Riordan, P. (1998). Unsupervised recognition of individual tigers and snow leopards from their footprints (Vol. 1).
Abstract: This study presents the testing of two unsupervised classification methods for their ability to accurately identify unknown individual tigers, Panthera tigris, and snow leopards, Panthera uncia, from their footprints. A neural-network based method, the Kohonen self-organizing map (SOM), and a Bayesian method, AutoClass, were assessed using hind footprints taken from captive animals under standardized conditions. AutoClass successfully discriminated individuals of both species from their footprints. Classification accuracy was greatest for tigers, with more misclassification of individuals occurring for snow leopards. Examination of variable influence on class formations failed to identify consistently influential measurements for either species. The self-organizing map did not provide accurate classification of individuals for either species. Results were not substantially improved by altering map dimensions nor by using principal components derived from the original data. The interpretation of resulting classifications and the importance of using such techniques in the study of wild animal populations are discussed. The need for further testing in the field is highlighted.
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Rieger, I. (1978). Scent marking behaviour of ounces, Uncia uncia. In L. Blomqvist (Ed.), International Pedigree Book of Snow Leopards, Vol. 1 (Vol. 1, pp. 78–103). Helsinki: Helsinki Zoo.
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Rieger, I. (1980). Some aspects of the history of ounce knowledge. In L. Blomqvist (Ed.), International Pedigree Book of Snow Leopards, Vol. 2 (Vol. 2, pp. 1–36). Helsinki: Helsinki Zoo.
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Rieger, I. (1982). Breeding ounces, Uncia uncia (Schreber, 1775) in zoological gardens. In L. Blomqvist (Ed.), International Pedigree Book of Snow Leopards, Vol. 3 (Vol. 3, pp. 49–50). Helsinki: Helsinki Zoo.
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Riddell, M. L. G. (2004). Snow Leopard Expedition Kazakhstan 2004.
Abstract: This Newcastle University Expedition reviewed the conflict between man and snow leopard in the region east of Tekeli in the Dzhungarian Alatau range, Kazakhstan. After the soviet state breakup in 1991 snow leopards in Kazakhstan and in the other Asian republics were subjected to high levels of persecution. There are thought to be between 180-200 snow leopards in Kazakhstan, of which 37-40 individuals inhabit the Dzhungarian Mountains. No work has been done previously to review the present snow leopard-human conflicts in this region, and this project looked to update previous reports from Central Asia about predominant conflicts in these regions. The expedition team worked with the Institute of Zoology in Kazakhstan and two of the six person team were Kazakh students. Methods comparable to those used in previous studies were used to map and rank the threats in the western area of the range, over an eight week period. The expedition team lived in the mountains for periods of two-three weeks, carrying all their food and equipment and using local vehicles, horses and trekking to move from pasture to pasture. Semi-structured interviews, key informant interviews and prey counts were used to assess snow leopard-human conflicts including poaching of snow leopard, poaching of leopard wild prey, human disturbance and livestock overgrazing. The results from the report support much previous work from Kazakhstan and other areas in Central Asia, but serve as a useful update shedding light on an optimistic future for snow leopard conservation while highlighting what the expedition team perceives to be the major threats to snow leopards. The threats to snow leopards, in order of relevance from most to least, are loss of prey predominantly through hunting by local people (both legal and illegal), direct hunting of snowleopard for pelt/medicine, disturbance by herders on the pastures, snow leopard habitat fragmentation around the mountain bases, and least importantly overgrazing by domestic livestock. Retaliatory kills by herders are not a threat in the region and on livestock were killed by snow leopards. Levels of all hunting, legal and illegal, need to be reduced in the range until wildlife populations have recovered significantly from the mid-1990's over-hunting period. Levels of rural corruption among many stakeholders were high around the mountain region, and are thought to contribute negatively to wildlife conservation in the area. Ecotourism in the area, that incorporates local people around the mountain region, is proposed as a solution to offer local people's incentives to lower hunting levels. This report makes the following main recommendations:
ÿStrengthening law enforcement capacity
ÿIncreasing the number of ecological rangers
ÿIncreasing incentives of ecological rangers to prevent poaching
ÿEquipping the ecological rangers more sufficiently
ÿMore effective communication between ranger and National Park administrative regions
ÿThe involvement of all stakeholders in wildlife conservation including military officials and local herders
ÿWhistle blower policies to prevent illegal trade in all animals in the region
ÿMore geographic consistency between present and proposed protected areas in the region
Accurate snow leopard monitoring to build on valuable information previously collected in Kazakhstan
Provision of local incentives (ecotourism and community based hunting reserves) to reduce local hunting and local unemployment around the mountains
Increased interest and technical assistance in Kazakhstan from conservation International Non-Governmental Organizations
More government fund for the Institute of Zoology
Stronger cross border (Kazakhstan-China) legislation implementation Further research could involve establishing an annual, standardized, snow leopard
survey in the range, or could compare these findings of threats to snow leopards to other regions in Kazakhstan (eg. The Altai) or Central Asia.
This report has been replicated for all the expedition sponsors, put on the internet, and
distributed among contacts in the snow leopard conservation community.
The expedition team also spent some time exploring and photographing some of the remoter valleys around the study pastures, and made a short video of the teams exploits. Links were made between KIMEP University in Almaty, and Newcastle University, registered a research centre with the Royal Geographical Society, and lectured about the Dzhungarian range and snow leopard conservation at; the Royal Geographical Society, Newcastle University, Royal Zoological Society for Scotland(Edinburgh Zoo), and Wilderness Lecturers (Bristol).
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Richardson, N. (2010, 16 Dec 2010). The snow leopard: ghost of the mountains. The telegraph.
Abstract: Snow leopards face the threats of poaching, habitat loss and diminishing prey. In remotest Mongolia, a research team is keeping tabs on this iconic and elusive species.
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Ricciuti, E. R. (1976). This fragile earth/Part II: Mountains besieged. International Wildlife, (November-December), 24–33.
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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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Razmakhnin V.E. (1977). Siberian wild ibex.
Abstract: It provides a detailed description of biology, distribution, geographic variability, behavior, and locomotion features of ibex in the USSR. Its population was defined as 100,000 animals, main enemies being wolf, snow leopard, and golden eagle. Wolf mainly preys on ibex at the end of winter; old males, weakened during the heat mostly becoming a prey. Snow leopards prey on ibexes all year round. Golden eagles mostly prey on young ibexes.
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Rashid, W., Shi, J., Rahim, I. U., Dong, S., Sultan, H. (2020). Issues and Opportunities Associated with Trophy Hunting and Tourism in Khunjerab National Park, Northern Pakistan. Animals, 10(597), 1–20.
Abstract: Trophy hunting and mass tourism are the two major interventions designed to provide various socioeconomic and ecological benefits at the local and regional levels. However, these interventions have raised some serious concerns that need to be addressed. This study was conducted in Khunjerab National Park (KNP) with an aim to analyze comparatively the socioeconomic and ecological impacts of trophy hunting and mass tourism over the last three decades within the context of sustainability. Focus Group Discussions (FGDs) with key stakeholders and household interviews were conducted to collect data on trophy hunting and mass tourism, and on local attitudes towards these two interventions in and around KNP. The results revealed that 170 Ibex (Capra sibirica) and 12 Blue sheep (Pseudois nayaur) were hunted in the study area over the past three decades, and trophy hunting was not based on a sustainable harvest level. Trophy hunting on average generated USD 16,272 annual revenue, which was invested in community development. However, trophy hunting has greatly changed the attitudes of local residents towards wildlife: a positive attitude towards the wild ungulates and strongly negative attitude towards wild carnivores. In addition, trophy hunting has reduced the availability of ungulate prey species for Snow leopards (Panthera uncia), and consequently, Snow leopards have increased their predation on domestic livestock. This has, in turn, increased human–snow leopard conflict, as negative attitudes towards carnivores result in retaliatory killing of Snow leopards. Furthermore, according to ocial record data, the number of tourists to KNP has increased tremendously by 10,437.8%, from 1382 in 1999 to 145,633 in 2018. Mass tourism on average generated USD 33,904 annually and provided opportunities for locals to earn high incomes, but it caused damages to the environment and ecosystem in KNP through pollution generation and negative impacts on wildlife. Considering the limited benefits and significant problems created by trophy hunting and mass tourism, we suggest trophy hunting should be stopped and mass tourism should be shifted to ecotourism in and around KNP. Ecotourism could mitigate human–Snow leopard conflicts and help conserve the fragile ecosystem, while generating enough revenue incentives for the community to protect biodiversity and compensate for livestock depredation losses to Snow leopards. Our results may have implications for management of trophy hunting and mass tourism in other similar regions that deserve further investigation.
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Rashid, W., Shi, J., Rahim, I. U., Dong, S., Ahmad, L. (2020). Research trends and management options in human-snow leopard conflict. Biological Conservation, 242(108413), 1–10.
Abstract: Conservation of the snow leopard (Panthera uncia) is challenging because of its threatened status and increase in human-snow leopard conflict (HSC). The area of occupancy of the snow leopard comprises mountainous regions of Asia that are confronted with various environmental pressures including climate change. HSCs have increased with a burgeoning human population and economic activities that enhance competition between human and snow leopard or its preys. Here we systematically review the peer-reviewed literature from 1994 to 2018 in Web of Science, Google Scholar, Science Direct and PubMed (30 articles), to evaluate the current state of scholarship about HSCs and their management. We determine: 1) the spatio-temporal distribution of relevant researches; 2) the methodologies to assess HSCs; 3) and evaluate existing interventions for conflict management; and 4) the potential options for HSC management. The aim of the current study is thus to identify key research gaps and future research requirements. Of the articles in this review, 60% evaluated the mitigation of HSCs, while only 37% provided actionable and decisive results. Compensation programs and livestock management strategies had high success rates for mitigating HSCs through direct or community-managed interventions. Further research is required to evaluate the efficacy of existing HSC mitigation strategies, many of which, while recommended, lack proper support. In spite of the progress made in HSC studies, research is needed to examine ecological and sociocultural context of HSCs. We suggest future work focus on rangeland management for HSC mitigation, thus ultimately fostering a co-existence between human and snow leopard.
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Rashek V.A. (1980). The Chatkal State nature reserve. Aksu Jabagly nature reserve.
Abstract: It describes history of the Chatkal and Aksu Jabagly nature reserves' establishment and provides data concerning hydrography, soils, climate, landscapes, altitude zoning, flora and fauna, and main aspects of scientific work.
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Rana, B. S. (1997). Distinguishing kills of two large mammalian predators in Spiti Valley Himachal Pradesh. J.Bombay Nat.Hist.Soc, 94(3), 553.
Abstract: The author studied livestock killed by predators in the Spiti Valley, India, to determine what species had killed yaks, horses, donkeys, and other domestic animals. Eleven of the kills examined were made by snow leopards and six by the Tibetan wolf. Wolves were involved in surplus killings, while snow leopards kill as food is needed. lgh
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Raj, R. D. (1999). A Green Chief Minister in a Green State.
Abstract: As chief minister of the Indian state of Sikkim, Pawan Kumar Chamling has the onerous job of protecting one of the hottest biodiversity properties in the world. Chamling has been more than equal to the task. Last month, he earned the title of “greenest chief minister” of India's 22 federal states for policies that range from banning plastic bags to cancelling a major hydro-electric project.
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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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Puzanov I.I. (1938). Central Asia sub-area.
Abstract: The author describes fauna of the Central Asia sub-area. Snow leopard is a typical inhabitant of the sub-area highlands.
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Proskuryakov M.A. (1969). Almaty nature reserve.
Abstract: A description of the Almaty nature reserve is given and includes as follows: data of establishment, location, physic and geographic description, types of soils, climate, flora and fauna. In the nature reserve there are 39 mammals and 117 birds. Snow leopard, wild ibex, brown bear, lynx, wild boar, red deer, wolf, fox etc. inhabited in the nature reserve.
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Prokopov K.P. (1990). Taxonomic list of mammal fauna of eastern Kazakhstan (Vol. Vol. I.).
Abstract: During the period 1965 through 1988, studies were conducted in the north-east of Kazakhstan (Kazakhstan's Altai, Zaisan depression, Saur-Tarbagatai) and list of mammals (104 species) for the area made.
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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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Prater, S. H. (1971). The Book of Indian Animals: The snow leopard, or ounce, Panthera uncia (Schreber). (Vol. Third, pp. 69–70).
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Prasad, S. N., Chundawat, R. S., Hunter, D. O., Panwar, H. S., & Rawat, G. S. (1991). Remote sensing snow leopard habitat in the trans-Himalaya of India using spatial models and satellite imagery preliminary results. In G. J. Buhyoff (Ed.), (pp. 519–523).
Abstract: The snow leopard (Panthera uncia) is a flagship species for conservation in the high mountain regions of central Asia. Data on snow leopard predation, habitat conditions and range of main prey species were gathered along with thematic maps of the study area for elevation, snow cover, sighting data, kill data, blue sheep use areas, and vegetation data. These data were entered into a GIS and used to help delineate surface features from a satellite image. Preliminary results show that general physiographic features of snow leopard habitat can be detected using satellite imagery and that GIS cartographic modeling techniques can improve this delineation. -from Authors
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Prakash, I. (1985). Asian predators of livestock. Parasites, pests and predators.World animal science, B2, 405–410.
Abstract: Outlines the distribution, status and predatory behaviour on livestock of Chinese alligator Alligator sinensis, gharial Gavialis gangeticus and several species of Crocodylus and Python; and of wolf Canis lupus, Asiatic jackal C. aureus, dhole (Indian wild dog) Cuon alpinus, brown bear Ursus arctos, Asiatic black bear Selenarctos thibetanus, striped hyaena Hyaena hyaena, clouded leopard Neofelis nebulosa, leopard (panther) Panthera pardus, tiger P. tigris, lion P. leo, snow leopard P. uncia, other Felidae and Viverridae. -P.J.Jarvis
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Poyarkov, A. D., & Subbotin, A. E. (2002). The Snow Leopard Status in Russia.. Islt: Islt.
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Poyarkov, A. D., & Subbotin, A. E. (2002). Strategic Priorities and the System of Measures for Snow Leopard Conservation in Russia.. Islt: Islt.
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Poyarkov, A. D., Samoylova, G. S., & Subbotin, A. E. (2002). Evaluation of Potential Habitats of Snow Leopard (Uncia Uncia, Schreb.) In Altay-Khangay-Sayan Region and in Territory of Russian Federation: GIS Approach.. Islt: Islt.
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