18 Autumn 2006 Pallas’ Cat ecology and Conservation in the Semi-desert Steppes of Mongolia James D. Murdoch 1, Tserendorj Munkhzul 2 , and Richard P. Reading 3 T he Pallas’ cat Otocolobus manul is a unique, arid-adapt- ed cat that ranges across the steppes of Central Asia. Known to occur from Tibet in the south to Sibe- ria in the north, the Pallas’ cat inhab- its a wide variety of grassland, semi- desert, and desert habitats (Heptner & Naumov 1992). Despite its range, little is known of the ecology or be- haviour of the species and few details exist on its population and conserva- tion status. The paucity of informa- tion on the species poses considerable challenges to wildlife managers and conservationists in Asia. In 2005, we began a research project to understand basic information on the ecology and conservation of Pallas’ cats in the semi-desert steppes of Mongolia – a region where the status of the species remains largely unknown. Our goals are to quantify the fundamental ecology of the species, identify major threats to its survival, and develop conservation ac- tions for populations in arid regions of Mongolia. Our study site is in the Ikh Nartiin Chuluu Nature Reserve, which is located in the Dalanjargal Soum (county) of the Dornogobi Aimag (prov- ince) in central Mongolia (N45.723º E108.645º). The reserve lies along the eastern edge of the Gobi Desert at the confluence of grassland and semi-desert ecosystems and includes a variety of steppe habitats. The reserve harbours Pallas’ cats and several other carnivores including marbled polecats Vormela peregusna, corsac foxes Vulpes corsac, red foxes Vulpes vulpes, Eurasian badg- ers Meles meles, wolves Canis lupus, and lynx Eurasian Lynx lynx. Our in- vestigations of Pallas’ cats are part of a larger study that examines the ecology of these and other steppe carnivores. To date, we have captured and de- ployed radio transmitters on 4 Pallas’ cats, 1 male and 3 females. Our results at this point, however, remain quite pre- liminary. We captured cats using large wire-mesh box traps and opportunisti- cally by hand – Pallas’ cats are docile and rarely flee far when approached. We fitted each cat with a ~35g VHF radio collar that comprised approximately 1% of body weight. Using locations obtained through radio telemetry, we estimated home range size for 3 cats from January 2005 to June 2005. Preliminary home ranges for these animals were 15.2 and 5.8 km 2 for females and 12.5 km 2 for the male (calculated as 90% fixed kernels – LSCV; ranges based on >35 nightly locations per animal). We captured the fourth cat in May, but require additional locations to generate a range. Although our sample size is small, in the coming months we hope to capture additional cats to evaluate habitat use and activity patterns through sequential tracking. Weekly observations indicate that Pallas’ cats are primarily nocturnal, resting in shallow rock crevices and dens during the day. They typically rest in steep, rocky, semi-desert areas and hunt in open grasslands where the density and diversity of small mammals are highest. We have collected some cat faeces from our study site that will be analyzed in 2006. However, droppings are often difficult to find as the cats bury them. A preliminary analysis of faeces suggests that Pallas’ cats feed mainly on gerbils Meriones spp. and jerboas Dipus sagitta and Allactaga spp. Pallas’ cats also prey on argali sheep Ovis ammon lambs at our site during spring months (Reading et al. 2005). The Pallas’ cat is listed as Near Threatened by the IUCN and under Appendix II in CITES (IUCN - World Conservation Union 2004; UNEP- WCMC 2004). Both listings are in response to a perceived decline of the species throughout its range. The extent of the decline remains unknown and requires quantification to better under- stand the current plight facing this cat. Several factors threaten the survival of Pallas’ cats and other steppe carnivores including loss of habitat, hunting, and illegal trade (Pratt et al. 2004; Reading et al. 1998; United Nations Environ- ment Programme 2001; World Bank Group 2001). In Mongolia, Pallas’ cats are threat- ened mainly by over-hunting and poaching. Despite their near threatened status, Pallas’ cats are legally hunted in Mongolia. The national law governing wildlife stipulates that Pallas’ cats may be hunted for ‘household purposes’, provided that hunters obtain permits from local (soum) governments (Win- gard & Odgerel 2001). The permit sys- tem, however, is largely ineffective and unrealistic as herders in rural areas rare- ly have the resources to travel to soum centres to obtain permits. The law is also ambiguously worded. Permits are valid for up to 5 days, but details on the number of cats that may be harvested per permit are not provided. Similarly, the law does not indicate the number of permits that may be obtained by each household per year or include an ade- quate reporting process. Such ambigui- ties allow wide interpretation that could lead to over-exploitation of the species. In any case, law enforcement through- out most of Mongolia is weak at best. In the Ikh Nartiin Chuluu Nature Reserve, Pallas’ cats are actively hunt- ed. Although all forms of hunting are illegal in the reserve, poaching of cats inside the reserve occurs – indeed, an illegal hunter killed one radio collared cat within reserve boundaries in 2005. To gather information on attitudes to- ward hunting and factors that lead to poaching, we conducted interviews with herders living in the reserve and surrounding areas. Our preliminary re- sults found that Pallas’ cats are hunted mainly for furs that are sold to Chinese traders. Furs sell from US$10 to $15 to traders and are often manufactured into hats and coats for Russian and Chinese markets. Pallas’ cats are also sought for the live trade. In our study area, interna- tional traders pay up to US$100 for live cats that are illegally exported to China. Herders also use Pallas’ cat body parts locally for medicinal purposes. For ex- ample, herders often use the fat of Pal-
CAT News 45 19 las’ cats to sooth and relieve frostbite. The impacts of hunting for household and commercial purposes on Pallas’ cat populations remains unknown. Disease may also pose a risk to Pal- las’ cats in our study area. Studies in central Mongolia indicate that toxoplas- mosis occurs in free-ranging Pallas’ cats and may contribute to declines (Brown et al. 2002). Disease exposure among Pallas’ cats in the drier Ikh Nartiin Chu- luu Nature Reserve is not known. How- ever, feral cats range across much of the reserve and have been observed during spotlight surveys and captured in traps. Feral cats may act as vectors for a vari- ety of diseases such as toxoplasmosis. Pallas’ cat conservation in the semi- desert steppes of Mongolia requires several actions. Among the most impor- tant include: 1. Improving law enforcement efforts, especially in protected areas, to con- trol trade and limit poaching. In most of Mongolia, including many pro- tected areas, rangers and nature offic- ers from local administrative centres are tasked with law enforcement. Yet, they generally lack the equipment, training, and funding to adequately enforce wildlife laws. The Mongo- lian government and international or- ganizations desperately need to fund, train, and recruit more wildlife rang- ers to strengthen enforcement efforts. 2. Revamping the hunting permit sys- tem. In rural Mongolia, the permit system is ineffective and not en- forced. A more realistic system that is acceptable to local people must be de- veloped and implemented to regulate hunting of the species. 3. Establishing monitoring programs for Pallas cats’ and other carnivores. Information on population trends is important for evaluating the status of the species, assessing the impact of threats, and calculating harvest rates. In addition, the monitoring program should strive to assess harvest rates for all fur bearers such as corsac fox- es, red foxes, and badgers. Currently, no such monitoring program exists. Scientific research is also needed to un- derstand and better manage Pallas’ cats, not only in Mongolia, but across Central Asia. More information, for example, is needed on the spatial and habitat re- quirements of Pallas’ cats across much of their range from the steppes of Mon- golia and China to Siberia. Behavioural research is also needed to understand the basic social organization of the spe- cies. For more information on our project and Pallas’ cats in the Ikh Nartiin Chu- luu Nature Reserve, please visit our website at: http://www.wildcru.org/ links/mongolia/mongolia.htm. Acknowledgements Our research is supported by the Denver Zoological Foundation, Rufford Founda- tion, Trust for Mutual Understanding, and Small Cat Conservation Alliance. We thank Claudio Sillero-Zubiri and Jim Sanderson for reviewing this article. References Brown M., Lappin M. R., Brown J. L., Munkhtsog B. M. and Swanson W. F. 2002. Exploring the ecologic basis for extreme susceptibility of Pallas’ cats to fatal toxoplasmosis: Comparisons of wild and captive populations. Proceed- ings of the American Association of Zoo Veterinarians:12-15. Heptner V. G. and Naumov N. P. (eds). 1992. Mammals of the Soviet Union. E.J. Brill, New York. IUCN - World Conservation Union. 2004. The 2004 IUCN Red List of Threatened Species. IUCN World Conservation Un- ion, Gland, Switzerland. Pratt D. G., Macmillan D. C. and Gordon I. J. 2004. Local community attitudes to wildlife utilisation in the changing eco- nomic and social context of Mongolia. Biodiversity and Conservation 13, 591- 613. Reading R. P., Amgalanbaatar S., Wingard G. J., Kenny D. and DeNicola A. 2005. Ecology of Argali in Ikh Nartiin Chuluu, Dornogobi Aymag. Erforsch. Biol. Ress. Mongolei (Halle/Saale) 9, 77-89. Reading R. P., Mix H., Lhagvasuren B. and Tseveenmyadag N. 1998. The commer- cial harvest of wildlife in Dornod Aimag, Mongolia. Journal of Wildlife Manage- ment 62, 59-71. United Nations Environment Programme- WCMC. 2004. Checklist of CITES Spe- cies. Convention on International Trade of Endangered Species. United Nations Environment Programme. 2001. Mongolia: State of the Environ- ment 2002, Ulaanbaatar, Mongolia. Wingard J. R. and Odgerel P. 2001. Com- pendium of environmental law and prac- tice in Mongolia. GTZ, Ulaanbaatar, Mongolia. World Bank Group. 2001. Mongolia Envi- ronment Monitor, Ulaanbaatar, Mongo- lia. 1 Wildlife Conservation Research Unit, Uni- versity of Oxford, Tubney House, Abingdon Road, Tubney OX13 5QL, UK <james.murdoch@zoo.ox.ac.uk> 2 Institute of Biology, Mammalogy Labora- tory, Mongolian Academy of Sciences, Jukov Avenue, Ulaanbaatar-51, Mongolia 3 Department of Conservation Biology, Denver Zoological Foundation, 2300 Steele Street, Denver, Colorado 80205, USA Pallas’ cat in the Ikh Nartiin Chuluu Nature Reserve, Dornogobi, Mongolia. Pallas’ cats of- ten use rock crevices for shelter and protection from predators during the day (Photo: R. P. Reading).
Pallas’ Cat ecology and Conservation in the Semi-desert Steppes
of Mongolia
James D. Murdoch1, Tserendorj Munkhzul2, and Richard P. Reading3
T
he Pallas’ cat Otocolobus
manul is a unique, arid-adapted cat that ranges across the
steppes of Central Asia. Known to
occur from Tibet in the south to Siberia in the north, the Pallas’ cat inhabits a wide variety of grassland, semidesert, and desert habitats (Heptner
& Naumov 1992). Despite its range,
little is known of the ecology or behaviour of the species and few details
exist on its population and conservation status. The paucity of information on the species poses considerable
challenges to wildlife managers and
conservationists in Asia.
In 2005, we began a research project
to understand basic information on the
ecology and conservation of Pallas’ cats
in the semi-desert steppes of Mongolia
– a region where the status of the species
remains largely unknown. Our goals are
to quantify the fundamental ecology of
the species, identify major threats to its
survival, and develop conservation actions for populations in arid regions of
Mongolia. Our study site is in the Ikh
Nartiin Chuluu Nature Reserve, which
is located in the Dalanjargal Soum
(county) of the Dornogobi Aimag (province) in central Mongolia (N45.723º
E108.645º). The reserve lies along the
eastern edge of the Gobi Desert at the
confluence of grassland and semi-desert
ecosystems and includes a variety of
steppe habitats. The reserve harbours
Pallas’ cats and several other carnivores
including marbled polecats Vormela
peregusna, corsac foxes Vulpes corsac,
red foxes Vulpes vulpes, Eurasian badgers Meles meles, wolves Canis lupus,
and lynx Eurasian Lynx lynx. Our investigations of Pallas’ cats are part of a
larger study that examines the ecology
of these and other steppe carnivores.
To date, we have captured and deployed radio transmitters on 4 Pallas’
cats, 1 male and 3 females. Our results
at this point, however, remain quite preliminary. We captured cats using large
wire-mesh box traps and opportunisti-
18
cally by hand – Pallas’ cats are docile
and rarely flee far when approached. We
fitted each cat with a ~35g VHF radio
collar that comprised approximately 1%
of body weight. Using locations obtained
through radio telemetry, we estimated
home range size for 3 cats from January
2005 to June 2005. Preliminary home
ranges for these animals were 15.2 and
5.8 km2 for females and 12.5 km2 for the
male (calculated as 90% fixed kernels
– LSCV; ranges based on >35 nightly
locations per animal). We captured the
fourth cat in May, but require additional
locations to generate a range. Although
our sample size is small, in the coming
months we hope to capture additional
cats to evaluate habitat use and activity
patterns through sequential tracking.
Weekly observations indicate that
Pallas’ cats are primarily nocturnal,
resting in shallow rock crevices and
dens during the day. They typically
rest in steep, rocky, semi-desert areas
and hunt in open grasslands where the
density and diversity of small mammals
are highest. We have collected some cat
faeces from our study site that will be
analyzed in 2006. However, droppings
are often difficult to find as the cats bury
them. A preliminary analysis of faeces
suggests that Pallas’ cats feed mainly on
gerbils Meriones spp. and jerboas Dipus
sagitta and Allactaga spp. Pallas’ cats
also prey on argali sheep Ovis ammon
lambs at our site during spring months
(Reading et al. 2005).
The Pallas’ cat is listed as Near
Threatened by the IUCN and under
Appendix II in CITES (IUCN - World
Conservation Union 2004; UNEPWCMC 2004). Both listings are in
response to a perceived decline of the
species throughout its range. The extent
of the decline remains unknown and
requires quantification to better understand the current plight facing this cat.
Several factors threaten the survival of
Pallas’ cats and other steppe carnivores
including loss of habitat, hunting, and
illegal trade (Pratt et al. 2004; Reading
et al. 1998; United Nations Environ-
ment Programme 2001; World Bank
Group 2001).
In Mongolia, Pallas’ cats are threatened mainly by over-hunting and
poaching. Despite their near threatened
status, Pallas’ cats are legally hunted in
Mongolia. The national law governing
wildlife stipulates that Pallas’ cats may
be hunted for ‘household purposes’,
provided that hunters obtain permits
from local (soum) governments (Wingard & Odgerel 2001). The permit system, however, is largely ineffective and
unrealistic as herders in rural areas rarely have the resources to travel to soum
centres to obtain permits. The law is
also ambiguously worded. Permits are
valid for up to 5 days, but details on the
number of cats that may be harvested
per permit are not provided. Similarly,
the law does not indicate the number of
permits that may be obtained by each
household per year or include an adequate reporting process. Such ambiguities allow wide interpretation that could
lead to over-exploitation of the species.
In any case, law enforcement throughout most of Mongolia is weak at best.
In the Ikh Nartiin Chuluu Nature
Reserve, Pallas’ cats are actively hunted. Although all forms of hunting are
illegal in the reserve, poaching of cats
inside the reserve occurs – indeed, an
illegal hunter killed one radio collared
cat within reserve boundaries in 2005.
To gather information on attitudes toward hunting and factors that lead to
poaching, we conducted interviews
with herders living in the reserve and
surrounding areas. Our preliminary results found that Pallas’ cats are hunted
mainly for furs that are sold to Chinese
traders. Furs sell from US$10 to $15 to
traders and are often manufactured into
hats and coats for Russian and Chinese
markets. Pallas’ cats are also sought for
the live trade. In our study area, international traders pay up to US$100 for live
cats that are illegally exported to China.
Herders also use Pallas’ cat body parts
locally for medicinal purposes. For example, herders often use the fat of Pal-
Autumn 2006
las’ cats to sooth and relieve frostbite.
The impacts of hunting for household
and commercial purposes on Pallas’ cat
populations remains unknown.
Disease may also pose a risk to Pallas’ cats in our study area. Studies in
central Mongolia indicate that toxoplasmosis occurs in free-ranging Pallas’ cats
and may contribute to declines (Brown
et al. 2002). Disease exposure among
Pallas’ cats in the drier Ikh Nartiin Chuluu Nature Reserve is not known. However, feral cats range across much of the
reserve and have been observed during
spotlight surveys and captured in traps.
Feral cats may act as vectors for a variety of diseases such as toxoplasmosis.
Pallas’ cat conservation in the semidesert steppes of Mongolia requires
several actions. Among the most important include:
1. Improving law enforcement efforts,
especially in protected areas, to control trade and limit poaching. In most
of Mongolia, including many protected areas, rangers and nature officers from local administrative centres
are tasked with law enforcement. Yet,
they generally lack the equipment,
training, and funding to adequately
enforce wildlife laws. The Mongolian government and international organizations desperately need to fund,
train, and recruit more wildlife rangers to strengthen enforcement efforts.
2. Revamping the hunting permit system. In rural Mongolia, the permit
system is ineffective and not enforced. A more realistic system that is
acceptable to local people must be developed and implemented to regulate
hunting of the species.
3. Establishing monitoring programs
for Pallas cats’ and other carnivores.
Information on population trends is
important for evaluating the status of
the species, assessing the impact of
threats, and calculating harvest rates.
In addition, the monitoring program
should strive to assess harvest rates
for all fur bearers such as corsac foxes, red foxes, and badgers. Currently,
no such monitoring program exists.
Scientific research is also needed to understand and better manage Pallas’ cats,
not only in Mongolia, but across Central
Asia. More information, for example,
is needed on the spatial and habitat requirements of Pallas’ cats across much
CAT News 45
Pallas’ cat in the Ikh Nartiin Chuluu Nature Reserve, Dornogobi, Mongolia. Pallas’ cats often use rock crevices for shelter and protection from predators during the day (Photo: R. P.
Reading).
of their range from the steppes of Mongolia and China to Siberia. Behavioural
research is also needed to understand
the basic social organization of the species.
For more information on our project
and Pallas’ cats in the Ikh Nartiin Chuluu Nature Reserve, please visit our
website at: http://www.wildcru.org/
links/mongolia/mongolia.htm.
Acknowledgements
Our research is supported by the Denver
Zoological Foundation, Rufford Foundation, Trust for Mutual Understanding, and
Small Cat Conservation Alliance. We thank
Claudio Sillero-Zubiri and Jim Sanderson
for reviewing this article.
References
Brown M., Lappin M. R., Brown J. L.,
Munkhtsog B. M. and Swanson W. F.
2002. Exploring the ecologic basis for
extreme susceptibility of Pallas’ cats to
fatal toxoplasmosis: Comparisons of
wild and captive populations. Proceedings of the American Association of Zoo
Veterinarians:12-15.
Heptner V. G. and Naumov N. P. (eds). 1992.
Mammals of the Soviet Union. E.J. Brill,
New York.
IUCN - World Conservation Union. 2004.
The 2004 IUCN Red List of Threatened
Species. IUCN World Conservation Union, Gland, Switzerland.
Pratt D. G., Macmillan D. C. and Gordon
I. J. 2004. Local community attitudes to
wildlife utilisation in the changing economic and social context of Mongolia.
Biodiversity and Conservation 13, 591613.
Reading R. P., Amgalanbaatar S., Wingard
G. J., Kenny D. and DeNicola A. 2005.
Ecology of Argali in Ikh Nartiin Chuluu,
Dornogobi Aymag. Erforsch. Biol. Ress.
Mongolei (Halle/Saale) 9, 77-89.
Reading R. P., Mix H., Lhagvasuren B. and
Tseveenmyadag N. 1998. The commercial harvest of wildlife in Dornod Aimag,
Mongolia. Journal of Wildlife Management 62, 59-71.
United Nations Environment ProgrammeWCMC. 2004. Checklist of CITES Species. Convention on International Trade
of Endangered Species.
United Nations Environment Programme.
2001. Mongolia: State of the Environment 2002, Ulaanbaatar, Mongolia.
Wingard J. R. and Odgerel P. 2001. Compendium of environmental law and practice in Mongolia. GTZ, Ulaanbaatar,
Mongolia.
World Bank Group. 2001. Mongolia Environment Monitor, Ulaanbaatar, Mongolia.
1
Wildlife Conservation Research Unit, University of Oxford, Tubney House, Abingdon
Road, Tubney OX13 5QL, UK
<james.murdoch@zoo.ox.ac.uk>
2
Institute of Biology, Mammalogy Laboratory, Mongolian Academy of Sciences, Jukov
Avenue, Ulaanbaatar-51, Mongolia
3 Department of Conservation Biology, Denver
Zoological Foundation, 2300 Steele Street,
Denver, Colorado 80205, USA
19
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Competition often occurs between sympatric species that exploit similar ecological niches. Among canids, competition may be reduced by partitioning resources such as food, time, and habitat, but the mechanisms of coexistence remain poorly understood, particularly among fox species. We described the food habits of two foxes that live sympatrically across northern and central Asia, the corsac fox (Vulpes corsac) and red fox (V. vulpes), by analyzing scats collected during a field study in Mongolia. We analyzed 829 corsac and 995 red fox scats collected from April 2005 to August 2007 and tested the extent to which food partitioning occurred. The diets of both species consisted mainly of insects followed by rodents, but also included birds, reptiles, large mammal remains (carrion), plant material (including fruits and seeds), and garbage. Despite high overlap in the proportion of food items consumed, differences existed between species in overall diet with corsacs more frequently consuming beetles, but proportionally fewer crickets and large mammal remains than red foxes. We detected interspecific differences during the pup rearing and dispersal seasons, when prey was abundant, but not during the breeding season, when prey was scarce and diet overlap highest. Each species' diet also differed seasonally and exhibited moderate overall breadth. Corsacs consumed proportionally more beetles and rodents during pup rearing and crickets during dispersal relative to other seasons, whereas red foxes consumed proportionally more crickets during pup rearing and dispersal and more rodents and large mammals during pup rearing and breeding relative to other seasons. Our results suggest that partitioning of food resources during most of the year facilitates coexistence, and that the potential for competition is highest during winter months.
The toad headed agama (Phrynocephalus versicolor) ranges across the arid steppe regions of southern and western Mongolia and represents one of the most common reptiles in the country. However, few details of the species' population characteristics exist, which may be important for evaluating population trends and assessing its conservation status. We estimated toad headed agama density in Ikh Nart Nature Reserve, Mongolia based on surveys conducted in the summers (Jun-Sep) of 2005, 2006, 2008, and 2009. We conducted surveys in three steppe habitats including tall grassland (n = 7), shrub-steppe (n = 7), and semi-shrub steppe (n = 8), and calculated density using Distance methods. Mean density across all surveys was 66 agamas/ha (95 % C.I. = 48-92; range: 24/ha to 112/ha). Agamas occurred in highest density in shrub-steppe and lowest in semi-shrub across years. Density was similar between shrub-steppe and tall grassland. However, density in these habitats was significantly higher than in semi-shrub steppe. Our results provide baseline estimates of toad headed agama density, and indicate that agamas are capable of reaching higher density than previously recorded. Our results also suggest that agamas benefit from the cover afforded by more structurally complex vegetation communities like those found in shrub-steppe and tall grassland habitats.
Red (Vulpes vulpes) and corsac foxes (V. corsac) live sympatrically throughout most of Mongolia, but few details of their home range characteristics exist. We captured and radio-tagged 13 red fox (♂ = 5, ♀ = 8) and 15 corsac foxes (♂ = 8, ♀ = 7) between 2004 and 2008. We tracked their movements to estimate home range sizes and examined the effects of four factors on home range size, including sex, age, season, and year. We determined mean home range size for 12 red and 10 corsac foxes that had suffi cient data using fi xed kernel methods. Mean home range size (90 % kernel) was 15.4 ± 2.2 SE km 2 for red foxes and 4.5 ± 0.8 SE km 2 for corsac foxes. Core areas within home ranges (50 % kernels) averaged 3.59 ± 0.68 km 2 for red foxes and 1.43 ± 0.32 km 2 for corsac foxes. Home ranges varied by sex, age, season, and year for both species and we found signifi cant effects of sex among corsacs, with males occupying larger ranges than females; age among red foxes, with adults occupying larger ranges than yearlings; and year among red fox home ranges. We believe that resource availability probably infl uenced patterns of home range variability along with the signifi cant variables we found. Our results provide among the fi rst quantitative estimates of red and corsac fox home range size in Mongolia and a baseline for developing management and conservation actions.
We studied the nesting ecology and movement patterns of Eurasian black vultures (Aegypius monachus) nesting in and near Ikh Nart Nature Reserve, Dornogobi Aimag, Mongolia. From 2003 till 2009, we monitored nesting pairs from incubation to fledging and compared nesting success for pairs nesting on rocks and trees. We captured chicks just prior to fledging to apply leg bands and wing tags. We also captured adults in June and attached solar-powered global positioning system (GPS)/satellite telemetry units, leg bands, and wing tags. We collected re-sighting data on marked birds opportunistically and telemetry data on tagged birds. We moni-tored 363 nesting pairs from 2003 to 2009. Most nesting failures occurred during the ~ 55 day incubation period. Overall, 50.9 % of nesting pairs raised a chick to fledgling. Nesting substrate (i.e., rock or tree) did not influence nesting success. Between 2006 and 2009 we received re-ports of sightings for 21 individual birds and on 37 occasions (n = ...
In arid regions of the developing world, pastoralists and livestock commonly inhabit protected areas, resulting in human–wildlife conflict. Conflict is inextricably linked to the ecological processes shaping relationships between pastoralists and native herbivores and carnivores. To elucidate relationships underpinning human–wildlife conflict, we synthesized 15 years of ecological and ethnographic data from Ikh Nart Nature Reserve in Mongolia's Gobi steppe. The density of argali (Ovis ammon), the world's largest wild sheep, at Ikh Nart was among the highest in Mongolia, yet livestock were >90% of ungulate biomass and dogs >90% of large-carnivore biomass. For argali, pastoral activities decreased food availability, increased mortality from dog predation, and potentially increased disease risk. Isotope analyses indicated that livestock accounted for >50% of the diet of the majority of gray wolves (Canis lupus) and up to 90% of diet in 25% of sampled wolves (n = 8). Livestock composed at least 96% of ungulate prey in the single wolf pack for which we collected species-specific prey data. Interviews with pastoralists indicated that wolves annually killed 1–4% of Ikh Nart's livestock, and pastoralists killed wolves in retribution. Pastoralists reduced wolf survival by killing them, but their livestock were an abundant food source for wolves. Consequently, wolf density appeared to be largely decoupled from argali density, and pastoralists had indirect effects on argali that could be negative if pastoralists increased wolf density (apparent competition) or positive if pastoralists decreased wolf predation (apparent facilitation). Ikh Nart's argali population was stable despite these threats, but livestock are increasingly dominant numerically and functionally relative to argali. To support both native wildlife and pastoral livelihoods, we suggest training dogs to not kill argali, community insurance against livestock losses to wolves, reintroducing key native prey species to hotspots of human–wolf conflict, and developing incentives for pastoralists to reduce livestock density. Efectos Negativos y Positivos del Pastoreo de Ganado sobre la Fauna Silvestre Poco Común en el Desierto del Gobi Resumen: En las regiones´ aridas de los países en desarrollo, los pastores y el ganado comúnmente habitanáreas protegidas, lo que resulta en conflictos entre humanos y la vida silvestre. El conflicto está conectado inextricablemente con los procesos ecológicos que forman las relaciones entre el pastoreo del ganado y los herbívoros nativos y los carnívoros. Para elucidar las relaciones que apoyan el conflicto humano-vida silvestre sintetizamos 15 años de datos ecológicos y etnográficos de la Reserva Natural Ikh Nart en la estepa del Gobi
A significant portion of the manul’s Otocolobus manul global range is situated in the Central Asian countries Mongolia, Kazakhstan, Kyrgyzstan, Uzbekistan, and
Tajikistan, and several adjacent provinces of Russia. We estimated the manul current Extent of Occurrence EOO in the region at 1,225,313 km2, which is about 84%
of the predicted area of suitability calculated from the MaxEnt distribution model.
Based on a conservative assessment of manul population density (4–8 cats/100 km2), we roughly estimated the regional population size at 49,000–98,000 manuls. Mongolia holds almost 60% of the estimated potential area of suitability in the region and over
50% of the estimated regional population. Kazakhstan and Russia both have relatively abundant manul populations while in Uzbekistan and Tajikistan the manul presence remains questionable. Killing by herding dogs, wildfires, and rodents poisoning are at present the main threats to the manul in this region. Manul is listed in the Red Data Books of Russia, Kazakhstan and Kyrgyzstan. Hunting ban or regulation, respectively, and protected areas are currently the main conservation instruments for the species.
Protected areas cover approximately 15% of the manul habitats in Mongolia, 12% in Russia, 7% in Kazakhstan, and 6% in Kyrgyzstan. We recognise a lack of knowledge
regarding manul ecology and biology in the region, its geographical distribution, and a lack of correct assessment of its population size. These gaps should be filled to raise conservation efficiency. Conservation efforts should include securing manul and its habitats in key areas, minimising dog attacks and poaching, and establishing a broad, long-term monitoring.
The extensive Mongolian grasslands hosts a high variety of micro-habitats which wildlife uses as corridors that enable species to expand their range. Between May 2017 and March 2018, we conducted an intensive survey in the Mongolian-Manchurian Grassland Ecoregion using camera trapping, field transects, live trapping and opportunistic observations, in mountain outcrops, grass steppe and sand dune habitats across seasons. Our aim was to compile the first satisfactory inventory of mammals based on scientific methods for a diverse landscape in the Mongolian provinces of Tov and Dundgovi. Furthermore, our research seeks to fill in knowledge gaps on species distribution and range expansions in the endangered west Mongolian-Manchurian Grassland ecoregion and identify biodiversity hotspot areas encompassed in this biogeographic crossroad. We recorded 31 species of non-volant mammals, including a globally Endangered species and two Near Threatened species, according to the IUCN Red List, and...
The Daurian hedgehog ranges across northern Mongolia, southern Siberia, and northern China. However, few details of the species' behavior, ecology, or distribution are known. We conducted a pilot study of the ranging behavior and diet of Daurian hedgehogs in Ikh Nart Nature Reserve, Mongolia. We captured and radio-tagged eight hedgehogs (six males/two females) between June and September 2006. We tracked their movements until hibernation to estimate home range sizes and daytime nest characteristics. We also analyzed scats (N = 38) to gain a preliminary understanding of the food habits of the species. During the study, we collected 237 hedgehog locations, including 91 night, 141 day, and fi ve hibernation sites. Hedgehogs were followed a mean of 53.43 ± 4.35 SE days from capture before entering hibernation. Mean home range size for seven hedgehogs was 422.72 ± 94.07 SE ha. Daytime nest sites had one, rarely two entrances, and usually occurred in rocky outcrops or at the base of sh...
Understanding the factors infl uencing survival of ungulate neonates facilitates successful management programs, particularly as they relate to population dynamics and adaptive species management. However, kid survival of near threatened Siberian ibex (Capra sibirica) remains poorly understood. During 2005-2013, we captured and collared 21 ibex kids in Ikh Nart Nature Reserve in southeastern Mongolia, to monitor their survival and cause-specifi c mortality. We found no diff erences in morphometric measurements between male and female kids, except body mass being males weighing more than females. A total of 11 mortalities were documented and predations by red foxes (n=5, Vulpes vulpes) and grey wolf (n=1, Canis lupus) was the leading cause of the mortalities. Known fate models indicate the monthly survival of kids best explained by body mass and fi rst month of life (April-May + weight). Monthly survival estimates ranged from 0.077 (95% CI = 0.60-0.88) in April-May to 0.97 (95% CI = 0.90-0.99) in June-March, with an annual survival rate of 0.45 (95% CI = 0.24-0.68). We found little support for the hypotheses that body mass or birth date infl uenced survival; however, our small sample size limited the power of the analyses. Overall, our results indicated that predation and other factors led to high kid mortality during the period shortly after birth. Otgonbayar, B. , Buyandelger, S., Amgalanbaatar, S. & Reading, R. P. 2017. Siberian ibex (Capra sibirica) neonatal kid survival and morphometric measurements in Ikh Nart Nature Reserve, Mongolia. Mong. J. Biol. Sci., 15(1-2): 23-30.
The disruption of animal movements is known to affect wildlife populations, particularly large bodied, free-ranging mammals that require large geographic ranges to survive. Corridors commonly connect fragmented wildlife populations and their habitats, yet identifying corridors rarely uses data on habitat selection and movements of target species. New technologies and analytical tools make it possible to better integrate landscape patterns with spatial behavioral data. We show how resource selection functions can describe habitat suitability using continuous and multivariate metrics to determine potential wildlife movement corridors. During 2005–2010, we studied movements of argali sheep (Ovis ammon) near the Mongolia-Russia border using radio-telemetry and modeled their spatial distribution in relation to landscape features to create a spatially explicit habitat suitability surface to identify potential transboundary conservation corridors. Argali sheep habitat selection in western ...