Madagascar Group Overview
At 587,000 square kilometres,
Madagascar is the world’s fourth largest
island after Greenland, New Guinea and Borneo.
Madagascar is also recognised as one of the
world’s top ten hotspots for biodiversity
(Mittermeier et al., 1999; Myers et al.,
2000; Brummitt & Nic Lughadha, 2003).
Estimates vary for the total number of plant
species present on the island. The lowest
figure - 7370 (including Pteridophytes) (Perrier
de la Bathie, 1936) is clearly out of date
and certainly too low. A highest estimate
of 12,000 species has been suggested by Guillaumet
(1984). Myers et al. (2000) give 12,000 as
their estimate of total plant species in
the hotspot of Madagascar, but this figure
includes the species present on the surrounding
islands of Mauritius, Reunion, the Seychelles
and the Comoros. Either way Madagascar has
an extremely diverse flora and fauna - and
its most striking feature is the degree of
endemism both at species level – and at higher
taxonomic levels.
The figures of Myers et al. (2000) give
a level of species endemism at 81% of the
total flora. This is broadly consistent with
older figures – for example Perrier de la
Bathie identified 5820 of his 7370 species
as endemic in 1936 (86%). Humbert (1959),
editor of the Flore de Madagascar et des
Comores, proposed that 6400 of his known
7800 species were strictly endemic (81%).
Perrier de la Bathie (1936) identified 238
(20%) of the 1289 native genera as endemic.
White (1983) identified eight endemic plant
families out of a total of 191. These were
Asteropeiaceae, Didiereaceae, Didymelaceae,
Diegodendraceae, Geosiridaceae, Humbertiaceae,
Sphaerosepalaceae and Sarcolaenaceae. Some
of these family groups have since been revised
as a result of phylogenetic studies (e.g.
Didieraceae is no longer considered endemic
as three continental African genera have
been sunk into it (Schatz, 2001)).
In addition to its considerable biodiversity
value, Madagascar scores highly on the second
criterion of Myers et al. (2000) - degree
of risk. Madagascar is one of the world’s
poorest countries and this, combined with
a large population growth rate, increases
pressure on the land for production. Deforestation
has been occurring across the country for
hundreds of years, and around 90% of Madagascar’s
primary vegetation appears to have been lost
since humans first inhabited the island around
2000 years ago (Du Puy and Moat,
1996).
RBG Kew has been working in Madagascar for
17 years, and our work there has mainly been
in carrying out plant diversity research
in the form of systematic treatments of key
families for the region. In addition, Kew’s
Madagascar Geographical Information
System Project, started in 1994, has made a major
contribution to the management of protected
areas in Madagascar. The past five years
have seen the publication of two comprehensive
monographs –the Legumes of Madagascar and
the Palms of Madagascar. Kew staff have also
been involved in the production of a complete
checklist of all the orchid species present
on the island and, in collaboration with
the Missouri Botanical Garden, the Generic
Tree Flora of Madagascar – which gives descriptions,
illustrations and keys for all tree genera
on the island.
More recently, the focus of RBG Kew’s programme
in Madagascar has centred around the conservation
and sustainable utilisation of Madagascar’s
plant diversity as defined in the Convention
on Biological Diversity and
the Global Strategy for Plant Conservation (l.
RBG Kew has a permanent base in Antananarivo
with an office/house
and seven Malagasy staff, and is currently
supporting three PhD and four Masters students
in botanical studies. Current projects in
Madagascar have a combined budget in excess
of $1000,000, and ten Kew staff members spend
a significant amount of their time working
on the flora of Madagascar.
Our long term aim is to develop
a team of Malagasy botanists with the skills
to support
Kew’s programme in Madagascar, and provide
a service to users of plant information in
Madagascar. In particular, we want to encourage
plant identification skills and good practice
in specimen collecting, plant naming, databasing,
report writing etc. There is a growing demand
for species inventory work in particular,
and field identification skills will always
be essential to Kew’s
work in Madagascar.In 2002 RBG Kew signed
an Accord de Siege with the Government of
Madagascar, formalising our status as a recognised
conservation NGO in Madagascar.
References
- Brummitt, N. and Nic Lughadha, E. (2003).
Biodiversity: where’s hot and where’s not.
Conservation Biology 17 (5), 1442-1448.
- DU
PUY, D.J. and MOAT, J. (1996). A refined
classification of the primary vegetation
of Madagascar based on the underlying geology:
using GIS to map its distribution and to
assess its conservation status. In: W.R.
Lourenço (editor). Proceedings of
the International Symposium on the Biogeography
of Madagascar, pp. 205--218, + 3 maps.
Editions de l’ORSTOM, Paris.
- Guillaumet (1984). Guillaumet, J. -L.,
1984. The vegetation an extraordinary diversity.
In: Jolly, A., Oberle, P. and Albignac, E.
R., (eds) Key Environments: Madagascar. Pergamon,
Oxford: 27-54.
- Humbert (1959). Humbert, H., 1959. Origines
présumées et affinities de
la flore de Madagascar. Mémoires de
l'Institut Scientifique de Madagascar, Séries
b (Biol. vég.) 9: 149-187.
- Mittermeier, R.A., Myers, P.R. Gil and
Mittermeier, C.G. (1999). Hotspots: Earth’s
biologically richest and most endangered
terrestrial ecoregions. CEMEX, Conservation
International and Agrupacion Sierra Madre,
Mexico.
- Myers, N., Mittermeier, C.G., da Fonseca,
G.A.B. and Kent, J. (2000). Biodiversity
hotspots for conservation priorities. Nature
403, 853-858.
- Perrier de la Bâthie (1936). Biogéographie
de plantes de Madagascar. Société d'Edition
Géographiques, Maritimes et Coloniales,
Paris.
- Schatz,
G.E. (2001), Generic Tree Flora of
Madagascar
- White, F. (1983). The AETFAT chorological
classification of Africa: history, methods,
and applications. Bull. Jard. Bot. Natl.
Belg. 62: 225-281.
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