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Mangrove biodiversity survey south of the Onilahy River - Frontier ...

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Conclusions and recommendations<br />

<strong>Mangrove</strong> trees are used for firewood and for making charcoal. In <strong>the</strong> East Africa region, many<br />

mangrove forests (particularly those close to urban areas) have been subject to indiscriminate<br />

cutting and <strong>the</strong> destruction <strong>of</strong> entire mangrove habitats (Semesi, 1996). <strong>Mangrove</strong>s to <strong>the</strong> North <strong>of</strong><br />

Madagascar have been progressively exploited for firewood, with recent incursions into <strong>the</strong><br />

mangroves at Songoritelo being noted by Vasseur (1997), shrimp farming and salt extraction.<br />

Although <strong>the</strong> pressure on <strong>the</strong> mangrove forests for charcoal remains small in this area due to <strong>the</strong><br />

local preference for xerophilic (terrestrial) timber (Lebigre, 1997), <strong>the</strong>re is a local preference for A.<br />

marina as a fuelwood (<strong>Frontier</strong>-Madagascar, unpublished data). Where mangroves are common<br />

and close to centres <strong>of</strong> population (e.g. Toliara), <strong>the</strong>y are subject to considerable felling activity. In<br />

fact Salomon (1981) showed that <strong>the</strong> charcoal requirements <strong>of</strong> Toliara result in <strong>the</strong> clearance <strong>of</strong><br />

5,000ha <strong>of</strong> (terrestrial) forests annually; <strong>the</strong> natural xerophilic vegetation now covers only 27% <strong>of</strong><br />

<strong>the</strong> <strong>south</strong>west <strong>of</strong> <strong>the</strong> country (Lebigre, 1997). As this terrestrial vegetation becomes exhausted, <strong>the</strong><br />

resources <strong>of</strong> <strong>the</strong> mangroves are more likely to come under threat.<br />

Semesi and Howell (1989) state that <strong>the</strong> most destructive activities affecting mangroves are clearfelling<br />

for rice cultivation, salt and charcoal production, aquaculture, or for firewood; whereas<br />

selective felling for export and local construction purposes is not a major threat if adequately<br />

controlled. Rice culture is not possible in this area (<strong>the</strong> driest in Madagascar), and can be<br />

discounted as a threat to <strong>the</strong> mangroves. Traditional fishing in Western Madagascar relies<br />

extensively on forest products, much <strong>of</strong> which originate from readily accessible mangroves<br />

(Rasol<strong>of</strong>o, 1997), but <strong>the</strong>re is little use <strong>of</strong> smaller mangroves for this purpose. Nor is salt<br />

production a real concern for <strong>the</strong> tannes, since despite <strong>the</strong> favourable climate (Hamilton and<br />

Snedacker, 1984), <strong>the</strong> dune-derived relief and access difficulties are probably enough <strong>of</strong> a logistical<br />

barrier to discourage any large-scale operation. The major problems facing mangroves to <strong>the</strong> North<br />

(poor agricultural practises, tree felling, salt production, and shrimp fishing and aquaculture (Iltis,<br />

1997)) are largely absent from this section <strong>of</strong> <strong>the</strong> coastline, although <strong>the</strong> first two are present and are<br />

likely to become increasingly important factors influencing <strong>the</strong> local environment.<br />

The cutting <strong>of</strong> any mangrove tree technically requires a permit in Madagascar, but <strong>the</strong>re is no<br />

enforcement <strong>of</strong> this edict (Cooke et al., 2000). <strong>Mangrove</strong> wood is highly dense, an attribute that<br />

confers resistance to fungi and termites (Semesi, 1996). For construction purposes <strong>the</strong><br />

Rhizophoraceae are most prized, as <strong>the</strong>y most <strong>of</strong>ten have <strong>the</strong> forked trunk preferred for wooden<br />

domiciles. Good management <strong>of</strong> mangrove forests has been demonstrated in Belo-sur-Mer, where<br />

local people have exploited <strong>the</strong> resource in a sustainable manner for many decades (Henry Chartier<br />

and Henry, 1997), and we conclude that <strong>the</strong> people living near <strong>the</strong>se mangals are likewise already<br />

engaged in an element <strong>of</strong> stewardship <strong>of</strong> <strong>the</strong>ir mangrove forest. With this in mind, a<br />

recommendation can be made to <strong>the</strong> local village that <strong>the</strong> creek is dredged in order to link it with<br />

<strong>the</strong> sea to prevent fur<strong>the</strong>r mangal loss in Lovokampy.<br />

The three mangals are far from a pristine condition and if <strong>the</strong>y are to be conserved into <strong>the</strong> future<br />

<strong>the</strong>n management <strong>of</strong> <strong>the</strong>ir current diversity and restoration <strong>of</strong> a fuller diversity need to be <strong>the</strong><br />

priorities. These three mangals are all important sites for <strong>the</strong> proposed Man and Biosphere reserve<br />

yet <strong>the</strong>y are in a generally poor state <strong>of</strong> health being exploited by local populations and under threat<br />

from environmental factors. Future work combining satellite imagery, GIS techniques,<br />

hydrological, chemical and socio-economic studies, and continued biological <strong>survey</strong> work are<br />

essential to production <strong>of</strong> a suitable management plan and monitoring scheme.<br />

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