Kreuzberg-Mukhina, E., Esipov A.V., Bykova, E. A., Vashetko, E. V., & Aromov, B. (2003). Development of the national Action Plan for the conservation of Snow Leopard in Uzbekistan. Report: 1-51 (Vol. 1-51). Uzbekistan.
Abstract: This document is the final report on the ISLT Project “Development of national Action plan for the conservation of Snow Leopard in Uzbekistan” and a Conservation Strategy for the Snow leopard in Uzbekistan. It includes biology and current status, limiting factors, existing and necessary conservation measures.
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Kyes, R., & Chalise, M. K. (2003). Snow Leopard Study Summary 2003, Langtang National Park, Nepal.
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Lukarevskiy V.S. (2003). Peculiarities of communicative behavior of leopard, irbis, lynx, and caracal.
Abstract: It gives the description of communicative behavioral system (visual, olfactory and vocal elements) for two groups of large Felidae species such as leopard-irbis and lynx-caracal. General and specific behavioral regularities are given.
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Medvedev D.G. (2003). Distribution and migration of the snow leopard in Baikal region.
Abstract: It provided description of snow leopard distribution in Eastern Sayan, South Transbaikalia and mountains of Baikal lake as well as its migratory ways within the region.
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Prokopov K.P. (2003). The Red Data Book of vertebrate animals in eastern Kazakhstan.
Abstract: After the inventory of all rare and endangered species the categories of threat in the Red Data Book of eastern Kazakhstan has changed for most of the species: 24 species were referred to category 1 (endangered species) (in Kazakhstan's Red Data Book 14 species); 26 (14) species to category 2 (decreasing species); 11 (24) to category 3 (rare); and 1 (3) to category 5 (rehabilitated). There are three nature reserves in the region: Markakol, West Alatai, and Alakol to protect wild vertebrate animals.
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Raghavan, B., Bhatnagar, Y., & Qureshi, Q. (2003). Interactions between livestock and Ladakh urial (Ovis vignei vignei); final report.
Abstract: The Ladakh urial (Ovis vignei vignei) is a highly endangered animal (IUCN Red List 2000) listed in the Appendix 1 of CITES and Schedule 1 of the Indian Wildlife Protection Act 1972. Its numbers had been reduced to a few hundred individuals in the 1960s and 70s through hunting for trophies and meat (Fox et al. 1991, Mallon 1983, Chundawat and Qureshi 1999, IUCN Red List 2000). However, with the protection bestowed by the IWPA 1972, and resultant decrease in hunting, the population seems to have shown a marginal increase to about 1000-1500 individuals in its range in Ladakh (Chundawat and Qureshi 1999, IUCN Red List 2000). Although the species had in the past, been able to coexist with the predominantly Buddhist society of Ladakh, the recent increase in the population of both humans and their livestock has placed immense pressures on its habitat (Shackleton 1997, Chundawat and Qureshi 1999, Raghavan and Bhatnagar 2003). This is especially important considering that the Ladakh urial habitat coincides with the areas of maximum human activity in terms of settlements, agriculture, pastoralism and development, in Ladakh (Fox et al. 1991, Chundawat and Qureshi 1999, Raghavan and Bhatnagar 2003). Increased developmental activities such as construction of roads, dams, and military bases in these areas have also increased the access to their habitat. This has consequently made the species more vulnerable to the threats of poaching and habitat destruction (Fox et al. 1991, Chundawat and Qureshi 1999, Raghavan and Bhatnagar 2002). Pressure from increased livestock grazing is one of the major threats faced by the species today (Shackleton 1997, Fox et al. 1991, Mallon 1983, IUCN Red List 2000 Chundawat and Qureshi 1999, Raghavan and Bhatnagar 2003). In the impoverished habitat provided by the Trans-Himalayas, there is great competition for the scarce resources between various animal species surviving here (Fox 1996, Mishra 2001). The presence of livestock intensifies this competition and can either force the species out of its niche (competitive exclusion) by displacing it from that area or resource, or lead to partitioning of resources between the species, spatially or temporally, for coexistence (Begon et al. 1986, Gause 1934).
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Sokolov G.A. (2003). Predatory mammals of Central Siberia, status of populations, influence of anthropogenic factors.
Abstract: The species resources of Siberia's fauna decrease from south to north. The highest diversity of species is observed in the mountain systems, the lowest in sub-zones of south and central taiga and steppe zone, where the cat family species are absent. During the last 50 150 years number of species has decreased two- to tenfold. Imperfect hunting management, farming, and mining operations resulted in transformation of the animal habitats. Population of fox, polecat, and sable has reduced; snow leopard and dhole becoming endangered species. If current tendencies continue to develop some species will disappear in the region in decades to come.
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Tursunov Kh. (2003). The Ugam-Chatkal national park. The Chatkal state biosphere nature reserve.
Abstract: Established in 1990, the Ugam-Chatkal national park occupies an area of 668,350 ha and is the largest protected natural area in Uzbekistan. This area is famous for its rich species diversity. A number of rare and endangered plant and animal species, including among the others snow leopard, is found here. Being a core zone (strictly protected natural area), the Chatkal nature reserve is an integral part of the park. Snow leopard is periodically observed in the Tereksay river valley in the Maidantal area.
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Karanth, K. U., Nichols, J.D., Seidensticker, J., Dinerstein, E., David Smith, J.L., McDougal, C., Johnsingh, A.J.T., Chundawat, R.S., Thapar, V. (2003). Science deficiency in conservation practice: the monitoring of tiger populations in India. Animal Conservation, 6, 141–146.
Abstract: Conservation practices are supposed to get refined by advancing scientific knowledge. We study this phenomenon in the context of monitoring tiger populations in India, by evaluating the ‘pugmark census method’ employed by wildlife managers for three decades. We use an analytical framework of modern animal population sampling to test the efficacy of the pugmark censuses using scientific data on tigers and our field observations. We identify three critical goals for monitoring tiger populations, in order of increasing sophistication: (1) distribution mapping, (2) tracking relative abundance, (3) estimation of absolute abundance. We demonstrate that the present census-based paradigm does not work because it ignores the first two simpler goals, and targets, but fails to achieve, the most difficult third goal. We point out the utility and ready availability of alternative monitoring paradigms that deal with the central problems of spatial sampling and observability. We propose an alternative sampling-based approach that can be tailored to meet practical needs of tiger monitoring at different levels of refinement.
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(2002). Biological resources.
Abstract: It provides a summary of plant and animal resources in Uzbekistan. Among 15,000 animal species, 664 are vertebrate species including 424 bird, 97 mammal, 83 fish, 59 reptile and three amphibian species. Snow leopard, snow cock, ibex, and other species are typical for highlands.
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