|Scientific Name:||Ceylonthelphusa kandambyi|
|Species Authority:||Bahir, 1999|
|Taxonomic Notes:||This species was formerly included in the Parathelphusidae but has recently been reassigned to the Gecarcinucidae; Parathelphusidae is now regarded as a junior synonym of Gecarcinucidae (Klause et al. in press).|
|Red List Category & Criteria:||Near Threatened ver 3.1|
|Assessor(s):||Bahir, M.M., Ng, P.K.L., Crandall, K. & Pethiyagoda, R. and Cumberlidge, N.|
|Reviewer(s):||Darwall, W. (IUCN Freshwater Biodiversity Assessment Unit), Pollock, C.M. (IUCN Red List Unit) and McIvor, A.|
Listed as Near Threatened because although the extent of occurrence (EOO) is around 1,750 km² and area of occupancy (AOO) is <100 km², and the species is known from only five locations (which would allow it to qualify as EN if the habitat extent or quality was declining), at least part of the range lies within protected areas administered by the Sri Lankan Forest Department. Currently it is also locally common. If, however, protection was removed from the area, the species is likely to decline rapidly due to habitat degradation, which is occurring elsewhere on Sri Lanka.
|Previously published Red List assessments:|
|Range Description:||Endemic to Sri Lanka. Extent of occurrence 1,750 km². Area of occupancy <100 km². Known from five locations.|
Near Pituwala waterfall at Elpitiya; Galle District; Matara District; Udugama; Kurutara District (see Bahir 1999).
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||Abundance of species at each site of occurrence is locally common.|
|Current Population Trend:||Stable|
|Habitat and Ecology:||Occurs in freshwater aquatic habitats in the wet zone area of Sri Lanka. Species appears to be entirely aquatic, and restricted to areas above and around 80m above mean sea level. It was observed in shallow water and at the bottom of pools 1-2 m deep, in both well-lit and shaded areas.|
Sri Lanka’s aquatic habitats are threatened by invasive alien species (>90 percent of the freshwater-fish biomass comprises exotics: Pethiyagoda 1994) and pollution, while its forests are threatened by encroachment and illegal produce extraction. The greater threats to the island’s remaining wet zone habitats are perceived to be from indirect sources exacerbated by ‘island effects’ resulting from fragmentation— invasive species, pesticide influx, edge effects, local climate change and rainwater acidification.
Pesticides are a serious concern given that these substances are freely and widely used in Sri Lanka. Regulation presently addresses only human safety issues, and not impacts on other non-target organisms or the environment in general (Anon. 1980). Given that 24 of Sri Lanka’s 49 freshwater crab species are restricted to montane and sub-montane habitats, poor sloping-land management and unwise land-use change in the highlands continues to be a serious problem (Hewawasam et al. 2003). An estimated 292 MT ha-1 yr-1 of topsoil is lost to erosion from these lands, degrading habitats and increasing silt loads in streams and rivers (ADB 2003).
Even species with wide ranges and apparent tolerance of land-use changes could suffer catastrophic declines as a result of changes, for example, in land developments, hydrology or pesticide-use regimes. For example, the populations of two species of widely-distributed freshwater fishes (Labeo lankae and Macrognathus aral) assessed in 1980 as "common" (Senanayake 1980) crashed within a decade, without warning, for reasons still unknown— they are now presumed extinct (Pethiyagoda 1994).
The long-term security of Sri Lanka’s biodiversity will depend on minimizing fragmentation impacts through effective land-use planning and restoration initiatives while maximizing habitat connectivity between forest sites. Such goals can be met only through a policy framework built on sound scientific data, implemented through sustained, long-term financing mechanisms. Planning on such a scale is not imminent in Sri Lanka, and in the mean time, it is best that conservation activities be aimed primarily at preserving the integrity of sites and habitats while at the same time closely monitoring key populations.
The conservation of freshwater crabs hinges almost entirely on preserving patches of natural forest large enough to maintain the good water quality of the original streams. Many parathelphusids are extremely sensitive to polluted or silted waters, and will not survive when exposed to these factors.
|Citation:||Bahir, M.M., Ng, P.K.L., Crandall, K. & Pethiyagoda, R. and Cumberlidge, N. 2008. Ceylonthelphusa kandambyi. The IUCN Red List of Threatened Species 2008: e.T61696A12528475.Downloaded on 26 March 2017.|
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