critical comparison of nutrient (n,p,k) recovery ... · critical comparison of nutrient (n,p,k)...
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Critical comparison of nutrient (N,P,K)
recovery techniques from sludge,
biosolids and manure
Symposium sur les eaux usées
Boucherville
October 24th 2013Céline VANEECKHAUTE,
Erik MEERS, Filip TACK, Evangelia BELIA, Peter A. VANROLLEGHEM
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Presentation outline
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PROBLEM STATEMENT
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Global use of synthetic fertilizers
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Sutton et al. (2013)Demand ↑⟹ Energy use ↑ ⟹ Costs ↑
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Increasing demand
vs. anticipated depletion
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Cordell et al. (2011)Natural resources ↓ ⟹ Quality ↓
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On the other hand:
nutrient excesses in the environment
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Sutton et al. (2013)
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Environmental concerns
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Need for sustainable
resource management !
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OBJECTIVES
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Global objectives
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Renewable
energy
Organic-
biological
waste
Municipality
Agriculture
Energyproduction
Waste water treatment
Waste water,
urine
Sludge
Renewable
fertilizers
Synthetic
fertilizers
Fossil
energy
Renewable
energy
Renewable
energy
Manure,
sludge
(Biological)
food
Fossil
energy
Fossil
energy
Environment
Environment
Environment
Nutrients
Nutrients
Nutrients
Current practice
Sustainable practice
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Specific objectives
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Haber Bosch Process: N2 → NH4
P-mining: Apatite → Ortho-P
K-mining: Potash → K2O
Bioavailablenutrients
Waste water and sludge treatment
Non-bioavailable
nutrients
NH4 → N2
Ortho-P → Fe/AlPO4
K2O → ?
NH4, ortho-P, K2O → struvite, (NH4)2SO4, … ?Waste Water Treatment Plant (WWTP)
→ Water Resource Recovery Facility (WRRF)
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Points of attention
The nutrient recovery process must have
equivalent treatment efficiency as
conventional treatment
The process must be cost-effective
The process must be simple to operate and
maintain
There must be a market for the recovered
nutrient products
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Status in Québec
± one million tonnes of fertilizer residuals are used
annually on agricultural soils
‘Plan agro-environnemental de valorisation’ (PAEV)
MDDEP promotes the valorisation of reusable resources,
such as nutrients, organic matter and energy from municipal
biosolids and sludges
Valorisation must rely on good management practices:
• Strategies to reduce the risks for the environment and human
health to a minimum
• Strategies to reduce greenhouse gas emissions to a minimum
• Take in account the effectiviness and value of the resources
(product efficiency)
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NUTRIENT RECOVERY
TECHNIQUES (NRT)
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Three step framework
Waste
water,
manure
ConcentrationSludge/
biosolids
Stabilization/
Hygienisation/
Release
Extraction
Low
nutrient
effluent
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RECOVERED
NUTRIENTS
EBPR
Adsorption/ion exchange
Biomass production
Chemical precipitation
Nanofiltration
Reversed osmosis
Anaerobic digestion
Aerobic digestion
Thermochemical
Fatty acids
Pre-digestion lysis
Bioleaching
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Evaporation
Thermal drying
Mechanical separation (with or without
polymer addition)
NRT 1: P crystallizationComposting
NRT 2: NH3 strippingThermal drying
NRT 4: Membrane filtration Forward osmosis
ElektrodialysisTransmembrane-chemosorption
CombustionPyrolysis
PyrolysisP extraction
Digestate
Liquid fractionSolid fraction
Air
NRT 3 : Acid air scrubber
Air + NH3
Extraction of nutrients
after anaerobic digestion
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NRT 5: Biomass production and harvest
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NRT1: P crystallization
Soluble P (ortho-phosphate) can be precipitated by: Ca2+
Ca3(PO4)2
Mg2+ MgNH4PO4.6H2O or MgKPO4.6H2O (MAP of struvite)
K+ K2NH4PO4 (potassium-struvite)
Status: Full-scale for waste water, digested centrate and calf
manure; Pilot scale for raw digestate
Valorisation end-product:
Slow release fertilizer
Economic viability Slow release fertilizer
Elimination of Fe/Al
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Design: Fluidized bed reactor
or continuously stirred tank reactor
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Multiform Harvest (2013)
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NRT2: NH3-stripping and absorption
Mass transfer of NH3 from
aqueous to gas phase Elevated pH & T
Lime softening step
Design: Packed column Status: Full-scale
Bottlenecks: Fouling of the
packing material
Improved design: Water-sparged aerocyclone Status: Lab-scale (Quan et al. 2010)
Higher air stripping efficiency, better mass transfer
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Gustin and Marinsek-Logar (2011)
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NRT3: Acidic air scrubber
Capture of NH3, dust particles, water vapour, odour
compounds in acid, mostly H2SO4
NH3 + H2SO4 → (NH4)2SO4
Design: Packed bed reactor or
venturi scrubber
Botlleneck: Corrosion problems
Status: Full-scale
Valorisation end-product Sulphur content (30-40 kg m-³) !
Variable N-content (30-70 kg m-³)
Low pH (3-7), high salt content
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http://www.croll.com/wetscrubbers.html
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Evaporation
Thermal drying
Mechanical separation (with or without
polymer addition)
NRT 1: P crystallizationComposting
NRT 2: NH3 strippingThermal drying
NRT 4: Membrane filtration Forward osmosis
ElektrodialysisTransmembrane-chemosorption
CombustionPyrolysis
PyrolysisP extraction
Digestate
Liquid fractionSolid fraction
Air
NRT 3 : Acid air scrubber
Air + NH3
Extraction of nutrients
after anaerobic digestion
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NRT 5: Biomass production and harvest
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NRT4: Membrane filtration
Types: RO, UF, MF
Valorisation end-product: N/K fertilizer (RO) Variable N (2-10 g kg-1) and K2O (4-14 g kg-1) content
High salt content
Status: Full-scale for digestate and manure
Bottleneck: Blocking of membranes (SS, salts, …)
Economic viability High chemical requirements
High energy use
High operational costs
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Emerging membrane techniques
Electrodialysis Ion exchange membrane + electrical voltage
Transfer of NH4+, K+ en HCO3
-
Status: No full-scale for digestate,
tests on lab-scale
Transmembrane chemosorption Diffusion of NH3 through membrane & capture in H2SO4
Status: Pilot in NL (pig slurry)
Forward osmosis Use of draw solution instead of pressure (RO)
Status: Full-scale for sea water, food waste;
no testing (?) with digestate
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NRT5: Biomass production
Removal of P&N by plant uptake (algae, duckweed)
Status: Lab tests (algae) + pilots
Bottlenecks Suspended solids, humic acids,...
reduction of light penetration
Large surface required
High energy consumption and high costs
Harvest method
Valorisation harvested biomass Bio-based chemicals or fertilizer
Biofuels
Animal feed
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DISCUSSION
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Comparison of
techniques and end-products
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Technique P-crystallisationNH3- stripping &air scrubbing
Membrane filtration
Biomass production
% recovery80-90% P0-40% N
> 90 % N Depends on
pretreatment80-90 % N and P
End-productsStruvite or Ca-P crystals= Slow-release fertilizer
(NH4)2SO4 solution= N-S fertilizer
NK-fertilizer (RO) Biomass:Duckweed (30% Pon DW)
Main technicalbottlenecks
Precipitation in
piping/equipment Fouling /
corrosion
Membrane
blocking
Harvest method
Reduced light
penetration
Ecologicalevaluation
Chemical use Fe/Al ↓
Odor ↓ Energy ↑ Acid ↑ Can replace N-D
Chemicals ↑ Energy ↑
Surface ↑ Energy ↑ Use of polymers
Economicalevaluation
Can be profitable Can replace N-D Interest in S ↑
High capital and
operational costsHigh costs (algae)
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CONCLUSIONS AND
PERSPECTIVES
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Conclusions
Best available techniques for
nutrient recovery: Struvite precipitation
NH3-stripping and absorption in
acidic air scrubber
Further technical fine tuning Fertilizer quality
Energy and chemical reduction
Further developments will only take
place if recovery is profitable
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Perspectives
modelEAU / PrimodalDynamic modeling of physico-
chemical nutrient recovery systems
for wastewater and sludge streams
to sustainably produce marketable
fertilizers with high nutrient use
efficiency (BMP Innovation
doctorat, NSERC/FRQNT)
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THANK YOU FOR
THE ATTENTION
QUESTIONS?
Further reading:
Inventory Techniques for nutrient
recovery from digestate
http://arbornwe.eu/downloads