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ISSN 1027-2992
IUCN
The World Conservation Union
CAT
news
N° 54 | SPRING 2011
CATnews 54 Spring 2011
02
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CATnews 54 Spring 2011
ANNA BARASHKOVA1 AND ILYA SMELANSKY1
Pallas’s cat in the Altai
Republic, Russia
Pallas’s cat Otocolobus manul is a small wild cat occurring in Russia at the north-
ern periphery of its global range. The results of Pallas’s cat surveys conducted in
the Altai Mountain area are presented in this paper. Before the 2000s, there was no
special research undertaken on Pallas’s cat population numbers and distribution in
the Altai part of its range, except for the gathering of interview data in the late 1990s.
This study carried out snow-tracking and obtained survey data on the species from
2006 to 2009 in the Altai Republic, one of the core habitats for Pallas’s cat in Rus-
sia. Pallas’s cat density reaches 1.20-2.18 individuals per 10 km2 in the main Pallas’s
cat habitats. A total of 480-650 Pallas’s cats were estimated to live within the Altai
Republic. The areas of high conservation value for Pallas’s cat are situated on the
Sailughem and Kurai ridges. The main threats to the species are poaching and killing
by dogs. It is necessary to estimate the threats from possible human activity, such as
mining. It is presumed that educational work with local people will reduce deaths
amongst Pallas’s cats. The creation of new protected areas within the key habitat of
Pallas’s cat in the Altai Republic, including the enlargement of the recently created
national park on Sailughem ridge, is very encouraging.
The Pallas’s cat is a rare small wild cat pre-
sently listed in the IUCN Red Data List as
Near Threatened (Ross et al. 2008). Pallas’s
cat is listed as “a rare species on the peri-
phery of its range” in the Red Data Book of
the Russian Federation (Dronova 2001). On
the northern edge of its geographic range in
Russia, Pallas’s cat is found along the borders
with Mongolia and China mainly in the Altai,
Tyva and Buryatia Republics and in Zabaikals-
ky Region. The southeastern part of the Altai
Republic (Kosh-Agach District) is one of the
original contribution
important areas for Pallas’s cat in Russia as
its population density here is relatively high
(Heptner & Sludski 1992, Dronova 2001).
The Altai Mountains Ecoregion is included
in the WWF Global 200 and contains The
Golden Mountains of Altai UNESCO World
Natural Heritage Site. Pallas’s cat is listed in
the regional Red Data Book of the Altai Re-
public as a species with declining numbers
(Chassovskikh 2007). However, prior to 2000,
no work was done on Pallas’s cat in the Altai
Mountains. Before being listed in the natio-
nal Red Data Book of Russia, Pallas’s cat was
hunted for its skin. At that time, the local
game department was purported to conduct
regular snow-tracking surveys to evaluate the
cat’s resources, whereas, in fact, the surveys
were often on paper only and their results
were not published. Only in the late 1990s did
specialists from the Wildlife Agency (Mos-
cow) conduct interviews. They estimated that
the Pallas’s cat population numbered bet-
ween 200 and 300 animals (Dronova 2001).
The present study aimed to obtain up-to-date
data on Pallas’s cat population numbers and
distribution in the Altai Republic of Russia
and to identify threats to the species in the
area investigated.
Study area
The study sites are situated in the Kosh-
Agach District of the Altai Republic where
Pallas’s cat occurs in three relatively separate
areas. The largest area includes the Chuia
intermountain depression (Chuia Steppe) and
surrounding mountain slopes (of the Kurai,
Sailughem, South Chuisky, North Chuisky,
Chikhachev’s ridges and Talduair Massif).
Two smaller and more remote areas are the
Kurai intermountain depression (Kurai Step-
pe) and the Ukok Plateau (Fig. 1). The distri-
bution of the Pallas’s cat is clearly limited by
snow depth as well as by prey density and
availability. The main prey items are different
species of pika (Ochotona sp.) (Heptner &
Sludski 1992, Kiriliuk 1999).
The sites we investigated are the main are-
as where Pallas’s cat is known in the Altai
Mountains. All the sites are located at ele-
vations between 1,800 m and 2,500 m. The
slopes of the Kurai ridge differ from the site
on the Sailughem ridge by having steeper slo-
pes and deeper snow cover. On average, the
Kurai ridge has less arid steppe vegetation
than Sailughem ridge.
Methods
Information on Pallas’s cat numbers and dis-
tribution was collected by snow-tracking and
conducting interviews from 2006 to 2009.
The snow-tracking we used is the standard
method adopted by the State Wildlife Agency
in Russia. Density estimation was calculated
according to Formozov (1932) with correction
factor by Malyshev & Pereleshin (Glushkov et
al. 2007):
S=n/(L x d)
where: S = density (individuals per 1 km2),
n = number of tracks crossed,
L = length (km) of route surveyed,Fig. 1. Study site and survey results in the Russian Altai Republic.
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CATnews 54 Spring 2011
Pallas’s cat in the Altai Republic, Russia
d = average distance (km) covered by indivi-
dual per day.
As a rule, the value of d is specific for every
species and habitat composition. It is taken
from direct tracking of daily movement and
for most game mammals in Russia was de-
termined several decades ago. Only a few
investigations have been made more recently
for Pallas’s cat (Kiriliuk 1988; our own data).
According to these studies, we assume that
Pallas’s cat daily movement is approximately
1.5-2 km. This value was used for estimating
the population density.
The total length of routes surveyed was ap-
proximately 210 km, this being travelled by
2-3 groups of fieldworkers. Two survey plots
were identified in December 2006 and 2009:
(1) the Sailughem ridge (Ulandryk River valley
with tributaries and the Buraty River valley
– total route length is 105.7 km); and (2) the
Kurai ridge (southern slopes from Yanterek to
Kokorya valley – total route length is 62.3 km).
Other survey routes were put on the Chuia
Steppe (32.3 km), and along the foot of the
Talduair Massif (9.7 km) – a separate moun-
tain massif to the southeast from the Kurai
ridge. The survey routes traversed typical ha-
bitat of Pallas’s cat (ie. screes, rocks, ravines
and pika colonies at the foot of mountains),
as well as less appropriate areas, in order to
fully represent the habitat range. All Pallas’s
cat tracks encountered on the survey route
were counted and their number was used for
the calculation according to Formozov’s for-
mula (see above).
The interview data were obtained from 48
winter and summer livestock-herding camps
during snow-tracking research and also dur-
ing field trips in April and July 2009. Addi-
tional data on Pallas’s cat occurrence was
taken from our data base compiled from
2004 (results of interviewing hunters, ran-
gers, tourists, students and other people who
visited or worked in the area; a total of 17
respondents and 40 reports on Pallas’s cat).
Interview data were used for determining the
boundaries of Pallas’s cat distribution and for
understanding actual threats to the species.
The total area that Pallas’s cat inhabits
within the Altai Mountains was estimated
using spatial analyses of remote sensing
data (Landsat TM, ETM), a digital elevation
model and a landscape map of the Altai re-
gion. Three main types of habitat were di-
stinguished, namely: well-suited to Pallas’s
cat, moderately-suited and unsuited habitats.
This habitat assessment was conducted ba-
sed on the following assumptions: (1) snow
cover is a limiting factor – in suitable habitat
the snow should not be deeper than 20 cm,
or some patches should be free of snow all
winter; (2) the spatial distribution of Pallas’s
cat in the area has an altitudinal limit of 2,600
m, probably because the permafrost line and
steppe/tundra border occur at this height; (3)
the landscape types under investigation are
representative of the whole of the Pallas’s
cat’s range in the Altai Republic. Data were
treated using GIS methods (ie. Spatial Ana-
lyst, ArcView 3.2, ArcGIS 9.3, ESRI, USA).
Results and discussion
Pallas’s cat numbers and distribution
No Pallas’s cat tracks were crossed on the
Chuia Steppe and on the basis of survey data
we assumed that Pallas’s cats only occasio-
nally disperse into this area. Thus we estima-
ted Pallas’s cat number only on two survey
sites: (1) Sailughem ridge site and (2) Kurai
ridge site united with the closely situated
and similar Talduair Massif. On average, the
density of Pallas’s cat tracks was 1.86 tracks
per 10 km. The figure for the Sailughem site
was 1.4 times higher than for the Kurai site
(2.08 and 1.53 tracks per 10 km, respectively).
Taking into account that the daily distance
moved by Pallas’s cat is approximately 1.5-2
km (see above), the Pallas’s cat population
density in the Sailughem ridge was estima-
ted as 1.63-2.18 individuals per 10 km2 and
in the Kurai ridge as 1.20-1.60 individuals
per 10 km2 (Table 1). Considering the pro-
Fig. 2. Pallas’s cat habitats in the main part of the species’ range in the Altai Republic.
Fig. 3. Pallas’s cat in the Bar-Burgazy valley (Photo I. Rozhkov).
05
CATnews 54 Spring 2011
portion of similar habitats in the main part
of the Pallas’s cat range (Fig. 2) in the Altai
Mountains (Chuia Steppe and surrounding
mountain slopes), it is estimated that the to-
tal population in this area of about 3,000 km2
is 420-560 individuals. It is considered that
no more than 10-20 Pallas’s cats occur in
the Kurai Steppe, while no more than 50-70
Pallas’s cats are found on the Ukok Plateau.
In total, therefore, the Pallas’s cat population
in the Russian part of Altai is estimated to be
around 480-650 individuals.
Some differences in habitat use were found
within the Sailughem ridge. Pallas’s cat was
found to occur here almost three times more
often in valleys/ravines with steep slopes
(ie. greater than 40 degrees) than in those
valleys with gentle slopes (ie. from 5 to 30
degrees). Pallas’s cat was never found in flat
steppe habitats (Naidenko et al. 2007). This
finding, however, did not apply to the Kurai
ridge. Most likely, this is because of the very
deep snow experienced during 2009-2010
(up to 30-40 cm) when Pallas’s cats probab-
ly moved to almost snowless, steep-sloped
areas featuring outcrops, rocks and stones.
Pallas’s cat tracks were not recorded in re-
latively flat and snowy places, even if pika
colonies were present.
Information from the interviews
Only four herders interviewed were com-
pletely unfamiliar with Pallas’s cat. 35 out of
48 respondents reported that they had perso-
nally encountered Pallas’s cats or their tracks.
Usually, the area in which the encounter
took place was the grazing area around the
livestock-breeding camp that livestock can
reach during their daily grazing. This can be
up to 100 km2, but is more often 50-80 km2.
In 11 (22.9%) of the interviews, Pallas’s cats
were not reported to occur in the vicinity of
the camps, but in most cases these respon-
dents explained that Pallas’s cat can be found
in other places nearby.
Our surveys show that the Pallas’s cat is
very rare in the Kurai Steppe. This is perhaps
because the Kurai Steppe represents the ex-
treme northern edge of the species’ range.
The study suggests that Pallas’s cat is not
abundant here because of the deep snow co-
ver and a lack of available prey. Snow depth
was 20-30 cm in December 2009, and pika
colonies in the area were few and small in
size. The winter of 2009-2010, however, was
definitely very snowy, so we cannot make a
general conclusion. There is some evidence
that Pallas’s cats occur sporadically north of
the Kurai Steppe, namely in the Lower Chuia
valley near Chibit village and in the Ineghen
valley. It is suggested that Pallas’s cats only
rarely disperse into this area and it is doubtful
that a breeding population exists there. Addi-
tional data are necessary for a more accurate
assertion.
Results from this study differ by a factor
of almost 2 from the estimations of Dro-
nova (2001) made for the Altai Republic
from interview data obtained at the end of
the 1990s. She estimated about 200-300
Pallas’s cats in the Altai Republic. This dif-
ference probably comes from the methods
used. The interview method is not accura-
te and cannot replace surveys in the field.
At the same time, the study of so rare and
secretive a carnivore as Pallas’s cat should
include additional methods, such as home
range determination, etc. The authors are of
the opinion that the Pallas’s cat population
size has been underestimated and that ad-
ditional investigations are therefore needed
to clarify its status.
Threats to Pallas’s cat
In spite of a relatively high Pallas’s cat den-
sity within the Altai Mountains, the species
is still threatened in the area. About 25%
of 52 respondents who gave instances of
Pallas’s cat deaths reported cats being kil-
led by herders’ dogs. Seven respondents
reported that Pallas’s cats were killed in
traps set for hares Lepus tolai, marmots
Marmota baibacina, red foxes Vulpes vul-
pes and corsacs V. corsac. Four respondents
reported that they had killed the cats with
their own hands. We know of one case of
a Pallas’s cat being killed by a vehicle. In
two instances Pallas’s cats were killed by
dogs, and we once came across a carcass
without skin lying close to a herder’s camp;
it may have been poached. Local residents
have noted incidences of Pallas’s cats being
killed by steppe polecats Mustela evers-
manni. We have not recorded any case of
Pallas’s cat being killed by either carnivore
Fig. 5. The Sailughem ridge (Photo I. Smelansky).
Table 1. Density estimation for Pallas’s cat based on snow-tracking data
Surveyed site Area
km2
Transect
length km
Tracks
/10 km
# individuals
/10 km2
Sailughem ridge 450 105.7 2.08 1.63-2.18
Kurai ridge and Talduair Massif 385 72.0 1.53 1.20-1.60
Fig. 4. Pallas’s cat (Photo A. Barashkova).
06
Barashkova & Smelansky
CATnews 54 Spring 2011
or raptor species in the Altai, although the-
re is evidence that this is happening. Mal-
kov (1979) reported a golden eagle Aquila
chrysaetos attacking a Pallas’s cat and, in
1999, the remains of Pallas’s cats were
found in eagle owl Bubo bubo and golden
eagle nests in the Sayan Mountains (Tyva
Republic; Karyakin, pers. comm.).
Future conservation work
This study’s results suggest that Pallas’s cat
populations should be monitored in the Altai
Republic on a regular basis. We recommend
that conservation efforts be undertaken to
reduce threats to Pallas’s cats, such as
trapping and direct killing. Other potential
threats to Pallas’s cats, such as habitat loss
resulting from increased economic activity
in the form of mining, recreation and the
construction of hydropower plants, should
be evaluated. Educational work with local
people is a crucial activity for the success
of Pallas’s cat conservation (Fig. 7). We urge
the creation of new protected areas in the
key habitats of the Pallas’s cat in the Altai
Republic, including the enlargement of the
recently-proclaimed national park in the
Sailughem ridge.
Acknowledgements
This study was kindly supported by the Panthera
Foundation and the People‘s Trust for Endangered
Species. The authors are also grateful to Svetla-
na Goryunova, Alexey Gribkov, Aldar Dambain,
Alexander Kapin, Sergey Naidenko, Ekaterina
Shichkova, Salavat Tadyshev, Andrey Tomilenko
and Maria Ushakova, all of whom accompanied
us in the tasks and hardships involved in the field
work.
References
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of Altai Republic: Animals. Gorno-Altaisk, pp.
363-366.
Dronova N.A. 2001. Manul. In Red Data Book of
Russian Federation. Moscow, pp. 647-648.
Formozov A.N. 1932. The formula for quantitative
countings of mammals by tracks. In Zoological
Journal. Tome 11, part 2, pp. 66-69.
Glushkov V. M., Grakov N. N., Grevtsev V. I., Za-
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Mashkin. – the 2nd edition, revised. VNIIOZ,
RAAS, VSAA. Kirov, p. 40.
Kiriliuk V.E. 1988. Rare mammals of southeastern
Zabaikalie (biological bases for conservation).
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1778) nutrition and behaviour in the southeas-
tern Transbaikal region. In Moscow Bulletin
of Naturalists. Moscow. Vol.104, Part. 6, pp.
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Malkov N.P. 1979. Notes on birds of central and
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Barnaul, pp. 143-145.
Naidenko S. V., Smelansky I. E. & Barashkova A. N.
2007. Pallas’s cat (Otocolobus manul) status in
the southeast of Altai Republic. In Theriofauna
of Russia and contiguous territories (YIII Con-
ference of Theriological Society). Materials of
international workshop. Moscow, p. 322.
Ross S., Murdoch J., Mallon D., Sanderson J. &
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1 NGO Siberian Environmental Center, P.O. Box
547, Novosibirsk 630090, Russia
<manul-project@yandex.ru>
Fig. 6. The south slopes of Kurai ridge (Photo A.Barashkova).
Fig. 7. Pallas’s cat: children’s art. Picture by Vladislav Turlunov (Grade 4 schoolboy, Kurai
village, Altai Republic)
07
Pallas’s cat in the Altai Republic, Russia