|
By Marc Cadotte
A Canadian mining corporation,
QIT-Fer et Titane, Inc., will be sponsoring a large-scale mining project
in the extreme south eastern region of Madagascar. The project will
result in the removal of much of the remaining coastal littoral rain
forest.
The QIT-Fer mining
project will be centred around the city of Fort Dauphin (or Tolagnaro)
in the extreme south eastern coast of the Island (Fig 1). This region
is significant as much of the habitat diversity that Madagascar is famous
for, is concentrated in this region (Goodman 1999). During a 50 km drive
along Route Nationale 12, one can see coastal marine areas, coastal
littoral forest, montane rain forest, dry deciduous forest, and the
unique spiny desert.
QIT-Fer
will be mining for ilmenite (or titanium dioxide), used primarily in
the production of paints, paper, and plastics. This project may involve
the removal of 2540 Ha of littoral forest, or 73% of the remaining south
eastern coastal forest, leaving only about 940 ha of highly fragmented
and isolated forest patches along a 100 km stretch of coast. The clearing
of the forest on the proposed mining project will undoubtedly have some
profound consequences. Using the species-area relationship, S = cAz
(MacArthur and Wilson 1967) we can predict that a 73% decrease in natural
forest could entail up to 30% of species becoming locally extinct. Most
affected will be the highly localised endemics, which could vanish forever.
For example, in the mining region at least 18 species of tree and shrub
are found nowhere else on the island (Dumetz 1999), and one Gecko species
(Phelsuma antanosy) lives primarily in the to-be-cleared forests of
the southeast (Nussbaum et al. 1999).
It
is unavoidable that biodiversity will be lost at many levels, from genetic
variation of populations to specific communities that form the littoral
forest ecosystem. As a result of further fragmentation will, through
metapopulation level effects, increase the probability that local populations
will go extinct (decreased patch size) while the probability of immigration
saving an imperilled local population will decrease (increased isolation)
(Wilcox and Murphy 1985; Gilpin and Hanski 1991). Increased fragmentation
will also increase the perimeter-to-area ratio, which is synonymous
with the injurious "edge effects". Increasing the edge effects by increasing
fragmentation can result in increased tree mortality and reduced biomass
within 100m from the edge (Laurance et al. 1998), increased intrusion
by exotic species, predators, or parasites (e.g., Wilcove et al. 1986),
as well as increased wind penetration and temperature, and decreased
humidity (Biorregaard et al. 1998). Once fragments fall below 100-400
ha in size, these effects can be greatly exacerbated (Laurance et al.
1998).
These are the consequences of straight out habitat destruction, but
there have been indications put forth by QIT-Fer that they will undertake
a restoration programme after the mining project. Much of the land cleared
in Madagascar has been severely denuded as to preclude any chance of
successful restoration projects (Terborgh and Van Shik 1997). Fig. 2
shows cleared land in the region of St. Luce to be included in the proposed
conservation area; exposed white sand indicates that no top soil remains
and only a few hardy species thrive in this environment (especially
Philippia sp., Ericaceae). Impediments to restoration of complex tropical
ecosystems include: many intricate evolved mutualisms between all types
of organisms, long intervals of time required for many tropical trees
to recover, and invasive species commonly acquire a foothold in disturbed
habitats. Similarly, many tropical forests represent communities which
may be impossible to put back together, despite all our knowledge and
efforts (Pimm 1994). Another caveat to the issue of restoration is the
cost, Vianne et al. (1997) found that the cost to restore a degraded
9.5 ha patch of rain forest in Brazil was $2,718.50 (U.S.), and this
price only included planting, enrichment and vine control. However,
the calculation of this cost did not include fire suppression, nor control
of resource extraction or hunting. This value translated into the hundreds
or thousands of hectares to be restored, equates to a large financial
commitment by a private interest.
Bibliography
Bierregaard, R. O. Jr.,
Lovejoy, T. E., Kapos, V., dos Santos, A. A., and Hutchings, R. W. 1992.
The biological dynamics of tropical rainforest fragments. BioScience
42: 859-866.
Cincotta, R. P., Wisnewski, J., and Engelman, R. 2000. Human population
in the biodiversity hotspots. Nature 404: 990-992.
Dumetz, N. 1999. High plant diversity of lowland rainforest vestiges
in eastern Madagascar. Biodiversity and Conservation 8: 273-315.
Ehrlich, P. R. and Wilson, E. O. 1991. Biodiversity studies: science
and policy. Science 253: 758-762.
Gadgil, M. 1995. Prudence and profligacy: a human ecological perspective.
In, T. M. Swanson (ed.), The Economics and Ecology of Biodiversity Decline:
The Forces Driving Global Change, pp. 99-110. Cambridge University Press,
Cambridge.
Gilpin, M. and Hanski, I. (eds.) 1991. Metapopulation Dynamics: Empirical
and Theoretical Investigations. Biological Journal of the Linnean Society
42 (1 & 2).
Goodman, S. M. 1999. Description of the Reserve Naturelle Integrale
d'Andohahela, Madagascar, and the 1995 biological inventory of the reserve.
Fieldiana 94: 1-9.
Green, G. M. and Sussman, R. W. 1990. Deforestation history of the eastern
rain forests of Madagascar from satellite images. Science 248: 212-215.
Janzen, D. H. 2000. Costa Rica's Area de Conservacion Guanacaste: a
long march to survival through non-damaging biodevelopment. Biodiversity
1: 7-20.
Jernvall, J. and Wright, P. C. 1998. Diversity components of impending
primate extinctions. Proceedings of the National Academy of Sciences,
USA 95: 11279-11283.
Kremen, , C., Niles, J. O., Dalton, M. G., Daily, G. C., Ehrlich, P.
R., Fay, J. P., Grewal, D., and Guillery, R. P. 2000. Economic incentives
for rain forest conservation across scales. Science 288: 1828-1832.
Laurance, W. F. 1999. Reflections on the tropical deforestation crisis.
Biological Conservation 91: 109-117.
Laurance, W. F., Ferreira, L. V., Rankin-de Merona, J. M., and Laurance,
S. G. 1998. Rain forest fragmentation and the dynamics of Amazonian
tree communities. Ecology 79: 2032-2040.
MacArthur, R. H. and Wilson, E. O. 1967. The Theory of Island Biogeography.
Princeton University Press, Princeton, New Jersey.
May, R. M. 1994. Past efforts and future prospects towards understanding
how many species there are. In, O. T. Solbrig, H. M. vanEmden, and P.
G. W. J. van Oordt, Biodiversity and Global Change, pp. 71-84. CAB International,
Paris.
Mittermeier, R. A., Myers, N., Thomsen, J. B., da Fonseca, G. A. B.,
and Olivieri, S. 1998. Biodiversity hotspots and major tropical wilderness
areas: approaches to setting conservation priorities. Conservation Biology
12: 516-520.
Myers, N. 1995. Tropical deforestation: population, poverty and biodiversity.
In, T. M. Swanson (ed). The economics and ecology of biodiversity decline:
the forces driving global change. Cambridge, Cambridge University Press.
pp. 111-122.
Myers, N., Mittermeier, R. A., Mittermeier, C. G., da Fonseca, G. A.
B., and Kent, J. 2000. Biodiversity hotspots for conservation priorities.
Nature 403: 853-858.
Nussbaum, R. A., Raxworthy, C. J., Raselimanana, A. P., and Ramanamanjato,
J. B. 1999. Amphibians and reptiles of the reserve naturelle integrale
d'Andohahela, Madagascar. Fieldiana 94: 155-173.
Pimm, S. L. 1994. Biodiversity and the balance of nature. In, E. D.
Schulze and H. A. Mooney (eds.), Biodiversity and Ecosystem Function,
pp. 347-359. Springer-Verlag, New York.
Pimm, S. L., Russell, G. J., Gittleman, J. L., and Brooks, T. M. 1995.
The future of biodiversity. Science 269: 347-350.
Prance, G. T. 1997. Valuation and sustainable use of tropical rainforest.
Journal of Biological Education. 31: 258-262.
Prance, G. T., Beentje, H., Dransfield, J., and Johns, R. 2000. The
tropical flora remains undercollected. Annals of the Missouri Botanical
Gardens 87: 67-71.
Sierra, R. 1999. Traditional resources-use systems and tropical deforestation
in a multiethnic region in north-west Ecuador. Environmental Conservation
26: 136-145.
Terborgh, J. and van Schaik, C. P. 1997. Minimizing species loss: the
imperative of protection. In, R. Kramer, C. van Schaik, and J. Johnson
(eds.), Last Stand: Protected Areas and the Defense of Tropical Biodiversity,
pp. 15-35. Oxford University Press, New York.
Tilman, D. 2000. Overview: causes, consequences and ethics of biodiversity.
Nature 405: 208-211.
Viana, V. M., Tabanez, A. A. J., and Batista, J. L. F. 1997. Dynamics
and restoration of forest fragments in the Brazilian Atlantic moist
forest. In, W. F. Laurance and R. O. Bierregaard, Jr. (eds): Tropical
forest remnants: ecology, management, and conservation of fragmented
communities. Chicago, University of Chicago Press. pp 351-365.
Wallace, A. R. 1892. Island Life: Or The Phenomena and Causes of Insular
Faunas and Floras Including a Revision and Attempted Solution of the
Problem of Geological Climates. Macmillan and Co., London.
Wilcove, D. S., McLellan, C. H., and Dobson, A. P. 1986. Habitat fragmentation
in the temperate zone. In, M. E. Soule (ed.), Conservation Biology:
The Science of Scarcity and Diversity, pp. 237-256. Sinauer Associates,
Sunderland MA.
Wilcox, B. A. and Murphy, D. D. 1985. Conservation strategy: the effects
of fragmentation on extinction. American Naturalist 125: 879-887.
Wilson, E. O. 1992. The Diversity of Life. W. W. Norton and Company,
New York.
Whitemore, T. C. 1997. Tropical forest disturbance, disappearance, and
species loss. In, W. F. Laurance and R. O. Bierregaard, Jr. (eds): Tropical
forest remnants: ecology, management, and conservation of fragmented
communities. Chicago, University of Chicago Press. pp 3-12.
|
|
|