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Green recovery of energy and nutrients from
wastewater in the frame of the Circular
Economy
ELENA FICARA
POLITECNICO DI MILANO
Dipartimento di Ingegneria Civile e Ambientale - Sezione ambientale
Dipartimento di Ingegneria Civile e Ambientale
Content
- Introduction: general circular economy framework
- Technologies for resource recovery in WWTPs
- Overview on applying algae for wastewater treatment for nutrients/energy
recovery/savings
Dipartimento di Ingegneria Civile e Ambientale
The role of wastewater treatment plants
Challenges of sanitation systems:
 Supply safe (drinking) water
 Limit environmental impacts by
wastewater discharges
Historically…
but…
 Growing population,
 Life style changing,
 Climate change
are modifying water
availability and request
new challenges are to be faced
Uptake Use discharge
Dipartimento di Ingegneria Civile e Ambientale
The circular approach ….
Water,
energy,
resources
Water source treatment
Reuse
treatment
discharge
New hierarchy
use
Dipartimento di Ingegneria Civile e Ambientale
The circular approach ….
Dipartimento di Ingegneria Civile e Ambientale
Looking beyond the current
"take, make and dispose”
extractive industrial model, the
circular economy is restorative
and regenerative by design.
Dipartimento di Ingegneria Civile e Ambientale
Which kind of resources to be recovered?
Biodegradable organics:
12 – 14 W/PE
Total organics:
18 – 20 W/PE
Ammoniacal N: 8 W/PE
TOTAL: 20 – 28 W/PE
(4-5 times energy required
for WW treatment)
Clean water
Chemical energy
Nutrients (N, P)
Wastewater 40-70 m3/PE/y
2-3 kg N/PE/y
0,5-1 kg P/PE/y
= WWTP  WRRP
Water Resource
Recovery Platform
Dipartimento di Ingegneria Civile e Ambientale
Energy request for the water sanitation
o 10-17 W/PE
o 90-150 kWh/PE/y
• Reducing water consumption
• Optimizing processes
• Recovering energy from wastewater
2-3% of electric energy consumption
up to 7%
(in EU and USA)
How to save energy?
In Italy:
Total consumption 7500 GWh/y
(2,5% national electric energy
consumption)
Campanelli, Foladori, Vaccari (2013)
•water supply 57%
•water treatment 43%
Dipartimento di Ingegneria Civile e Ambientale
Energy recovery from wastewater
Thermal: Wastewater temperature: 14 - 23°C.
Heat pumps to warm (winter) or cool (summer) buildings.
e.g.: Nosedo (Milano) WWTP recovers 200 kW
Hydro-electric: by taking advantages of head loss
e.g.: Folgaria (TN) WWTP recovers 40 kW (50 L/s for 236 m)
Chemical energy: typically recovered from the sludge line
In Italy: today 121 GWh/y from AD of waste sludge (GSE, 2014)
Potential: 2100 GWh/y (= all plants with tertiary treatments would use
conventional AD)
Dipartimento di Ingegneria Civile e Ambientale
Energy positive WWTP: utopic?
• Recover energy with effective AD
• Optimizing energy intensive processes
New pathways in biological treatment
Optimization of existing treatment
e.g.: Aeration systems
Optimized processes
Energy consumption
P.E. served
WWTP of Strauss (Austria)
250 000 P.E.
Energy cost for treatment:
11.3 kWh/PE/y, offset by biogas
production
Dipartimento di Ingegneria Civile e Ambientale
Recovery of phosphorus
Accessible stocks of P-rocks are going to be exhausted SOON
Use
Wastes
Agriculture
Plants
P mining
Water bodies
(WWTP)
 P is fundamental in
sustaining agriculture
 Demand is growing
together with word
population
 Uneven distribution
of P mines (Morocco,
Cina, US)
 EU is P deficient About 18% of the P request could be
recovered from waste streams
Cordell & White, 2011, Sustainability, 3(10), pp. 2027-2049
Dipartimento di Ingegneria Civile e Ambientale
Recovery of phosphorus
Biological processes:
P-iperaccumulating
microorganisms
Recovery from ashes from
sludge inciniration:
P + N, K, P, Mg, Ca
Chemical precipitation:
Addition of Al(OH)3 /
Ca5(PO4)3OH
Struvite precipitation
Recovery alternatives
Dipartimento di Ingegneria Civile e Ambientale
Recovery of phosphorus - struvite
𝐌𝐠𝐍𝐇 𝟒 𝐏𝐎 𝟒 ∙ 𝟔𝐇 𝟐 𝐎 ∶ 𝐬𝐥𝐨𝐰 𝐫𝐞𝐥𝐞𝐚𝐬𝐞 𝐟𝐞𝐫𝐭𝐢𝐥𝐢𝐬𝐞𝐫
1 2After AD
Efficiency up to 90%
Low Purity
After S/L separation
Efficiency: 40% – 60%
High Purity
http://www.phosphorusplatform.eu/p
latform/news/1308-eu-organic-
farming-committeepositive-opinion
Dipartimento di Ingegneria Civile e Ambientale
Recovery of bioplastics (PHA)
“European Strategy for Plastics in a
Circular Economy”, 16/1/2018
(http://ec.europa.eu/environment/circula
r-economy/pdf/plastics-strategy.pdf
Carbonera WWTP – pilot demonstration
Expected increase in PHA production by 2022:
24000 tonPHA/y
(european-bioplastics.org)
Motivation
Dipartimento di Ingegneria Civile e Ambientale
San Rocco
(1.050.000 PE) Nosedo
(1.250.000 PE)
Recovery of water in agriculture
Milano WWTPS:
Tertiary treatments
120 millions m3/y (185 gg) to agriculture
Only 2% of WWTP is reused (Lautze et al., 2014)
Dipartimento di Ingegneria Civile e Ambientale
HRAP: High rate algal pond
Primary
sludge
PRIMARY
SETTLER
ACTIVATED
SLUDGE
SECONDARY
SETTLER
ANAEROBIC
DIGESTION
PRE -
TREATMENTS
INFLUENT EFFLUENT
BIOSOLIDS
Mixed sludge
Recirculation
Biogas
SOLID/LIQUID
SEPARATION
TERTIARY
TREATMENT
Secondary
sludge
New GREEN solutions: Microalgae & WWTP
Dipartimento di Ingegneria Civile e Ambientale
Microalgae
Oxygenic photosynthesis
H2O  O2
• 2.8 billons years
• Allowed aerobic organisms to develop 
Large increase in productivity
O2
Microalgae
• Mostly autotrophic/photosynthetic
• Versatile
• Biodiverse
Dipartimento di Ingegneria Civile e Ambientale
Highly productive
Combined production
Fine chemicals/goods
Biodiesel/biogas
Limited competition for soil with crop production
Allow nutrients recovery
Process
Integration WWTP, AD plants
Power stations
Microalgae - claims
Dipartimento di Ingegneria Civile e Ambientale
First applications: earlier than 1960 in California
New recent interest
«Microalgae + wastewater + treatment»
Scopus, 2017
Microalgae & WWTP
Dipartimento di Ingegneria Civile e Ambientale
Advantages of microalgae in wastewater treatment:
- Low energy cost (extensive treatment based on solar energy)
- Integration algae/bacteria
- Nutrient recovery + COD removal
- Production of algal biomass
- Other interesting effects:
 Disinfection
 Removal of micropollutants
 Removal of heavy metals
Microalgae & WWTP
Dipartimento di Ingegneria Civile e Ambientale
Water-stream - secondary treatment
 Activated sludge algae/bacteria processes
 Nutrient recovery(N, P)
• Uptake
• Conversion (CO2, N2)
Removal efficiencies
• COD: 60 – 95 %
• NH4
+: 70 – 99 %
• PO4
3-: 50 – 95 %
Primary
sludge
PRIMARY
SETTLER
ANAEROBIC
DIGESTION
PRE -
TREATMENTS
INFLUENT EFFLUENT
BIOSOLIDS
P-56
Mixed sludge
Microalgal
biomass
Biogas
SOLID/LIQUID
SEPARATION
TERTIARY
TREATMENT
PBR SOLID/LIQUID
SEPARATION
(A)
Microalgae & WWTP
Dipartimento di Ingegneria Civile e Ambientale
Primary
sludge
PRIMARY
SETTLER
ACTIVATED
SLUDGE
SECONDARY
SETTLER
ANAEROBIC
DIGESTION
PRE -
TREATMENTS
INFLUENT EFFLUENT
BIOSOLIDS
Mixed sludge
Recirculation
Biogas
SOLID/LIQUID
SEPARATION
(B/C)
PBR SOLID/LIQUID
SEPARATION
Microalgal
biomass
Secondary
sludge
Water-STREAM – tertiary treatment
 Disinfection
 Polishing
 Efficiencies (lab -scale):
• COD: 85 – 90 %
• NH4
+: 80 – 100 %
• PO4
3-: 75 – 99 %
Microalgae & WWTP
Dipartimento di Ingegneria Civile e Ambientale
Side-stream (sludge line)
Nutrient removal from the liquid fraction of digestate
 Reduction of the N and P load by uptake to the water line  savings
 Recycling of N-oxidized forms (nitrification)
 Removal efficiencies (lab/pilot scale):
• COD: 60 – 70 %
• NH4
+: 60 – 95 %
• PO4
3-: 50 – 95 %
Primary
sludge
PRIMARY
SETTLER
ACTIVATED
SLUDGE
SECONDARY
SETTLER
ANAEROBIC
DIGESTION
PRE -
TREATMENTS
INFLUENT EFFLUENT
BIOSOLIDS
P-106
Recirculation
Biogas
SOLID/LIQUID
SEPARATION
TERTIARY
TREATMENT
Secondary
sludge
PBR
(D)
Microalgal
biomass
SOLID/LIQUID
SEPARATION
Mixed sludge
Microalgae & WWTP
Dipartimento di Ingegneria Civile e Ambientale
Examples of demonstrative WWTP applying algae as a secondary treatment:
• South of Spain (Chiclana)
• California (Dehli and San Luis Obispo)
• New Zealand (Christchurch, Hamilton)
• Morocco
HARP = High Rate Algal Pond
Microalgae & WWTP
Dipartimento di Ingegneria Civile e Ambientale
Pilot plant in Chiclana
ALL GAS FP7-PROJECT (AQUALIA):
• HRAP = primary/secondary treatment
• Algal suspension: DAF floatation, AD+biogas
upgrading BioCH4
• Energy request = 0,16 kWh/m3
Energy produced = 0,17 kWh/m3
• Land request =2 m2/P.E.
Microalgae & WWTP
Dipartimento di Ingegneria Civile e Ambientale
Biofuels
Biofertilizers
Biomaterials
Nutrients
In WW
Simplified (low costs)
culturing systems
Wastewater treatment
WWTP  algae  resources
Dipartimento di Ingegneria Civile e Ambientale
Polisaccaride (Porphyridium)
PHA (cianobacteria)
PHB (Arthrospira, Sinechocystis)
Bioplastics
Algal
Biomass
Fermentation to
VFA
PHA by
iperaccumulating
bacteria
Bioflocculants
Bioplastics
WWTP  algae  biomaterials
Dipartimento di Ingegneria Civile e Ambientale
Conversion
Process
Product
Termochemical Biochemical Fisico-chemical
Gasification
Pyrolysis,
Combustion
Syngas
Electricity/heat
Fermentation
Anaerobic digestion
Methane
Hydrogen
Ethanol
alcohols
Extraction
Trans-esterification
Biodiesel
WWTP  algae  biofuels
Dipartimento di Ingegneria Civile e Ambientale
Species
Theoretical BMP
(Sialve et al. 2009)
LCH4/gVS
Cell wall
Actual BMP
(Mussgnug et al. 2010)
LCH4/gVS
Dunaliella salina 0.68 None 0.32
Chlamydomonas reinhardtii 0.69 Protein 0.39
Arthrospira platensis 0.47–0.69 Protein 0.29
Euglena gracilis 0.5–0.8 Protein 0.32
Chlorella kessleri 0.63–0.8 Polysaccharide 0.22
Scenedesmus obliquus 0.59–0.69 Polysaccharide 0.18
WWTP  algae  biogas
Dipartimento di Ingegneria Civile e Ambientale
Issues/limitations
• Low C/N ratio co-digestion
• Cell wall resistance to
biodegradation pretreatment
thermophilic digestion
• Low economic value compared to
other algae-derived products
DA integrated into a biorefinery
concept
WWTP  algae  biogas
Dipartimento di Ingegneria Civile e Ambientale
Estimated high productivity (Chisti et al., 2007)
crop Oil yield
(L ha-1)
Maize 172
Soy 446
Colza 1190
Jatropha 1892
Cocco 2689
Palma 5950
Microalgae 136.900
Microalgae 58.700
1: 70% lipids
2: 30% lipids
High lipid content:
• Special strains (Chlorella, Dunaliella, Isochrysis,
Nannochloris, Nannochloropsis, Neochloris, Nitzschia,
Phaeodactylum and Porphyridium spp.)
• Environmental growth conditions (lack in
N/stress)
Unrealistic expectations !!
More realistic values: 18.000-23000 L/ha
WWTP  algae  biodiesel
• Production costs (Norsker et al., 2011)
 1 ha  10 €/kg
 100 ha  4 €/kg
 Goal (0.40 €/kg)  combined strategies
Dipartimento di Ingegneria Civile e Ambientale
Cost reduction strategies
Biomass productivityg/m2/day 20
CO2 usage kg/kgbiomass 4
Water evaporation L/m2/day 10
Mixing power
consumption W/m3 2
Labour people/ha 0.1
Production days Days 365
Land area ha 100
Ratio V/S m3/m2 0.15
CO2 fixation
efficiency 0.45
Dilution rate 1/day 0.2
Total culture volume m3 150000
Scenario Inputs Reactor Harvesting
1Water, CO2 and fertilizers Raceway Centrifugation
2Water, CO2 and fertilizers Raceway Flocculation-Sedimentation+Centrifugation
3Free flue gases and wastewater Raceway Flocculation-Sedimentation+Centrifugation
4Free flue gases and wastewater Raceway
Flocculation-
LamellarSedimentation+Centrifugation
5Free flue gases and wastewater Raceway Flocculation-LamellarSedimentation+Filtration
6Free flue gases and wastewater Raceway Flocculation-LamellarSedimentation+Filtration
WWTP  algae  biodiesel
Dipartimento di Ingegneria Civile e Ambientale
Algal biomass as:
-Slow release fertiliser
-Natural pesticide
-biostimulants
Slow release fertilizer
Application rate similar to
conventional organic
fertilisers
6.5–10 t biomass ha−1
Algal biomass
• No phyto-toxicity
• Stimulating effects as
phyto-ormons
• Increase in germination
indexes
Luxury P uptake
 P recovery
WWTP  algae  biofertilisers
Dipartimento di Ingegneria Civile e Ambientale
1
10
100
1000
10000
Ni Cu Pb Zn
(mg/kg)
0
5
10
15
20
25
Cd
(mg/kg)
D.lgs. 99/1992 Sludge disposal Sludge Directive (in preparation)
Metal content in algal biomass
35WWTP  algae  biofertilisers
Dipartimento di Ingegneria Civile e Ambientale
First project approved in the water sector
(University of Valencia)
Sustainable wastewater treatment using innovative
anaerobic membrane bioreactors technology (AnMBR).
• Acceptable metal content
• Pathogens, micropollutants –> same levels as
for sludge
Legislation barriers
WWTP  algae  biofertilisers
Dipartimento di Ingegneria Civile e Ambientale
Conclusions
• WWTP  resources is mandatory
• Technical solutions exist
• Potential for applying microalgae-based processes
However:
• Economics: no established value chain for recovery products / lack on incentives,
lack of standard business models
• Still on-going pilot/demonstrative projects to validate techno-economic feasibility
• Regulatory barriers

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Green recovery of energy and nutrients from wastewater in the frame of the Circular Economy.

  • 1. Green recovery of energy and nutrients from wastewater in the frame of the Circular Economy ELENA FICARA POLITECNICO DI MILANO Dipartimento di Ingegneria Civile e Ambientale - Sezione ambientale
  • 2. Dipartimento di Ingegneria Civile e Ambientale Content - Introduction: general circular economy framework - Technologies for resource recovery in WWTPs - Overview on applying algae for wastewater treatment for nutrients/energy recovery/savings
  • 3. Dipartimento di Ingegneria Civile e Ambientale The role of wastewater treatment plants Challenges of sanitation systems:  Supply safe (drinking) water  Limit environmental impacts by wastewater discharges Historically… but…  Growing population,  Life style changing,  Climate change are modifying water availability and request new challenges are to be faced Uptake Use discharge
  • 4. Dipartimento di Ingegneria Civile e Ambientale The circular approach …. Water, energy, resources Water source treatment Reuse treatment discharge New hierarchy use
  • 5. Dipartimento di Ingegneria Civile e Ambientale The circular approach ….
  • 6. Dipartimento di Ingegneria Civile e Ambientale Looking beyond the current "take, make and dispose” extractive industrial model, the circular economy is restorative and regenerative by design.
  • 7. Dipartimento di Ingegneria Civile e Ambientale Which kind of resources to be recovered? Biodegradable organics: 12 – 14 W/PE Total organics: 18 – 20 W/PE Ammoniacal N: 8 W/PE TOTAL: 20 – 28 W/PE (4-5 times energy required for WW treatment) Clean water Chemical energy Nutrients (N, P) Wastewater 40-70 m3/PE/y 2-3 kg N/PE/y 0,5-1 kg P/PE/y = WWTP  WRRP Water Resource Recovery Platform
  • 8. Dipartimento di Ingegneria Civile e Ambientale Energy request for the water sanitation o 10-17 W/PE o 90-150 kWh/PE/y • Reducing water consumption • Optimizing processes • Recovering energy from wastewater 2-3% of electric energy consumption up to 7% (in EU and USA) How to save energy? In Italy: Total consumption 7500 GWh/y (2,5% national electric energy consumption) Campanelli, Foladori, Vaccari (2013) •water supply 57% •water treatment 43%
  • 9. Dipartimento di Ingegneria Civile e Ambientale Energy recovery from wastewater Thermal: Wastewater temperature: 14 - 23°C. Heat pumps to warm (winter) or cool (summer) buildings. e.g.: Nosedo (Milano) WWTP recovers 200 kW Hydro-electric: by taking advantages of head loss e.g.: Folgaria (TN) WWTP recovers 40 kW (50 L/s for 236 m) Chemical energy: typically recovered from the sludge line In Italy: today 121 GWh/y from AD of waste sludge (GSE, 2014) Potential: 2100 GWh/y (= all plants with tertiary treatments would use conventional AD)
  • 10. Dipartimento di Ingegneria Civile e Ambientale Energy positive WWTP: utopic? • Recover energy with effective AD • Optimizing energy intensive processes New pathways in biological treatment Optimization of existing treatment e.g.: Aeration systems Optimized processes Energy consumption P.E. served WWTP of Strauss (Austria) 250 000 P.E. Energy cost for treatment: 11.3 kWh/PE/y, offset by biogas production
  • 11. Dipartimento di Ingegneria Civile e Ambientale Recovery of phosphorus Accessible stocks of P-rocks are going to be exhausted SOON Use Wastes Agriculture Plants P mining Water bodies (WWTP)  P is fundamental in sustaining agriculture  Demand is growing together with word population  Uneven distribution of P mines (Morocco, Cina, US)  EU is P deficient About 18% of the P request could be recovered from waste streams Cordell & White, 2011, Sustainability, 3(10), pp. 2027-2049
  • 12. Dipartimento di Ingegneria Civile e Ambientale Recovery of phosphorus Biological processes: P-iperaccumulating microorganisms Recovery from ashes from sludge inciniration: P + N, K, P, Mg, Ca Chemical precipitation: Addition of Al(OH)3 / Ca5(PO4)3OH Struvite precipitation Recovery alternatives
  • 13. Dipartimento di Ingegneria Civile e Ambientale Recovery of phosphorus - struvite 𝐌𝐠𝐍𝐇 𝟒 𝐏𝐎 𝟒 ∙ 𝟔𝐇 𝟐 𝐎 ∶ 𝐬𝐥𝐨𝐰 𝐫𝐞𝐥𝐞𝐚𝐬𝐞 𝐟𝐞𝐫𝐭𝐢𝐥𝐢𝐬𝐞𝐫 1 2After AD Efficiency up to 90% Low Purity After S/L separation Efficiency: 40% – 60% High Purity http://www.phosphorusplatform.eu/p latform/news/1308-eu-organic- farming-committeepositive-opinion
  • 14. Dipartimento di Ingegneria Civile e Ambientale Recovery of bioplastics (PHA) “European Strategy for Plastics in a Circular Economy”, 16/1/2018 (http://ec.europa.eu/environment/circula r-economy/pdf/plastics-strategy.pdf Carbonera WWTP – pilot demonstration Expected increase in PHA production by 2022: 24000 tonPHA/y (european-bioplastics.org) Motivation
  • 15. Dipartimento di Ingegneria Civile e Ambientale San Rocco (1.050.000 PE) Nosedo (1.250.000 PE) Recovery of water in agriculture Milano WWTPS: Tertiary treatments 120 millions m3/y (185 gg) to agriculture Only 2% of WWTP is reused (Lautze et al., 2014)
  • 16. Dipartimento di Ingegneria Civile e Ambientale HRAP: High rate algal pond Primary sludge PRIMARY SETTLER ACTIVATED SLUDGE SECONDARY SETTLER ANAEROBIC DIGESTION PRE - TREATMENTS INFLUENT EFFLUENT BIOSOLIDS Mixed sludge Recirculation Biogas SOLID/LIQUID SEPARATION TERTIARY TREATMENT Secondary sludge New GREEN solutions: Microalgae & WWTP
  • 17. Dipartimento di Ingegneria Civile e Ambientale Microalgae Oxygenic photosynthesis H2O  O2 • 2.8 billons years • Allowed aerobic organisms to develop  Large increase in productivity O2 Microalgae • Mostly autotrophic/photosynthetic • Versatile • Biodiverse
  • 18. Dipartimento di Ingegneria Civile e Ambientale Highly productive Combined production Fine chemicals/goods Biodiesel/biogas Limited competition for soil with crop production Allow nutrients recovery Process Integration WWTP, AD plants Power stations Microalgae - claims
  • 19. Dipartimento di Ingegneria Civile e Ambientale First applications: earlier than 1960 in California New recent interest «Microalgae + wastewater + treatment» Scopus, 2017 Microalgae & WWTP
  • 20. Dipartimento di Ingegneria Civile e Ambientale Advantages of microalgae in wastewater treatment: - Low energy cost (extensive treatment based on solar energy) - Integration algae/bacteria - Nutrient recovery + COD removal - Production of algal biomass - Other interesting effects:  Disinfection  Removal of micropollutants  Removal of heavy metals Microalgae & WWTP
  • 21. Dipartimento di Ingegneria Civile e Ambientale Water-stream - secondary treatment  Activated sludge algae/bacteria processes  Nutrient recovery(N, P) • Uptake • Conversion (CO2, N2) Removal efficiencies • COD: 60 – 95 % • NH4 +: 70 – 99 % • PO4 3-: 50 – 95 % Primary sludge PRIMARY SETTLER ANAEROBIC DIGESTION PRE - TREATMENTS INFLUENT EFFLUENT BIOSOLIDS P-56 Mixed sludge Microalgal biomass Biogas SOLID/LIQUID SEPARATION TERTIARY TREATMENT PBR SOLID/LIQUID SEPARATION (A) Microalgae & WWTP
  • 22. Dipartimento di Ingegneria Civile e Ambientale Primary sludge PRIMARY SETTLER ACTIVATED SLUDGE SECONDARY SETTLER ANAEROBIC DIGESTION PRE - TREATMENTS INFLUENT EFFLUENT BIOSOLIDS Mixed sludge Recirculation Biogas SOLID/LIQUID SEPARATION (B/C) PBR SOLID/LIQUID SEPARATION Microalgal biomass Secondary sludge Water-STREAM – tertiary treatment  Disinfection  Polishing  Efficiencies (lab -scale): • COD: 85 – 90 % • NH4 +: 80 – 100 % • PO4 3-: 75 – 99 % Microalgae & WWTP
  • 23. Dipartimento di Ingegneria Civile e Ambientale Side-stream (sludge line) Nutrient removal from the liquid fraction of digestate  Reduction of the N and P load by uptake to the water line  savings  Recycling of N-oxidized forms (nitrification)  Removal efficiencies (lab/pilot scale): • COD: 60 – 70 % • NH4 +: 60 – 95 % • PO4 3-: 50 – 95 % Primary sludge PRIMARY SETTLER ACTIVATED SLUDGE SECONDARY SETTLER ANAEROBIC DIGESTION PRE - TREATMENTS INFLUENT EFFLUENT BIOSOLIDS P-106 Recirculation Biogas SOLID/LIQUID SEPARATION TERTIARY TREATMENT Secondary sludge PBR (D) Microalgal biomass SOLID/LIQUID SEPARATION Mixed sludge Microalgae & WWTP
  • 24. Dipartimento di Ingegneria Civile e Ambientale Examples of demonstrative WWTP applying algae as a secondary treatment: • South of Spain (Chiclana) • California (Dehli and San Luis Obispo) • New Zealand (Christchurch, Hamilton) • Morocco HARP = High Rate Algal Pond Microalgae & WWTP
  • 25. Dipartimento di Ingegneria Civile e Ambientale Pilot plant in Chiclana ALL GAS FP7-PROJECT (AQUALIA): • HRAP = primary/secondary treatment • Algal suspension: DAF floatation, AD+biogas upgrading BioCH4 • Energy request = 0,16 kWh/m3 Energy produced = 0,17 kWh/m3 • Land request =2 m2/P.E. Microalgae & WWTP
  • 26. Dipartimento di Ingegneria Civile e Ambientale Biofuels Biofertilizers Biomaterials Nutrients In WW Simplified (low costs) culturing systems Wastewater treatment WWTP  algae  resources
  • 27. Dipartimento di Ingegneria Civile e Ambientale Polisaccaride (Porphyridium) PHA (cianobacteria) PHB (Arthrospira, Sinechocystis) Bioplastics Algal Biomass Fermentation to VFA PHA by iperaccumulating bacteria Bioflocculants Bioplastics WWTP  algae  biomaterials
  • 28. Dipartimento di Ingegneria Civile e Ambientale Conversion Process Product Termochemical Biochemical Fisico-chemical Gasification Pyrolysis, Combustion Syngas Electricity/heat Fermentation Anaerobic digestion Methane Hydrogen Ethanol alcohols Extraction Trans-esterification Biodiesel WWTP  algae  biofuels
  • 29. Dipartimento di Ingegneria Civile e Ambientale Species Theoretical BMP (Sialve et al. 2009) LCH4/gVS Cell wall Actual BMP (Mussgnug et al. 2010) LCH4/gVS Dunaliella salina 0.68 None 0.32 Chlamydomonas reinhardtii 0.69 Protein 0.39 Arthrospira platensis 0.47–0.69 Protein 0.29 Euglena gracilis 0.5–0.8 Protein 0.32 Chlorella kessleri 0.63–0.8 Polysaccharide 0.22 Scenedesmus obliquus 0.59–0.69 Polysaccharide 0.18 WWTP  algae  biogas
  • 30. Dipartimento di Ingegneria Civile e Ambientale Issues/limitations • Low C/N ratio co-digestion • Cell wall resistance to biodegradation pretreatment thermophilic digestion • Low economic value compared to other algae-derived products DA integrated into a biorefinery concept WWTP  algae  biogas
  • 31. Dipartimento di Ingegneria Civile e Ambientale Estimated high productivity (Chisti et al., 2007) crop Oil yield (L ha-1) Maize 172 Soy 446 Colza 1190 Jatropha 1892 Cocco 2689 Palma 5950 Microalgae 136.900 Microalgae 58.700 1: 70% lipids 2: 30% lipids High lipid content: • Special strains (Chlorella, Dunaliella, Isochrysis, Nannochloris, Nannochloropsis, Neochloris, Nitzschia, Phaeodactylum and Porphyridium spp.) • Environmental growth conditions (lack in N/stress) Unrealistic expectations !! More realistic values: 18.000-23000 L/ha WWTP  algae  biodiesel • Production costs (Norsker et al., 2011)  1 ha  10 €/kg  100 ha  4 €/kg  Goal (0.40 €/kg)  combined strategies
  • 32. Dipartimento di Ingegneria Civile e Ambientale Cost reduction strategies Biomass productivityg/m2/day 20 CO2 usage kg/kgbiomass 4 Water evaporation L/m2/day 10 Mixing power consumption W/m3 2 Labour people/ha 0.1 Production days Days 365 Land area ha 100 Ratio V/S m3/m2 0.15 CO2 fixation efficiency 0.45 Dilution rate 1/day 0.2 Total culture volume m3 150000 Scenario Inputs Reactor Harvesting 1Water, CO2 and fertilizers Raceway Centrifugation 2Water, CO2 and fertilizers Raceway Flocculation-Sedimentation+Centrifugation 3Free flue gases and wastewater Raceway Flocculation-Sedimentation+Centrifugation 4Free flue gases and wastewater Raceway Flocculation- LamellarSedimentation+Centrifugation 5Free flue gases and wastewater Raceway Flocculation-LamellarSedimentation+Filtration 6Free flue gases and wastewater Raceway Flocculation-LamellarSedimentation+Filtration WWTP  algae  biodiesel
  • 33. Dipartimento di Ingegneria Civile e Ambientale Algal biomass as: -Slow release fertiliser -Natural pesticide -biostimulants Slow release fertilizer Application rate similar to conventional organic fertilisers 6.5–10 t biomass ha−1 Algal biomass • No phyto-toxicity • Stimulating effects as phyto-ormons • Increase in germination indexes Luxury P uptake  P recovery WWTP  algae  biofertilisers
  • 34. Dipartimento di Ingegneria Civile e Ambientale 1 10 100 1000 10000 Ni Cu Pb Zn (mg/kg) 0 5 10 15 20 25 Cd (mg/kg) D.lgs. 99/1992 Sludge disposal Sludge Directive (in preparation) Metal content in algal biomass 35WWTP  algae  biofertilisers
  • 35. Dipartimento di Ingegneria Civile e Ambientale First project approved in the water sector (University of Valencia) Sustainable wastewater treatment using innovative anaerobic membrane bioreactors technology (AnMBR). • Acceptable metal content • Pathogens, micropollutants –> same levels as for sludge Legislation barriers WWTP  algae  biofertilisers
  • 36. Dipartimento di Ingegneria Civile e Ambientale Conclusions • WWTP  resources is mandatory • Technical solutions exist • Potential for applying microalgae-based processes However: • Economics: no established value chain for recovery products / lack on incentives, lack of standard business models • Still on-going pilot/demonstrative projects to validate techno-economic feasibility • Regulatory barriers

Editor's Notes

  1. Le nuove sfide  Gerarchia di gestione: Ridurre i prelievi (ottimizzare, ridurre consumi, educare) Recuperare e riciclare l’acqua usata e ciò che contiene Recuperare energia / ridurre i costi energetici dei trattamenti
  2. Nel corso dell’anno 2013 è entrata in esercizio la centralina idroelettrica realizzata sfruttando il dislivello di circa 260 m che separa il depuratore dal rio Cavallo, accettore finale dello scarico; la condotta forzata in ghisa, si sviluppa per 642 m ed alimenta la centrale di produzione realizzata sulla sponda destra del rio Cavallo, costituita da una macchina a turbina della potenza di 50 kW e potenza massima di 106 kW. La produzione registrata nel mese di agosto 2013 (primo mese di funzionamento) è stata mediamente di 800 kWh/giorno; da questo impianto ci si attende una produzione annua di circa 260.000 kWh/anno. L’energia prodotta viene autoconsumata o immessa in rete a seconda del fabbisogno del depuratore. L’impianto idroelettrico è stato progettato da SWS engineering, il costo dell’opera ammonta a circa 490.000 euro Iva esclusa. I lavori sono stati realizzati dall’A.T.I. fra Tecnoimpianti Paternoster e Elettreteam. Le azioni combinate di efficientamento energetico e di autoproduzione di energia elettrica da fonte rinnovabile hanno portato il bilancio complessivo annuale del depuratore ad un completo autosostentamento: la somma dell’energia derivante dal fotovoltaico pari a 85.000 kWh/anno e dall’idroelettrico pari a 260.000 kWh/anno, equivale infatti al fabbisogno medio annuo di 340.000 kWh/anno; secondo le attuali proiezioni della produzione di energia e del consumo dell’impianto, ci si attende addirittura un bilancio in positivo, con un surplus di energia prodotta rispetto a quella consumata.
  3. Controllo aerazione Diffusori efficienti Sistema fanghi attivi a 2 stadi Anammox sul side stream Preispessimento Motore CHP(38% invece di 33) http://www.ewmce.com/Resources/Documents/A%20Case%20Study%20-%20Net%20Energy%20Positive%20WWTP%20near%20Innusbruck,%20Austria%20-%20G%20Crawford.pdf alta efficienza
  4. San Rocco + Nosedo 90% del carico trattato
  5. Non sono seguite significative alter realizzazioni se non recentemente grazie ad una sostanziale modifica nella modalità con cui si guarda all’impianto di depurazione che oggi, oltre a garantire la necessaria protezione sanitaria ed ambientale deve essere concepito come una piattaforma per il recupero delle risorse ed in particolare di acqua, nutrienti ed enegia ,in un ottica di uso ottimale delle risorse e di economia circolare
  6. I fattori che rendono le microalghe interessanti in questo nuovo contest li trovate qui elencati e sono