Difference between revisions of "Biogas Basics"

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== What is biogas? ==
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[[Portal:Biogas|►Back to Biogas Portal]]
  
Biogas typically refers to a&nbsp; gas produced by the anaerobic digestion of organic matter including manure, sewage sludge, municipal solid waste, biodegradable waste or any other biodegradable feedstock, under anaerobic conditions. Biogas is comprised primarily of methane and carbon dioxide. It also contains smaller amounts of hydrogen sulphide, nitrogen, hydrogen, methylmercaptans and oxygen<ref name="Energy Technology">GTZ (2007): Eastern Africa Resource Base: GTZ Online Regional Energy Resource Base: Regional and Country Specific Energy Resource Database: I - Energy Technology</ref>.
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= Overview =
 +
 
 +
'''Biogas''' typically refers to a gas produced by the anaerobic digestion of organic matter including manure, sewage sludge, municipal solid waste, biodegradable waste or any other biodegradable feedstock, under anaerobic conditions. Biogas is comprised primarily of methane and carbon dioxide. It also contains smaller amounts of hydrogen sulphide, nitrogen, hydrogen, methylmercaptans and oxygen<ref name="Energy Technology">GTZ (2007): Eastern Africa Resource Base: GTZ Online Regional Energy Resource Base: Regional and Country Specific Energy Resource Database: I - Energy Technology</ref>.
  
 
Biogas originates from bacteria in the process of bio-degradation of organic material under anaerobic (without air) conditions. The natural generation of biogas is an important part of the biogeochemical carbon cycle. Methanogens (methane producing bacteria) are the last link in a chain of micro-organisms which degrade organic material and return the decomposition products to the environment. In this process biogas is generated, a source of renewable energy.
 
Biogas originates from bacteria in the process of bio-degradation of organic material under anaerobic (without air) conditions. The natural generation of biogas is an important part of the biogeochemical carbon cycle. Methanogens (methane producing bacteria) are the last link in a chain of micro-organisms which degrade organic material and return the decomposition products to the environment. In this process biogas is generated, a source of renewable energy.
  
== Biogas and the global carbon cycle ==
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The gases methane, hydrogen and carbon monoxide can be combusted or oxidized with oxygen. Air contains 21% oxygen. This energy release allows biogas to be used as a fuel. Biogas can be used as a low-cost fuel in any country for any heating purpose, such as cooking. It can also be utilized in modern waste management facilities where it can be used to run any type of heat engine, to generate either mechanical or electrical power. Biogas is a renewable fuel and electricity produced from it can be used to attract renewable energy subsidies in some parts of the world.
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 +
Below is the biogas equivalent to different fuels<ref name="https://energypedia.info/images/2/2e/Biogas_Technology.pdf">https://energypedia.info/images/2/2e/Biogas_Technology.pdf</ref>:
 +
 
 +
*1 Kg firewood => 0.2 m³ biogas
 +
*1 Kg dried cow dung => 0.1 m³ biogas
 +
*1 Kg Charcoal => 0.5 m³ biogas
 +
*1 Litre Kerosine => 2.0 m³ biogas
 +
 
 +
 
 +
= Anaerobic Fermentation =
 +
 
 +
Knowledge of the fundamental processes involved in methane fermentation is necessary for planning, building and operating biogas plants. [[Anaerobic Methods of Waste Treatment|Anaerobic fermentation]] involves the activities of three different bacterial communities. The process of biogas-production depends on [[Parameters and Process Optimisation for Biogas|various parameters]]. For example, changes in ambient temperature can have a negative effect on bacterial activity.
 +
 
 +
Biogas microbes consist of a large group of complex and differently acting microbe species, notably the methane-producing bacteria. The whole biogas-process can be divided into three steps: hydrolysis, acidification, and methane formation. Three types of bacteria are involved.
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 +
{| cellspacing="0" cellpadding="0" border="0" class="IMGcenter"
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|-
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| style="width: 45%" | <br/>
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| [[File:Fermscheme s.gif|border|right|550pxpx|The three stages of anaerobic fermentation of biomass|alt=Fermscheme s.gif]]<small class="IMGLEGEND">'''The three-stage anaerobic fermentation of biomass'''</small><ref name="Production and Utilization of Biogas in Rural Areas of Industrialized and Developing Countries, Schriftenreihe der gtz, No. 97, p. 54; after: Märkl, H.: Mikrobielle Methangewinnung; in: Fortschritte der Verfahrenstechnik, Vol. 18, p. 509, Düsseldorf, FRG">Production and Utilization of Biogas in Rural Areas of Industrialized and Developing Countries, Schriftenreihe der gtz, No. 97, p. 54; after: Märkl, H.: Mikrobielle Methangewinnung; in: Fortschritte der Verfahrenstechnik, Vol. 18, p. 509, Düsseldorf, FRG</ref>
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| style="width: 45%" | <br/>
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|}
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== Hydrolysis ==
 +
 
 +
In the first step (hydrolysis), the organic matter is enzymolyzed externally by extracellular enzymes (cellulase, amylase, protease and lipase) of microorganisms. Bacteria decompose the long chains of the complex carbohydrates, proteins and lipids into shorter parts. For example, polysaccharides are converted into monosaccharides. Proteins are split into peptides and amino acids.
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 +
<br/>
 +
 
 +
== Acidification ==
 +
 
 +
Acid-producing bacteria, involved in the second step, convert the intermediates of fermenting bacteria into acetic acid (CH<sub>3</sub>COOH), hydrogen (H<sub>2</sub>) and carbon dioxide (CO<sub>2</sub>). These bacteria are facultatively anaerobic and can grow under acid conditions. To produce acetic acid, they need oxygen and carbon. For this, they use the oxygen solved in the solution or bounded-oxygen. Hereby, the acid-producing bacteria create an anaerobic condition which is essential for the methane producing microorganisms. Moreover, they reduce the compounds with a low molecular weight into alcohols, organic acids, amino acids, carbon dioxide, hydrogen sulphide and traces of methane. From a chemical standpoint, this process is partially endergonic (i.e. only possible with energy input), since bacteria alone are not capable of sustaining that type of reaction.
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<br/>
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== Methanogenesis ==
  
Each year some 590-880 million tons of methane are released worldwide into the atmosphere through microbial activity. About 90% of the emitted methane derives from biogenic sources, i.e. from the decomposition of biomass. The remainder is of fossil origin (e.g. petrochemical processes). In the northern hemisphere, the present tropospheric methane concentration amounts to about 1.65 ppm.
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{| cellpadding="10" border="0" align="right" style="width: 297px" class="IMGright"
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|-
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| [[File:Bacteria.gif|border|297px|Bacteria.gif|alt=Bacteria.gif]]<small class="IMGLEGEND">'''Various types of methanogenic bacteria. The spherically shaped bacteria are of the ''methanosarcina'' genus; the long, tubular ones are ''methanothrix'' bacteria, and the short, curved rods are bacteria that catabolize furfural and sulfates. The total length of the broken bar at top left, which serves as a size reference, corresponds to 1 micron.'''</small><ref name="Production and Utilization of Biogas in Rural Areas of Industrialized and Developing Countries, Schriftenreihe der gtz, No. 97, p. 55">Production and Utilization of Biogas in Rural Areas of Industrialized and Developing Countries, Schriftenreihe der gtz, No. 97, p. 55</ref><br/>
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|}
  
== Biology of methanogenesis ==
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Methane-producing bacteria, involved in the third step, decompose compounds with a low molecular weight. For example, they utilize hydrogen, carbon dioxide and acetic acid to form methane and carbon dioxide. Under natural conditions, methane producing microorganisms occur to the extent that anaerobic conditions are provided, e.g. under water (for example in marine sediments), in ruminant stomachs and in marshes. They are obligatory anaerobic and very sensitive to environmental changes. In contrast to the acidogenic and acetogenic bacteria, the methanogenic bacteria belong to the archaebacter genus, i.e. to a group of bacteria with a very heterogeneous morphology and a number of common biochemical and molecular-biological properties that distinguish them from all other bacterial general. The main difference lies in the makeup of the bacteria's cell walls.
  
Knowledge of the fundamental processes involved in methane fermentation is necessary for planning, building and operating biogas plants. Anaerobic fermentation involves the activities of [[Microbiological Methanation|three different bacterial communities]]. The process of biogas-production depends on [[Parameters and Process Optimisation for Biogas|various parameters]]. For example, changes in ambient temperature can have a negative effect on bacterial activity.
+
<br/>
  
== Substrate and material balance of biogas production ==
+
== Symbiosis of Bacteria ==
  
In principle, all organic materials can ferment or be digested. However, only homogenous and liquid substrates can be considered for simple biogas plants: faeces and urine from cattle, pigs and possibly from poultry and the wastewater from toilets. When the plant is filled, the excrement has to be diluted with about the same quantity of liquid, if possible, the urine should be used. Waste and wastewater from food-processing industries are only suitable for simple plants if they are homogenous and in liquid form. The maximum of [[Utilization of Biogas#Gas_production|gas-production]] from a given amount of raw material depends on the type of [[Substrate Types and Management|substrate]].
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Methane- and acid-producing bacteria act in a symbiotic way. On the one hand, acid-producing bacteria create an atmosphere with ideal parameters for methane-producing bacteria (anaerobic conditions, compounds with a low molecular weight). On the other hand, methane-producing microorganisms use the intermediates of the acid-producing bacteria. Without consuming them, toxic conditions for the acid-producing microorganisms would develop.
  
== Composition and properties of biogas ==
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In practical fermentation processes the metabolic actions of various bacteria all act in concert. No single bacteria is able to produce fermentation products alone.
  
Biogas is a mixture of gases that is composed chiefly of:
 
  
*'''methane''' (CH<sub>4</sub>): 40-70 vol.%
 
*'''carbon dioxide''' (CO<sub>2</sub>): 30-60 vol.%
 
*'''other gases''': 1-5 vol.%; including hydrogen (H<sub>2</sub>: 0-1 vol.%) and hydrogen sulfide (H<sub>2</sub>S: 0-3 vol.%)
 
  
Like those of any pure gas, the '''characteristic properties''' of biogas are pressure and temperature-dependent. They are also affected by the moisture content. The factors of main interest are:
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= Composition and Properties of Biogas<br/> =
 +
 
 +
The composition of biogas varies depending upon the origin of the anaerobic digestion process. Landfill gas typically has methane concentrations around 50%. Advanced waste treatment technologies can produce biogas with 55-75% CH4.
 +
 
 +
<br/>
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{| class="wikitable FCK__ShowTableBorders" style="width: 100%;" border="1"
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|-
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| style="background: rgb(180, 238, 180); width: 50%; text-align: center;" | '''Component'''
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| style="background: rgb(180, 238, 180); text-align: center;" | '''Content [%]'''
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|-
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| Methane, CH<sub>4</sub>
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| 50-75
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|-
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| Carbon dioxide, CO<sub>2</sub>
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| 25-50
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|-
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| Nitrogen, N<sub>2</sub>
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| 0-10
 +
|-
 +
| Hydrogen, H<sub>2</sub>
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| 0-1
 +
|-
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| Hydrogen sulphide, H<sub>2</sub>S
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| 0-3
 +
|-
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| Oxygen, O<sub>2</sub>
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| 0-2
 +
|}
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 +
Like those of any pure gas, the '''characteristic properties''' of biogas are pressure and temperature-dependent.
 +
 
 +
<u>They are also affected by the moisture content. The factors of main interest are:</u>
  
 
*change in volume as a function of temperature and pressure,
 
*change in volume as a function of temperature and pressure,
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*change in water-vapor content as a function of temperature and pressure.
 
*change in water-vapor content as a function of temperature and pressure.
  
The '''calorific value''' of biogas is about 6 kWh/m<sup>3</sup> - this corresponds to about half a litre of diesel oil. The net calorific value depends on the efficiency of the [[Utilization of Biogas#Biogas_burners|burners]] or [[Biogas Appliances|appliances]]. Methane is the valuable component under the aspect of using biogas as a fuel.
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<br/>
  
== Utilization ==
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The '''calorific value''' of biogas is about 6 kWh/m<sup>3</sup> - this corresponds to about half a litre of diesel oil. The net calorific value depends on the efficiency of the [[Biogas Appliances#Two-flame Burners|burners]]&nbsp;or [[Biogas Appliances|appliances]]. Methane is the valuable component under the aspect of using biogas as a fuel.
  
The [[History of Biogas|history]] of biogas utilization shows independent developments in various developing and industrialized countries. The European biogas-history and that of Germany in particular, as well as developments in [[History of Biogas#China_and_India|Asian countries]] form the background of German efforts and programmes to promote biogas technology worldwide.
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<br/>
  
Normally, the biogas produced by a digester can be used as it is, just in the same way as any other combustible gas. But it is possible that a [[Utilization of Biogas#Conditioning_of_biogas|further treatment or conditioning]] is necessary, for example, to reduce the hydrogen-sulfide content in the gas. When biogas is mixed with air at a ratio of 1:20, a highly explosive gas forms. Leaking gas pipes in enclosed spaces constitute, therefore, a hazard. However, there have been no reports of dangerous explosions caused by biogas so far.
 
  
A first overview of the [[Types of Biogas Digesters and Plants|physical appearance]] of different types of biogas plants describes the three main types of simple biogas plants, namely balloon plants, fixed-dome plants and floating-drum plants.
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= Substrate and Material Balance =
  
== Applications of Biogas<br/> ==
+
In principle, all organic materials can ferment or be digested. However, only homogenous and liquid substrates can be considered for simple biogas plants: [[Annual_Manure_Yield_and_Nutrient_Content_of_Animal_Excrements|faeces and urine from cattle, pigs and possibly from poultry]] and the wastewater from toilets. When the plant is filled, the substrate has to be diluted with about the same quantity of liquid, if possible, the urine should be used. Waste and wastewater from food-processing industries are only suitable for simple plants if they are homogenous and in liquid form. The maximum of gas production from a given amount of raw material depends on the type of substrate.
  
Biogas can be used for direct combustion in cooking or lighting applications; and to power combustion engines for motive power or electricity generation. The technology is particularly valuable in agricultural, waste treatment or animal processing units where there is excess manure, farm waste or municipal waste. Typical applications in off grid settings in developing regions are cooking and lighting<ref name="Energy Technology">GTZ (2007): Eastern Africa Resource Base: GTZ Online Regional Energy Resource Base: Regional and Country Specific Energy Resource Database: I - Energy Technology</ref>.
+
<br/>
  
== The Benefits of Biogas Technology<br/> ==
+
= Benefits of Biogas Technology<br/> =
  
Well-functioning biogas systems can yield a whole range of [[Benefits for Biogas Users|benefits for their users]], the society and the [[Environmental Benefits of Biogas Technology|environment]] in general:
+
<u>Well-functioning biogas systems can yield a whole range of benefits for their users, the society and the environment in general:</u>
  
 
*production of energy (heat, light, electricity);
 
*production of energy (heat, light, electricity);
 
*transformation of organic waste into high quality fertilizer;
 
*transformation of organic waste into high quality fertilizer;
 +
*reduction of volume of disposed waste products;
 
*improvement of hygienic conditions through reduction of pathogens, worm eggs and flies;
 
*improvement of hygienic conditions through reduction of pathogens, worm eggs and flies;
 +
*encouragement of better sanitation;
 
*reduction of workload, mainly for women, in firewood collection and cooking.
 
*reduction of workload, mainly for women, in firewood collection and cooking.
 
*environmental advantages through protection of soil, water, air and woody vegetation;
 
*environmental advantages through protection of soil, water, air and woody vegetation;
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*macro-economical benefits through decentralized energy generation, import substitution and environmental protection
 
*macro-economical benefits through decentralized energy generation, import substitution and environmental protection
  
Thus, biogas technology can substancially [[Contribution of Biogas Technology to Conservation and Development|contribute to conservation and development]], if the concrete [[Contribution of Biogas Technology to Conservation and Development#Under_which_conditions_can_biogas_technology_contribute_to_development_and_conservation.3F|conditions are favorable]]. However, the required high investment capital and other [[Limitations of Biogas Technology|limitations of biogas technology]] should be thoroughly considered.
+
Thus, biogas technology can substantially [[Biogas_Technology_for_Development|contribute to conservation and development]], if the concrete [[Biogas_Framework|conditions are favorable]]. However, the required high investment capital and other [[Limitations_of_Biogas_Technology|limitations of biogas technology]] should be thoroughly considered.
  
== The Costs of Biogas Technology ==
+
► Also see: [[Biogas_-_Costs_and_Benefits|Biogas - Costs and Benefits]]
  
An obvious obstacle to the large-scale introduction of biogas technology is the fact that the poorer strata of rural populations often cannot afford the [[Costs of a Biogas Plant|investment cost]] for a biogas plant. This is despite the fact that biogas systems have proven economically viable investments in many cases.
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== Fertilizer from Biogas Plants ==
  
Efforts have to be made to reduce construction cost but also to develop [[Financing and public support for Biogas Plants|credit and other financing systems]]. A larger numbers of biogas operators ensures that, apart from the private user, the society as a whole can benefit from biogas. Financial support from the government can be seen as an investment to reduce future costs, incurred through the importation of petrol products and inorganic fertilizers, through increasing costs for health and hygiene and through natural resource degradation.
+
In developing countries, there is a direct link between the problem of fertilization and progressive [[Environmental_Frame_Conditions_of_Biogas_Technology|deforestation due to high demand for firewood]]. In many rural areas, most of the inhabitants are dependant on dung and organic residue as fuel for cooking and heating. Such is the case, for example, in the treeless regions of India (Ganges plains, central highlands), Nepal and other countries of Asia, as well as in the Andes Mountains of South America and wide expanses of the African Continent. According to data published by the FAO, some 78 million tons of cow dung and 39 million tons of phytogenic waste were burned in India alone in 1970. That amounts to approximately 35% of India's total noncommercial/nonconventional energy consumption.
  
== Fuel and Fertilizer ==
+
The burning of dung and plant residue is a considerable waste of plant nutrients. Farmers in developing countries are in dire need of fertilizer for maintaining cropland productivity. Nonetheless, many small farmers continue to burn potentially valuable fertilizers, even though they cannot afford to buy chemical fertilizers. At the same time, the amount of technically available nitrogen, potassium and phosphorous in the form of organic materials is around eight times as high as the quantity of chemical fertilizers actually consumed in developing countries. Especially for small farmers, biogas technology is a suitable tool for making maximum use of scarce resources: After extraction of the energy content of dung and other organic waste material, the resulting sludge is still a good [[Organic_Fertilizer_from_Biogas_Plants|fertilizer]], supporting general soil quality as well as higher crop yields.
  
In developing countries, there is a direct link between the problem of fertilization and progressive [[Environmental Frame Conditions of Biogas Technology|deforestation due to high demand for firewood]]. In many rural areas, most of the inhabitants are dependant on dung and organic residue as fuel for cooking and heating. Such is the case, for example, in the treeless regions of India (Ganges plains, central highlands), Nepal and other countries of Asia, as well as in the Andes Mountains of South America and wide expanses of the African Continent. According to data published by the FAO, some 78 million tons of cow dung and 39 million tons of phytogenic waste were burned in India alone in 1970. That amounts to approximately 35% of India's total noncommercial/nonconventional energy consumption.
+
► Also see: [[Organic_Fertilizer_from_Biogas_Plants|Organic Fertilizer from Biogas Plants]]
  
The burning of dung and plant residue is a considerable waste of plant nutrients. Farmers in developing countries are in dire need of fertilizer for maintaining cropland productivity. Nonetheless, many small farmers continue to burn potentially valuable fertilizers, even though they cannot afford to buy chemical fertilizers. At the same time, the amount of technically available nitrogen, pottasium and phosphorous in the form of organic materials is around eight times as high as the quantity of chemical fertilizers actually consumed in developing countries. Especially for small farmers, biogas technology is a suitable tool for making maximum use of scarce resources: After extraction of the energy content of dung and other organic waste material, the resulting sludge is still a good [[Organic Fertilizer from Biogas Plants|fertilizer]], supporting general soil quality as well as higher crop yields.
+
<br/>
  
== Public and Political Awareness ==
+
= Further Information<br/> =
  
Popularization of biogas technology has to go hand in hand with the actual construction of plants in the field. Without the [[Information and Public Relation Campaigns for Biogas|public awareness]] of biogas technology, its benefits and pitfalls, there will be no sufficient basis to disseminate biogas technology at grassroots level. At the same time, awareness within the government is essential. Since impacts and aspects of biogas technology concern so many different governmental institutions (e.g. agriculture, environment, energy, economics), it is necessary to identify and include all responsible government departments in the dissemination and awareness-raising process.
+
*[[Portal:Biogas|Biogas Portal on energypedia]]
 +
*[https://www.dropbox.com/sh/duyqp3mny5vdpoy/526VFrVTG2 Books on Biogas Basics]
 +
*[https://www.dropbox.com/sh/3tcze3qc1tn5cgq/b7ryEgR5FQ Presentations on Biogas Basics]
 +
*[https://www.dropbox.com/sh/hlogu3q3x2ll9gz/Dbq4EgIKAP Surveys and Reports on Biogas Basics]
 +
*[https://www.dropbox.com/sh/d3mynngyf4n8jxs/PhPLQEOurr Other files related to Biogas]
 +
*[http://www.biogas-zentrum.de/ibbk/aktuell.php Biogas-Zentrum: Biogas & IBBK Bioenergie]
 +
*[http://practicalaction.org/biogas Practical Action - Biogas, power from cow dung]
  
== References<br/> ==
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<br/>
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= References<br/> =
  
 
<references />
 
<references />
 
[[Biogas| back to "Biogas Portal"]]
 
  
 
[[Category:Biogas]]
 
[[Category:Biogas]]
 +
[[Category:Impacts]]

Latest revision as of 11:19, 19 September 2018

►Back to Biogas Portal

Overview

Biogas typically refers to a gas produced by the anaerobic digestion of organic matter including manure, sewage sludge, municipal solid waste, biodegradable waste or any other biodegradable feedstock, under anaerobic conditions. Biogas is comprised primarily of methane and carbon dioxide. It also contains smaller amounts of hydrogen sulphide, nitrogen, hydrogen, methylmercaptans and oxygen[1].

Biogas originates from bacteria in the process of bio-degradation of organic material under anaerobic (without air) conditions. The natural generation of biogas is an important part of the biogeochemical carbon cycle. Methanogens (methane producing bacteria) are the last link in a chain of micro-organisms which degrade organic material and return the decomposition products to the environment. In this process biogas is generated, a source of renewable energy.

The gases methane, hydrogen and carbon monoxide can be combusted or oxidized with oxygen. Air contains 21% oxygen. This energy release allows biogas to be used as a fuel. Biogas can be used as a low-cost fuel in any country for any heating purpose, such as cooking. It can also be utilized in modern waste management facilities where it can be used to run any type of heat engine, to generate either mechanical or electrical power. Biogas is a renewable fuel and electricity produced from it can be used to attract renewable energy subsidies in some parts of the world.

Below is the biogas equivalent to different fuels[2]:

  • 1 Kg firewood => 0.2 m³ biogas
  • 1 Kg dried cow dung => 0.1 m³ biogas
  • 1 Kg Charcoal => 0.5 m³ biogas
  • 1 Litre Kerosine => 2.0 m³ biogas


Anaerobic Fermentation

Knowledge of the fundamental processes involved in methane fermentation is necessary for planning, building and operating biogas plants. Anaerobic fermentation involves the activities of three different bacterial communities. The process of biogas-production depends on various parameters. For example, changes in ambient temperature can have a negative effect on bacterial activity.

Biogas microbes consist of a large group of complex and differently acting microbe species, notably the methane-producing bacteria. The whole biogas-process can be divided into three steps: hydrolysis, acidification, and methane formation. Three types of bacteria are involved.


Fermscheme s.gif
The three-stage anaerobic fermentation of biomass[3]

Hydrolysis

In the first step (hydrolysis), the organic matter is enzymolyzed externally by extracellular enzymes (cellulase, amylase, protease and lipase) of microorganisms. Bacteria decompose the long chains of the complex carbohydrates, proteins and lipids into shorter parts. For example, polysaccharides are converted into monosaccharides. Proteins are split into peptides and amino acids.


Acidification

Acid-producing bacteria, involved in the second step, convert the intermediates of fermenting bacteria into acetic acid (CH3COOH), hydrogen (H2) and carbon dioxide (CO2). These bacteria are facultatively anaerobic and can grow under acid conditions. To produce acetic acid, they need oxygen and carbon. For this, they use the oxygen solved in the solution or bounded-oxygen. Hereby, the acid-producing bacteria create an anaerobic condition which is essential for the methane producing microorganisms. Moreover, they reduce the compounds with a low molecular weight into alcohols, organic acids, amino acids, carbon dioxide, hydrogen sulphide and traces of methane. From a chemical standpoint, this process is partially endergonic (i.e. only possible with energy input), since bacteria alone are not capable of sustaining that type of reaction.


Methanogenesis

Bacteria.gifVarious types of methanogenic bacteria. The spherically shaped bacteria are of the methanosarcina genus; the long, tubular ones are methanothrix bacteria, and the short, curved rods are bacteria that catabolize furfural and sulfates. The total length of the broken bar at top left, which serves as a size reference, corresponds to 1 micron.[4]

Methane-producing bacteria, involved in the third step, decompose compounds with a low molecular weight. For example, they utilize hydrogen, carbon dioxide and acetic acid to form methane and carbon dioxide. Under natural conditions, methane producing microorganisms occur to the extent that anaerobic conditions are provided, e.g. under water (for example in marine sediments), in ruminant stomachs and in marshes. They are obligatory anaerobic and very sensitive to environmental changes. In contrast to the acidogenic and acetogenic bacteria, the methanogenic bacteria belong to the archaebacter genus, i.e. to a group of bacteria with a very heterogeneous morphology and a number of common biochemical and molecular-biological properties that distinguish them from all other bacterial general. The main difference lies in the makeup of the bacteria's cell walls.


Symbiosis of Bacteria

Methane- and acid-producing bacteria act in a symbiotic way. On the one hand, acid-producing bacteria create an atmosphere with ideal parameters for methane-producing bacteria (anaerobic conditions, compounds with a low molecular weight). On the other hand, methane-producing microorganisms use the intermediates of the acid-producing bacteria. Without consuming them, toxic conditions for the acid-producing microorganisms would develop.

In practical fermentation processes the metabolic actions of various bacteria all act in concert. No single bacteria is able to produce fermentation products alone.


Composition and Properties of Biogas

The composition of biogas varies depending upon the origin of the anaerobic digestion process. Landfill gas typically has methane concentrations around 50%. Advanced waste treatment technologies can produce biogas with 55-75% CH4.


Component Content [%]
Methane, CH4 50-75
Carbon dioxide, CO2 25-50
Nitrogen, N2 0-10
Hydrogen, H2 0-1
Hydrogen sulphide, H2S 0-3
Oxygen, O2 0-2

Like those of any pure gas, the characteristic properties of biogas are pressure and temperature-dependent.

They are also affected by the moisture content. The factors of main interest are:

  • change in volume as a function of temperature and pressure,
  • change in calorific value as a function of temperature, pressure and water-vapor content, and
  • change in water-vapor content as a function of temperature and pressure.


The calorific value of biogas is about 6 kWh/m3 - this corresponds to about half a litre of diesel oil. The net calorific value depends on the efficiency of the burners or appliances. Methane is the valuable component under the aspect of using biogas as a fuel.



Substrate and Material Balance

In principle, all organic materials can ferment or be digested. However, only homogenous and liquid substrates can be considered for simple biogas plants: faeces and urine from cattle, pigs and possibly from poultry and the wastewater from toilets. When the plant is filled, the substrate has to be diluted with about the same quantity of liquid, if possible, the urine should be used. Waste and wastewater from food-processing industries are only suitable for simple plants if they are homogenous and in liquid form. The maximum of gas production from a given amount of raw material depends on the type of substrate.


Benefits of Biogas Technology

Well-functioning biogas systems can yield a whole range of benefits for their users, the society and the environment in general:

  • production of energy (heat, light, electricity);
  • transformation of organic waste into high quality fertilizer;
  • reduction of volume of disposed waste products;
  • improvement of hygienic conditions through reduction of pathogens, worm eggs and flies;
  • encouragement of better sanitation;
  • reduction of workload, mainly for women, in firewood collection and cooking.
  • environmental advantages through protection of soil, water, air and woody vegetation;
  • micro-economical benefits through energy and fertilizer substitution, additional income sources and increasing yields of animal husbandry and agriculture;
  • macro-economical benefits through decentralized energy generation, import substitution and environmental protection

Thus, biogas technology can substantially contribute to conservation and development, if the concrete conditions are favorable. However, the required high investment capital and other limitations of biogas technology should be thoroughly considered.

► Also see: Biogas - Costs and Benefits

Fertilizer from Biogas Plants

In developing countries, there is a direct link between the problem of fertilization and progressive deforestation due to high demand for firewood. In many rural areas, most of the inhabitants are dependant on dung and organic residue as fuel for cooking and heating. Such is the case, for example, in the treeless regions of India (Ganges plains, central highlands), Nepal and other countries of Asia, as well as in the Andes Mountains of South America and wide expanses of the African Continent. According to data published by the FAO, some 78 million tons of cow dung and 39 million tons of phytogenic waste were burned in India alone in 1970. That amounts to approximately 35% of India's total noncommercial/nonconventional energy consumption.

The burning of dung and plant residue is a considerable waste of plant nutrients. Farmers in developing countries are in dire need of fertilizer for maintaining cropland productivity. Nonetheless, many small farmers continue to burn potentially valuable fertilizers, even though they cannot afford to buy chemical fertilizers. At the same time, the amount of technically available nitrogen, potassium and phosphorous in the form of organic materials is around eight times as high as the quantity of chemical fertilizers actually consumed in developing countries. Especially for small farmers, biogas technology is a suitable tool for making maximum use of scarce resources: After extraction of the energy content of dung and other organic waste material, the resulting sludge is still a good fertilizer, supporting general soil quality as well as higher crop yields.

► Also see: Organic Fertilizer from Biogas Plants


Further Information


References

  1. GTZ (2007): Eastern Africa Resource Base: GTZ Online Regional Energy Resource Base: Regional and Country Specific Energy Resource Database: I - Energy Technology
  2. https://energypedia.info/images/2/2e/Biogas_Technology.pdf
  3. Production and Utilization of Biogas in Rural Areas of Industrialized and Developing Countries, Schriftenreihe der gtz, No. 97, p. 54; after: Märkl, H.: Mikrobielle Methangewinnung; in: Fortschritte der Verfahrenstechnik, Vol. 18, p. 509, Düsseldorf, FRG
  4. Production and Utilization of Biogas in Rural Areas of Industrialized and Developing Countries, Schriftenreihe der gtz, No. 97, p. 55