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Koshkarev, E. (1998). Snow leopard along the border of Russia and Mongolia. Cat News, 28, 12–14.
Abstract: The author discusses the distribution of snow leopards along the border of Russia and Mongolia. The range extension of the leopard indicates their ability to cross desert areas that separate mountain habitats.habitat; range extension; scat analysis; techniques; tracks/tracking | snow leopard
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Krever V. (1998). Ecosystems of the High Mountains Species of Special Interest in Uzbekistan.
Abstract: It gives description complexes of mountain ecosystems fauna of Central Asia, endangered vertebrates, main threats to biodiversity and existing protected areas network. Among the rare animal species of the alpine and subalpine meadows first of all should be listed the West Tien Shan endemic, the Menzbier's marmot (Marmota menzbien); the markhor wild goat which still inhabits the Vakhsh range in Tadjikistan; the dhole (Cyon alpinus) which is practically extinct; the Tien Shan bear (Ursus arctos isabellinus), and the snow leopard (Uncia uncia); among birds, the wlute-chested dove (Columba leuconota), sandgrouse (Syrrhaptes tibetanus, snowcocks (Tetraogallus tibetanus, T.altaicus) and bearded vulture (Gypaetus barbatus).
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Linnell, J., Swenson, J., Landa A., & and Kvam, T. (1998). Methods for monitoring European large carnivores – A worldwide review of relevant experience. NINA Oppdragsmelding, 549, 1–38.
Abstract: Against a background of recovering large carnivore populations in Norway, and many other areas of Europe, it is becoming increasingly important to develop methods to monitor their populations. A variety of parameters can monitored depending on objectives. These parameters include: presence/absense, distribution, population trend indices, minimum counts, statistical estimates of population size, reproductive parameters and health/condition. Three broad categories of monitoring techniques can be recognised each with increasing levels of fieldwork required. The first category includes those techniques that do not require original fieldwork. The second category involves fieldwork, but where individually recognisable carnivores are not available. The third category includes methods where fieldwork has recognisable individuals available. Different mehtods tend to have been used for different species, mainly because of limitations imposed by the different species' ecology. The most precise estimates of population size have been obtained in research projects with relatively small study sites and with the help of radio-telemetry. However, it may be difficult, or impossible, to apply these methods over large monitoring areas. Therefore, in terms of practical management, a combination of minimum counts, supported by an independent index may be more useful than statistical population estimates. All methods should be subject to a careful design process, and power analysis should be conducted to determine the sensitivity of the method to detect changes.
Based on the review of over 200 papers and reports we recommend a package of complementary monitoring methods for brown bear, wolverine, lynx and wolf in Norway. These include the use of observations from the public and reports of predation on livestock to determine broad patterns of distribution, and an index based on hunter observations per hunting day, for all four species. Minimum counts of reproductive units, natal dens, family groups, and packs, should be obtained from snow-tracking for wolverines, lynx and wolves respectively. In addition a track-count index should be obtained for wolverines and lynx. As much data as possible should be obtained of lynx and wolvereines killed in the annual harvest. Brown bears will be difficult to monitor without the use of radio-telemetry, therfore they may require periodic telemetry based, mark-recapture studies. Such a program can easily be constructed within existing central and regional wildlife management structures, but will require extensive involvement from hunters.
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Maier, F. (1998). Tracking the snow cat of Ice Mountain. Wildlife Conservation, 101(3), 36.
Abstract: Snow leopard preservation efforts by Russian biologist Eugene Koshkarev are hampered by the lack of technology and the attitudes of the local population. Without access to radio-collars until recently, the biologists have had to use low-tech research methods such as field observation. The chabani, or semi-nomadic herders of Central Asia, fear the leopards as predators and set traps. Local governments also allow hunting
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Meszaros, M. (1998). Einsam im Land des Dschingis Khan. Universum, , 68–76.
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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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Myroniuk, P. (1998). Snow leopards down under. In L. Blomqvist (Ed.), International Pedigree Book of Snow Leopards (Vol. 7, p. 25). Helsinki: Helsinki Zoo.
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Nishine, Y. (1998). The captive snow leopard programme (SSCJ) in Japan. In L. Blomqvist (Ed.), International Pedigree Book of Snow Leopards (Vol. 7, pp. 21–25). Helsinki: Helsinki Zoo.
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Pavlinov I.Ya. (1998). Taxonomy of mammals in the USSR: additions.
Abstract: A full hierarchic system of mammal fauna in the USSR and CIS countries, list of synonyms, comments on taxonomy, and information about geographical distribution are given. Genus Uncia Gray, 1854 includes one species U. uncia (Schreber, 1776) distributed in highlands (up to 5,000 m) of Central Asia (Tibet, Pamir, Tien-Shan, Altai). Synonyms: irbis.
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Reed-Smith, J., & Kumpf, M. (1998). Snow leopards (Uncia uncia): family group management alternatives. Anim.Keepers' Forum, 25(10), 386–391.
Abstract: The authors offer insights into creating family groups of snow leopards in zoos. The programs at the Denver Zoo, Denver, Colorado, and at John Ball Zoological Gardens, Grand Rapids, Michigan, are highlighted. lgh.
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