~ , I

Monitorinq Recamendat ions :

Disposal/Waste Treatment:

osjjn 3 ~ n ~ ~ n p - i , 21 C ~ % \ ~ \ \ p , \ o ( , . , - \ , , p L l ~ : , i

Health Hazards and F i r s t Aid:

SK\Q - ~ofi:il\ L L ) Sonf> I- L ~ , - ; I F Z ',, G?C,> - \:I : - , , I ,...,/ ,. I ,- it - J

?E~,~O,IF rn' FEES; r t l e IF s ~ C ; z c ' c ~ ~ n E

Svmotoms: Acute: EYE t r v \ o C c l , ~ _ C _ I T-\F 1-rli3PP-F 1 EL' IT, ) , . . - -i- ~ (' k\ ', -- - * p ~ ~ ~ ~ I q ~ ~ . I I ,. 31 , c - k 3 p i11 i ~ , C - , l ~ ; ~ 7 1 ~ , , . 1 ; r ~ l l , , . ~ ~ ~ ,J

Chronic: r \ o ( ! ~ E d ? T k h r l S RW.E . \ \ ) , X - p j 3 ~ , - ) \ , f ) c- I-- ij: ~JF-

-r A-17 e r o l y y lend e R L r u n W t 8 ~ . 8 8 1

l a , < : < > 1 < ) [ : y ; i l b ( l t1,IlV I r o l l ~ l ~ ! I l I,, I I ) < :

Ilnzrrrd Eva lua I. i oil o T Cltcrnj ca 1 :; IZegion V - Cliicago

Chemical Name Cadmium llate 4 - 21-'65' WLK)'~' Classification Jut, Nurnbcr ;- ( /J ?/ 9 .) ) -.-

I

c ; a1 so inc 1 udc M!;L)S if tljjprojjra tc? . ) Index Hazard1 irre ~ 0 1 . 1 1 1 )

Safety HanualC:'$$) f i m m xicology , Niostl Occupa tiorial Heatliguid

l l f l A l , l l , l ' I l : ( S y n r y ~ n s : C . 1 '771eU 1 C:llen~ical Foi-nlula Cd MW112.4 Ioniza!.iol~ i-'ot.c!r~t.i;~l--N~-& -- Physical State Crystals Boiling Point141Z0 F Freezing Point C O Y o F' Flash Point N/A Flammable Limits N/A Vapor Pressure Specific Gravity/Density 8.642 Odor/Odor Threshold None

Solubility-water: Insoluble Solubility-other: Incornpatabilities & Reactivity:Strong o x i d i z e r s , s u l f u r . s e l e r ~ i u m , z i ~ ~ c , a m ~ ~

TOXICOLOGICAL PROPERTIES: (dust 1 (Fume ) Exposure Limits: TLV-TWA (ACGIH) .0 5m,E/m3 PEL ( OSHA ).2rn,e/n13 . 1 m~/ni3

STEL None est. Ceiling Limits .6m,q/m3 / . 3mfi/m3 1DLH 4U m,e/n13 - Toxicity Data: (Indicate duration of study) Human ; IHL Tclo 39m,c/m3L20M Dermal Oral Rat/Mouse;IHL Dermal Oral LD5U 22511le/k.~ Aquatic: N/A Other : Carcinogen animal-POS Mutagen exp. - Reproductive l'oxine-y~er .-tcrat_ooge

Iloute(s) of exposure - (circle all that apply): haJ a Lioa f i l ~ e s t i c ~ ~ ~ Dermal Contact Eye(ocu1ar)" Llermal Absorption ptther

IMNLILING IECOMMENL)A1l'10NG: (personal protective measures) Respirators: > any detectable air concentraton - use SCBA Protective Clothing: Chemical resistant gloves & boots. Special Equipment: None

DISPOSAL.FlIZE and SPILLS:(Use numbered codes;see attaclled sllects for explanation.)

Disposal P Fire 13 Leaks&Spills 7.10 Decomposition Products: Toxic Cd fumes

FIRS?' AID: - INL: Large quantities of water, inducevoniiting, medical a t.terit IHG: Remove to fresh air,art. resp.if necessary, med.attent.imrned. Eye/Skin: Irrigate/wash with water for at least 15 mjn.

SYMP'l'OMG : - -- acule(immediate) exposure effects: IHL: irritation of nose & ttlroa L , ~ - I I c J \ delay before symptoms of cough, chest pain, nausea, vomi tirlg, dj zzir~ass,

b' ,hills, stomach distress. IL4G Nausea, vornitir~g, diarrllea, ab0111i11nl cranrps

chronic(1ong term) exposure effects: loss of srnel1,ulccration of rlose, shortness of breath, 1 iver damage, kidney damage (most affected ) , n ~ j I d

, a ,lll,t\ ,11111 0 1 9 , i ~ a n v t l r \ q . t t ~

ane~nia,emphyeerha;~linked to cancer & hypertension. A- 18

r c ~ r o d u c t i ~ ~ ~ ~ & & ~ ~ t s : Possibly cuases prostate caw&w~+ d t % ~ 3 T b ~ r n i c i n : l \

l i a ~ a r d Evoluo Lion of C l ~ c r n i c a l r; --. .

Region V - Chicago -

Benze Dato L/ /J

cmical N n m e ne - FY

n'wassification Job Number if /J -!

FERlTNCL;.S CONSU.L~EEL) (circle; also include MSDS i f/\Poclcot Merck Index eazPard1 i 119 @sll/c!st

G l f 4 -c & Hazardous Safety Manua other:

IE&IC~L~I~OP~~RTIES: (Synonyms: benzol, benzole, cyclohexatr i crle)

c11iica1 Forn~ula- Cs IIG MW 78 1or1izaLiori PclLc!~~C,iaL---$~:i!l..!!c-v-- lysical State liquid Boiling Point 176" F F'rec-.zir~rr t'oir~t-42" F ash Point 12°F ~lammable Limits 1.3-7.1% Vapor Pressure 75111rn becific Gravity/Density 0.879 Odor/Odor Threshold 4.68 P P I ~ llubility-water: sliahtl~ Solubility-other: tcompatabilities & Reactivity: strong oxidizers,chlorine.bromine

)XICOLOG 1 CAL PROP&RgSI ES : :posure Limits: TLV-TWA (ACGIH) 10 P P ~ PEL (OSHA) 10 pvrn STEL none Ceiling Limits >25<50pprn/lOmin L D L H 2UOU PPIII - )xicity Data: (Indicate duration of study) Human ; IHL Tclo 100/CNS Dermal Oral l ' d l m / k ~ : CNS Rat/Mouse;IHL Tclo 50/24H Dermal Oral LD50 3UOUm~/kg

latic: Tlm96:lOO-10ppm Other: IHL:Man TC 2100m~/m3/4Y; carc.

'Y cinogen human-sus Mutagen exper. Reproductive T o x i n e x p e r . )u e s of exposure - (circle all that apply): f l r i t ~ a l a t i ~ ~ r l p , e s t l o ~ ~ :r~nal AfS Con t a c q y e ( ocular> @ern,al AbsorptioQ Other

SULING RECOMMENDATIONS: (personal protective measures) zspirators: 10 ppm use SCBA rotective Clothing: excel-viton;good-neoprene;saranax;poor-but~l,~~atural lbber for gloves. Avoid skin/eye contact. ~ecial Equipment: none

LSPOSAL. FIIE and SPILLS: (Use numbered codes; see attacl~ed sl~celri for explanation.)

isposal D . Fire 6.7 Leaks&Spills 3.4-5.6.9 :composition Products: toxic fumes of carbon dioxide,carbor~ monoxide

[RST AID: JG: Do not induce vomiting,give water or milk,medical attent.. imnled. iL: Remove to fresh air,give artificial resp. if needed,medical attent. re/Skin: Flush with water,rinse/wash skin with soap & water thorougtily.

IMPTOMS : :ute(immediate) exposure effects: skin irritant,CNS depressant,rnostly 4~,initial excitation followed by headache,dizziness,vomiting,delirium, - re exposure may see trernors,blurred vision,shallow resp.,convulsions. w -~ronic(long term) exposure effects: anorexia,drowsiness,arlen~ia,bleeding lder skin,reduced blood clotting;liver,kidney,bone marrow danlage,leukemia.

# ,? . ! I",! \ ,I.,>, "<'I"!.\ 1 1 1 ' 1 1 1 1 , , , 1 1 b , , 1 1 1 , 1 1 1

-productive efrecks: None reported in humans.

recycled paper A- 19 rrology and rn+onrneni 12

C t r c m i c a l Nnmc Lead L)a t c y-21- [/ - -

L C l a s s i I i c a t i o n - J o b Nurnl~cr C/o '/O(!d 7 4 ; j 9 - 9 2 - 1 Chi; Numlbcr

a l s o i t i c : S ~ ~ ( l c Mf;JI!; i IrideA Qla:;-a~-d l j

S a f e t y Marlua

I~:M1-CA~L-J'~~OJ~li:ll'~l~~~: ( S y r ~ v t ~ y ~ n s : W l i i tc l e a d , pl ~ i ~ t ~ t ~ \ i ~ i i I e r i i i c a I k'c.11-11111 1 a- - Fa LJ Id\,' 2Ll'; f c~rti ~ 3 t . i or] Pcqt f a r i t i i~ I - ll,'-A y s i o a l S t a t e V a r i a b l e B o i l i n g P o i r ~ t 31 64" F F r e c z i r l g P C J ~ I I ~ a s h P o i n t I n c o m b u s t . F lammable L i m i t s Incornbus Vapor P r e s s u r e v a r i a b l e e c i f i c G r a v i t y / D e n s i t y 1 1 . 3 @61°FOdor / Odor T l ~ r e s h o l d None l u b i l i t y - w a t e r : I n s o l u b l e S o l u b i l i t y - o t h e r : - c o m p a t a b i l i t i e s &. R e a c t i v i t y : S t r o n g o x i d i z e r s , p e r i o x i c i e s , a c Live n i e t a l s

XICOLWICAL PlIOPE11TIES: p o s u r a L i m i t s : TLV-TWA ( A C G I H ) . 1 5 r n ~ / r n 3 PEL ( OStlA 1- 5UugLn13 STEL None e s t . C e i l i n g L i m i t s None e s t . I D L H V a r i a b l e - x i c i t y D a t a : ( I n d i c a t e d u r a t i o n o f s t u d y ) Human ; I H L Dermal O r a l TdlU 4 % ) n a k ~ / 6 Y Hat/Mouse;IHL Dermal O r a l I ' d lo 7YUnig/k~ F 3t ic : Unknown O t h e r : T o x i c i t y v a r i e s w i t h l e a d c p d s . U r J c i n o g e n Inclef . Mutagen I n d e f R e p r o d u c t i v e T o x i r ~ . e . x p , t e r a t o p s . ~

o f c x p o s u r e - (c i rc le a l l t h a t a p p l y ) : 0 r l h a l ; t E*M lEva oc ~ j o 5 c r 1 ~ e s t i o a

u l a r D h a 1 ~bsorpt-1011) O t h e r

NDLJNG' RECOMMENDATIONS: ( p e r s o n a l p r o t e c t i v e m e a s u r e s ) s p i r a t o r s : 5mg/ms h i g h e f f i c i e n c y p a r t i c u l a t e r e s p i r a t o r , o t l l c r

c o n c e n t r a t i o n s - SCBA. o t e c t i v e C l o t h i n g : Avoid s k i n and ey? c o n t a c t ecial E q u i p m e ~ ~ t : None . .- . SPOSAL.FIRE a n d SPILLS:(Use numbered c o d e s ; s e e a t t a c l l e d s t i e c t s f o r

e x p l a n a t i o n . ) s p o s a l P F i r e 1 3 L e a k s & S p i l l s 7 . 8 . 1 0 z o m p o s i t i o n P r o d u c t s : T o x i c fumes o f l e a d

!ET A I D : 2: G i v e w a t e r , i n d u c e v o m i t i n g , m e d i c a l a t t e r l t i o n ininted. L: Move t o f r e s h a i r , a r t i f i c a l r e s p . i f n e c e s s a r y , m e d i c a l a t t e r l t . % / S k i n : I r r i g a t e / w a s h w i t h w a t e r . Wash s k i n t h o r o u g l ~ l y w i t h s o a p & w a t e r .

~P*I'OMSL ~ t e ( i m m e d i a t e ) e x p o s u r e e f f e c t s : C u m u l a t i v e r i e u r o t o x i ~ I - C O I ~ I I I I C ~ I I ~ ~ o c c u r s x i p r o l o n g e d e x p o s u r e . Symptoms i n c l u d e s t o r n a c i ~ d i s t r e s s , vonii t i i l g ,

? l e a , b l a c k s t o o l s , a n e m i a , n e r v o u s sys ten i e f f e c t s . V i c ( l o r l [ : t c r n ~ ) c x p o s u r c effects: 3 c l i r i i c s l typer,:a-t~j l ~ ~ ~ ~ ~ r ~ t . ; ~ ~ . y - . a t , o l r i i r r a I i n , discor;if o r t , c o r ~ s t i p a t i o n o r d i a l - r h e a , m e t a l 1 i c t a s t t , , l e a d 1 i115 or, gun1 idr tche . b - n i i e r o m u s c ~ i l a r , m u s c l e w e a k n e s s , j o i n t / m u s c l e p a i n , d i z z i n e s s , jonlnia, p a r a 1 y s i s c - e r ~ c e p h a l i c : b r a i n i n v o l v e n i e r ~ t , s t u ~ ~ @ y , , , , ~ ; . , ~ ~ ~ ~ , , ~ . f : a ~ ) ~ , r a r e .

( 1 , d ,,.g,<:t -)reductive e f f 2 c b s . Human e p i d . s t u d i e s have c o n c l u d e d i l l a t . l e a d i s a I s(:lr~ to ~nclle &. f er11s1 e ger-ni c e 11s ; i r l c r e a s e d i ~ l c i c i e i ~ c f - of' I I I ~ - ~ c a l . r j ;tp,c:rs , L l l b i r t f l s , i n f e m a l e s : s ~ e r m ~ p D T ~ q c , i n n fi. ~ ~ S % ~ % ' Z E ~ $ L ? I ~ Z T ~ P ' ~ I+:.* 4 . -

A- 20

o A 1 1 E6E d r i l l i n g p e r s o n n e l w i l l have r e a d and u n d e r s t o o d t l ~ e t e rms o f E 6 E d r i l l i n g SOP.

o D a i l y i n s p e c t i o n of r i g and components - o b v i o u s o r q u e s t i o n - a b l e s a f e t y c o n d i t i o n s w i l l be c a u s e f o r work i n t e r r u p t i o n .

o Only approved d r i l l e r s w i l l r e m a i n i n p r o x i m i t y t o b o r e h o l e d u r i n g d r i l l i n g and i n any e v e n t , a n a p p r o x i m a t e . 4 ' x 8 ' s u p e r - e x c l u s i o n a r e a w i l l be i n p l a c e a round moving a u g e r . No p e r s o n n e l w i l l e n t e r t h i s zone w h i l e d r i l l i n g i s ongoing.

o C o n t i n u o u s O, / exp los imete r m o n i t o r i n g a t b o r e h o l e u s i n g remote s a m p l i n g hose .

o A l l f i e l d team members w i l l be b r i e f e d on p lanned d r i l l i n g o p e r a t i o n s and p o s s i b l e problems b e f o r e work commences on day one . A l l w i l l b e shown l o c a t i o n and - o p e r a t i o n o f " k i l l s w i t c h e s " . These s w i t c h e s w i l l be o p e r a t i o n a l l y checked e a c h morning.

o F i r e e x t i n g u i s h e r ( s ) w i l l b e s t a g e d n e x t t o r i g b e f o r e d r i l l i n g / r e f u e l i n g o p e r a t i o n s .

o W e l d i n g / c u t t i n g a c t i v i t i e s w i l l o n l y be pe r fo rmed a t a d i s t a n c e f rom i g n i t i o n s o u r c e s approved a s s a f e by t h e S i t e S a f e t y O f f i c e r (SSO), Team L e a d e r .

o A p p r o p r i a t e p e r s o n n e l p r o t e c t i v e equipment ( b a s e d on h a z a r d s a s s o c i a t e d w i t h assumed w e l l c o n t a m i n a n t s ) w i l l b e worn a s d i r e c t e d by t h e SSO and t e rms of t h e s i t e s a f e t y p l a n . A s a minimum,- s t e e l - t o e d b o o t s , h a r d - h a t s , and f a c e s h i e l d s w i l l b e worn d u r i n g any a c t i v e d r i l l i n g .

o O u t r i g g e r s t a b i l i z e r s must be i n p l a c e b e f o r e d r i l l i n g commences. The r i g must a l s o be l e v e l e d .

A

o D r i l l r i g boom must be h o r i z o n t a l d u r i n g movement of r i g . I t w i l l n o t be e r e c t e d w i t h i n 25 f e e t o f o v e r h e a d l i n e s .

o E l e c t r i c a l s t o r m s w i t h i n e a r s h o t of t l ie j o b s i t e w i l l be c a u s e f o r work t e r m i n a t i o n u n t i l deened s a f e by t h e SSO and Team Leader .

o Wllere underground u t i l i t i e s a r e s u s p e c t e d i n a v a c i n i t y o f o p e r a t i o n s , t h e l o c a l u t i l i t i c s s h a l l be c o n t a c t e d . Where u t i l i t i e s a r e i d e n t i f i e d , t h e y s h a l l b e marked u s i n g f l a g s .

o Wlrc&e b u r i e d drums, e t c . a r e s u s p e c t e d , a,.,A.ull,,~sur;zr,wy,,,of recycled 11;'

recrc~e&bling zone i s r e q u i r e d u s i n g nppropriaae1lq~4n~~rurnrptt!'btion r i o r t o ground b r e a k i n g .

recyciJpaper ecology and environment

A- 2 1

o Utlly t r a l n c d , e x p e r i e n c e d s t a f f w i l l o p e r a t e t l lc c a t t l e a d . P e r s o n r i e l n u s t be k n o w l e d g e a b l e i n s a f e good p r a c t i v e pro- c e d u r e s f o r c a t h e a d u s e .

o O ~ l l y p r o p e r l y l i c e n s e d s t a f f w i l l d r i v e t h e d r i l l r i g . A ' d a i l y s a f e t y c h e c k of t h e v e h i c l e w i l l b e c a r r i e d o u t by t h e d r i v e r , p e r E6E p r o t o c o l .

o C l i o l b i l ~ g o n v e r t i c a l boom is n o t p e r m i t t e d by L 6 E s t a f f .

recycled paper

recycled paper

t ~ a . ~ ~ l * ~ ~ \ t t t t a l I . I B > ~ ~ ~ D I ~ ~ U ~ ~ , I B I

ecology and environment r -

APPENDIX B

PEOTOGRAPEIC LOGS

recycled paper rculoey and rnvironrnent

ecology and environment, inc.

P B O T O G R A P B I C R E C O R D

Client: NYSDEC E r E J o b N o . : YN4080

Camera: Make Kodak Fling 35mm Disposable SN : N/A .

Photographer: G. Florentine Date/Time: 5/17/89 1220

Lens: Type N/A SN: N/A Frame No.: 6 (Roll 2 )

Comments: View to north of proposed GW-7 well location. Note area is surrounded by junked vehicles.

B- 2 ~c.olugy and rn~uironment recycled paper


P B O T O O R A P B I C R E C O R D

Client: NYSDEC E & E Job No.: YN4080

Camera: Make Kodak Fling 35mm Disposable SN: N/A

Photographer: G. Florentino Date/Time: 5/17/89 1235

Lens: Type N/A SN: N/ A Frame No.: 5 (Roll 2)

Commanta: View to south of proposed GW-1 well location (stake). Note: Driveway in foreground and

Conrail tracks in background.

recycled paper B- 3 rrolog? and rnvvironrnent

ocology and onvironmont, inc.

P H O T O Q B A P B L C R E C O R D

- - ~- pp

Client: NYSDEC E r E J o b N o . : YN4080

Camera: Make Kodak Fling 35mm Disposable SN: N/A

Photographer: G. Florentino Dato/Timo : 5/17/89 1345

Lens: Typo N/A SN: N/A Frame No.: 4 (Roll 2)

Comments: View to north of proposed GW-2 location (stake). Note: Conrail tracks in background.

recycled paper B-4 ecology and environment

ecology and environment, inc. I

I client: NYSDEC E L E Job No.: YN4080 I 'cr

Camera: Make Kodak Fling 35mm Disposable SN : N/A I

P B O T O Q R A P H I C R E C O R D

Photographer: G. Plorentino Date/Time: 5/17/89 1430

Lens: Type N/A SN : N/A Frame No.: 3 (Roll 2)

Comments: View to vest of proposed GW-5 well location (stake) on edge of fill area.

recycled paper B- 5 r~.olopy end environment


1 client: NYSDEC E c E J o b N o . : YA4080 I Camera: Make Kodak Fling 35mm Disposable SA : N/A

Photographer: G. Plorentino DatefTime: 5/17/89 1620

SN : N/A Frame No.: 2 (Roll 2) I Comments: View to west of proposed GW-4 well location (stake). Note: Site boundary is to right, I

I490 is to left. I

B- 6 ,.cology and cnvimnmen~ recycled paper

pcoloqy and environment, inc.

P E O T O Q P A P H I C R E C O R D

Client: NYSDEC E L E Job No.: YN4080

Camera: Make Kodak Fling 35mm Disposable SN : N/A

Photographer: G. Florentino Datapime: 5/17/89 1710

Lens: Type N/A SN: N/A Frame No.: 1 (Roll 2)

Comments: View to west of proposed GW-3 well location (stake). Note: Site boundary is to right,

B- 7 ecology and environnler~t recycled paper

ecology and environment, inc. I P H O T O O R A P ~ I C R E C O R D I ..

I NYOYBDEC E L E Job No.: YA4080 I Camera: Make Kodak Fling 35mm Dispos~blo SN : N/A I Photographor: 0 . Florontino Dato/Timo: 5/17/89 1145

Lens: Typo N/A SN : N/ A Framo No.: 0 (Roll 3)

Comments: Viow to west of proposed GW-6 well location (stake).

recycled paper

APPENDIX C

GEOPHYSICAL SURVEY


ENGINEERING INVESTIGATIONS AT L INACTIVE HAZARDOUS WASTE SITES

PHASE I1 INVESTIGATIONS

GEOPHYSICAL SURVEY GOLDEN ROAD DISPOSAL SlTE

SlTE NUMBER 8 2 8 0 2 1 TOWN OF CHILI, MONROE COUNTY

June 1989

Prepared for:


50 Wolf Road, Albany, New York 12233 Thomas C. Jorling, Commissioner

Division of Hazardous Waste Remediation Michael J. O'Toole, Jr., P.E., Director

Prepared by:

Ecology and Environment Engineering, P.C.

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Sect ion

TABLE OF CONTENTS

Page

1 INTRODUCTION .......................................... C-5

2 OBJECTIVES ............................................ C-6

3 METHODS ............................................... C-7

4 DATA INTERPRETATION ................................... C-8

5 CONCLUSIONS AND RECOMMENDATIONS ....................... C-14

Appendix

..................... C-1 MAGNETOMETER AND EM31 SURVEY DATA C-15

C-2 MAGNETOMETER AND EM31 SURVEY CONTOUR MAPS ............. C-30

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LIST OF ILLUSTRATIONS

Figure Page

4 - 1 Geophysical Survey and Proposed Groundwater Monitoring Well Locations, Golden Road Disposal Site, Chili, New York ............................................... C-9

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1. INTRODUCTION

This geophysical investigation report for the Golden Road Disposal

site (I.D. No. 828021) on Golden Road in Chili, New York, was prepared

by Ecology and Environment Engineering, P.C. (E & E), under contract to

the New York State Department of Environmental Conservation (NYSDEC).

The geophysical investigation consisted of an EM31 (electromagnetic

terrain conductivity) survey and a portable proton magnetometer (total

earth field magnetics) survey. This report includes field data

(Appendix C-1) and contour maps (Appendix C-2) for the' geophysical sur-

vey performed at this site on May 17, 1989, as part of the Phase I1

Investigation. Additionally, interpretations of the data generated,

along with conclusions, are provided in this report.


2. OBJECTIVES

The geophysical survey program at the Golden Road Disposal site was

designed to achieve several general goals. The main objectives of the

geophysical methods used were to optimize the locations of the seven

proposed on-site groundwater monitoring wells; reduce the risks asso-

ciated with drilling into unknown terrain and wastes; reduce overall

projecttime and cost; improve the accuracy and confidence of the inves-

tigation; identify the existence and boundaries of buried waste or

groundwater contamination plumes; and to determine vertical and

horizontal anomalies.


Grids were set up at each of the prospective monitoring well loca-

tions. The X and Y axes of each survey grid were initially oriented

approximately east-west and north-south, respectively. Precise compass

orientations were then obtained for each of the survey grid axes. Sur-

vey grid coordinate 0,O is located in the southwest corner of each con-

tour map. Semi-permanent wooden stakes mark the proposed well locations

for reference during drilling.

The dimension and station spacing of each survey grid varied due to

physical restrictions at each proposed site (i.e., dense vegetation,

steepness of slope, standing water, metal debris, railroad tracks, power

lines, fences, etc.). Both horizontal and vertical dipole readings in

north-south/east-west orientations were recorded at each survey grid

node when performing the EM31 survey. The effective depths of

penetration provided by the EM31 in the vertical and horizontal dipole

modes is - <18 feet and - <9 feet, respectively. These depths were

considered adequate to delineate any buried materials which may be

encountered while drilling. Magnetometer readings were recorded at each

node in both north-south/east-west orientations.

All geophysical field data were initially recorded in two log books

dedicated to this site investigation. Magnetometer data were reduced by

averaging station readings for north-south and east-west orientations

and correcting these values for diurnal variation based on background

station readings. EM31 conductivity data were averaged for north-south

and east-west orientations for both vertical and horizontal dipole posi-

tions. The reduced geophysical data (see Appendix C-1) were then

plotted and contoured for each survey (see Appendix C-2).

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4. DATA INTERPRETATION

The purpose of interpreting the results of the magnetometer and

EM31 surveys is to provide a probable explanation for anomalous geophys-

ical contours. The presence of buried utilities, metal objects, wastes,

and contaminant plumes is often manifest as relatively elevated or

decreased station readings and gradient values. The following inter-

pretations are based on the contour maps generated from magnetometer and

EM31 data which are listed in Tables 1 and 2 in Appendix C-1. The

survey grids encompass each of the seven groundwater monitoring well

locations as proposed by NYSDEC in the Phase I1 Investigation Work Plan

for the Golden Road Disposal site (see Figure 4-1).

The following discussion provides details of each of the seven

survey grids:

Survey Grid Area No. 1

A review of magnetometer data contours at the no. 1 grid location

indicates that this 1,200-square-foot survey area is without substantial

geomagnetic anomalies. The risk of drilling into any shallow ferrous

material is expected to be minimal.

In general, low electromagnetic conductivity values measured with

the EM31 (3.5 to 12.5 millimhos/meter) were observed in both vertical

and horizontal dipole modes. These low values indicate the absence of

near-surface metal debris and/or contamination. Higher values and

negative values were observed in the northeast corner and along the

western border of the survey grid. These values are the result of

interference caused by a hay wagon, farm machinery, and other metal

debris. Negative conductivity readings indicate very high conductivity

beyond the capabilities of the instrument.


COW PASTURE

JUNKED M H

SURVEY GRID NO. 2

Figure 4-1 GEOPHYSICAL SURVEY AND PROPOSED GROUNDWATER MONITORING WELL LOCATIONS

The installation of the proposed monitoring well GW-1 at the loca-

tion indicated on the contour map is suitable. The well location may

also be moved to any area within the survey grid if required to facil-

itate rig access.


A review of magnetometer data contours at the No. 2 grid location


geomagnetic anomalies. There is an isolated area at coordinate 30,10

where the magnetic field decreases. This may be due to the presence of

a very small, shallow object because an anomalous response by the EM31

at the same station was lacking. The risk of drilling into any shallow

ferrous material within this grid area is expected to be minimal.

Low electromagnetic conductivity values measured with the EM31 (7.5

to 10 millimhos/meter) were observed in both vertical and horizontal di-

pole modes. These low values indicate the absence of near-surface metal

debris and/or contamination.


tion indicated on the contour map is suitable. The location may also be

moved to any area within the survey grid if required to facilitate rig

access.



indicates that this 1,200-square-foot survey area contains several

geomagnetic anomalies. The apparent anomalies are located in the

southern portion of the survey grid. The source of these anomalies is

probably due to interference from construction material of Interstate

490 along with the effects of passing vehicles approximately 10 feet to

the south of the survey grid.

Electromagnetic conductivity values measured with the EM31 (13.5 to

41.5 millimhos/meter) were observed in both vertical and horizontal di-

pole modes. These values were relatively low and consistent in the

central portion of the survey grid, thus indicating the absence of near-

surface metal debris and/or contamination. Conductivity increased to

the south and north of the survey grid. Once again, the increase to the

recycled paper rrulogy and envirnnrnenc

south was caused by Interstate 490, and the increase to the north was

due to the presence of a fence 10 feet to the north of the survey grid.




access.



indicates that this 1,200-square-foot survey area contains one

geomagnetic anomaly. This anomalous area in the southeast corner of the

survey grid is probably due to the effects of Interstate 490

approximately 10 feet to the south of the survey grid. The risk of

drilling into any shallow ferrous material within this grid area is

expected to be minimal.

Electromagnetic conductivity values measured with the EM31 (12.0 to

44.5 millimhos/meter) were observed in both vertical and horizontal di-

pole modes. These values were relatively low and constant in the

central portion of the survey grid, thus indicating the absence of near-

surface metal debris and/or contamination. Conductivity increased to

the north due to the presence of a fence and to the south due to the

effects of Interstate 490 ten feet outside the survey area.




access.



indicates that this 1,600-square-foot survey area contains two

geomagnetic anomalies. These anomalous areas, located in the northwest

corner of the grid and at coordinate 10,20, probably represent small,

shallow metallic objects because of the lack of anomalous responses of

the EM31 in the same areas. Care should be taken when drilling in this

area because it appears the survey grid is located on fill material.

recycled paper ecology and envimnrwnt


to 14.0 millimhos/meter) were observed in both vertical and horizontal

dipole modes. These low values indicate the absence of near-surface

metal debris and/or contamination.


tion indicated on the contour map is unsuitable due to the presence of

the magnetic anomaly. The location should be moved to any other area

within the survey grid outside of coordinates 0,40 to 10,40 and 0,20 to

10,20.




geomagnetic anomalies. The risk of drilling into any shallow ferrous

material within this grid area is expected to be minimal.


to 9.5 millimhos/meter) were observed in both vertical and horizontal

dipole modes. These low values indicate the absence of near-surface

metal debris and/or contamination.

The installation of the proposed monitoring well GW-6 at the

location indicated on the contour map is suitable. The location may

also be moved to any area within the survey grid if required to

facilitate rig access.



indicates that this 600-square-foot survey area contains several

geomagnetic anomalies. The main cause of these anomalies is

interference from adjacent junked vehicles. The risk of drilling into

any shallow ferrous material within this grid area is unknown due to the

low reliability of the data.

Electromagnetic conductivity values measured with the EM31 ranged

from 12.3 to 31 millimhos/meter along with negative values along the

borders of the survey grid in both vertical and horizontal dipole modes.

Negative meter readings indicate very high conductivities beyond the


capabilities of the instrument. These high values also were caused by

the presence of the junked vehicles.

The installation of the proposed monitoring well GW-7 at the

location indicated on the contour map is questionable. The well should

be moved to a location free from cultural interferences, or the vehicles

should be removed and the area should be re-surveyed.


5. CONCLUSIONS AND RECOMMENDATIONS

Based upon the interpretations discussed in Section 4, the proposed

locations of 5 of the 7 groundwater monitoring wells appear to be

satisfactory with only minor adjustments. On-site field observations

indicate that survey grid area no. 5 is probably located over a fill

area. Particular care should be exercised in order to avoid drilling

through potentially hazardous material. The location of GW-7 should be

moved to an area free from cultural interferences, or the vehicles

should be removed and the area re-surveyed.

Prior to drilling, the underground-utility locating service should

be contacted to indicate possible public utilities buried in the vicin-

ity of the drill sites.

All proposed well locations should be confirmed with a NYSDEC

representative prior to the commencement of drilling, especially GW-5.

The presence of a magnetic anomaly at the GW-5 well location indicates

that this well should be moved to an area outside the 0,40 to 10,40 and

0,20 to 10,20 coordinates as discussed in Section 4.

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APPENDIX C-1

HAGNETOIIETER AND

EH31 SURVEY DATA


Table 1

AVERAGE NORTH-SOUTB/gAST-WEST HAGRETOMETER READIAGS

WLDEA ROAD DISPOSAL SITE

Grid Ao. 1

Station $

Average N-S/E-W (Gammas J

Corrected Data* (Gammas J

*Data has been corrected for natural magnetic fluctuations (i.e., drift) by using data obtained at an on-site base station.

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Table 1

AVERAGE NORTH-SOUTE/EAST-WESF ~ U E T O n E T E R READINGS


Grid No. 2

Station #

Average N-S/E-W (Gammas

Corrected Data* (Gammas )



AVERAGE AORTA-SOUTB@AST-WEST MGKETOMETER W I N G S


Grid Ro. 3

Station #

Average N-S/E-W (Gammas )



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T a b l e 1

AVERAGE AORTB-SOUTH/EAST-WEST MAGlVETOHETER READIAGS

GOLDEN ROAD DISPOSAL S I T E

G r i d A o . 4

Station $

Average N-S/E-W (Gammas




AVERAGE NORRI-SOUTIf/EAST-WEST U A G A E M H E T E R READINGS


Grid No. 5

Station #


Corrected Data* (Gammas)



AVERAGE NORTH-SOUTB/EAST-WEST MAGNETOMETER RGADIRGS

GOLDEA R O M DISPOSAL S I T E

G r i d N o . 6

Station il

Average N-S/E-W Corrected Data* (Gammas ) (Gammas )

'Data has been corrected for natural magnetic fluctuations (i.e., drift) by using data obtained at an on-site base station.


T a b l e 1

AVERAGE AORTB-SOUTErnT-WEST MAGHETOUETXR R E M I A G S

GOLDEA ROAD DISPOSAL S I T E

G r i d A o . 7

Station #


Corrected Data* (Gammas)



T a b l e 2

AVERME IlORTE-SOUTE/KAST-WEST GROWtD COICDUCTIVITY READIUGS

WITH EM31

GOLDEU ROAD DISPOSAL S I T E

S u r v e y G r i d I l o . 1

Vertical Dipole Horizontal Dipole Station # (millimhos/meter) (millimhos/meter)

O,O 9.5 8.0

0,lO 36.5 Neg .

0.20 24.0 Ncg . 0.30 13.0 3.5

0.40 12.0 11.5

0,50 Neg . 18 .O

0.60 11.0 8.5

10,O 8.0 7.0

10,lO 9.0 7.5

10.20 7.0 8.5

10,30 8.0 8.5

10,40 10.0 11 .O

10.50 8.5 12.5

10,60 11.0 9 .O

20,o 10.0 9 .o

20,lO 10.5 8.5

20,20 10.5 8.0

20,30 11.5 8.0

20,40 8.5 11.5

20.50 11.0 11.5

20,60 36.0 12.5

[UZ]YN4030:D2419, #1638, PM=30

Neg. = Negative meter reading. This is caused by very high conductivity beyond the capabilities of the instrument .

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AVERAGE UORTH-SOm/EAST-WEST G R O m C O H D U C T I V I ~ RRADIUGS

WITH ruul

GOLDEU ROAD DISPOSAL S I T E

S u r v e y G r i d Uo. 2

Vertical Dipole Horizontal Dipole Station 1 (millimhos/meter) (millimhos/metor)


Tabla 2

AVERAGE UORTH-SOUTE/gAST-WEST GROUUD COWDUCTIVITY READIES

WITH E m 1

GOLDEU ROAD DISPOSAL SITE

Survey Grid Uo. 3



Tabla 2

MLDEU ROAD DISPOSAL SITE

Survey Grid no. 4

Vertical Dipole Horizontal Dipole Station % (millimhos/meter) (millimhos/meter)

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AVERAGE IIORT6-SO--T-WEST GROIJDD M U D U C T I V I R R M D I l l O S

WIT6 EIC31

GOLD- ROAD DISPOSAL S I T E

Survoy G r i d Ha. 5


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T a b l a 2

GOLDEN ROAD DISPOSAL S I T E

S u r v a y arid l o . 6

Vertical Dipole Horizontal Dipole Station R (millimhos/meter) (millimhos/meter)


WLDIEII ROAD DISPOSAL SITE

Survey Grid no. 7

Vertical Dipole Horizontal Dipole Station W (millimhos/meter) (millimhos/meter)

2 0 , 2 0 Neg . 16.0

Neg. = Negative meter reading. This is caused by very high conductivity beyond the capabilities of the instrument.

NA = Data not available due to inaccessibility of a given survey station (i.0.. the presence of junked vehicles).

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APPENDIX C-2

KAGNETOHETER AND

~ n 3 i SURVEY CONTOUR MAPS


C I ~ L ~ E N &A DISBSM Sr7-C Sf4 Ho. n&t/

pp+6nrmrr*m 5 u e ~ ~ ' 4

, G R I D N o . 1 Cela rn m*s )

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I F I L L OUT B A C K OF LOG AND SIGN YOUR NAME

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APPENDIX D

DRILLING LOGS FOR GROUNDWATER HONITORING YELLS

recycled paper rrology and rnvirunmenc

APPENDIX E

GEOTECBNICAL ANALYSES


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APPENDIX F

RAV ANALYTICAL DATA SUIU4ARIES

recycled paper rrulogy and m\ironrnrnt

QUALIFIER CODE LEGEND

ORGANIC ANALYSES

U - Indicates compound was analyzed for but not detected. The sample quantitation limit must be corrected for dilution and for percent moisture. For example, 10 U for phenol in water if the sample final volume is the protocol-specified final volume. If a 1 to 10 dilution of extract is necessary, the reported limit is 100 U. For a soil sample, the value must also be adjusted for percent moisture. For example, if the sample had 24% moisture and a 1 to 10 dilution factor, the sample quantitation limit for phenol (330 U) would be corrected to:

(330 U ) x df where D = 100 - % moisture D 100

and df = dilution factor

at 24% moisture, D = 100 - 24 = 0.76 100

(330 U) x 10 = 4,300 U rounded to the appropriate number of - .76 significant figures

For soil samples subjected to GPC cleanup procedures, the CRQL is also multiplied by 2 to account for the fact that only half of the extract is recovered.

J - Indicates an estimated value. This flag is used either when estimating a concentration for tentatively identified compounds where a 1:l response is assumed, or when the mass spectral data TIC indicate the presence of a compound that meets the identification criteria but the result is less than the sample quantitation limit but greater than zero. For example, if the sample quantitation limit is 10 vg/L, but a concentration of 3 vg/L is calculated, report it as 35. The sample quantitation limit must be adjusted for both dilution and percent moisture as discussed for the U flag, so that if a sample with 24% moisture and a 1 to 10 dilution factor has a calculated concentration of 300 vg/L and a sample quantitation limit of 430 vg/kg, report the concentration as 3005 on Form I.

C - This flag applies to pesticide results where the identification has been confirmed by GC/MS. Single component pesticides 210 ng/pl in the final extract shall be confirmed by GC/MS.

recycled paper rrulopy and rnvironmen~

B - This flag is used when the analyte is found in the associated blank as well as in the sample. It indicates possible/probable blank contamination and warns the data user to take appropriate action. This flag must be used for a TIC as well as for a positively identified TCL compound.'

E - This flag identifies compounds whose concentrations exceed the calibration range of the GC/MS instrument for that specific analysis. This flag will not apply to pesticides/PCBs analyzed by GC/EC methods. If one or more compounds have a response greater than full scale, the sample or extract must be diluted and re-analyzed according to the specifications in Exhibit D. All such compounds with a response greater than full scale should have the concentration flagged with an "En on the Form I for the original analysis. If the dilution of the extract causes any compounds identified in the first analysis to be below the calibration range in the second analysis, then the results of both analyses shall be reported on separate Form 1's. The Form I for the diluted sample shall have the "DLff suffix appended to the sample number.

D - This flag identifies all compounds identified in an analysis at a secondary dilution factor. If a sample or extract is re-analyzed at a higher dilution factor, as in the "En flag above, the "DL" suffix is appended to the sample number on the Form I forthe diluted samples, and all concentration values reported on that Form I are flagged with the "Dlf flag.

A - This flag indicates that a TIC is a suspected aldol-condensation product .

X - Other specific flags and footnotes may be required to properly define the results. If used, they must be fully described and such description attached to the Sample Data Summary Package and the Case Narrative. If more than one is required, use "Y" and "Z" as needed. If more than five qualifiers are required for a sample result, use the "X" flag to combine several flags as needed. For instance, the "X" flag might combine the "A, " "B, " and "D" flags for some sample.

INORGANIC ANALYSES

C - Concentration qualifier: Enter "B" if the reported value is less than the Contract Required Detection Limit (CRDL) but greater than the Instrument Detection Limit (IDL). If the analyte was analyzed for but not detected, a "U" must be entered.

Q - Q qualifier: Specified entries and their meanings are as follows:

E - The reported value is estimated because of the presence of interference. An explanatory note must be included under Comments on the Cover Page (if the problem applies to all samples) or on the specific FORM I-IN (if it is an isolated problem).

recycled paper ecologv and rnvironmen~

M - Duplicate injection precision not met.

N - Spiked sample recovery not within control limits.

S - The reported value was determined by the Method of Standard Additions (MSA).

W - Post-digestion spike for Furnace AA analysis is out of control limits (85-115%), while sample absorbance is less than 50% of spike absorbance (see Exhibit E).

* - Duplicate analysis not within control limits.

+ - Correlation coefficient for the MSA is less than 0.995.

Entering "S, "V, or If+'' is mutually exclusive. No combination of these qualifiers can appear in the same field for an analyte.

M - Method qualifier: Enter:

P - for ICP;

A - for Flame AA;

F - for Furnace AA;

CV - for Manual Cold Vapor AA;

AV - for Automated Cold Vapor AA;

AS - for Semi-Automated Spectrophotometric;

C - for Manual Spectrophotometric;

T - for Titrimetric; and

NR - if the analyte is not required to be analyzed.


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B CRDL = Contract Required Detection Limit

?

DATA SUMMARY FORM: V 0 L A T I L E S

Site Name: S O & L ) E ~ ROAD SOIL SAMPLES

ah!%L (uglKg) 2 Case #: 3@ Sampling Date(s): TO calculate sample quantltalion limft: Li

u (CRQL Dilutlon Fador) / ((100 - % molslure)/100)

Dilution Factor % Moisture g z

Location

CRQC COMPOUND 4

10 Chloromclhane

SEE NARRATIVE FOR CODE DEFINITIONS

revised 12/88

,-

q 0

3 Vinyl Acetate I I I I I I I I I I I I I I I I I I Brornodichlorornethane

2

2. Page I of DATA SUMMARY FORM: V 0 L A T I L E S

Site Name: GOLDC~ kb~b D;SP~JCIL 347s SOIL SAMPLES

P

q D L = Contract Required Detection Limit

(ug/Kg) k a s e #: 87'&-00( Sampling Date(s): TO calculate sample quantnatlon limn: 3 b 8't3.0,3 (CROL Dilution Factor) 1 ((100 - % molsture)/100)


revised 12/88

I

u Sample No. - 4 3 Dilution Factor 1. 0

I

I

~ / o Moisture Location

17

- b.2 #k 10-3 3 -6 h)O

/ a 0 rL

/.Q /6

~u-Jfl-2 3.0 /vn

W - 3 ~ 3 4 2 6 AJD


\ , ' I I Site Name: ( - ~ ~ \ & . . - . l h ! c d , , ' SOIL SAMPLES I

To catcutate sample quanlllatbn M: (CRQL Mkrtion Factor) / ((100 - % mdstum)/100)

f . CRQL = Contract Requlnd Quantltation UmH

Dilution Factor

SEE NARRATIVE FOR CODE DEFlNmONS

revised 12/88

5 1 ,I ,2.2-Telrachloroethane 5 Tduene

a5 Chlorobenzena

5 5 Ethylbenzene I 5 Styrene T5 Total Xvlen-

------------- -----

- '"P

e6ed


silo Name: gar^ w SOIL SAMPLES /

(ug/Kg) Case #: 9 a o vdlp Sampling Dato(s): To calculate sample quantitatlon Ilrnk: - 2 i ($ AQ& <d S& 8 Sample N o . X, u Dilution Factor 4 % Moisture

Location

rlOL COMPOUND I -- 1 2 Dlc l i l o rop ro r~~nc

i I

CfQL = Contract Required Quantitation Limit SEE NARRATIVE FOR CODE DEFINITIONS - 7

3 -

2 -71 revised 1ZAM < 2 I + 2

U1

- 1- 0

- @ C

1. 0 5%

\

1-6 t o 0 44 53

( - b 33 3.3 36-

-


Site Name: GOUIEU ROAD SOIL SAMPLES

Y

5 CRQL = Contract Required Quantitation Limit P


DATA SUMMARY FORM: V 0 L A T I L E S 2

site Name: 6 4 ~ ~ &M SOIL SAMPLES

2 Case #: 9m.300 Sampling Date(s): &/6/% To calculale sample quantibtlon RmA:

(CRQL Dilution Factor) / ((100 - % moisture)/100) '1

B rn Sample NO. S- /a 364- 13 JED-J~ ~ - ~ f i ~ - r b b ~ n s a 4tD - 15 a - # n r --Undb L

0 u Dilution Factor 1-6 - 1.0 I. 0 I* 0 l a 0 I S 0 S I- 0 % Moisture sa - 6 5 S Y H SY

Location HOT rn~Cr/b

COMPOUND XQL I I

5 1.2-Dichloropropane I 5 Cis-1.3-Dichloroprooene

5 Tnchloroelhene I

~ C R Q L = Contract Required Quantitation Limit SEE NARRATIVE FOR CODE DEFlNlnONS 0

I- revised 12/88

2 7 I

2 w 4

DATA SUMMARY FORM: V 0 L A T I L E S 2

Site Name: 6 ouw ROAD SOIL SAMPLES

Case #: 872.00) sampling Date(r): 0

d Sample No.

Dilution Factor % Moisture

CRQL 1

Location

COMPOUND

5 Cis-1 -3-Dichloropropene

5 Trichloroelhene

5 Dibromochlnrornethane . -

5 1 Telrachloroclhene I 5 1 1.1.2.2-Telrachloroelhane

-

I I 5 ( Toluene

Chlorobcnzene

Elh lbenzene

St renc

Total X enes

5 CRQL = Contract Required Quantitation Limit P

To calculate sample quantbtlon Imlt:

(CRQL Dilutlon Factor) / ((100 - % molsture)/100)


rwlsed 12/88


site ~ m s : vwJ 0; *.$ > + I , -'* id SOIL SAMPLES 2 2 (uglKg)

Case C: 8h.a( Sampllng Date(s): 6/15/87

Page 4 L o f 5

To calculate sample quantllatlon rml: (CRQL DRuHon Factor) / ((100 - X mdstum)/100)

- P 7 Sample NO. s9m5 S 4 m ~ b -/rlsb& S ro tS II Sir PC

Dilution Factor 1 - 6' /- 0 1.0 I . 0 I. 0 % Moisture I 7 / 3 17 I 4 a 5 a(

Location

COMPOUND

5' CRQL = Contract Requlred Quantitatlon Urn# SEE NARRATIVE FOR CODE DEFINITIONS 2

revised 12/88

Page L o f L DATASUMMARYFORM: T E N T A T I V E L Y I N D E N T I F I E D C O M P O U N D S

Site

Case

Name: &I&- &J b13~)PIp S ~ P #: 5772 sampling Date: b// (/YO

SOIL SAMPLES (ug/Kg)

To calculate sample quantitatlon limit (CRQL ' Dilution Factor) / ((1 - % molsture/100)

-

-rl I N CRQL = Contract Required Quantitation Llmit C--'

DATASUMMARYFORM: T E N T A T I V E L Y I N D E N T I F I E D C O M P O U N D S

Site Name: 2 &I$_ Q i

Case I: m2,40/ Sampling Date: n 2 n


To calculate sample quantitation lid: (CRQL Dilution Factor) / ((1 - % molslure1100)

7-1 CRQL = Contract Required Quantitation Limit

Page I of

DATASUMMARYFORM: T E N T A T I V E L Y I N D E N T I F i E D C O M P O U N D S

Site Name: &&h Y a ~ I Y . 2 4 S L ~ 2 g Case #: 873-00 1 Sampling Date: 6/~/~4.


To calculate sample quantitation limit:

z . . (CRQL Dilqllon Factor) I ((1 - % molsture/100)

CRQL = Contract Required Quantitatlon Limit . -rl

- - Sample No. 3s 1. S 3 Dilution Factor 2- 0 2 -0 3 3 - b - 3 - U 3-0

% Moisture 2 1 < I ( P ) I L I -

Location

CRQL COMPOUND .

/ I " '

B m

w .9

P

4. g : .I -

N q:m r

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DATA SUMMARYFORM: T E N T A T I V E L Y I N D E N T I F I E D C O M P O U N D S

a SOIL SAMPLES

I - B

m 3 P

-V

3 -l

3 * -

-n CRQL = Contract Required Quantitation Llmit L J L - d i r . u-l

5 ~ 0 . it , J m c t A L.4-

------ --

- -


- Site Name: SOIL SAMPLES (P

- -

-r( CRQL = Contract Required Quantitation Limit I r0

CRQL = Contract Required Quantitation Umit 7 - l I


Site Name: Gd 1L bd hGPd3J fitf - d 0 -< g Case #: 9 - e 486 Sampling Date: a/(/?$


To calculate sample quantkation limit: (CRQL Dilution Factor) I ((1 - % moisture/100)

CRQL = Contract Required Quantitation Limit I W 0

Page 1_ of I DATASUMMARYFORM: T E N T A T I V E L Y I N D E N T I F I E D C O M P O U N D S

Site Name: SOIL SAMPLES - d -<

Case #: 073 ,C@I Sampling Date: b//~?/ To calculate sample quantilation limit: (CRQL Dilution Factor) / ((1 - % moisture1100)

CRQL = Contract Required Quantitation Limit 7 I

W

recycled p:

Page 1 of / DATASUMMARYFORM: T E N T A T I V E L Y I N D E N T I F I E D C O M P O U N D S

A r l

7 . ... \ ' \

Site Name: f( ( I , , [./ ', I &jdcc .&i-J.. 0 . 8 .

d f

Case #: ,m2 Sampling Date: (./1 ly 1c : j 6 7 I

2 I

SOIL SAMPLES (uglKg)

To calculate sample quantiiatlon Ikni: (CRQL Dilution Factor) / ((1 - % molsture/100)

-11 CRQL = Contract Required Quantitation Umlt I

DATA SUMMARY FORM: B N A S

Slte Name: (-j&U a & s~b- SOIL SAMPLES

3 Case X: 83a. Sampling ~ate(s): G 1/51

m u

8, Sa~nple NO. 51 52 53 S 4 D % Ollution Factor 10.0 2 . 0 d .d d.0 a.0

% Moisture 17 I / 21 24 - Location

I CROL 1 COMPOUND

CRQL = Contract Required Quantitatlon Llmlt

To wlcubte sample quanUtatlon Iknn: (CROL D R u h Factor) 1 ((100 - % molstwe)/100)


revlsed 12/88

DATA SUMMARY FORM: I3 N A S

Site Name: (-1 ~ k h \ 7 c ~ > d 0;' ,;hi+' SID SOIL SAMPLES

s Case #: f72-d~/ Sampllng Date(.): 0 <

bl I S /?o To calculate sample quantttatlon hA: (CRQL Dhtlon Factor) 1 ((100 - % molsture)1100)

Dilution Factor

CRQL = Contract Required Quantitation Limit SEE NARRATIVE FOR CODE DEFINITIONS

revised 12/88

recycle


site ~ a m e : G o I L boJht>fido( ~ t f g SOIL SAMPLES

Case #: ?a. YO6 Sampling Date(s): J/P/~o To mlculale sample quanlllallon Ilrnit: - (CROL ' Dilution Foclor) 1 ((100 - % r n o ~ s ~ u r i ) ~ ~ ~

. .

CRQL = Contract Required Quantitation Limit SEE NARRATIVE FOR CODE DEFINITIONS

recycled paper rcology a

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DATA SUMMARY FORM: B N A S 2

Slte Name: Go/& & 2

ad case *.: 872.m 1 Sampling s : 6 / / 4 8 ~ i


To cdculate sample quantlatlon mn: , (CROL D$Uoh Fador) / ((100 - X molsturs)I100)

CRQL = Contract Required Quantitation Llmit

COMPOUND


revised 12/68

330 Acenaphthylene 330 2,6-Dmltrolduene

\‘/m

------------- 1600 330

21 600 3600 ..I

''330 - 3 3 0 $330 5330

3-Nkroanlllne Acenaphthene 2,4-DinHrophenol 4-Nitrophenol Dibenzofuran 2,4-DlnHrotolums Diethylphthalate 4-Chlorophenyl-phenylelha

,3330 1600

1600

Fluorene 4-NitroanHine 4.6 Dinitro-2-rnelhvl~hmd

DATA SUMMARY FORM B N A S

Site Name: d f 0 SOIL SAMPLES a 0 (uglKg)

Case #: 87a-~Q 2 Sampling Date@): i To d a b t e sample qusntHatlon h k (CRQL Dfluth Fsclw) / ((100 - % molsture)/100)

CRQL = Contract Required Quantitatlon Umlt SEE NARRATIVE FOR CODE DEFINITIONS

revlsed 12/88


Site Name: 6 0 ~ b ~ h ) SOIL SAMPLES

Page of-

2 Case #: 873.001 Sampling Date(s): i clrsl'P 7 To calculate sample quantkation nmn:

(CRQL Dilution Factor) / ((100 - % molsture)1100)

CRQL = Contract Required Quantitalion Limit SEE NARRATIVE FOR CODE DEFINITIONS

revlsed 12/88

DATA SUMMARY FORM: I3 N A S Page i .

Case #: %l 8 4dC Sampling Date(s): T

W

SOIL SAMPLES

(ug/Kg) To celculale sample quenlttallon kmil: - (CROL Dilulion Factor) / ((100 - % molstu~)ltO!

CRQL = Contract Required Quantitation Limit SEE NARRATIVE FOR CODE DEFlNrrlONS

revised 12/88

DATA SUMMARY FORM: B N A S Page 3 . 6 _

Sllo Name: &/L ed SOIL SAMPLES (uglKg)

Case #: fm- 4db Sampling Date(s): d ~ - . ) / ' d To calculate somple quanthatlon limit:

CROL = Contract Required, Quanlilalion Llrnit SEE NARRATlVl

2 0 (& 562 e& i Sample No. @ 1 - fl - P S U S 9

I

FOR CODE DEFINITIONS

E Dilution Factor u % Moisture 2

Location

COMPOUND

1.v 4C

a, o ( a

d *O 1.0 1 . 0 44 53

4- o 33

3 . ‘ ~ - acp

- - -

-


Slte Name: SOIL SAMPLES (ug/Kg)

Case #:TdQO. feD Sampling Date(s): To calculale sample quanthatlon limit:

CRQL = Contract Required Quantitation Llmit SEE NARRATlVE FOR CODE DEFINITIONS

I DATA SUMMARY FORM: B N A S

Sito Narno: GO/& & a d SOIL SAMPLES

Case #: W / Sampling Date(s): &/H To calculale sample quantitallon nrnk (CRQL Dilullon Factor) 1 ((100 - % molst~e)lrc

Location I

;ROL 1 COMPOUND

Sample NO.

Dilution Factor % Moisture

330 1 Chrysene 330 1 t1is(2.Elhylhexyl)phlhalnlc a Y d

U x a-0 I

f b

w l d- 0 I 7

CRQL = Contract Required Quantitation Limit SEE NARRATIVE FOR CODE DEFINITION'

1 -


(ul&fi SHe Name: . . . f - 1 . SOIL SAMPLES 0

h (uglK9) 8 Case #: &?a. 601 Sampling Date(s): 2 n

To calcubte mmpb quantkahn Iknll: (CRQL DhrHar Factor) 1 ((100 - % mohhrrs)/100)

CRQL = Contract Requlred Quantltation Llmit SEE NARRATIVE FOR CODE DEFlNmONS

B

71 revised 12/88 I Ul 0

Sample No. Dilutlon Factor

% Moisture L~cation

I

I

,/",w 7 - 2.8 / /

\q,\q&-

9

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OCC OCC OCC

I OM: OCC

auazuaqo~o1q3ewa~ om ~l(la~uaqd-fiuaqdou(o~e-~ OCC

oullue~ualld!~osoJl!~-~ OCC

DATA SUtAMARY FO f m: B N A S

Sito Namo: SOIL SAMPLES

Case #: 96a0. YO(, Sampling Dale(s): ad - 2 s d - . % P Dilution Factor 0 e % Moisture

Location

COMPOUND

(ug/Kg) To calculate sample quantitellon Itmlt:

*

CRQL = Contract Required Quantitation Limit SEE NARRATIVE FOR CODE DEFINITION

s

Page 1 of( 2 DATA SUMMARY FORM: P E S T I C I E S A N D P C B S

Slte Name: 60 l L b%~asr( S~&Q SOIL SAMPLES

pling Date(s): To calculale sample quenlitation Ilmit: .

COMPOUND

16

1 G 16

QO "

0 ,

k q60

b - UO 80

00

160

160 - - C R Q L = C o n t r a c t Requlred Q u a n t i t a t l o n Llrnit SEE NARRATIVE FOR CODE DEFlNmONS n rwlsed 12/68

4:l'DDD

Endo-,ullan Sullalc

d.d'.DDT

Mclhowch'or

Endnn kelune

Alpba Chlordane

G ~ m r n a - C h l o r d ~ n c

Tox3ohcne

Aroclor-1016

ArocIor.1221

Aroclor-1232

Aroc!or.1242

Aroclor- 1248

Arocfor.1254

Arcc!cr-1 ?GO - -

I -

1 --

I

I

1

Q, a a n II, - u - 0 9

?

A

& / o - r

,

3 of( 3 Page - - DATA SUMMARY FORM: P E S T I C I D E S A N D P C B S

rdPh ed Site Name: (TO SOIL SAMPLES

Z R Q L = Contract Required Quantitation Llrnit SEE NARRATIVE FOR CODE DEFINITIONS rwlsed 12/80

Page I ot a DATA SUMMARY FORM: P E S T I C I D E S A N D P C B S

-. , - < Site Name: (-*)kblh i)~ud 1 1 . J - ' .> 1 'a SOIL SAMPLES

To calculate sample quanfttatkm MI: (CRQL Dlkrtlon Factor) 1 ((100 - X molsturs)/lW)

Sample NO. C; I 34 5'5 SCP S 7 58 Dilution Factor 2.0 1 . 0

% Moisture Location

---------

- - - - - - -

--

ZRQL

8

8 8 8

8 8 8 8 16 18 18 18 18

a6

8 6 80 %s

COMPOUND

alpha-BHC beta-BHC *

delta-BHC Qam-BHC (Llndane) Heptachlor Aldrin Heptachlor Epoxlde Endosuilan I Dieldrin 4.4'-DOE Endfin Endosulfan R --- 4,4'-ODD Endosulfan SuHate 4,4'-ODT Methoxychlm Endrin ketone

------

. . .I."*

3

Alpha-Chlordane

80 80 80 160 160

La"! P

7-70 I :m:a

$0 560 80 80

----pi

T

Gamma-Chlordane To~aphene - Aroclor-1016 A~oc~w-1221 Aroclor-1232 Aroclor- 1242 --- Aroclor-1248 Aroclor-1254 Aroclor-1260

I

'3/0 8EE

- ----

NARRATIVE FOR DEFINITIONS

A5 7

CODE

Page of d DATA SUMMARY FORM: P E S T I C I D E S A N D P C 8 S

S H ~ me: h i s,& SOIL SAMPLES

SEE NARRATIVE FOR CODE DEFINITIONS . .

C] f (uglKg)

Sampling Date(s): To calculate sample quanmaUcm rrm: u (CROL + MIullon Fador) 1 ((100 - % mdslure)1100)

Sample NO.

I Dilution Factor % Moisture

Location

I I I I 1 I I I

S / O r. 0 /4

S9w7,( 1. 0 /k

c 5 9 / r l < b

I R

3 // /. a &q

I - :

1 I 3 O R G A N I C LUALYSIS DATA SHEET

Lab Nane: & U 6 y h & / d ~ r / m f l 2 C . c o n t r a c t : D D O / S L I ~ I I S t Lab C

K a t r i

L e v e l

?; S o l

C o l o r

' ode : case NO. : fln.ooi SAS NO. : Y&- f /OB SDC NO. : L - / - x ( s o i l / w a t e r ) : SOIL Lab Sample I D : . 4/5-67

( low/med) : God , Date R e c e i v e d : O / / C / ~

i d s : 88.7 c o n c e n t r a t i o n Units (ug/L or rq/kg d r ' w e i g h t ) : MG/&

I I I I cxs NO. 1 A n a l y t e I I I I 17429-90-5 I ~ l m i n u - 1 17440-36-0 J A n t i ~ o n y (7440-38-2 ( 7440-39-3 ( 7440-41-7 17440-43-9 17440-70-2 17440-47-3 (7440-48-4 (7440-50-8 ( C o p p e r I (7439-89-6 ( I r o n I 17439-92-1 ILead I 17439-95-4 I E a g n e s r u a l 17439-96-5 IMansanesel 17439-97-6 JMercury-1 0, / / (7440-02-0 I N i c k e l I

7 (7440-09-7 ( P o t a s s l u x ( 17782-49-2 ( S e l e n i u n - (

' 17440-22-4 ( S i l v e r I - (7440-23-5 17440-28-0 17440-62-2 17440-66-6 !PI . I I Cyanide- I / * / Ic-l I 1 I 1 - 1 1-1

B e f o r e : C l a r i t y Before: T e x t u r e : kS C o l o r Af te r : C l a r i t y After: A r t i f a c t s : -

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e INORGANIC ANALYSIS DATA SHEET I

Lab Nane: LW~Y f&v'1/20A/"lM~L I SL

contract: D D O / S ~ ' ~ I

Lab Code:

M a t r i x (soil/water) : SOIL

L e v e l (low/med) : GO& Date Received: bkb/f i

% Solids:

Concentration Units (ug/L or ng/kg dri weight): m ~ / k -

I lCXS No.

I I I q l f l l Analyte IConcentzationi Cl % I

I I I I I

Arsenic - 1 Bariux

1 4 3 1 - 1 % I F l I L4.3 I I 171

Cobalt - Copper- Iron Lead I Nagnes r u n 1

Mercury - 1 N i c k e l 1 7

Potasslunl Seleniun ( Silver - 1 ~odiu-1 - Thallium I vanadin: 1

Cyanide - I 583 1 - 1 I c l I I I I

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Lab Nane: &~06)l f & , R o I r / r l M ~ C . C o n t r a c t : a00/flq I I 53 Lab Code: Case No.: / SAS No. : m-f/02~ SCG NO. : L - /

L e v e l ( low/ined) :

% S o l i d s :

Lab Sample I D : - L//<71 Date R e c e i v e d : O / / C / ~

C o n c e n t r a t i o n U n i t s (ug/L o r ng/kg d r j w e i g h t ) : mb/f i

I - I I .

I I

17440-38-2 I A r s e n i c

(7439-89-6 ( I r o n 17439-92-1 I Lead 17439-95-4 I X a q n e s l u l

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ILL IBI I P I

' (7440-22-4 ISilver-1 I ~ I T I E I

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NYSDEC

1 NYSDEC S ~ P L E INORGXUIC LUXLYS IS DATA SHEET

I

Lab Name: & ~ L O ~ V f & , / 2 0 k / m f l ~ t . Contract: B D O / ~ ~ I I 5.f Lab Code: c a s e No.: B 7 2 . 0 ~ 1 S X No.: Y h / - q U D SX N O . : L - /

Matrix ( s o i l / w a t e r ) : SOIL Lab Sample ID: 41~72

Level ( low/aed) : L4kl Date Received: b/ /b /dq

S S o l i d s :

Color Before:

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incentrat ion Units (uq/L o r nS)kg d& w e i g h t ) : N G / !

I JCXS No.

I

322 0

1 Arsen ic

( Eerylllucl

357

( Nicke l 7 I P o t a s s r u ~

1 selenium- 1 S i l v e r - ( Sodium - ( T h a l l i u n - ( V a n a d i u - ( Zinc I ~ y a n r -

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NY SDEC

1 KYSDEC SAMPLE N( INORGANIC ANALYSIS DATA SHEET

h w I Lab N a m e : !&,&PIVMZ(.

I contract: Dvo/SL/Y I 5 5

Lab Code: Case NO.: flZ?.~o/ SAS N O . : M/-./Om SIX N O . : L - /

Matrix (soil/water) : SOIL

Level (low/

% Solids:

Lab Sample ID: . L//c73 'med) : G ~ J . D a t e Received: ~ h b / f i

Concentration Units (ug/L or mg/kg dry weight): ~ C / W

I 1 I I 1 - q I I ICAS No. I Analyte IConcentrationlCI )I 1 I I I I I I I

Color Before:

Color After:

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1 I Y O R G A N I C LVALYS I S DATA SHEET

NYSDEC SAXPLE NI I

L I

Lab Nane: &LOGY f & , & l m f l ~ C . c o n t r a c t : D D O / ~ ~ ? I S b I

Lab Code:

Leve l ( low/

% S o l i d s :

'med

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Lab S a n p l e I D : . f/hA7{ D a t e Rece ived : b k b / f i

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17440-36-0 I L ~ t i z ~ o n y - I / . 3 4 @ I n / ( 7440-38-2 I A r s e n i c I

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( 7440-39-3 (Eariux I I - I ~ I E I

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C l a r i t y Before :

C l a r i t y After:

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k Lab Nane: & U ~ Y 4 & ~ / 2 0 A / r l N ~ ( .

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c o n t r a c t : ~ D O / S L / ~ I 5 7 Lab Code: case N O . : B7'2.00/ S X No. : Yu-@2V SDC N O . : L - /

M a t r i x ( s o i l / w a t e r ) : SOIL Lab Sample ID: . 41'3~7~' Level ( low/ned) : Go& Date Received: b ) b / f l

% S o l i d s :

C o n c e n t r a t i o n U n i t s (ug/L q / k g d r j w e i g h t ) : m 6 / ~

I lCXS Ho.

1 a t i z o n y - 1 Arsenic-

I Copper- 1 I r o n ( Lead - ( Maqnes lun (Manganese 1 ~ e r c u r y - 1 Nickel

1 1 P o t a s s l u n s e l e n i u m -

1 S i l v e r - ( S o d i w - I Thal l ium- 1 V a n a d i u - 1 Z i n c 1 c y a n i d e -

C l a r i t y Before: T e x t u r e : & Color Befo re :

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NYSDEC S t U F L E S

I

Lab Naie: &UIY ) ~ ; l v & N l m M ~ . contract: D o o / S S ~ ~ I

I Lab Code: case No. : fl7?.00/ S U No. : Y & - L / 0 2 ~ sx NO. : L-/

~ a t r i x (soil/water) : SotL Lab Sanple ID: 4/bd7b Level (low/aed) : k 7 J Date Received: b / / b / d

t Solids: H3

concentration Units (ug/L or ng/kg d r - weight): ~ t & / f i

I 1

I -

17440-47-3 1 ~ > r c = i u T l - b Z T 9 l,I,klpl 17440-40-4 1 Cobalt 17440-50-8 lco~per-I 17439-89-6 IIron 17439-92-1 1 Lead

I

(7439-95-4 lHagneslunl (7439-96-5 (Hanganesel (7439-97-6 ( E e r c x y I 17440-02-0 INickel -1- - 4 3 B 1 - 1 * IpI 17440-09-7 1 Pctassru[ 8% G 17782-49-2 (Selenium-1 /. /

' 17440-22-4 ( S i l v e r 1 17440-23-5 17440-28-0 ( 7440-62-2 17440-66-6 ( Z i n c I

IPI I

I I I 1 - 1 1-1 1-

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828

1 ' NYSDEC SAYPLE x( I N O R G A N I C ANALYSIS DATA SHEET I *

~ a b Nane: &LOh)l f & l * r / m 6 ~ ~ . contract: DDO/SV~ 1 I s q Lab Code: case NO. : #Z.OO/ SAS No. : YA/-'#ZV S X NO. : L - /

Eatrix (soil/water) : SOIL Lab Sample ID: L//c77 Level (low/ned) : God . Date Received: b//b/bq

% Solids: '92 8 Concentration Units (ug/L or ng/kg d r j weight) : ~ L I x c

I (CXS No. I 17429-90-5 17440-36-0 17440-38-2 17440-39-3 17440-41-7 (7440-43-9 JCadziua 1 112 161 (7440-70-2 (~alciun-

IpI (7440-47-3 IChroaiu3 ( (7440-48-4 (Cokalt ( (7440-50-8 I ~ 0 ~ p e r - 1 ( 7439-89-6 ( Iron I 17439-92-1 1 Lead - I 17439-95-4 (Kagneslunl (7439-96-5 (Manganese)

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17439-97-6 (Mercury 1 (7440-02-0 [Nickel - 1 - 17440-09-7 (Potasslunl 17782-49-2 ISelenium-1

' 17440-22-4 1Silver-1 17440-23-5 (7440-28-0 17440-62-2 17440-66-6 I I I 1 - 1 1- I

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Color A f t e r : C l a r i t y A f t e r : Artifacts :

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recycled paper 1.1 r m l a ~ ~ ~ 111111 V I I S I ~ ~ ~ I I ~ I I ~ ~ I

829

1 IYORGA'TIC LVXLYSIS DATA SHEET

NYSDEC S W L E N

I

L I

Lab Nane: & U ~ Y ! & , h M f l 6 ~ < . contract: DDO/SL~Y I I s / D Lab Code: Case NO. : B7'Z.oo/ S ; L ~ NO. : Y U - ~ ~ Z D SDC NO. : L - /

Matrix (soil/water) : SOIL I Lab Sample ID: • d/g70 Level (low/xed) : &Id . Date Received: L * / / L / ~

% Solids:

concentration Units (ug/L or ng/kg d r j weight): fl&/!&

I - I I cXS No. I Analyte I I I 17429-90-5 (Alcinu:: (7440-36-0 ( h t i z o n y 17440-38-2 JArsenic 17440-39-3 (Zariux 17540-41-7 18erylllu:l 17440-43-9 17440-70-2 17440-47-3 17440-48-4 ICckalt - 1 17440-50-8 17439-89-6 1 Iron

\ (7439-92-1 (Lead 17439-95-4 I X a g n e s l ~ l (7439-96-5 JMansanesel 17439-97-6 I M e r c u r y I 17440-02-0 INickel (7440-09-7 17782-49-2 JSeleniun-1

' (7440-22-4 (7440-23-5 (7440-28-0 17440-62-2 17440-66-6 1 I I I 1 - 1 1-1

Color Before: Clarity Before: Texture: & Color After: Clarity After: Artifacts: - ^omments :

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1 NYSDEC SAlQ'LE NO I NORGXNI C ANALYSIS DATA SHEET

I I - !&~!ers~r JAC. contract: ZB/~YT I I s / / ( Lab Name: &J~DGV

Lab Code: case NO. : 872.00f sxs NO. : YC/-qoa SDG NO. : L? Matrix (soil/water) : , Lab Sample ID: . 4/n4 ' Level (low/med) :

Solids:

Date Received: 4

Concentration Units (ug/L or mg/kg dry weight): w//G-

I - I 1 I I ' B (CAS No. ( Analyte IConcentration(CI %

I I A l u i n u I lmtinony: 1 Arsenic -

I Copper- I ?--"

( Lead (Magnesium

1 Mercury- INickel - IPotasslun i Selenium- 1 Silver- ( Sodium- ( Thallium- I Vanadium- ] Zinc I cyan- - I

Color Before: clarity Before: Texture :

Color After: Clarity After: Artifacts:

Comments :

'cr.

rI.:;KFB"8&E:' recycled paper

NYSDEC . /

1 W S D E C SAMPLE NO. I N O R G A N I C JUIALYSIS DATA SHEET 1

1 s a I

tb Naae: ~ O L D ~ Y ,IJD &VIROMWS-, /,uc. c o n t r a c t : 4 W - I I I

rb Code: EAAd 12 C a s e No. : 4000- (106 SAS N O . : r'N - ~ 0 2 0 SDC No. :

~ t r i x ( s o i l / w a t e r ) : 501~ Lab Sample I D : . ffi385

: v e l (low/med) : &Ur Date R e c e i v e d : o t / , o / c t ~

S o l i d s : x&L n c e n t r a t i o n U n i t s (ug/L o r ng/kg d r j w e i g h t ) : Mg,

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191 ( C a d n i u n 1

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NYSDEC

1 NYSDEC SAMPLE SO.

C I N O R G A N I C IUIALYSIS DATA SHEET I

I I

3b Nane: Ecouctv ncJD &L~ROMWT, /NC. Contract: I

3b Code: EAAbC Case ~0.:~000.406 SAS NO.: I IA-LJo;ZO- SDC; NO.:

a t r i x (soil/water) : ~ I L Lab Sample ID: b S + B b

eve1 (low/med) : L o u J Date Received: ot / ,o 190

Solids: 4 ~ . r

concentration Units (ug/L or mg/kg dry weight):

I . I I I I' Q Ifil NO. I Analyte IConcentrationICI (#I

I 1 1 1 - 1 I I 17429-90-5 ~ ~ l u n i n u - I 4830 1- 1 ITI 17440-36-0 !Antimony - I A?. 2 !%I 17440-38-2 JArsenic-l 2.q 181

lei IF1

17440-39-3 1 B a r i u m 1 2 lal ILI (7440-41-7 JEerylllu31 oaqt 17440-43-9 ICadaiun-1

Id 1 5.3 141

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17440-48-4 (Cobalt-I 4 s l & l ILI 17440-50-8 (copper 1 -1-1 l ~ l 1

(7439-89-6 (Iron I +L(CO 1 - 1 17439-92-1 1 Lead I 5 b . z - 1 - 1 17439-95-4 IEagneslu1 LI 30 It21 101

ILl 17439-96-5 IHanganesel I I ~ 1 - 1 17439-97-6 Ilfercurj- I 0-23 161

lei I HI

) 7440-02-0 1 N i c k e l 1 I b . 3 h-1 17440-09-7 1 Potassiunl 1+3 la1 lei

- . 17782-49-2 Iseleniun-1 /,Z I& d \el ' 17440-22-4 l~ilver-I 4.5 la1 17440-23-5 JSodiun-I

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'olor After: Clarity After: Artifacts:

NYSDEC r

1 WSDEC S N L E NO.

b INORCAN1 C NIALYSIS DATA SHEET I

3b Name: &OLD&V flrlO I c C o n t r a c t : I I

3b Code: EAADG Case No. : 7000. L(06 SAS No. : YA - +om SM; NO. :

Lab Sample I D : 65383.

eve1 (low/med) : Leu, Date Received: oa/,o lqO

S o l i d s : s

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o n c e n t r a t i o n U n i t s (ug/L o r mg/kg d ry weight):

1 I - i n A I I ~ 1'- I I Antimony-1 2 Y . r I g I

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Ip_l 3 0 0 I @ '

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NYSDEC r

1 bf

NYSDEC SAMPLE rro. INORGANIC A N A L Y S I S DATA SHEET

ab Name: &OLOC~V flJO &VIIQOMWS-, //CIC. Contract: I ''-1

&t: I

ab Code: EAhlbE Case No. : 4000*YOb SAS No. : YA +Om SDC No. : - atrix (soil/water) : OIL Lab Sample ID: .653.8@

eve1 (lov/med) : &a Date Received: ot/m fcio

Sol ids:

:olor Before: Clarity Before: Texture: H w w u ~

:olor After: Clarity After: Artifacts: $5

NYSDEC r

1 NYSDEC S ~ L E :lo. b I N O R G A l 4 1 C NIALYSIS DATA SHEET I

~b Name: & o u & y nrJP & V I R O M W ~ , /&c. Contract: I I

3b Code: EAIUbE Case No. : ~000~406 S A S NO. : Ybd - ~02.0 SDC NO. :

Lab Sample ID: . 65789

Date Received: o t / l o /YO

Solids:

concentration Units (ug/L or ng/kg d q weight) :

I - I I I I - Q lfll I w No. I Analyte IConcentrationICI I $1

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NY SDEC r

1 NYSDEC S W L E ::o. b INORGANIC N I A L Y S IS DATA SHEET

I 1

ab Naae: &OLO(+YAJD &rllrW~~r, /NC. Contract: I

ab Code: E A N b L Case No. : 4000.406 SAS NO. : YA - ~ 0 3 D SDG No. :

atrix (soil/vater) : & I L Lab Sample ID: - 6 ~ 7 9 0

eve1 (lov/med) : Lo& Date Received: ot/m /qo

Solids: Auf-

concentration Units (ug/L or mg/kg dry veiqht):

1 I I I I - Q I r c r l l 1- ~ o . ( Jbalyte IConcentrationlCI ,It' la/l I I I 1 - 1 1-1 17429-90-5 1~luminu3-I 5-00 1-1 17440-36-0 JAntimony - 1 2s. 3 17440-38-2 (Arsenic-1

141 4-4 1-1

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re1 17440-48-4 ~~obalt--)

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NY SDEC f

1 INORGANIC AIiALYSIS DATA SHEET

I - a b Name: &o&&y nLID &IIIRPYWT, /&C. C o n t r a c t : I

a b Code: EAr(bG Case N o . : ~ 0 0 o ~ Y O b SAS No. :YEl-+dm SDC No.:

a t r i x ( s o i l / w a t e r ) : & r ~

. e v e 1 ( low/med) : LPN

S o l i d s : 6%. 0

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Date R e c e i v e d : oz/,o 190

:o lor B e f o r e :

' o n c e n t r a t i o n Units (ug/L o r mg/kg d r y w e i g h t ) :

I - I I 1 I - q l f l l lu\s No. I J m a l y t e I C o n c e n t r a t i o n l ~ ~ ,W I/$] I I I 1 - 1 1-1 17429-90-5 1 ~ 1 u i n u 3 - I a b o 1 - 1 17440-36-0 IAntimony-1 i + a 4

IPl IdI-IPI

(7440-38-2 ( A r s e n i c - ( a, 8 18: 17440-39-3 ( B a r i u n ) Q l . 0 1 - 1 17440-41-7 I B e r j l l l u n l O.bO Id1

'5' (7440-43-9 ) C a d n i u n I I c l _ I

IvI (7440-70-2 JC3lc iun- I IY 6 0

lEl la I

(7440-47-3 ( C 3 r c n i u a 1 -1-1 17440-48-4 ~ c o t a l t - I 4,s - la1 If l (7440-50-8 ( C o p p e r 1 106.2 1 - 1 17439-89-6 J I r o n I 16 loo

Inl 1 - 1

( 7439-92-1 1 Lead I lo -+ 1 - 1 (el

17439-95-4 IEaqnes lu= l bb'f IEl

142 I (7439-96-5 I E a n g a n e s e l ~ ( , I 17439-97-6 IEercury - I 0.1s Igl 17440-02-0 j H i c k e l ( 4%5 1 - 1 (7440-09-7 ( P o t a s s l u n l 1 1 9

(el 17782-49-2 ISe len iun-1 1- 5 la1 s 121

I 17440-22-4 (S i lver -1 3.0 lrh 1 IEI

17440-23-5 ( S O ~ ~ W - I 205 121

(7440-28-0 I T h a l l i u n 1 161

0.40 141 1 2 . 1 IF1

17440-62-2 I ~ a n a d i - I ( 38b 17440-66-6 1 Z i n c

181 1-1-1

121

I I ~ j a n K I I I

*. - 1

I% I :el 1 - 1 1-1

C l a r i t y B e f o r e : Texture:

: o lo r A f t e r : C l a r i t y A f t e r : A r t i f a c t s : \/a

NYSDEC

1 I N O R G A N I C NIALYSIS DATA SHEET

, t ~ Naae: &OLO(~Y' AJD GUVIROMWT, /NC. C o n t r a c t : I I

~b Code: EAAd E Case No. : 700OlC106 S k 5 NO. : YE( - SI)C; N O . :

Lab Sample I D : b ~ q q z

Date Rece ived: ot/m (qo

S o l i d s :

I n c e n t r a t i o n U n i t s (ug/L o r ng/kg dry weight): & -- -

I JCXS No.

I I I - qlml I C o n c e n t r a t i o n I CI )t/ I $1

I

I A l u m i n u - 1 Antimony- 1 A r s e n i c 1 Barium - 1 B e r j l l r u n Cadniun I ~ a l c i u n - 1 ~ h r o n i u i ( - C o k a l t I - Copper-I Iron I Lead I F?agneslu=l Manganese1

N i c k e l 1 7

It.0 1 - 1 1 P o t a s s i u n ) 358 h I

lei l f l , Seleniun-1 0.75 I&ld

Silver I lEl - ? t + la1

sodiun I t b d lQl ler I p I

~ h a l l i c l a54 l!g 151 V a n a d i u - 1 roe 5 1st IcI Z i n c 1-1-1 ~ i a n i d e 1 1, 3 1% I

[el - 1 I I

lrl I I

3lor Before: C l a r i t y Before: Texture : & O ~ E A I E O

lor After: Clarity A f t e r : A r t i f a c t s : %5

NY SDf C r

1 w W S D E C S m L & NO. IHORGAl4IC IUIALY S IS DATA SHEET

I

3b Name: &OLD&V AJD & ( ~ l t U ~ l r ( ~ r , /NC. Contract: I I

ab Code: EAr(bt2 Case No. : 7000. ctob SAS No. : W - 4020 SDC No. : - atrix (soil/water) : &rc Lab Sample ID: - 65393

Date Received: oz/m fq6

Solids: 38.0

concentration Units (uq/L or mg/kq d& weight): +j,h

Antimony - 1 >I.& Arsenic - I I1 6,

I I ~ ~ ~ I A - I - I 1 Lead I L 1 - 1 . - I Kagnes r u [ t r 90 l @ l

:g; I I

I Manganese l -1 - 1 I t?ercurjI o, 2 i 1% 1 I H i c k e l l -I - I

19; I I

IPotasslunl 161 ISeleniun-1

re1 / ,a I ~ ~ J I L I

[Silver I 6.3 Id1 Isodiu I 33fl 1141

lei IThalliur? I Id1 lei l~anadiu=lIl 11.3 101 1 Zinc 1 . 1 - 1

g; I cjanTZi-I

I I L C

I - 1 1 Yl I I

ILI I I

:olor Before: clarity Before: Texture : / ~ o ~ ~ ~ E . o c ) J

:olor After: Clarity After: ~ r t i fasts : &

NYSDEC r

1 NYSDEC SAMPLE NO. I N O R G A N I C ANALYSIS DATA SHEET

I 3b Naae: & o u & y flu0 ~ J I ~ W Y U S - , /&c. Contract: I

3 t 1 Code: EAADE Case No. : 7000* clOb S A S NO. : YA - +Om SDC NO. : - tvel (lou/med) : L o u J

Sol ids :

Cc

Lab Sample ID: . ~ - 7 4 . 4

Date Received: ot/la fqa

~ncentration Units (ug/L or ng/kg dry weight): 4 U

I . I I 1 I - Q lfll IC\S No. ( halyte IConcentrationlCI 1 g'l

I - I 1-1 1'- I IAluninu-I W [Antinany-I " 1q.a 131 IPl IArsenic - I . b 1 - 1

121 IBariun I

IEI - d e IB;

1 Eerylllu~l 0 . 6 C lql lei ICadniua I

121 2 a 3 1 - 1

1~alciuz-1 10.9 o o lei

1-1 1 chroniu31

le_l - I011 1 - 1 -

(Cotalt 1 121 - 3.3 ' la1

I C o p p e r I A % % 1-1 IPl

I Iron I 16 Y 00 lei

1 - 1 ( Lead 1 44#6 1 - 1

lei 1 Kagnes rua 1 2 t o o 1 - 1 IEl IHanganesel 14 2 1 - 1

re1 I E e r c u r y 1 0.16 I jl

lei IHickel I 1

200s 1 - 1 (Potasslunl 419 181 ISeleniun - 1 0 , b O IgI \rJ I F 1 1 S i l v e r 1 3-31 Igl (SO~~U-I Z L ( ~ la 1

121 IThallium I 666 Id1 ILl ~~an a d i u - 1

IEI 9. C -

1 Zinc I 110 1-1 161

l~anfde_l /,c I& 1 ILI

olor Before: Clarity Before: Texture: k € & a &

'olor After: Clarity After: ~ e t i r a ~ t ~ : 6 'omments:

NYSDEC r

1 NYSDEC SAHPLE NO.

b d INORGANIC ANALYSIS DATA SHEET I

Lab Name: Ecowoy AFJD M E , contract: I I

Lab code: EAIUaE case No. : 9moeY2b SAS NO. : )/N-~&zo SDC NO. : - Matrix (soil/water) : 501 L

Level (low/med) : Lo

Lab Sample ID: . 6bo=11

Date Received: oz 113 /-o

Sol ids : q 2 * 5

ncentration Units (ug/L or mg/kg dry weight) :

I - I I 9

I 1 - 0 lfll IcW No. I Analyte JConcentrationlCI I/J I I I 1 - 1 1-1 (7429-90-5 (~1uminu.m I 24 GO 1 - 1 17440-36-0 l~ntimony-I - 12.0 131 lei 17440-38-2 [Arsenic - 1 2.1 161

lei 17440-39-3 ]Barium-I 22.6 141 141

17440-41-7 18eryllium) 0 . 4 3 Id1 121

17440-43-9 ]Cadmium-1 f,l 141 (7440-70-2 I~alcium-( 87900 1 - 1

If l 1-1

17440-47-3 IChromium ( 944 1 - 1 (7440-48-4 lcobaltzl 3 e z ' la( 121

17440-50-8 copper-I 1 3 . 1 1 - 1 17439-89-6 )Iron I 12 300 1.1

'%I

17439-92-1 JLead IEI

1 I 1 b ~ 4 1.1 I

(7439-95-4 (Hagnesluml 7ww 1 - 1 (7439-96-5 (Manganese1 236

ILl IPI

17439-97-6 lMercuryI 0-11 1 1 lul 17440-02-0 INickel I - e.2 1 - 1 I I I 17440-09-7 )Potasslum) Y W 161

ILI 17782-49-2 JSelenium 1 o,zz laid

lei 17440-22-4 (silver -1 2 2 I&/ 17440-23-5 I S O ~ ~ U I 2 3 q la I IPI lei 17440-28-0 (Thallium ( 0.q3 1g1 17440-62-2 ~~anadium-1 6 a la1 12-1 17440-66-6 JZinc -I 3 1-1

l c y a n i d a ~ I [ * I 141 -1

ILI I I 1-1 1-1

Color Before: clarity Before: Texture : k o C ~ E ~ S D C ?

Color After: Clarity After: ~rtificts: YES Comments:

F-84 FORn I - IN

recycled paper V ~ , I ) ~ I P ~ ! 4111tl I ,~I \~~~~I I I I I<, I I I 402

NY SDEC <

w Lab N

Lab C

Eatri

Level

% Sol

Color

1 INORGANIC ANALYSIS DATA SHEET I

contract: ~ b 0 / 5 q I,W- /L I I

:ode : case No.: fbd380 S U No.: Y~C/"/UW dr;, NO.:

x (soil/water): S b l ~ Lab Sample ID: .65327

( 1 ow/med) : &d , Date Received: . t / ~ / f 0

ids : 4 2 concentration Units (ug/L or mg/kg d r y weight) : M ~ W

I I 1 I I q I r r l l ICAS NO. I Malyte IConcentrationlCI I I I 17429-90-5 IAluminun-l /O/m 17440-36-0 (Antimony-l &?. 8 17440-38-2 JArsenic-1 2 1 1

(7440-39-3 1 Eariua 1 - /O 0 17440-41-7 (Eeqlliuxl 17440-43-9 1,Cadniun-( 17440-70-2 1Calciux-I I 17440-47-3 JChroniu3-1 (7440-48-4 ICotalt-1 17440-50-8 (7439-89-6 (7439-92-1 17439-95-4 (7439-96-5 (Manganese1 (7439-97-6 (Mercury-I (7440-02-0 ( N i c k e l l 17440-09-7 JPotasslunl 17782-49-2 ISelenium-1

' (7440-22-4 (Silver-1 (7440-23-5 17440-28-0 17440-62-2 17440-66-6 /O2 I I

Before: Clarity Before: Texture: &- Color After: Clarity After: Artifacts:

Comments:

recycled paper

NYSDEC r

NYSDEC SAMPLE SO.

'(r INORGANIC ANALYSIS DATA SHEET

I

Contract: I

Lab Name: I

Lab Code:

Matrix (soil/water) : ~ I C ~ a b Sample ID: .653q

Level (low/med) : LO& Date Received:

% Solids: %.4 Concentration Units (ug/L or mg/kg dry weight): &$b

I . I I I 1 - Q I f l I ICAS No. 1 Analyte IConcentration(C1 I/$/ I 1 I 17429-90-5 [Aluminm-I 17440-36-0 (Antimony 17440-38-2 17440-39-3 IBariun-1 17440-41-7 IBeryll~unl 17440-43-9 ICadniun-I 17440-70-2 ~Calciun-I 17440-47-3 1Chroniuz-1 17440-48-4 ICobalt-I 17440-50-8 [Copper-) (7439-89-6 17439-92-1 (7439-95-4 (7439-96-5 (7439-97-6 ( M e r c u r y I (7440-02-0 ( N i c k e l 1 (7440-09-7 (Potassium( (7782-49-2 1Selenium_l

' 17440-22-4 (Silver-( 17440-23-5 17440-28-0 13 -- (7440-62-2 17440-66-6 I I I I 1 - 1 1-1

Color Before: Clarity Before: Texture :

Color After: Clarity After:

Comments : 0 7 3

recycled paper rc-olop r l n c , r n v i r t t r l i t . n f 699

NY SDEC r

1 INORGANIC ANALYSIS DATA SHEET -

Lab Name: f&wmr b~. contract:

Lab Code: case NO. : %.38P SAS NO. : !.-4@0 SM; NO.:

~ a t r l x (soilpater) : a / L Lab Sample ID: . bg3Zf Level (low/med) : Low Date Received: 2 / 6 / ~ % Solids: 4'Kd

concentration Units (ug/L or mg/kg dry weight) :

I

I 17429-90-5 lAluminum-I 17440-36-0 (Antimony-( 17440-38-2 !Arsenic-1 ( 7440-39-3 ( Barlun 1 - 17440-41-7 JBeql1:unJ 17440-43-9 (Cadniun-

(7439-89-6 (Iron -

- *

(7440-23-5 (Sodium- 17440-28-0 lThal1ium-I ( 7440-62-2 (Vanadium-1 17440-66-6 )Zinc I 1 c y a n i d e I

-1 I I 1-1

Color Before: Clarity Before: Texture: & ~ r * e

Color After: Clarity After: ~ r t i f L t r : YG Comments:

i F-87

FORM I - IN -

recycled paper - 701 t~ (olog> IIII<I vn\um~ttrnt 111

NYSDEC

1 IYORGXNIC LUXLYSIS DATA SHEET

NYSDEC SATLE Nc

I - w Lab Name: . & L D ~ Y C & I / 2 o d f l N ~ t .

I ' W l Contract: DDO/SL/? 1

Lab Code: case NO.: - 872.00/ S X No.: Y&-f/DZD SDC NO.: &-/ - Matrix (soil/water): SOIL

Level (low/med) :

4 Solids:

Lab Sample ID: q/c80

Date Received: L . / / C / ~

- concentration Units (ug/L or ng/kg d ~ j weight) : fl~/!G

I 1 I I cXs No. ( Analyte 1 I I I (7129-90-5 IAlulnn-l 17440-36-0 IAnti~ony (7440-38-2 (Arsenic 17440-39-3 17440-41-7 17440-43-9 (7440-70-2 17440-47-3 (7440-48-4 17440-50-8 I

17439-89-6 (7439-92-1 ( b a d - 17439-95-4 (Hagneslunl 17439-96-5 (Manqanesel (7439-97-6 (7440-02-0 (7440-09-7 17702-49-2 17440-22-4

. 1pI lkl-

I I I 1 - 1 1-1

Color Before: Clarity Before: Texture :

Color After: Clarity After: Artifacts: - Comments :

- .

I

F-88 recycled paper tar r~lrtpt c~nd c n \ ~ r o t ~ r n c ~ ~ ~

iwtltid $dbU -- FORn I - I N t ; . : ~ , I ~ ~ ~ ~ , ~ ~ ~ ~ ; , I ~ ~ t ~ t f 4 ~ f t f t , t !I 'll\~rnlllll(.lll 832

NY SDEC

1 I N O R G X U I C ANALYSIS DATA SHEET

NYSDEC SaPLE NO

I

'L- Lab Name: &6)1 ! & , & k / m f l ~ ; ~ ~ . c o n t r a c t : D D O / & ~ i d'z-

I

Lab Code: c a s e NO. : #?2.00/ sXS NO. : M - ~ Q ~ D SDC NO. : L - /

Matrix ( s o i l / w a t e r ) : SOIL ~ a b Sample ID: . 4/<B/ --

Level (low/med) : ~ b d . D a t e Received: b / / b / d

?i; S o l i d s : &I- c o n c e n t r a t i o n U n i t s (ug/L o r ng/kg d i weigh t ) : NG/&

I ( Analyte 1 [ A l u s i n u - ( Ant inony- 1 Arsenic - ) Eariun - 1 Bery l l l un

I lCXS Ho.

1 Cadmium - 1 Calciun I ~ h r o n i u c 1 Cobalt - l Copper- 1 I r o n ( Lead 1 Vagnes lun (Manganese ( Mercury- 1 H i c k e l 7 1 Potasslum

i ~ e l e n i u m - 1 S i l v e r - 1 Sodium- 1 Thallium 1 vanadiun: ( Zinc I cyan=

Color Before: C l a r i t y Before: Texture :

Color Af t e r : . C l a r i t y After: A r t i f a c t s : - Comments :

I . . . - recycieb paper F-89 P,Y,I,V b II!III ~tivir1111me111

reckc led pdper I.b ,,f;" I I I I~ I I ~ I U \ I ~ ~ ~ ~ ~ I I I ~ I ~ I

. . . recycled paper . - .--.. Fdmf 1 - IN I - I . I I ~ ~ I ~ ~ IIIIII ~ . t ~ v i r ~ , r ~ ~ ~ t t * t t ~ 833 ---.- -I_._._ . _ _ _ _ _ _

1 - I.

Nl'SDEC SAMPLE NO. INORGAN1 C ANALYSIS DATA SHEET I

'b' W - 3 I I

tab Name: &UXY ) E ; L / , @ , ~ M ~ Z , contract: D O o / N 4 I I

Lab C

Matri

Level

4 Sol

Color

Color

'ode : Case N O . : ~ ~ . O O ~ SAS N O . : )/L/-W20 SDC N O . :

x (soi l /water) : M.MWJ~ clQvlD - Lab Sample I D : 4754 7 . (low/med) : L ON . Date Received: f/2</8'7

ids : -.

Concentration U n i t s (ug/L or mg/kg -: _MC/IX~

I . I lus NO. I linalyte I 17429-90-5 17440-36-0 17440-36-2 (7440-39-3 17440-41-7 (7440-43-9 17440-70-2 (7440-47-3

- 17440-46-4 (7440-50-8 17439-89-6

I I (7439-92-1

I I 17439-95-4 (7439-96-5 IHanganese(

I I 17439-97-6 J X e r c u r y I (7440-02-0 17440-09-7 . (7782-49-2

' 17440-22-4 17440-23-5 17440-28-0 ( 7440-62-2 17440-66-6

(cyanide1 /. 0 141 ICI I -1 I I 1-1 1-1

Before: Clarity Before: Texture:

After: Clarity After: Artifacts:

Comments: I SOL^ &v &PD&*~ w 4 & ~ m ~ . 7 l / r ~ " &sx.

recycled paper c~.ta~t,p? n ~ u l rnrin,llmvlrt 1.27

1 INORGANIC NIALYSIS DATA SHEET

NYSDEC SAMPLE NO.

I I

3b Nane: G o u c t v nrJD GVIROY~AS-, /NC. Contract: I L-2 I I I

3b Code: EAAbE Case No.:~oQO.L(Ob S A S NO.: YEIoYO;LO SDC NO.:

3trix (soil/water) : dorc Lab Sample ID: . 6 5 0 0 3

eve1 (low/med) : LDH) Date Received: ot /m Iq0

Solids: 58.4.1

concentration Units (ug/L or n s / k s d r f weiqht) : M*./Y~

I . I I I I - n JCAS NO. 1 Analyte IConcentrationlCI ,W jg ' j

I I I 1 - 1 1'. I 17429-90-5 ( ~ l u i n - - l ~ l , I 121 17440-36-0 (mtimony - I 24s l dl 17440-38-2 J A r s e n i c I

lei 6.) I,'

17440-39-3 1 Bariun - 1 7 S 4 C 1JE.l

1 - 1 17440-41-7 IBeryll~n~l

IQI 0.68 IdI

17440-33-9 JCadaiun I 1.3 141 (7440-70-2 1 ~ a l c i u z 1 ) 163 04 1 - 1 $ 1 17440-47-3 j~hroniu=-1 60.3 I I

lei IpI

17440-48-4 ~cokalt-1 a(r I& I ~ I 17440-50-8 ] C o p p e r 1 qS.4 1 - 1 (7439-89-6 (Iron I r b 4 0 0

\el 1-1

17439-92-1 !Lead 1 3 3.3 I1 l (el I P I

17439-95-4 It=?agnesruI 681 o 1 - 1 17439-96-5 JManganesel 4'44

lei 1 - 1

(7439-97-6 leercury - I 0.1- IgI ICI I lei

17440-02-0 JNickel I I

1 1 8 1 - 1 (7440-09-7 (Potdsslu31 3 64 - 17782-49-2 I Seleniun-1 0 . 9 1% 1

' 17440-22-4 lsilver-1 3.q Ill f l I

17440-23-5 JSodiun I f24 161 I I (7440-28-0 (Thalliu-1 a6e 161 IpI 17440-62-2 IVanadiul-1 9.3 191 17440-66-6 12inc I 69.6 1 - 1 1-u 101

1 ~ ~ y a n r ~ I IYI ICl - 1 I I - I I I I

'olor Before: . Clarity Before: Texture: /fwarAlrg

'olor After: Clarity After: Artifacts: &or5

'ornments:

'clrv

NYSDEC

1 INORGANIC ANALYSIS DATA SHEET

NYSDEC SAMPLE NO. i

b I I cw7 I

z. I Lsb Name: &GY f 6 J I a A ) R M c o n t r a c t : b a o l ~ f I I

Lab code: c a s e NO. : 872wt SAS NO. : W-qoto SDC NO. :

Matrix ( s o i l / w a t e r ) : SWL Lab Sample ID: ,47977 Leve l (low/med) : W W . Date Received: ~/zq/0/89

& 1 S o l i d s :

Concentrat ion U n i t s (ug/L o r mg/kg dry w e i g h t ) : WG/B

Color Before: c l a r i t y Before: ~ e x t u r e : &I- Color After: C l a r i t y Af ter : A r t i f a c t s :

Comments:

recycled paper

DATA SUMMARY FORM: V 0 L A T I E S

G o I&- && boss ( s*,++ Site Name: WATER SAMPLES

(ug/L) $ Case #: 9dlD: q o f sampling' Date(s): 2/$/$0 To calculate sample quantitation himf: 2 m a (CRQL Dilution Factor)

Sample No. 3 bu - 1 S d - Z S W - 3 - CN- c SW-7 Jbd- p' - Dilution Factor 1. 0 !. 0 1-0 /- h 1- b b /- 0 1- n- -

Location

COMPOUND

5 CRDL = Contract Required Detection Limit 3 2 . 7

*Action Level Exists SEE NARRATlVE FOR CODE DEFINITIONS

revised 12/88


WATER SAMPLES

$ Case #: 900.3m Sampling Date(s): d / 6 / 7 d H J/~/?o (uglL)

1 a -

Page _L of 1

To calculate sample quantital;on limit: (CROL Dilution Factor)

- - CRDL = Contract Required Detection Limit

n

*Action Level Exists

w u Sample No. z

Dilution Factor Location

SEE NARRATIVE FOR CODE DEFlNmONS

revised 12/88

-

6p.b I /. d

- 1-

(;w*G~Q L d

G w - 5 /* t?

L w - l ~ s b / ,b

Gw -L /. 0

tu, - 'I /. 0

Gw ~3 k&-4 /. d 1- 4


Site Name: WATER SAMPLES (ug/L)

To calculate sample quantllsllon MI: (CRQL Dilution Factor)

COMPOUND

GAOL = Contract Required Detection Umlt ' -a *Action Level Exlsts SEE NARRATIVE FOR CODE DEFlNmONS

revised 12/80


Slte Name: c a l k , cad Case #: 4m. YO^ Sampling Date(s):

7 \ n, 0

-.c

WATER SAMPLES

n

n, a Sample No. _5tU - I 5 ~ - 3 $ U J 3 ( * sbd- L/ S j N _ _ ( - u OI u Dilution Factor I- 0 /I r) I , L) /- 0 /. D

. : . . Location

{QL ( COMPOUND

C R ~ L - = Contract Required Detection Limit - -rl

*Action Level Exists

To calculate sample quantlation bnl: - (CRQL Dilution Factor)

c i . ' - -

SEE NARRATIVE FOR CODE DEFINITIONS L

2 - revised 12/8$

1) - U > 2

?


Site Name: SOIL SAMPLES 9- (/bC (udKg)

Case #: 9000. ~ 1 4 Sampling Date(s): 2 0 J

To calculate sample quantbtlon Umlt: (CROL Dilutlon Factor) / ((100 - % molsture)1100)

CPQL - = Contract Required Quantitation Limit SEE NARRATIVE FOR CODE DEFINITIONS

9 t.0

.

I

- 4 /- 0

~ & r W I D 6

-/3 re 0

SW - /3 SW - I 2 - 0 n. Sample No. u L1) Dilution Factor 2 % Moisture

Location

I CROL

5 5 5

313 C & 4 0

COMPOUND

1,2-Dichloropropane Cis-1,3-Dichloropropene Trichloroethene

Jw-II I. 0

a

m

. m

V

) 0

recycle

d p

al


s n Name: ~ O L D E A ) ROW ~ ~ s P o J ~ K S;TE

CL X: O72amI sampling ~ate (s ) : P / ~ Y / J 9 X -0

WATER SAMPLES

To calculate sample quantltation lid: (CRQL ' Dilution Factor)

C ~ L = Contract Required Detection Limit 2 *Action Level Exists SEE NARRATIVE FOR CODE DEFlNmONS -

m

revised 12/88

sample No. Dilution Factor

Location

D l i -R ib 0- &

CRQL COMPOUND

i


Site Name: GO/& Rd - ' Case #: ZR)~ . YQc Sampling Date: .)/g- ?/Ao I WATER SAMPLES

i u g ~ ~ ) To calculate sample quantitation limit:

, (CRQL Dilution Factor)

CRQL = Contract Required Quantitation Limit

DATA SUMMARYFORM: T E N T A T I V E L Y I N D E N T I F I E D C O M P O U N D S

Site Name: /d& f d ; 2

6ase #: 0 - - O< Sampling Date: 0 : P 0

WATER SAMPLES (ug/L)

To calculate sample quantitalion limit: (CRQL ' Dilution Factor)

CRQL = Contract Required Quantitation Limit I w 0

DATA SUMMARYFORM: . T E N T A T 1 V E L Y I N D E N T I F I E D C O M P O U N D S

Site Name:

$ -- Case #: 9 m. 380 Sampling Date: d 6 d1/1/9b

WATER SAMPLES i u g ~ ~ )

To calcuhle sample quantitalion limit: (CRQL Dilution Faclor)

-I-I CRQL = Contract Required Quantitation Limit I

recycled

recycled


- CRDL = Contract Required Detection Limit 'Action Level Exists SEE NARRATIVE FOR CODE DEFlNITONS

revised 12/88

Page of - DATA SUMMARY FORM: B N A S 1

Site Name:

Case #: 9da). 40.T Sampling Date(s): ID 0 <

WATER SAMPLES

To calculate sample quantilatlon hid:= - (CRQL . Dilutlon Factor) 5 - - - - -

rD a Sample No. SW- / $&-t S . W - 3 S W - Y Sh~*r Sib - [a 3 - u - 7 Ju--8 f ~ . L q D, Dilution Factor I 0 1.0 I - 0 I. 0 1- 0

- D I . 0 1. ri 2 Location - - -

A

F

- CRDL = Contract Required Detection Limit *Action Level Exists SEE NARRATIVE FOR CODE D E F ~ N ~ O ~ ~ S

revised 12/88


Site Name: & ~ ( o A , ~ A C ( WATER SAMPLES

To calculate sample quanttlation Mt: (CRQL Dilution Factor)

.- .

CRDL = contract Required Detection Limit *Action Level Exists SEE NARRATIVE FOR CODE DEFINITIONS

revised 12/88


Site Name: G d k , Rd WATER SAMPLES

Case #: (j ~ V O 380 Sampling Date(s): 314 - 4 / 9 8 z n

To calculate sample quanlilallon h i d : , (CROL Dilution Factor) - -

- DL = Contract Required Detection Limit

TI I I-' I-' 0,

'Action Level Exists SEE NARRATIVE FOR CODE D E F I N ~ O N S

revised 12/88

.. ' . + . . . . ,. ,?!.. ,.,: . ,. . )w,;z4;i$::,< , <\,??;,*>.- , .$ ..:, ., . . , . . , .. a,+.'- -, I r. :

,: -.,. .. . I 1 1 - ; ;,:. ir : * : : , - . , ' - . , ; , ' ? .

, . - .-. , :: <c5"$'*,~i;!,% ;*.. . .. . . y. ::-, .'; . ; .&$Q<

I ,t: :.. . -*,, , . , -

. . 1 . 1 , Page

J DATA SUMMARY FORM: B N A S 2 -

Site Name: el& h~ thw--P s& w: ~ 2 - ~ n ) / - Sampling bate(:): 6//sk0

WATER SAMPLES - (ug/L) ', *

To calculate sample quantlleUon RJt: (CRQL DRullon Factor)

CRDL = Contract Required Detection Umit *Action Level Exists SEE NARRATIVE FOR CODE DEFINITIONS

revised 12/88


Site Name: 6 6 PC! Cpse #: w. Yo$ Sampling Date(s): a / f - d / ~ & d 2

WATER SAMPLES

(ug/L) To calculate sample quanlitatlon hit:, - (CROL ' Dilution Factor) L E

COMPOUND

CRDL = Contract Required Detection Limit *Action Level Exists SEE - NARRATIVE FOR CODE DEFINITIO~S

revised 12/88

DATA SUMMARY FORM: B N A S Page -

Site Name: 6 p /kc d Case #: YO<

z )m* v2G Sampling Date(s):

WATER SAMPLES

To celculale sample quanlitalion limttI (CROL . Dilution Factor)

d I .-

a a Sample No. 5 we16 C W @ If 5w-rlMs'j, < c ~ l - l l h d S W - r ~ C w 4 1 2 ~ J (k-t2m$b $kg 13 3 ~ - ~q u Dilution Factor I* 0 1 - D l* 0 I- 0 0 I. 0 \-D - u

bJ0- Location m, 1

COMPOUND

CRDL = Contract Required Detection Limit *Action Level Exists SEE NARRATIVE FOR CODE DEFINITIONS

revised 12/88

of - DATA SUMMARY FORM: B N A S 2

Site Name: ~ e d Case #: 3 80 Sampling Dale(s):

2

WATER SAMPLES (u g/L)

To calculale sample quanlitallon hh:; (CROL Dilulion Factor)

/

- CRDL = cdntiact Required Detection Limit

0 - Sample No. 5 a a ~d-fg Dilution Factor X

? Location

*Action ~ e v e i Exists SEE NARRATIVE FOR CODE D E F I N I T I O ~ ~

-

1 -

- - -

3 -

50

10

10

10

10

10

'50

50 ,

revised 12/88

COMPOUND

4-rdi~rophcnol

2 Dlbcnzoluran - F2.4-Dinilrololuene ,. ': - Dielhylphlhalale - IJ.Chloropt~enyl-phenylelher 3)

3 Fluorcne

? 4-~~lroani l ine

2 4 6 Oinilro.2-melhvlohcnol -


Site Name: (,?\LA @ Case #: 5m). 3& Sampling Date(s): 2

f Page 3. of 6

2

WATER SAMPLES (ug/L)

To calculale sample quantitatlon hn:, (CROL Dilution Factor)

- ,

CRDL = Contract Required Detection Limit

10 5 10 3

'Action Level Exists SEE- NARRATIVE FOR CODE DEFINITIONS

revised 12/80

4 - ~ h l o r o p h e n ~ l p h e n ~ e t h e r

Fluorcne

- - ? -

50 3 4.N:lroaniline

50 4 4 O i n 1 i r o - 2 - m ~ l h v I ~ h ~ n o l -

Page DATA SUMMARY FORM: B N A S 2

Site Name: J ) ; ~ ~ & A L ~;TE

C ~ B #: 872 *D@ 9 Sampling Date(.): 8la~I89 WATER SAMPLES

(ug/L) To calculate sample qusntitatlon limb: (CROL Dilutlon Factor)

revised 12/88

- m. U 7J 0, Sample No.

8 Dilution Factor Location

ROL 1 COMPOUND

- CRDL = Contract Required Detection Limit *Action Level Exists SEE NARRATIVE FOR CODE DEFINITIONS

p)3 h i 1.0

M.~ I .& '&~s ~ ~ i f / ~ ; ~ / n s b 1.0 1.6

DATA SUMMARY FORM: 8 N A S

Site Name: bbh h& 51- b WATER SAMPLES

&se x: md.a~ sampling Die(s): b / / ~ / 9 0 (ug/L)

n

Page 3 *

To arlculale sample quantllation I& (CRQL Dllullon Factor)

~ R D L = Contract Required Detectlon Limit *Action Level Exlsts SEE NARRATIVE FOR CODE DEFINITIONS

revised 12/88


site Name: 6 6 )dl Ed . . WATER SAMPLES

(ug/L) ~ s e #: 7 . d C Sampling Date(s): &- ?/$A0 0 'z 0

To calculale sample quantitatlon h$ (CRQL Dilullon Factor) 5

-

&DL = Contract Required Detection Limit *Action Level Exists

- u a Sample NO. D 2 Dilution Factor

Location

CRDL 1 COMPOUND

SEE NARRATIVE FOR CODE DEFINITI~JS

revised 12/88

S W - / /.Q

10

10

to

50

10

10

1 10 10

10

10

20 - 10

10

N N~lrosod~phenylamtne

4 Bromophenyl phenylelher

*Hoxachlorobenzene *Pontachlorophonol

Pl~cnnnllircne

Anlhraccnc -- Dl n bulylphlhalalc

Fluornnlticne

Pyrenc --- Bulylbcnqlptilh~lalc

3.3 D~chlorobenz~dlnc

Bcnzo(a)anlhraccnc

Chrysene

Tw-2 A

S w - 7 1 . f!

0 /7 10

10 _ 10 g 10 3 - 10 i

$a-3 1.0

-----

4 I f

-or

r w - P / - 0

/I?' 3a A

3

-- bls(2 Elhylhcxyl)ptithalaIe I 3 01 n oclylphthalatc

Benzo(b)lluoranlhcne

Benzo(k)fluoranlhene

~ w - p 1- b

a fl

T Z 6 2

3 #

/&

10 5 10 5 - 10 2

- J-4-4 I ,&

a n

U

.

aJ- T

1 3 1 ---

(3

.,3 1 l3

lndeno(1.2.3 cdlpyrene

Dtbenz(a.h)anthraccne

Benzo(a.h,~)perylcnc

SAJ-J-

/. d

a

3

m a

1 3 >

Benzo(rt)pyrene

-

Sw-L, /. ill

3

------------

I t

2

7

3- -

tad-


Site Name: & b

Case #: '$me 3m Sampling Date(s): 2 0 5

WATER SAMPLES

To cnla~lale sample quanlitallon KrnH; (CRQL Dilullon Factor)

' ~ R D L = Contract Required Detection Limit , I

\,

m ~1 Sample No. u a, u Dilution Factor 2 Location

C ~ D L 1 COMPOUND

10 1 N N~lrosod!phcnyl~m~nc

*Action Level Exists SEE NARRATIVE FOR CODE DEFlNrrlQNS

SW - 15 !. 0

I

revised 12/88

I I

L -

I I I

* " , - Page of - - . DATA SUMMARYFORM: P E S T ' I C I D E S . A N D P C B s

Site Name: (;g / WATER SAMPLES

(uglL) TO calculate sample quant&tion Bmh:

(0

P - (CROL Dilution Factor) -h)

Sample No. 2 Dilution Factor

Location

I I I I 1 1 I I I I I I I I I I I I

CRDL = Contract Required Detection Llmit *Action Level Exists SEE NARRATIVE FOR CODE DEFlNmONS revised 12/88

S W - / /. 0

SW-J h 9

- /, 0

$w-Y 1 0

SdU 75 f. 0 -

.Jk-r /. 0

4s w c ? f . 0

r e I. L/

TY-9 f r f 9

o i DATA SUMMARY FORM: P E S T I C I D E S . A N D P C B S

Site Name: G d /Afi EL/ WATER SAMPLES

;" CRDL = Contract Required Detection Limit Y

*Action Level Exists SEE NARRATIVE FOR CODE DEFlNrrlONS revised 12188

DATA SUMMARY FORM: P E I C I D E S . A N D P C B s

site Name: GblL &f WATER SAMPLES

Case #: 3@ Sampling Date(s): 7

To calculate sample quanllta:ion nmR: (CROL Dilution Factor)

CRDL = Contract Required Detection Limit

3'

*Action Level Exists SEE NARRATIVE FOR CODE DEFlNKlONS revised 12/88

G o l L leWJ Site Name: WATER SAMPLES

CRDL = Contract Required Detection Limit 3'

*Action Level Exists SEE NARRATIVE FOR CODE DEFlNrflONS revised 12/88

3

DATA SUMMARY FORM: P E S T I C I D E S A N D P C 8 S

Site Name: 6&(Q f i & X: 67d *LVA Sampling Date(s):

< < l o _

WATER SAMPLES

To calculete sample quanttlation Irnk (CRQL Dlfutlon Faclor)

CRDL = Contract Requlred Detection Urnit n

*Action Level Exlsts SEE NARRATIVE FOR CODE DEFINITIONS revised 121118

NYSDEC r

1 NYSDEC SAMPLE NO. INORGANIC ANALYSIS DATA SHEET I I

L.l

Lab Name: t&,&V contract: m/w I cw- / I nmr hi I I

Lab Code: case NO.: 9OW.M SAS No.: ) l U - f 0 ~ SDC NO.:

Matrix (soil/water) : W A E Z ~ a b sample ID: . C53/i? DL

Level (low/med) : LON , Date Received: 2/8/90

% Solids: 0

Concentration Units (ug/L or mg/kg dry weight): LI~/L

(Chroniur~ - 1 I Cobalt- l I copper- I 1 Iron I I b a d I IHagneslunl IHanganesel I ~ercury- I 1 N i c k e l I (Potassruml [Selenium-1

. -

( S i l v e r 1 ( S o d i u a l (Thallium-( IVanadium-1 1 Zinc 1 I I I I

Comments :

Color Before: 8/20u/d clarity ~efore: &VDY

Clarity After:

Texture:

Artifacts:

recycled paper

NY SDEC


NYSDEC SAMPLE NO, I - ' GUJ-l 1

Lab Name: &Y { G , & N ~ Q M x C , contract: -W?m I f/rmm I I

Lab Code: case NO.: 9 ~ ~ . 3 8 0 SAS NO.: ~N+D& SDG NO.:

Eatrix (soil/water) : Uf7Z%. Lab Sample ID: - U X Z d 7

Level (low/med): Lo& Date Received: +/$/TO

% Solids: 0 concentration Units (ug/L or mg/kg dry weight) :

1- No. I 17429-90-5

-~ - - i7439-89-6 irrbb - j 17439-92-1 (Lead I

Color Before:

1 malyte iconcentrationici ifi ,I I J A l u m i n u 1 ! P I

ISelenium I lgl L4/

33. G - -

I cyanide- l I I 1-1 1-1

Clarity Before: k Text ure:

color ~fter: &.EM- . Clarity After: &%& Artifacts: -

Conments :

recycled paDer


Lab Name: &LOG)' C & ~ / ~ N M M Z - ~ ; C .

I

Contract: 300/3-fl 1 Cw-z I

I I

Lab Code: case ~o.:fm.3f" SAS NO.: YK-i l4?~ SDG NO.:

~ a t r i x (soil/water) : Lab Sample ID: . u3/8 b&

Level (low/med) : W1J , Date Received: 2,/,,/90

% Solids: 0

Concentration Units (ug/L or mg/kg dry weight) :

~ C A S No. Analyte i~oncentrationici Ibi/ i '

-- -~ -

(7440-47-3 (Chro~iu3 ( 17440-48-4 l ~ o b a l t - - ~ E 17440-50-6 ICopper 1 (7439-89-6 JIron I , 17439-92-1 (Lead I I, 17439-95-4 IMaaneslunl 1 - - - -

I - a - - ~ - - '. 17439-96-5 JManganesel k 17439-97-6 (Mercury-1 6'. 17440-02-0 (Nickel. I 17440-09-7 JPotasslunl - . 17782-49-2 /Selenium-1 5 0

' (7430-22-4 (Silver I 17440-23-5 ISodiu I u d

17440-28-0 j~halli' - . 17440-62-2 IVanadium-1 (7440-66-6 (Zinc I I

Color Before: &0wd Clarity Before: Texture :

Color After: YWCJ * Clarity After: L u b y Artifacts:

Comments :

C FOR24 I - IN

recycled paper F-137 rcv~loq 11ttc1 ~n~irottrnr~t~ 684

NY SDEC r

1 WSDEC SAVLE NO.

w INORGANIC ANALYSIS DATA SHEET I GcU-t I

Lab Name: &f f ~ ~ h l y @ J ~ ~ contract: 1 7/~m<m I I

Lab Code: case NO. : ?m, 36% SAS NO. : YN-YO@ ~x NO. : natrix (soil/vater) : w m ~ a b sample ID: 653/.f,07

Level (low/med) : COW Date Received:

% Solids: 0

Concentration Units (ug/L or mg/kg dry weight): U?/L 1 I I I - Q IflI

NO. I malyte IConcentrationIC, I$I ,I I~luminun- I Antimony-

ICadmium-1 7d70 i f f ; lcalcium I / 7000

1 ~3roniuCl I D . 0 15 l ( C o b a l t 1 /o*o 141

1 Lead

I Mercury- I I N i c k e l I /X 0 1 Potasslum( ( Selenium-( ISilver-I

1 Vanadium 1 /o.o la[ 1 Zinc I /? 2 @I I cyan= 1

- 1 1 - 1

I 1-1 1-1

Color Before: &?@ Clarity Before: k Texture :

Color After: & Comments:

Clarity After: && Artifacts:

recycled paper

NYSDEC r

1 NYSDEC SAMPLE NO. INORGANIC ANALYSIS DATA SHEET

I I

i 6w-3 I

h b Name: EMLW f&qvn~,qMz. contract: D00/.4 I I I

Lab Code: Case NO.: PbM.Jgb AS No.: ~N%w SDG NO.:

Level (low/med) : Our

% Solids: 0

tab Sample ID: . b 5 3 / 9 , 4

Date Received:

Color Bef or

Color After

,ncentration Units (ug/L or rng/kg dry weight): U<[L

I I 1 I - Q I f l I ICAS NO. I m a l y t e iconcentration1C) ,W I 1 I (7429-90-5 17440-36-0 (7440-38-2 (7440-39-3 - 17440-41-7 (Beryllluril 17440-43-9 JCadaium-1 (7440-70-2 ICalcium 1 (7440-47-3 ( ~ h r o n i u c ( 17440-48-4 17440-50-8 (7439-89-6 (7439-92-1 (Lead 17439-95-4 lHagnesluinl 17439-96-5 JHanganeseJ 17439-97-6 JHercury-1 (7440-02-0 (Nickel-1 17440-09-7 IPotasslun( 17782-69-2 JSelenium-1 17440-22-4 17440-23-5 (7440-28-0 17440-62-2 17440-66-6 I I I 1 - 1

b N d Clarity Before: L o ~ p y Texture

/mu . clarity After: Artifac

Comments:

recycled paper

NY SDEC r


NYSDEC SAVLE NO.

I

Gw-a I - Lab Name: c o n t r a s t : m/3v I ~ / ‘ m m

I I

Lab Code:.

M a t r i x ( s o i l / w a t e r ) : a Leve l (low/med) : LOW

k S o l i d s : 0

Lab Sample ID: - L53/9 ,67

Date Rece ived : 1/Bhl7

c o n c e n t r a t i o n U n i t s (ug/L o r mg/kg d r y w e i g h t ) :

I I 1 1 Q l f l l 1 ens NO. I m a l y t e [ c o n c e n t r a t i o n / lp'l I (7429-90-5 (7440-36-0 (7440-38-2 17440-39-3 53.0 17440-41-7 17440-43-9 JCadniun-( &O (7440-70-2 JCalciuz-1 17440-47-3 (Chroniu3- ( 17430-48-4 !Cobalt-1 (7440-50-8 /O.O t

17439-89-6 3 s 17439-92-1 17439-95-4 17439-96-5 (Manganese! ( 7439-97-6 (Mercuq-1 (7440-02-0 ( N i c k e l (7440-09-7 - . 17782-49-2

' 17440-22-4 17440-23-5 JS0diu~3-I 70700 (7440-28-0 ( T h a l l i u I 2 , O 17440-62-2 l ~ a n a d i u z 1 1 /o. o 17440-66-6 JZinc I /Oa 0 I I c y a n x I

-1 I I 1-1 1-1

l o r B e f o r e : CLEM C l a r i t y Before: &%! T e x t u r e :

l o r A f t e r : &#d- ' C l a r i t y A f t e r : k A r t i f a c t s :

mments :

- - -

reckcled paper ' 687 F- 140 c . v ~ ~ l t ~ p 111111 c n \ i r ~ ) ~ ~ r n r ~ ~ ~

NY SDEC


contract: I G w - 4 I

Lab Name: I I

Lab code: case NO. : a SAS NO. : ) ' rV-foh SDC NO. :

~ a t r i x (soil/water) : w m ~ a b Sample ID: .~25320.+

~ e v e l (low/med) : Lou Date Received: z/~/,$. % Solids: 0

Concentration Units (ug/L or mg/kg dry weight): &- I I I I - Q I m I

NO. I Analyte IConcentrationlCI ,M' I I 17429-90-5 - 17440-36-0 17440-30-2 (7440-39-3 17440-41-7 IBerillruxl 1 7440-43-9 (Cadnlua-I 17440-70-2 ~Calciu3-I / 62 boo 17440-47-3 IChro=iua-I /Of D w ( 7440-48-4 ( C o b a l t 1 17440-50-8 1 17439-89-6 17439-92-1 17439-95-4 (7439-96-5 17439-97-6 1 7440-02-0 /5.0 17440-09-7 17782-49-2

' (744'3-22-4 (7440-23-5 17440-28-0 (7440-62-2 17440-66-6 ( Z i n c I

1 c y a n i d e I 10. o I I4 I ICI I I - 1 1 - 1 1 -1

color Before: CW Clarity Before: Texture:

Color After: k . clarity After: Artifacts:

Comments :

recycled paper

NYSDEC r

1 NYSDEC SAMPLE NO.

W INORGANIC ANALYSIS DATA SHEET I Gw-LJ- I L

Lmb Name: A/~oNM~- Tc. Contract : ~ / f i ~ ~ j i I *me3 I

I

Lab Code: c a s e N O . : 9m.m SAS N O . : $V-L/o& SX N O , :

Matrix ( s o i l / w a t e r ) : w ~ W

Level (low/med) : &kc- Lab Sample I D : -um.~7 Date Received: </!I98

5 S o l i d s : 0

~ n c e n t r a t i o n U n i t s (ug/L o r mg/kg d r y w e i g h t ) : &- I . I I I I- Q r m ~ 1 CAS No. ( Analyte 1 Concentration1 C l Jn/ ( g/(

Color Before: k Color After: &W '

Comments:

C l a r i t y Before: h C l a r i t y A f t e r : LEhe

Texture :

Arti facts :

recycled paper F-142

NYSDEC f

1 NYSDEC SAMPLE No. INORGANIC ANALYSIS DATA SHEET I 1

Lab Name: f ~ * b d R p T j r ; ~ . contract: 7b0&4 I GN-5 I I I

Lab Code: case NO. : 9 ~ ~ 3 8 0 SAS NO. : 1 ~ 4 ~ SIX NO. :

Matrix (soil/water) : rc/&mb, Lab Sample ID: . 653W 06

Level (low/med) : LON Date Received: 2/ukD % Solids: 0

Concentration Units (ug/L or mg/kg dry weight): d- I) L

Color Before :

Color After:

Comments :

--

I (m No.

,I I I Aluminum- l IAntimony-l (Arsenic- l

( Cadmium- 1 1Calciurn-1 ( Chroniun- ( 1 C o b a l t 1 l C o p p e r I 1 Iron I 1 b a d - I (Magnesluml

I ~ercury- 1 (Nickel I 7

IPotasslum( (Selenium-1 1 S i l v e r 1 1 Sodiun- 1 IThallium-1 IVanadium-1 1 Zinc I I c y a n i d e l I I 1-1 1-1

Clarity Before: & O U D ~ Textur'e :

Clarity After: ~ ( O V D ~ Artifacts:

recycled paper

NY S DEC

1 r '.

NYSDEC S M L E NO. - - INORGANIC ANALYSIS DATA SHEET ' G W - 4 I

)llC, I contract: DOi~5y7 I FicmtD I

Lab Name: &LO&Y G/&IICIM &. I

Lab Code: case NO. : q m su NO. : @--t/,w SDC NO. :

Matrix (soil/water) : k%m Lab Sample ID: -653~~07

Level (low/med) : Date Received: z / $ / ~ b

% Solids: 0 concentration Units (ug/L or mg/kg dry weight):

I I I

&- I I - Q IPIl

~w NO. I Analyte IConcentrationlCI )I/ ljdl I I I 17429-90-5 (Aluminum-l . (7440-36-0 (Antimony-1 17440-38-2 IArsenic- 17440-39-3 (Barium 1 - 17440-41-7 IBerylllurnl X @ o I &I (7440-43-9 JCadmium-1 KO 141 17440-70-2 lCalcium-1 73300 1 - 1 17440-47-3 IChromium-1 10, 0 Ic 1 (7440-48-4 (Cobalt-1 / O , 0 I&I 17440-50-8 jcopper-1 10.0 v 17433-89-6 (Iron (7439-92-1 ( b a d , I I. 0 l 3 1 17439-95-4 JXagnes~umJ 57300 1- 1 17439-96-5 (Manganese1 &I-1 17439-97-6 ( M e r c u r y 1 0. 13 IgI 17440-02-0 JNickel-1 17440-09-7 IPotasslumI - . 17782-49-2 ISelenium-1

' 17440-22-4 l~ilver-1 /O o IP I 17440-23-5 1 s o d i m - l - x l q l I ~ I 17440-28-0 JThallium-( T, 0 Id IF I (7440-62-2 JVanadiu-1 lo-0 &!I 17440-66-6 [Zinc I lo, o MI I I cyan= I 1.1 I I I 1.1 1-1

color ~efore: &'4h clarity Before: bR( Texture :

Color After: ~~ ' clarity After: k Artifacts:

Comments :

b i FORn I - IN

recycled paper

NYSDEC r

1 NYSDEC SAMPLE No. INORGANIC M A L Y SIS DATA SHEET

'w I I I CUl-6

c o n t r a c t : B o / ~ I I Lab Name: &wb)' t 6 V l ~ d r l ~ ~ . I

Lab Code

M a t r i x (

Leve l ( 1

Z S o l i d s

so i

Case NO. : 9m~.Jg6 sx NO. : y n / - * ~ SIX

l / v a t e r ) : fl%~X- Lab Sample I D : . med) : LQd Date Received:

n c o n c e n t r a t i o n U n i t s (ug/L o r mg/kg dry w e i g h t ) :

I - I I W No. I A n a l y t e I I (7429-90-5 IAlumin--1 25000 17440-36-0 (Antimony-1 17440-38-2 J ~ r s e n i c - I (7440-39-3 )Barium-I 17440-41-7 ( B e r y l l i u m ( 17440-43-9 J C a d m i u m I 17440-70-2 lcalcium-1 (7440-47-3 (Chromium-( 17440-48-4 17440-50-8 (7439-89-6 17439-92-1 !Lead I

(7439-95-4 JMagneslumJ (7439-96-5 (Manganese1 17439-97-6 [Mercury-I 17440-02-0 J N i c k e l ) (7440-09-7 ( P o t a s s l u m l 17782-49-2 (Selenium-( I I

' 17440-22-4 /Silver-1 17440-23-5 ( S o d i u m 1 (7440-28-0 IThalliurn-( 17440-62-2 17440-66-6 I I I I 1-1 1-1

No.:

h d d C o l o r Before : C l a r i t y Before: T e x t u r e :

color l f t e r : C l a r i t y After: L " ~ y A r t i f a c t s :

Comments:

recycled paper F-145 I ~ C I I ~ I P ~ ? I I I I I I ~ n v i r c ~ ~ l r p ~ , ~ ~ ~


'. M S D E C S W L E NO.

I

'Cr' w-6 I

Lab Name: &utf &W,V~EM 5. Contract: D w ~ ( fi~m3 I I

Lab Code: case NO.: fbv.320 SAS NO.: YX*%W SDG NO.:

Matrix (soil/water) : W m

Level (low/med): Ulr/

Lab Sample ID: .65322.07

Date Received:

% Solids: 0


Color Before:

Color After:

Comments :

I . I ICAS NO. I Malyte I I I (7429-90-5 (Aluminum-1 /6V 17440-36-0 (Antimony-1 17440-38-2 JArsenic-1 (7440-39-3 (7440-41-7 17440-43-9 17440-70-2 (7440-47-3 (Chromium-( 17440-48-4 ICobalt-1 17440-50-8 JCopper-1 (7439-89-6 (Iron 17439-92-1 (7439-95-4 (7439-96-5

(7782-49-2 ISelenium-1 I I 17440-22-4 ( S i l v e r ( 17440-23-5 J S o d i - I

IpI 17440-28-0 JThallium 1 2. 0 ( 7440-62-2 (vanadium-( 1 0 . 0 ,

IF I

-1 17440-66-6 (Zinc /s. 4 I I CyanLda_l I I I

lh?L-' Clarity Before: &V? Text

k . Clarity After: c ~ 4 h Art i

NYSDEC

1 I

NYSDEC SAMPLE NO, ZNORCANIC ANALYSIS DATA SHEET I I

'+w Lab Name: & ; o ~ o b ~ t & R o A / r l ~ ~ . contract: mf4/9 i GW-7 I

I I

Lab Code: case NO. : 9flt3fl SAS NO. : Y N - ~ o z D SDG NO. :

Matrix (soil/water) : W47Ep

Level (low/med) : LDU/

Lab Sample ID: .M3WB06

Date Received: L / B / ~ % Solids: 0


I . I I 1 1 - B Ifll ICAS No. I Analyte (Concentration(C( )f ($I I I I 4-1 17429-90-5 J~luminum-I 2-000

i / i -.ILL

(7440-36-0 (Antimony-/ 171

1

17440-38-2 ~~rsenic-I j 7440-39-3 1 Barium I 17440-41-7 (Beryllium1 (7440-43-9 (Cadmium-1 - (7440-70-2 ( C a l c i u m ( 2 17440-47-3 (Chromium-( 0.0 17440-48-4 (Cobalt I 17440-50-8 lCopper I (7439-89-6 llron I (7439-92-1 (Lead 17439-95-4 i~agn; 17439-96-5 IUanganeseI 17439-97-6 ( U e r c u r y I 17440-02-0 I Nickel I 17440-09-7 1 potass5 - . 17782-49-2 ~ ~ e ~ e n i u m - 1 /: 0

' 17440-22-4 JSilver I 17440-23-5 J S o d i u m I (7440-28-0 (Thallium-I (7440-62-2 (Vanadium1 (7440-66-6 (Zinc

-+ I-

color ~cfora: Clarity Before: Texture :

Color After: & Clarity. After: h)' Artifacts:

Comments:

recycled ~ a o e r c.c.~,lc~p! I I I I ~ rnr i rc~yrntr t~

NY SDEC r

1 WfSDEC SAHPLE NO. INORGANIC ANALYSIS DATA SHEET 1

&lu-7 I ++

Lab Name: &;OLDG.J t&ku~rlW TM . c o n t r a c t : n&'9 I f/~/ma I I

Lab Code: @.,%D Slu No.: YB/N-$~ SIX No.: Case No-,

Matrix (soil/water) :

Level (low/med) : LOW

Lab Sample ID: .k43Z3167

Date Received: @/?Q Solids: P

Concentration Units (ug/L or mg/kg dry weight):

Color Before: h Color After: '

Clarity Before: & Clarity After: 6 e 4 ~

Texture:

Artifacts:

Comments :

recycled paper

NYSDEC

'Irrr Lab

Lab

Name:

Code:


AL LOG^ ~.L~IKCWAEUT~. contract: b ~ / ~ / q Case NO.:$~J.#~ SAS NO.: Y#-+o.zo

Matrix (soil/water) : W m

Level (low/med) : COW - Z Solids: 0

I NYSDEC SAMPLE NO,

. -

I I

SDG No.: - Lab Sample ID:

Date Received:

Concentration Units (ug/L or mg/kg dry weight): - -

I ( CAS NO.

1 Aluminum 1 ~ntimonyz 1 Arsenic- 1 Barium- 1 Beryllium 1 Cadmium 1 calcium- 1 chromium_ ( Cobalt- I Copper- ( Iron 1 Lead _. 1 Magnesium (Manganese i ~ercury- 1 Nickel 1 1 Potasslum

i Selenium- 1 Silver- 1 sodium- JThallium- 1 Vanadium- - 1 Zinc I cyanide_

Color Before: ) IEUO& Clarity Before: ~ W D Y Texture : - . Color After: Clarity After: Artifacts:

Comments :

recycled paper

N Y S D E C r

1 NYSDEC SAHPLE NO. INORGANIC ANALYSIS DATA SHEET I I -

Lab Name: & C O L ~ - Y AND E~vl / 'Rorla~, /& Contract: I I 5Ld-1 I I

Lab code: EANOE Case No.:‘?oa3-WS SAS No.:YN-4020 SDC NO.:

Matrix (soil/water) : N ~ E R Lab Sample ID: 65 3 4 4

Level ( low/med) : W\c/ Date Received: 02/10 /?o

' 8 Solids: 0 Concentration Units (u,g/L or mg/kg dry weight): 4 4

I I - 1.1 -

i ' i I Aluminum I /b 300 1.1 I Antimony- 1 60.0 lgl

lei I~rsenic-1 16-6 1-1 IPI 1 B a r i u m 1 3 oq 1.1 1 Berylliuml t o kl

lei (Cadmium-( 4.5 1 I ICalcium-l i rzooo

I f ! IChromium-I 43.0

1:1rzz121 1-1

1 Cobalt-1 10.0 131 1 copper- 1 10 Q 1.1

'+I

1 1ron I ~ 0 3 0 0 I$

1.1 133

I I IL-d I (Hagneslum ( 3 8 5 0 0

IEI IUanganesal e b 2

i::--l&l '1-1

IHercury I IPI

INickel -1 0*3+ 1.1 la! 1

7 ES.. 6 1.1

1 ~otasslum 1 3450 18 1 JSelenium-1

1% 1 3 I B I S ' IEI

I silver-I /O.O 1 ~ 1 I S~~~=,-I-I.IECI~I (Thallium ( 3 . 0 IS1 1 vanadium- 1 53.7 1.1 1 Zinc

I f l l ~ o l . 1 - I ~ I

1 ~ y a n r l 1 - 1

10 .0 la1 I I I I

Color Before: houlu Clarity Before: CLOLIOV Texture :

Color After: '/duar3' Clarity After: ~ D V Artifacts:

Comments :

F O R M I - I N ss c . w l a a k j ~ u d & ~ i i R m ~ h ~

F-150

NYSDEC r


tab Name: & ND b n / ~ / ~ Q o ~ e f i , l . Contract: i 5 N - 2 I

cocwv A I I

Lab Code: EANDE case No.:4000-WS SAS No.: 2/d-4020 SDG NO.:

Matrix (soil/water) : YPTER Lab Sample ID: . 65368 Level ( low/med) : /od . Date Received: 02/ro 190

4 Solids: a Concentration Units (ug/L or ag/kg d& weight) : &&

I . I I (CASNO. ( Analyte I I 17129-90-5 lAluminun-1 r 17440-36-0 J~ntimony-1 (7440-38-2 IArsenic-1 2.5 181 1x1 (7440-39-3 (barium I .s)d

17440-41-7 lBexyllluml A-0 IS1 If-1

17440-43-9 ICadmium-1 161

(7440-47-3 (Chromium-1 r0.o 121 17440-70-2 (Calcium_I ,qriozO I 1 - 1 ~ 1

. (7440-48-4 (Cobalt-( 10.0 - (a1 1-1 '&I 17440-50-6 !copper-( 14-\ 1-1 (7439-89-6 IIron ( ~ 1 - 1

6 (7439-92-1 IUad , I 17439-95-4 InagnerlumI fIrlel (7439-96-5 Inanganese I -1-1 17439-97-6 ~ n e r c u r y l o*= lgl

lei 17440-02-0 INickel-I tS.0 121 17440-09-7 IPotasslumI 2 5 6 0 IP1 (7782-49-2 (Seteniurn-( 1-.r 181

' 17440-22-4 (Silver-I /O*O Id1 (El

17440-23-5 ISodi~-( 245000 ILI

17410-28-0 IThallium 1 I I L I

0 I E I 17440-62-3 ~~anadium-1 lodo Id1 17440-66-6 [Zinc -I 15 2

[el lei I I cyanIG-1 10.0

I -1 101

1 1-1 [.,I . Color Befor.: k o a u Clarity Befor.: &dm Texture :

color ifter: YELLOW. - Clarity After: C~oaoll, Artifacts :

Comments:

F O R M I - I N iE*& @?$3f% F-151 1 c d m , t ~ % + f A ~ & ~

NYSDEC r

1 W S D E C SAHPLE NO, INORGANIC ANALYSIS DATA SHEET I I

fab Name: E c o ~ c x l ~ A ND E~vtRD/?cilvt,/,c Contract: I 1 5 d - 3 I

I

Lab Code: EANOE Case No. : 4000-WS SAS No. : Z'N-4020 SDC No. : - Matrix (soil/water) : NAT~R Lab Sample ID: . 6 5 S b q

8 Solids:

. Date Received: 0zho /90

concentration Units (u.g/L or mg/kg dry weight): 4~ I I - 1-1

- )Aluminuzn-1 /Y? IAntimony-1 (0.0

181 ( Arsenic-1 I, 0

lei Idla-,lf,l

1 B a r i u m 1 32. \ 1Q1IPI 1 Berylliuml 2.0

ICadmium 1 .O I calcium-1 ++s:o (Chromium ( 10.0 1-1 ( ~ o b a l tL I JO.0 1-1 I copper- l /o. 0 1 Xron I b a d - I /, 0 (Hagneslum( 20690 IHanganeseI 1 36 1-1 IHercury I o*m IS1

lei INickel -1 7

15.0 1 a1 1 PotasslumJ 21 10 JSelenium 1 IOO

161 1 silver--l /D. D

141 ISodfu-1 9 2300

ler 14-lel I ~ a l l i = - I ~ l yl IVanadiua I /o-0

-1 1.1

1 zinc 16.9 kl IPI I C y a n T ~ 1 -1

la.0 la1 I I

ICI 1. I

Color Before: Clarity Before: bcena T8xture :

Color After: CLUR ' Clarity After: CLEAC Artifacts :

NYSDEC


NYSDEC SAMPLE NO.

I I

Lab Name: & COLWY A ND Ed~~rtomiM, /PJC Contract : I I did-9 I

I

Lab Code: E A N D E Case No. : 900O0WS S U No. : Y'N-40ztr SDC No. : - Matrix (soil /water) : MNEQ Lab Sample I D : . 6 5 3 ~ . t e v e l (low/med) : /9d . Date Received: 02/10 190

8 Sol ids : 0 Concentration Units (ug/L o r mg/kg d& weight) : 4~

I . I I (CAS No. 1 Analyte

m- 1 2Zoo 1-1- mtimony- 1 6 0 ~ 0 la1 Arsenic-1

IZI 2.a 1 bl IPI

lsarium-I 0v .e I Q I 121 ( Beryllium (Cadmium-( (Calcium-( 1 14 ooo ( Chromi urn- ( (Cobalt- (

z* CI I Copper- I I 1 Iron .CTOOO

( Lead _. I 6b IUagnesiu( 2aroo

IUercurY-l ~ , ~ g . l d l la1 INickel - I IS. o ~ ~ o t a s s i u m l ;'3b?o I Seteniunr_ 1 1 S i b e r I

1.0 10.0

ISodium-I Z ~ % O O O JThall iua I 2.0 I vanadium: 1 10.0 1 Zinc 1 1 - 1 !cyan=! I O . 0 ! A!

Color Before: % ~ u Clar i ty Before: C L O A O ~ Texture :

Color After: \ I E L L O ~ Clar i ty After: C w u q Art i facts :

Comments:

NYSDEC r

1 HYSDEC SAMPLE NO, INORGANIC ANALYSIS DATA SHEET

I I

tab Name: E COLW J A ND ~ ~ ~ v ~ / / R D M G ~ , /NC contract: I I A/-5 I I

Lab Code: € A N D € case NO.:~OW-'MS SAS NO.: YN-4020 SDC ~o.: - Lab Sample ID: .65?=+(

. Date Received: cz//c/4c

Solids: 0 Concentration Units (ug/L or aq/kg d& weight) : d~

I . I I JCAS No. 1 Analyte

Color Befora: - 1 ~ Clarity Boforo: Q w a Texture :

color ~fter: $ 5 ~ ~ 0 3 Clarity After: C e a a Artifacts:

Comments :

1 WSDEC S M L E No, INORGANIC ANALYSIS DATA SHEET I I

tab Name : ECOL-~ AND Edv/Ro~bfl, /NC Contract: I 1 ad-6 I I

Lab C

Matri

Leva1

. t Sol

ode: E A N D E Case No. : 9000-WS SAS No. : '/E/-4020 SDG NO. : - x (soil/water) : N ~ C R Lab Sample ID: . 65772

( low/med) : - /od . ate ~eceived: or/to 190

ids : 0 concentration Units (U.g/L or mg/kg dry weight):

I . I (w No. ( Analyte I I I 17429-90-5 IAlur~inun_l 46 3 (7440-36-0 JAntimony-I 60.0 (7440-38-2 ( ~ r s e n i c l 6. B 18 1 IEI 17440-39-3 1 Barium7( 5 b 6 3 la l 17440-41-7 1Berylliuml 2.0

lei (7440-43-9 JCadmium-1 5.0 17440-70-2 (Calcium1 W R ~ O 17440-47-3 IChromium-1 10.0 17440-46-4 ICobalt-1 40.0

131

lgl '&I 1 1 1 1 - 1 1

(7440-50-8 ICopper-l 23 .R (7439-89-61Iron 1 ' t ~ - 1 , 1 17439-92-1 IfRad . I 13. 1 1-1, 17439-95-4 JUagnesiumI 14 80- 1,l~lPI 17439-96-5 Inanganesel m 1,1121 17439-97-6 (nercury-I 0.20 161 17440-02-0 ( N i c k e l 1 S.0 191

1

17440-09-7 JPotassiuml 3sb0 . 17787-49-2 JSelenium-1 /, o @I ral ' 17440-22-4 ISilver-1 10.0 It1 17440-23-5 (Sodiu-1 3bSOO

lei 17440-28-0 IThalliu-(

I . I ~ I L I 17440-62-2 IVanadium-1

2.0 ldl- ' 0 .0 1.1

17440-66-6 lzinc 1 a S . I - 1 If l IPI

I I cyan= I -1

r 0.0 lkJl I 1 1-1 I.,I . IAI

Color Before: Clarity Before: b u o y Texture :

Color After: )~ELLOLS_ Clarity After: @ L O ~ D ~ Artifacts:

Comments:

rec cl d pa er re&c%d &er

NYSDEC

1 N S D E C SAHPLE NO, INORGANIC ANALYSIS DATA SHEET I I

Lab Name: - ECOLWY AND E w / & n l ; ~ , /dc Contract: I I Slhi'? I

I

Lab Code: E A N D E case No. : qooO-WS SU No. : r'N-40 zo S ~ G NO. : - Matrix (soil/water) : L ~ A T E R Lab Sample ID: . 65'$73 b v e l (low/med) : W\rl Date Received: 02/10 140

8 Solids: 0 ncentration Units (u,g/L or mg/kg dry weight):

I . I I I I - Q I r [as No. ( Analyte (ConcentrationJCI 1 3 1 -

I - I 1-1 1 Aluminum I 21 zo 1-1

i/-i IAntimony-1 60. o

lZl l y l

JArsenic-1 a%*', 1 - 1 lei 1x1

1 B a r i u m 1 I 4b 1 Berylliuml 2.0

IB I let I Cadmium- 1 JCalcium-1 594 oo (Chromium ( 1 -1 1 cobalt- ( 10.0 - IaI- I '+I - I I Copper- l la e

I 1.1

1 Iron ( h a d 7

JHagnesruml te coo I I L I IXanganeseI 1 ( 1Xercury I 0.20

lei JNickel -1

1 2 0 1-1

( P o ~ ~ s s ~ u ( 3360 1 GI (Selenium_( I . I 181U I Silver-1 ro. o 1E1

rq 400 1'4 1

I soaim-l let 1 1 e 1

JThallir.lrI 2.0 I k l lvanadiu-1 ZY .I) la-IPI 1 Zinc 1 3 0 2 1 . 1 I ~yanid._l r 0.0 la1

Color 80f0t8: -h6d~1 clarity ~eiore: h 5 y Textuie :

Color After: )IELLDJ Clarity After: Cauoy Artifacts :

Comments:

NYSDEC r

1 mSDEC SAHPLE NO, INORGANIC ANALYSIS DATA SHEET I I

Lab Name: E c o c w y AND E~v~//Ronl;f l , /~c contract: I 5 W - a I I

Lab Code: EANBE Case No. : 9000.WS SAS No. : )"iV-You, SM; NO. : - Matrix (soil/water) : Ldrn~a

Level (low/med) : /0\3

Solids: 0

Lab Sample ID: -657 3q

. Date Received: 02lrc 190

Concentration Units (ug/L or mg/kg dry weight) : dL

Color Before:

Color After:

Comments :

Clarity Befor.: o q Texture :

Clarity After: Crouoy Artifacts:

rec cl d rec?'ycYeB&p"Qr

NYSDEC r

1 NYSDEC SAMPLE NO, INORGANIC ANALYSIS DATA SHEET

I I

Lab Name: E COL-Y A HD En/~~Roncfl, / ,c Contract : I SN-9 I I

Lab Code: E A N D E Case No.:90001WS S M No.: YN-4020 SDG No.: - Matrix (soi l /water) : N ~ E R

Level (low/med) : / o \ E /

Solids: 0

Lab . Sample ID: . 6 5 ~ 3 5

Date Received: 02/10 190

Concentration Units (ug/L or mg/kg d q weight):

I - I JCAS N o . I Analyte

Color Beform: BPDW~\~ Clarity Before: &UO$ Texture:

color After: {&u3 c l a r i t y ~ f t e r : C L O U Q ~ Artifacts:

rec c l d a er reZyc7ecPptper

NYSDEC r

1 W S D E C SAKPLE NO. I HORCANIC ANALYSIS DATA SHEET I I

~ a b Name: E c 0 L - Y A ND ~ ~ ~ l ~ o n r ; ~ , / . c Contract: I I SN-10 I I

Lab Code: EANBE Case No.:~o~O,WS SAS No.: W-40m SDG NO.: - Matrix (soil/water) : NATEI;L Lab Sample ID: . k 5 7 3 6 . Level (lov/med) : U d . Date Received: ozho 190

t Solids: 0 Concentration Units (u.g/L or mg/kg dry weight): d~

Color Beform:

Color After:

Coamentr :

I I - 1.1 -

r',I (Aluminm-1 3420 1.1lPl IAntimony-1 60.0 151 IArsenic-1 . . 8. + la lpl

lei 1 Bariuml\ 113 I& I 121 IBeryll~uml 2.0 1 Cadmium- 1 5, o I Calciura-1 43700 ( Chromium- ( I s.4 1.1 ( Cobalt- 1 10.0 ' Igl- I '*I - I I Copper- I 15 I 1 Iron 1 ztboo 1.1,- 1 Lead - I /o l 1.1 lnagnesiuml r8 too l l ~ l l X a n g a n e s e l ~ 1 . 1 l&l I nercury- I 0.20 ILblIMl 1 Nickel-I 3 . la1 IPotass~umJ 35Ra 101 ISelenium I 1 silver--l

1.1 I H I ~ I E I /oeo Id1

l s ~ i ~ U I P l IlcoOO lei

I , I ~ I L I (Thallium I 2-0 I&I ILI (Vanadium, I 191 1 Zinc I 3 \ \ 1.1- - lei ( ~ a n i d . 1

lP l 1 6 0 ,

-1 ~ I ~ I

I I I I. I I I 1 , 1 I I

Ah&L Clarity Before: Ccovoy Texture :

+ELLOW Clarity After: l couol Artifact

rec c l d pa er re&& pfper

NYSDEC r

1 N Y S D E C SAMPLE NO, INORGANIC ANALYSIS DATA SHEET

I I

Lab Name: k o r o b \ / qda ~?.IO~U.-UVT, ),UC Contract : I ~ V I - 1 1 I I I

Lab Code: EANi lE case NO. : 9000- 726 SAS NO. : W-402.0 SDG NO. : - Matr ix ( s o i l / w a t e r ) : L ~ A ~ c

Level (low/med) : d.04

Lab Sample I D : -66030 . Date Received: o2//3190

% S o l i d s : 0

c o n c e n t r a t i o n U n i t s (ug/L o r mg/kg d r y weight ) : G./L

I 1-1 I/, i ~ l u m i n u - 1 113 IBI i f - 1 Antimony- I Arsenic- 1 1.3

re1 IEI

Barium - 1 2 6 b d Beryllium1 p.0 kg lei Cadmium- 1 5.0 lYl Calcium-1 5 ?LOO 1 - 1 Chromium- I 10.3

lei C o b a l t 1 c o p p e r I p . 3 IUI

1 I r o n l Lead

1-1-1 I

[el 1.0 ILI'LJIEI

(Manganese ( %-1:1 I Mercu-1 O*Lo IU (Nicke l 1 7

/ a I % ( 1 Potasslum 1 25 30 lgl (Selenium I I ~ i l v e r L 1 1 Sodium__l JThal l ium I l ~ a n a d i u m I ( 1 Zinc I I cyan-l

Co lo r Before: C L E ~ R C l a r i t y Before: &-R Texture :

Colo r Af t e r : C L E A ~ ' C l a r i t y After: A r t i f a c t s :

Comments:

recycled paper

NYSDEC r

1 '. NYSDEC SAMPLE NO.

INORGANIC ANALYSIS DATA SHEET I I * I

Lab Name: t & , ~ d r ) w 7 contract: n ~ m I Slu-/Z I xi. I I

Lab Code: case NO.: fm.380 su NO.: Xb-foz.0 S D ~ NO.:

Matrix (soil/vater) : I C / / ~ E ~

Level (low/med): LON

~ a b Sample ID: . I ;S~Z*DL

Date Received: f</b

Z Solids: 0 concentration Units (u,g/L or mq/kq d?, w e i g h t ) : u<L

Color Before:

Color After:

Comments :

I . I I I I' B lrnl ( c i s NO. 1 Malyte IConcentrationlCI I

17440-47-3 JChromium-1 (7440-48-4 (Cobalt-1 17440-50-8 !Copper-1 (7439-89-6 (Iron 17439-92-1 [Lead I

17439-95-4 IMagneslumJ I I

1 1-1

k' clarity Before: d& Text

k Clarity After: & Art i

'e:

cts:

recycled paper

WSDEC r

1 WSDEC SAMPLE NO. INORGANIC ANALYSIS DATA SHEET I

I

Lab Nase: E & u ) d ~ ~ & / ~ ~ 3 ~ . Contract: -a?o/3jf l I

Lab Code: case NO. : 9 n ~ ~ 4 5 0 SAS NO. : Y W O M SDG NO. :

narrix (soilpater) : W e Lab Sample ID: - 6 5 3 ~ 06

~ e v e l (low/med) : LOd Date Received: 2 8 78 % Solids: D

// concentration Units (ug/L or mg/kg dry weight): U ~ L

I - I I I 1 - Q I f l I IcAS No. I Analyte [Concentration(CI W/

Color

Color

Comme

* Before

After:

nts:

I

Clarity Before: &~th Text

clarity After: k Arti ts:

recycled paper I * I . I I ~ I I ~ ! I I I I I ~ I * ~ V ~ P I I I I I ~ I ~ - I I I

F-162 698

h Lab Name: &L&Y & , w N & W T ~ C contract: W~/fi? I 1 su/-/5 I I

Lab Code:

-

Case NO. : PPm. JBb SAS NO. : Y , v o ~ sw NO. :

Matrix (soil/water) : 1JM Lab Sample ID: LC326 '

Mr. , * ,---, .-.--, - -- -- ..--.-*. b". -, ", {"

1 Solids: 0 concentration Units (ug/L or mg/kg d q weight): yb


NYSDEC SAMPLE 60.

I 1

17440-48-4 JCobalt 1 ( 7440-50-8 (Copper I (7439-89-6 (Iron I ( 7439-92-1 (Lead - I 17439-95-4 lMagneslunl 7 1 17439-96-5 l~an~anesel- 17439-97-6 JMercux-y-1 17440-02-0 JNickel 1

7

(7440-09-7 (Potasslum( 15 - . 17782-49-2 (Selenium 1 . 7 - * 17440-22-4 ISilver-I e

17440-23-5 (Sodium 17 17440-28-0 JThallium-1 17440-62-2 IVanadium_) (7440-66-6 JZinc 1

Color Before: )hwu/ Clarity Before: Textur'e :

Color Aftar: Yw& Comments :

Clarity Attar: k Artifacts:

recycled paper

NYSDEC

1 NYSDEC SAMPLE NC INORGANIC AYALYSIS DATA SHEET I

Qw I

Lab Name: &EM)/ f ~J,&A/IuEM J;;(. contract: BOO/*? I I A/

Lab Code: Case NO. : B ~ J . u o / SAS NO. : YN*L/o~D sx NO. : b-1 - Matrix (soil/water) : WTFR

Level (low/med) : L D ~

~ a b Sample ID: . Y / f l ~ Date Received: b,//b/g9

% Solids:

Concentration Units (ug/L or mg/kg dry weight): U ~ L

I I I I 1 - 1 I (CXS No. 1 Analyte (ConcentrationlCI M ( Q (

I Aluninu- 1 Antimony- I Arsenic - 1

Chroniua - I Cobalt I - Copper- I Iron I Lead I Hagnes i in 1 Manganese( Mercury 1 Nickel -1 7

Potassruml Selenium-( Silver-1 Sodiun 1 ~ h a l l i c l Vanadiun- 1

Color Before:

I 1 - 1 1-1

Clarity Before: Texture :

Color After: Clarity After: Artifacts :

Comments:

recycled paper rec.yilr:tf pd11t:r recycled paper

APPENDIX G

SUBSURFACE SOIL, GROUNDVATER, SURFACE SOIL,

SURFACE WATER/SEDIWENT, AND LEACHATE SAnPLING PROCEDURES

recycled paper

Subsurface Soil Sampling

One subsurface soil sample was collected during drilling for

chemical analysis and seven for geotechnical analysis. The sample for

chemical analysis was collected from the soil horizon exhibiting

discoloration and odor (17-19 feet) from GW-7 well bore. All of the

samples were collected using a decontaminated split-spoon sampler driven

by a 140-pound hammer on the drill rig. Blow counts and total recovery

were recorded for each sample (see Appendix D). After retrieving the

sample, it was screened with the HNu and a pre-cleaned stainless steel

spoon was used to place the sample for chemical analysis in a

pre-cleaned, acid-rinsed, 8-ounce jar equipped with a Teflon-lined lid.

Samples for geotechnical analyses were placed in 16-ounce Mason jars.

Groundwater Sampling

Seven groundwater samples were obtained from each of the seven

wells on site and analyzed for TCL organics and inorganics. A

dedicated, decontaminated PVC bailer was used with new, dedicated nylon

rope at each well. Prior to sampling, a groundwater-level reading was

obtained, along with a total depth-of-well reading. An amount equaling

three standing water volumes was calculated and purged prior to

sampling. The first bottles to be filled were those containing sample

water for volatile organic compound analysis. This was to minimize the

turbidation of the water so that the volatile content would remain

intact. The second bottles to be filled were those for total metals and

dissolved metals analysis. A reading of the turbidity was immediately

taken using a portable nephelometer. If the reading was greater than 50

NTUs, the dissolved metals bottle was retained for filtration. If the

turbidity was lower than 50 NTUs, only the total metals analysis was

performed.

Additional field parameters measured included pH, temperature, and

conductivity. Measurements of pH were taken in triplicate, while

measurements of conductivity were taken in quadruplicate for accuracy

purposes. Prior to filling, all sample bottles were labeled with water-

proof ink and labels were covered with clear mylar tape. After all

bottles were filled, the bailer was placed in the well and suspended

above the water table, and the well casing lid was locked. The filled

recycled oaper

bottles were packed into coolers containing vermiculite and ice, then

transported at the end of the day back to E & E's ASC for analysis. All

samples for metals, both total and dissolved, were preserved by adding

concentrated nitric acid to the sample until the pH of the sample was

lowered to less than 2.0. All samples for cyanide analysis were

preserved by the addition of sodium hydroxide. Pellets of NaOH were

added until the pH was raised to greater than 12.0.

Surface Soil Sampling

Eleven locations were selected for surface soil sampling. All

samples were analyzed for TCL organic and inorganic compounds. The

individual soil sample was obtained from the top 6 inches of topsoil by

using a pre-cleaned stainless steel spoon to fill a pre-cleaned,

acid-rinsed, 8-ounce clear glass soil jar equipped with a Teflon-lined

lid. This volume served for total metals, base/neutral and acid

extractables analysis and PCB/ pesticide and cyanide analysis. In

addition to the 8-ounce jar, two 40-1111 clear glass vials, each equipped

with Teflon septum, were filled for volatile organic analysis.

Surface Water/Sediment Sampling

Fifteen points were delineated in the work plan as locations at

which both a surface water and sediment (SW/SWS) sample would be

obtained. The field locations were matched as closely as possible to

the locations described in the work plan. These samples were analyzed

for TCL organics and inorganics. Eight additional samples were

collected, as directed by the NYSDEC on-site representative for the

railroad drainage swale off site. These samples were analyzed for

PCBs/pesticides only.

Sediment samples were obtained by using a pre-cleaned stainless

steel spoon to fill an 8-ounce pre-cleaned, acid-rinsed jar equipped

with a Teflon-lined lid. This volume served for total metals, base/

neutrals and acid extractables, PCB/pesticide, and cyanide analyses. In

addition to the eight-ounce jar, two 40-1111 glass vials, each equipped

with a Teflon septum, were filled with sediment for volatile organics

analysis.

recycled paaer

Three waste samples were collected at the Golden Road site. Two

samples were foundry sand and one sample was a resin-like substance

obtained from a partially buried drum. The samples were collected using

the sample procedures outlined in the surface'soil sampling section, and

all of the samples were analyzed for TCL organics and inorganics.

Leacha t e

Two leachate samples were collected at the Golden Road site. One

was in liquid form and one consisted of leachate-stained sediment due to

insufficient liquid content. The liquid sample was collected by direct

immersion of the appropriate sample bottles (see Section 4.4.2). The

soil sample was collected using the same procedures as the surface soil

and sediment samples. Both of the samples were analyzed for TCL

organics and inorganics.

recycled paper

APPENDIX EI

SITE SURVEY HAP

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APPENDIX I

SITE FIELD LOGBOOKS

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OM P. POPLI, P. E.

NYSDEC PHASE I1 IHVESTICATIONS

DAILY SITE REPORT

Date 6//1/B9 - NYSDEC IDA 8 z@OZ\ Site Name GO LDE r\l ROAD D S P O ~ A L SIT& S ~ ~ ~ N O . V N L ( O Z O < A & O Z ) Work Start Lunch Finish Weather Conditions - Personnel On Site:

NYSDEC Om P. Pop1i.P.E Driller

Personnel Safety Equipment: Om P. Popli, P. E. Driller

Level of Protection r or ryvdu

r of Tyvek Booties

w I of Disposable Clover

Environmental Equipment On Site:

Meter I

Calib. Date

Readings Above Bachqroundo

HHu Meter 901394 5 bplorimeter C T Y ~ Y ~ & t o x (HCN) 035863

- --

Mini-Rad 20655 Y H Meter ephlomeler r;

Cunur 303cnl74 Water Level

Indicetor TU) Badge SC-6954 0004 1

.If meter rudings exceeded background. see reverse side for Commentr.

recycled paper

- -----', '---- -.. - NYSDEC PHASE I1 INVESTIGATIONS

'u DAILY SITE REPORT

Date b ,,h5 /H - TMUL,

Work Start UC;50 & NYSDEC m#*) Site Name &OLDE/ &Ha ~i3fb.sA'~ f

. - Lunch /lob ,- //30 -& Finish /hZ5 & . Weather Conditions Q/&ZX/SSI. . s ~ / Q . / l Bk€E&, ~ # / / l c k A d , b5 *F 3

/

I d' , , ' , - 1 ._ . . . ..'V , . " 5 , . i , . , t

Personnel On Site: .' :,.,.;;: . . . .. >. . .

NYSDEC Om P. Popli,P.E. Driller - n//c,4L /%5@1d4 - -6 (-%?/&LC

. .- *


Level of Protection

l of Tyveks IofTyvekBootia

/ of ~ i s ~ o s a b l e Gloves


Meter Used Calib. # Today Date BY

HNu Meter 901394 Explosimeter C2537 Monitox (HCN) 035863 Mini-Rad 20655 pH Meter - - Nephlometer - - Camera 30302174 r / N A ' NA Water Level \

Indicator d N A N A TLD Badge SC-6954 0004 7 N A N A

Readings Above Background

r l

.If meter readings exceeded background, see reverse side for Comments.

'age l of 2 recycled paper

Equipment On Site: Deconlam ination Z z

Drill Rig Type Water Tanker / Steam Jenny / Bulldozer / Air Compressor / Other /

I

Detergent Wash Potable H20 Methanol Distilled Water Plastic Cover Other

DESCRIPTION OF WORK COMPLETED , . , . , . <

SPECLAL COMMENTS I

- / 1 . I

Approvals. - e

Driller NYSDEC

Page 2 of 2 L

recycled paper

L' I .

NYSDEC PHASE I1 INVESTIGATIONS

DAILY SlTE REPORT

Date / - ~ e s / ~ g 8 / t t / 5 4 NYSDEC IDA 82602I Site Name 'c-ddeq toad D: roola 5 :fc - Site No. YN Y o 20 Work Start //30 Lunch / t o o - / Z 3 U Finish /700 Weather Conditions v 8 0 ' - / t b 4 f d4~ 'zz /c rwd 0 f d II/

1 I - - ..,,

Personnel On Site: , -' . , :, ,

I

NYSDEC . Om P. Pou1i.P.E I, Driller

I : . . . :- Om P. Popli, P. E. Personnel Safety Equipment: Driller

Level of Protection 5' D

'Isl I of Tyvek Booties I of D i s p a b l e Gloves

Environmental Ecruipment On Site:

Meter Used Calib. I Today Date BY

M u Meter 901394 Explosime ter C2537 Monitox (HCN) 035863 Mini-Rad 20655 pH Meter Nephlometer Camera 30302174 Water Level

Readings Above Background*

Indicator A N A N A N A TLD Badge SC-6954 0004 Y N A N A N A

30 6QfYdoor v

I f meter readings exceeded background. see reverse side for Comments.

Page 1 of 2 recycled paper

I Equipment 00 Site:

Drill Rig Type ALki/ Water Tanker '( Steam Jenny 'f Bulldozer H

I Air Compressor Y I Other

Decontarninalion Zone:

Detergent Wash 1

Potable H-0 4 Methanol Distilled Water L _Y -

Piastic Cover Y Other . S - ~ C O ~ cfu-

DESCRIPTION OF WORK COMPLETED i

- 7.0 ' ~cflcefi.~-&LbZLL$ 8% fi PCLM ,UYSD~C -w& A& 'd /4.b6(& 7h-k &) x " R

-D I /.f d I 300 - J ~ O O 0 vr 1 - r e d P o v : P d /r;f

f~ use OW , 5 - ~ & 6 , J

SPEClAL COMMENTS

,--

Approvals -

OM P. POPLI, P. E.


DAILY SITE REPORT

Date NYSDEC I D A B z e o t 1 SiteNarne Gb\b& SiteNo. \/EJ@ZO Work Start O 730 - Lunch /ZOO - / 2 3 6 Finish /6$0 Weather Conditions M ; W TO'\ <\I;LL b.teezc

1 . .

, . 1 . . . s , . , \

Personnel On Site: .i: , ... . : . 1 I

NYSDEC - - Om P. Pop1i.P.E Driller - ', - ? I

s . L o b e t / ' , JCLNSEN

' ' V & N ; ; ~ ~ & U 8. 6 r o d b

Personnel Safety Equipment: .. Om P. Popli, P. E. Driller

Level of Protection G' / of Tyveks /ofTyvek+tia

I - / of Dismable Gloves , /d OA; I? 4

. > Y


Meter Used Calib. # Today Date BY

HNu Meter 901394 Y e /z3 /8? 3-D Explosimeter C2537 Monitox (HCN) 035863 Mini-Rad 20655 pH Meter Nephlometer Camera 30302174 \1 N A ' NA Water Level

Indicator TLD Badge SC-6954 0004

.If meter r;rdings exceeded background. see reverse side for Comments.

I - 39


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Equipment On Site: D e c o n t a m i n a t i o n Zone:

Drill Rig Type kc, w Water Tanker * Steam Jenny J Bulldozer d- Air Compressor 9 Other -

Detergent Wash Potable H 2 0 Methanol Distilled Water Plastic Cover Other

h DESCRIPTION O F WORK COMPLETED

- ,de~fL o-f IAL\! 17.2' I

SPECIAL COMhlENTS

Page2of 2 qfl recycled paper

OM P. POPLI, P. E. * > .

& . . , I


DAILY SITE REPORT

Date 7lu/rA 11 ~ / Z Y /8? NYSDEC IDA 82002./ Site Name H o d 3 1 ; p o ~ n 1 5,qr;- Site No. I/# 44 7 /, Work Start 0 73d ' ~ u n c h /z3o - /300 Finish /63G A .

Weather Conditions d o v l y 767 /

Personnel On Site: . .

NYSDEC ' Om P. Popli,P. E Driller

Fib WAN X. D A P J ~ N G E R Z. lJ-€tds~d


Level 01 Protection

f of Tyveks f o f T y v e k b t i n

- f of Disposable Gloves

Environmental Equipment On Site: . .

Meter Used # Today

HNu Meter 901394 Y Explosimeter' C2Y7 - Monitox (HCN) 035863 'r Mini-Rad #)655 Y pH Meter Nephlometer Camera 30302174 f Water Level

Indicator f l TLD Badge SC-6954 0004 .1

3 9 6153 Y - NH-69500003 r(

Calib. Date BY

Readings Above Backgroundw

, * .I1 metu readings exceeded background. see reverse side lo; Comments.

?age 101 2 recycled paper

Equipment On Si le: Dccontamination Zone:

Drill Rig Type Ilk4 Water Tanker Steam Jenny Y Bulldozer y Air Compressor f Other

v Detergent Wash I AILOAOY Potable H20 'f Me than01 Y Distilled Water y Plastic Cover r Other J ~ c ~ W d~*i.,

'. DESCRIPTION O F WORK COMPLETED

I

., , / y Approvals L.-LYb,/f-

L/NYS$ EC

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NYSDEC PHASE 11 1HVESTIGATIONS

DAILY SITE REPORT

Date fiidpl/ 8/~5/#/19 NYSDEC ID# 8z8°zl Site Name ' c-~/dc@ 4d O;S/O/A / 5,.f c . Site No. YNYazo Work Start 0730 -- Lunch /zao -1236 Finish / 7 G 0

Weather Conditions v 7< - !

Personnel On Site: -.

. . NYSDEC % . . . Om P. Pop1i.P. E Driller


Level of Protection 9 I of Tyveks .. , - 4 IofTyvekBooties - I 01 D ~ S ~ O S ~ ~ I ~ Gloves -


Meter I

Used Today

Calib. Date

Readings Above Backgroundm

M u Meter 901394 /r/ Explosimeter (2537 N

- -

Monitox (HCN) 035863 N Mini-Rad 20655 pH Meter

N Nephlomeler

Y A

Camera 30302174 N Water Level

Indicalor n/ TLD Badge SC-6954 0004

*If meter ieadings exceeded b~:kground, see reverse side for Comments.

recycled paper

Equipment OD Site: Decontamination Z s

Drill Rig Type ~ r k c f Water Tanker

+ Steam Jenny Y ' Bulldozer N Air Compressor 4/ Other

Detergent Wash N Potable H20 N

Methanol N

Distilled Water Plastic Cover L 'f

Other s + ~ A - c[eah

DESCRIPTION OF WORK COMPLETED

SPECIAL COMMENTS

1-44

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NYSDEC P H A S E 11 1NVESTlGATlONS

DNLY S I T E REPORT

1 & / 3 / 8 9 Date NYSDEC ID# %f - 05 SiteName AIQ- hi]' k': Site No. Yflqb20 - I#OZ

- -

Work Start 06a0 Lunch C ~ i n i s h jug Weather Conditions C . b & . - 5 \ r q h k VL- ,

" P e r s o n n e l On Site:

NYSDEC Om P. Popli, P. E Dri l l e r . - . hztPq&v

. -

P e r s o n n e l S a f e t y Equipment: Om P. Popli, P. E. Dri l ler

Level of Protection I of Tyvau I of Tyvek Boo ties h. of Espa*le cloves

Envi ronmenta l Equipment On Si te :

Meter I

Used Today

Calib Date

Readings Above Background.

HNu Meter 901394 J Explosirneter C2537 d

-

Monitox (HCN) 035863 d Mini-Rad 20655 J pH Meter Nephlometer Camera 30302174 f l Water Level I

Indicator 1 TLD Badge SC-6954 0004 ~1

.I1 meru readings exceeded background. see reverse side for Commenrs.

recycled paper

Equipmcnl On Site:

Drill Rig Tjpe /

Water Tanker /

Steam Jenny I

Bulldozer 4

Air Compressor /

Other

/

Detergent Wash Potable H20 - Methanol /

Disl.illed Water /

Plastic Cover /

Other /

DESCRIPTION O F WORK COMPLETED

SPECIAL COMMENTS

Approvals Om P. Fopli, P. E. Driller NY SDEC

- Weather Conditions

NYSDEC - DRILLER

- DRILLER

# of Tyrek Booda . . .

# of DIsposabie Cloves

Meter Used # Today

HXu Meter 9 0 1 3 9 4 1 Exploslmeter C 2 5 3 7 1 blonitox (HCh7035863 1 Mini-Rad 20655 1 pH ,Meter 1 Nephlometer 1 Cnmera 3 0 3 0 2 1 7 4 . 0

Callb. Date

Wnter Lever Indicator @\r14-v'm L I IVA NA TLD Badge SC-Q5G44MW A A

NH-6950 0003 & A

If ;Meter rradlngs exceeded background, see reverse slde for Comments.

Readlngs Above Backgroando

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Drill Rig Type

Water Tanker

Steam Jenny

Bulldozer

.Air Compressor

Other

DESCRIPTION OF W O R K COMPLETED

Detergent W x h

Potable Hz0

Methanol

Distilled Water

Plastic Cover

Other

-

SPECIAL COhIhlENTS

Approvals Om P. Popll, P.E. Drlller KYSDEC

Page 2 of 2

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I) \ b A! t/F L\ 1>11/(\ ~ i - AX@+ - DRILLER Level of Protrcrloo

-1 of T - w e b

# of Tyvek Bootfa

;Y of Disposable Cloves

Meter Used # Today

Caiib. Date


HZu Meter 901394

Exploslmerer C2537 \/ hlonitox (HChi031863

Nephlometer d Camera 30302174 4 Water Lever lndlcator ~q'75.4 \'aa-?t

A/

TLD Badge

IT ~ i e t e r rerdlngs exceeded background, see reverse slde for Comments.

bi Page 1 or 2

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Drill Rig Type

Water Tanker f Steam Jenny A Bulldozer Jl .

Air Compressor ~d Other

Deter~ent Wash

Potable H20

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DESCRIPTION OF WORK COMPLETED I

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FC Page 2 or 2

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YYSDEC PHASE 11 I Y V E S T T ~ 4 ~ 1 0 " ~ ~ 6

Work S t a r t t L * ~ W L I ~ L unch / Z m -/& Finish 3-35 - Weather Conditiong OC:=&~

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Perso- - DRILLER Levei of Protection 'u b

if of Tyveks

d o f Disposable Cloves

. .

Meter Used # Today

Caiib. Date

HXu Meter 901394 -Tt Erploslmeter C2537 \;I 1 \ 9 \,'io

hionitox (HChi0361163 1141qc Mlnl-Rad 20655 y \\Sl,qc

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Readings Above Background8

-

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DriIt Rig Type

Water Tanker L Steam Jenny 2

d . - Bultdozer

Air Com pressor d Other . .. , . ,,,. . .- .

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Potable HZ0

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SPECIAL COMhIENTS .PFPLK. q R S 2"- (0" # & 77YE2.2 2'' f L*IW< tc?? ;d LcrT. &or/ C7' &c) -3

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ON P. P O P L I . P .E,

1,Y SITE REPORT

- [ I ~ O I C I O Y Y S D E C ID$ 2,&? OZ ( s i t e Name W T , ~ &D, k l ~ ~ ' ~ %'rC Site N o , Y A / $ ~ L ~ ( ~ )

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Pergo- QM P. POPLI. P.F, DRILLER Level of Prorcctfon ?> b

8 of Dtsposable Cloves

hw . . . .

Meter Used # Today

Cailb. Date

Readings Above Backgroundo

I HSu Meter 901594 A Exploslmeter C2537 d bIonitox (HChi035863 A/

Mlni-Rad 20655 A/ pH Meter r/ Nephlometer

Camera Y

30302174

Wnter Lever Indicator

a r 5 4 f o m t TLD Badge S-

XH-6950 0003

If hitter rendlngs exceeded background, see reverse slde for Comments.

W Page 1 of 2

recycled paper

Dril l Rig Type .I/ Water Tanker

Steam Jenny A/

Bulldozer 6 Air Compressor

Other i - .

Detergent Wash

Potable H20

Methanol

Distilled Water

Plastic Cover

Other


SPECIAL COhIMENTS

Approvnls Om P. Popli, P.E. Drlller S Y S D E C

recycled paper

QA1T.Y SITE REPORT

7 3 L L a:', Work Surf L u n c h F i o i s b (-,--.- A!/ L

Weather Conditlong

NYSDEC - DRILLER

Level of Protectlorn

# of Disposable Cloves

. ..

Meter Used # Today

H S u Meter 901394 1

Caiib. Date

Water Lever Indicator

TLD Badge SC4954 0004 1 WA y A

I If bitter rendlags exceeded bqckground, see reverse slde for Comments.

Readings Above Backgroundg

Y Page 1 of 2

recycled paper

On

Drill Rig Type I

Water Tanker

Steam Jenny

Bulldozer

Air Compressor.

Other

Detergent Wash

Potable H2U

Methanol

Distilled Water i

PIastic Cover I

I

Other I I

SPECIAL COMhIENTS

A p p r o r a l s Dr i l l er SYSDEC

Page L of 2

1-56

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OM P, POPLI . P,E,

YYSDEC PII.ASE IT. PJt"ESTTGATTO?S

DAAJ1.Y SITE RFpoRT

- -~ - 1- "2& w o r k tau . /w,>~~~- Luncb 12:~ -ti-,- F i n i s h G-t-

. - -- Weather Condition$ - DRILLER

Level of Protection

# o f Tyvelu

# of Tyvek Bootles


DRILLER

1 ! Environmental Eaui~rnent On Site;

Meter Used ,

# Today Caiib.

Date Readings Above

B? Bac~grouudw

I I I Exploslmeter C2537

I I ;Yep hlometer 1 A I 4 7 .',

I

30302174 Camera F' A 1

A Water Lever lndlcator 1 YA A Y A

TLD Badge SC-6954 0004 I NA YA y..d I

K11-6950 0003 1 NA I*IA yh

I f & h e r readings see reverse side lor Comments.

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I I

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Om P. Popll, P.E. Driller SYSDEC

h u Page 2 of 2

recycled paper

OM P, POPLI. P.E,

PYSDEC PHASE I1 INVESTTGATTONS

Work Star$ L u n c b F i n i s b ~ - Weather Condition3

NYSDEC DRILLER

- DRILLER Level of Protection

# of Tyvek Bootles


Meter Used # Today

Callb. Date

HNu Meter 9 0 1 3 9 4 5 wys Explosimeter C2537 0

Monitox (HCN)035863 0 Mlnl-Rad 20655 0 pH Meter 2. -&{5

Nephlometer 2, v:{:! I

Camera 30302174 0 N

Wnter Lever Indicator.

TLD Badge SC-6954 0004 5 a'[% NH-6950 0003 5 y3

If k e t e r readlngs exceeded background, see reverse side for Comments.


h Page 1 of 2

recycled paper

DEC P W E I1 INVESTIGATION$

ITE REPORT

z/b(cio . Date T(,f%~r,\/ N Y S D E ~ ID# , 8280z1 Site Name G D L ~ ~

a d ~ r , Site NO. I ,&WU (it&@ -

Work Start 8 . c ~ ~ ~ Lunch / z w - /a+~tL . Finish 5 WSlr- =IL 01

Weather Conditions - A u ~ l - ~ v , 5 C

On s& NYSDEC - I)RILLER

b 6 b& &I. h(&?G?lTr ? \IAAWCL - _i

DRILLER Level of Protection

# of Tyveks

# of Tyvek Bootles

& # of Dkposable Gloves

Meter Used # Today

Callb. Date

Readlngs Above B y IJackgroundg

HNu Meter 901394 f elb(q0 h; NOUL r ..

Exploslmeter C2537 , . ,d Monltox (HCN)035863 A/

MIDI-Rad 20655

pH Meter NA Nephlometer . . a NA Camera ' 30302174 d A NA NA

Water Lever Indicator A A A

NA NA

NA NA NA

k If Meter readlngs exceeded background, see reverse slde for Comments.

Page 1 of 2 1-60

recycled paper

On Site;

"CI Drill Rig Type I Water Tanker 1 Steam Jenny

BuIldozer

Air Compressor

Other

Detergent Wash f

Potable HZ0

Methanol 4

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Plastic Cover

Other

DESCRIPTION O F WORK COMPLETED

SPECIAL COMMENTS

3 ~ l u k ~ (h& cc i Approvals P. Popli, P.E. Drlller NYSDEC

Page 2 of 2

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,VYSDEC PHASE IT INvESTTG~4TTO%5

D,,, ic\~i)*!em!-q 2 /7 /90 . WYSDEC ID$ Bz%c~z( \

Site Name b'-&d 6 ~ . 31%- Qm s i t e N o ~ ~ ~ ~ ~ c ? ( / & Z )

Work Stars 8*hnc / Z > ~ J - 10" 3 Z r 2 , - Lunc-Fiaisb

Weather Condi t ioa~ o ~ > ~ ~ * ~ 44"~ u f - DRILLER

X of Dbposable Gloves w Meter Used '

# Today Calib.

Date Readings Above

Backgroundg

HSU Meter 9 0 1 3 9 4 f Explosimeter C2537 d hfooitox (IIChiO35863 A/

Mini-Rad 20655 d pH Meter

;Yephlometer

Camera 30302174 d Water Lever Indicator as(sso\ TLD Badge v %zmr3--

If hitter readlngs exceeded background, see reverse side tor Cornmenu.

Page 1 of 2

recycled paper

b Drill Rig Type 1 Water Tanker I Steam Jenny I Air Compressor

I

Detergent Wash f Potable Hz0

Methanol

Distilled Water

Plastic Cover

Other s= I Other


-. -

SPECIAL COhIhlENTS

Approvals Dri l ler KYSDEC .

W Page t of t

recycled paper

- ~*VPew-\l Z ) Y ) ( I ~ L N Y S D m I D 8Zt"Ll

\

Site Name 6 5 i t e &m*1 L> >~"~L'.:c * K& N ~ , Y L I ~ ( ~ Z O Z \ I

Work Starj 8 2 A , ~ ~ ~ Lunch lZ9 - I " Finish 4%:~. Weather Conditions 2t'ddv. ? Gay

Oa I I

NYSDEC DRILLER 406 bdcz 4. h\mC I F

Safen E- - QfUIJdB

Level of Protection

# of Tyvelu


..

Environmental Eauiornmt On Site; w

Meter Used # Today

m u Meter 901394

Exploslmeter C2537 id

AIonitox (HCN)035863 h I

Mlnl-Rad 20655 A1

p~ Meter A Nephiometer A Camera 30302174 hl

Calib. Date

Water Lever Iodlcator ' A A

F A F'A

A Nh

If ~ l g t e r readlngs exceeded background, see reverse slde for Comments.

W Page ' . 1 of 2

Readlngs Above Background*

recycled paper

Drill Rig Type

Water Tanker

Steam Jenny

Bulldozer

Air Compressor

Other -

f Detergent Wash

Potable H20

Methanol

Distilled Water

Plastic Cover

Other


Driller

w Page 2 of 2

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Date ~YWK~ z /Q (40 NYSDEC IDA

sire inme ~ L C . € ~ L i~t.~&+.J- SKI?, site NO, YA/&H&Z )

Work Sbrj q'+5br~~ Lunc4 Fin isb ,'cc'-, - b77s:8L - -

Weather Condition3 ma . 1 Oa Sitr;

NYSDE(I - DRILLER

? \'M W-E ( / --

/ I

-- DRILLER eve^ of ~ r o t e c t ~ o n b I


Meter Used # Today

Calib. Date

Readings Above BY Background*

WSU Meter 901394 )1 Z/ 9 ('10 ,\ /,:,@-

Exploslmeter C2537 A I

h.1 onitox (HC21)035863 A Minl-Rad 20655 4 pH Meter A/ 1

r/ Camera 30302174 N A NA

Water Lever Indicator d NA A Nh 6 9 9 \'-I . I TLD Badg- A A A

A EIA

If hiuer readings exceeded background, see reverse slde lor Comments.

recycled paper

Drill Riq Tvpe I I'

Water Tanker I I

Steam Jenny A Bulldozer I Air Compressor A Other

/ Deteryent Wash

I .

Potable H2O

Methanol

Distilled Water

Plastic Cover

Other


SPECIAL COMhlENTS -/I? 7tW 31,- -23 w- &r~~od.lhL ~ , I L ~ A F % ~ PF t)( F T F b ? \ I 4 & TJ E ~ l u ~ d AT /m / ~ n ~ d t&

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Approvals Om P. Popll, P.E. Drlller N Y S D E C

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YYSDEC PHASE IT IYVESTIC 4TTOUs

Si te Namr h d PD Lv_J~)~-L&~F s i t e N ~ , ~ & & ~ ( A F ~ Z ) I

Work Star; L u n c h F i n i s b

n * \ : - DRILLER

6 M € w \ ~ \ YI

Ad. M5 .la - D R I L L E R ~ c v e ~ of Protectfon b

-5

# of Tyveks -

# of T n e k Booties

d of Disposable Gloves &>L

Environmental On Site;

Meter Used Calib. Readlnps Above # Toda y Date Y Background.

HSU Meter 901394 Z/ ldQ0 >' ,I &/V&

Exploslmeter C2537 A hlonitox (HCw035863 ‘ hl Mial-Rad 20655 A pH Mcter - A(

* NA

Nephlorneter A! I NA

Camera 30302174 * d A

Wnter Lever Indicator A/

bTAf-( ,, TLD Badge SC635411W

~ q c . \ ( c e - * M95tH3003

If hlcter rendlags exceeded background, see reverse side lor Comments.

recycled paper

gllY' Drill Rig Type + Water Tanker I Steam Jenny

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Air Compressor 1 Other

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Potable H20 P Methanol k' Distilled Water 'y Plastic Cover

Other


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SPECIAL COXIhlENTS 50 -11 lu7+ &vi, V U I F&=L Z / / S / ~ O

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'&/I&\ mdi i A p p r o ~ n l s 3 P. Popll, P.E. Drlller N Y S D E C

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OM P, POPLZ. P,E,

NYSDEC PHASE I1 INVESTI('.ATIONS

\ Q Si te Name &a "l ?ID .?J~KUL A*, Sife NO. y,\ / I/&)- (' J@- )

/ z m - / p (2' 2 . W o r k Start / 0 3°,:tt L Lunch Finish +?,I-

I

Weather Cond i t ions ,

NYSDEC - D R I L m 7 ~ , ,LA~/ t ?E (

Level of Protectlon

# of Tyveks

# of Tyvek Booties

# of Disposable Gloves I i

I

Meter Used # Today

Callb. Date

Rendlngs Above BY Background*

I I HNu Meter 901394

Exploslmeter C2537 t ! I !

Monltox (HCN)035863 1 ! I 7

L Mlnl-Rad 20655

I I 1 pH Meter A I Nephlometer 1 A

Camera 30302174 ' A A A

Water Lever Indicator

I TLD Badge SC-6954 0004 1 & A A

I If Meter readlngs exceeded background, see reverse side for Comments.

Page 1 of 2

recycled paper

t On Site;

Drill Rig Type

Water Tanker

Steam Jenny

Bulldozer

Air Compressor

Other

Detergent Wash

Potable H20

Methanol

Distilled Water

Plastic Cover

Other


SPECIAL COMMENTS

Approvals -?I/)(( ~ I ( C / J ? ( P. Popll, P.E.

Page 2 of 2

recycled paper

OM P. POPLI. P,E,

I1 INVESTI(:ATIONS - opte ~~-~;+r.,?:.,l Z/ LTJ JQc NYSDEC ID# , 2 zs2 czr

\ - \ C Site Name E,:,(L~~A[ ry>. .. 12; --?L - nc Site No. )'i/ & ,- (ei ' )

1 c 50 3 - / Finish - Work Start - - Lunch

Weather Conditions ,

el On Sit%

NYSDEC - DRILLER I

.- 3 \ ,ilA!WE ( \

I [ I

I Safetv Ea- - -

I Q d U R

Level of Protection I

# of Tyveks

# of Tyvek Booties

# of Disposable Gloves

Meter Used # Today

Calib. Date

Readlngs Above BY Background*

HNu Meter 901394 1 I Explosimeter C2537 1' 1

Monitox (HCNl035863

Mlni-Rad 20655 1 pH Meter 1 ;rlA Nephiometer A

Camera 30302174 t NA

Water Lever I 1 Indlcator A A ' A A

TLD Badge SC-6954 0004 1 A A A

I If Meter readings exceeded background, see reverse side for Comments.

Page 1 or 2

recycled paper

On Sitm;

Drill Rig Type / Water ~ a n k e r

Steam Jenny

Bulldozer

Air Compressor

Other

Detergent Wash

Potable I120 i

Methanol I Distilled Water

plastic' Cover

Other I I


SPECIAL COMMENTS

Approvals >mu(d~v.CO(i i P. Popll, P.E. Driller N Y S D E C

Page 2 of 2

recycled paper

OM P. POPLI. P.E,

DEC PHASE I1 INVESTIGATIONS - 7-

ate ~plr~~( ~ 1 1 ~ . 140 N Y S D E ~ ID# - $ ~ % ~ z ( .

n Site Name &xh( ? h > . t l ? i - f i ? ~ ~ , i r r s i t e NO. )'A/ q L a {&LC \:)

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Work Start Lunch d - Finish #a':, 1- W e a t h e r C o n d i t i o n s ,

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NYSDEC - DRILLER I

i

el Safe tv Ea- Q M P. POPLI. P . L J l I u h F 5

Level of Protectton 1 # of Tyveks f # of Tpvek Bootles

# of Disposable Gloves I

hvironme-t On Site;

Meter #

HNu Meter 901394

Exploslmeter C2537

Monltox (HCN)035863

Mlnl-Rad 20655

pH Meter

Nephlometer

Cnmera 30302174

Used Today

I I !

Cnllb. Date

I \ Water Lever Indicator & A

TLD Badge SC-6954 0004 1 A N1\

NH-6950 0003 ! A A I

If Meter readings exceeded background, see reverse slde for Comments.

' Rendlngs Above Background*

Page 1 of 2

recycled paper

On

k Drill Rig Type I

Water Tanker I

Steam Jenny A Bulldozer

Air Compressor

Other

Detergent Wash

Potable H20 I

Methanol 1 ~ i s t i l l ed ' Water 7 Plastic Cover

Other IL 1


SPECIAL COMMENTS

Approvals / P. Popll, P.E. Drlller N Y S D E C

Page 2 of 2

1-75

recycled paper

OM P. POPLI, P. E.

E N V I R O N M E N T A L FIELD S A M P L I N G FORM

C* site Location k 517.' ~ j ~ , ~ ~ ~ ~ b ~ ~

Weather 0 5 , 5 f & f , ' / /

Equipment Used: Auger . L ] Trowel [ ] S.S. Spmns [d Trier [ ] S.S. Bowl [d

Number of Samples Taken /d Sample Designations 5 1 - 5 / / f s f ~ p m j / m s i h p t h of Samples O -/d "

Comments Other I 1 # of Photos Taken 0 D/5CaPA77od 6 SOIL ~ 4 5 No,-) h'f 5,9,56 #' S, ~3 : J ~ / 4 / 4 7 PETRLYLL//~~ 0 D 0 k @ SZ. ,

4' 2.) Sediment Sampling Yes [ ] No [ . . .

Equipment Used: Other [ ] Nurn ber of Samples Taken

I 1 Sample Designations Bottle [ ] Depth of Samples

Comments # of Photos Taken

3) Surface Water Sampling Yes [ ] No [ d' Equipment Used: Dip Bo tUe [ ] Number of Samples Taken

I..adle I 1 Other [ ] Sample Designations

Thief [ ] Depth of Samples


LI Page 1 of 2

recycled paper

4.) Leachate Sampling yes [ d N o [ 1

Equipmen1 Used: Boffle 1 Number of Samples Taken I Ladle [Vf S.S. Bowl [d Sample Designations L \ Thief [ 1 Funnel [ 1 ' Depth of Samples 5 L, E F M

L, 4

Comments Other [ ] # of Photos Taken @@DL g.L! I? - L J KC 3 - c ON SJpdS~ U F

LL-Y&IC//~~-~P ,' .L/ddji/M- &&%% 4 &~~3?% ' ,

Equipment Used: Auger 1 1 Number of Samples Taken 25 Trowel [ ] S.S. Spoons [d Sample Designations W I $ W Z Trier [ ] Other [ 1 Depth of Samples 0-/J" Commenls #of Photos Taken

Page 2of2

recycled paper

OM P. POPLI, P. E.

c.cc,lc~c! I I I I~ r ~ ~ v i r ~ ~ r ~ r n c ~ ~ ~

OM P. POPLI, P. E.

ENVIRONMENTAL FIELD SAMPLING FORM

L - site k c i o n &ij~,J ')Il.- bi%30.% ge. Site Number $ ~ W W (A-)

~ e a t h e r g ~ a y , L h k ~ Date Z / G / ~ O d

/ 1.) Surfical Soil Sampling Yes [ ] No [ ]

Equipment Used: Auger -1- ] Number of Samples Taken

Trowel [ 1 S.S. Spoons [ ] Sample Designations

Trier [ 1 S.S.Bowl [ ] Depth of Samples

Comments other , [ 1 f of Photos Taken

.. . - ., . . - . .

-. . . ~

/ 2 ' Sediment Sampling Yes [ ] No [ ]

Equipment Used: Other [h%~l@> 9mC Number of Samples Taken 3 Ladle I 1 *A Sample Designations dd - 12. , sli' - I )+ , I %I?- 15 Bottle [ ] Depth of Samples 0 -/k" Cornments f of Photos Taken LA^. Uo 4U(m-~m LX - 'CIL ~ - . ' J L L + C E ~ ( I ~e Z P f 41 c,c/ ,L-.,='<L'/;?'? i,r--& 77M-7- k K E w c : u D T H 5 w W I ~ - W C 9!e TS b1-2~ - A m ~lc15 E !

J 3.) Surface Water Sampling Yes [ ] No [ ]

Equipment Used: Dip Bottle [ ff 2

Number of Samples Taken 4

Ladle [ 1 Other [ ] Sample DesignationsAC-lL , ~ r t > - / + , 3i. - I5 Thief [ ] Depth of Samples 3 ~ ~ 9 f l E

Comments f of Photos Taken AoA-05 bEC, S~fE?5Z?b TO b t * G w U G C bX&Ti :A 3lC- /3 ~ E P * ,\/,J $c a?$,*-

C L L T L &&T+t!l wc4T1ad $ &E%~'T- f l 2 i K L ~ a E t E i +&C. f _ v rd ~ # 3 /c_~=-f-

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x Page 1 of 2

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4.) Leach.de Sampling Yes [ I No[ 4" 1

Equipment Used: BotUe [ 1 Number of Samples Tahen - Ladle [ 1 S.S. Bowl [ ] Sample Designations

Thief [ 1 Funnel [ ] Depth ol Samples

Comments Other [ ] X ol Pholos Taken

--- /' 5.) Wasle Pile Sampling Yes [ ] No [ ]

Equipment Used: Auger [ I Number 6f Samples Taken

Trowel [ ] S.S. Spoons [ 1 Sample Designations Trier [ ] Other 1 1 Depth of Samples Comments # of Photos Taken

1 Signature of Sampler >t A t c l ~ \ ~ t u c ~ l l k i

Page 2 of 2 .OM P. POPLI, P. E.


OM P. POPLI, P. E.


hw \ L & CT

site tion on P ~ k i b ~~ZCPA-L -. r' c Site Number ,kp/*ZO (;GO2 )

Weather ~ C A U ~ , wF Date ~ 1 % / 96 L

J 1.) Surfical Soil Samplirq Yes [ ] No [ ]

Equipment Used: Auger [--I Number of Samples Taken

Trowel [ ] S.S. Spoons [ 1 Sample Designations

Trier [ ] S.S. Bowl [ ] Depth of Samples

Comments . Other [ 1 # of Photos Taken

2 ) Sediment Sampling Yes [ / ] No [ ]

Equipment Used: Other [ 4 4 1 N ~ l C t ~ t "X<L Number of Samples Taken 7 Ladle [ I Sample hignations 211. -( ,sc~\-Z , 5 ~ - 3 , , ~ L C Y ~ , ~ L L - ~

Bottle [ 1 Depth of Samples 2u.J -'I $ %- w 0 -/Z" Comments f of Photos Taken iVdA l5

4' 3.) Surface Water Sampling Yes [ ] No [ ]

Equipment Used: Dip Bottle [ / ] Number of Samples Taken 7 I 1 Other [ I ~ a m ~ l e h i ~ n a t i o n s ~ c ? - / , ~ - t , % I \ - s , ~ L ~ - ~ , % L . - &

Thief [ ] DepthofSamplr 9 W - Y ~ u R F ~

Comments /of Photos Taken &ode 2 ~ - 8 \4 U C L Z E ~ t~ CFAKCL &.ui;l C ~ W ! a n e w ' ; u e % ~ c m <

I

recycled paper ecology and en-ironrnenc

Leachate Sampling Yes [ J 1 No I 1

Equipment Used: Bottle [ ] Number of Samples Taken 1 Ladle [ ] S.S. Bowl [ ] Sample Designations L - l

Thief [ ] [k Depth of Samples 0 -/Z" Comments Other [ 3l7U.J IT-L --EL # of Photos Taken A / C J ~ ~

fp" u tAw%iZ PEG73 To 'k IAI Wd,, ~ - A € & f r ( € d T - 9 h r t , q ~ ~ &

Waste Pile Sampling Yes [ ] NO [ d Equipment Used: Auger [ I Number of Samples Taken

Tmwel [ ] S.S. Spoons [ I Sample Designations Trier [ ] Other I 1 Depth of Samples

Comments t of Photos Taken

f Signature of Sampler &/,c( (&Jn/)ll/qC

Page 2 of 2

recycled paper

OM P. POPLI, P. E.

ecology and envimnrnen~


w Site Location Wb 2 KC Site Number )'>A:!>' ( ,L~uL' )

weather h d , *aOf Dare z / Q / @ *

J 4

1.) Surfical Soil Sampling Y e [ ] No [ ]

Equipment Used: Auger I- 1 Number of Samples Taken

Trowel [ ] S.S. Spoons [ ] Sample Designations

Trier [ ] S.S. Bowl [ ] Depth of Samples

Comments Other [ I # of Photos Taken

Sediment Sampling Yes [

Equipment Used. Other [ / ] 5 ~ ~ 2 b ,WC Number of Samples Taken 12 3ixdhl. ,"0>-5 "LC-(< 2tc - ,>LC,- , ~ u \ - ,Z?L\ Latile I I Smp~e~erignationwo;t&;~i -4 z,,.-$a,r:!u,d:u>:

Bottle [ ] Depth of Samples o -lZ1' Comments # of Photos Taken ,VO&€

J 3.) - Surface W a t e r Sampling Yes [ ] No [ ]

Equipment Used: Dip Bottle [ / ] Number of Samples Taken / Z / t 3N-5,,9ctl-i- JIL\-7 . ? r ~ ~ - l l , > c c ~ - 1 ~ , ~ ~ ~ ~ ~ 7

Ladle I 1 Other [ ] Sample Designations~ro-it ,3t~1-17'.:~1:-~!0, - tl , ,LO- Z L , ~

Thief [ ] Depth of Samples ScFyA&

Comments # of Photos Taken MoAIE 3- -ld TW 3~0 -23 liFK ACUTl0hld% 2XIf-w ?&SL'F>~C &y f. f ez U ~ A F - ~ ?c/P, 1 3 ~ ~ q c l ~ 5 ( I D I ~ P ~ . -hi j $ I'o.L'!L~)

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'T Page 1 012


OM P. POPLI, P. E.


\

si te ~oca l i on &ell J;)IW,L Sm site Number },I/'&' ( ~ C Z , } -

Weather %//OW. 33'3 4

1.) Surfid Soil Sampling Yes [ ] No [

Equipment Used. Auger [--I Number of Samples Taken


Trier [ 1 S.S. Bowl [ ] Depth of Samples

Comments Other [ ] f of Pholos Taken

/ 2.) Sdiment Sampling Yes [ ] No [, ]

Equipment Used: 3 d r r J W ahcL Number of Samples Taken 1 k l l e [ 1 A?A Sample Designations 73r~ - l I Bottle [ ] Depth of Samples o - /z" Comments f of Photos Taken ,Clc'/ClF

J ' 3.) Surface Water Sampling Yes [ ] No [ ]

Equipment Used: Dip Bottle [ 4 Number of Samples Taken I Ladle [ I Other [ 1 Sample Designations 910 -1 I

Thief [ ] ~ e p t h of Samples a L'VUJ~ Comments f of Photos Taken A ~ A / &

~nwpm %-(( &wa& OAE cy -me C ~ A R Z J ~ O ~ e07- W I ~ * I F ~ O O C z/Lf/qo [ti4.!3 NOT A8cE TO &&?&!~lcj& /A/ ~ ~ 0 h J t ~ i ~ l o d

Page 1 of 2

Y

recycled paper ecology and envvonment

4.) Leachate Sampling Yes [ I N o [ / ]

EquipmentUsed: Bottle [ I Number of Samples Taken Ladle [ ] S.S. Bowl [ ] Sample Designations Thief [ ] Funnel [ J Depth of Samples Comments Other [ ] # of Photos Taken

5.) Waste Pile Sampling Yes [ ] No [ /]

Equipment Used: Auger [ 1 Number of Samples Taken Trowel [ ] S.S. Spoons [ ] Sample Designations Trier [ ] Other I I Depth of Samples


Signature of Sampler ,& t d K I.,~u L

OM P. POPLI, P. E.

ecology and environment recycled paper

4.) Leachate Sampling Yes [ I N o [ / 1

Equipment Used: Bottle [ ] Ladle [ ] S.S. Bowl [ ]

Number of Samples Taken

Sample Designations

Thief [ ] Comments

Funnel [ ] Depth of Samples Other [ ] I of Photos Taken

/ Waste Pile Sampling Yes [ ] No [ ]

I

Equipment Used: Auger [ 1 ~ u m & r of ~ a r n ~ l e s Taken


Trier [ ] Other [ 1 Depth of Samples

Comments f of Photos Taken

Signature of Sampler >~ItC(o,b/dfl( C.

Page2of2

recycled paper

OM P. POPLI, P. E.


OM P. POPLI, P. E. GROUNDWATER MONITORING FIELD FORM

w f l e Location: 63~b~1.1 &a bikm9- %E. S11c Number- {~'@ZO G ~ z ) lVcrarher. 0- \ wf Dare: 1/7/90

L

P ~ r g e Method: . . . . Baler: [d PVC [ d i e f l o n [ 1 St. Steel I I Other - 1 .

!:- Pump: [ 1 Paristaltic [ 1 Submerpble [ J Other ;. ;..- ' . . . , . . .. - - . . - . . "oIume CaJcll.tion - , . . . . . . . . . . ,.- ' " . -l, ' . -Groundwater Elevation Calculation- . - '.

' , , L C . . . . . .

1 t . 5 We!l Elevation (ft) MSL -L Hell Depth (It) .,. - 'is.

' i . 3 .2 b h c r ~ _ ,. Static Water Level (It) S tar~c Water Level (ft) r, I

Deprh of Warer Column (ft) 3.3 Groundwater Elev. MSL It

S. ~ ~ ' P _ I I Constant (gal/ft) X = 0. I (c

.. Voiuln.: 5rmding in Well 1.3 - .

\'el! Constants (X) . . -

.. - . . .

; 0. lo gal,'!( = i" OD well: .0.65 gal/ft = 4" 0 0 w d . C a l c ro Dererrnine Constanr:] - . . . . . . . . . . .

[ io?.sr.;lr 1 a0.7654 x (casingdiameter in inches) * x 12 1 - . . - . -- - . . - .

231 . . . . . . . . . . . . . . . . . . .. . . . . - -

Time:

Tirra~ volume Purged: .c" gallons

r c ~ f \ olume Casings purged: 3

Purging Obscnarion\hleasurernents

/ / S J I I ~ U ~ I ~ C rn!orrnarlon: Sample Method: Bailer [ J PVC [ ] Teflon [ ] St. Steel [ ] Other

Pump: [ I Parisraltic [ ] Submergible [ ] Other

0% Time: W c

Number of BottlesTaken: Field Preservation (I or N); &I&&I { C Y N ~ ~ Field ~ i l t e r e d a r N). DatefTime Z 1 1 9 0 Filtering Method ~ - L G D ~ & b1'~9&& SUER o.% wmd


Field Measurements: . . A - . . . - . . . ,

HeterNumber , Parameter Unit Replicate 1 Replicate 2 Replicate 3 Replicate 4

gtrr/ PH S.U.

Spec. Cond. umhos/cm 2- 24,m Z O zzLo Temp. OC . 8 . 3 c a . 1 .[ # A .9 B.9

Turbidity N l U q f - % w - ? ? OP-%L&, ! . .

. " . METER CALIBRATIONS , , . . . . . . . . .,-; . ........ . :r-, . , . . . . .

, ( ,....,... J...'i.,i .4'-.-.:..- .L--.-,i .&*'L. -.. - . . . ' I . . .... . - . . . . . ... . . . . . . . . . . .<,;, . . . . . . . . . " ,:. ,. . -, ''L - ; . .

' 1 " ' . ( . , I . . . . . . . pH: Buffer 7.00 - . . .... . z . : . Field Meter Calibrations Date/Tiie . ... . . . . . . . . . Buffer 4.00 - ,, - .:-

. . ~ u f f e r 10.0 - ' " 10.0 =Vrea?i.ii," .... ,,: ;, . . . . . . . . . . . . . . . . .... .

Buffer 7.00 - .3' ' " ' :7;0- , . -._ .-i

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.j' . . . ;;)" ..:.;< 'T .,&' . . . . : . . . . . . ' . . . . . ; . , - .---. . . . - . . - -. -

. . Field Observations: ' . . . -

Crew Members: 4. M ~ R H ( ~ ~ M W L

. .

NYSDEC ,&d&hdq~ Om P. Popli. P. E. Signature

* Page 2 of 2

recycled paper ecology and envjmnmen~

O M P. POPLI, P. E. GROUNDWATER MONITORING FIELD FORM , , . . . . . . . . . . . . !

- r e : O U C F : ~ ~ \ Dare: z/ 7/90

Pxge Method: Bailer: [l/fPYC h f e f l o n , [ 1 St. Steel 1 ] Other I I

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. I ,

Pump: L 1 Pyisraltic ' C 1. Submergible [. . I . Other . <,. .;.. ' . . , ; _ . .

. . . .: * ; ; . . . ,-;:t. ;:.,I. ... - , . : ' : - . . . . . . . . . . . '. . ' . , ' . . , . - ,. I. . ,.I i ' , 1

. . . ... , . . . . . -GroYnduater Etevation Calculation- !::!:<; - 14.: .. , .. , . : . . x . . . . . . . . . . : . l&;:'..,;'.,,r I . . . . . . . . . a , . . . . , . . " ". , . -, -, ,!- .+ ,:, : 617.3 -.> *:.rb .. ... . . . . . . . . ,l . . 2 : : ' .: . . . - ....... . . . .., . ,, *.?'Ii ; 7- "*. . ". . . . . . . . .

. . ': WeU Elmaion (f;) &' - .-.-....-... : \Vc!l Deprk (f:) . . . . . . . . . . . . . . .

b ,;:;. .- .- '. ."...... - . . . , . : - I* ;; ...... & -.,--.- --, >,+ . . d . , . ? ' . , '

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'

" . C; . . . . . . . . . . . . . . . . . . ' "' . . . r :. ' , .

: + . , - . Depth of Water Column (It) oundwacer Uev. MSL , . .

f t ,

. 107:. . . . . . . . . . . . . . . . Vaiurnc 4 t a d i n q in Well g d o n s I, ,._. _ .__.-. _ ___._ .__ ._.. ..._ .- _ _ _ _ _ -, _.._ - __._,. - _ &_. - - - --.- . . . ...... ... .. . .. . ... . . . _ . . - . .

- ,.- . .

3. t o gal, ft = i* OD well: .0.65 gal/ft - 4" OD well. Calc. to De:errnine Constant:] . - . - Cansrx11 X '0.7654 x (casing diameter in inches) x 12 1 . . . . . . . . . . . . . - - - - . - -. - .-

23 1 _. ___,_____, -- _--- _ - ..-- - - . . . . , _ A . . _ .. . . . . . .. . . . . . . . . . . .

?-:rze Time: 5 ~ ~ 4 . '

Total Volur;.e P-~rged: !5+ gallons -.-

r c.T Vurur;ll Cdslngs purged: 3

Sarn~dicn ~l !orrnat~on: SampleMethod: Bailer: [ 1 PVC [ 4 Teflon [ ] St.Steel [ 1 Other

Pump: [ ] Paristaitic [ 1 Submergible [ ] Other

4 Number of Bottles Taken: Field Preservation (Y or N):

Fle!d ~iltered@r N). Datflime t 1 7 1 90 Filtering Method d ~ ~ l ~ ~ ' ~ O - ~ N ~ W A

,,,:1,i1! Appearance: nuJmy

recycled paper ecology a n d environment

. . . . . . . . Field Measurements: . . . . . - . . . - . . . . . . . _ . . ,.

. .

Meter Number Parameter . ; . . Unit Replicate 1 Replicate 2 Replicate 3 Replicate 4 * i PH S.U. 8.4 7.3 7.8 7.8

Spec. Cond. umhos/cm 3- 3- 2900 Z(jz0 ~ e m p . OC . b.\ b17 . 65 6.7

Turbidity NTU OffL%UE off-% C F F - W . . O~F- . ? 0--.. .. ,

. . , . .

. . . . ,.. . . METER CALIBRATIONS . ' i ' i : - . . ' - , . - - . . . , . . . . ' I . I . :i,..7i..-;,.; ,&.- y , . . . . ... .-. . - , %;:& . - . ,, ,; ., -:,:; ,.! ;s" ; , ! , < I :;:. . . . . . . . . . . " . . .... ;r=,-z;i;,~--;..-..:# .,--. . . . ' . - - 4 ..- ::,> ..-. r'*- "' . . ' . : . ' . . . . . . . . ., ,:;.. , . . . :!: ,, .ly.:*:>) ,. ;;;:; *,~!$ y .; ..: ,,;<- ;, . , .7,:.,. ~ , - . <-;?< , ,. . .< . . . . ..,: , ; .j*.. ik.' . . . . . A ,... . 6 . , . , : ., ..: . , . . , * ' . .

pH: Buffer 7.00 --. ' 1.780 " set i.:,', - . . 1.. . i '4 .f, . . set/ read .. - - " .-.-

.: kield Me& hibratic& &>me E i 7 / 90 i. 1 . :- . ! ! .. ';., , . ; . . : : . , ' : L , i ,: , . - - ..-.. Bufier 4.00 - " . -- "- . . . . . . . . . - . ,.. , , ., . . . . . . : s ' , .: . . - , : . ( _ . . .. 7' ! .... , , . .

Buffer 10.0- " 10.0 Wread' ;. '. , , . . : 4 - :, .::, ,: ~ c . . . . . . . . . . . . , 9 ,- .;>&:. ,: ,, ,,4g ,;

. . . * . ; ;,.; ..... l..,rcr, .-. - i...., . - ... -. - . . . . 1.5

. . . Buffer 7.00 - . '*- ' ..7-.0- m d , . , . ..'. ., 'L," . . . . . . , . . , , . . . ' 7

! , , 9 . . . .: .: , \ . + . . . : . . > - , . , . , , , #a.;;'.3 . - . . ,, ;* : , ., ;: .,.. , ,. ..;, .. ,[;:;.!;,a,., ... . . .- ....-...-i--.. .. . . . - i : t . : ,. L.. , .?.!Y2. . 1 .

. . . . . . . . . . -.++ , - j h-. :.- ...- -. .-. ". .: "? :; ;>. : . -, ; , i . !.; . - - , . , . ' . . . . * . " . . . , ' . . . . . . . . ! . < ... ,i. ' . . . . . . . . . . . . . . . . , . . . :A, . . . , . , . . . . . . . . . . . . . . . . .,. : . . . . . . , . , . . . . _ . 9

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' . . . . . . . . ' . . . . . . . . . . . . . .~ . . . . . : 8 -

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*lo 'nnlmh~ e & d G ~ o d ~

- -

. . . . . - Crew Members: 5. W H ~ , :! J4drn.1

NYSDEC I Om P. Popli. P. E. Signature

Page 2 of 2

recycled paper ecology and environqent

OM P. POPLI, P. E. GROUNDWATER bIONITORING FIELD FORM

.. ..,, ; :.- *-I.+ -

b e ~ o c s i o n : b d h 8 ! 4 c Sltc Number.

iveather: %nc 3(.'d , f Dare: 2/71 10 L

PIJRCE INFORMATION .. ... ..-...... . _ . . . . . . . . . . , . - . . , . , . , , . ,

. :::, .'. ;, , 1,: ,. ,;-'

+~rqe Method: Bailer: [ Teflon [ 12. Steel [ ] Other I .:

. - .. ", ,:'.;. i . . . - . . . . ,- . , ' . . . . . . . * , ,'. , ' : . - . - -- .- . . . , '. .E : i

. . .I. I

.. . . . . . Pump: [ 1 Parisrallic [ 1 Submerpble C I other

"',. .? , ;.a , , - : - c - . . . . , . I . . ' . ..,.,.4. . , . y.... . . . . - Volume Ca,cu,ation ;. ,. ?,.:,3;'-=.'-'" i17 . s*.::: '! 3 ;

. . Croundwatrr Elevarion C~lculation- i c . ., . ' , . . . . . ,, I. , 18.2, . .

,:, 1, t i ...'; . . We11 Depth (11) Well Elevat~on (fr) MSL ..%.,c , . : ! s . a ,

ctatrc Warer Level (ft) . (~'5 &hut qfb

eprh of IVater Column (ft) 1 6.7

. . L .

Static Water Level (ft) . . - . , : L , .

., . . , . , ,.,,.,. . ( . . . . - . . . . I . . .... " . . ,, : 1 . . . . f t i 1: '. _ _ * roundw water Elev. MSL .-,. , '

* % ., . . . I ,, - , : f

. : . . . . .

X. \\.e:l Constant (gaUft) X = 0.

~o:um:: 'tanding rn Well 2.67 gdlons ' a$&- - . -

a!! :onsranrs (X) : . . .

- - - - . . 9 10 pau't - i' OD well: . 0.65 gaYft = 4' OD well. Calc. to Determine Constant:] - -. - -. - 2 - - - .. -. - .- .

: i o n s r x t 1 '0.7654 x (casinqdiameter in inches) x I2 1 . ........ . . . . . . . . .... . . . . . . . . . . . . . . . . . .- - --..-. - . .

231 ....... - - _._ . - _ _ ._._ ,_.- _. . . . . . . . . . . . . . . . . . . . . . . . . . .

. 4+ Total volume D~rqed: gallons . [mi- FiFltCFlhl% f &t?.Lv i I

r of Loi.~me Casings purged: 3

J J Samolirc Informarlon: SampleMethod: Bailer: [ 1 PVC [ ] Teflon [ ] St-Steel [ 1 Other

Pump: [ j Paristaltic [ ] Submergible [ j Other

z= Time:

Number o[ Boules Taken: Field Preservation (Y or N); / ~)'h!l@d

Fe!d Filtere& N). Dateflimc / 7 1% Filtering Method WE bl~:mfi~~ 0.a m ~ m d

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. : . ^ . . . < .. Field Measurements: . . . . ~. . . . . . . . a _. . - , - . ...,- ... -. - . ' : ~ ..,. . . . . . -. . -. . . . . .

, . . . - . . . . .

' 9 . . . : . leter Number Parameter .:: , Unit Replicate 1 : Replicate 2 Replicate 3 Replicate 4

pH S.U. 5.L 8.I 7, ') 7. % Spec. Cond. umhos~cm T i 3 3100 2 7 70 310(>

Temp. OC * B83 8 . 3 , 9.q %lf-

. . . . , . - . . , * ' . . . . - . . ' . . . .

. - -. .-.'-- ".. ' . . . ."- .--, i- . . - \ .

. . METER CALIBRAT IONS . , ; . . . . . . . , . . . . .r,:- -. - ---.. ?+ --- --. --. '- . . j . :, s , ,>a..Gl~~.!.'7 Y?..,,. , 'i. . ; r 7 . . . . . ................. ... .?.. .- . .

. . ... . ..) : : . . . . . . . \, .. , I . .; . . . . ..Y .. ..: 1, . id:..' . ' , . , - . - ,

,. , . . 1'

pH: Buffer 7.00 - ' "7.O ' set ,... .?: ,... 'L .* . ;. . . . . . ' : ' Field hie& Calibrstions Datemme / 7 1 90 . : . ;?' _ . . . . . . . . . . . .

, ~ ~ f f ~ ~ 4.00 - ' 1' - 0 rmd'- ' -. ' - . i - . . . . _ . . , . . . . . , . . .

. . . . Buffer 10.0 - " 10.0 . uvrurd : . . I ' % . . . . . . . . . . _ a .dL .* . . . . 7 . ; 0' "read . . Buffer 7.00 - "' " '. ' 7 . . .

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Page 2 of 2

, recycled paper I '


OM P. PO PLl, P. E. GROUNDWATER 1.IONITORING FIELD FORM

,? . *L e Locallon: GOIIEI? O&bl%-&~ 3 e

'1, Site Number.

&3 7- li'carher: CJ wL5T , Date: Z / - I ] ~ T J

W e l l ~ ~ r G u ' ' - ~

PlJRCE INFORMATION

. . _. Pxqe Method: Bailer: [ Teflon [ ] St. Steel [ ] Other . .

. . . . - a -- "5 -. . , ...... - . - , - . . . . ,', Pump: [ I Parrstaltic [ I Subrnerpble 1 I Ot.'ler e,: 4:.

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:.r . ' .

vC15 ;;; ?;~-:,d: . ,: !-:.':"., LI ell Deprh ( f : ~ We!l Elevation (it) MSL . , . :. .. .... . . . . ,, ,,;..i..; ; . , . . . . .. Static Water eve^ ( ~ t ) 5.L '\&<I&

Depth of lvater Column (ft) I Q13

x. ;veil consrant (gaUft) X = O,'L

Star~c Water Lcvcl (ft) . . , - . . - ..... * . . r

Groundwater Elev. MSL It . -, ,. :, . - . , . . , , . , - ! .<' .

q - . . _. .,

. . . . . . . . . . . . . . . . Volurn:: 5t;nding in Well 3.1 gallons = 9 ,2 c ~ ( L Q . -. .- - - d -- - - . . . . . . ... .. . . . . . . . . . . . . . . . . . . -, -. .-.--.

. . . . . . . ... a ! Canst ants f Y ) : - . .-- .. . . -..- - . .

. . . . . . . . . . .-- o yal:.r = i' OD well; . 0.65 gaVft = 4" OD well. Calc. to Determine Consrant:] . . . . . . . . . . . . . . . . . -

Jns;:r.r 1 = 0.7654 x (casing diameter in inches) x 12 1 . . . . . . . . . ..- . - . . . . ...-..-.. - 231 . . . . . . .. - - . . . . . . . . . . . . . .-a ...... -.: . - -... . . . . . . . . . . . . . . . .

Pz3e Time:

T o r ~ l Voluize P~rqed : 9 . 9 - gallons

t of '4olun:r Casings purged: 3

Purging Obsenation\hle~surements

S J I I ~ O ~ I ~ C ~n!ormatlon: Sample Method: Ba~ler: [ Teflon [ ] St.Steel [ J Other

Pump: ( 1 Par~staltlc [ ] Submergible [ ] Other

7 Number of Bottles Taken: Field Presenation (Y or N); *c& f C~M(=

F~e!d ~ I l t e r e d G r N). Date/Time 2 / 7 / l a Filtering ~ e t h o d blo~vuFu- we?*(

recycled paper ecology and cnvironrnen~

Field Measurements:

... . . *

Parameter , Unit .' Replicate 1 '. Replicate 2 Replicate 3 Replicate 4 . .

PH S.U. 3, I $.y, %*?, 2,. I Spec. Cond. umhos/cm 2~~33 Z%iu ZZLQ z-za.3

Temp. OC , % , % , a?( 4 2 %.?

Turbidity NVJ OF-%& (+-.2= v-%e 0 f f - u ! ' '

' . ' . ..... .... . . <- - - -. .-. .--.-, -- '. . , . . . . . . . . . . . . . . . . . . . .

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, *. ' .. . . METER CALIBRATIONS . . . , . . . ... . . . . . '....I. . . . -. . ., .T-;" ;. ;

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', Buffer 4.00 - ' 4.0 set/ read." ?-- . A " " ' .- I . is. ,

. . Buffer 10.0 - " - 10 -C set/re+,,,;..,; .,,, & . ,, , . "_. .- _...... .. -'% . . . .. Buffer 7.00 - *'*.- ' sr 7 . o " - n a d -.:., , . , , ".'.I. ;'

>. L.

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recycled paper ecology and rnvirunmen~

OM P. POPLJ, P. E. GROUNDWATER MONITORING FIELD FORM

. ,

. . . . . . . . h 7 j , . I ; . . mhb :L.#: ::p.7 !!..!., W t e ~ocation: b Site Number:

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. . . . . . . . . . . . . . . . . . . - - -. . L 0.16 galift = i' OD well: . 0.65 gal/ft = 4- OD well. Calc. to Dexrmine Consrant:] . - . ..- - . - . - . - . . . . . - -.- [ C o n s i s ~ t S = 0.7854 x (casing diameter in inches) ' x 12 ] . .... . .. . . . . . . . - . . . . . -. - - - - ..- ,.&,. . . - .A- -. -. & -

.. , . . 231 . . . . . . _ _ __ .._._._ _ -__ . -- -- -. . . . . . . . . . - . . . . . . . . . . . . ... ...... ... -.- ...-. - .-.,. . . -

Pzqe Time: 10 wd4. I \ ~ ~ - I Z O ~ Purging Observarion\hleasurements

Totd Volurc P~rqed: qt gallons -. . - .- . .

3 ff of Voiuo~r Casings purged:

Salnoli!!~ ln:ormjtion: SampleMerhod: Bailer: [ Teflon [ ] St.Sree1 [ 1 Other

Pump: [ ] Paristaltic [ ] Submergible [ 1 Other

. . . . . . . . . . . . . . . I . . L B O , ' . . - Time:

7 Number of Bottles Taken: Field Preservation (Y or N); &CALS '# C Y u l m

Fie!J ~ i b e r e a r N). DatMime / 7 / 90 Filtering Method b l w f i U i 6-& m t w

pie Appearance: U J ~ WV c@-2- ~7 A* T k ' W A ~ ' S

age I of 2


Field Measurements:

Number Parameter , Unit Replicate 1 Replicate 2 . . ' Replicate 3 . . Replicate 4

- -

PH S.U. 7 . b 8. fi 3,. r 7.9 Spec Cond. umhos/cm Zq 70 29 -& ,3333

~ e m p . OC . * 8.9 8Jl , 9.4 B .q . .

Turbidity NN -*a -3kfL , - .-. .- . I . '

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v, ' - . ., .. . . . . . . ,'.~! ... ...: . 1 _:. . . . ; .4 . ...> .t I : . .- I , ....

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' A ~ l d ~ e t s Crlibrations O a f & i i e 2 1' 7 / 9 0 , : $ :. . , -. . . ..... Buffer 4.00 - " ' - -LC80 -set/ read-' - - "' . . . . . . . _..,; .

. , : . . , . . . . . . . . . . . . .,. . Buffer 10.0 - . . -.:. , . .

..., +.I.-. r , . , . ?%'f I, . i

, ~ ~ f f ~ ~ 7.00 - '' '- .,.' '7; 0" . . . .: \ - . . . . ". - ,,.. k . . . .I; . ..:.. . : . , - . . . . .,.,,, :! -. . . . . ... ' . r , . . , , : ..*..,, , 2 ,..,. . . . . ,. , .... -. . .< .... . . , : : ...... . &: ,".'-&....i .- .- .-..- ,*T~'-&.r'-2.- ' .-; ,,, . . . . . . . > . . . 4;'..- .

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AD c)u U ! % - : + L O3%€FUKiodas . . .

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recycled -paper ecology and environment

OM P. POPU, P. E. GROUNDWATER MONITORING FIELD FORM , . 2 t 3 : . 4 b x ,

... . . , , . . . ,': ,', ' ., .. , . . ' , . . ' . r . . , . , . .

" .r pG,->!t,;,~ ' * * . . r i . ., r!.'.*c .... . . ' ;ir;.! i ~ z ' : : .,;!,I, i, fi (:id,!,; .....a. site Number:

...

d J Pllrqe Method: Baller: [ PVC [ I Teflon [ ] St.Steel [ ] Other .- . . . . . :1 . . . , . . , . . . . . -

: , . . , i ; : - ,;. . ;:\ . , '. . ' . . . . . ......-.........-.- . . . . . . . . . . . . . . ~ , ;,,:;, . ., . . . Pump: [ ] Paristaltic C J Submergible L:"] ' Other . , . . . . .,. rn ".;;:,:.'j?:., z , -;:. .!. . . 3 . . . . . . . . . - . . . .

( !, . ; . .;,A i .4 : ; ,,.: . G \ , , : <,,;, . , ,, . . . . . . . . . . . . . . . . . . . , . . , . . . * - 1 . . . . ; .. - ... . . . . . . ; . . . . . . . - !.,I ; - ' I , . . . ' , . ' k . . , , ' .

(. . . . .9jF$:?$;*a:,L;.s",, 7;7$3 f I L z t 7 L . . ' - , ' L;L-.&~s -2$-:h ;! - Volume Calcularion - . . . ,,)! . . . . . ..,-. .. Groundwater ~levat/Gh Calculation-. I? \ ' 5 , 7, .,: ;..* , , .._ .. ,, . I. I . . . . , ..,- ., .~ . *,-., ra.4, ,.;;I 1;

. . . . . . , . - . h + . ! . : ~ u ;-*..-. ,< .-*. .:- ... . . . , , .... 8 : . , . .,r .., . . . >. . \ Ip,b':"." ; . . . . . . . -- . - - . . - .

WpJl .:;,-y::i: .::a:.

\ , ell Depth (I;) - , ,, . . . . . .. .,, - . . . . . . . . . . . . . . . - 4- ' .>. . , , , ..-*.-,. . ;\ 5 : , . . . . . :&:+I*-. ,.- .-; . - . . . . . .

Static Water Level (it) a wc ~ f b . ' ' ' . st=tic w n e r . k v e l eft] . , . . .

,. . I \.' - .

* .2 . . . . . & . . . . . . . ' . . . ,; . . > . . . . . . . . . * , , . . . . . . . . ' ,f .?.';,, " . . - . Depth of Water Column (ft) ' I 5.9 . ' . ~ r o u n d w a c u Elev. MSL ft , ' .

S. \\..ell Constant ( g u f t ) X = 0 a Ib

. . . . . . . . . . . . V J I U ~ : : Standing m Well z * 5 :.7,6$&.. .. . . -

. . . . . . . . . . . . - 9.!o yalifr = i" OD we!!; . 0.65 gal/ft = 4" OD well. Calc. to Derermine Constant:] . . . . . . . . - . . - -

[ ionst:at S ~ 0 . 7 6 5 4 x (casingdiameter in inches) x 12 ] . .. .. - . . . . . . . _ _ I . . - _ .

231 . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . - . - - - - . - . . - - - - - .- 4 ..- -

P q e Time: I 5 n u d 3 IZw-IZ"j ,

Total Volune ?!~rged: 7. b+ gallons - - - - -

r of Volume Casings purged: 3

J / Sampltnc 1fi!ormarlon: Sample Method: Bader: [ 1 PVC [ I Teflon [ I St.Stee1 [ 1 Other

Pump: [ 1 Paristaltic [ ] Submer~ble [ 1 Other

. . . .

2% Time:

Number of Boales Taken: Field Preservation (Y or N): ' flcx~3 f ~ Y W I ~ t Field ~ikere@r N). Datc/Tirne 2 / / 70 Filtering Merhod [U


Field Measurements: , . ., , -. - .- . . . .--

kter Number Parameter Unit Replicate I Replicate 2 Replicate 3 Replicate 4 * -.

cr .4- pH S.U. ?,.$.. A,?, <A,.! . .

Spec. Cond. umhos/cm 1 ?;>A I ? 1!3-{(3 I r) 1 tL, . L- .'

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Buffer 7.00 - ' "7.0 set .. . . r.-.:.!c. ::' . :: . . . Field Meter Cdibrations D a t f l i e 'z (o 1.90 .' ::' . .:.i,.y< ' " !. '.': . . . . . . . . . . . . '. mffu 4-00 - -.. +;O .-set/ read -"- .-' .-- - : ; ' . . . . . -- .---s. 5 A

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Buffer 10.0 - " 10.0 =r/read, ! !:;, ..,, ,, , . . . . . . . . . :. . ,. . . . . . ,:-!; .... ;

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O M P. POPLI, P. E. GROUNDWATER MONITORING FIELD FORM

. . . ,,. , . . . . . . . - . .

. . . ; , : . - . ' . . . . . . ' , ' 1 . ' * . , . . , . .

2 ,. , "',: . . . . ' I .- -., , :+;!I". .., ?..:L-\*.; 4-.; , .'

Site Number: . ire ~ocation: 60L1';~-

I rmcE INFORMATION . . . . . . ... -. .

P ~ r g e Method: Bailer: [ Cf PVC [ 4 T e f l o n [ 1 St. Steel _C

Pump: [ ] Paristaltic [ ] Submergible [ ' :: . . ' . . . . -., - . . . . f : ....., . . . . .. . . . . >. .I, ' . . .........

ti, -,: ..: r: . - . > ,sq,b.,:! , .,. ;r:3,- - ., ' .* '.Jolurne Calculation .---, ,, . . .

... 1 7'

e!I Depth (ft) ,b. / 7 , L . , .

Static Water Lwel (ft) . - .

Depth of Water Column (ft) . ' IZaQ5

.. L - , _ . . . . . . : . . . . [ I Other

. . . . .- .- . . ,' ;.>. t -:, ! ,.'! ::;:*-=~.2!i: ... ; . , ' , 1 Other

i .. , ' -$; ", L ' . . . . : . . . . . . - . ... :. . ' ! .: . .I .L - .T. -. o is . I * Groundwater Elevation Calcularion- .--

. . . . . . . . . . . . - , , - i , . * : * : . i rh .:. , I ' . .

: Well Elevation (ft)'&'l' . . . . , . . . 7.:'. i. .; ., . . . . . . . . . . , ' . . . . . . . .- . . ,. , . . . .. -

. . . Static Warm Level (ftl ,,. +i;...., , f>, :

' . > , . ,$ ..: , , ., -! . -. , ' I -L ..:: . ., :, . < ' F L . '

lt - , . i\.- , .... ~roundwacer Elev. MSL -.., ,. . < - I .

, . . - , -

2. r , . . . . . . . . . . . . . . . . . Volume Srw-ding in Well gdlonS -&p3@3'c. ...- . , ....- .. ,-. .,.--- . . . . . : c... .--;. .

. . . . . . . . . . .-. ..- . . . -- . . . . . . - .-. ... -- -..------- - .. -.-- . . . . . --. ..-. . . . . -.... - .:... . . . . . . . . . . . . . . . - -.-. --- - . . -,.' - . - ... .- . . . . . . . .

- . _ . - - .....-.... . . . . . . . _ . . - . . . ___ .- . --1.- -.. . . . . ; 3-10 gal,'fr Y OD well; . 0.65 gd/ft = 4- OD well. Calc to Determine Constant:] . . . . . . . . . . . . . . . . . . . . . . . - . --.. -., ..--. -. . --.

1 Conrr2nr Y ~0.5654 x (&singdiameter in inches) x 12 1 ..... -. . -. -. .... .. . . . - ~ _ - . -

23 1 ... . . . . . . . . . . . . . . . . . . . . . . . . . . . . ... . . . - - _ _ .- . ._ _. - - -.-. -..- --.---. .... -. ---. . Pxge Time: 1 5 ~ ~ 5 . I C ~ " - I ~ * P u r ~ n g O b s e n a t l o n \ h f e ~ e m e n t s

b+ . . Torai Volume P~rqed: gallons - - -- --'

I r ol volume Cas~ngs purged: 3

I Sa~noltne In/orrnar~on: Sample Method: Bailer: [ Teflon [ ] St.Steel [ 1 Other

Pump: [ 1 Paristaltic [ 1 Submergible [ I Other

I 7 Number of Bottles Taken: Field ~resenatio&r N); - A/C& ( CYW(-

Field ~iltere@r N), Oatmime 2 / 1 90 Filtering Method ~UA(E b 1 3 ~ m F u ~ 04s/'umA/

recycled paper ecology and envtonmen~

- . Field Measurements: . 3 '

Replicate 4 . . . .

PH SU. 7.5 7.1 7.d 6.2) Spec. Cond urnhos/cm ZZZD z= 2 7 3 zz~.zo T ~ D . -,. :.: oc -, ... - 8.3 8.3 8$4 8.9

Crew Members: b. i t [ ~ 4 ;I &=(

-. . - NYSDEC

; 1 I Om P. Popli. P. E. Signature

Page 2 of 2


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