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4/22/2017
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Pilot-scale Evaluation of AirPrex for Phosphorus Management
JTAC
Innovation Program—Phosphorus Initiative
4 Angles
1
2
3
4
Liquid stream
TP removal
SolidsTP
removal
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Phosphorus Initiative: Solids Stream Phosphorus Removal
GOALTo find the most effective and sustainable phosphorus management approach through an intensive study phase of phosphorus recovery technologies under the phosphorus initiative
Internal Sidestreams
Return Activated Sludge (RAS)
Secondary Treatment
Centrate (recycle flow)
Primary Treatment
Digester
Centrifuge
Phosphorus Recovery
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Less than 1% of the flow but 25% of the Phosphorus Load
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DIGESTATE RECOVERY PILOT WORKPhosphorus Recovery Pilot Work
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Effective and Sustainable Phosphorus Management
5Measures for Success
1. Break the phosphorus recycle loop
2. Biosolids dewatering costs
3. Struvite‐scale issues for O&M
4. Phosphorus loading on soils
5. Recovery of a finite resource
1 lb of phosphorus equates to 8 lbs of struvite.7,000 lbs of phosphorus enter the RWHTF each day!
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AirPrex Pilot Testing
Hypothesis:Will create a controlled environment to precipitate struvite from District solids to simultaneously address:
Break P-Recycle Loop
Biosolids Dewatering
Struvite Issues
Phosphorus Index
Product Recovery 7
Proven Innovation
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Full Scale Installations:
5 in Germany
4 in the Netherlands
1 Belgium
1 in China
Other US Pilot Investigations:
Miami, FL
Stevens Point, WI
Fox River, IL
Fond du Lac, WI
Meridian, Idaho
Pima County, AZ
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How Does AirPrex Work?
Anaerobic Digestion
Centrifuge
Centrate
Biosolids
AirPrex
Struvite
Digester effluent is fed to AirPrex reactorReactor is aerated which strips the CO2 from the reactor and raises the pH
Magnesium is dosed to the reactor causing struvite to
precipitate
CO2 Mg
Struvite settles and is pumped out and cleaned
AirPrex effluent, stripped of phosphorus, is sent to dewatering centrifuges
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AirPrex Pilot
• Pilot onsite from June 6th through August 3rd
• Reactor operated continuously at a flow of 11 gpm
• Centrisys CS10-4 centrifuge operated 6 – 8 hours per day
• Mg:P molar dosing ratio varied between 0.7:1 – 1.7:1
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Sampling and Testing Protocol
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• Weekly water quality analyses• Daily dewatering analyses• Over 3000 water and solids analyses!
Parameter Reactor CentrifugeInfluent Underflow Effluent Influent Centrate Cake
pH Temperature Total Solids (TS) Volatile Solids (TVS) Total Ca, Mg, Fe, K, Na Dissolved Ca, Mg, Fe, K, Na Orthophosphate Total Phosphorus Water Extractable Phosphorus Acid‐cake Struvite Test Ammonium Conductivity Total Alkalinity CODEPS
Modeling
• Thermodynamic modeling to model nuisance struvite formation potential upstream and downstream of the digesters and recovery technologies
• Struvite Tool (Office of Water Programs, Sacramento, California)
• Visual Minteq (KTH, Sweden)
• BioWin
• Effects of reduction in recycle phosphorus would have on Bio P performance 12
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Driver 1: Phosphorus Recycle Control
0
100
200
300
Typical Untreated Mg:P0.7:1
Mg:P1.4:1
Mg:P1.7:1
Phosphorus, m
g/L
Orthophosphorus Particulate Phosphorus
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• OP and TP were observed to decrease in the centrate as the Mg:P molar dosing ratio increased to 1.4:1
• At 1.7:1 Mg:P molar ratio, OP was lowest while TP increased –potentially due to fines loss
Driver 1: Phosphorus Recycle Control
0
100
200
300
400
500
0
0.05
0.1
0.15
0.2
0.25
0.3
No Recovery Digestate
Centrate Recycle Soluble
P, m
g/L
Secondary Effluent
Soluble P, m
g/L
Secondary Effluent Soluble P Centrate Recycle Soluble P
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• Reducing recycle soluble phosphorus concentrations from 400 mg P/L to 30 mg P/L would result in a decrease in secondary effluent OP
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Driver 2: Dewatering Performance
50.0
55.0
60.0
65.0
70.0
75.0
80.0
85.0
90.0
95.0
100.0
0
10
20
30
40
50
60
70
Jan‐15 Feb‐15 Apr‐15 May‐15 Jul‐15 Sep‐15 Oct‐15 Dec‐15 Feb‐16 Mar‐16 May‐16
Cap
ture Efficiency (%)
Chemical Pounds per Dry Ton / Cake
%TS
Cake %TS Polymer lbs/DT Fe lbs/DT Capture Efficiency
40% of Facility 100% of Facility in EBPR
Intentional EBPR Turned Off
While more economically sustainable than chemical precipitation, Bio P does have significant impacts on full scale operations
Driver 2: Dewatering Performance
• Cost Centers: $ Polymer consumption
$ Wet mass of biosolids for hauling and dispersal
Tracked cake total solids and polymer consumption Polymer dose varied in 5 active pound/dry ton increments Higher average centrifuge hydraulic pressures for AirPrex
treated
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Solids Correction – Dry Mass
CentrifugeAirprex Apx Eff Biosolids
Cen
trate
MgCl2
fp
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NH4MgPO4●6H2O Generated in AirPrex
Total solids ∆ ∗
Fraction of struvite in biosolids matrix ‐ fb
Digestate
Product
Fraction of struvite fines in centrate ‐ fcFraction of struvite that settles and is pumped out as product ‐ fp
fp + fc + fb = 1
fb
fc
Solids Correction – Dry Mass
CentrifugeAirPrex Apx Eff Biosolids
Cen
trate
fp
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Digestate
Product
fb
fc
Acidification tests performed on dewatered biosolids to estimate total struvite
Untreated cake struvite content ~5.3% AirPrex treated cake struvite content ~11.7% ~6.4% increase in struvite - 80% retention in cake
Assumed negligible based on centrate TP at optimal operation
~0
~80%
~20%
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Solids Correction
NH4MgPO4●6H2OAmmonia and water evaporate from struvite in
the temperature range of 55 oC to 250 oC
Traditional TS concentration test measures a portion of struvite mass as water, underestimating total solids in sample
NH4 + 6H2O = 51.4% of struvite mass
This affects metrics traditionally used for assessing sludge dewaterability
Solids Correction Method
Corrected TS concentration measurement Ongoing work to determine actual extent of struvite evaporation Assumed 51.4% loss of struvite due to evaporation
Digestate TS correction:% % ∗ 1 0.053 ∗ 0.514
• AirPrex effluent TS correction:% % ∗ 1 0.117 ∗ 0.514
• Wet tons calculation:
%20
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AirPrex - DewaterabilityComplete Dataset
15%
17%
19%
21%
23%
25%
27%
29%
0 1 2 3 4 5 6 7
Cake % Total Solid
s (Uncorrected for Struvite)
Polymer Dose (Active Pounds per Hour)
AirPrex Effluent
Digestate
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297 data points analyzed
8.9 % reduction in wet tons hauled
AirPrex – DewaterabilitySorted - 10 gpm, 90% OP removal
15%
17%
19%
21%
23%
25%
27%
29%
0 1 2 3 4 5
Cake % Total Solid
s(Uncorrected for Struvite)
Polymer Dose (Active Pounds per Hour)
AirPrex
Effluent
Digestate
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61 data points analyzed
12.44% reduction in wet tons hauled
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AirPrex – DewaterabilityPaired Dataset
15%
17%
19%
21%
23%
25%
27%
29%
0 1 2 3 4 5
CAKE % TOTA
L SO
LIDS
(UNCORREC
TED FOR STR
UVITE)
POLYMER DOSE (ACTIVE POUNDS PER HOUR)
AirPrex
Digestate
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20 data points analyzed
8.7% reduction in wet tons hauled
17.6% decrease in polymer consumption
Sensitivity Analysis of Assumptions
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• Assumptions on product recovery and evaporated TS mass do impact the estimation of wet tons hauled per day
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AirPrex Biosolids Dewatering Costs
Approximately 15–20% decrease in polymer use
8.7% reduction of biosolids hauled
Untreated Biosolids21 Hauled Truckloads
After AirPrex Treatment19 Hauled Truckloads
Difference of 2 truckloads per day or 730 truckloads per year!
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Driver 3: Nuisance Struvite Reduction
0
200
400
600
800
1000
1200
1400
6/9 6/19 6/29 7/9 7/19 7/29
Pre AirPrex, Post AirPrex, and
Centrate
Struvite Production, lb/d
Untreated Digestate Airprex Treated Digestate
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Significant reduction of struvite mass predicted between untreated and AirPrex treated
0
100
200
300
400
500
600
700
800
6/9 6/19 6/29 7/9 7/19 7/29
Pre AirPrex, Post AirPrex, and
Centrate
Struvite Production, lb/d
Untreated Centrate Treated Centrate
Reduced Mg Feed Reduced Mg Feed
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Driver 3: Digester Struvite Reduction
0
5,000
10,000
15,000
20,000
No Recovery AirPrex Treated
Struvite Production in
Digesters, ppd P
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• Modeling efforts in BioWin show a reduction in struvite production from 18,000 lb/d to 13,000 lb/d with digestate phosphorus recovery
Driver 5: Product Recovery
150 tons of phosphorus recovered annually
Potential distribution
Composters
Fertilizer manufacturers
Potential uses
Turf grass
Alfalfa
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Driver 5: Product RecoveryStruvite Product - Metals Analysis
Pollutant"High Quality"
Pollutant ConcentrationLimits (mg/kg)
Pilot MAP Results(ppm)
Lab Analysis from Previous Pilot (ppm)
Arsenic 41 BDL2
Cadmium 89 BDL BDLCopper 1500 71 19Lead 300 18.9
Mercury 17 1.7Molybdenum1 < 75 0.8
Nickel 420 BDL BDLSelenium 100 BDL
Zinc 2800 33 26
1. There is currently no limit for Molybdenum for High Quality while rules are awaiting EPA investigation. Ceiling limit is 75 ppm.
2. Levels were below detection limit
Struvite product produced by Airprex is well below limits of “high quality” pollutant concentrations
Driver 5: Product RecoveryStruvite Product - Pathogen Testing
Fecal Coliforms Drying Test (MPN/g‐TS)
Sample Date Initial 24hr 48hr
8/2/2016 31 26 65
Class A: maximum density of fecal coliform < 1000 MPN per gram total solids (dry‐weight basis)
2 Samples were taken for pathogen testing using fecal coliforms July 19: 1000 MPN/g TS August 2: Investigate fecal coliform with drying time
Current testing of product shows Airprex struvite may be within Class A categorization for biosolids
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AirPrex Pilot Testing Results
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PhosphorusRecycleControl Reliable OPandTPReduction
Biosolids Dewaterability
Polymer ~17%polymerreduction
TruckHauls ~8.7%reductionhauledmass
Struvite Reduction
Digesters ~25%reductiondigesterstruvite
Dewatering Significantreductionindewateringnuisancestruvite
Phosphorus IndexAccumulationofphosphorusinbiosolids
Product Recovery 25%‐ 35%productrecovery
PHOSPHORUS WAS STRIPPING AND CENTRATE RECOVERY PILOT WORK
Phosphorus Recovery Pilot Work
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Ostara PearlFirst installation 2008
CalgaryEdmonton
Saskatoon
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How Ostara+WASSTRIP Works
ThickeningDewatering
Anaerobic Digestion
WASSTRIPProcess
Struvite
Biosolids
Centrate
Phosphorus‐stripped WAS from the WASSTRIP reactor is thickened
Phosphorus is released into the liquid stream and separated from the biosolids
Low P
High P
Centrate from dewatering is high in ammonia and is combined with liquid stream from WASSTRIP
Caustic
Mg
Caustic is added to raise the pH
Magnesium is dosed to the reactor, causing struvite to precipitate
Struvite pearls settle and are pumped out and cleaned
Ostara Pearl effluent, stripped of phosphorus, is recycled back to mainstream
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Phosphorus Stripping Pilot Test
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Pilot October 2016 to ongoing
Evaluate features and benefits of WAS phosphorus stripping
Dewatering performance
Nuisance struvite reduction
Batch WAS phosphorus stripping reactor with thickening press
Phosphorus Stripping Pilot Test
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Control Train receives TWAS, test train receives stripped TWAS
Two separate activated sludge trains allows for centrate recycle to be fed to North; control train reflects bio‐P with recycle control
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Nuisance Struvite and Dewaterability Improvements Project
0
50
100
150
200
250
300
350
400
450
0
0.05
0.1
0.15
0.2
0.25
0.3
No Recovery Digestate Centrate &Stripped Filtrate
Cen
trat
e R
ecyc
le S
olu
ble
P,
mg
/L
Sec
on
dar
y E
fflu
ent
So
lub
le P
, m
g/L
Secondary Effluent Soluble P Centrate Recycle Soluble P
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<0.1
Digester Nuisance Struvite Production
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0
4,000
8,000
12,000
16,000
20,000
No Recovery Digestate Centrate &Stripped Filtrate
Struvite Production in
Digesters, lb/d
Anaerobic Digestion
Method of determination: • Mass balance on measured analytes• BioWin modeling• XRD analysis
25% 45%
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Biosolids Production
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0
100
200
300
400
500
No Recovery Digestate Centrate & StrippedFiltrate
Biosolid
s Production, tpd
Dry Mass, dtpd Total Mass, wtpd
Preliminary Pilot Testing Results
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DigestatePhosphorusStripping
PhosphorusRecycleControl
Reliable OPandTPreduction
Assessingneedforlamellaplatesettlers
Biosolids Dewaterability
Polymer ~17%polymerreduction Awaitingadditionaltesting
TruckHauls~8.7%reductionhauledmass
~6.6%reductionhauledmass
Struvite Reduction
Digesters~25%reductiondigesterstruvite
~55%reductiondigesterstruvite
DewateringSignificantreductionindewateringnuisancestruviteduetolimitingOP
SignificantreductionindewateringnuisancestruviteduetolimitingMg
Phosphorus IndexImprovementoverchemicalsequestration
Improvementoverchemicalsequestration
Product Recovery 25%‐ 35%productrecovery
70%+productrecovery
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Next Steps
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Complete WAS phosphorus stripping digester pilot
Complete Business Case Evaluation for phosphorus recovery systems
Select a path forward for near‐term implementation