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CONSERVATION STRATEGIES OF SHOREA LUMUTENSIS (DIPTEROCARPACEAE) IN PENINSULAR MALAYSIA<br />

100<br />

90<br />

80<br />

70<br />

% of alleles<br />

60<br />

50<br />

40<br />

30<br />

20<br />

10<br />

0<br />

10 30 50 70 90 110 130 150 170 190 210 230 250 270 290 310 330<br />

No. of individua ls<br />

Fig. 6. Changes in % of alleles maintained with changes in the number of individuals of S.<br />

lumutensis removed. All values were based on a mean of 1000 resamplings with standard<br />

errors (SE). Dotted lines represent standard errors.<br />

DISCUSSION AND RECOMMENDATIONS<br />

This study showed that S. lumutensis comprises only five populations and perhaps no more<br />

than 500 large individuals; extinction of the species is likely if nothing is done to conserve it.<br />

There are two basic conservation strategies for plants, in situ and ex situ conservation. In situ<br />

conservation involves the designation, management and monitoring of species at the location<br />

where they are currently found, whereas ex situ conservation involves the sampling, transfer<br />

and storage of species away from the original locations where they were found. Conserving S.<br />

lumutensis in its natural habitat is clearly the first step. However, ex situ conservation is also<br />

necessary to provide insurance against catastrophic events and to facilitate the possibility of<br />

future reintroduction into appropriate habitats.<br />

Selection of In situ Conservation Area<br />

Shorea lumutensis has >90% of its total genetic diversity residing within the population and<br />

displays mix-mating system. As the species is endemic to Peninsular Malaysia and comprises<br />

only five populations and perhaps no more than 500 large individuals, the five populations<br />

need to be conserved. The cluster analysis showed that Segari Melintang harbors some unique<br />

genetic characteristics which should receive additional attention for conservation purposes.<br />

The minimum population size needed to maintain 95% of its genetic diversity was estimated as<br />

270 individuals (in the range of 200-310) and the mean breeding unit size was estimated as 52<br />

individuals. When planning a conservation area, however, a minimal population size should be<br />

regarded only as a last resort and an extreme compromise. For added safety, much larger<br />

population or area should constitute units of in situ conservation (Hawkes et al. 1997). However,<br />

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