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Kattel, B., & Bajimaya, S. S. (1997). Status and Conservation of Snow Leopard in Nepal. In R.Jackson, & A.Ashiq (Eds.), (pp. 21–27). Lahore, Pakistan: International Snow Leopard Trust.
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Kogan M.I. (1931). The Kazakh SSR. The Kyrgyz SSR. The Uzbek and Tajik SSR. The Turkmen SSR.
Abstract: It describes geographical, soil, climatic and hydrological features of Kazakhstan, Kyrgyzstan, Uzbekistan, and Tajikistan. Types of economic activities including fur-trade are described, too. Game preserves are classified, and list of game fauna species inhabiting these republics is given. Snow leopard lives in rocky mountains and is hunted very rarely.
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Koshkarev, E. (2000). What Has Happened to the Snow Leopard After the Break-Up of Soviet Union? Snow Line, Xvi.
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McCarthy, T. (1999). Snow Leopard Conservation Plan for the Republic of Mongolia.
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Mishra, C., & Fitzherbert, A. (2004). War and wildlife: a post-conflict assessment of Afghanistan's Wakhan Corridor. Oryx, 38(1), 102–105.
Abstract: Prior to the last two decades of conflict, Afghanistan's Wakhan Corridor was considered an important area for conservation of the wildlife of high altitudes. We conducted an assessment of the status of large mammals in Wakhan after 22 years of conflict, and also made a preliminary assessment of wildlife trade
in the markets of Kabul, Faizabad and Ishkashem. The survey confirmed the continued occurrence of at least eight species of large mammals in Wakhan, of which the snow leopard Uncia uncia and Marco Polo sheep Ovis ammon are globally threatened. We found evidence of human-wildlife conflict in Wakhan due to livestock depredation by snow leopard and wolf Canis lupus. Large mammals are hunted for meat, sport, fur, and in retaliation against livestock depredation. The fur trade in Kabul is a threat to the snow leopard, wolf, lynx Lynx lynx and common leopard Panthera pardus.
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Koshkarev, E. (1994). Poaching in Former USSR (Vol. xii). Seattle: International Snow Leopard Trust.
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Maming, R. (2012). Market prices for the tissues and organs of snow leopards in China. Selevinia, (20), 119–122.
Abstract: The population of snow leopard (Uncia uncia) is plummeting as waterfall in
the last ten years. The illegal trade of snow leopard products is one of the fatal
factors. The biggest range and the biggest population of snow leopard both are in
China, and the largest trade is also in the country. Through questionnaires and
investigation with informants from 2002 to 2012, a lot of data were collected
through variety ways in different regions. In this paper 387 cases of snow leopard
poaching including smuggling routes, product list, price system and product usages
from Xinjiang Uygur Autonomous Region were collected for analysis and discussion. In
the face of rapid development in the west of China, the results showed that our
government did not try to protect the snow leopards, and the text of law was
practically useless. International organizations such as WWF, WCS, IUCN, PANTHERA,
SLT & SLN with SLSS were also powerless and helpless to stop snow leopard poaching
and trading. As a result, the fate of the snow leopard is very bad, and this is
worrying.
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Sultan, H., Rashid, W., Shi, J., Rahim, I. U., Nafees, M., Bohnett, E., Rashid, S., Khan, M. T., Shah, I. A., Han, H., Ariza-Montes, A. (2022). Horizon Scan of Transboundary Concerns Impacting Snow Leopard Landscapes in Asia. Land, 11(248), 1–22.
Abstract: The high-altitude region of Asia is prone to natural resource degradation caused by a variety of natural and anthropogenic factors that also threaten the habitat of critical top predator species, the snow leopard (Panthera uncia). The snow leopard’s landscape encompasses parts of the twelve Asian countries and is dominated by pastoral societies within arid mountainous terrain. However, no investigation has assessed the vulnerability and pathways towards long-term sustainability on the global snow leopard landscape scale. Thus, the current study reviewed 123 peer-reviewed scientific publications on the existing knowledge, identified gaps, and proposed sustainable mitigation options for the longer term and on larger landscape levels in the range countries. The natural resource degradation in this region is caused by various social, economic, and ecological threats that negatively affect its biodiversity. The factors that make the snow leopard landscapes vulnerable include habitat fragmentation through border fencing, trade corridor infrastructure, non-uniform conservation policies, human–snow leopard conflict, the increasing human population, climatic change, land use and cover changes, and unsustainable tourism. Thus, conservation of the integrated Socio-Ecological System (SES) prevailing in this region requires a multi-pronged approach. This paper proposes solutions and identifies the pathways through which to implement these solutions. The prerequisite to implementing such solutions is the adoption of cross-border collaboration (regional cooperation), the creation of peace parks, readiness to integrate transnational and cross-sectoral conservation policies, a focus on improving livestock management practices, a preparedness to control human population growth, a readiness to mitigate climate change, initiating transboundary landscape-level habitat conservation, adopting environment-friendly trade corridors, and promoting sustainable tourism. Sustainable development in this region encompasses the political, social, economic, and ecological landscapes across the borders.
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Kanderian, N., Lawson, D., Zahler, P. (2011). Current status of wildlife and conservation in Afghanistan. International Journal of Environmental Studies, 68(3), 281–298.
Abstract: Afghanistan’s position in latitude, geography and at the intersection of three biogeographic realms has resulted in a surprising biodiversity. Its wildlife includes species such as the snow leopard, Asiatic black bear, Marco Polo sheep, markhor and greater flamingo. Principal threats include high levels of deforestation, land encroachment and hunting for food and trade. Continuing security issues have also made it difficult to monitor species abundance and population trends. Over the last decade, however, survey efforts have provided the first collection of species and habitat data since the late 1970s. Initial findings are enabling the Government and rural communities to begin implementing important conservation measures. This process has included policy development and protected area planning, promoting alternative livelihoods and responsible community management, and continuing research into the status of biodiversity in the field.
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Heinen, J. T., & Leisure, B. (1993). A new look at Himalayan Fur Trade. Oryx, 27(4), 231–238.
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