617:, destroys the heat-trapping gas methane, and the gas is generated by deposits of waste that are already in place. 450 of the 2,300 landfills in the United States have operational landfill gas utilization projects as of 2007. LMOP has estimated that approximately 520 landfills that currently exist could use landfill gas (enough to power 700,000 homes). Landfill gas projects also decrease local pollution, and create jobs, revenues and cost savings. Of the roughly 450 landfill gas projects operational in 2007, 11 billion kWh of electricity was generated and 78 billion cubic feet of gas was supplied to end users. These totals amount to roughly 17,500,000 acres (7,100,000 ha) of pine or fir forests or annual emissions from 14,000,000 passenger vehicles.
521:, another form of internal combustion engine, usually meet an efficiency of 20 to 28 percent at full load with landfill gas. Efficiencies drop when the turbine is operating at partial load. Gas turbines have relatively low maintenance costs and nitrogen oxide emissions when compared to RP engines. Gas turbines require high gas compression, which uses more electricity to compress, therefore reducing the efficiency. Gas turbines are also more resistant to corrosive damage than RP engines. Gas turbines need a minimum of 1,300 cfm and typically exceed 2,100 cfm and can generate 1 to 10 MW. A gas turbine (greater than 3 MW) can typically cost $ 1,400 per kW with annual operation and maintenance costs of $ 130 per kW. Estimates are in 2010 dollars.
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Flares are useful in all landfill gas systems as they can help control excess gas extraction spikes and maintenance down periods. In the U.K. and EU enclosed flares, from which the flame is not visible are mandatory at modern landfill sites. Flares can be either open or enclosed, but the latter are typically more expensive as they provide high combustion temperatures and specific residence times as well as limit noise and light pollution. Some US states require the use of enclosed flares over open flares. Higher combustion temperatures and residence times destroy unwanted constituents such as un-burnt hydrocarbons. General accepted values are an exhaust gas temperature of 1000 °C with a retention time of
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387:, where it is used much in the same way as natural gas. Landfill gas is cheaper than natural gas and holds about half the heating value at 16,785 – 20,495 kJ/m3 (450 – 550 Btu/ft3) as compared to 35,406 kJ/m3 (950 Btu/ft3) of natural gas. Boilers, dryers, and kilns are used often because they maximize use of the gas, limited treatment is needed, and the gas can be mixed with other fuels. Boilers use the gas to transform water into steam for use in various applications. For boilers, about 8,000 to 10,000 pounds per hour of steam can be generated for every 1 million metric tons of waste-in-place at the landfill. Most direct use projects use boilers.
457:, and amine scrubbing. Oxygen and nitrogen are controlled by the proper design and operation of the landfill since the primary cause for oxygen or nitrogen in the gas is intrusion from outside into the landfill because of a difference in pressure. The high-Btu processing equipment can be expected to cost $ 2,600 to $ 4,300 per standard cubic foot per minute (scfm) of landfill gas. Annual costs range from $ 875,000 to $ 3.5 million to operate, maintain and provide electricity to. Costs depend on quality of the end product gas as well as the size of the project. The first landfill gas to LNG facility in the United States was the
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502:, because of relatively low cost, high efficiency, and good size match with most landfills. RP engines usually achieve an efficiency of 25 to 35 percent with landfill gas. However, RP engines can be added or removed to follow gas trends. Each engine can achieve 150 kW to 3 MW, depending on the gas flow. An RP engine (less than 1 MW) can typically cost $ 2,300 per kW with annual operation and maintenance costs of $ 210 per kW. An RP engine (greater than 800 kW) can typically cost $ 1,700 per kW with annual operation and maintenance costs of $ 180 per kW. Estimates are in 2010 dollars.
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collection header and further downstream. A 40-acre (160,000 m) landfill gas collection system with a flare designed for a 600 ft/min extraction rate is estimated to cost $ 991,000 (approximately $ 24,000 per acre) with annual operation and maintenance costs of $ 166,000 per year at $ 2,250 per well, $ 4,500 per flare and $ 44,500 per year to operate the blower (2008). LMOP provides a software model to predict collection system costs.
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201:(LMOP) provides the LandGEM (Landfill Gas Emissions Model), a first-order decay model which aids in the determination of landfill gas production for an individual landfill. Typically, gas extraction rates from a municipal solid waste (MSW) landfill range from 25 to 10000 m/h where Landfill sites typically range from 100,000 m to 10 million m of waste in place.
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explosion concerns, the carbon dioxide content must be as close to zero as possible to avoid freezing problems encountered in the production, and nitrogen must be reduced enough to achieve at least 96% methane. A $ 20 million facility is estimated to achieve $ 0.65/gallon for a plant producing 15,000 gallons/day of LNG (3,000 scfm). Estimates are in 2007 dollars.
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states and private foundations give incentives to landfill gas projects. A Renewable
Portfolio Standard (RPS) is a legislative requirement for utilities to sell or generate a percentage of their electricity from renewable sources including landfill gas. Some states require all utilities to comply, while others require only public utilities to comply.
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Microturbines can produce electricity with lower amounts of landfill gas than gas turbines or RP engines. Microturbines can operate between 20 and 200 cfm and emit less nitrogen oxides than RP engines. Also, they can function with less methane content (as little as 35 percent). Microturbines require
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In situations with low gas extraction rates, the gas can go to power infrared heaters in buildings local to the landfill, provide heat and power to local greenhouses, and power the energy intensive activities of a studio engaged in pottery, metalworking or glass-blowing. Heat is fairly inexpensive to
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If gas extraction rates do not warrant direct use or electricity generation, the gas can be flared off in order to avoid uncontrolled release to the atmosphere. One hundred m/h is a practical threshold for flaring in the U.S. In the U.K, gas engines are used with a capacity of less than 100m3/h.
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are from landfills. Landfill gas projects help aid in the reduction of methane emissions. However, landfill gas collection systems do not collect all the gas generated. Around 4 to 10 percent of landfill gas escapes the collection system of a typical landfill with a gas collection system. The use of
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all provide federal incentives for landfill gas projects. Typically, incentives are in the form of tax credits, bonds, or grants. For example, the
Renewable Electricity Production Tax Credit (PTC) gives a corporate tax credit of 1.1 cents per kWh for landfill projects above 150 kW. Various
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Lohila, Annalea, Tuomas
Laurila, Juha-Pekka Tuovinen, Mika Aurela, Juha Hatakka, Tea Thum, Mari Pihlatie, Janne Rinne, Timo Vesala, Tuomas Laurila, Juha-Pekka Tuovinen, Mika Aurela, Juha Hatakka, Tea Thum, Mari Pihlatie, Janne Rinne, and Timo Vesala. "Micrometeorological Measurements of Methane and
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MSW landfill gas typically has roughly 45 to 60% methane and 40 to 60% carbon dioxide, depending on the amount of air introduced to the site, either through active gas extraction or from inadequate sealing (capping) of the landfill site. Depending on the composition of the waste in place, there are
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in Los
Angeles has realized $ 1.40 per gallon of gasoline equivalent with the flow rate of 250 scfm. Cost per gallon equivalent reduces as the flow rate of gas increases. LNG can be produced through the liquification of CNG. However, the oxygen content needs to be reduced to be under 0.5% to avoid
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in situations where leachate is fairly expensive to treat. The system to evaporate the leachate costs $ 300,000 to $ 500,000 to put in place with operations and maintenance costs of $ 70,000 to $ 95,000 per year. A 30,000 gallons per day evaporator costs $ .05 - $ .06 per gallon. The cost per
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The rate of landfill gas production varies with the age of the landfill. There are 4 common phases that a section of a MSW landfill undergoes after placement. Typically, in a large landfill, different areas of the site will be at different stages at the same time. The landfill gas production rate
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Landfill gas is extracted and piped to a main collection header, where it is sent to be treated or flared. The main collection header can be connected to the leachate collection system to collect condensate forming in the pipes. A blower is needed to pull the gas from the collection wells to the
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Efficient gas collection can be accomplished at both open and closed landfills, but closed landfills have systems that are more efficient, owing to greater deployment of collection infrastructure since active filling is not occurring. On average, closed landfills have gas collection systems that
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Landfill gas must be treated to remove impurities, condensate, and particulates. The treatment system depends on the end use. Minimal treatment is needed for the direct use of gas in boilers, furnaces, or kilns. Using the gas in electricity generation typically requires more in-depth treatment.
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S removal) and siloxane removal are required for molten carbonate fuel cells. Fuel cells are typically run on hydrogen and hydrogen can be produced from landfill gas. Hydrogen used in fuel cells have zero emissions, high efficiency, and low maintenance costs.
341:. Gas cooling and compression are common in primary processing. Secondary treatment systems employ multiple cleanup processes, physical and chemical, depending on the specifications of the end use. Two constituents that may need to be removed are
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extensive gas treatment and come in sizes of 30, 70, and 250 kW. A microturbine (less than 1 MW) can typically cost $ 5,500 per kW with annual operation and maintenance costs of $ 380 per kW. Estimates are in 2010 dollars.
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which is said to result in greater than 98% destruction efficiency. The combustion temperature is an important controlling factor as if greater than 1100 °C, there is a danger of the exponential formation of thermal NOx.
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will reach a maximum at around 5 years and start to decline. Landfill gas follows first-order kinetic decay after decline begins with a k-value ranging 0.02 yr-1 for arid conditions and 0.065 yr-1 for wet conditions.
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Staley, Bryan, Morton Barlaz, and Morton Barlaz. "Composition of
Municipal Solid Waste in the United States and Implications for Carbon Sequestration and Methane Yield." Journal of Environmental Engineering, 135.10 (2009):
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of 33.95 MJ/Nm^3 which gives rise to energy generation benefits. The amount of methane that is produced varies significantly based on composition of the waste. Most of the methane produced in MSW landfills is derived from
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Kaplan, P. Ozge, Joseph
Decarolis, Susan Thorneloe, Joseph Decarolis, and Susan Thorneloe. "Is It Better to Burn or Bury Waste for Clean Electricity Generation?." Environmental Science & Technology, 43.6 (2009):
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capture about 84% of produced gas, compared to about 67% for open landfills. Landfill gas can also be extracted through horizontal trenches instead of vertical wells. Both systems are effective at collecting.
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saves $ 500,000 on energy costs per year at each of the four plants owned by
General Motors that has implemented landfill gas boilers. Disadvantages of Boilers, dryers, and kilns are that they need to be
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Urban, W, H Lohmann, J.I. Salazar Gomez, H Lohmann, and J.I. Salazar Gomez. "Catalytically
Upgraded Landfill Gas as a Cost-effective Alternative for Fuel Cells." Journal of Power Sources, 193.1 (2009):
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Landfill gas can be converted to high-Btu gas by reducing its carbon dioxide, nitrogen, and oxygen content. The high-Btu gas can be piped into existing natural gas pipelines or in the form of CNG (
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could be fueled by landfill gas. Molten carbonate fuel cells require less purity than typical fuel cells, but still require extensive treatment. The separation of acid gases (HCl, HF, and SO
453:). CNG and LNG can be used on site to power hauling trucks or equipment or sold commercially. Three commonly used methods to extract the carbon dioxide from the gas are membrane separation,
109:. It is important not only to control its emission but, where conditions allow, use it to generate energy, thus offsetting the contribution of two major sources of greenhouse gases towards
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to produce electricity, heat, fuels, and various chemical compounds. After fossil fuel and agriculture, landfill gas is the third largest human generated source of methane. Compared to CO
198:
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U.S. Environmental
Protection Agency. "Fueling the Economy and a Sustainable Energy Future While Improving the Environment." Landfill Gas Energy. December 2008. Web. 26 November 2009.
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U.S. Environmental
Protection Agency. "Adapting Boilers to Utilize Landfill Gas: An Environmentally and Economically Beneficial Opportunity." September 2008. Web. 26 November 2009.
349:, which are damaging to equipment and significantly increase maintenance cost. Adsorption and absorption are the most common technologies used in secondary treatment processing.
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If the landfill gas extraction rate is large enough, a gas turbine or internal combustion engine could be used to produce electricity to sell commercially or use on site.
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In 2005, 166 million tons of MSW were discarded to landfills in the United States. Roughly 120 kg of methane is generated from every ton of MSW. Methane has a
891:
U.S. Environmental Protection Agency. "An Overview of Landfill Gas Energy in the United States." Landfill Methane Outreach Program, June 2009. Web. 26 November 2009.
901:
Powell, Jon T.; Townsend, Timothy G.; Zimmerman, Julie B. (2015-09-21). "Estimates of solid waste disposal rates and reduction targets for landfill gas emissions".
124:. These projects collect the methane gas and treat it, so it can be used for electricity or upgraded to pipeline-grade gas to power homes, buildings, and vehicles.
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gallon increases as the evaporator size decreases. A 10,000 gallons per day evaporator costs $ .18 - $ .20 per gallon. Estimates are in 2007 dollars.
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of 25 times more effective of a greenhouse gas than carbon dioxide on a 100-year time horizon. It is estimated that more than 10% of all global anthropogenic
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for vertical wells call for about one well per acre of landfill surface, whereas horizontal wells are normally spaced about 50 to 200 feet apart on center.
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U.S. Environmental Protection Agency. "Project Technology Options." LFG Energy Project Development Handbook. 9 September 2009. Web. 26 November 2009. <
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U.S. Environmental Protection Agency. "Landfill Gas Energy Basics." LFG Energy Project Development Handbook. 16 February 2009. Web. 26 November 2009. <
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U.S. Environmental Protection Agency. "Landfill Gas Modeling." LFG Energy Project Development Handbook. 30 January 2009. Web. 26 November 2009. <
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The number of landfill gas projects, which convert the gas into power, went from 399 in 2005 to 519 in 2009 in the United States, according to the
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Landfill gas collection is typically accomplished through the installation of wells – vertically and/or horizontally – in the waste mass. Design
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Bade Shrestha, S.O, G Narayanan, and G Narayanan. "Landfill Gas with Hydrogen Addition a Fuel for SI Engines." Fuel, 87.17/18 (2008): 3616-3626.
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1047:"EPA - LMOP - Funding Guide: State Renewable Portfolio Standards (RPS)." U.S. Environmental Protection Agency. Web. 8 November 2009. <
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in order to accept the gas and the end user has to be nearby (within roughly 5 miles) as pipelines will need to be built.
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Treatment systems are divided into primary and secondary treatment processing. Primary processing systems remove moisture and
1096:"Environmental Protection Agency LMOP: Benefits of Energy." U.S. Environmental Protection Agency. Web. 27 November 2009. <
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which comprise 19.4 ± 5.5%, 21.9 ± 5.2%, and 20.9 ± 7.1% respectively on average of MSW landfills in the United States.
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employ with the use of a boiler. A microturbine would be needed to provide power in low gas extraction rate situations.
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Whittington, H. "Electricity Generation: Options for Reduction in Carbon Emissions", 360.1797 (2002): 1653-1668. .
1060:"EPA - LMOP - Funding Guide: Federal Resources." U.S. Environmental Protection Agency. Web. 8 November 2009. <
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http://www.sepa.org.uk/waste/waste_regulation/idoc.ashx?docid=d2a6df2b-8ea9-4326-af87-e6803f769d47&version=-1
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Carbon Dioxide Fluxes at a Municipal Landfill." Environmental Science & Technology, 41.8 (2007): 2717-2722.
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Various landfill gas project incentives exist for United States projects at the federal and state level. The
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Scottish Environment Protection Agency. Guidance on Landfill Gas Flaring. November 2002. Web. <
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465:. The same process is used for the conversion to CNG, but on a smaller scale. The CNG project at
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1031:"EPA - LMOP - Funding Guide." U.S. Environmental Protection Agency. Web. 8 November 2009. <
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Gas separator membrane skid used in membrane separation process to extract carbon dioxide
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source because it offsets the use of environmentally damaging fuels such as oil or
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emissions. In anaerobic conditions, as is typical of landfills, methane and CO
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These projects are popular because they control energy costs and reduce
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719:"Building on Success: New Ways to Keep Methane Out of the Atmosphere"
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many other minor components that comprises roughly 1% which includes
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Percent composition of each major component of landfill gas over time
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151:. Aerobic conditions (presence of oxygen) leads to predominately CO
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More than 70 percent of all landfill electricity projects use
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Research has been performed indicating that molten carbonate
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deal primarily with the United States and do not represent a
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The gas coming from the landfill can be used to evaporate
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is a process of gathering, processing, and treating the
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http://www.epa.gov/lmop/res/guide/state_resources.htm
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Internal combustion engines to generate electricity.
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400:Infrared heaters, greenhouses, artisan studios
143:(LFG) is generated through the degradation of
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32:The examples and perspective in this article
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290:A layout of landfill gas collection system
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571:States with Renewable Portfolio Standard.
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371:Boiler retrofitted to accept landfill gas
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70:Learn how and when to remove this message
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880:http://www.epa.gov/lmop/res/handbook.htm
832:http://www.epa.gov/lmop/res/handbook.htm
773:http://www.epa.gov/lmop/res/handbook.htm
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318:Flares: Open (left) and enclosed (right)
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147:(MSW) and other biodegradable waste, by
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933:"NOx Emissions from Silicon Production"
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514:Gas turbines that utilize landfill gas.
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105:, methane is 25 times more potent as a
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118:U.S. Environmental Protection Agency.
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500:form of internal combustion engine
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46:, discuss the issue on the
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742:Koch, Wendy (2010-02-25).
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459:Frank R. Bowerman Landfill
375:Pipelines transmit gas to
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690:US EPA, OA (2015-12-23).
585:Department of Agriculture
463:Orange County, California
1145:Greenhouse gas emissions
602:global warming potential
122:greenhouse gas emissions
91:Landfill gas utilization
657:Landfill gas monitoring
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632:Atmospheric methane
627:Anaerobic digestion
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