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Other Names chat pêcheur, chat viverrin (French) Fischkatze (German) gato pescador (Spanish) mecho biral, mecho bagh (Bangladesh) mach bagral, bagh dasha (Bengali: India) bun biral, khupya bagh (Hindi: India) kucing bakau (Indonesia) sua hay (Laos) kyaung ta nga (Myanmar) mach billi (Pakistan) |
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kola diviya, handun diviya (Sinhalese: Sri Lanka) |
Description and Behavior
The fishing cat, however, is still appropriately named, for fish have been found to be its most frequently taken prey
in Nepal’s Royal Chitwan National Park (D. Smith in litt. 1993). Fishing cats are good swimmers, and
have been observed to dive into water after fish (Breeden 1989), as well as attempt to scoop them out
of water with their paws (Leyhausen 1979). Other water-associated prey are probably taken as well,
ranging from crustaceans and molluscs to frogs and snakes. Fishing cats also prey on rodents, small Indian civet,
young chital fawns and wild pig (P. Sanyal in litt. 1991, D. Smith in litt. 1993), as well as domestic goats,
calves, dogs and poultry (Sterndale 1884, Phillips 1935, de Alwis 1973, Bhattacharyya 1988, Sanyal 1992).
Birds are the least frequently taken prey item in Chitwan (D. Smith in litt. 1993). Roberts (1977)
reports that in Pakistan fishing cats have been seen to catch waterfowl by swimming up to them while fully
submerged and seizing their legs from underneath. A fishing cat was seen scavenging a cow carcass in India’s
Keoladeo National Park (Haque 1988), and in Chitwan, fishing cats have been observed to scavenge tiger
kills, as well as livestock carcasses (D. Smith pers. comm.).
Phillips (1935) noted that, in Sri Lanka, fishing cats could be met “at any hour of the day.”
Biology
Gestation (C): 63 (Ulmer 1968) - 70 days (Mellen 1989)
Litter Size (C): 2.61+0.28 (n=13) (Mellen 1989); range 1-4 (Green 1991)
Age at Independence (W): 10 months (Weigel 1975)
Longevity (C): average 12 years (K. Corbett in litt. 1993)
Habitat and Distribution
The fishing cat also has a discontinuous distribution (Figure 11).
It has long been thought to be absent south of the Isthmus of Kra, but a new record has emerged from
Peninsular Malaysia, where a fishing cat was captured in 1967 and taken to a zoo (van Bree and Khan
1992). It is not clear whether the fishing cat has colonized Peninsular Malaysia from the north in recent
years, whether it has always been present but rare, or whether the new record represents an escape from
captivity. The new record does suggest, however, that the presence of the species in Singapore, Bali and Borneo
-- where three old and possibly erroneous records exist - deserves further investigation (van Bree and Khan
1992). There is no record of the fishing cat from China (Wang and Wang 1986), but it might be
found in Guangxi or Yunnan near the border with Vietnam. Swinhoe (1862) reported the presence of
the fishing cat on Taiwan, but it does not actually occur there. In India, the fishing cat is found in the valleys of
the Ganga and Brahmaputra rivers, and along the upper part of the east coast and possibly still the south-west
coast, but not elsewhere in the peninsula. In Pakistan, it is mainly found along the lower reaches of the Indus
River, although a few stragglers penetrate the northeast of the country along the Ravi and and Sutlej rivers
(Roberts 1977).
In Java, the fishing cat appears to be restricted to small numbers in isolated coastal wetlands: there were no
records during recent surveys further inland than 15 km and it must be considered critically endangered
(Melisch et al. 1995). The habitat is threatened by human encroachment or agriculture and aquaculture,
and pollution by pesticides.
Population Status
Fishing cats are locally common around wetlands. Major systems which potentially support large numbers of
fishing cats include the Sundarbans mangrove forests of Bangladesh and India, the terai region along the foot of
the Himalayas in India and Nepal, the floodplain of the Ganges and the Brahmaputra, Cambodia’s Great Lake
(Tonle Sap), the coastal floodplains of eastern Sumatra, and the deltas of the Salween, Irrawaddy, Red, Mekong,
and Indus rivers (Sanyal 1983, Khan 1986; R. Salter, C. Santiapillai, C. McDougal in litt.). However,
all of these areas have been highly affected by human activities. While fishing cats are reportedly common
around villages in wetland areas where habitat conversion has not been drastic, such as the outskirts of Calcutta
where the dominant land use is aquaculture (Sanyal 1992), they do not appear to be so adaptable to
rice paddy and other irrigated forms of cultivation (de Alwis 1973, Dao Van Tien in litt. 1990, K. Mukherjee
in litt. 1991). Along India’s thickly-populated south-western coast and in the Indus river basin in Pakistan,
fishing cats are probably on the verge of extinction (U. Karanth, T. Roberts, B. Wright in litt. 1991, 1993)
D. Smith (in litt. 1993) recorded home range size for females in Nepal’s Chitwan National Park of 4-8
km2 (n=3); a single male had a home range of 22
km2. Jungle cats were observed in parts of all four fishing cat
home ranges.
Protection Status: CITES Appendix II
National Legislation:
Hunting Regulated:
No Legal Protection:
No Information:
Wetland destruction is the primary threat facing the species. A survey of the status of Asian wetlands found that 50% of over 700 sites were faced with moderate to high degrees of threat, including settlement, draining for agriculture, pollution, and excessive hunting, wood-cutting and fishing. Severely threatened sites include the estuaries of the Karnataka coast (south-western India) and the deltas of the Irrawaddy, Indus, Mekong and Red rivers (Scott and Poole 1989). In addition, clearance of coastal mangroves over the past decade has been rapid in Tropical Asia (Dugan 1993).
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© 1996 IUCN - The World Conservation Union