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Koshkarev, E. P. (1989). The snow leopard in Kyrgyzstan. The composition of the area, ecology, and protection.
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Koshkarev, E. P. (1989). The snow leopard in Kirgizia. Ilim, Frunze.
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Kuznetsnov, G. U., & Matyushkin, E. N. (1980). The snow leopard hunts. Int.Ped.Book of Snow Leopards, 11, 44–48.
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Lane, B. C. (1984). Stalking the snow leopard: a reflection on work. The Christian Century, 101, 79.
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Limbu, R. (1999). Snow Leopards could save Mountain Biodiversity.
Abstract: The woman in the picture is wrapped in a luxurious fur coat and hat. The distinctly spotted pelt is that of a snow leopard -- that elusive and endangered species found in the mountains of central and south Asia. “A coat like that would probably cost $60,000-$80,000 in a big shop,” said Dr Rodney Jackson at a presentation he made recently on the status of his favorite subject. “Fortunately, changing norms of the fashion world and increasing consumer awareness (mean that) fewer people are wearing snow leopard pelts,” noted Dr Jackson, Conservation Director of the International Snow Leopard Trust. Still, the threat of extinction persists, he warns. “The demand for fur may have gone down but the demand for bones and body parts as marketable items for use in traditional Chinese medicine has gone up.” Further, conflict with humans is rapidly becoming the single most important issue, he said.
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Macdonald, A. A., & Johnstone, M. (1995). Comparative anatomy of the cardiac foramen ovale in cats (Felidae), dogs (Canidae), bears (Ursidae) and hyaenas (Hyaenidae). J Anat, 186 ( Pt 2), 235–243.
Abstract: The structure of the foramen ovale from 16 species representing 4 carnivore families, the Felidae, Canidae, Ursidae and Hyaenidae, was studied using the scanning electron microscope. The Felidae were represented by 9 domestic cat fetuses (Felis catus), 2 snow leopard neonates (Uncia uncia), an ocelot neonate (Leopardus pardalis), 2 lion neonates (Panthera leo), a panther neonate (Panthera pardus) and 3 tigers (Neofelis tigris), comprising 2 fetuses and a neonate. The Canidae were represented by a golden jackal neonate (Canis aureus), a newborn wolf (Canis lupus), 8 domestic dog fetuses (Canis familiaris), 3 red fox neonates (Vulpes vulpes) and a dhole neonate (Cuon alpinus). The Ursidae were represented by a brown bear neonate (Ursus arctos), a day-old grizzly bear cub (Ursus arctos horribilis), a polar bear neonate (Ursus maritimus), and 2 additional bear fetuses (species unknown). The Hyaenidae were represented by a striped hyaena neonate (Hyaena hyaena). In each species, the foramen ovale, when viewed from the terminal part of the caudal vena cava, had the appearance of a short tunnel. A thin fold of tissue, the developed remains of the embryonic septum primum, extended from the distal end of the caudal vena cava for a variable distance into the lumen of the left atrium and contributed towards the 'tunnel' appearance in all specimens. It constituted a large proportion of the tube, and its distal end was straight-edged. There was fibrous material underlying the endothelium of the flap, the apparent morphology of which suggested that it comprised cardiac muscle.(ABSTRACT TRUNCATED AT 250 WORDS)
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Malik, M. M. (1985). Management of Chitral Gol National Park, Pakistan. In J. A. McNeely, J. W. Thorsell, & Chalise S.R. (Eds.), People and protected areas in the Hindu Kush – Himalaya (pp. 103–106). Kathmandu, Nepal: King Mahendra for Natura Conservation and Integrated Centre for Mountain Development.
Abstract: Notes snow leopard is only a visitor and no longer a resident in Chitral Gol
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Mishra, C., & Rawat, G. S. (1998). Livestock grazing and Biodiversity Conservation: Comments on Saberwal. Conservation Biology, 12, 25–32.
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Mongar, T. B. (1992). Protected Area System Network: A Strategy for Managing Biodiversity in Bhutan..
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Murray, D., Kapke, C., Evermann, J., & Fuller, T. (1999). Infectious disease and the conservation of free-ranging large carnivores. Animal Conservation, 2, 241–254.
Abstract: Large carnivores are of vital importance to the stability and integrity of most ecosystems, but recent declines in free-ranging populations have highlighted the potentially devastating effect of infectious diseases on their conservation. We reviewed the literature on infectious diseases of 34 large (maximum body mass of adults >20 kg) terrestrial carnivore species, 18 of which are considered to be threatened in the wild, and examined reports of antibody prevalence (seroprevalence) and cases of infection, mortality and population decline. Of 52 diseases examined, 44% were viral, 31% bacterial and the remainder were protozoal or fungal. Many infections were endemic in carnivores and/or infected multiple taxonomic families, with the majority probably occurring via inhalation or ingestion. Most disease studies consisted of serological surveys for disease antibodies, and antibody detection tended to be widespread implying that exposure to micro-organisms was common. Seroprevalence was higher in tropical than temperate areas, and marginally higher for infections known to occur in multiple carnivore groups. Confirmation of active infection via micro-organism recovery was less common for ursids than other taxonomic groups. Published descriptions of disease-induced population decline or extinction were rare, and most outbreaks were allegedly the result of direct transmission of rabies or canine distemper virus (CDV) from abundant carnivore species to less-common large carnivores. We conclude that the threat of disease epidemics in large carnivores may be serious if otherwise lethal infections are endemic in reservoir hosts and transmitted horizontally among taxa. To prevent or mitigate future population declines, research efforts should be aimed at identifying both the diseases of potential importance to large carnivores and the ecological conditions associated with their spread and severity.
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