tmdl wkh workshop 17, 2011 - us epa · tmdl wkh workshop february 17, 2011 ... green...
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TMDL W k h
TMDL Workshop February 17, 2011
S. Joh Kang, Ph.D., P.E. and K. Olmstead, Ph.D., P.E. Tetra Tech Inc. Ann Arbor, MI
o us Reduct o
Outline of Presentation y Long term strategies y Introduction of Nutrient Removal technologies Manual EPA 2008 and a new study by WEF/WERF Manual, EPA, 2008 and a new study by WEF/WERF y Nitrogen Reduction y Phosphorus Reductionosp y Costs‐ capital, O&M and energy y Costs of Nutrient Trading y Future: Emerging Technologies y Future: TMDL Considerations Sy Summary
Long term strategies for nutrientLong term strategies for nutrient reduction y IJC – Great Lakes on P : 80 %, 1 mg/l, at 1 MGD or +
y Chesapeake Bay : 40% for N and P, more now
y TMDLs y Reduction y of nutrients into sewer system‐ low p detergent, low nutrient fertilizer, etc. yy Reduction of overflows during wet weather periods viaReduction of overflows during wet weather periods via green infrastructures
y Recoveryy of nutrients, P and N as fertilizers
Goals of the EPA Manual, 2008 y A planning reference for permit writers and permittees y Current nutrient reduction technologies and their
li bilireliability
y Costs of technologies F f d i d iy Factors for design and operation
The Municipal Nutrient Removal Technologies Reference Document is available on the EPA web site at: htt // / / tb/i d hthttp://www.epa.gov/owm/mtb/index.htm
Highlights of EPA ReferenceHighlights of EPA Reference Document(2008) y 30 plants volunteered to participate
y Provided 12 months data
y Provided capital and O&M costs y In‐depth case studies at 9 plants
WEF/WERF Cooperative StudyWEF/WERF Cooperative Study of Nutrient Removal Plants:
Statistics for Low Effluent Limits Achievable Technology Performance Achievable Technology Performance
Overall Highlights of The TwoOverall Highlights of The Two References y 47 well‐operating plants participated
y All regions of the U.S. and Canada represented
y No attempts were made to optimize operation
y A few plants were operated at design flow; most were d d d i floperated under design flow
y Permit limits varied at most facilities
Nitrogen Species y Ammonia‐‐‐NH3 or NH4
+
y Organic Nitrogen
y Nitrite ‐‐‐NO2 ‐
y Nitrate ‐‐‐NO3 ‐
Nitrogen Cycle y Ammonia N‐‐‐Nitrification to NO3
‐
y Increase aeration
y Organic N y If available, oxidation/nitrification to NO3
‐
If t il bl d l d fi iti d t ly If not available, develop definition and protocol y NO2
‐ ‐‐‐nitrification to NO3 ‐
y Increase aerationy Increase aeration
y NO3 ‐ ‐‐‐denitrification to N2
y Set up anoxic conditionsSet up anoxic conditions
Best Performing NitNitrogen RRemovall Pl Plants (WERF) t (WERF)
CARBOCARBOCARBONNNALUMDENITRIFICATION IN LOW DO ZONES
FiFiestta VillageFiFiestta Vill VillageVill
CACACARRRBBBOOONNNCACACARRRBBBOOONNN
River OaksRiver Oaks
ALUMCACACARRRBBBOOONNN
WesternWestern BranchBranch
TruckeeTruckee MeadowsMeadowsMeadows
PHPHOOSSTTRRIPIP CARCARCARBOBOBONNN
1 Log‐Normal Probability
1
Lg/
m
COV = stdev (ln(x)) mean (ln(x)) m,
usph
or
0.1
osh
mean (ln(x))
1 S.D. Mean h
PlaTo
t 50 - 84%
0.01 0.05 1 2 5 10 20 30 50 70 80 90 95 98 99.5 99.95
Percent Less Than or Equal To
1 84 92
/L
gg, m
ussp
hor
0.1
soh Plat
To
3 84 3.84
0.01
0.05 1 2 5 10 20 30 50 70 80 90 95 98 99.5 99.95 Percent Less Than or Equal To
84 92
Comparison of Percentiles 50 95 98 99
N technologiesN technologies
Exemplary N Technologies
10
g ro
gen,
mti
N
1
0.1
100
Denitrification Filter--Central Johnston Co, NC Five-Stage Bardenpho--Marshall St/Clearwater, FLDenitrification Filter--Lee Co., FL Biological Filter--Cheshire, CTPhased Isolation Ditch--North Cary, NC
/L
g
y
0.05 1 2 5 10 20 30 50 70 80 90 95 98 99.5 99.95
Percent Less Than or Equal To
Nitrogen Removal Technology Selection MenuSelection Menu
Permit Condition Target Concentration Technologies
Annual Average 8 mg/L (TN) All*
(50th Percentile) 5 mg/L Phased Isolation Ditch, MLE, Westbank, others
3 mg/L Denitrification Filter, 4‐Stage Bardenpho
Maximum Month 8 mg/L MLE, Westbank
Maximum Day 8 mg/L MLE Westbank
g ,
5 mg/L Phased Isolation Ditch
3 mg/L AVAILABLE?
Maximum Day 8 mg/L MLE, Westbank
5 mg/L Phased Isolation Ditch
3 mg/L NOT AVAILABLE *EPA Manual, Chapter 5 (2008)
Fraction of Organic N vs. Total r N (WERF)action of Organic N vs. Total N (WERF) F
0 9
1.0
0.7
0.8
0.9
0.5
0.6
of ON
to TN
0.3
0.4
Ratio
o
0.1
0.2
0.0 0.0 0.5 1.0 1.5 2.0 2.5 3.0 3.5 4.0
50th Percentile Daily TN, mg/L
Comparison of Plants with Lowest Effluent Ammonia (WERF)
Plant Maximum Day, in Record, mg/L
Daily, 99 percentile, mg/L
Annual, 50 percentile, mg/L
Utoy Creek 2.20 0.50 0.057 Kelowna 2.74 1.68 0.39 Fiesta Village 3.11 1.68 0.042 Tahoe Truckee 2 53 0 83 0 28 Tahoe Truckee 2.53 0.83 0.28
Best out of 13 Plants Surveyed
MI permits : daily limit : 2.0 mg/l in May‐October 30 day average : 0.5 mg/l
‐
Phosphorus Species
y Solid‐phase P
y Di l d P y Dissolved P – y orthophosphate‐ PO4
3‐
y Non‐reactive P y Non reactive P
Available Technologies:Available Technologies: Physical/Chemical � High dose Al, Fe or Ca for precipitation ‐ Cp = f(Metal dose, P concentration, pH, Ca2+, HCO3
‐) ‐ Si l T A li ti P i Single vs. Two Application Pointts ‐ the solubility limit
� Filtration : granular media, cloth media, & MembraneFiltration : granular media, cloth media, & Membrane
� Soil Ion Exchange/Infiltration Bed
BPR Organisms y Phosphate Accumulating Organisms(PAO) – Natural in Wastewater
PAO b i h iy PAOs consume carbon source without oxygen or nitrate by generating energy from stored polyphosphate and glycogeng y g
y PAOs take up phosphate under aerobic conditions y PAOs accumulate P up to 4 ‐6% by weight
Daily Technology Performance Statistics (mg/L) for Best Performing PhosphorusBest Performing Phosphorus Removal Plants (WERF and EPA)
Plant 3.84% (14d) 50% 95% 3.84%/50% 95%/50%
Iowa Hill WRF, CO 0.004 0.012 0.045 0.33 3.8 Pinery, CO 0.014 0.023 0.045 0.58 2.0 F. Wayne Hill, GA 0.020 0.040 0.110 0.50 2.8y ASA, VA 0.025 0.050 0.120 0.50 2.4
Brighton, MI 0.01 0.01 0.01 1.00 1.0
-
Selected P Technologies To
talP
hosp
horu
s, m
g/L
10
Chem Addn+Clarifiers+Land Application--Brighton, MI MBR+Chem Addn--Hyrum UT MBR+Chem Addn- Hyrum, UT A/O--Genesee Co.,MI EBPR w/ VFA Addn & Filters--Kalispell, MT 1
Genesee Co. 0.1
Kalispell
Hyrum
Brighton, MI 0.01
0.001 0.05 1 2 5 10 20 30 50 70 80 90 95 98 99.5 99.95
Percent Less Than or Equal To
P technologiesP technologies
e ce t e 0.5
a de o O
Bio‐Phosphorus Technology Bio Phosphorus Technology Selection Menu
Permit Condition Target Concentration Technologies
Annual Average 1 mg/L All*
(50th Percentile) 0.5 mg/L All*(50 ) g/
0.2 mg/L Step Feed with fermenter and filter
Maximum Month 1 mg/L Step Feed 5‐Stage Maximum Month 1 mg/L Step Feed, 5 Stage Bardenpho, A2O
0.5 mg/L Step Feed, 5‐Stage Bardenpho, A2Op ,
0.2 mg/L NOT AVAILABLE
Maximum Day 1 mg/L Step Feed, 5‐Stage Bardenpho, A2Op ,
0.5 mg/L NOT AVAILABLE
0.2 mg/L NOT AVAILABLE *EPA Manual, Chapter 5 (2008)
e ce t e 0.5 C e ca dd t o
Chemical Phosphorus TechnologyChemical Phosphorus Technology Selection Menu
Permit Condition Target Concentration Technologies
Annual Average 1 mg/L Chemical Addition
(50th Percentile) 0.5 mg/L Chemical Addition
M i M h /L Ch i l Addi i
(50 ) g/
0.1 mg/L Chemical with Filter
0.05 mg/L Chemical w/ Special Process
Maximum Month 1 mg/L Chemical Addition
0.5 mg/L Chemical Addition
0.1 mg/L Chemical with Filter
0.05 mg/L Chemical w/ Special Process
Maximum Day 1 mg/L Chemical Addition
0 5 mg/L Chemical with Filter 0.5 mg/L Chemical with Filter
0.1 mg/L NOT AVAILABLE
COSTS y existing facilities y permit limits y available site
y wet weather flows
ta Costs e o a
D D
DD
tal)
dies
MGD
MG MG
CT (Incre
menta
Case S
tudie PDET @
10MG
APET @
5 MG
APET @
1 MG
MD/CT
CAPD
CAP
CAP
Capital Costs—TN RemovalCap
$3 50 $4.00
paci
ty
$2 00 $2.50 $3.00 $3.50
$/gp
d C
ap
$0 50 $1.00 $1.50 $2.00
ial C
ost $
$0.00 $0.50
Cap
iti
MD/
emen
tal)
e Studies
@10
MGD
@5 M
GD
@1 MGD
CT (Incre
m
Case S
CAPDET @1
CAPDET @
CAPDET @ O&M C TN R lO&M Costs—TN Removal
$3.50$3.50 $3.00 $2.50 $2.00 $1.50 $1.00 $0.50 $0 00 $0.00
O&
MM C
ostss
$/lb
TNN
rem
ovved
Energy Usage in Wastewater gy g Treatment Plants in U.S.
y Average Plant : 1500 KWh/Million Gallons (MG) d f dtreated for secondary treatment
y Advanced Treatment Plant: 2000 – 3000 KWh/MG
e c e Cost ea do
$
D R E k S
Denite
Filter
PID
SBR ag
e Bard
enph
o
MLE
Wes
tbank
Step
Feed/A
S ag
e Bard
enph
o
4 Stag
S
5 Stag
N Life‐Cycle Cost BreakdownCy
$3.50
Capital ESTIMATED Labor Chemical Energy
$2.50
$3.00
mov
ed
$1.00
$1.50
$2.00
$/lb
TN
rem
$0.00
$0.50
e c e Cost ea do
S D k R
St tepFee
d/AS
age B
arden
pho
PID
Wes
tbank
SBR wi h
out C
hem P
/O
with C
hem
P
5 Stag
A/Owi
A/O
P Life‐Cycle Cost BreakdownCy
$30.00
Capital ESTIMATED Labor Chemical Energy
$20.00
$25.00
oved
$10.00
$15.00
$/lb
P re
mo
$0.00
$5.00
Costs for Nutrient Trading: Costs for Nutrient Trading: “Market Rates” y Nitrogen: $2.00/lb for trading (CT and VA) y Phosphorus: $4.00/lb for trading (VA) y Intended to covers only parts of O&M costs
y Market rates will vary in the future
ec o o es
Emerging Technologiese g g g � Phosphorus : target at 0.05 mg/l � Filtration : Membrane � Densadeg® � Co‐Mag® � Ballllastedd Flloccullation/ActiFllo® � Soil Ion Exchange/Infiltration Bed
� Nitrogen : below 3 mg/lNitrogen : below 3 mg/l � Membranes (MF/UF or Reverse Osmosis) � Biological Aerated/Anoxic Filter
� Both � Automatic Controls with on‐line sensors
f
Future Considerations for TMDL: P i W iPermit Writers
y Specify the limits for critical periods to protect water quality : annual average, max month, max week , or max daymax day y The worst day in the river is usually the best day at the pplant((a low flow & at high temp)g p)
y TIN (vs. TN) should be considered where appropriate
y Account for developpment time for new technologgies to meet future needs y Continued Support for technology development, $$$
Future Considerations for TMDL: Permitees
y Match the permit with right technologies(no over‐design) y M kMake nutriient removal sustai bl inable with respect to l i h energy, greenhouse gases, and new sludge production
y Encourage nutrient recovery where feasible y Encourage nutrient recovery, where feasible
S N lSummary – N removal y Practical limit is Annual average at 3 mg/l. y 4 or 5‐stage Bardenpho plants come close to meeting the TN of 3 mg/l, 95 percent of the time; 10 Florida plants show a capability of 3 5 mg/Lcapability of 3.5 mg/L. y More sustainable technologies are feasible for higher target limits y Organic Nitrogen is a critical variable
y Costs depend on existing facilities and target limit
S P lSummary ‐ P removal
y Practical limits are Annual Average of 0.2 mg/L by biological process and 0.1 mg/L by chemical addition with biological process, and 0 1 mg/L by chemical addition with filter. y Lower targget limits reqquire site‐sppecific advanced technologies y Soil ion exchange is possible if sufficient land is available
l bly Non‐reactive P is a critical variable
y Costs depend on existing facilities and target limit yy Recovery of P is encouraged for sustainable futureRecovery of P is encouraged for sustainable future
Thank You!