Abstract
The utilization of microbial activity to treat agricultural,
industrial, and domestic wastes has been common practice for a half century. In
recent years, biogas systems have attracted considerable attention as a
promising approach to decentralized rural development. Developed and developing
countries and several international organizations have shown interest in biogas
systems with respect to various objectives: a renewable source of energy,
bio-fertilizer, waste recycling, rural development, public health and hygiene,
pollution control, environmental management, appropriate technology, and
technical cooperation. This paper provides an overview of biogas technology and
opportunities to use this technology in livestock facilities across the ruler
area. First, a brief description of biogas technology is provided. Then the
benefits of biogas technology are discussed. Finally, the experience and status
of biogas technology development in the India are described.
Keywords-
Biogas, Fermentation, Methane, Rural Energy, Renewable Energy
1. Introduction
Developing-country rural areas have a variety of
available biomass materials, including fuel wood, agricultural wastes, and
animal wastes. In particular, many countries have large cattle and buffalo
herds, whose considerable wastes have much energy potential. Traditionally,
these wastes are carefully collected in India and used as fertilizer,
except in places where villagers are forced by the scarcity of fuel wood to
burn dung-cakes as cooking fuel. Since biogas plants yield sludge fertilizer,
the biogas fuel and/or electricity generated is a valuable additional bonus. It
is this bonus output that has motivated the large biogas programmes in a number
of developing countries, particularly India
Rural energy planning requires choices among energy
technologies. Up to the day, the choices have been confined to centralized
energy supply technologies - power plants based on hydroelectricity, coal, oil,
or natural gas. The problem is local and global environmental degradation. It
has, therefore, become essential to extend the list of technological alternatives
for energy decision-making to include decentralized sources of supply.
2.
Biogas
Biogas is actually a mixture of gases, usually carbon
dioxide and methane. It is produced by a few kinds of microorganisms, usually
when air or oxygen is absent. (The absence of oxygen is called "anaerobic
conditions.") Animals that eat a lot of plant material, particularly
grazing animals such as cattle, produce large amounts of biogas. The biogas is
produced not by the cows themselves, but by billions of microorganisms living
in their digestive systems. Biogas also develops in bogs and at the bottom of
lakes, where decaying organic matter builds up under wet and anaerobic
conditions.
Besides
being able to live without oxygen, methane-producing microorganisms have
another special feature: They are among the very few creatures that can digest
cellulose, the main ingredient of plant fibres. Another special feature of
these organisms is that they are very sensitive to conditions in their
environment, such as temperature, acidity, the amount of water, etc.
Methane, which is the main constituent a colourless,
odourless, inflammable gas, it has been referred to as sewerage gas, klar gas,
marsh gas, refuse-derived fuel (RDF), sludge gas, will-o'-the-wisp of marsh lands,
fool's fire, gobar gas (cow dung gas), bioenergy, and "fuel of the
future." The gas mixture produced is composed roughly of 65 percent CH4,
30 percent CO2, and 1 per cent H2S. A thousand cubic feet
of processed biogas is equivalent to 600 cubic feet of natural gas, 6.4 gallons
of butane, 5.2 gallons of gasoline, or 4.6 gallons of diesel oil. For cooking
and lighting, a family of four would consume 150 cubic feet of biogas per day,
an amount that is easily generated from the family's night soil and the dung of
three cows. In addition, rural housewives using the biofuel are spared the
irritating smoke resulting from the combustion of firewood; cattle dung cakes,
and the detritus of raw vegetables
3.
History of Biogas
People have been using biogas for over 200 years. In
the days before electricity, biogas was drawn from the underground sewer pipes
in London and
burned in street lamps, which were known as "gaslights." In many
parts of the world, biogas is used to heat and light homes, to cook, and even
to fuel buses. It is collected from large-scale sources such as landfills and
pig barns, and through small domestic or community systems in many villages.
The decomposition breaks down the organic matter,
releasing various gases. The main gases released are methane, carbon dioxide,
hydrogen and hydrogen sulphide. Bacteria carry out the decomposition or
fermentation. The conditions for creating biogas have to be anaerobic that is
without any air and in the presence of water. The organic waste matter is
generally animal or cattle dung, plant wastes, etc. These waste products
contain carbohydrates, proteins and fat material that are broken down by
bacteria. The waste matter is soaked in
water to give the bacteria a proper medium to grow. Absence of air or oxygen is
important
for decomposition because bacteria then take oxygen from the waste material
itself and in the process break them down.
4. Biogas is a Form of Renewable Energy
Flammable biogas can be collected using a simple tank, as shown here.
Animal manure is stored in a closed tank where the gas accumulates. It makes an
excellent fuel for cook stoves and furnaces, and can be used in place of
regular natural gas, which is a fossil fuel. Biogas is considered to be a
source of renewable energy. This is because the production of biogas depends on
the supply of grass, which usually grows back each year. By comparison, the
natural gas used in most of our homes is not considered a form of renewable
energy. Natural gas formed from the fossilized remains of plants and animals-a
process that took millions of years. These resources do not "grow
back" in a time scale that is meaningful for humans
Biogas generation cycle
There are two types of bio gas plants that are used in India. These
plants mainly use cattle dung called “gobar” and are hence called gobar gas
plant. Generally a slurry is made from cattle dung and water, which forms the
starting material for these plants.
The two types of bio gas plants are
1. Floating gas-holder type
1. Floating gas-holder type
2. Fixed dome type
Floating
gasholder type of plant: The diagram below shows the details of a floating
gasholder type of bio gas plant. A well is made out of concrete. This is called
the digester tank T. It is divided into two parts. One side has the inlet, from
where slurry is fed to the tank. The tank has a cylindrical dome H made of
stainless steel that floats on the slurry and collects the gas generated. Hence
the name given to this type of plant is floating gas holder type of bio gas
plant. The slurry is made to ferment for about 50 days. As more gas is made by
the bacterial fermentation, the pressure inside H increases. The gas can be
taken out through outlet pipe V. The
decomposed matter expands and overflows into the next chamber in tank T. This is then removed by the outlet pipe to
the overflow tank and is used as manure for cultivation purposes.
5.
Energy in Biogas
The
main problem in the economic evaluation is to allocate a suitable monetary
value to the non-commercial fuels, which have so far no market prices. For the
majority of rural households biogas is primarily a means of supplying energy
for daily cooking and for lighting. They use mainly firewood, dried cow dung
and harvest residues as fuel. But even if the particular household does not
purchase the required traditional fuel, it's value can be calculated with the
help of fuel prices on the local market. Theoretically, the firewood collector
of the family could sell the amount that is no longer needed in the household
As
an example, the rural households in India use the following quantities
of non-commercial fuel per capita daily:
-
firewood: 0.62 kg
-
dried cow dung: 0.34 kg
-
harvest residues: 0.20 kg
For rural households in the People's Republic of China the daily
consumption of
firewood
is similar: between 0.55 - 0.83 kg per person.
Which
sources of energy have been used so far and to what extent they can be replaced
must be determined for the economic evaluation of biogas by means of calorific
value relations. The monetary benefits of biogas depend mainly on how far
commercial fuels can be replaced and their respective price on the market.
1
m3 Biogas (approx. 6 kWh/m3) is equivalent to:
Diesel,
Kerosene (approx. 12 kWh/kg) 0.5 kg
Wood
(approx. 4.5 kWh/kg) 1.3 kg
Cow
dung (approx. 5 kWh/kg dry matter) 1.2 kg
Plant
residues (approx. 4.5 kWh/kg d.m.) 1.3 kg
Hard
coal (approx. 8.5 kWh/kg) 0.7 kg
City
gas (approx. 5.3 kWh/m3) 1.1 m3
Propane
(approx. 25 kWh/m3) 0.24 m3
6. The Benefits for Biogas
Individual
households judge the profitability of biogas plants primarily from the monetary
surplus gained from utilizing biogas and bio-fertilizer in relation to the cost
of the plants. The following effects, to be documented and provided with a
monetary value, should be listed as benefits: expenditure saved by the
substitution of other energy sources with biogas.
If
applicable, income from the sale of biogas; expenditure saved by the
substitution of mineral fertilizers with bio-fertilizer. Increased yield by
using bio-fertilizer. If applicable, income from the sale of bio-fertilizer;
savings in the cost of disposal and treatment of substrates (mainly for
waste-water treatment); time saved for collecting and preparing previously used
fuel materials (if applicable), time saved for work in the stable and for
spreading manure (if this time can be used to generate income). Monetarizing
individual benefits The economic evaluation of the individual benefits of
biogas plants is relatively simple if the users cover their energy and fertilizer
demands commercially. In general, the monetary benefits from biogas plants for
enterprises and institutions as well as from plants for well-to-do households
should be quite reliably calculable. These groups normally purchase commercial
fuels e.g. oil, gas and coal as well as mineral fertilizers. In industrialized
countries, it is common practice to feed surplus electric energy, produced by
biogas-driven generators, in the grid. Biogas slurry is a marketable product
and the infrastructure allows it's transport at reasonable cost. Furthermore,
treatment of waste and waste water is strictly regulated by law, causing
communes, companies and farmers expenses which, if reduced with the help of
biogas technology, are directly calculable benefits. In contrast, small farmers
in developing countries collect and use mostly traditional fuels and
fertilizers like wood, harvest residues and cow dung. No direct monetary
savings can be attributed to the use of biogas and bio-fertilizer. The monetary
value of biogas has to be calculated through the time saved for collecting
fuel, the monetary value for bio-fertilizer through the expected increase in
crop yields. Both in theory and in practice, this is problematic. In practice,
a farmer would not value time for fuel collection very highly as it is often
done by children or by somebody with low or no opportunity costs for his/her
labor. In theory, it is difficult to define the value of unskilled labor.
Similarly, the improved fertilizing value of biogas slurry will not be accepted
by most farmers as a basis for cost-benefit analysis. They tend to judge the
quality of slurry when counting the bags after harvest. Because a monetary
calculation is not the only factor featuring in the decision to construct and
operate a biogas plant, other factors come in which are less tangible:
convenience, comfort, status, security of supply and others that could be
subsumed under 'life quality'. Acceptance by the target group Besides the
willingness and ability to invest considerable funds in biogas technology,
there is a complex process of decision making involved when moving from
traditional practices to a 'modern' way of producing fertilizer and acquiring energy. Hopes and fears, expected
reactions from the society, previous experiences with modern technology, all
these feature in a decision. For a biogas program, it is important to realize
that economic considerations are only part of the deciding factors in favor or
against biogas technology. All these factors can be subsumed under acceptance.
Acceptance is not a collection of irrational, economically unjustifiable pros
and cons that a biogas extension project is called upon to dissolve. Rural
households, as a rule, take rational decisions. But rural households and biogas
programs often have information deficits that lead to non-acceptance of biogas
technology by the target groups. Bridging this information gap from the farmer
to the project and vice versa is a precondition for demonstrating the economic
viability in a way that is understandable, relevant and acceptable to the
farmer.
7. Biogas programs
Biogas
programs, however, should not neglect the argument of improved yields.
Increases in agricultural production as a result of
the use of bio-fertilizer of 6 - 10 % and in some cases of up to 20 % have been
reported. Although improved yields through biogas slurry are difficult to
capture in a stringent economic calculation, for demonstration and
farmer-to-farmer extension they are very effective. Farmers should be
encouraged to record harvests on their plots, before and after the introduction
of biogas. Statements of farmers like: "Since I use biogas slurry, I can
harvest two bags of maize more on this plot" may not convince economists,
but they are well understood by farmers.
As mentioned earlier, to tap the
potential of various renewable resources of energy, a variety of technology
dissemination programmes are being implemented by the government in active
collaboration with NGOs (non-governmental organizations), like TERI. In the last
two decades, complexities in rural energy planning have been seriously
considered and linked with overall development planning by way of decentralized
planning. Programmes are being implemented at block level, such as the IREP
(Integrated Rural Energy Programme), which was coordinated by the Energy Cell
of the Planning Commission. The MNES earlier started with village-level
planning and implementation of projects. Later, it attempted to develop a
methodology for district-level energy planning in select districts of the
country. In order to be more effective in implementation as well as
administration of energy activities, the MNES has now chosen to devise energy
plans at the block level. The studies are being undertaken in select 100 blocks
in different states.
8.
Conclusions-
Biomass is available all round the year. It
is cheap, widely available, easy to transport,
store, and has no environmental hazards.
It can be obtained from plantation of land having no competitive use.
Biomass-based power generation systems, linked to plantations on wasteland, simultaneously address the vital issues of wastelands development, environmental restoration, rural employment generation, and generation of power with no distribution losses.
It can be combined with production of other useful products, making it an attractive
byproduct.
Biogas,
although typically used for heating and cooking, can also be used to fuel a
genset to produce electricity. 3.4 million biogas digesters are in daily use in
India,
and smaller store, and has no environmental hazards.
It can be obtained from plantation of land having no competitive use.
Biomass-based power generation systems, linked to plantations on wasteland, simultaneously address the vital issues of wastelands development, environmental restoration, rural employment generation, and generation of power with no distribution losses.
It can be combined with production of other useful products, making it an attractive
byproduct.
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