On the status of Barbastella barbastellus (Schreber, 1774)
in the Caucasus.
The data on all earlier and 12 new records of Barbastella barbastellus
in the Caucasus are given. A new record of B. barbastellus in Georgia
was the first since 1906. The absence of records from the Taman
and Kertch peninsulas demonstrates that the Caucasian part of the
range is isolated from the Crimean one. The occurrence of the barbastelle
in the territories of Chechnya, Ingushetia and Daghestan is doubtful
and must be confirmed. In contrast with earlier estimates, recent
studies indicate that barbastelles are quite abundant and widely
distributed in the forest zone of the Western Caucasus. Despite
protective measures urgently needed for this species it does not
have any official conservation status in the Russian Federation.
Key words: Barbastella
barbastellus, Caucasus
1.
Introduction
The Caucasus is one of the largest mountain areas in the Palearctic
region with various types of landscapes and climate. More than 30
bat species occur here (RAKHMATULINA 1999) but data on their status
is insufficient. The barbastelle was considered rare throughout
the Caucasus (see KUZYAKIN 1950, RAKHMATULINA 1996, KOZHURINA &
STRELKOV 1999). Nevertheless, the current status of barbastelles
must be revised after recent investigations in the Western Caucasus
(GAZARYAN 2000).
The distribution of B. barbastellus in the easternmost part
of its range is not clear at the moment. In some of the latest papers
(e.g. RYDELL & BOGDANOWICZ 1997) it has been shown as a continuous
belt from central Ukraine to the Caspian Sea. But this is not confirmed
by the current state of knowledge barbastelles are missing
from large territories of Ukraine between the right bank of the
Dnepr River and the Crimean mountains (KOVALYOVA & TARABORKIN 2001).
Also, records of barbastelles have never been reported from the
eastern part of the Crimean peninsula (KONSTANTINOV et al. 1976).
Outside the former USSR, Asian records of B. barbastellus came only
from Turkey (STEINER & GAISLER 1994). This species has never been
found in Iran (DEBLASE 1980) or any other part of this continent
(HORACEK et al. 2000). It seems that the Caucasus is more or less
isolated from any other part of the barbastelle's range. All earlier
and new records of B. barbastellus are described here in order to
clarify its distribution in the Caucasus region. In an attempt to
evaluate its relative abundance, the frequency of records and conservation
status was assessed for the territory of the Western Caucasus.
2.
Materials and Methods
The survey of bats was conducted mainly in the Russian part of the
Western Caucasus between 1997-2003. Special expeditions to the Crimean
peninsula, Abkhasia (illegitimate republic in the territory of Georgia)
and Daghestan were made in 2002-2003 with a goal to find barbastelles.
Observations were carried out in more than 170 locations in all
seasons. Bats were identified and counted visually in their hibernation
roosts; photographs were used for counting in large colonies. Mist
nets and a mobile trap (BORISSENKO 1999) were applied to catch bats
near the entrances of summer roosts and in foraging areas. For the
analyses of geographic distribution, collections of the State Museum
of Georgia (SMG), the Zoological Museum of Moscow State University
(ZMU), Zoological Institute of Russian Academy of Science (St.-Petersburg)
(ZIN), Daghestan, Stavropol, Rostov-on-Don and Abkhazian universities
were revised. All available literature sources were also used.
Relative abundance (A) and frequency of records (F) were calculated
after Strelkov & Iliyn (1990) for the Russian territory of the Western
Caucasus (Fig. 1). Estimates were made separately for hibernation
time (from the end of November till the beginning of April) and
other times of the year:
A = N1/ N x 100%, where N is the total number of recorded bats,
N1 is the number of a given species;
F= L1/ L x 100%, where L1 is the number of record sites for a given
species, L is the number of known sites of records for all bat species.
If one site (e.g. a hibernation roost) was checked several times,
the maximum number of each species was used for estimating relative
abundance.
3.
Results and Discussion
3.1. Distribution
Western barbastelles occur throughout the Caucasus in the mountain
and pre-mountain forested areas (Fig. 1). There are 57 localities
of reliable records, and 35 of them are situated in the Western
Caucasus (Tab. 1, 2). Fieldwork supports the absence of barbastelles
from the westernmost part of the Caucasus (Taman peninsula) and
in the easternmost part of Crimea (Kertch peninsula). Therefore,
the Crimean and Caucasian populations are probably isolated from
each other. The shortest distance between the nearest record localities
in the Caucasus (Tab. 1, locality 10 ) and in the mountains of Crimea
(Karadag, 44o56'N 35o14'E, KONSTANTINOV et al. 1976) is about 200
km.
Fig. 1. Distribution of B. barbastellus
in the Caucasus: I - location of records; II - boundary of the territory
that was investigated on relative abundance and frequency of records.
For further explanations see the text and tables.
While
the recent records of B. barbastellus in the Russian part
of the Western Caucasus are frequent, data from the neighboring
parts of the Caucasus are scarce. Only 3 records are known from
the northern slopes of the Central Caucasus (Tab. 1, localities
24, 25, 26). Confirmed records are absent for the territories of
Chechnya, Ingushetia and Daghestan. One locality in Daghestan (Tab.
1, locality 28) was pointed out by N. K. VEREZHAGIN (1959) as a
plot in the map of distribution, without any description. This doubtful
record of the western barbastelle has never been mentioned by previous
authors (RADDE, 1899; OGNEV, 1928; KRASOVSKY, 1932; GEPTNER, FORMOSOV,
1941) and was not confirmed by museum specimens. The presence of
B. barbastellus in the bat fauna of Daghestan has not been
investigated by subsequent research (AMIRKHANOV, 1980). Also, the
western barbastelle was not found in the underground quarters of
Daghestan.
The finding of the barbastelle in Uaz-Abaa cave (Tab. 2, locality
12) became the 6th one in Georgia and the first for this country
since 1906.
Tab.
1. List of earlier records of B. barbastellus in the Caucasus
Name and number of locality Country and geographic area*
Name and number of locality
|
Country and geographic area*
|
Coordinates
|
Literature source of information or museum
collection
|
1.
|
Psebay
village
|
RF,
W
|
44o10’N
40o52’E
|
Radde 1899
|
2.
|
Ashe
village
|
RF,
W
|
44o00’N
39o20’E
|
ZIN
|
3.
|
Krasnaya
polyana village
|
RF,
W
|
43o40’N
40o12’E
|
MSU
|
4.
|
Khadzhokh
cave
|
RF,
W
|
44o17’N
40o10’E
|
Kazakov & Garlikova 1973
|
5.
|
Azish
cave
|
RF,
W
|
44o07’N
40o01’E
|
Duvarova 1980
|
6.
|
Ozernaya
cave
|
RF,
W
|
44o05’N
40o02’E
|
Ibid.
|
7.
|
Svetlaya
cave
|
RF,
W
|
44o11’N
40o54’E
|
Ibid.
|
8.
|
Derbentskaya
mine
|
RF,
W
|
44o46’N
38o30’E
|
Gazaryan 2000
|
9.
|
Canyon
cave
|
RF,
W
|
44o09’N
39o45’E
|
Ibid.
|
10.
|
Maly
Utrish settlement
|
RF,
W
|
44o42’N
37o28’E
|
Ibid.
|
11.
|
Bogatyrskaya
cave
|
RF,
W
|
44o35’N
39o04’E
|
Ibid.
|
12.
|
Fanagoriyskaya
cave
|
RF,
W
|
44o28’N
38o59’E
|
Ibid.
|
13.
|
Nezhnaya
cave
|
RF,
W
|
44o09’N
40o05’E
|
Ibid.
|
14.
|
Ambitsug’s
cave
|
RF,
W
|
44o04’N
40o26’E
|
Ibid.
|
15.
|
Zubastchenko
cave
|
RF,
W
|
44o15’N
40o01’E
|
Ibid.
|
16.
|
Masliaev’s
cave
|
RF,
W
|
44o14’N
40o34’E
|
Ibid.
|
17.
|
Gunkina-1
cave
|
RF,
W
|
44o10’N
40o53’E
|
Ibid.
|
18.
|
Gunkina-4
cave
|
RF,
W
|
44o09’N
40o55’E
|
Ibid.
|
19.
|
Rozhnov’s cave
|
RF,
W
|
44o06’N
41o01’E
|
Ibid.
|
20.
|
Dedova
Jama cave
|
RF,
W
|
44o10’N
40o17’E
|
Ibid.
|
21.
|
Vorontsov’s
cave
|
RF,
W
|
43o38’N
39o57’E
|
Ibid.
|
22.
|
Kholodilnik
cave
|
RF,
W
|
43o57’N
40o31’E
|
Ibid.
|
23.
|
Sukhum
town
|
G,
W
|
43o00’N
41o00’E
|
Satunin 1913
|
24.
|
Verhnij
Tchegem village
|
RF,
C
|
43o25’N
43o15’E
|
MSU
|
25.
|
Dzivgiss
cave
|
RF,
C
|
42o52’N
44o20’E
|
ZIN
|
26.
|
Nivdzin-Lagat
cave
|
RF,
C
|
42o58’N
44o23’E
|
Kuryatnikov et al. 1987
|
27.
|
Tiflis
(Tbilisi)
|
G,
C
|
41o40’N
44o50’E
|
Radde 1899
|
28.
|
Vicinities of Mahachkala**
|
RF,
E
|
Not
known
|
Verezhagin 1959
|
29.
|
Dzhary
village
|
Az,
E
|
41o40’N
46o41’E
|
Rakhmatulina 1988
|
30.
|
Khazra
village
|
Az,
E
|
41o30’N
48o15’E
|
Ibid.
|
31.
|
Kabala
town
|
Az,
E
|
40o58’N
47o50’E
|
Ibid.
|
32.
|
Rustov
village
|
Az,
E
|
41o15’N
48o35’E
|
Ibid.
|
33.
|
Ialama
railway station
|
Az,
E
|
41o46’N
48o34’E
|
Ibid.
|
34.
|
Nabran
settlement
|
Az,
E
|
41o46’N
48o41’E
|
Ibid.
|
35.
|
Kaladjik
village
|
Az,
E
|
40o58’N
48o03’E
|
Ibid.
|
36.
|
Kaladarija
village
|
Az,
E
|
40o45’N
48o33’E
|
Ibid.
|
37.
|
Bakuriani
town
|
G,
L
|
41o45’N
43o31’E
|
Radde 1899
|
38.
|
Signakhi
town
|
G,
L
|
41o37’N
45o55’E
|
GSM
|
39.
|
Bordjomi
town
|
G,
L
|
41o52’N
43o25’E
|
Satunin 1913
|
40.
|
Northern
coast of Sevan lake
|
Ar,
L
|
Approximately
40o40’N
45o00’E
|
GSM
|
41.
|
Adjikend
settlement
|
Az,
L
|
40o31’N
46o20’E
|
GSM
|
42.
|
Gosmalijan
village
|
Az,
L
|
38o40’N
48o22’E
|
Rakhmatulina 1988
|
43.
|
Nuvedi
village
|
Az,
L
|
38o42’N
48o40’E
|
Ibid.
|
44.
|
Isti-su
settlement
|
Az,
L
|
38o46’N
48o50’E
|
Ibid.
|
45.
|
Amburdarija
village
|
Az,
L
|
38o39’N
48o20’E
|
Ibid.
|
*Abbreviations:
RF - Russian Federation, G - Georgia, Az - Azerbaijan, Ar - Armenia;W
- the Western Caucasus, C - the Central Caucasus, E - the Eastern
Caucasus, L - the Lesser Caucasus and Talysh mountains;ZIN - Zoological
Institute of Russian Academy of Science (St.-Petersburg), MSU -
Zoological Museum of Moscow State University, GSM - Georgian State
Museum.
** - see the text about this record
Tab.
2. New records of B. barbastellus in the Caucasus Name and
number of locality Country and geographic area*
Name and number of locality
|
Country and geographic area*
|
Coordinates
|
Date of record
|
Total number, sex and age of censored specimens
|
1.
Zolushka cave**
|
RF,
W
|
43o48’N
40o50’E
|
04.09.1981
|
Fresh
remains (> 200 specimens)
|
2.
Okhotnitchya cave
|
RF,
W
|
44o08’N
40o00’E
|
06.08.1997
|
Fresh
remains of 4 specimens
|
3.
Babaylov’s cave
|
RF,
W
|
43o56’N
40o34’E
|
16.09.2001
|
21,
18 male, 3 female, ad only
|
4.
Tru-40 cave
|
RF,
W
|
43o54’N
40o35’E
|
17.09.2001
|
1
male, ad
|
5.
Durshlag cave
|
RF,
W
|
43o53’N
40o37’E
|
18.09.2001
|
Fresh
remains of 1 specimen
|
6.
Pshada river
|
RF,
W
|
44o30’N
38o30’E
|
11.08.2001
|
1
male, sad
|
7.
Pryjamaya cave
|
RF,
W
|
44o07’N
40o01’E
|
20.10.2002
|
4
|
8. Old mine near Novy settlement
|
RF,
W
|
44o41’N
38o20’E
|
19.01.2003
|
1
male, ad
|
9.
Porozhki cave
|
RF,
W
|
44o17’N
40o20’E
|
9.03.2003
|
3
|
10.
Mayskaya cave
|
RF,
W
|
43o51’N
40o49’E
|
1.05.2003
|
19,
7 male, 2 female, ad
|
11.
Pogrebok cave
|
RF,
W
|
43o51’N
40o49’E
|
29.04.2003
|
6,
4 male, 2 female, ad
|
12.
Uaz-Abaa cave
|
G,
W
|
43o05’N
40o59’E
|
17.12.2002
|
1
female, ad
|
* -
Abbreviations as in Tab. 1
** - Based on materials from the archive of ZIN
3.2.
Frequency of records and relative abundance in the Western Caucasus
Barbastelles are particularly frequent during the hibernation period,
being the fourth most abundant among 19 bat species in the Western
Caucasus during winter (Fig. 2). By relative abundance in the cold
season, B. barbastellus was one of two dominating species (Fig.
3). The overwhelming majority of hibernating barbastelles were counted
in Canyon cave, where up to 7000 animals hibernate (GAZARYAN 2000).
Probably, thousands of barbastelles hibernate each year in the newly
explored Mayskaya and Babaylov's caves (Tab. 2). Such a conclusion
is based on the large amount of bones and guano in these caves.
The number in other underground shelters did not exceed several
tens.
Summer records are not rare; but most of them are related to large
hibernation roosts where adult males and non-reproductive females
occur from spring to autumn. Only two summer records outside underground
roosts are known - in the vicinity of Krasnaya Polyana village (Tab.
1, locality 3) and at the Pshada river (Tab. 2, locality 6). In
the last case one subadult male was captured by a mobile trap over
the river (A.V. Borissenko, personal communication). Although barbastelles
are not as abundant during the summer time as in winter, they are
still quite numerous, because relatively large numbers of animals
were netted and counted near the entrances of caves during the period
of swarming, from mid-August to the beginning of October.
Fig. 2. Frequency of records (F) of 23 bat species
in the Western Caucasus.
Fig. 3. Relative abundance (A) of B. barbastellus
in the Western Caucasus during the hibernation period and in other
times of the year in 1997-2003 (about 17 000 and 23 000 individuals
of different species were counted consequently).
3.3.
Conservation status
The reported change in status is not related to population growth,
but results from detailed study of the bat fauna. B. barbastellus
is the most abundant and frequently found species in Holocene
subfossil material from caves of the Western Caucasus (own data).
A large number of skulls was gathered in large hibernation roosts,
for example in Babaylov's and Canyon caves. Following the information
of cavers, the number of bats in the last cave decreased markedly
from the date of first exploration in 1978. Special observations
concluded that disturbance from only one winter expedition of cavers
may lead to a drastic decline in the number of barbastelles in Canyon
cave. Four hibernation roosts (Tab. 3, localities 4, 5, 11, 13,
21) were abandoned by barbastelles since 1997 as a result of frequent
commercial excursions. In some non-commercial caves (Tab. 3, localities
6, 12) the number of hibernating animals also greatly decreased
because disturbance from visitors grew significantly in the last
years. The protection of several key winter roosts is urgently needed
for the conservation of species in the Russian Federation.
Tab.
3. Records of B. barbastellus in the Western Caucasus.
Name of locality
|
Date of record
|
Number, sex and age of specimens (if censored)
|
Literature source or (and) collection
|
¹ in Fig.1
|
1.
Psebay vil.
|
unknown
|
-
|
Satunin 1915
|
15
|
2.
Ashe vil.
|
25.04.1914
|
1
male, ad
|
ZIN
|
6
|
3.
Krasnaya polyana vil.
|
July
1913
|
1
male, ad
|
MSU
|
20
|
4.
Khadzhoh cave
|
01.02.1972
|
1
male, 1 female
|
RSU
|
8
|
5.
Rock cavity near
Malyi Utrish vil.
|
18.08.1990
|
1
male, ad
|
ZIN
|
1
|
6.
Azish cave
|
01.01.1974
|
13,
both sexes
|
ZIN;
Duvarova 1980
|
10
|
|
02.01.98
|
1
male, 2 female
|
Own
data
|
|
|
02.01.00
|
2
male, 2 female
|
Own
data
|
|
7.
Pshada river
|
11.08.01
|
1
male, sad
|
MSU
|
3
|
8.
Ozernaya cave
|
Jan.
1974
|
1
female
|
Duvarova 1980
|
10
|
9.
Svetlaya cave
|
2.02.1975
|
1
male, 1 female
|
Duvarova 1980
|
15
|
|
04.12.1999
|
2
|
Own
data
|
|
10.
Bogatyrskaya cave
|
16.01.98
|
2
female, ad
|
-
|
5
|
11.
Nezhnaya cave
|
01.01.98
|
1
male
|
-
|
9
|
12.
Ambitsug’s cave
|
06.03.00
|
5
|
-
|
13
|
13.
Zubastchenko cave
|
29.01.99
|
1
|
-
|
12
|
14.
Masliaeva cave
|
30.01.99
|
2
male
|
-
|
12
|
15.
Gunkina-1 cave
|
01.02.98
|
44,
both sexes
|
-
|
15
|
|
04.12.99
|
64,
both sexes
|
-
|
|
16.
Gunkina-4 cave
|
03.02.98
|
1
male, 1 female
|
-
|
15
|
|
04.12.99
|
1
female
|
-
|
|
17.
Rozhnov’s cave
|
04.02.98
|
1
male, 2 female
|
-
|
16
|
18.
Dedova Jama cave
|
06.02.98
|
4
|
|
14
|
19.
Vorontsov’s cave
|
25.01.98
|
13
|
-
|
21
|
|
03.02.01
|
9
|
-
|
|
20.
Kholodilnik cave
|
11.03.97
|
1
|
-
|
17
|
21.
Babaylov’s cave*
|
16.09.01
|
21:
18 male, 3 female, ad only
|
-
|
18
|
22.
Tru-40 cave*
|
17.09.01
|
1
male, ad
|
-
|
18
|
23.
Durshlag cave
|
18.09.01
|
Fresh
remains
|
|
19
|
24.
Nikel mines
|
09.12.01
|
7,
both sexes
|
-
|
11
|
25.
Okhotnitchya cave
|
06.
08. 97
|
Fresh
remains
|
-
|
10
|
26.
Fanagoriyskaya cave
|
6 times in 1997-2001, all year-round
|
1-28,
both sexes, ad only
|
-
|
4
|
27.
Derbentskaya mines
|
9 times in 1999-2002, all year-round
|
1-9,
both sexes, ad only
|
-
|
2
|
28.
Canyon cave
|
12 times in 1998-2002, all year-round
|
from
3 to 7000, both sexes, ad only
|
-
|
7
|
* -
Netted during swarming
4.
Conclusions
B. barbastellus is widely distributed in the Caucasus but
is common only in the western part of these mountains. The northern
boarder of distribution is associated with the edge of the forest
zone and does not reach the 45o parallel. B. barbastellus
is missing in the steppe parts of the Precaucasus, Crimea and Taman
peninsula. Its occurrence in Ingushetia, Chechnya and Daghestan
must be confirmed.
Estimation of relative abundance and frequency of records demonstrates
that barbastelles in the Western Caucasus are even more common than
in Eastern Europe (URBANCZYK 1989, UHRIN 1995). The major threats
for the population are also similar with those known from the European
part of the range (RICHARZ 1989, RYDELL & BOGDANOWICZ 1997). Demanding
conservation measures have not been undertaken because B. barbastellus
wasn't included in the Russian Red Data Book of Threatened Species.
It indicates that the recent list of threatened bats in the Russian
federation is incomplete and must be revised urgently.
Acknowledgments
I would like to thank P.P. Strelkov, G.B. Bakhtadze, A. Bukhnikashvili,
S.V. Kruskop and A.V. Borissenko, who kindly provided access to
museum collections and own unpublished data. The author is grateful
to Dr. B.S. Tuniev from the Caucasian State Reserve for the support
of expeditions in this protected area and to all cavers from Krasnodar
and Moscow who helped me in expeditions. I also wish to thank T.
Postawa for the idea of this paper.
Studies in 2000-2001 were performed with the support of the Program
on Global Security and Sustainability's Research and Writing Initiative
of the John D. and Catherine T. MacArthur Foundation (grant #00-62799).
Investigations in 2002 partially founded by DEFRA / FFI Flagship
Species Fund (project ¹ 02/20/05 FLAG).
5.
References
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