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6/12/2011
1
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2011 Idaho Water Reuse ConferenceBoise, IdahoMay 24-25
Mark Holtzen, P.E.J-U-B ENGINEERS, Inc.
Twin Falls, ID(208) 733-2414
1. Background2. Planning and Modeling3. WWTP Improvements4. WWTP Performance5. Lessons Learned6. Questions
6/12/2011
2
Rural Community in South Central Idaho
Located on Canyon Rim Above Snake River
1. Background
Murtaugh
1. Background
Cell #1 Cell #2
RI Basin #1
RI Basin #2
Influent
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Parameter 2008 2028Service Population 235 350
Flow (gpd)
Average Day 27,900 41,700
Max Month 36,100 53,800
Peak Day 56,00 83,400
BOD (ppd)
Average Day 69 102
Max Month 120 177
Peak Day 165 244
1. Background
0
25
50
75
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125
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225
250
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Sep-
08
Mar
-09
TSS
(mg/
L)
Effluent TSS
Reuse Permit Limit
1. Background
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Tota
l-Nitr
ogen
(mg/
L)Effluent Total Nitrogen
Reuse Permit Limit
1. Background
November 2006 City Entered into Consent Order with IDEQ
October 2007 Complete Facilities PlanDecember 2008 Complete Plans and SpecsApril 2009 Begin ConstructionApril 2010 Commissioning
1. Background
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IDEQ → Continued Use of Lagoons and RI Basins Not a Likely Option
Surface Water Discharge Not Feasible Limited Waste Load Allocation Available
Initial Improvement Alternatives1. Upgrade Existing Lagoons, Winter Storage, and
Slow-Rate Land Application2. Mechanical Plant with RI Basins3. Regional Treatment
2. Planning and Modeling
AlternativeCapital Cost ($Million)
Annual O&M Costs ($Million)
Monthly User Rate A($/month)
Lagoons & Slow-RateLand Application
$2.2 - $2.5 $0.053 $103 - $166
Mechanical WWTP $2.5 - $3.1 $0.107 - $0.113 $160 - $250
A – Dependent on Amount of Grant and Loan Funds Provided for Project
All Costs in 2008 Dollars.
2. Planning and Modeling
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Costs for Traditional Solutions Not Feasible City and IDEQ Agreed to Investigate a
Potential Variance to the Reuse Standards for Nitrogen and TSS Continue Using Existing Lagoons and RI Basins with
Improvements to Optimize their Performance?
Identify Key Design Parameters1. Nitrogen Impacts on Groundwater2. Phosphorus Impacts on Surface Water3. TSS Impacts on RI Basin Operation
Analyze System Performance1. Nitrogen and Phosphorus Removal
and Transport Modeling2. TSS Management Strategies
2. Planning and Modeling
Nitrification/Denitrification in RI Basins Soil Characteristics Effluent Carbon/Nitrogen Ratio RI Basin Management Predicts Dosing/Resting Periods and C:N Ratio’s
Nitrogen Impacts on Groundwater Modeled Using Mixing Zone Analysis
2. Planning and Modeling
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NH3
NH3
NH3
NH3
NH3
Dosing Cycle
Lagoon Effluent
Upper 2’-3’ of Soil
Lower Soil/Rock
2. Planning and Modeling
Resting Cycle
Percolate
Oxygen
Upper 2’-3’ of Soil
Lower Soil/Rock
NH3
NH3
NH3
NH3
NH3NO3
NO3NO3
NO3NO3
2. Planning and Modeling
NH3
NO3
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Lagoon Effluent/Carbon
Dosing Cycle
Upper 2’-3’ of Soil
Lower Soil/Rock
N2 NO3
NO3NO3
NO3NO3 N2
N2
N2
N2NH3NH3NH3
NH3
Nitrogen Gas
2. Planning and Modeling
Parameter Model Output Typical ValueDosing Period 8 – 11 days 7 – 12 days
Resting Period 5 – 7 days 10 – 16 days
Min. BOD for Denitrification 11.2 mg/L 87 mg/L
Nitrogen Removal 60 – 80% 50 – 80%
Percolate Nitrogen 4.6 – 9.3 mg/L -
2. Planning and Modeling
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Parameter Units60% N
Removal80% N
Removal
Upgradient Groundwater Nitrogen
mg/L 2.3 2.3
Percolate Nitrogen mg/L 9.3 4.6
Mixed Groundwater Nitrogen
mg/L 3.3 2.6
Increase in Downgradient Groundwater Nitrogen
mg/L 1.0 0.3
Acceptable to IDEQ? mg/L
2. Planning and Modeling
Phosphorus Removal Mechanisms Filtration, Adsorption, Precipitation, Etc. Generally Termed “Sorption”
30 – 100% Phosphorus Removal (EPA) Langmuir Isotherm Analysis
Phosphorus Sorption Capacity RI Basin #1 – 1,377 ug/g RI Basin #2 – 1,054 ug/g
2. Planning and Modeling
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2. Planning and Modeling
0
1,000
2,000
3,000
4,000
5,000
6,000
7,000
8,000
9,000
10,000
2005 2010 2015 2020 2025 2030 2035 2040
Phos
phor
us L
oadi
ng (l
bs)
Year
RIB #1 Cumulative P Loading
RIB #1 Max P Sorption Capacity
RIB #2 Cumulative P Loading
RIB #2 Max P Sorption Capacity
Discharge Effluent At Night Avoid Discharging During Algal
Blooms Provide Sufficient Drying Periods
Between Discharge Maintain Plant Growth in RI Basins Scarify Surface of RI Basins as
Needed) Install Mechanical Surface Aerators A. Source: WEF Natural Systems for
Wastewater Treatment, 2nd Edition
Average Annual TSS Effluent Loading Rate(lbs/acre-d)
Typical Design
Loading Rate A
(lbs/acre-d)
25 40 - 158
2. Planning and Modeling
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0.0
0.2
0.4
0.6
0.8
1.0
1.2
1.4
2005 2010 2015 2020 2025 2030 2035 2040
Hyd
raul
ic L
oadi
ng (i
n/d)
Year
RI Basin #1RI Basin #2Design Hydraulic Loading Rate
2. Planning and Modeling
IDEQ Granted a Variance to the Reuse Rules in March 2009
New Reuse Permit Limits (30-Day Averages) Total Nitrogen – 30 mg/L TSS – 150 mg/L
Revise O&M Manual for TSS Management Reuse Activities Cannot Cause a Violation of
Idaho Groundwater Quality Rule
3. WWTP Improvements
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3. WWTP Improvements
Cell #1 Cell #2
RI Basin #1
RI Basin #2
Influent Coarse Screen & Flow Measurement
RI Basin #3 (1 acre)
Surface Aerators (4)
AlternativeCapital Cost ($Million)
Annual O&M Costs ($Million)
MonthlyUser Rate A($/month)
Lagoons & Slow-RateLand Application B
$2.2 - $2.5 $0.053 $103 - $166
Mechanical WWTP B $2.5 - $3.1 $0.107 - $0.113 $160 - $250
Upgrade Lagoons & New RI Basin C
$0.54 $0.039 $41 - $48
A – Dependent on Amount of Grant and Loan Funds Provided for Project
B – Costs in 2008 Dollars.
C – Costs in 2010 Dollars.
3. WWTP Improvements
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3. WWTP Improvements
3. WWTP Improvements
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TSS
(mg/
L)
Effluent TSSOld Reuse Permit LimitNew Reuse Permit Limit
4. WWTP Performance
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Tota
l-Nitr
ogen
(mg/
L)
Effluent Total NitrogenOld Reuse Permit LimitNew Reuse Permit Limit
4. WWTP Performance
6/12/2011
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RI Basins are a Viable Option for Small Lagoon Systems
Water Quality Variances May be an Alternative Solution
Operation, Management, and Monitoring are Critical
Work Closely with Regulatory Agencies
5. Lessons Learned
6. Questions
Mark Holtzen, [email protected]
115 Northstar Avenue | Twin Falls, Idaho 83301Ph (208) 733-2414 | Fax (208) 733-9455