| COUNTRY
Madagascar
NAME Tsingy de Bemaraha Strict Nature Reserve
IUCN MANAGEMENT CATEGORY
Ia (Strict Nature Reserve)
Natural World Heritage Site - Criteria iii and iv
BIOGEOGRAPHICAL PROVINCE 3.09.04 (Malagasy woodland/savanna)
GEOGRAPHICAL LOCATION The reserve lies 60-80km
inland from the west coast in the northern sector of the Antsingy region
of the Bemaraha Plateau, north of the Manambolo River Gorge. 18°17'-19°06'S,
44°36'-44°58'E
DATE AND HISTORY OF ESTABLISHMENT The area was
first established as a strict nature reserve on 31 December 1927, and
is now protected under Decree No. 66-242 of 1 June 1966. The ancient cemeteries
within the Manambolo Gorge, the gorge itself, and the "forêt et rochers"
(which includes the reserve), are all designated "natural monuments and
sites" under a decree of 25 August 1937, all three being listed by an
'arrêté' of 11 February 1939. However, this latter designation does not
imply any degree of management or protection. Inscribed on the World Heritage
List in 1990.
AREA 152,000ha
LAND TENURE Government
ALTITUDE 150m to 700m
PHYSICAL FEATURES Much of the area comprises
highly dissected limestone karst, part of the Bemaraha Plateau. This massif
is delimited to the east by abrupt cliffs, the Bemaraha Cliff, which rises
some 300 to 400m above the Manambolo River valley and extends several
tens of kilometres from north to south. The western slopes of the massif
rise more gently, and the whole western region of the reserve forms a
plateau with rounded hillocks which slope away, with decreasing steepness,
to the west. To the north undulating hills alternate with limestone extrusions,
while in the south extensive pinnacle formations make access extremely
restricted. The northern side of the Manambolo River Gorge lies within
the reserve, with cliffs falling some 100m. Both seasonal and permanent
rivers flow on the plateau (draining to the west), and numerous permanent
springs arise at the base of the Tsingy on both sides. The Tsingy is an
important water catchment for surrounding lands, particularly those to
the west.
CLIMATE Rainfall is seasonal, with a dry season
of six to eight months, and a wet season around December-March. Annual
rainfall is about 980mm, and the Tsingy is wetter than all areas lying
to the west. Mean annual temperature is above 26°C, and mean monthly temperatures
remain above 20°C. Extremes of 38°C and 9°C have been registered in December
and July, respectively.
VEGETATION Vegetation is characteristic of the
calcareous karst regions of western Madagascar, with dense, dry, deciduous
forest, and extensive anthropogenic savannas throughout. Although there
have been few studies (mostly carried out more than 40 years ago), and
the flora is not well known, many of the species are unique to this formation,
including Diospyros perrieri (the ebony of the west coast), several
Delonix species, and Musa perrieri (the only wild banana
in Madagascar). Also, baobabs Adansonia are found here, and xerophytic
plants such as Aloe on rocky formations. Notable families include
Flacourtiaceae, Orchidaceae, Leguminosae, Euphorbiaceae, Annonaceae, Bombacaceae
and Moraceae. The aquatic Aponogeton fenestrale occurs in some
of the rivers. The vegetation is similar to that of the Tsingy de Namoroka
(R.N.I. No. 8), but the much larger area and the greater height of the
karst relief make the vegetation richer here.
FAUNA The fauna of the region has not been studied
in any detail. The Tsingy is the only known location for chameleon Brookesia
perarmata (known from only a few specimens). Amongst the 53 species
of bird recorded here, this is the only western dry forest site known
for Madagascar grey-throated rail Canirallus
kioloides (only previously known from north-western and eastern
Madagascar). The reserve is also the only protected area where the endemic
nesomyine rodent Nesomys
rufus lambertoni is known to occur (a subspecies which is thought
to be sufficiently distinctive to warrant full species status). There
is also an unconfirmed report of aye-aye Daubentonia
madagascariensis (E) being seen just outside the reserve near
Bekopaka. Other notable species include goshawk Accipiter
henstii, which may be threatened, and lemurs Propithecus
verreauxi deckeni, western gentle lemur Hapalemur
griseus occidentalis (V), forked marked lemur Phaner
furcifer (R), and Milne-Edwards sportive lemur Lepilemur
edwardsi (R).
CULTURAL HERITAGE A number of ancient cemeteries
occur on the plateau and in the Manambolo Gorge.
LOCAL HUMAN POPULATION Several families live
within the reserve (illegally), and parts are affected by the activities
of people living in adjacent villages.
VISITORS AND VISITOR FACILITIES Tourism could
potentially be important in this region, although access is currently
forbidden by law, other than for scientific purposes. There are, therefore,
no facilities within the reserve (and the nearest hotels are in Maintirano,
150km by road from the edge of the reserve). Visitation is restricted
to occasional visits to the pinnacle region to the south or to the forests
in the north, and guides based at Antsalova and Bekopaka lead overnight
trips to them.
SCIENTIFIC RESEARCH AND FACILITIES Little work
has been done in this region apart from a few collecting expeditions.
The reserve was apparently surveyed in the 1930s, and the vegetation reported
upon around 1970, although details are lacking. Studies of prosimians
made in similar forests in other areas are reported on by Petter et
al. (1977) andCharles-Dominique et al. (1980), and
of birds by Milon et al. (1973). There are no research facilities.
CONSERVATION VALUE In terms of its large size
and relatively low surrounding human population pressure, Bemaraha Reserve
is the single most biologically important protected area in western Madagascar
(IUCN, 1990). Vegetation consists mainly of dense dry deciduous forests,
which are characteristic of the limestone plateaux of western Madagascar.
The Tsingy de Bemaraha is the principle source of water for much of the
surrounding region (Nicoll and Langrand, 1989).
CONSERVATION MANAGEMENT There is no current
management plan, the reserve is not zoned, and staff are insufficient
to adequately run the reserve. However a WWF project to help improve protected
area management within the country has made several recommendations on
management of the area (Nicoll and Langrand, 1989). A national workshop
on the conservation of the reserve (Mahajanga, 13-18 October 1989) recommended
the development and implementation of a management plan as the priority
action for effective implementation of the reserve. When this plan is
drafted, the objectives of the reserve and its management will also be
reviewed (Gouvernement malgache, 1989).
MANAGEMENT CONSTRAINTS The pinnacle region to
the south is relatively well protected through its inaccessibility, but
much of the rest of the reserve is seriously threatened by fire. Several
tracks traverse the reserve or run north-south through it, and fires are
set along them throughout the dry season (right of passage along these
paths is legally recognised). In addition to grassland burning, forest
edges are deliberately set on fire, damaging or destroying them, and rocky
areas are burnt frequently, denuding the surface and allowing cattle access
to the sparse grass between exposed limestone blocks. Cattle damage also
occurs through much of the accessible forest, and may reduce regeneration
locally. Some timber exploitation occurs near the villages, but its effects
appear to be limited, as do the effects of hunting. Village agriculture
on the eastern boundary is encroaching the reserve. An all-weather oil
exploration service road from Antsalova penetrates approximately 30km
into the reserve, crossing the Tsingy. While this access could be of value
to reserve management, currently it is used daily by villagers crossing
the reserve, and provides easy access for cattle.
Despite the age of the reserve, no comprehensive resource
inventory is available, there is no management plan, there are no facilities,
boundaries are not marked, and there is no resident staff or budget. No
effort is made to patrol the reserve or prevent legal infractions, including
burning. This is in part a result of the relatively large size of the
reserve, but also a result of insufficient personnel and a lack of transport
and camping equipment. In addition, no public awareness or education programmes
have been instigated in surrounding settlements in any attempt to reduce
damage to the reserve, and it is likely that most people in the region
do not realise that the reserve exists. However, despite these problems,
Petter and Rajery (1987) indicate that the degradation of the natural
environment is considerably less than in many other regions of Madagascar,
and that the potential here is high.
STAFF The Chef de la Réserve lives in Antsalova.
At least one other auxiliary guard lives in Bekopaka.
BUDGET None
LOCAL ADDRESSES
Service de la Protection de la Nature, Direction des
Eaux et Forêts, B P 243, Antananarivo 101
Service Provincial des Eaux et Forêts, B.P. 27, Mahajanga
Circonscription des Eaux et Forêts de Maintirano, B
P 67, Maintirano
REFERENCES
Andriamampianina, J. and Peyrieras, A. (1972). Les réserves
naturelles intégrales de Madagascar. In: Comptes rendus de la Conférence
internationale sur la Conservation de la Nature et de ses Ressources à
Madagascar, Tananarive, Madagascar 7-11 octobre 1970. IUCN, Switzerland.
Charles-Dominique, P., Cooper, H.M., Hladik, A., Hladik,
C.M., Pagès, F., Pariente, G.F., Petter-Rousseaux, A., Schilling, A. and
Setzer, H.W. (eds) (1980). Nocturnal Malagasy Primates: Ecology, Physiology
and Behaviour. Academic Press, New York.
Gouvernement malgache (1989). Réserve naturelle de Bemaraha.
Formulaire de proposition d'inscription sur la liste du patrimoine mondial.
Submitted to Unesco November 1989.
IUCN (1990). World Heritage Nomination - IUCN Technical
Evaluation for Bemaraha Integral Nature Reserve, Madagascar.
Leandri, J. (1933). Compte rendu d'une mission au Bemaraha.
Bulletin du Muséum d'histoire naturelle de Paris.
Leandri, J. (1937). Reconnaissance botanique de la partie
médiane de l'Ouest malagache. Bulletin de l'Académie malagache
19.
Leandri, J. (1938). La forêt d'Antsingy. La Terre
et la Vie: 18-27.
Leandri, J. (1951). Sur quelques traits de la végétation
des plateaux calcaires dans l'Ouest de Madagascar. Index bibliographique:
Webbia, Vol. VIII. Pp. 155-175.
Milon, P., Petter, J-J., and Randrianasolo, G. (1973).
Faune de Madagascar No. 35, ORSTOM-CNRS, Paris.
Nicoll, M.E. and Langrand, O. (1989). Madagascar:
Revue de la conservation et des aires protégés. WWF, Gland,
Switzerland. Pp. 55-58.
Petter, J-J. and Rajery, L. (1987). Parc Bemaraha-Manambolo:
Projet d'Amenagement de la region d'Antsalova sur le principe d'une réserve
de la biosphère. Rapport pour son inclusion sur la liste du World Heritage
de l'Unesco.
Petter, J-J., Albignac, R. and Rumpler, Y. (1977). Mammifères
lémuriens (Primates prosimiens). Faune de Madagascar No.44, ORSTOM-CNRS,
Paris.
Rakotoariason, N., Mutschler, T. and Thalmann, U. (1993).
Lemurs in Bemaraha World Heritage Landscape Western Madagascar. Oryx
27(1): 35-40.
DATE April 1988, revised 1990 |