M Jeri Imansyah,Tim S Jessop, Claudio Ciofi, Deni Purwandana,
(Abstract presented in the International Seminar of Biology, Gadjah Mada University, Yogyakarta Indonesia, 7-8 September 2007)
INTRODUCTION
Insular species are mostly susceptible to threatening processes due to limiting environmental factors including habitat loss, harvesting and invasive species because they are isolated and occur on smaller land masses (Burkey, 1995). Komodo dragon (Varanus komodoensis) is an endemic and vulnerable species inhabiting five islands in the Lesser Sunda region, southeastIndonesia. To facilitate implementation of management and conservation strategiesfor Komodo dragons in
MATERIALS AND METHODS
The study was undertaken from 2003 to 2006 across 10 study sites on the islands of Komodo (393.4 km2), Rinca (278.0 km2), Gili Motang (10.3 km2), and Nusa Kode (9.3 km2) within the boundary of
RESULTS AND DISCUSSION
The study showed significant insular divergences in Komodo dragon population density, body size for both SVL and weight, and Timor deer density as its main prey (One way ANOVA F3,3=120.67, p<0.001;>F3,99=10960.97, p<0.001) name="OLE_LINK4">F3,99= 6707.63, p<0.001), style="color: black;">F3,1218=120.67, p<0.001, respectively) (Table 1). Smaller islands showed significantly lower values of these parameters than the larger islands.
The study suggests that there are major divergences in both population (density and body size) and ecological parameter (main prey density) among insular Komodo dragon populations. In particular, the Komodo dragon population on Gili Motang island displayed significant differences in both population size and individual body mass from the other islands. Ciofi & Bruford (1999) showed that the Gili Motang population had the lowest level of genetic diversity compared to other insular populations as a result of limited gene flow and high genetic drift. Low population density, a reduced degree of genetic variation and a shortage of main prey species demand for island-specific conservation strategies for Komodo dragons on Gili Motang. Current management strategies adopted by
Table 1. Summary results of Komodo density, body size, and prey density index
Island | Komodo Density (ind/km2) | Komodo SVL (cm) | Komodo weight (kg) | Deer density (pellet group/ transect) | |||
Komodo | 18.83 | 142.80 | 63.93 | 26.97 | |||
Rinca | 30.59 | 128.80 | 48.16 | 20.27 | |||
Gili Motang | 13.68 | 99.41 | 17.06 | 5.64 | |||
Nusa Kode | 11.80 | 95.53 | 15.99 | 7.81 |
Figure 1. Correlation between Deer density index and Komodo density
REFERENCES
[1] Burkey, T.V., “Extinction rates in archipelagos: implications for populations in fragmented habitats”, Conservation Biology 9, 527–541. 1995.
[2] Ciofi, C., Bruford, M.W., ”Genetic structure and gene flow among Komodo dragon populations inferred by microsatellite loci analysis”, Molecular Ecology 8, S17–S30.1999.
[3] Jessop, T.S., Madsen, T., Ciofi, C., Imansyah, M.J., Purwandana, D., Rudiharto, H., Arifiandy, A., Phillips, J.A, “Island differences in population size structure and catch per unit effort and their conservation implications for Komodo dragons”, Biological Conservation 135:247-255. 2007.
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