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Charcoal production and coppice management at
Wakehurst Place
For hundreds, if not thousands, of years Britain's hardwood
forests have been sustainably managed for the production of
timber and fuel, including charcoal. The intense heat produced
by burning charcoal made it an important fuel for iron smelting,
which has been carried out on an industrial scale in Britain
as far back as the Roman Empire. However, the widespread use
of fossil fuels in the nineteenth and twentieth centuries
led to a dramatic decline in charcoal production in Britain.
Consequently many of the woodlands which had been carefully
managed for this valuable economic product fell into disrepair
or were destroyed in an attempt to secure a more profitable
use of the land.
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| Filling the charcoal kiln |
Much of the charcoal was produced from woodland that had
been coppiced. This ancient practice, whose name is derived
from the French verb Couper (to cut), involves cutting
shrubs and trees to ground level and regularly harvesting
the shoots which regrow from dormant buds in the stumps and
roots. Traditionally a limited number of trees, known as standards,
are retained in coppiced woodland for the production of larger
timber. A balance of standards to coppice is then struck in
order to ensure both crops have adequate light to grow. If
the shoots are not cut back on a regular basis they become
over-mature, often leading to a reduction in vigour, decay,
death, or a reversion to high forest. Miraculously, however,
when old coppice shoots are cut back the whole stump can be
rejuvenated.
Most British native broadleaved trees and shrubs can be coppiced
and the time between cuts depends on both the species and
the product required. Hazel (Corylus avellana), for
example, is typically coppiced every 7-10 years to produce
pea sticks, bean poles, thatching spars, hurdles and fuel.
Sweet chestnut (Castanea sativa) is usually cut at
15 years for fencing, whilst oak (Quercus robur) can
be left from 25-35 years for firewood and charcoal production.
Other important coppiced trees in Britain include alder (Alnus
glutinosa), beech (Fagus sylvatica), birch (Betula),
field maple (Acer campestre), small-leaved lime (Tilia
cordata), sycamore (Acer pseudoplatanus), willow
(Salix spp.) and wych elm (Ulmus glabra).
Some coppiced woodlands are ancient woods descended from the
original primeval woodland cover, whilst others are recent
plantations. A coppiced small-leaved lime at Westonbirt Arboretum,
Tetbury, is estimated to be over 2000 years old. Over this
period it has radiated from a central stump which has long
since decomposed and its outer stems form a circle appearing
rather like a fairy ring. An individual tree of this species
would be expected to survive only a few hundred years; its
increased longevity is due to the rejuvenating influence of
coppicing.
The regular cycle of coppice management creates an open woodland
habitat favoured by many plants and animals. In over-mature
coppice, the dense canopy reduces the light available to plants
on the woodland floor and only the most tenacious survive,
often by growing in late winter before the canopy casts its
dense shade. Following coppicing, the extra light that reaches
the woodland floor stimulates a riot of colour from various
native plants as they burst into flower. These may include
daffodils (Narcissus pseudonarcissus), bluebells (Hyacinthoides
non-scripta), wood anemones (Anemone nemorosa),
violets (Viola riviniana), wood spurge (Euphorbia
amygdaloides) and primroses (Primula vulgaris).
These plants which can survive vegetatively under the old
coppice canopy are soon joined by others like foxgloves (Digitalis
purpurea) and St John's worts (Hypericum) which
germinate from buried seed.
A wide range of invertebrates thrive in the warm microclimate
and on the bonanza of food plants in young coppice. Some species
have declined alarmingly with the reduction of coppicing and
the future survival of several butterflies including the rare
heath fritillary may be dependent upon a return to this traditional
woodland management.
As the coppiced shoots regrow, bramble often invades providing
dense cover for small mammals and birds such as the garden
warbler and nightingale. The rare dormouse also benefits but
care must be taken to ensure that the coppice cycle is long
enough (10-15 years) for its food plants, especially hazel,
to flower and fruit.
Coppicing is, however, not a panacea for all wildlife conservation
and should be a part of a planned woodland management programme.
For example, some birds and invertebrates including the speckled
wood and white admiral butterflies and the robin enjoy the
deep shade and structure of neglected coppice. Others enjoy
the dead wood habitats and larger trees provided by standards
or high forest.
In pursuit of Kew's objective to help ensure better management
of the earth's environment, many of the woodlands at Wakehurst
Place are being restored by bringing over-mature coppice back
into a matrix of sustainable woodland management. Care is
taken to balance the habitat requirements of its rich communities
of plants and animals with the harvest of woodland products.
Using traditional skills, hazel with standards is cut on a
10-12 year cycle to provide pea sticks to support the herbaceous
plants at Kew and Wakehurst Place whilst ash and other species
are cut on a 20-30 year rotation to produce 'BAR-B-KEW' charcoal.
In Britain today, charcoal is used as fuel for domestic barbecues,
in fireworks and in medicinal biscuits. As it can absorb gases
and impurities, it is employed in chemical, water and vodka
filtration. Approximately two thirds of the estimated 60,000
tonnes of charcoal sold in Britain every year are used in
barbecues. Of this vast quantity only 3 per cent (1,800 tonnes)
is produced in England. A large proportion of the remainder
is derived from unsustainable harvesting in the tropical forests
and mangrove swamps with the cheapest imports coming from
South-east Asia. This is particularly disturbing when one
estimate suggests that there is 800,000 tonnes of low value
wood including over-mature coppice in the south-east of England
alone. This wood is currently of little economic value but
could be used for the production of high quality British hardwood
charcoal.
Charcoal production is dependent on heating wood without
enough air for complete combustion. Under these conditions,
water is expelled from the wood and volatile substances such
as tars and oils are released, leaving charcoal containing
up to 90 per cent carbon. In most charcoal production processes,
some of the wood in the kiln is burnt to produce the necessary
heat. If thoroughly air-dried wood is used, ideally with a
moisture content below 20 per cent, then 4 tonnes will yield
1 tonne of charcoal. This yield is halved if unseasoned timber
is used since a higher proportion of the wood in the kiln
has to be burnt to provide the required heat.
Many different kilns are used throughout the world. Some,
known as earth kilns, utilise only materials from the woodland
to seal them. At Wakehurst Place, a less labour-intensive
portable steel kiln is moved around the woodlands to each
new coppice block. Other initiatives in Britain could lead
to huge static kilns to which timber growers take their coppiced
wood.
At Wakehurst Place up to 3 tonnes of BAR-B-KEW charcoal is
made each year. Like other British hardwood charcoal, it has
a high carbon content which makes it easy to light and quick
to reach a high cooking temperature. These qualities make
it a superior product to most imports and it provides an alternative
to charcoal produced from endangered sources such as tropical
rainforest and mangrove swamps. Its retail is helping to perpetuate
a traditional practice and will contribute to wildlife conservation
at Wakehurst Place.
Aarron, J., 1980. The production of Wood Charcoal in Britain.
Forestry Commission Forest Record, 121. HMSO
Anon., 1993. Statistics of charcoal imports. Centre for Environmental
Information, 24 Roseberry Road, Cheam, Surrey. SM1 2BW
Buckley, G.P. (ed.), 1992. Ecology and Management of Coppice
Woodlands. Chapman and Hall
Fuller, R.J. and Warren, M.S., 1990. Coppiced Woodlands: their
management for wildlife. Nature Conservancy Council
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