The Renewable Energy Institute offers three types of Biogas Feasibility Reviews & Studies: Phase I Biomass Preliminary Screening Review - Depending on the specific type of study, location, amount of time we require, and any additional requirements that may be added by the client. This review averages about $10,000.00 to $20,000.00 and requires 30 to 60 days to complete and may include a site visit to one of our affiliated plants. Phase II Biomass Feasibility Study and Analysis - Provides a solid basis for moving a potential renewable energy project forward. The cost for this depends on the type, location, amount of time we require, and any additional requirements that may be included by the client. This study can cost from $50,000.00 and run as high as $100,000.00 and requires 90 to 120 days, on average, to complete. Final result is usually a basis for a loan or other investment funding. Phase III Biomass Detailed Concept, Engineering and Design Analysis - the actual renewable energy project is conceived, designed and engineered. Final result is usually ready for a company to start construction. A Phase III can take about 6 months to complete and will cost anywhere from 5% to 10% of the overall cost of the project. Our Feasibility Reviews, Studies and Analyses are led by one of our engineers and PhD's that serve on our Scientific Advisory Board. They are each recognized leaders in the renewable energy industry and/or academia. Our goal is to help you determine whether your renewable energy is viable, identify the merits of your proposed renewable energy project, identify weak points, provide our recommended course of action, as well as our recommendations for products and equipment that need further review or consideration. Our Feasibility Studies are an excellent "foundation" for building your next renewable energy project. What is Biomethane? BioMethane is generated from Anaerobic Digesters, Anaerobic Lagoons, Biomass Gasification, Biomass Gasifiers, Biogas Recovery, BioMethane, Concentrated Animal Feeding Operations Landfill Gas to Energy, and Methane Gas Recovery. Unlike most companies, we are equipment supplier/vendor neutral. This means we help our clients select the best equipment for their specific application. This approach provides our customers with superior performance, decreased operating expenses and increased return on investment. The Renewable Energy Institute is leading the engineering and design to develop the world's best Anaerobic Digesters. Anaerobic
Digesters recover Biomethane from organic
materials and prevents the Biomethane - which has a
Global
Warming Potential that is 21 times more harmful to our climate than Carbon
Dioxide Emissions - from entering the atmosphere.
Biomethane
- The Best Renewable Fuel? Thursday, 29
June 2006 We
are designing and engineering the world's best Anaerobic
Digesters. Biomethane, which we also refer to as "Renewable Natural Gas" is used as a renewable fuel for our cogeneration and trigeneration power plants. Alternatively, we may sell the Biomethane to a customer and transport it to them from our Anaerobic Digesters via natural gas pipelines. We believe Anaerobic Digesters and Biomethane represent an exciting opportunity for multiple reasons: 1. Anaerobic Digesters take an existing liability and waste (Biomethane) and convert it into an asset and profit generator. 2. Anaerobic Digesters mitigate and reverse by preventing Biomethane to escape into the atmosphere, which is one of the major causes of global warming and climate change. Of all Greenhouse Gas Emissions, Biomethane is 21 times more harmful to the atmosphere than are Carbon Dioxide Emissions. 3. Anaerobic Digesters are vital for renewable energy production and helping our country's drive for energy independence. 4. EVERY wastewater treatment plant as well as ALL Concentrated Animal Feeding Operations (CAFO's) - IN EVERY COUNTRY - will soon be installing Anaerobic Digesters to prevent Biomethane from entering the atmosphere and help reverse climate change as well as for use as a renewable fuel. 5. The country of Sweden is the global leader in Biomethane production. Sweden has identified the Biomethane opportunities and is converting biowaste derived from agricultural material and residues into usable Biomethane. The Biomethane is used to generate clean, renewable electricity, residential heating, and also as a transportation fuel. Biomass sources make up 45% of Sweden’s Biomethane. Sweden's Biomethane industry has been growing at an annual rate of around 20% over the last five years. Biomethane powers more than 8,000 transit buses, garbage trucks, and 10 different models of passenger cars in Sweden. Sweden now has more than 25 Biomethane production facilities and 65 filling stations. The country believes that since Biomethane is developed from natural, organic sources that would have been released into the atmosphere, that Biomethane is considered one of the most climate-friendly fuels. Biomethane is 98% methane and easily meets the Swedish and California pipeline standards. The electric grid is changing!
To the "Smart Grid" of tomorrow - which resembles the slide below - will be very efficient, decentralized or "distributed," non-polluting, low-cost and "smart."
What
is BioMethane, BioMethanation and
Methanogenesis? BioMethane, after installation of the requisite equipment, is essentially free, as opposed to buying natural gas, presently costing around $6.00/mmbtu. Methanogenesis
is the production of CH4 and CO2 by biological processes that are carried out by
methanogens. More
About Biomass Gasification and BioMethanation Technology The production and disposal of large quantities of organic and biodegradable waste without adequate or proper treatment results in widespread environmental pollution. Some waste streams can be treated by conventional methods like aeration. Compared to the aerobic method, the use of anaerobic digesters in processing these waste streams provides greater economic and environmental benefits and advantages. As
previously stated, Biomethanation is the process of conversion of organic matter
in the waste (liquid or solid) to BioMethane (sometimes referred to as "BioGas)
and manure by microbial action in the absence of air, known as "anaerobic
digestion." Interest
in BioMethanation as an economic, environmental and energy-saving waste
treatment continues to gain greater interest world-wide and has led to the
development of a range of anaerobic reactor designs. These high-rate,
high-efficiency anaerobic digesters are also referred to as "retained
biomass reactors" since they are based on the concept of retaining viable
biomass by sludge immobilization. More and more, cities, counties and municipalities are faced with greater environmental compliance issues relating to their municipally-owned landfills, Publicly Owned Treatment Works ("POTW's") or Wastewater Treatment Systems. A city's landfill and/or POTW provides an excellent opportunity for cities to reduce their emissions as well as provide an additional revenue stream. These facilities may have valuable gases that our company recovers and pipes to one of our clean, environmentally-friendly cogeneration or trigeneration energy systems. Our company provides economic and ecological solutions for cities and municipalities and provide a new cash flow simultaneously. We offer turn-key solutions for cities that includes the preliminary feasibility analysis, engineering and design, project management, permitting and commissioning. We provide very attractive financing packages for cities that does not add to a city's liability, yet provides a valuable new revenue stream. And, we are also able to offer a turn-key solution for qualified municipalities that includes our company owning, operating and maintaining the onsite power and energy plant. At
the heart of the system is a (Bio) Methane Gas Recovery system similar those
used in Flare Gas Recovery or Vapor Recovery Units. Methane Gas Recovery,
Flare Gas Recovery, Vapor Recovery, Waste to Energy and Vapor Recovery Units all
recover valuable "waste" or vented fuels that can be used to provide
fuel for an onsite power generation plant. Our waste-to-energy and waste
to fuel systems significantly or entirely, reduces your facility's emissions
(such as Methane
Gas Recovery and vapor recovery units can be located in hundreds of applications
and locations. At a landfill, Wastewaster Treatment System (or Publicly
Owned Treatment Works - "POTW") gases from the facility can be
captured from the anaerobic digesters, and manifolded/piped to one of our onsite
power generation plants, and make, essentially, "free" electricity for
your facility's use. These associated "biogases" that are
generated from municipally owned landfills or wastewater treatment plants have
low btu content or heating values, ranging around 550-650 btu's.
This makes them Additionally, if heat (steam and/or hot water) is required, we will incorporate our cogeneration or trigeneration system into the project and provide some, or all, of your hot water/steam requirements. Similarly, at crude oil refineries, gas processing plants, exploration and production sites, and gasoline storage/tank farm site, we convert your facility's "waste fuel" and environmental liabilities into profitable, environmentally-friendly solutions. Our
Methane Gas Recovery systems are designed and engineered for these specific
applications. It is important to note that there are many internal
combustion engines or combustion turbines that are NOT suited for these
applications. Our systems are engineered precisely for your facility's
application, and our engineers know the engines and turbines that will work as
well as those that don't. More importantly, we are vendor and supplier
neutral! Our only concerns are for the optimum system solution Our turn-key systems includes design, engineering, permitting, project management, commissioning, as well as financing for our qualified customers. Additionally, we may be interested in owning and operating the flare gas recovery or vapor recovery units. For these applications, there is no investment required from the customer. For more information, please provide us with the following information about the flare gas or vapor:
What is an Anaerobic Digester? An
Anaerobic Digester is a device for optimizing the anaerobic digestion of biomass
and/or animal manure, and possibly to recover biogas also referred to as BioMethane
for energy production. Digester types include batch, complete mix, continuous
flow (horizontal or plug-flow, multiple-tank, and vertical tank), and covered
lagoon. Anaerobic
digestion is a biological process that produces a gas principally composed of
methane (CH4) and carbon dioxide (CO2) otherwise known as biogas. These gases
are produced from organic wastes such as livestock manure, food processing
waste, etc. The
The
U.S. EPA AgSTAR is an outreach program designed to reduce methane emissions from
livestock waste management operations by promoting the use of biogas recovery
systems. A biogas recovery system is an anaerobic digester with biogas capture
and combustion to produce electricity, heat or hot water. Biogas recovery
systems are effective at confined livestock facilities that handle manure as
liquids and slurries, typically swine and dairy farms. Anaerobic digester
technologies provide enhanced environmental and financial performance when
compared to traditional waste management systems such as manure storages and
lagoons. Anaerobic digesters are particularly effective in reducing methane
emissions but also provide other air and water pollution control opportunities.
AgSTAR provides an array of information and tools designed to assist producers
in the evaluation and implementation these systems, including:
Methane
(and Biomethane) Emissions from Animal Waste Management Methane
emissions occur whenever animal waste is managed in anaerobic conditions. Liquid
manure management systems, such as ponds, anaerobic lagoons, and holding tanks
create oxygen free environments that promote methane production. Manure
deposited on fields and pastures, or otherwise handled in a dry form, produces
insignificant amounts of methane. Currently, livestock waste contributes about 8
percent of human-related methane emissions in the Biomethane from Anaerobic Digesters Methane (and Biomethane) is a gas that contains molecules of methane with one atom of carbon and four atoms of hydrogen (CH4 ). It is the major component of the "natural" gas used in many homes for cooking and heating. It is odorless, colorless, and yields about 1,000 British Thermal Units (Btu) [252 kilocalories (kcal)] of heat energy per cubic foot (0.028 cubic meters) when burned. Natural gas is a fossil fuel that was created eons ago by the anaerobic decomposition of organic materials. It is often found in association with oil and coal. The same types of anaerobic bacteria that produced natural gas also produce methane today. Anaerobic bacteria are some of the oldest forms of life on earth. They evolved before the photosynthesis of green plants released large quantities of oxygen into the atmosphere. Anaerobic bacteria break down or "digest" organic material in the absence of oxygen and produce "biogas" as a waste product. (Aerobic decomposition, or composting, requires large amounts of oxygen and produces heat.) Anaerobic decomposition occurs naturally in swamps, water-logged soils and rice fields, deep bodies of water, and in the digestive systems of termites and large animals. Anaerobic processes can be managed in a "digester" (an airtight tank) or a covered lagoon (a pond used to store manure) for waste treatment. The primary benefits of anaerobic digestion are nutrient recycling, waste treatment, and odor control. Except in very large systems, biogas production is a highly useful but secondary benefit. Biogas produced in anaerobic digesters consists of methane (50%-80%), carbon dioxide (20%-50%), and trace levels of other gases such as hydrogen, carbon monoxide, nitrogen, oxygen, and hydrogen sulfide. The relative percentage of these gases in biogas depends on the feed material and management of the process. When burned, a cubic foot (0.028 cubic meters) of biogas yields about 10 Btu (2.52 kcal) of heat energy per percentage of methane composition. For example, biogas composed of 65% methane yields 650 Btu per cubic foot (5,857 kcal/cubic meter). Anaerobic Digester DesignsAnaerobic digesters are made out of concrete, steel, brick, or plastic. They are shaped like silos, troughs, basins or ponds, and may be placed underground or on the surface. All designs incorporate the same basic components: a pre-mixing area or tank, a digester vessel(s), a system for using the biogas, and a system for distributing or spreading the effluent (the remaining digested material). There are two basic types of digesters: batch and continuous. Batch-type digesters are the simplest to build. Their operation consists of loading the digester with organic materials and allowing it to digest. The retention time depends on temperature and other factors. Once the digestion is complete, the effluent is removed and the process is repeated. In a continuous digester, organic material is constantly or regularly fed into the digester. The material moves through the digester either mechanically or by the force of the new feed pushing out digested material. Unlike batch-type digesters, continuous digesters produce biogas without the interruption of loading material and unloading effluent. They may be better suited for large-scale operations. There are three types of continuous digesters: vertical tank systems, horizontal tank or plug-flow systems, and multiple tank systems. Proper design, operation, and maintenance of continuous digesters produce a steady and predictable supply of usable biogas. Many livestock operations store the manure they produce in waste lagoons, or ponds. A growing number of these operations are placing floating covers on their lagoons to capture the biogas. They use it to run an engine/generator to produce electricity. The Digestion ProcessAnaerobic decomposition is a complex process. It occurs in three basic stages as the result of the activity of a variety of microorganisms. Initially, a group of microorganisms converts organic material to a form that a second group of organisms utilizes to form organic acids. Methane-producing (methanogenic) anaerobic bacteria utilize these acids and complete the decomposition process. A variety of factors affect the rate of digestion and biogas production. The most important is temperature. Anaerobic bacteria communities can endure temperatures ranging from below freezing to above 135° Fahrenheit (F) (57.2° Centigrade [C]), but they thrive best at temperatures of about 98°F (36.7°C) (mesophilic) and 130°F (54.4°C) (thermophilic). Bacteria activity, and thus biogas production, falls off significantly between about 103° and 125°F (39.4° and 51.7°C) and gradually from 95° to 32°F (35° to 0°C). In the thermophilic range, decomposition and biogas production occur more rapidly than in the mesophilic range. However, the process is highly sensitive to disturbances such as changes in feed materials or temperature. While all anaerobic digesters reduce the viability of weed seeds and disease-producing (pathogenic) organisms, the higher temperatures of thermophilic digestion result in more complete destruction. Although digesters operated in the mesophilic range must be larger (to accommodate a longer period of decomposition within the tank [residence time]), the process is less sensitive to upset or change in operating regimen. To optimize the digestion process, the digester must be kept at a consistent temperature, as rapid changes will upset bacterial activity. In most areas of the United States, digestion vessels require some level of insulation and/or heating. Some installations circulate the coolant from their biogas-powered engines in or around the digester to keep it warm, while others burn part of the biogas to heat the digester. In a properly designed system, heating generally results in an increase in biogas production during colder periods. The trade-offs in maintaining optimum digester temperatures to maximize gas production while minimizing expenses are somewhat complex. Studies on digesters in the north-central areas of the country indicate that maximum net biogas production can occur in digesters maintained at temperatures as low as 72°F (22.2°C). Other factors affect the rate and amount of biogas output. These include pH, water/solids ratio, carbon/nitrogen ratio, mixing of the digesting material, the particle size of the material being digested, and retention time. Pre-sizing and mixing of the feed material for a uniform consistency allows the bacteria to work more quickly. The pH is self-regulating in most cases. Bicarbonate of soda can be added to maintain a consistent pH, for example when too much "green" or material high in nitrogen content is added. It may be necessary to add water to the feed material if it is too dry, or if the nitrogen content is very high. A carbon/nitrogen ratio of 20/1 to 30/1 is best. Occasional mixing or agitation of the digesting material can aid the digestion process. Antibiotics in livestock feed have been known to kill the anaerobic bacteria in digesters. Complete digestion, and retention times, depend on all of the above factors. Producing and Using BiomethaneAs long as proper conditions are present, anaerobic bacteria will continuously produce biogas. Minor fluctuations may occur that reflect the loading routine. Biogas can be used for heating, cooking, and to operate an internal combustion engine for mechanical and electric power. For engine applications, it may be advisable to scrub out hydrogen sulfide (a highly corrosive and toxic gas). Very large-scale systems/producers may be able to sell the gas to natural gas companies, but this may require scrubbing out the carbon dioxide. Using the EffluentThe material drawn from the digester is called sludge, or effluent. It is rich in nutrients (ammonia, phosphorus, potassium, and more than a dozen trace elements) and is an excellent soil conditioner. It can also be used as a livestock feed additive when dried. Any toxic compounds (pesticides, etc.) that are in the digester feedstock material may become concentrated in the effluent. Therefore, it is important to test the effluent before using it on a large scale. EconomicsAnaerobic digester system costs vary widely. Systems can be put together using off-the-shelf materials. There are also a few companies that build system components. Sophisticated systems have been designed by professionals whose major focus is research, not low cost. Factors to consider when building a digester are cost, size, the local climate, and the availability and type of organic feedstock material. In the United States, the availability of inexpensive fossil fuels has limited the use of digesters solely for biogas production. However, the waste treatment and odor reduction benefits of controlled anaerobic digestion are receiving increasing interest, especially for large-scale livestock operations such as dairies, feedlots, and slaughterhouses. Where costs are high for sewage, agricultural, or animal waste disposal, and the effluent has economic value, anaerobic digestion and biogas production can reduce overall operating costs. Biogas production for generating cost effective electricity requires manure from more than 150 large animals. Below-ground, concrete anaerobic digesters have proven to be especially useful to agricultural communities in parts of the world such as China, where fossil fuels and electricity are expensive or unavailable. The primary purpose of these anaerobic digesters is waste (sewage) treatment and fertilizer production. Biogas production is secondary. Accomplishments
The AgSTAR Program has been very successful in encouraging the development and
adoption of anaerobic digestion technology. Since the establishment of the
program in 1994, the number of operational digester systems has doubled. This
has produced significant environmental and energy benefits, including methane
emission reductions of approximately 124,000 metric tons of carbon equivalent
and annual energy generation of about 30 million kWh. The graph below shows the
historical use of biogas recovery technology for animal waste management.
The
development of anaerobic digesters for livestock manure treatment and energy
production has accelerated at a very fast pace over the past few years. Factors
influencing this market demand include: increased technical reliability of
anaerobic digesters through the deployment of successful operating systems over
the past five years; growing concern of farm owners about environmental quality;
an increasing number of state and federal programs designed to cost share in the
development of these systems; and the emergence of new state energy policies
(such as net metering legislation) designed to expand growth in reliable
renewable energy and green power markets. In
the past 2 years alone, the number of operational digester systems has increased
by 30%. For more detailed information on anaerobic digester use in the The
process of anaerobic digestion consists of three steps. This
section describes the anaerobic digestion (AD) process, outlines guidelines for
assessing the feasibility of AD and biogas usage at a swine facility and
provides summary information on AD system performance and reliability. Anaerobic
Digestion Technology Description AD
promotes the bacterial decomposition of the volatile solids (VS) in animal
wastes to biogas, thereby reducing lagoon loading rates and odor. The primary
component of an AD system is the anaerobic digester, a waste vessel containing
bacteria that digest the organic matter in waste streams under controlled
conditions to produce biogas. As an effluent, AD yields nearly all of the liquid
that is fed to the digester. This remaining fluid consists of mostly water and
is allowed to evaporate from a secondary lagoon, land-applied for irrigation and
fertilizer value or recycled to flush manure from the swine building to the
digester. The
benefits of AD include:
AD
takes place in three steps: hydrolysis, acid formation, and methane generation.
During the first step, hydrolysis, bacterial enzymes break down proteins, fats
and sugars in the waste to simple sugars. During acid formation, bacteria
convert the sugars to acetic acid, carbon dioxide and hydrogen. Then the
bacteria convert the acetic acid to methane and carbon dioxide, and combine
carbon dioxide and hydrogen to form methane and water. Digester
technologies that can be used to collect biogas from swine facilities include:
Although
a sequencing batch reactor has been used for AD at one swine facility in the Appendix
B provides contact information that can help producers find AD system
designers/installers, odor control technologies, generators, heating and cooling
equipment, and other information to help manage air and water quality at hog
facilities. Covered
lagoon digesters are the simplest AD system. These systems typically consist of
an anaerobic combined storage and treatment lagoon, an anaerobic lagoon cover,
an evaporative pond for the digester effluent, and a gas treatment and/or energy
conversion system. Figure 1 shows a typical schematic for a floating covered
anaerobic lagoon.
Figure
1 . Covered anaerobic lagoon digester Covered
lagoon digesters typically have a hydraulic retention time (HRT) of 40 to 60
days. The HRT is the amount of time a given volume of waste remains in the
treatment lagoon. A collection pipe leading from the digester carries the biogas
to either a gas treatment system such as a combustion flare, or to an
engine/generator or boiler that uses the biogas to produce electricity and heat.
Following treatment, the digester effluent is often transferred to an
evaporative pond or to a storage lagoon prior to land application. Climate
affects the feasibility of using covered lagoon digesters to generate
electricity. Engine/generator systems typically do not produce sufficient waste
heat to maintain temperatures high enough in covered lagoon digesters in the
winter to sustain consistently high biogas production rates. Using propane or
natural gas to provide additional heat for the lagoon contents is typically not
an economically viable option. Without that additional heat, most covered lagoon
digesters produce less biogas in colder temperatures, and little or no gas below
39 FACE= "Symbol">° F. As a result, covered lagoon digesters are
most appropriate for use in warm climates if the biogas is to be used for energy
or heating purposes. Complete
mix digester systems consist of a mix tank, a complete mix digester and a
secondary storage or evaporative pond. The mix tank is either an aboveground
tank or concrete in-ground tank that is fed regularly from underfloor waste
storage below the animal feedlot. Waste is stirred in the mix tank to prevent
solids from settling in the waste prior to being fed to the digester. The
complete mix digester is essentially a constant-volume aboveground tank or
in-ground covered lagoon that is fed daily from the mix tank. Complete mix
digesters with in-ground lagoons often employ covers similar to those used in
covered lagoon digesters. In the digester, a mix pump circulates waste material
slowly around the heater to maintain a uniform temperature. Hot water from an
engine/generator cogeneration water jacket or boiler is used to heat the
digester. A cylindrical aboveground tank, such as that shown in Figure 2,
optimizes biogas production, but is more capital intensive than in-ground tanks.
The only operating AD system in Source:
EPA. (February 1997). AgStar Technical Series: Complete Mix Digesters – A
Methane Recovery Figure
2 . Complete mix digester schematic Complete
mix digesters have an HRT of 15 to 20 days, which means that complete mix
digesters can reduce the overall lagoon volume required for waste storage and
treatment. This makes complete mix digesters comparable to covered lagoon
digesters in cost, despite the increased complexity of stirring, mixing and
plumbing components. In addition, biogas production rates, and therefore heat
and electricity production, are greater and more consistent than for covered
lagoons. This can help reduce system payback periods compared to covered lagoon
systems. Like covered lagoon systems, digester effluent from complete mix
digesters is frequently stored in evaporative ponds or storage lagoons. System
Requirements This
section provides guidelines for conducting a preliminary assessment of the
feasibility of using AD at a swine facility. Although AD system requirements
will vary depending on the application and system design, there are some
rule-of-thumb measures that should be noted when assessing the feasibility of AD
at a given location. For AD to potentially be technically feasible and
cost-effective, a swine facility should:
If
the above characteristics are present, the facility is a possible candidate
for AD. Many pre-existing waste storage and treatment lagoons are too large to
practically or cost-effectively employ covers over their entire area. Partial
covers may be an option to recover methane from these older systems, as an
alternative to installing a completely new storage and treatment lagoon
system. If
energy recovery is to be employed, methane production and gas quality should
be considered and compared to energy requirements at the facility. Daily
biogas production at installed farm-based anaerobic digesters in the Facilities
that are located south of the line of climate limitation in Figure 3 are
usually warm enough for cost-effective energy recovery from covered lagoon
digesters. In most cases, facilities north of the climate line in Figure 3 are
too cold for cost-effective energy recovery from covered lagoon digesters.
Complete mix digesters can be used in cold or warm climates. If odor control
is the only objective, either covered lagoon or complete mix digesters may be
used, but odor control will be less effective in the winter for covered lagoon
digesters south of the line of climate limitation in Figure 3. In general,
complete mix digesters are the most appropriate choice for use in Colorado. Figure
3 . Line of climate limitation for biogas energy recovery Table
2 shows which digesters are appropriate for the waste collection strategies at
covered swine facilities. Complete mix digesters can operate with a waste
total solids (TS) percentage between 3 and 10 percent, while covered lagoon
digesters can use waste with a TS percentage less than 2 percent. Table
2 . Matching a digester to existing waste collection practices
Source
– Adapted from: EPA. (July 1997). AgStar Handbook: A Manual for Developing
Biogas Systems at Commercial Appendix
C describes each of the various waste collection technologies listed in Table
2. Biogas Utilization Systems This
section discusses some of the biogas utilization options that are available for
use with AD. Electricity generation with waste heat recovery (cogeneration) and
direct combustion and use in equipment that normally uses propane or natural gas
are the two primary options for biogas utilization. Electricity generated using
biogas can be generated for on-farm use or for sale to the electric power grid
if an economically attractive power purchase agreement can be negotiated through
the local utility or rural electric cooperative. Direct combustion allows the
gas to be used in existing equipment that normally uses propane or natural gas
such as boilers or forced air furnaces with minor equipment modifications.
Combustion is usually a seasonal use for biogas, as most boiler and furnace
applications are only required during the winter. The EPA FarmWare manual
describes some characteristics of engine/generator and direct combustion systems
that can be used with biogas. The following subsections draw from the FarmWare
manual to provide some basic information about the use of these systems at
covered swine facilities and other farm applications. Electricity Generation Commercial
electricity generation systems that use biogas typically consist of an internal
combustion (IC) engine, a generator, a control system and an optional heat
recovery system. IC
engines designed to burn propane or natural gas are easily converted to burn
biogas by adjusting carburation and ignition systems. Such engines are available
in nearly any capacity, but the most successful varieties are industrial engines
that are designed to work with wellhead natural gas. A biogas-fueled engine will
normally convert 18 to 25 percent of the biogas Btu value to electricity. Two
types of generators are used on farms: induction generators and synchronous
generators. Induction generators operate in parallel with the utility and cannot
operate as a stand-alone power source. Induction generators derive their phase,
frequency and voltage from the utility. Synchronous generators operate as an
isolated system or in parallel to the utility, and require more sophisticated
intertie systems to match output to utility phase, frequency and voltage. Control
systems are required to protect the engine and the utility. Control packages are
available that can shut the engine off due to mechanical problems, utility power
outage or utility voltage and frequency fluctuations, or in the event that
excess power is generated that the utility will not accept. Generators that
operate in parallel with the utility system, such as induction generators,
require an intertie system with safety relays to shut off the engine and
disconnect from the utility in the event of a problem. Intertie negotiations
with a utility for induction generators are typically much easier than for a
synchronous generator, due to the level of control the utility has over the
characteristics of power entering the grid from an induction generator. The
primary advantage of a synchronous generator is its ability to act as a
stand-alone power source. However, if operated as an isolated system, a
synchronous generator must be oversized to meet the highest electrical demand,
while operating less efficiently at average or partial loads. Due to the system
size and more complicated control requirements, a synchronous generator
operating as an isolated system is typically more expensive than an induction
generator. Biogas
engines reject approximately 75 to 82 percent of the energy input as waste heat.
This waste heat can be used to heat the digester and/or provide water or space
heat to the facility. Commercial heat exchangers can recover waste heat from the
engine water cooling system and the engine exhaust, recovering up to 7,000
Btu/hour for each kW of generator load. Waste heat recovery increases the energy
efficiency of the system to 40 to 50 percent. Ongoing
research and development is focusing on the use of microturbines and fuel cells
for converting biogas to electricity. Microturbines are high-speed, small-scale
(typically less than 100 kW) gas-driven turbine systems
that produce electricity efficiently, have low emissions and require little
maintenance. Reflective Energies in The
Department of Energy’s WRBEP funded a project in fiscal year 2000 in Direct
combustion of biogas on-site in a boiler or forced air furnace can provide
seasonal heat to nurseries, farrowing rooms and other facilities at a swine
facility. A cast iron natural gas boiler can be used for most farm boiler
applications. The air-fuel mixture will require adjustment and burner jets will
need to be enlarged for use with low-Btu gas. Cast iron boilers are available in
many sizes, from 45,000 Btu/hour and up. Untreated biogas may be used, but all
metal surfaces of the boiler housing should be painted to prevent corrosion.
Flame tube boilers with heavy gauge flame tubes may be used if the exhaust
temperature is maintained above 300 FACE= "Symbol">° F to prevent
condensation. Forced air furnaces can be used in place of direct fire room
heaters, but biogas must be treated to remove hydrogen sulfide because of
potential corrosion problems in metal ductwork. System
Performance and Benefits of AD There
are several measures of waste management system performance that are relevant
for producers considering
the use of AD. These include:
AD
is the only waste management strategy available that provides the option to
recover methane for energy production. The
APCD has determined that the minimum standard for compliance with odor control
regulations for waste vessels and impoundments is an 80 percent reduction in
all odor-causing gases, including hydrogen sulfide, ammonia and volatile
organic compounds from waste vessels or impoundments. Table 3 compares the
effectiveness of some of the odor control methods being implemented at covered
swine facilities in Table
3 . Odor control effectiveness of management strategies for anaerobic
lagoons
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