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148 Caesalpinia echinata
Leguminosae
ibirapitanga, pau brasil Distribution
Brazil (Alagoas, Bahia, Espírito Santo, Minas Gerais, Paraíba,
Pernambuco, Rio de Janeiro, Rio Grande do Norte, Sergipe) Habitat
The species occurs in littoral forest and woodland, generally
on sandy or sand-clay soils that are well drained, preferring open less
dense forest, frequently in dry high, light environments. Population
Status and Trends Natural stands have been severely
depleted as a result of centuries of exploitation and habitat destruction. The
exploitation of the species as a source of wine-red
dye dates back to 1501 and has resulted in the country being named after the tree.
The manufacture of synthetic dyes in 1875 caused a gradual
decline in the exploitation of wild sources and the species became important
as a commercial source of wood for the manufacture of bows for musical instruments.
It remains the most important wood for making professional
bows, but the scale of this industry is little known (Anon, 1997). The remaining
stands of the species exist in a few areas on coastal
plain, where deforestation rates have been rapid (Varty, 1996). Illegal extraction
of C. echinata
by farmers
and foresters
is thought
to still
occur, although
the extent
of this
activity remains
unknown.
The species
is included on
the official list of threatened species in Brazil (IBAMA, 1992). Role
of species in the Ecosystem Trees are frequently
covered with orchids and other epiphytes. Threats
Commercial exploitation, local use, clear-felling/logging of
the habitat Utilisation
The dye extracted from the heartwood is what the species is
famous for. The heavy timber has considerable value for use in construction
work and carpentry and handicraft, but its most commercial application is in the
manufacture of bows for musical instruments. The bark
is of local importance for its medicinal properties and trees are planted as ornamentals.
Trade Pau
brasil was
an important
source of
fiery red
colourant during
the middle
ages.
Enormous quantities
of dyewood
were exported
between 1501 and 1850, causing the loss of large areas of forest and enslavement
of Indians. Synthetic dyes began to become important
in the mid 1800s and have now almost completely taken over. Exports of brazilwood,
including the heartwood of a number of related
species from Central and South America to USA. and Western Europe, declined after
1950s. The extent of current trade is not known and
it is unlikely that brazilwood will
be exploited as a source of dye at anything other than
at a small scale (Green, 1995). The wood began to be used for making bows for
musical instruments in the last century. The vast
majority of professsional bows are now made from the species. There are no reliable
figures on the quantity of C.
echinata exported
for this
purpose but
one estimate
puts the
world demand
at 200m³.
The actual
figure is
likely to
be considerably
greater to take account of the large amount of wastage in processing. It is thought
that 70-80% of the wood is lost in converting logs into
bow blanks and a further 70-80% is then lost in processing bow planks into bows.
About 1500kg of wood is cut to provide 100-200kg of
suitable wood for bows; a single violin bow demanding 1 kg of wood. A professional
bow costs between US$ 2000-5000 (Anon, 1997). IUCN
Conservation category EN A1acd according to
Varty (1996). Conservation
Measures Two protected areas in Bahia and Pernambuco
were set up specifically to protect populations of C.
echinata. The species is also
recorded in other public and private reserves. The species is in cultivation in
Bahia, Alagos, Pernambuco and Rio de Janeiro and there
is also a reintroduction programme at Linares Reserve. IBAMA include the species
on the official list of threatened Brazilian plants.
Various federal and state laws exist restricting the export
and cutting of C.
echinata or its habitat type. However there appear
to be considerable loopholes and a lack of specific
measures to protect the species (Anon, 1997). Forest
Management and Silviculture Plants begin to flower
around 3-4 years of age. Seeds fail to germinate after storage for 30 days. The
development of heartwood in plantation trees is considerably
faster than in the wild; the DBH of a 17 year old plantation tree compares with
a 70 year old tree in the wild. The quality of wood
from plantations is, apparently, not suitable for making bows and consequently
there is a lack of interest in growing the species in plantation (Anon, 1997).
References Anon.
1997. Conservation and management of pau-brasil, Caesalpinia
echinata
An action plan. Fauna and Flora International
(UK), Botanical Gardens of Rio de Janeiro (Brazil), Margaret Mee Foundation (Brazil).
(Unpublished report). Green, C.L. 1995. Natural
colourants and
dyestuffs.
A review
of production
and development
potential.
Non-Wood
Forest Products
4. Food
and Agriculture
Organization of
the United
Nations, Rome.
IBAMA. 1992. Lista oficial de espécies da flora Brasileira
ameaçadas de extinçao. (unpublished). 4pp. Sociedade Botânica
do Brasil. 1992. Centuria plantarum Brasiliensium extintionis
minitata. Sociedade Botânica do Brasil. 175pp. Lewis,
G.P. 1987. Legumes of
Bahia. Royal Botanic Gardens, Kew. Varty,
Nigel. 1996. Data collection forms for Brazilian Atlantic forest species.