







| Kingdom | Phylum | Class | Order | Family |
|---|---|---|---|---|
| ANIMALIA | CHORDATA | ACTINOPTERYGII | CYPRINIFORMES | CYPRINIDAE |
| Scientific Name: | Labeo fisheri | |||
| Species Authority: | Jordan & Starks, 1917 | |||
Common Name/s:
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| Synonym/s: |
Labeo gadeya Deraniyagala, 1929
Morulius gadeya (Deraniyagala, 1929)
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| Red List Category & Criteria: | Endangered B1ab(iii) ver 3.1 | |||||||||||||||
| Year Assessed: | 2009 | |||||||||||||||
| Assessor/s: | Devi, R. & Boguskaya, N. | |||||||||||||||
| Reviewer/s: | Collen, B., Darwall, W., Ram, M. & Smith, K. (SRLI Freshwater Fish Evaluation Workshop) | |||||||||||||||
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Justification: L. fisheri has been assessed as Endangered due to its restricted range (Extent of Occurrence less than 5,000km²), continuing decline in habitat quality, and the fact the species is considered to be found in less than five locations. There are reports that L. fisheri has suffered from declines (unknown levels) and may be extinct, however further research is required to confirm this. |
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| History: |
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| Population: | It has been reported that L. fisheri may already be extinct, as a result of habitat loss following the Mahaveli River Development Project (Wikramanayake 1990), see Major Threats. |
| Population Trend: |
Unknown
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| Habitat and Ecology: | L. fisheri is a benthopelagic species that only inhabits deep, fast-flowing sections of the river. It has not been recorded from unshaded, silty or turbid waters. It moves fast through the water, staying close to the bottom. Juveniles have been observed picking algae off submerged rocks. It occurs sympatrically with (and possibly mistaken for) Puntius sp. 'martenstyn' throughout its known range. |
| Systems: | Freshwater |
| Major Threat(s): | There are a number of threats to the habitat of L. fisheri. The Accelerated Mahaweli Development Programme, initiated in 1979, included developing the Mahaweli River to provide irrigation facilities for dry zone agriculture and generate hydro-electric power, by constructing four new dams (Asian Development Bank 2006). In addition, the rainforests of Sri Lanka are rapidly being depleted by agriculture, mining, logging and urbanization. Between 1956 and 1980, total forest cover had been reduced from 44 to 25 percent. One result of this deforestation is stream degradation due to increased erosion, siltation, extreme flow fluctuations and decreased shade cover (Wikramanayake 1990). |
| Conservation Actions: | Surveys to confirm the suspected extinction of L. fisheri (Wikramanayake, 1990) are recommended. |
| Citation: | Devi, R. & Boguskaya, N. 2009. Labeo fisheri. In: IUCN 2011. IUCN Red List of Threatened Species. Version 2011.2. <www.iucnredlist.org>. Downloaded on 07 February 2012. |
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