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Paltsyn, M., Spitsyn, S.V., Kuksin, A. N., Istomov, S.V. |
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Snow Leopard Conservation in Russia |
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2012 |
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101 |
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This publication reviews potential actions for the long-term conservation of
snow leopards and their habitat in Russia in conditions of anthropogenic influence
and climate change in high elevation ecosystems. This edition is the result
of many years of research conducted in the framework of WWF’s “Ensuring the
long term protection of biodiversity in the Altai-Sayan Ecoregion” (1998-2011)
and the United Nations Development Program (UNDP) financed by the Global
Environment Facility “Conservation of Biodiversity in the Russian portion Altai-
Sayan Ecoregion” (2005-2010).
The publication contains materials needed to prepare a Russian Snow Leopard
Conservation Strategy and was prepared for use by the Russian Ministry
of Natural Resources to develop comprehensive priority conservation measures
to protect this species. In addition, this publication is intended for protected
area specialists and staff at federal and regional government agencies
responsible for the conservation and monitoring of species listed in the
Russian Federation Red Book.
Reviewer: B. Munkhtsog, Candidate in Biological Sciences, staff scientist at
the Institute for Biology, Mongolian Academy of Sciences, and president of the
Mongolian Snow Leopard Center.
Translation to English: J. Castner. |
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1384 |
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Mallon, D. |
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Title |
Trophy Hunting of Cites-Listed Species in Central Asia |
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2013 |
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Executive Summary:
The report is part of a project aiming to strengthen capacities to implement CITES, especially in
Central Asia and to satisfy the CITES‐related requirements of trading partners, to prevent
overexploitation and to ensure legal international trade in wild fauna and flora does not exceed
sustainable levels. The objective is to enhance the policies and regulations concerning trophy
hunting in selected range States of the Argali Ovis ammon: Kazakhstan, Kyrgyzstan, the Russian
Federation, Tajikistan and Uzbekistan and to provide a framework for the establishment of
sustainable hunting programmes that support conservation. This report is focused on the relevance
of trophy hunting for conservation and associated local livelihoods.
Sustainable use of biological diversity is an integral part of the Convention on Biodiversity (1992) and
is seen as a valuable tool in conserving biological diversity. The Addis Ababa Principles and Guidelines
(AAPG) set out the basis for sustainable use of natural resources. The IUCN SSC1 Guiding Principles on
Trophy Hunting as a Tool for Creating Conservation Incentives, and the European Charter on Hunting
and Biodiversity provide further guidance on the sustainability of trophy hunting, including on highly
threatened species. The International Council for Game and Wildlife Conservation (CIC) together
with the Food and Agriculture Organization of the United Nations (FAO) has also developed Best
Practice Guidelines for trophy hunting.
All five project countries are Parties to CITES, except Tajikistan, which has begun the accession
process. Argali are the focus of the trophy hunting in the region and they represent the most
expensive trophy in the five project countries. Other CITES‐listed hunting species are Brown Bear
Ursus arctos, Wolf Canis lupus, Musk Deer Moschus moschiferus, Eurasian Lynx Lynx lynx (all mainly
in Russia) and Houbara Bustard Chlamydotis undulata. Markhor Capra falconeri and Urial Ovis
orientalis have also been hunted at times but are not the object of regular trophy hunting
programmes at present. Other widely hunted species are not listed in the CITES Appendices.
A recent analysis by TRAFFIC of the CITES trade database showed that 10 245 hunting trophy items
from species listed in the CITES Appendices were exported from the project countries between 2000
and 2010. Almost all trophy items consisted of Argali, Brown Bear and Wolf. Most were exported
from Russia (9473 trophies), with smaller numbers from Tajikistan (705), Kyrgyzstan (668), and
Kazakhstan (126), and 13 from Uzbekistan.
In the region, wildlife is generally the property of the State, which awards rights to use it to
individuals or other entities. National legislation covering hunting and wildlife protection may refer
to sustainable use but this is undefined. The legal rights of local communities are also not generally
specified. FAO and CIC produced a review of national legislation that set out in detail the basic
principles of sustainable wildlife management laws (2008). One of the main findings was that
legislative frameworks in the region frequently consisted of different legal instruments that were not
always harmonized and sometimes overlapped. In some cases, there was also a lack of institutional
clarity, with overlapping jurisdictions among different agencies.
Poaching for meat and trophies or commercial products is a significant factor across the whole
region, negatively affecting all the main hunting species, as well as protected species. Wild
populations have been reduced, sometimes drastically so. Poaching of Argali and other mountain
ungulates may be carried out by military or border personnel and is not restricted to areas outside
formal nature reserves: indeed, law enforcement and protected area staff are sometimes complicit
in illegal hunting, driven in part by the very low salaries. There are numerous recent examples of
poaching and illegal trade in trophies of CITES‐listed species. The actual level of illegal off‐take is
unknown. Known cases may represent a very small fraction of the real total. The wildlife
conservation sector is under‐resourced across the region with a lack of funding, trained personnel,
transport and other equipment severely limiting the effectiveness of anti‐poaching efforts.
Memoranda of Understanding under the Convention on Migratory Species (CMS MoUs) and their
associated action plans for Saiga Saiga tatarica and Bukhara Deer Cervus elaphus bactrianus have
proven to be effective instruments in facilitating species recovery. A CMS Single Species Action Plan
for Argali is in preparation (Roettger & Singh, in prep) and will provide a framework for conservation.
Trophy hunting in the region is predominantly organized on a commercial basis. Community‐based
hunting initiatives in the region are in their infancy and face some legal and institutional obstacles.
There are however promising developments: for example, five community‐based NGOs in Tajikistan
are managing wildlife in legally assigned areas and three of them have hosted hunting clients (on
non‐CITES species). Well‐developed community‐based trophy hunting programmes operate in
Pakistan, targeted at Markhor Capra falconeri which is listed in CITES Appendix I, and in Namibia,
which is widely seen as a leader in such programmes, and while the specific conditions and sociopolitical
background of both differ in several ways from those in the region, they nonetheless
provide instructive guidance on the principles of successful community conservancy organization.
There is an extensive literature on trophy hunting, its potential to contribute to conservation of
biodiversity and local livelihoods, and the potential negative effects of selective harvesting on
species. The consensus view seems to be that selective harvest of trophy‐age males does not impact
negatively in the short term, if only a low proportion of the available trophy‐age individuals are
harvested, but uncontrolled harvest can lead to a decline in horn size and thus trophy quality, as well
as have negative demographic effects. Trophy hunting programmes raise substantial revenues in
some African countries, and in the best cases significant sums are received at community or
conservancy level. However, this is not universally the case and inequitable benefit sharing remains
a major challenge to be overcome. Good governance is an essential requirement when developing
hunting and other forms of community based management initiative.
A possible decline in size of Argali trophies in Kyrgyzstan has been reported and determining
whether this is actually the case, and the causes, is a priority. Standardized monitoring, involvement
of independent experts, transparency in quota setting and allocation of licences are all seen as
prerequisites of well‐managed and sustainable hunting operations. Allocation of long‐term leases for
concessions is needed to motivate managers to invest in anti‐poaching and other conservation
measures and remove the temptation for short‐term profit that threatens the sustainability of the
resource.
Developing all forms of Community‐based Natural Resource Management (CBNRM) – trophy hunting
and tourism – is also recommended. As the concept is still new to many parts of the region, and the
legal‐political background is not always sympathetic, building on examples of existing community
conservancies (in Tajikistan) or where there is an administrative basis for local management of
resources (Kyrgyzstan), is likely to be effective. Ensuring that communities and conservancies are
legally empowered to manage and utilise wildlife and to receive revenues for such use is a basic
requirement.
Recommendations on good practice are set out in several publications and salient points relevant to the region are highlighted. |
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1415 |
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Mallon, D., Kulikov, M. |
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Title |
Transboundary Snow Leopard Conservation in Central Asia: Report of the FFI/CMS Workshop, 1-2 December 2014 |
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2015 |
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Fauna & Flora International |
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In Partnership with Convention on Migratory Species |
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1419 |
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Ferretti, F., Lovari, S. |
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Predation may counteract climatic change as a driving force for movements of mountain ungulates |
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2016 |
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Behavioural-Processes |
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101-104 |
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Climate change, Environmental change, Interspecific interactions, Large cats, Predator-prey interactions |
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Temperature variations are expected to influence altitudinal movements of mountain herbivores and, in
turn, those of their predators, but relevant information is scarce. We evaluated monthly relationships
between temperature and altitude used by a large mountain-dwelling herbivore, the Himalayan tahr
Hemitragus jemlahicus, and its main predator, the snow leopard Panthera uncia, in an area of central
Himalaya for five consecutive years (2006–2010). In contrast to expectations, there was no significant
direct relationship between altitude of tahr sightings and temperature. The mean altitude of tahr sightings
decreased by c. 200 m throughout our study. As expected, snow leopard movements tracked those of tahr,
although the core area of the snow leopard did not move downwards. Tahr remained the staple of the
snow leopard diet: we suggest that the former did not move upwards in reaction to higher temperature
to avoid encounters with the latter. Avoidance of competition with the larger common leopard Panthera
pardus at lower altitudes could explain why snow leopards did not shift their core area downwards.
Apparently, interspecific interactions (predation; competition) influenced movements of Himalayan tahr
and snow leopards more than climatic variations. |
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1441 |
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Nowell, K., Li, J., Paltsyn, M., Sharma, R. K |
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Title |
An ounce of prevention: Snow Leopard Crime Revisited |
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2016 |
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Traffic |
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Snow Leopard poaching and trafficking – referred to herein as Snow Leopard crime – is revisited 13 years after TRAFFIC’s first report on the subject, Fading Footprints: The Killing and Trade of Snow Leopards (Theile, 2003). This report builds on a preliminary analysis published in May 2016 (Maheshwari and von Meibom, 2016). It addresses a major information gap concerning the linkage between retaliatory killing for livestock depredation and poaching for trade, and the scale at which both are taking place. The focus is on 12 Snow Leopard range countries: Afghanistan, Bhutan, China, India, Kazakhstan, the Kyrgyz Republic, Mongolia, Nepal, Pakistan, Russia, Tajikistan and Uzbekistan. There is little evidence of illegal trade in Snow Leopards outside these countries.
Two sets of data were developed in the research for this report. The first is a Snow Leopard crime database containing records of seizures (legal actions taken by government authorities) and observations (reports of Snow Leopard killing, capture or trade, including market surveys). The database contains records dating back to 1989 (which are discussed in Annex 1), but the analysis focuses on the period since the release of Fading Footprints, the first TRAFFIC report: 2003-June 2016. Seizures are a function of law enforcement effort, effectiveness and publicization, as well as the magnitude of illegal trade, and so observations are an important component of the analysis, particularly for countries where few seizures are made or reported. However, detailed observations are not regularly published, and may be are biased toward countries where there is more effort, so a simple multiple choice survey was designed for Snow Leopard experts. Completed by 42 of them in 2016, and covering all 12 range countries, the survey asked experts for their total number of known cases, case outcomes, and reasons for killing Snow Leopards.
Based on the average number of cases known to experts over the average of nine years spent working in their geographic areas of knowledge, 221-450 Snow Leopards were estimated to have been poached annually since 2008. With the average rate of poaching detection estimated by experts at less than 38%, these numbers could be substantially higher. Of these, 55% are killed in retaliation for livestock depredation, 21% killed for trade and 18% taken by non-targeted methods such as snares. Although retaliatory killing is estimated to account for roughly half of Snow Leopard poaching (55%), experts estimate that there is a 50-50 chance (48%) that a poaching attempt will take place after a depredation incident. On average, experts estimate that 60% of retaliatory and non-targeted poaching incidents result in an attempt to sell; accounting for differences in this estimate between countries, a total of 108-219 Snow Leopards potentially enter into illegal trade. Over 90% of annual Snow Leopard poaching is estimated to occur in five range countries: China (103-236), Mongolia (34-53), Pakistan (23-53), India (21-45) and Tajikistan (20-25).
Given the uncertainties about population numbers, as well as the low rate of poaching detection, it is difficult to assess the impact of this offtake on the viability of the species. Snow Leopard range is used as a proxy for Snow Leopard population numbers; most national Snow Leopard population estimates are derived from extrapolating study site densities across likely range. Although China had by far the highest number of seizures and observations (309 Snow Leopards from 2003-2016) and the highest annual poaching estimate, its share of Snow Leopard crime was not disproportionate to its large share (at least 60%) of Snow Leopard range. Countries flagged for having disproportionate shares of crime levels relative to share of range included Afghanistan and Russia (seizures and observations), and Nepal and Pakistan (annual poaching estimates). China and Russia were most frequently identified as destinations for animals poached in other countries.
The expert survey indicates that the scale of Snow Leopard crime is more serious than apparent from the annual average number of Snow Leopard seized (18) or observed (34) from 2003-2016. This could be in part due to the challenges of law enforcement in the Snow Leopard’s remote montane habitat. Indeed, the survey found that an average of 23% of known cases were investigated by authorities, and only 14% prosecuted.
The minimum number of Snow Leopards in the seizures and observations database fell by 43% from the first half of the analysis period (2003-2009) compared to the second (2010-June 2016) (from 451 to 259). However, the decline was in the number of Snow Leopards observed in trade and in market surveys, which fell by 80% (from 280 to 54), with the largest decline taking place in China. There were more market surveys in the first half of the analysis period (13) than the second (5), but they
TRAFFIC report: An Ounce Of Prevention: Snow Leopard Crime Revisited xi
were repeated in the same places (Kabul, Afghanistan and cities in western China), and far fewer skins were seen (for example, 60 skins in the Chinese city of Linxia in 2007, compared to one in 2011). The numbers of Snow Leopards in other observations were roughly equivalent for the two periods (108 in the first and 100 in the second), but the numbers in trade observations fell by 46% (from 52 to 28). Otherwise, the number of Snow Leopards seized rose by 16% (from 115 to 133), and the number of individual seizure cases rose by 77% (from 44 to 78). The number of poached Snow Leopards seized doubled (from 31 to 60), and the observed number of poached Snow Leopards also increased by 14% (from 56 to 64). The number of Snow Leopards in trade seizures was the same in both periods (55), and the number smuggled roughly equivalent (29 seized in the first period, and 24 seized and observed in the second).
There are three possible interpretations of this situation of rising numbers of Snow Leopards poached (as measured by seizures and observations), steady numbers in smuggling and trade seizures, and steeply declining numbers in trade observations and market surveys. It could be that the limitations of available data and the authors’ inability to collect all of it has resulted in an incorrect picture. It is apparent that illegal trade has become more clandestine and difficult to detect in most countries, so that secondly, it could be increasing, as indicated by the apparent rise in poaching numbers. However, the number of Snow Leopards seized in large cases (more than 3 Snow Leopards per case), indicative of organized trafficking activity, declined from 60 in the 2003-2009 to 23 in 2010-2016. This points to a third possibility: that trade (and perhaps demand) is declining, possibly due to increased enforcement, but local people continue to opportunistically sell Snow Leopards they poached primarily to protect livestock.
With skins being the main Snow Leopard product type in trade (78%), the primary motive for buyers appears to be for display, with some observations of skins hanging on walls in homes and restaurants, as well as stuffed taxidermy specimens. Priced in the thousands of US dollars, skins have been described as a “symbol of wealth and power.” However, there probably exists very little in the way of a definable consumer segment deliberately seeking out such items. They are most likely purchased opportunistically – “impulse buys” – and most consumers probably only buy one in their lifetime. Once in a home, the illegal possession has very low probability of detection, and moreover law enforcement authorities may be reluctant to investigate in such situations. The purchase itself also has a low probability of detection, as indicated by the sharp decline in observed numbers of Snow Leopard skins being offered for sale. While growing personal wealth in Asia has been highlighted as a primary driver of illegal wildlife trade, poverty is also recognized as a driver, and the Snow Leopard trade may be more driven by rural people in Snow Leopard habitat attempting to make money and make up for livestock losses to predators than by wealthy people placing orders for luxury household decorations. Unlike the demand-driven Tiger trade (Annex 2), to which it otherwise bears many similarities, the market for Snow Leopards may be more a function of supply, and actions should focus on the communities living near Snow Leopards to reduce incentives to poach and sell. This notion is reflected in the aphorism behind the title of this report: an ounce of prevention equals a pound of cure. Preventing livestock losses, offsetting the costs of losses and improving community support for Snow Leopard conservation are the most important approaches to tackling the problem of Snow Leopard trafficking.
Recommendations focus on addressing the leading cause of Snow Leopard poaching (retaliatory killing/Human-Wildlife Conflict) as well as measures to stem illegal trade, and are primarily targeted at the 12 Snow Leopard range countries. They are aligned with existing recommendations and planned actions, including CITES recommendations, draft Decisions and consultant’s reports around implementation of Resolution Conf. 12.5 (CITES 2015, 2016; Nowell and Pervushina, 2014); the Global Snow Leopard and Ecosystem Protection Program (GSLEP, 2013, 2015, n.d.); the SLN’s Snow Leopard Survival Strategy (SLN, 2014); and WWF’s Snow Leopard Species Action Plan (WWF, 2015 and Sharma, 2016). There was also an informal discussion about recommendations to address poaching and illegal trade at the Second China Snow Leopard Forum, held in Urumqi, Xinjiang province 24-26 August 2016 (B. Weckworth, Panthera, pers. comm.).
Recommendations are grouped according to four primary actors in Snow Leopard conservation: 1) governments of Snow Leopard range countries; 2) communities living in Snow Leopard range; 3) conservation organizations and Snow Leopard experts; and 4) donor governments and agencies. |
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1447 |
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Murali, R., Lkhagvajav, P., Saeed, U., Kizi, V. A., Nawaz, M. A., Bhatnagar, Y. V., Sharma, K., Mishra, C. |
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Title |
VALUATION OF ECOSYSTEM SERVICES IN SNOW LEOPARD LANDSCAPES OF ASIA |
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2017 |
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1-46 |
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Snow leopards occur in Asia�s high mountain ranges of the Himalayas, Hindu Kush, Karakoram, Pamir, Tien Shan, Kunlun, Altai and Sayan. In all the 12 countries where they occur, snow leopards face intensifying threats to their survival, including habitat fragmentation and degradation due to increasing human populations, mining and developmental projects, poaching and illegal wildlife trade, weak law enforcement, inadequate involvement of local people in conservation efforts, and depletion of natural prey populations due to hunting by people and overgrazing by livestock.
To address the urgent needs of conservation of the snow leopard and the sustainable development of mountain peoples, the Governments of snow leopard range countries came together and agreed to invest efforts to conserve snow leopards in 23 large landscapes across its range under the Global Snow Leopard Ecosystem Protection Program (GSLEP).
These landscapes where the snow leopards occur are inhabited by agro-pastoral and pastoral peoples who depend on well functioning ecosystems for ecosystem services, i.e., the benefits that humans derive from nature. Many threats that impact snow leopards also impact the well-being of people living in these landscapes. However, till date, there have been no studies that have attempted to quantify peoples� dependence on ecosystem services in snow leopard landscapes, or understand the impacts that alternate land-use decisions such as mining or infrastructure can have on the ecosystem services and on the local people who are dependent on them.
In this report, we provide the first assessment of the economic value of provisioning ecosystem services � the material goods from ecosystems � used by local people in five study sites from four GSLEP landscapes: Spiti Valley and Changtang region of Ladakh in India�s Hemis-Spiti Landscape, Gurez Valley in the Himalayan Landscape of Pakistan, Tost Nature Reserve in the South Gobi Landscape of Mongolia, and the Sarychat region in the Central Tien Shan Landscape of Kyrgyzstan. In study sites that had both pastoral and agro-pastoral communities, we estimated ecosystem services separately for the two production systems.The average value (± SE) of ecosystem services per household amongst the agro-pastoral
communities of Gurez Valley (4125 ± 190 USD/HH/yr) was 2.5 times the average local household income. In the agro-pastoral communities of Spiti Valley (3964 ± 334.8 USD/HH/yr) it was 3.6 times the average local household income, while it was 3.7 times amongst the agro-pastoral communities of Changtang (15083 ± 1656 USD/HH/yr). Amongst the pastoral communities, the value of ecosystem services used by households was several times higher than the average household income: it was 26.1 times amongst the pastoral communities of Changtang (79303 ± 9204 USD HH/yr), 38.7 times among communities in Tost Nature Reserve (150100 ± 13290 USD/HH/yr), and 7.4 times among the pastoral communities of Sarychat (25473 ± 5236 USD/HH/yr). It was lower, although still substantial at 0.6 times, for the downstream agro-pastoral communities living outside the landscape boundary in Sarychat (2094 ± 189 USD/HH/yr).
Our work reveals substantially high levels of dependence of local communities on ecosystem services provided by snow leopard landscapes of Asia. The estimated economic value of provisioning ecosystem services used by human households in these landscapes ranged from 0.6 to up to 40 times the local annual household incomes. This economic support that nature provides people is critical for humanity but remains hidden and unaccounted for. Land use change decisions, especially those that are damaging for nature and biodiversity, must start accounting for the value of ecosystem services in their cost-benefit analyses. |
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1458 |
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Planning Wildlife Conservation in Leh and Kargil Districts of Ladakh, Jammu and Kashmir |
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Establising Snow Leopard Information Management System (SLIMS) at WII Phase 1 – Trans Himalaya |
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1999 |
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Wildlife Institute of India |
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Nature Conservation Division; Department of Forests and Park Services; Ministry of Energy and Natural Resources; Royal Government of Bhutan |
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Snow Leopard Status in Bhutan – National Snow Leopard Survey Report 2022-2023 |
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2023 |
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NSLS Report |
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The National Snow Leopard Survey (NSLS) report 2022-2023 provides an updated status of the snow leopard in Bhutan. The report is an outcome of the camera trapping survey spanning five protected areas namely Jigme Khesar Strict Nature Reserve, Jigme Dorji National Park, Wangchuck Centennial National Park, Bumdeling Wildlife Sanctuary and Jigme Singye Wangchuck National Park and two Divisional Forest Offices of Paro and Thimphu. A total of 310 camera stations were setup across the field sites that accumulated a survey effort of 22,636 trap nights, with over 10,000 images of snow leopards captured. A careful review of 476 images identified 96 adult individuals and 10 cubs across the landscape. Bayesian-based Spatially Explicit Capture Recapture (SECR) modelling estimated 134 snow leopards, as compared to the 2016 baseline of 96 individuals. Snow leopard density was estimated at 1.34 snow leopards per 100 km2 with the possibility of higher density in western Bhutan than in central and eastern Bhutan. Habitat distribution modeling also suggests more suitable habitats in western Bhutan as compared to other regions. |
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1740 |
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Tuyatsatsral, T., Ganbold, B., Ganbat, O., Enkhee, C., Nyambat, N. |
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Buy Sheep Program and Environmental Planning of Herder Communities Assessment Report |
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2009 |
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Mongolia, herder, livestock, compensation, insurance |
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Apparently with the decrease of number of globally endangered snow leopard due to reduction of prey species and loss of habitat, new approaches have been initiated to mitigate conflicts between herders and wildlife, ensuring local participation and building up stakeholders’ responsibility in nature conservation through supporting and guiding of local communities in participation and implementation of collaborative management in sustainable natural resource use. Actually, herder communities, aimed to protect the nature become one of that approaches and made it common consideration, especially in the buffer zones of the Turgen mountain SPA, Tsagaanshuvuut SPA and Gulzat local protected areas of Uvs aimag, where WWF MPO, UNDP and MNET are performing projects, such as “Community based conservation of biodiversity in the mountain landscapes of the Mongolia’s Altai Sayan ecoregion”. Since 2007, in Uvs aimag, particularly in Khaliunbulag bag of Khovd soum, WWF MPO initiated the compensation scheme for herders, aimed to mitigate conflicts between herders and snow leopard, reducing their loss caused by snow leopard and to support them mentally as well.
Current assessment focused on performance evaluation of “Buy sheep” program in Khaliunbulag bag and capability of herder communities , that are established around protected areas, in developing their yearly environmental workplan, including its implementation process. |
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Report is also available in English in this bibliography |
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1097 |
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Maheshwari, A., Takpa, J., Kujur, S., Shawl, T. |
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An Investigation of Carnivore-Human Conflicts in Kargil and Drass Areas of Jammu and Kashmir, India |
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2010 |
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India, snow leopard, Kargil, Drass, Jammu and Kashmir, Department of Wildlife Protection, WWF India |
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Still, there are areas from where very poor information is available on snow leopard and associated species. Keeping this in view, Kargil and Drass areas of Ladakh,Jammu and Kashmir were identified as “gaps” in available information on snow leopard. Kargil has not received much attention for wildlife studies due to its proximity to the International Boundary between India and Pakistan and resultant security implications. The only information available from the area is from a study done by Sathyakumar (2003) on the occurrence of Himalayan brown bear from Zanskar and Suru Valleys in Ladakh. But there was very poor information on the occurrence and distribution of other carnivores and conflicts with humans in Kargil. Therefore, this study was felt necessary to establish the following objectives:
1. Surveys for the occurrence and distribution of snow leopard and other large
carnivores and their prey
2. To estimate abundance of prey species
3. To study food habits of snow leopard and other carnivores based on scat analysis
4. To study the of carnivore – human conflicts
5. To study the socio-economic conditions of rural community and develop local
awareness programme |
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Report submitted to Rufford Small Grant. |
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1093 |
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