METHODS OF GENERATING ENERGY FROM BIOMASS
Nearly all types of raw
biomass decompose rather quickly, so few are very good long-term energy stores;
and because of their relatively low energy densities, they are likely to be
rather expensive to transport over appreciable distances. Recent years have
therefore seen considerable effort devoted to the search for the best ways to
use these potentially valuable sources of energy. In considering the
methods for extracting the energy, it is possible to order them by the
complexity of the processes involved:
Direct
combustion of biomass.
Thermochemical processing to upgrade
the biofuel. Processes in this category include pyrolysis, gasification and
liquefaction.
Biological processing. Natural processes such as anaerobic
digestion and fermentation which lead to a useful gaseous or liquid fuel.
The immediate ‘product, of some of these processes is heat - normally used
at place of production or at not too great a distance, for chemical processing
or district heating, or to generate steam for power production. For other
processes the product is a solid, liquid or gaseous fuel: charcoal, liquid fuel
as a petrol substitute or additive, gas for sale or for power generation using
either steam or gas turbines.
COMBUSTION
The technology of direct combustion
as the most obvious way of extracting energy from biomass is well understood,
straightforward and commercially available. Combustion systems come in a wide
range of shapes and sizes burning virtually any kind of fuel, from chicken
manure and straw bales to tree trunks, municipal refuse and scrap tyres. Some of
the ways in which heat from burning wastes is currently used include space and
water heating, industrial processing and electricity generation. One problem
with this method is its very low efficiency. With an open fire most of the heat
is wasted and is not used to cook or whatever.
Combustion of wood can be divided into four phases:
Water inside
the wood boils off. Even wood that has been dried for ages has as much as 15 to
20% of water in its cell structure.
Gas content is freed from the wood.
It is vital that these gases should burn and not just disappear up the
chimney.
The gases emitted mix with atmospheric air and burn at a high
temperature.
The rest of the wood (mostly carbon) burns. In perfect combustion
the entire energy is utilised and all that is left is a little pile of
ashes.
Three things are needed for effective burning:
high enough
temperatures;
enough air, and
enough time for full combustion.
If not enough air gets in, combustion is incomplete and the smoke is black
from the unburned carbon. It smells terrible, and you get soot deposited in the
chimney, with the risk of fire. If too much air gets in the temperature drops
and the gases escape unburned, taking the heat with them. The right amount of
air gives the best utilisation of fuel. No smell, no smoke, and very little risk
of chimney fires. Regulation of the air supply depends largely on the chimney
and the draught it can put up. Direct combustion is the simplest and
most common method of capturing the energy contained within biomass. Boiling a
pan of water over a wood fire is a simple process. Unfortunately, it is also
very inefficient, as a little elementary calculation reveals. The
energy content of a cubic metre dry wood is 10 GJ, which is ten million kJ. To
raise the temperature of a litre of water by 1 degree Celsius requires 4,2 kJ of
heat energy. Bringing a litre to the boil should therefore require rather less
than 400 kJ, equivalent to 40 cubic centimetres of wood - one small stick,
perhaps. In practice, with a simple open fire we might need at least fifty times
this amount: a conversion efficiency no better than 2%. Designing a
stove or boiler which will make rather better use of valuable fuel requires an
understanding of the processes involved in the combustion of a solid fuel. The
first is one which consumes rather than produces energy: the evaporation of any
water in the fuel. With reasonably dry fuel, however, this uses only a few
percent of the total energy. In the combustion process itself there are always
two stages, because any solid fuel contains two combustible constituents. The
volatile matter is released as a mixture of vapours or vaporised tars and oils
by the fuel as its temperature rises. The combustion of these produces the
little spurts of pyrolysis. Modern combustion facilities (boilers)
usually produce heat, steam (used in industrial process) or electricity. Direct
combustion systems vary considerably in their design. The fuel choice makes a
difference in the design and efficiency of the combustion system. Direct
combustion technology using biomass as the fuel is very similar to that used for
coal. Biomass and coal can be handled and burned in essentially the same
fashion. In fact, biomass can be “co-fired” with coal in small percentages in
existing boilers. The biomass which is co-fired are usually low-cost feedstocks,
like wood or agricultural waste, which also help to reduce the emissions
typically associated with coal. Coal is simply fossilized biomass heated and
compressed over millions of years. The process which coal undergoes as it is
heated and compressed deep within the earth, adds elements like sulphur and
mercury to the coal. Burning coal for heat or electricity releases these
elements, which biomass does not contain.
PYROLYSIS
Pyrolysis is the simplest and almost certainly the
oldest method of processing one fuel in order to produce a better one. A wide
range of energy-rich fuels can be produced by roasting dry wood or even the
straw. The process has been used for centuries to produce charcoal. Conventional
pyrolysis involves heating the original material (which is often pulverised or
shredded then fed into a reactor vessel) in the near-absence of air, typically
at 300 - 500 °C, until the volatile matter has been driven off. The residue is
then the char - more commonly known as charcoal - a fuel which has about twice
the energy density of the original and burns at a much higher temperature. For
many centuries, and in much of the world still today, charcoal is produced by
pyrolysis of wood. Depending on the moisture content and the efficiency of the
process, 4-10 tonnes of wood are required to produce one tonne of charcoal, and
if no attempt is made to collect the volatile matter, the charcoal is obtained
at the cost of perhaps two-thirds of the original energy content.
Pyrolysis can also be carried out in the presence of a small quantity of
oxygen (‘gasification’), water (‘steam gasification’) or hydrogen
(‘hydrogenation’). One of the most useful products is methane, which is a
suitable fuel for electricity generation using high-efficiency gas turbines.
With more sophisticated pyrolysis techniques, the volatiles can be
collected, and careful choice of the temperature at which the process takes
place allows control of their composition. The liquid product has potential as
fuel oil, but is contaminated with acids and must be treated before use. Fast
pyrolysis of plant material, such as wood or nutshells, at temperatures of
800-900 degrees Celsius leaves as little as 10% of the material as solid char
and converts some 60% into a gas rich in hydrogen and carbon monoxide. This
makes fast pyrolysis a competitor with conventional gasification methods (see
bellow), but like the latter, it has yet to be developed as a treatment for
biomass on a commercial scale. At present, conventional pyrolysis is
considered the more attractive technology. The relatively low temperatures mean
that fewer potential pollutants are emitted than in full combustion, giving
pyrolysis an environmental advantage in dealing with certain wastes. There have
been some trials with small-scale pyrolysis plants treating wastes from the
plastics industry and also used tyres - a disposal problem of increasingly
urgent concern.
GASIFICATION
The basic principles of gasification have been
under study and development since the early nineteenth century, and during the
Second World War nearly a million biomass gasifier-powered vehicles were used in
Europe. Interest in biomass gasification was revived during the “energy crisis”
of the 1970s and slumped again with the subsequent decline of oil prices in the
1980s. The World Bank (1989) estimated that only 1000 - 3000 gasifiers have been
installed globally, mostly small charcoal gasifiers in South America.
Gasification based on wood as a fuel produces a flammable gas mixture of
hydrogen, carbon monoxide, methane and other non flammable by products. This is
done by partially burning and partially heating the biomass (using the heat from
the limited burning) in the presence of charcoal (a natural by-product of
burning biomass). The gas can be used instead of petrol and reduces the power
output of the car by 40%. It is also possible that in the future this fuel could
be a major source of energy for power stations.
SYNTHETIC FUELS
A gasifier which uses oxygen rather than air
can produce a gas consisting mainly of H2, CO and C02, and the interesting
potential of this lies in the fact that removal of the C02 leaves the mixture
called synthesis gas, from which almost any hydrocarbon compound may be
synthesised. Reacting the H2 and CO is one way to produce pure methane. Another
possible product is methanol (CH3OH), a liquid hydrocarbon with an energy
density of 23 GJ per tonne. Producing methanol in this way involves a series of
sophisticated chemical processes with high temperatures and pressures and
expensive plant, and one might wonder why it is of interest. The answer lies in
the product: methanol is that valuable commodity, a liquid fuel which is a
direct substitute for gasoline. At present the production of methanol using
synthesis gas from biomass is not a commercial proposition, but the technology
already exists, having been developed for use with coal as feedstock - as a
precaution by coal-rich countries at times when their oil supplies were
threatened.
FERMENTATION
Fermentation of sugar solution is the way how
ethanol (ethyl alcohol) can be produced. Ethanol is a very high liquid energy
fuel which can be used as the substitute for gasoline in cars. This fuel
is used successfully in Brazil. Suitable feedstocks include crushed sugar beet
or fruit. Sugars can also be manufactured from vegetable starches and cellulose
by pulping and cooking, or from cellulose by milling and treatment with hot
acid. After about 30 hours of fermentation, the brew contains 6-10 per cent
alcohol, which can be removed by distillation as a fuel. Fermentation
is an anaerobic biological process in which sugars are converted to alcohol by
the action of micro-organisms, usually yeast. The resulting alcohol is ethanol
(C2H3OH) rather than methanol (CH3OH), but it too can be used in internal
combustion engines, either directly in suitably modified engines or as a
gasoline extender in gasohol: gasoline (petrol) containing up to 20%
ethanol. The value of any particular type of biomass as feedstock for
fermentation depends on the ease with which it can be converted to sugars. The
best known source of ethanol is sugar-cane - or the molasses remaining after the
cane juice has been extracted. Other plants whose main carbohydrate is starch
(potatoes, corn and other grains) require processing to convert the starch to
sugar. This is commonly carried out, as in the production of some alcoholic
drinks, by enzymes in malts. Even wood can act as feedstock, but its
carbohydrate, cellulose, is resistant to breakdown into sugars by acid or
enzymes (even in finely divided forms such as sawdust), adding further
complication to the process. The liquid resulting from fermentation
contains only about 10% ethanol, which must be distilled off before it can be
used as fuel. The energy content of the final product is about 30 GJ/t, or 24
GJ/m3. The complete process requires a considerable amount of heat, which is
usually supplied by crop residues (e.g. sugar cane bagasse or maize stalks and
cobs). The energy loss in fermentation is substantial, but this may be
compensated for by the convenience and transportability of the liquid fuel, and
by the comparatively low cost and familiarity of the technology.
ANAEROBIC DIGESTION
Nature has a provision of destroying and
disposing of wastes and dead plants and animals. Tiny micro-organisms called
bacteria carry out this decay or decomposition. The farmyard manure and compost
is also obtained through decomposition of organic matter. When a heap of
vegetable or animal matter and weeds etc. die or decompose at the bottom of back
water or shallow lagoons then the bubbles can be noticed rising to the surface
of water. Some times these bubbles burn with flame at dusk. This phenomenon was
noticed for ages, which puzzled man for a long time. It was only during the last
200 years or so when scientists unlocked this secret, as the decomposition
process that takes place under the absence of air (oxygen). This gas, production
of which was first noticed in marshy places, was and is still called as ‘Marsh
Gas’. It is now well known that this gas (Marsh Gas) is a mixture of Methane
(CH4) and Carbon dioxide (CO2) and is commonly called as the ‘Biogas’. As per
records biogas was first discovered by Alessandro Volta in 1776 and Humphery
Davy was the first to pronounce the presence of combustible gas Methane in the
Farmyard Manure in as early as 1800. The technology of scientifically harnessing
this gas from any biodegradable material (organic matter) under artificially
created conditions is known as biogas technology.
Anaerobic digestion, like pyrolysis, occurs in the absence of air; but in
this case the decomposition is caused by bacterial action rather than high
temperatures. It is a process which takes place in almost any biological
material, but is favoured by warm, wet and of course airless conditions. It
occurs naturally in decaying vegetation on the bottom of ponds, producing the
marsh gas which bubbles to the surface and can even catch fire.
Anaerobic digestion also occurs in situations created by human
activities. One is the biogas which is generated in concentrations of sewage or
animal manure, and the other is the landfill gas produced by domestic refuse
buried in landfill sites. In both cases the resulting gas is a mixture
consisting mainly of methane and carbon dioxide; but major differences in the
nature of the input, the scale of the plant and the time-scale for gas
production lead to very different technologies for dealing with the two
sources. The detailed chemistry of the production of biogas and
landfill gas is complex, but it appears that a mixed population of bacteria
breaks down the organic material into sugars and then into various acids which
are decomposed to produce the final gas, leaving an inert residue whose
composition depends on the type of system and the original feedstock.
BIOGAS
is a valuable fuel which is in many countries produced
in purpose built digesters filled with the feedstock like dung or sewage.
Digesters range in size from one cubic metre for a small ‘household’ unit to
more than thousand cubic meters used in large commercial installation or farm
plants. The input may be continuous or in batches, and digestion is allowed to
continue for a period of from ten days to a few weeks. The bacterial action
itself generates heat, but in cold climates additional heat is normally required
to maintain the ideal process temperature of at least 35 degrees Celsius, and
this must be provided from the biogas. In extreme cases all the gas may be used
for this purpose, but although the net energy output is then zero, the plant may
still pay for itself through the saving in fossil fuel which would have been
needed to process the wastes. A well-run digester will produce 200-400 m3 of
biogas with a methane content of 50% to 75% for each dry tonne of input.

Digestors - outside view.

Digestor from inside.
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Biogas plant with integrated gas holder.

Biogas plant with separate gas holder.
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LANDFILL GAS
A
large proportion of ordinary domestic refuse - municipal solid wastes - is
biological material and its disposal in landfills creates suitable conditions
for anaerobic digestion. That landfill sites produce methane has been known for
decades, and recognition of the potential hazard led to the fitting of systems
for burning it off; however, it was only in the 1970s that serious attention was
paid to the idea of using this ‘undesirable’ product. The waste
matter is more miscellaneous in a landfill than in a biogas digester, and the
conditions neither as warm nor as wet, so the process is much slower, taking
place over years rather than weeks. The end product, known as landfill gas, is
again a mixture consisting mainly of CH4 and CO2. In theory, the lifetime yield
of a good site should lie in the range 150-300 m3 of gas per tonne of wastes,
with between 50% and 60% by volume of methane. This suggests a total energy of
5-6 GJ per tonne of refuse, but in practice yields are much less. In
developing a site, each area is covered with a layer of impervious clay or
similar material after it is filled, producing an environment which encourages
anaerobic digestion. The gas is collected by an array of interconnected
perforated pipes buried at depths up to 20 metres in the refuse. In new sites
this pipe system is constructed before the wastes start to arrive, and in a
large well-established landfill there can be several miles of pipes, with as
much as 1000 m3 an hour of gas being pumped out. Increasingly, the
gas from landfill sites is used for power generation. At present most plants are
based on large internal combustion engines, such as standard marine engines.
Driving 500 kW generators, these are well matched to typical gas supply rates of
the order of 10 GJ an hour.
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