| ||Background | Manure/energy production | Co-digestion biogas energy potential |
A viable anaerobic digestion system to process organic wastes can be costly, so producers who are considering adopting this type of technology need to examine all aspects of it. One key aspect to consider is the economic feasibility of anaerobic digesters.
This factsheet provides a fairly high level, theoretical approach to exploring the costs of the technology. Data is provided in the form of tables as well as through examples that are useful to determine the economic feasibility of adopting an anaerobic digester/biogas plant for agricultural operations. The numbers used in the tables are drawn from existing resources that are listed in the references section at the end of the factsheet.
- background information
- manure/energy production
- co-digestion biogas energy potential
- examples: co-digestion of dairy manure and animal fat, estimation of capital cost and simple payback period
Alberta has many agricultural operations that generate various types of organic wastes. These organic wastes require proper handling to reduce pollution and contamination.
Using anaerobic digesters to process these organic wastes appears to be an attractive option since the anaerobic digestion process can stabilize most agricultural, domestic and industrial organic wastes and produce biogas, a renewable energy. Biogas can be used as a fuel source to produce electricity and heat, just like natural gas.
The total capital costs of anaerobic digester plants are high and may range from a few hundred thousand to a few million dollars. However, most of the other waste processing technologies, which may also require a high capital investment, do not generate revenue like a biogas digester plant does.
Some of the feasibility studies in North America on anaerobic digesters concluded that the payback period ranges from 5 to 16 years when operated under optimum and worst conditions, respectively. Government financial incentives for producing green energy can potentially reduce the payback period significantly.
Table 1 contains data for daily manure and biogas production as well as the annual electricity and heat generation potential for the major livestock operations such as beef, dairy, swine and poultry. Table1 provides the data that will help agricultural producers estimate potential approximate annual revenue.
Table 1. Manure/energy estimation
* Multiply the values by 12 for every sow in a farrow-to-finish operation.
Manure quantity as excreted (kg/d)
Biogas production (m3/d)
Electricity potential (kW)/year
Energy potential (GJ)/year
|Poultry (100 - layer)|
Multiplying the amount of annual electricity and heat energy potentials in Table 1 by average electricity and heating costs provides the approximate annual energy revenue from anaerobic processing of manure as shown in Example 1.
|Number of animals||=||100 dairy cows|
|Average cost of electricity||=||$0.06/ kWh|
|Average cost of heat||=||$5.5/GJ|
|Annual electricity potential||=||1,227 kWh (from Table1)|
|Annual heating potential||=||5.5 GJ (from Table 2)|
|Savings from electricity||=||100 x 0.06 x 1,227 = $7,362|
|Savings from gas||=||100 x 5.5 x 5.5 = $3,025|
|Total annual savings from energy||=||$10,387 |
Co-Digestion Biogas Energy Potential
Table 2 and Table 3 contain the ranges provided in the literature for total solids, volatile solids and biogas yield (m3/tonne) and estimated total annual biomass production (tonnes) and energy potential (PJ) across the province. The purpose of these tables is to provide the total biogas energy potential in the province as well as to estimate the biogas energy potential for centralized digesters.
To assist in exploring the potential to locate centralized, manure-based biogas facilities, producers should check the following website for information on the relative amount of manure production in Alberta: http://www1.agric.gov.ab.ca/$department/deptdocs.nsf/all/agdex10335
Table 2. Inventory of livestock and municipal feedstock materials and biogas energy potential in Alberta
Note: 1 PJ is 1,000,000 GJ. 1 GJ is 1000 MJ.
|Feed material||Total solids %||Volatile solids % of total solids||Biogas yield |
|Yearly biomass production in tonnes*||Yearly energy potential in PJ||Methanecontent %|
|Beef cattle manure||8-12||80 - 85 ||19 - 46 ||51,890,736||20.0 - 48.0||53|
|Hog manure-grower to finisher||9-11||80 - 85 ||28 - 46 ||2,452,800||1.4 - 2.3||58|
|Dairy manure||12||80 - 85 ||25 - 32 ||3,994,195||2.0 - 2.6||54|
|Poultry manure||25 - 27 ||70 - 80 ||69 - 96 ||1,728,987||2.4 - 3.3||60|
|Animal fat||89 - 90 ||90 - 93 ||801 - 837 ||87,000||1.4 - 1.5||N/A|
|Animal carcass (homogenized-bovine)||34 - 39 ||90 - 93 ||348 - 413 ||264,023||1.8 - 1.2||N/A|
|Municipal wastewater sludge||30-20||90||17 - 140 ||539,835||0.2 - 1.5||65|
|Household waste||N/A||N/A||143 - 214 ||N/A||N/A||N/A|
|Total manure (including municipal sludge)||–||–||–||60,606,553||25.7 - 57.4||50 - 70|
Table 3. Inventory of agricultural crops and biogas energy potential in Alberta
* In this estimation, the requirement of cattle straw and soil conditioning was taken into consideration.
|Feed material||Total solids %||Volatile solids % of total solids||Biogas yield m3/tonne||Yearly biomass production in dry tonnes*||Yearly energy potential in PJ||Methanecontent %|
|Barley||36 - 86 ||90 - 95 ||169 - 291 ||1,404,671||4.75 - 8.18||60 - 70|
|Wheat||32 - 97 ||N/A||48 - 146 ||1,390,222||1.33 - 4.106||N/A|
|Oats||64||68||147 - 187 ||172,085||0.51 - 0.64||49 - 57|
|Rye||25 - 61 ||91 - 95 ||112 - 457 ||4,423||0.00 - 0.04||N/A|
|Triticale||27 - 66 ||93 - 97 ||150 - 554 ||9,526||0.03 - 0.11||60 - 70|
|Sugar beet leaves||N/A||N/A||40 - 50 ||197,887||0.16 - 0.20||49 - 57|
|Fodder corn||25 - 37||95||182 – 436||89,674||0.33 - 0.78|
|Leaves||80||90||72 - 216 ||N/A||N/A||N/A|
|Whey||1-5||80 - 95 ||6-45||N/A||N/A|
|Grass silage||20 - 25 ||90||75 - 126 ||N/A||N/A||N/A|
|Distiller grain wastewater||N/A||N/A||58||N/A||N/A||57 - 60|
|Total straw and other roughages||70||90||105 - 158 ||3,901,007||8.19 - 12.33||60 - 70|
Example 2 – Co digestion of dairy manure and animal fat
Multiplying the corresponding biogas yield in Table 2 or 3 by the tonnes of available feed stock provides the total biogas potential in m3. One cubic meter of biogas is equivalent to 20 MJ of heat energy. When used as fuel for a co-generator, 1 m3 of biogas can produce 1.7 kWh of electricity and 7.7 MJ of heat. Multiplying the total biogas potential in m3 by 1.7 and 7.7 provides total electricity and heat energy potentials, respectively, as shown in Example 2.
|Number of animals||=||100 dairy cows|
|Amount of animal fat available||=||250 tonnes/year|
|Biogas potential for animal fat||=||801 m3/tonne (Table 2)|
|Biogas potential for 1,000 tonnes||=||250 x 801 = 200,250|
|Electricity produced from 1 m3 of biogas in a co-generator||=||1.7 kWh|
|Excess heat available from 1 m3 of biogas after producing electricity||=||7.7 MJ|
|Electricity produced from 200,250 m3 of biogas||=||200,250 x 1.7 = 340,425 kWh|
|Heat available from 200,250 m3 of biogas ||=||200,250x 7.7= 1,541,925 MJ=1,541.9 GJ|
|Electricity production from 100 dairy cows ||=||1,227 x 100= 122,700 kWh (Example 1)|
|Heat production from 100 dairy cows||=||5.5 x 100= 550 GJ (Example 1)|
|Total electricity production from dairy manure and animal fat||=||340,425 +122,700= 463,125 kWh|
|Total heat production from dairy manure and animal fat||=||1,541.9 + 550 =2,091.9 GJ|
|Average cost of electricity||=||$0.06/ kWh|
|Average cost of heat||=||$5.5/GJ|
|Savings from electricity||=||0.06 x 463,125 = $27,787.50|
|Savings from gas||=||5.5 x 2,091.9 = $11,505.45|
|Total annual savings from energy or the energy potential for exporting into the grid||=||$27,787.5 + $11,505.45 = $39,292.95|
Example 3 – Approximate estimation of capital cost
Typically, the capital costs of a biogas electricity generating plant are $3,700 to $7,000/kWh. Example 3 illustrates how to estimate the approximate capital cost assuming a period of 30 days/year as a shutdown period for maintenance.
Even though it is possible to produce biogas energy continuously, as assumed in the examples, some experiences in North America show frequent interruption of operation due to unforeseen maintenance and process related issues. These types of interruptions may prolong the payback period. Unfortunately, in some worst case scenarios, there will not be any payback.
|Total electricity production from dairy manure and animal fat from Example 2||=||340,425 + 122,700 = 463,125 kWh|
|Assuming 30 days/year for maintenance shut down, number of operating days/year||=||335|
|Assuming a 24h/d operation, the capacity of the electricity generator||=||463,125/335/24 = 57.6 kWh|
|Assuming capital cost of $ 7,000/kWh, total cost of the system ||=||57.6 x 7,000 = $403,200|
Example 4 – Simple payback period
Typically, the running cost of a biogas electricity generating plant is $0.02/kWh. Example 4 illustrates how to estimate the approximate simple payback period.
|Capital cost from Example 3||=||$403,200 |
|Operating cost assumed||=||$0.02/kWh|
|Total electricity production from dairies and animal fat||=||463,125 kWh (Example 2)|
|Operating cost/year||=||0.02 x 463,125 = $9,262.50|
|Yearly energy revenue ||=||$39,292.95 (Example 2)|
|Subtracting operating cost from the yearly revenue||=||$39,292.95 - $9,262.50 = $30,030.45|
|Government incentives for renewable energy production (2007-2012)||=||$0.06/kWh|
|Total incentives||=||0.06 x 463,125 = 27,787.50|
|Total yearly revenue||=||30,030.45 + 27,787.5 = $57,817.95|
|The simple payback period ||=||403,200/57,817.95 = 6.97 years|
- Carbon credits and tipping fees may help to reduce the simple payback period. It is estimated that producing 1 MW of renewable energy is approximately equivalent to reducing 0.65 tonne of CO2 emissions.
- The nutrient value in the digestate of the manure digester will be more or less the same as the undigested manure. Therefore, the land application cost of digestate is likely to be as same as the cost for land applying manure.
- Transportation costs for bringing in co-digestion substrate material may increase the simple payback period.
- However, the co-digestion process may result in increased nutrient value in the digestate. Therefore, approval from Alberta Environment and more testing during land application may be required.
- Some experiences in North America show that the digestion process is interrupted frequently due to unforeseen maintenance and process related issues which means the payback period will either be significantly increased or there will be no payback at all.
- Smaller digester facilities may significantly exceed the assumed capital cost per kWh, which also means the payback period will be significantly increased.
- Government incentives are assumed to be the same throughout the payback period in the above example, which may or may not be the case in the actual scenario.
The typical simple payback for a biogas plant may be about seven years as long as the existing government incentive program is available and biogas energy is produced continuously without interruption except for scheduled regular maintenance. Some experiences in North America show that biogas energy production is often interrupted due to unforeseen maintenance and process related issues.
Even though anaerobic digestion is a century-old process, the adaptation of this process successfully on the commercial scale for producing energy is still evolving. Frequent interruptions in the process show that the technology and process related knowledge still have room to improve. Despite these drawbacks, the potential for carbon trading and increased consumer awareness regarding practicing environmentally sound and sustainable agricultural production methods will certainly add to the benefits of continuing to work with this technology.
Links for Case Studies
For additional information, check the following web pages:
- MUS system, http://www.climatechangecentral.com/files/attachments/IMUS.pdf
- Iron Creek biogem plant, http://www.climatechangecentral.com/files/attachments/BioGem.pdf
- US case study, http://www.epa.gov/agstar/pdf/gordondale_report_final.pdf
- European case study, http://www.epa.gov/agstar/pdf/gordondale_report_final.pdf
Anaerobic Digesters, Agdex 768-1
Anaerobic Digesters: Frequently Asked Questions, Agdex 768-2
Biogas Energy Potential in Alberta, Agdex 768-3
Integrating Biogas, Confined Feedlot Operations and Ethanol Production, Agdex768-4
Biogas Distribution– Rural Utilities Division of Alberta Agriculture and Rural Development,
Incentives for biogas production– Alberta Bioenergy Producer,
Angelidaki. I, L. Ellegaard 2003. Codigestion of manure and organic wastes in centralized biogas plants. Applied biochemistry and biotechnology 209:95-105.
Bjornsson, L., D. Batstone, K. Cristenson, B. Mattiasson 2001. Agrigas-Biogas production from crop residues. Department of Biotechnology, Lund University, Lund, Sweden.
Biocap. 2003. A Canadian Biomass Inventory: Feedstocks for biobased energy. Prepared for Natural Resources Canada.
Brenda, S. 2002. Overview of Alberta Poultry Industry. Alberta Agriculture and Rural Development
CFIA, 2005. Report on Feed Ban Review. Canadian Food Inspection Agency.
Corbett. R, 2006. Unpublished data from the database. Alberta Agriculture and Rural Development
David Spiess, 2006. Value-added opportunities for straw in Alberta. Alberta Agriculture and Rural Development
EWMCE 2006. Edmonton Waste Management Centre for Excellence. www.ewmce.com
Gao. M, Z. She, Jin. C, 2006. Performance evaluation of a mesophillic (37 C) upflow anaerobic sludge blanket reactor in treating distiller’s grains wastewater. Journal of Hazardous Materials.
Lapp, H. M, D. Shulte, M. A. Stevens, C. Bernier 1978. Biogas production from animal manure. Biomass Energy Institute, Winnipeg, Manitoba.
Lehtomaki, A., J. Rintala 2006. Biogas production from energy crops and crop residues. Department of biological and environmental sciences, University of Jyvaskyla, Finland.
Lehtomaki, A., J. Rintala, Huttenen, S. 2006. Laboratory investigations on co-digestion of energy crops and crop residues for methane production: Effect of crop manure ratio. Department of biological and environmental sciences, University of Jyvaskyla, Finland.
Lorimor, J. W. Powers, A. Sutton 2004. Manure characteristics. Midwest Plan Service-18 section 1. Iowa State University, IA.
Heiermann, M., M. Plochl, B. Linke, H. Schelle 2002. Preliminary evaluation of some cereals as energy crops for biogas production. Institute of Agricultural Engineering Bornim, Potsdam, Germany.
Statistics Canada, 2006. Hog Statistics. Vol. 5 no. 4.
Statistics Canada 2006. Cattle Statistics. Vol. 5 no. 2.
Statistics Canada 2003. Livestock feed requirement study 1999-2001. Catalogue No. 23-501-XIE.
Steffen, R., O. Szolar, R. Braun 1998. Feedstocks for anaerobic digestion. Institute of Agrobiotechnology, University of agricultural sciences, Tulln, Vienna.
Mahendran Navaratnasamy, Ike Edeogu and Lawrence Papworth
Agriculture Stewardship Division
Alberta Agriculture and Rural Development
Source: Agdex 768-6. June 2008.