A Perspective on Algae Biogas - About Task 37 - IEA...
Transcript of A Perspective on Algae Biogas - About Task 37 - IEA...
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A Perspective on Algae Biogas
Jerry D Murphy, Bernhard Drosg, Eoin Allen, Jacqueline Jerney, Ao Xia, Christiane HerrmannInternational Energy Agency Bioenergy Conference
Berlin, Germany27 & 28 October 2015
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Energy is not all about electricity
•The share of biofuels from cereal and other starch rich crops, sugar and oil crops limited to7% as of April 2015.
•Biofuels (from (1) grasses (2) algae, municipal solid waste, manures and residues) and (3)gaseous fuels from non biological origin shall be considered at 2 times energy content.
•Also require Green Energy in Industry (FDI) and heating
Directive 2009/28/EC(Renewable Energy Directive)
•Share of renewable energy sources intransport (RES-T) by 2020 at least 10%
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Green (Renewable) Gas
6 European gas gridshave committed to100% green gas in thegas grid by 2050
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GreGreen Gas in Ireland
Major demand for Green Gas is FDI..Factories of the future will use green gas
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Renewable Gas from marine sources
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Seaweed as a source of renewable gas
(3) Co-digestion
Slurry Straw Sugar beets Grass silageSeaweed +
(5) Optimal operating parameters for long-term continuous operation
Organicloading rate
Hydraulicretention time
Recirculationof digestate
(2) Pre-treatment and storage
Washing /wilting
Mechanicalpretreatment
Thermalpretreatment
Thermochemicalpretreatment
Ensiling
(1) Selection of feedstock
Seaweed species Harvest date
(4) Comparison of biogas production systems
Combined Biomethane &Biohydrogen production
MicrobialEcology
Biomethaneproduction
Biohydrogenproduction
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Algal blooms: Green seaweed, Ulva lactuca
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Green Seaweed
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10,000 t DS/a arise in Argideen,
Sufficient to power 265 cars
100,000 t DS/a arise in Lannion Bay, Brittany
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Substrate BMP yield(L CH4 kg-1
VS)
C:N ratio Increasedyield in co-digestion
Slurry 136 19.8
Dried U.lactuca 226 7.1
Fresh U.lactuca 205 9.1
Co-digestion of U. lactuca:
75% Fresh 220 11.8 + 17.0%
50% Fresh 200 14.5 + 17.0%
25% Fresh 183 17.1 + 19.6%
75% Dried 210 10.3 + 3.4%
50% Dried 193 13.5 + 6.7%
25% Dried 186 16.6 + 17.7%
Batch mono- and co-digestion of seaweedwith slurry
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Co-digestion of fresh and dried U. lactuca with dairy slurry in BMP tests: ratio of 25%, 50% and 75% seaweed (VS)
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R1 R2 R3 R4
Higher Seaweed Input
Higher Dairy Slurry Input
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Long term co-digestion of Seaweed & Slurry
optimum mix: 25% fresh U. lactuca and 75% dairy slurry by VS content levels in excess of 75% U. lactuca are not recommended optimum loading rate: 2.5 kg VS m-3 d-1
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Taxonomy of Ulva Digesters
Commonstarting point:
sharedinoculum
High-Ulva Reactor: higher diversity;many marine-assoc. species; vanishingmethanogens; ‘dominating’ species
Low-Ulva Reactor: large methanogen
population (10-25%) converting aceticacid; species evenly distributed
Alan DW Dobson; Jamie A Fitzgerald; Eoin Allen; David M Wall; Stephen A Jackson; Jerry D Murphy (2015)Methanosarcina play an important role in Anaerobic co-digestion of the Seaweed Ulva lactuca: Metagenomicsstructure and predicted metabolism of functional microbial communities. PLOS ONE (submitted August 2015).
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Energy Yield of brown seaweeds
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Brown Seaweed in Roaring Water Bay
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Specific methane yields of Seaweed
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Energy yield per hectare of Seaweed
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Seasonal variation in chemical composition (L. digitata)
CSTRs
Proximate Analysis Ultimate Analysis
MC % TS % VS % VS% TS Ash % C % H % N % O % C:N
January 89 11 7 61 39 26 3 4 28 7
February 89 11 7 64 36 26 4 4 30 7
March 90 10 6 67 33 30 4 4 29 8
April 86 14 9 65 35 30 4 2 28 13
May 88 12 9 73 28 32 5 2 33 15
June 86 14 10 73 27 34 5 2 32 19
July 86 14 11 77 24 33 5 2 37 22
August 80 20 16 82 18 37 6 1 38 32
September 81 19 16 82 19 37 5 1 39 40
October 84 16 12 76 25 33 5 1 37 27
November 85 15 11 75 25 37 5 2 32 24
December 92 8 5 60 38 31 4 3 21 9
Muhammad, R.T., Ao, X., Murphy, J.D. (2015). Seasonal variation and biomethanepotential of Irish brown seaweeds, Bioresource Technology to be submitted Nov,2015
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35 28 27 2418
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Seasonal variation in biochemical compositionL. digitata
Carbo. Protein others Ash C/N
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April May June July August September October November December
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[LC
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kgV
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JACOB, A., XIA, A., GUNNING, D., BURNELL, G., MURPHY, J.D., Is it beneficial to associate a seaweed biofuelindustry with Integrated Multi-trophic Aquaculture? International Conference on Environmental Science andDevelopment (submitted)
Aquaculture contributed 24 million tonnes of algae in 2012
Aquaculture contributed 66.6 million tonnes of fish in 2012, 42 % of global production.
Carbon footprint is 10 times less than for beef per unit of energy in food
Integrated multi-trophic aquaculture can reduce pollution through co-culture ofseaweed and mussels that utilise waste disposed from fish.
A model is investigated which would provide 1.25% of energy in transport in the EUfrom seaweed. This would involve annual production of 168Mt of seaweed (in excess ofpresent world harvest) integrated with 13Mt of farmed salmon.
The model proposes 2603 anaerobic digesters, each treating 64,500 t/a of Saccharinalatissima in coastal digesters
Integrated Multi-trophicaquaculture
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Cultivating Seaweed
Position adjacent to fish farmsIncreased yields of seaweed as compared to pristine watersClean water of excess nutrientsHarvest when yield is highest
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Ensiling of seaweed- Background
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Ensiling of seaweed
Experimental approach:
o Ensiling of 5 seaweed species: U. lactuca, A. nodosum, L. digitata, S. polyschides, S. latissima
o Ensiling in 1-Litre lab scale silos, collection of silage effluent
o Time course experiments: storage duration 2, 4, 7, 14, 90 days at 20°C
o Analyses of ensilability, products of silage fermentation, counts of lactic acid bacteria, biomethanepotential
Fig.: Ensiling of seaweed
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Ensiling of seaweed- Results
goodpoor
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Ensiling of macro-algae - Results
Gaseous storage losses 0.3 – 19% after 90 days of storage, dependent on seaweed species
Large amounts of effluent released – up to 28% of the ensiled biomass (FM) after 90 days of storage
goodpoor
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Ensiling of seaweed - Results
Seaweed species Storage BMP yield(L kg-1 VSadded)
BMP yield(L kg-1 VSorig)
U. lactuca Fresh 247.2gh 247.2c
Silage 314.1de 255.8cd
Effluent 220.3hi
A. nodosum Fresh 185.7i 185.7e
Silage 239.3gh 236.7d
Effluent 218.3hi
L. digitata Fresh 340.8bcd 340.8ab
Silage 371.4b 353.8ab
Effluent 376.1b
S. polyschides Fresh 358.8bc 358.8a
Silage 294.9ef 276.8c
Effluent 273.1fg
S. latissima Fresh 329.5cde 329.5b
Silage 353.4bc 329.8b
Effluent 422.5a
No losses in methane yield occurredduring 90 day storage for 4 of 5 seaweedspecies
Collection and use of silage effluent isimperative to avoid methane losses
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A perspective on algal biomassOkt. 2015 29
Microalgal biogas
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A perspective on algal biomass
What are microalgae?
… are the precursors of higher land plants
… the main reason for present oxygen levels in the atmosphere
… due to oxygenic photosynthesis
… extremely diverse group
Okt. 2015 30
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A perspective on algal biomass
Common strains
Chlorella sp. Scenedesmus sp.
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A perspective on algal biomass
Cultivation systems
Okt. 2015 32
Open systems Closed systems
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A perspective on algal biomassOkt. 2015 33
Parameters
Temperature
Light
pH-value
Conductivity
Mixing
Pathogens
Predation
Cell density
Relevant abiotic (filledspheres) and biotic(empty spheres)parameters formicroalgae cultivation
Challenges in cultivation:PhotoinhibitionPhotolimitationOxygeninhibition
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A perspective on algal biomass
Estimated world algae biomass production
Source: Benemann, 2013, Microalgae for biofuels and animal feeds. Energies,6(11), 5869-5886.
Algae Production (t drymatter/year)
Spirulina 10,000
Chlorella 4,000
Dunaliella 1,000
Haematococcus 200
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A perspective on algal biomassOkt. 2015 35
Micro-algae Main ProducersApplication andproduct
Price [€]
Spirulina sp. China, India, USA,Myanmar, Japan
Human nutritionAnimal nutritionCosmetics
36 kg-1
Chlorella sp. Taiwan, Germany,Japan
Human nutritionCosmetics
36 kg-1
Aquaculture 50 L -1
Dunaliella salina Australia, Israel,USA, Japan
Human nutritionCosmeticsß-carotene
215 - 2150kg-1
Aphanizomenon flos-aquae
USA Human nutrition
Haematococcus pluvialis USA, India, Israel Aquaculture 50 L -1
Astaxanthin 7150 kg-1
Current Market prices of algal biomass
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A perspective on algal biomass
Pharmaceutical products
Cosmetics
Food additives
Feed additives
Chemicals
Bulk chemicals
Energy
Current algae markets
Okt. 2015 36 36
Marketvalue
Marketvolume
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A perspective on algal biomass
Biogas as conversion technology
Advantages:
No pure cultures necessary(cheaper production)
No specific product needs tobe produced (e.g. Triglyceridesin biodiesel
Suitable as well for entire algalbiomass or residue afterextraction of high value product
Disadvantages:
Some algae have thick cellwalls (especially robust strains) pretreatment necessary
High protein content can leadto ammonia inhibition
dilution
37 16.05.2013
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A perspective on algal biomass
Pretreatment of microalgae
Chlorella vulgaris before (left) and after (right) ultrasound pre-treatment
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A perspective on algal biomass
A more probable approach –The microalgae biorefinery
Okt. 2015 39
Residues of microalgae are treated in a biogas plant
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A perspective on algal biomass
Further synergies of microalgaeand biogas
Digestate utilisation
Digestate from biogas plants is suitable as nutrient media for algae(at least for some strains)
Utilisation of CO2
Flue gas from combustion of biogas has a comparable high CO2-content
CO2-rich offgas from biogas upgrading
Utilisation of waste heat
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A perspective on algal biomass
Use of micro-algae to upgrade biogas
Niche applications such as use of micro-algae to biogas upgrading
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A perspective on algal biomass
Conclusions
Seaweed biogas
Cast seaweed has significant potential if considered unpleasant.
Digest residues associated with extraction of products from seaweed.
Cultivation may be advantagous if combined with fish farms forimprovement of marine environments.
Micro-algal biogas
Large scale capture of carbon from fossil fuel power plants isunrealistic at present; the technology requires very high carbon fines
Innovative applications associated with bioenergy systems
Optimum systems will involve cascading biorefinerys
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Coastal biogas production and offshore biogas upgrading system
Coastal biogas production
Offshore capture of CO2 and wastewater treatment
Microalgae
Seaweed associatedwith salmon farms
Offshore Membrane Enclosures for Growing Algae (OMEGA) system, http://www.nasa.gov/centers/ames/research/OMEGA/index.html
Surplus agri-biomass
CO2
O2
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A perspective on algal biomassOkt. 2015 44
BOKU - University of Natural Resourcesand Life Sciences. Vienna
Department for Agrobiotechnology. IFA-TullnInstitute for Environmental Biotechnology
DI Dr Bernhard Drosg
Konrad Lorenz Straße 20. A-3430 TullnTel.: +43 2272 66280-537. Fax: +43 1 2272 [email protected] . www.boku.ac.at. www.ifa-tulln.ac.at
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Prof Jerry D Murphy ([email protected])
Interim Director MaREI, Vice Director ERI,
IEA Task 37 “Energy from Biogas” Leader (2016 – 2018)