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Rieger, I. (1978). Management techniques of captive ounces, (Uncia uncia). Int.Ped.Book of Snow Leopards, 1, 50–70.
Abstract: Presents a comparison of housing and techniques for care and breeding at 16 zoos. Includes comments on factors which may influence breeding
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Schaller, G. B., Jurang, R., & Mingjiang, Q. (1988). Status of snow leopard (Panthera-uncia) in Qinghai-Province and Gansu Province-China. Biological Conservation, 45(3), 179–194.
Abstract: The status and distribution of the snow leopard Panthera uncia was investigated in two provinces of China. The cats occur over about 65,000km2 or 9% of the Qinghai Province, and in a few places along the western edge of Gansu Province. In many areas the animals have in recent decades been decimated or locally eradicated, as have their prey. Counts of wild ungulates in 9 mountain block, totalling 1375km2, known for abundant wildlife, had an average of 1.4-5.4 animals km2, principally blue sheep Psuedois nayaur, which together with marmot Marmota himalayana, represent the snow leopards main prey. Possibly 650 snow leopards survive in Qinghai but shooting and trapping of this legally protected animal and the hunting of blue sheep for local consumtion and export threaten their existence.
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Scheber. (1975). Snow Leopard in the south part of Gobi-Altai mountain range.
Abstract: Accorfing to the information from Gurvan its rumored that the snow leopards grow in number and many times they attacked the livestock entering into the domestic area causing damage, we investigated theGurvan Tes sumon of Umnogobi aimag and also Noyon sumon todisplay the reserve review and spreading area of snow leopard from 22 of December of 1975 to 10th of January of 1976.
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Shafiq, M. M., & Abid, A. (1998). Status of large mammal species in Khunjerab National Park. Pakistan Journal of Forestry, 48(1-4), 91–96.
Abstract: Study on the current status of large mammals species population was carried out in Khunjerab National Park, Northern Areas. The observation recorded showed that the population of Tibetan Red fox (Vulpes vulpes montana), Snow leopard (Uncia uncia), and Wolf (Canis lupus) have, though a bit, increased but are still in the rank of “Endangered”. While the population of Himalyan Ibex (Cpara ibex sibirica) is increasing more rapidly and their status is now “Common” in the Park. The limited population of Marcopolo sheep (Ovis ammon polii), Tibetan wild Ass (Equus hemionus kiang) and Brown bear (Urus arctos) is still under threat, and comes them under “Critical Endangered” category.
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Shrestha, B. (2008). Prey Abundance and Prey Selection by Snow Leopard (uncia uncia) in the Sagarmatha (Mt. Everest) National Park, Nepal.
Abstract: Predators have significant ecological impacts on the region's prey-predator dynamic and community structure through their numbers and prey selection. During April-December 2007, I conducted a research in Sagarmatha (Mt. Everest) National Park (SNP) to: i) explore population status and density of wild prey species; Himalayan tahr, musk deer and game birds, ii) investigate diet of the snow leopard and to estimate prey selection by snow leopard, iii) identify the pattern of livestock depredation by snow leopard, its mitigation, and raise awareness through outreach program, and identify the challenge and opportunities on conservation snow leopard and its co-existence with wild ungulates and the human using the areas of the SNP. Methodology of my research included vantage points and regular monitoring from trails for Himalayan tahr, fixed line transect with belt drive method for musk deer and game birds, and microscopic hair identification in snow leopard's scat to investigate diet of snow leopard and to estimate prey selection. Based on available evidence and witness accounts of snow leopard attack on livestock, the patterns of livestock depredation were assessed. I obtained 201 sighting of Himalayan tahr (1760 individuals) and estimated 293 populations in post-parturient period (April-June), 394 in birth period (July -October) and 195 November- December) in rutting period. In average, ratio of male to females was ranged from 0.34 to 0.79 and ratio of kid to female was 0.21-0.35, and yearling to kid was 0.21- 0.47. The encounter rate for musk deer was 1.06 and density was 17.28/km2. For Himalayan monal, the encounter rate was 2.14 and density was 35.66/km2. I obtained 12 sighting of snow cock comprising 69 individual in Gokyo. The ratio of male to female was 1.18 and young to female was 2.18. Twelve species (8 species of wild and 4 species of domestic livestock) were identified in the 120 snow leopard scats examined. In average, snow leopard predated most frequently on Himalayan tahr and it was detected in 26.5% relative frequency of occurrence while occurred in 36.66% of all scats, then it was followed by musk deer (19.87%), yak (12.65%), cow (12.04%), dog (10.24%), unidentified mammal (3.61%), woolly hare (3.01%), rat sp. (2.4%), unidentified bird sp. (1.8%), pika (1.2%), and shrew (0.6%) (Table 5.8 ). Wild species were present in 58.99% of scats whereas domestic livestock with dog were present in 40.95% of scats. Snow leopard predated most frequently on wildlife species in three seasons; spring (61.62%), autumn (61.11%) and winter (65.51%), and most frequently on domestic species including dog in summer season (54.54%). In term of relative biomass consumed, in average, Himalayan tahr was the most important prey species contributed 26.27% of the biomass consumed. This was followed by yak (22.13%), cow (21.06%), musk deer (11.32%), horse (10.53%), wooly hare (1.09%), rat (0.29%), pika (0.14%) and shrew (0.07%). In average, domestic livestock including dog were contributed more biomass in the diet of snow leopard comprising 60.8% of the biomass consumed whilst the wild life species comprising 39.19%. The annual prey consumption by a snow leopard (based on 2 kg/day) was estimated to be three Himalayan tahr, seven musk deer, five wooly hare, four rat sp., two pika, one shrew and four livestock. In the present study, the highest frequency of attack was found during April to June and lowest to July to November. The day of rainy and cloudy was the more vulnerable to livestock depredation. Snow leopard attacks occurred were the highest at near escape cover such as shrub land and cliff. Both predation pressure on tahr and that on livestock suggest that the development of effective conservation strategies for two threatened species (predator and prey) depends on resolving conflicts between people and predators. Recently, direct control of free – ranging livestock, good husbandry and compensation to shepherds may reduce snow leopard – human conflict. In long term solution, the reintroduction of blue sheep at the higher altitudes could also “buffer” predation on livestock.
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Wajrak, A. (1994). Snow Leopard Skins in Poland (Polowanie Na Sniezna Pantere).
Abstract: Full Text: In 1991, Dr Andrzej Kruszewicz of the Institute of Ecology of the Polish Academy of Sciences saw a “quite fresh” snow leopard skin on sale by a Russian in a Warsaw market for three million Polish zlotys ($300). A few weeks later he saw another skin in a shop in the centre of Warsaw. In spring 1992, Marcin Waslawski from the Institute of Geography saw a snow leopard skin in the same market for the equivalent of $200. The seller was an Asian from a former Soviet Republic. In summer 1992, Wajrak himself saw a snow leopard skin in a hunters' shop in Warsaw and in winter saw one in the home of a Polish hunter, who said it was a gift from a Mongolian friend. In winter 1994, a student from Britain saw a Polish long coat of snow leopard skins in Bialowieza. Wajrak saw a skin in a Warsaw shop, which the owner said was 15-20 years old; he got it from a Polish diplomat who had been in Mongolia and had three snow leopard skins. The skin was priced at the equivalent of $1,000. Wajrak added that he had been told that it was possible to buy tiger skins from Russians in Poland and he was trying to find one; I have not heard from him since.
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White, S. D., Stannard, A. A., Ihrke, P. J., & Rosser, E. J. (1981). Therapy of demodicosis in snow leopard challenged. J Am Vet Med Assoc, 178(9), 877–878.
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Abdunazarov B.B. (1994). Rare and endangered animal species in the Kashkadaraya region.
Abstract: 41 percent of all vertebrate species listed in the Red Book of the Uzbek SSR (18 mammal species, 29 bird, 6 reptile, and 8 fish species) inhabit the Kashkadarya region. The mammals are Tien Shan brown bear, Central Asian otter, Turkistan lynx, snow leopard, and goitered gazelle. Nesting bird fauna includes the following species: black stork, Turkistan white stork, short toed eagle, booted eagle, golden eagle, bearded vulture, black vulture, griffon vulture, saker falcon, houbara bustard, and eagle owl. Migrating and wintering bird species are dalmatian pelican, rose pelican, mute swan, osprey, tawny eagle, imperial eagle, pin-tailed sandgrouse; and possibly Bonnli's eagle and Barbary falcon that have not been seen here since 1950-s. Rare reptiles are represented by two species: desert monitor and Central Asian cobra.
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Abzalov A.A. (1974). Game management development.
Abstract: An issue of wildlife conservation in game preserves, forestries, and sanctuaries is discussed. In some regions of Uzbekistan there are various protected wildlife areas preserving unique and game species: marchor in the Kugitan hunting farm, Bukhara deer the Bukhara region, bear and snow leopard, argali, ibex, wild-boars, snow-cock, partridge, eagle, etc. in the Miraki hunting farm, pheasants in the Karadara forestry. To restore and upgrade the game management level in the country it is required to properly create game preserves, enlarge reproduction activity, strictly follow rules and terms of hunting and cultivate careful and solicitous attitude to wildlife and its resources in all hunters.
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Akimushkin I. (1988). Snow leopard or irbis.
Abstract: Snow leopard behavioral patterns, food preferences, and reproduction are described in a popular way. The population of snow leopard is defined to be 1,000 animals. A reason for the population decline is hunting for the sake of beautiful fur.
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