|
|
Anonymous. (1992). International Specialists Discuss China's Threatened Cats.
|
|
|
|
Anonymous. (1994). Resolutions Conservation of Snow Leopard, Seventh International Snow Leopard Symposium. In J.L.Fox, & D.Jizeng (Eds.), (pp. 329–331). Usa: Islt.
|
|
|
|
Anonymous. (1999). Livestock Predation Control Workshop.
|
|
|
|
Aramov, B. (1997). The Biology of the Snow Leopard in the Gissarsky Nature Reserve. In R. and A. A. Jackson (Ed.), (pp. 108–109). Lahore, Pakistan: Islt.
|
|
|
|
Aromov, B. (1982). The Materials of the Numbers of Dispersed Animal Species in Kyzylsu Nature Reserve..
|
|
|
|
Bajimaya, S., Baral N., & Yadav L.B. (1990). Report on Overall Assessment of Dhorpatan Hunting Reserve.
|
|
|
|
Bannikov A.G. (1966). Mountains of Middle Asia and Kazakhstan.
Abstract: The data on geographical location, plants and animals of mountain nature reserves of Middle Asia and Kazakhstan are given. Snow leopard and its preys (wild ibexes and sheep) were recorded in both Almaty and Aksu Jabagly nature reserves.
|
|
|
|
Bhatnagar, Y. V. (1997). Ranging and Habitat Use by Himalayan Ibex (Capra ibex sibirica) in Pin Valley National Park. Ph.D. thesis, Saurashtra University, .
|
|
|
|
Bhatnagar, Y. V. (2008). Relocation from wildlife reserves in the Greater and Trans-Himalayas: Is it necessary? (Vol. 6).
Abstract: The Greater and Trans-Himalayan tracts are cold deserts that have severe seasonal and resource scarce environments. Covering the bulk of Indian Himalayas, they are a rich repository of biodiversity values and ecosystem services. The region has a large protected area (PA) network which has not been completely effective in conserving these unique values. The human population densities are much lower (usually < 1 per sq km) than in most other parts of the country (over 300 to a sq km). However, even such small populations can come into conflict with strict PA laws that demand large inviolate areas, which can mainly be achieved through relocation of the scattered settlements. In this paper, I reason that in this landscape relocation is not a tenable strategy for conservation due to a variety of reasons. The primary ones are that wildlife, including highly endangered ones are pervasive in the larger landscape (unlike the habitat 'islands' of the forested ecosystems) and existing large PAs usually encompass only a small proportion of this range. Similarly, traditional use by people for marginal cultivation, biomass extraction and pastoralism is also as pervasive in this landscape. There does exist pockets of conflict and these are probably increasing owing to a variety of changes relating to modernisation. However, scarce resources, the lack of alternatives and the traditional practice of clear-cut division of all usable areas and pastures between communities make resettlement of people outside PAs extremely difficult. It is reasoned that given the widespread nature of the wildlife and pockets of relatively high density, it is important to prioritise these smaller areas for conservation in a scenario where they form a mosaic of small 'cores' that are more effectively maintained with local support and that enable wildlife to persist. These ideas have recently gained widespread acceptance in both government and conservation circles and may soon become part of national strategy for these areas.
|
|
|
|
Braden, K. (1984). Nature Preserves of the Soviet Union. In L.Blomqvist (Ed.), (pp. 11–14). Helsinki: Leif Blomqvist and Helsinki Zoo.
|
|
