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Physicochemical
Nutrient Recovery
Technologies
David A. Vaccari
dvaccari@stevens.edu
Cities of the Future
Lago di Como
May 13, 2016
Outline
• Nitrogen removal and recovery
– Stripping and Scrubbing
• Phosphorus precipitation
– Direct precipitation
– Crystallization
• Incinerator ash
– Leaching/extraction
– Thermal
2
Buckwell, A. Nadeu, E. 2016.
Nutrient Recovery and Reuse
(NRR) in European agriculture.
A review of the issues,
opportunities, and actions.
RISE Foundation, Brussels.
Ammonia Stripping/Scrubbing
4
NH4
+  NH3 pKa = 9.24
NH4
+ NH3
Ammonia Stripping/Scrubbing
(Nitrification must be avoided)
5
NH4
+ NH3
Caustic
Air
H2SO4
NH4SO4
or HNO3
or NH4NO3
Anaerobic/Ion Exchange (AN-IX)
Anaerobic Solids Blanket
ammonification to NH4
+
Ion Exchange Chambers
zeolite granular
ion exchange media
Sanitation
Water
Low
Nitrogen
Effluent
CH4, H2
Daniel P. Smith, Ph.D., P.E., DEE
Applied Environmental Technology, Garrett Park, Maryland
Phosphorus Removal and Recovery
7
• Mainstream processes
• 40% to 50% recovery
• Sludges, manure, etc.
• 90% recovery possible
• 50-60 mg P/L required
• 75-300 mg P/L typical in BNR
• Incinerator ash
• 90% recovery typical
E. Desmidt et al, Phosphorus Scarcity and P-Recovery Techniques (U. Gent, 2014)
Phosphorus precipitation
8
10 Ca2+ + 6 PO4
3- + 2 OH- ↔ Ca10(PO4)*6(OH)2 ↓
http://www.lenntech.com/phosphorous-removal.htm
Al3+ + HnPO4
3-n ↔ AlPO4 + nH+
Fe3+ + HnPO4
3-n ↔ FePO4 + nH+
Iron and Aluminum phosphorus precipitates are not readily bioavailable and
therefore not favored for fertilizer use
Forms of Calcium Phosphate
9
E. Desmidt et al, Phosphorus Scarcity and P-Recovery Techniques (U. Gent, 2014)
Phase formed is kinetically determined
DCPD forms preferentially at pH 5
OCP around pH 6
HAP above pH 7
HAP is most stable phase and ultimate form
http://www.lenntech.com/phosphorous-removal.htm
Post-precipitation can
give P < 0.5 mg/L
Co-precipitation has low
capital costs,
but P ~ 1 mg/L
Pre-precipitation
Buckwell, A. Nadeu, E. 2016.
Nutrient Recovery and Reuse
(NRR) in European agriculture.
A review of the issues,
opportunities, and actions.
RISE Foundation, Brussels.
Substance
Conc.
(mg/L)
Conc.
(mmolar)
PO4-P 87 2.8
Ca+2 51 1.3
Mg+2 7.2 0.3
NH4+N 1142 81.6
CO3 (as CaCO3) 1068 10.7
Chemical Composition of Anaerobic Digester Effluent
(Jie Ge and Xiaoguang Meng)
Struvite
Mg++
18%
NH4+
- N 10%
PO4-3
- P 23%
Dolomite Calcined
Ca 22% 42%
Mg 13% 25%
DL is provided by
Graymount Lime
Inc.
Ca and Mg content
in DL were 39.9%
and 22.4%,
respectively.
13
Dolomite Lime (CaMg(OH)4)
Dolomite
Dolomite Lime
Calcined
DL
Components
phase Molecular formula Wt. %
Periclase MgO 28.3
Portlandite Ca(OH)2 58.4
Brucite Mg(OH)2 12.3
Calcite CaCO3 1.0
Kinetic experiments
14
P
N
Mg
Ca
Mg2+ + NH4
+ + PO4
3 + 6H2O  MgNH4PO46H2O
Ca2+ + PO4
3- + OH-  Ca5(PO4)3OH
P in the effluent water = 98 ppm
Removal of Phosphate Using a Dolomite Lime
(CaMg(OH)4) in a Complete Mix Reactor
9
0
20
40
60
80
100
0 8 16 24 32 40 48
PO4
3--P(mg/L)
Time(h)
A
0.1g/L DL 0.3g/L DL 0.5g/L DL
0.8g/L DL 0.3 g/L lime
7
7.5
8
8.5
9
0 8 16 24 32 40 48
pH
Time (h)
B
0.1 g/L DL 0.3 g/L DL 0.5 g/L DL
0.8 g/L DL 0.3 g/L lime
0
20
40
60
80
100
0 8 16 24 32 40 48
Ca2+(mg/L)
Time (h)
C
0.1 g/L DL 0.3 g/L DL 0.5 g/L DL
0.8 g/L DL 0.3 g/L lime
0
50
100
150
200
0 8 16 24 32 40 48
Mg2+(mg/L)
Time (h)
D
0.1 g/L DL 0.3 g/L DL 0.5 g/L DL
0.8 g/L DL 0.3 g/L lime
SEM Images and XRD Spectra of the Solid Products
1
6
Chemical analysis of the solids: 23% P, 11% N, 4% K. The product contains
high contents of the nutrients.
S=struvite
C=calcite
Current Treatment Technologies
for Point Source Discharge
(Courtesy Chelskey Shepsko & Arun SenGupta
• Electrodialysis / Reverse Osmosis
Source: FuMA-Tech, 2016.
WAC and HAIX-Zr Ion Exchange
Process for Removal
HAIX-NanoZr Synthesis
HAIX-NanoZr Design
Cation exchanger
with negatively
charged sulfonic
acid groups as
the host resin.
Anion exchanger
with positively
charged quaternary
ammonium
groups as the host
resin.
The synergy of highly durable polymer support, Donnan
Membrane Principle, and zirconium oxide nanoparticles
Phosphorus Regeneration for
HAIX Column with WAC
Phosphate free
water
Phosphate loaded
water•Process to create
struvite
o Regenerate with
NH4OH
o Added
stoichiometric
MgCl2 to
regenerant
Some Commercially Available Full-Scale Processes
22
E. Desmidt et al, Phosphorus Scarcity and P-Recovery Techniques (U. Gent, 2014)
23
Mg2+ + NH4
+ + PO4
3- MgNH4PO4∙6H2O
Accidental Struvite Formation
(courtesy of Michael Ditton, Ostara Co.)
24
Fluidized Bed Struvite Precipitation
25
Phosphorus Recovery Intercepts Recycle to
Recover Phosphorus and Ammonia
(courtesy of Michael Ditton, Ostara Co.)
26
WASSTRIP Increases P Recovery while protecting
Digesters from Struvite Formation
(courtesy of Michael Ditton, Ostara Co.)
27
Crystalized Struvite Product
(courtesy of Michael Ditton, Ostara Co.)
Ostara Pearl®
STRUVITE PRECIPITATION ALTERNATIVES
Multiform
Harvest
Kansas
Environmental
Management
Associates
(KEMA)
Phred™
Crystallactor
29
Incinerator Ash
Vlasta Klima Balloun Lecture
Seaborne Process
Recovery of P and N; Removal of Heavy Metals
Energy Recovery by Incineration of Biosolids
31
Outotec – Ash Dec Process
32
http://www.chemengonline.com/p-recovery-on-the-move/?printmode=1
• 1000 degrees C
• Toxic metals are vaporized – reducing 99% less Cd and 90% less U content
of product than fertilizer from phosphate rock (suitable for organic farming)
• Product is calcined phosphate – combined with K salts to make fertilizer
Mephrec Process
33
• Coke and oxygen inputs
(reducing conditions)
• 1450 degrees C
• Heavy metals are reduced
to metallic state
• Utilizes energy content of
sludge
• Produces calcium-silico-
phosphate fertilizer
http://www.chemengonline.com/p-recovery-on-the-move/?printmode=1
Conclusion:
Nutrient Removal and Recovery is Hot!
May 16, 2016
AAEES Nutrient Recovery Workshop
New Jersey Water Environment Association Annual
Conference, Atlantic City, NJ
July 10-13, 2016
WEF/IWA Nutrient Removal and Recovery
The Hyatt Regency Denver - Convention Center
Denver, Colorado
34
What do you think?
David A. Vaccari dvaccari@stevens.edu

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Lectures Vaccari - Physicochemical Nutrient Recovery Technologies

  • 1. Physicochemical Nutrient Recovery Technologies David A. Vaccari dvaccari@stevens.edu Cities of the Future Lago di Como May 13, 2016
  • 2. Outline • Nitrogen removal and recovery – Stripping and Scrubbing • Phosphorus precipitation – Direct precipitation – Crystallization • Incinerator ash – Leaching/extraction – Thermal 2
  • 3. Buckwell, A. Nadeu, E. 2016. Nutrient Recovery and Reuse (NRR) in European agriculture. A review of the issues, opportunities, and actions. RISE Foundation, Brussels.
  • 4. Ammonia Stripping/Scrubbing 4 NH4 +  NH3 pKa = 9.24 NH4 + NH3
  • 5. Ammonia Stripping/Scrubbing (Nitrification must be avoided) 5 NH4 + NH3 Caustic Air H2SO4 NH4SO4 or HNO3 or NH4NO3
  • 6. Anaerobic/Ion Exchange (AN-IX) Anaerobic Solids Blanket ammonification to NH4 + Ion Exchange Chambers zeolite granular ion exchange media Sanitation Water Low Nitrogen Effluent CH4, H2 Daniel P. Smith, Ph.D., P.E., DEE Applied Environmental Technology, Garrett Park, Maryland
  • 7. Phosphorus Removal and Recovery 7 • Mainstream processes • 40% to 50% recovery • Sludges, manure, etc. • 90% recovery possible • 50-60 mg P/L required • 75-300 mg P/L typical in BNR • Incinerator ash • 90% recovery typical E. Desmidt et al, Phosphorus Scarcity and P-Recovery Techniques (U. Gent, 2014)
  • 8. Phosphorus precipitation 8 10 Ca2+ + 6 PO4 3- + 2 OH- ↔ Ca10(PO4)*6(OH)2 ↓ http://www.lenntech.com/phosphorous-removal.htm Al3+ + HnPO4 3-n ↔ AlPO4 + nH+ Fe3+ + HnPO4 3-n ↔ FePO4 + nH+ Iron and Aluminum phosphorus precipitates are not readily bioavailable and therefore not favored for fertilizer use
  • 9. Forms of Calcium Phosphate 9 E. Desmidt et al, Phosphorus Scarcity and P-Recovery Techniques (U. Gent, 2014) Phase formed is kinetically determined DCPD forms preferentially at pH 5 OCP around pH 6 HAP above pH 7 HAP is most stable phase and ultimate form
  • 10. http://www.lenntech.com/phosphorous-removal.htm Post-precipitation can give P < 0.5 mg/L Co-precipitation has low capital costs, but P ~ 1 mg/L Pre-precipitation
  • 11. Buckwell, A. Nadeu, E. 2016. Nutrient Recovery and Reuse (NRR) in European agriculture. A review of the issues, opportunities, and actions. RISE Foundation, Brussels.
  • 12. Substance Conc. (mg/L) Conc. (mmolar) PO4-P 87 2.8 Ca+2 51 1.3 Mg+2 7.2 0.3 NH4+N 1142 81.6 CO3 (as CaCO3) 1068 10.7 Chemical Composition of Anaerobic Digester Effluent (Jie Ge and Xiaoguang Meng) Struvite Mg++ 18% NH4+ - N 10% PO4-3 - P 23% Dolomite Calcined Ca 22% 42% Mg 13% 25%
  • 13. DL is provided by Graymount Lime Inc. Ca and Mg content in DL were 39.9% and 22.4%, respectively. 13 Dolomite Lime (CaMg(OH)4) Dolomite Dolomite Lime Calcined DL Components phase Molecular formula Wt. % Periclase MgO 28.3 Portlandite Ca(OH)2 58.4 Brucite Mg(OH)2 12.3 Calcite CaCO3 1.0
  • 14. Kinetic experiments 14 P N Mg Ca Mg2+ + NH4 + + PO4 3 + 6H2O  MgNH4PO46H2O Ca2+ + PO4 3- + OH-  Ca5(PO4)3OH P in the effluent water = 98 ppm
  • 15. Removal of Phosphate Using a Dolomite Lime (CaMg(OH)4) in a Complete Mix Reactor 9 0 20 40 60 80 100 0 8 16 24 32 40 48 PO4 3--P(mg/L) Time(h) A 0.1g/L DL 0.3g/L DL 0.5g/L DL 0.8g/L DL 0.3 g/L lime 7 7.5 8 8.5 9 0 8 16 24 32 40 48 pH Time (h) B 0.1 g/L DL 0.3 g/L DL 0.5 g/L DL 0.8 g/L DL 0.3 g/L lime 0 20 40 60 80 100 0 8 16 24 32 40 48 Ca2+(mg/L) Time (h) C 0.1 g/L DL 0.3 g/L DL 0.5 g/L DL 0.8 g/L DL 0.3 g/L lime 0 50 100 150 200 0 8 16 24 32 40 48 Mg2+(mg/L) Time (h) D 0.1 g/L DL 0.3 g/L DL 0.5 g/L DL 0.8 g/L DL 0.3 g/L lime
  • 16. SEM Images and XRD Spectra of the Solid Products 1 6 Chemical analysis of the solids: 23% P, 11% N, 4% K. The product contains high contents of the nutrients. S=struvite C=calcite
  • 17. Current Treatment Technologies for Point Source Discharge (Courtesy Chelskey Shepsko & Arun SenGupta • Electrodialysis / Reverse Osmosis Source: FuMA-Tech, 2016.
  • 18. WAC and HAIX-Zr Ion Exchange Process for Removal
  • 20. HAIX-NanoZr Design Cation exchanger with negatively charged sulfonic acid groups as the host resin. Anion exchanger with positively charged quaternary ammonium groups as the host resin. The synergy of highly durable polymer support, Donnan Membrane Principle, and zirconium oxide nanoparticles
  • 21. Phosphorus Regeneration for HAIX Column with WAC Phosphate free water Phosphate loaded water•Process to create struvite o Regenerate with NH4OH o Added stoichiometric MgCl2 to regenerant
  • 22. Some Commercially Available Full-Scale Processes 22 E. Desmidt et al, Phosphorus Scarcity and P-Recovery Techniques (U. Gent, 2014)
  • 23. 23 Mg2+ + NH4 + + PO4 3- MgNH4PO4∙6H2O Accidental Struvite Formation (courtesy of Michael Ditton, Ostara Co.)
  • 24. 24 Fluidized Bed Struvite Precipitation
  • 25. 25 Phosphorus Recovery Intercepts Recycle to Recover Phosphorus and Ammonia (courtesy of Michael Ditton, Ostara Co.)
  • 26. 26 WASSTRIP Increases P Recovery while protecting Digesters from Struvite Formation (courtesy of Michael Ditton, Ostara Co.)
  • 27. 27 Crystalized Struvite Product (courtesy of Michael Ditton, Ostara Co.)
  • 28. Ostara Pearl® STRUVITE PRECIPITATION ALTERNATIVES Multiform Harvest Kansas Environmental Management Associates (KEMA) Phred™
  • 30. Incinerator Ash Vlasta Klima Balloun Lecture
  • 31. Seaborne Process Recovery of P and N; Removal of Heavy Metals Energy Recovery by Incineration of Biosolids 31
  • 32. Outotec – Ash Dec Process 32 http://www.chemengonline.com/p-recovery-on-the-move/?printmode=1 • 1000 degrees C • Toxic metals are vaporized – reducing 99% less Cd and 90% less U content of product than fertilizer from phosphate rock (suitable for organic farming) • Product is calcined phosphate – combined with K salts to make fertilizer
  • 33. Mephrec Process 33 • Coke and oxygen inputs (reducing conditions) • 1450 degrees C • Heavy metals are reduced to metallic state • Utilizes energy content of sludge • Produces calcium-silico- phosphate fertilizer http://www.chemengonline.com/p-recovery-on-the-move/?printmode=1
  • 34. Conclusion: Nutrient Removal and Recovery is Hot! May 16, 2016 AAEES Nutrient Recovery Workshop New Jersey Water Environment Association Annual Conference, Atlantic City, NJ July 10-13, 2016 WEF/IWA Nutrient Removal and Recovery The Hyatt Regency Denver - Convention Center Denver, Colorado 34
  • 35. What do you think? David A. Vaccari dvaccari@stevens.edu