Background Note
The basics of biochar
Online only 10 September 2009
Anita
Talberg
Science, Technology, Environment and
Resources Section
Contents
Introduction
Soils have the ability to absorb carbon dioxide and
influence its concentration in the atmosphere. Biochar can be used to increase
the ability of soils to sequester carbon and simultaneously improve soil
health. The goal of this paper is to introduce the concept and origins of
biochar, discuss its production process, potential uses, and the benefits and
costs of biochar in its key roles in agriculture and climate change mitigation.
Biochar is just charcoal made from biomass—which is plant
material and agricultural waste—hence the name ‘biochar’. It is a fine-grained
charcoal produced from pyrolysis: the slow burning of organic matter in a low-
or no-oxygen environment. What differentiates biochar from charcoal is its
purpose; it is produced as an additive to soils, mainly to improve nutrient
retention and carbon storage. [1] Although the history of biochar extends thousands of years, its science is
still relatively poorly understood.
The term ‘biochar’ was coined in recent times, but the
origins of the concept are ancient.[2] Throughout the Amazon Basin there are regions—up to two metres in depth—of terra
preta.[3] This is a highly fertile dark-coloured soil that has for centuries supported the
agricultural needs of the Amazonians.
Analyses of the dark soils have revealed high concentrations
of charcoal and organic matter, such as plant and animal remains (manure, bones
and fish). Terra preta’s productivity is due to good nutrient retention
and a neutral pH, in areas where soils are generally acidic.[4] Interestingly, terra preta exists only in inhabited areas, suggesting
that humans are responsible for its creation. What has not been confirmed is
how terra preta was created so many years ago.
Many theories exist. A frontrunner is the suggestion that
ancient techniques of slash-and-char are responsible for the dark earth.
Similar to slash-and-burn techniques, slash-and-char involves clearing vegetation
within a small plot and igniting it, but only allowing the refuse to smoulder
(rather than burn). [5] Combined with other biomass and buried under a layer of dirt, the smouldering
char eventually forms terra preta. [6] It is from these hypotheses of early slash-and-char practices that modern
scientists have developed methods for producing biochar.
The biochar production process begins with biomass being fed
into a pyrolysis kiln—a furnace that burns with little or no oxygen. The
biomass could be crop residue, wood and wood waste, certain animal manure, or various
other organic materials.
At the end of this, two main products come out of the kiln.[7] The first is biochar, usually representing about 50 per cent of the carbon
content of the biomass. The other is biofuel. The biofuel is often syngas,
which is a mixture of mainly hydrogen and carbon monoxide, with a little carbon
dioxide. The proportions of the three gases vary according to the processes
used to create the syngas. However, the important point is that syngas is combustible
and so can be used as a fuel source. Depending on the process, the biofuel from
the kiln could also be bio-oil, which can be used as a substitute for diesel in
some engines.
The pyrolysis occurs at temperatures below 700˚C; but
some parameters can be altered, such as the rate of pyrolysis, or the quantity
of oxygen. Generally, faster pyrolysis results in more oils and liquids, slower
pyrolysis produces more syngas. Minimising the oxygen present during pyrolysis
optimises the production of biochar.[8]
Pyrolysis can be followed by a second stage: gasification. Gasification
liberates more energy-rich syngases from the char (usually hydrogen-based). There
may also be a ‘gas cleanup’ stage to remove some of the particulates,
hydrocarbons and soluble matter from the gas.[9]
The biofuel generated from the pyrolysis process can be used
to create the electricity needed to power the kiln or secondary stages of the
process. So it is possible for the system to run autonomous of external power
sources. The pyrolysis process described is summarised in Figure 1.
Figure 1: Simplified pyrolysis process flow
diagram
An important advantage
of biochar is that it can be produced either from small, simple mobile units or
from larger, stationary ones. Small-scale systems for biomass inputs of 50 to
1000 kilograms per hour can be used on farms, while large units of up to 8000
kilograms per hour can be operated by large industries.[10]
There are potentially three
broad types of pyrolysis systems:
- central pyrolysis plants for processing all the biomass in a
region.
- lower-tech pyrolysis kilns for individual farmers or small groups
of farmers (these kilns may not include some secondary stages such as the
gasification or gas cleanup).
- pyrolysis trucks powered by syngas that could be driven around for
processing biomass within a region. The biochar and bio-oil would be
transported on the truck back to the customers.
Biochar has been popularised by its potential role in
climate change mitigation. Biochar is rich in carbon and, depending on its
ultimate use, the biochar may retain the carbon, thereby delaying or completely
preventing the release of the carbon back into the atmosphere in the form of
carbon dioxide gas. The benefits of biochar go beyond this, however, extending
to the agricultural sector and to various types of waste management.
Furthermore, as outlined above, its production process co-generates biofuel, a
sustainable renewable energy source.
The agricultural sector can benefit from biochar in two
ways: soil improvement and animal and crop waste disposal. Soil improvement,
and therefore increased productivity, can be the driver behind biochar
production and use. Since 1980, field trials have been taking place around the
world experimenting with the application of biochar types on specific soils.
The type of biochar varies with biomass type—in many cases
rice, wood or bark has been used—and production parameters, such as the rate of
pyrolysis and kiln size. In most of the studies, acidic soils have been the
subject of research, and these have generally been in tropical or semi-tropical
regions. Experiments have also employed differing treatments, applying relatively
more or less biochar, with and without the use of other fertilisers.[11]
Results of trials have ranged from no increase in
productivity (the case of banana plantations in Brazil) to as much as a 151 per
cent increase in soybean yield in one project.[12] In many cases it was noted that soil acidity was reduced and mineral
uptake increased, with residual effects sometimes lasting through to the
following season or two.[13] Research is still required into the use of biochar for pastures or tree
plantations, and for soils in dry and/or temperate regions.
A second benefit of biochar production to the agricultural
sector (and some industries, such as the paper industry) is the fact that it
uses organic waste. Left to accumulate, animal and crop waste can contaminate
ground and surface waters. Waste management practices are aimed at preventing such
contamination, but they can become costly. Biochar presents an attractive
alternative if the economic costs can be kept below those of waste management.[14]
By accepting organic material as its input, the biochar
production process transforms waste into a resource. The pyrolysis process
reduces the weight and volume of the feedstock, and by operating at a
temperature above 350˚C, it also removes potential pathogens that can be a
problem if directly applied to soils.[15] Green urban waste and waste from some industrial processes, such as paper
milling, can also be used. [16]
Biochar has been given a lot of attention recently as one
means of addressing climate change. It has the capacity to do so in three ways:
the storage of carbon over long periods; the reduction of greenhouse gases such
as methane (CH4) and carbon dioxide (CO2) that can be
generated from waste disposal, waste processing or recycling; and the
production of renewable energy.
Through the production process, around 50 per cent of the
feedstock’s carbon content is retained in the biochar. This compares to the 10
to 20 per cent that remains in biomass after 5 to 10 years of natural decay, and
the less than 3 per cent that remains in ash after complete burning. [17] Some analyses have suggested that ‘up to 12% of the total anthropogenic [carbon]
emissions by land use change can be off-set annually in soil, if slash-and-burn is replaced by slash-and-char’. [18] If it proves practicable to replace traditional slash-and-burn practices with
slash-and-char methods, biochar may present a real quantifiable and verifiable
option for storing carbon in the long term.
At the same time, it has the potential to reduce emissions
from other activities that might need to take place in the absence of the
biochar option. These other activities are the waste disposal process described
above and any recycling process. Both can be sources of greenhouse gas emissions,
either as carbon dioxide from transport and processing, or methane from
landfill sites.
Finally, the pyrolysis process also produces viable forms of
renewable energy. The syngas and bio-oils that result from the biochar
production process, and the generated heat, can be used either to produce
electricity, or as fuel. [19] Not only does this represent a renewable energy alternative but it also
improves the energy efficiency of the pyrolysis process. [20] Moreover, it has been calculated that ‘the emission reductions associated with
biochar additions to soil appear to be greater than the fossil fuel offset in
its use as fuel’. [21]
Despite the potential benefits that biochar presents, there
are limits to its potential production and usage. A major limitation to the
production of biochar is that the biomass used cannot be drawn from just any
agricultural (or industrial or urban) waste. Some studies have estimated that
no more than three per cent of available biomass is suitable for producing
biochar.[22] On a global scale, using all aboveground biomass would sequester only 0.56
gigatonnes of carbon per year, just one third of what is emitted each year from
land use change, or less than a tenth of annual fossil fuel emissions. [23]
If plants are grown specifically for the production of
biochar (instead of using waste), then the plants must have a growth rate
matched to the rate of planned biochar production. Fast growing plants deliver
the best productivity, but these also mature earlier and may begin to decay sooner.
The most efficient way to capture the carbon used by the plant in
photosynthesis would be to harvest it before the growth rate begins to taper.[24]
Also, the purpose for the produced biochar will change the
potential benefits, so it must be clear from the beginning whether the goal is
to improve soil nutrient retention, sequester carbon or manage waste. Whatever
the objective, the process will be optimised for that purpose in order to
maximise financial return. This is often to the detriment of other benefits. By
targeting soil improvement, the resulting biochar may not produce any usable
renewable energy; or if bio-energy production is the main objective, the
resultant biochar may be too unstable to store any carbon long-term[25].
Such trade-offs are not to be neglected as the ultimate profitability of the
process will determine its potential net benefit.
Unfortunately, the profitability of biochar is an area where
little study has been undertaken. While numerous research projects and pilot
studies have looked at the possible increases in agricultural productivity from
various sorts of biochar, it seems that the cost-benefit analyses needed to
ascertain the ultimate bottom line are lacking. [26] The increased profits from improved productivity may be completely offset by
the costs incurred through the biochar production process—this could also be
influenced by any eventual price on carbon. [27] Generally, more research is needed in this area.
It appears that the biggest limitation to the immediate major
deployment of biochar is the need for further research. The CSIRO has
identified at least eight research gaps, including predictive biochar
knowledge, biochar interactions on the microbial level, water retention
capacity, and assessment of potential soil carbon.[28] It could be three to five years before biochar can be seriously considered for
carbon storage on any large scale. [29]
The overall concept of biochar is now well understood. Take
the farmyard scraps, feed them into a pyrolysis kiln, apply the material produced
back to the land and in doing so, improve soil health, lock away carbon, and
generate renewable energy. But not all biochar is the same. Production process,
applications, benefits and costs vary with the biomass, soil-types and ultimate
purpose. The scientific, financial and societal factors of biochar have yet to
be assessed on any significant scale. Biochar has a role to play in the capture
of terrestrial carbon, but its capacity to mitigate climate change should not
be overstated. It should be seen as a complementary measure to attempts at
reducing emissions.
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