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MALAYSIAN FRESHWATER CRABS: CONSERVATION PROSPECTS AND CHALLENGES<br />
The conservation of freshwater crabs hinges almost entirely on preserving patches of natural<br />
forest large enough to maintain the good water quality of the original streams. Potamids are<br />
extremely sensitive to polluted or silted waters, and will not survive when exposed to these<br />
factors. In Singapore for example, the small patch of primary forest of Bukit Timah Hill (ca.<br />
70 hectares) is quite sufficient to maintain a small but thriving population of the potamid<br />
Johora singaporensis. This species is known from only one other area in Singapore, which is<br />
threatened with development, and Bukit Timah is probably its last refuge (see Ng 1988, 1989,<br />
1990b). The same is true for Parathelphusa reticulata, which is known to occur only in a<br />
small remnant patch of peat swamp forest patch of less than 50 hectares in the Central Catchment<br />
Area of Singapore (Ng 1989, 1990a, b). Similar patterns have been recorded for the freshwater<br />
crabs of Sri Lanka (Bahir et al. 2005).<br />
Development, agriculture and exploitation of forest products probably cannot be halted, but<br />
compromises will have to be made if many freshwater crab species are not to be extirpated. It<br />
is likely that some species have already become extinct through extensive developments in<br />
some areas before their taxonomy can be better understood. Judicious and careful exploitation<br />
(e.g., controlled logging) is unlikely to cause extinctions as long as the water drainages are not<br />
polluted or redirected and the forest cover not completely stripped away. The recolonisation<br />
of many lowland plantations and estates by more adaptable species like Parathelphusa maculata<br />
is encouraging. How more montane taxa like potamids will cope is not known, but considering<br />
their fastidious habitat requirements, most species will not be able to adapt as readily as<br />
parathelphusids.<br />
The subjectivity of threat levels assigned here must be emphasised, as some of the limitations<br />
of this study echo the challenges faced in conservation. Conservation challenges are often<br />
associated with the amount of knowledge available on the species. The freshwater crabs of<br />
Singapore and southern Peninsular Malaysia are better known, and their biology and distribution<br />
better understood, as are the potential threats. This, of course, stems from an inherent bias for<br />
conservation efforts to target the better studied species, which are better known simply because<br />
they are more easily caught by workers in more accessible areas, e.g., Johora tiomanensis, a<br />
large, locally common aquatic species found in the lower stretches of the forest streams of the<br />
southern half of Pulau Tioman, which are mostly in close proximity to villages. Conversely,<br />
hard-to-find species tend to be neglected as we simply do not know enough to initiate directed<br />
conservation efforts, e.g., Geosesarma tiomanicum, a tiny terrestrial species that dwells among<br />
the leaf litter of the forest floor in the rugged, hilly parts of Pulau Tioman, often some distance<br />
away from water sources – encountering this species in the middle of the forest is purely a<br />
matter of chance, subject to weather, seasons, and their own fluctuating populations (Ng 1988;<br />
Yeo et al. 1999).<br />
Another aspect of our limited knowledge of some freshwater crabs that proves challenging<br />
for conservation, is the evolving taxonomy of some taxa. Some wide-ranging “species” that<br />
we might try to conserve (or worse, not see the need to conserve, presuming that they are<br />
widespread and common enough) may actually prove to be complexes of several distinct<br />
cryptic taxa, which could differ in various ways such as diets, habits, microhabitat preferences,<br />
ecological niches, local distribution, etc. One such possibility is Johora intermedia, which is<br />
here assigned the status of “Least Concern” primarily because it has been recorded from more<br />
than 20 sites throughout the lower half of the Main Range of Peninsular Malaysia (Selangor,<br />
Pahang, Negri Sembilan and northwestern Johor) in an estimated Extent of Occurrence of<br />
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