Abstract
The article presents the results of studying the fauna of ground beetles in the western part of the Zerafshan Range (Uzbekistan). The Carabidae list includes 81 species from 41 genera, 18 tribes and nine subfamilies. The ecological diversity of the ground beetle fauna is analyzed on three parts of the ridge. The greatest diversity of Carabidae is noted in the Karatepo Mountains (74 species), and the smallest in the Zirabulak-Ziyadin Mountains (54 species). The fauna of the ground beetles of the Chakalikalyan and Karatepa Mountains are closer to each other (Jaccard index – 0.79, Chekanovsky-Sørensen coefficient – 0.89). The lowest value of the similarity coefficients was noted between the Chakalikalyan and Zirabulak-Ziadin Mountains (0.64; 0.78). The most numerous are Anchomenus dorsalis (10.46%), Calathus ambiguus (8.23%), Amara aenea (7.48%) and Harpalus rufipes (6.03%).
Corresponding author: Fazlitdin Khalimov (xalimov1968@list.ru)
Academic editor: R. Yakovlev | Received 8 February 2023 | Accepted 23 February 2023 | Published 14 March 2023
http://zoobank.org/C53D0BCB-9C63-4605-A9F3-C791652C2830
Citation: Khalimov F (2023) Composition and structure of the fauna of ground beetles (Coleoptera, Carabidae) of the Zerafshan Range. Acta Biologica Sibirica 9: 113–125. https://doi.org/10.5281/zenodo.7725474
Keywords
Degree of dominance, ground beetles, species abundance, species composition, Zeravshan Range
Introduction
Ground beetles are a very large and diverse taxon among beetles, and about 100 new species are discovered every year (Kotze et al. 2011). They are an important link in food chains and thus play a huge role in energy transformation (Schirmel et al. 2012). They are sensitive to environmental changes, showing strong habitat specificity and low ability to quickly spread to neighboring sites (Work et al. 2008; Koivula 2011). Therefore, ground beetles have been widely used for ecological monitoring (Skalski et al. 2016; Kosewska et al. 2016; Bell et al. 2017; Kędzior 2020).
Many species of ground beetles, as universal predators with a wide food spectrum, can act as an essential component of biological regulation (Symondson et al. 2002; Stiling and Cornelissen 2005). And in agricultural landscapes, they play a very significant role in reducing the number of pests (Koval and Guseva 2008, Halimov 2020) and weeds (Talarico et al. 2016, Deroulers and Bretagnolle 2019).
The beetle fauna of Central Asia is very diverse and is characterized by many endemic forms. So, in the Tien Shan mountain system, within the republics of Kazakhstan, Kyrgyzstan, Tajikistan and Uzbekistan, 819 species of ground beetles were noted. And the fauna of ground beetles of the Pamir-Alai mountain system, located in the southeastern part of Middle Asia, includes 510 species (Kryzhanovsky et al. 1995).
The invertebrate fauna of the Zeravshan Range is still poorly understood, although in recent years some works have appeared on individual groups (Khalimov 2020, Narzullaev 2022).
Information about the fauna of the ground beetles of the Zarafshan valley can be found in general faunal studies (Alimdzhanov and Bronshtein 1956) or for the southern slopes of the Zarafshan ridge, located on the territory of Tajikistan (Mikhailov 1998). We previously reported the distribution of 49 species of ground beetles in this area (Khalimov 2020).
The purpose of our research was to study the species diversity and taxonomic composition of the ground beetles of the Zerafshan Range within the Republic of Uzbekistan.
Materials and methods
The studies were carried out in the period 2018–2022. The Zarafshan range on the territory of Uzbekistan is divided into four parts: the Chakilkalyan, Karatepa, Zirabulak and Ziadin mountains (Fig.1). The Chakilkalyan Mountains are the eastern part of the Zerafshan Range within Uzbekistan. The average height of the Chakilkalyan Mountains is 1000–2000 m. To the west of the Chakilkalyan Mountains are the Karatepa Mountains (the average height is 1000–2000 m). The western part of the Zerafshan ridge is formed by the Zirabulak and Ziadin mountains, which have the character of low mountains, the average height of which is 400–900 m (Zhumaev 1989).
Each of the above-mentioned parts of the Zeravshan Range has a peculiar hydrothermal regime and vegetation cover.
The beetles were collected using soil traps, light traps, an exhauster, and manual collection. The ground beetle system is given according to the Cataloque of Life (Lorenz 2021). The examined specimens are kept in the Entomological collection of Samarkand State University.
The degree of dominance was determined according to the Renkonen scale (Renkonen 1944), where more than 5% are dominant species, from 2% to 5% are subdominant species, 1–2% are few, and less than 1% are rare species.
Statistical calculations of biodiversity were carried out according to the guidance of E.A. Dunaev (1997).
Result
Over the years of research, 2686 beetle specimens belonging to nine subfamilies, 18 tribes, 41 genera and 81 species were collected (Table 1).
Subfamily | Tribe | № | Species name |
---|---|---|---|
Nebriinae | Nebriini | 1. | Nebria psammophila Solsky, 1874 |
2. | Notiophilus sublaevis Solsky 1873 | ||
Cicindelinae | Cicindelini | 3. | Cicindela turkestanica Ballion, 1871 |
4. | Cicindela fischeri M.Adams, 1817 | ||
Omophroninae | Omophronini | 5. | Omophron rotundatum (Fabricius, 1777) |
Carabinae | Carabini | 6. | Calosoma sycophanta Linnaeus, 1758 |
7. | Calosoma auropunctatum Gilber, 1833 | ||
8. | Carabus fedtschenkoi Solsky, 1874 | ||
9. | Carabus staudingeri Ganglbauer, 1886 | ||
Brachininae | Brachinini | 10. | Brachinus bayardi Dejean, 1831 |
11. | Brachinus brevicollis Motschulsky, 1844 | ||
12. | Brachinus explodens Duftschmid, 1812 | ||
13. | Mastax thermarum Steven, 1806 | ||
Scaritinae | Clivinini | 14. | Clivina collaris Herbst, 1784 |
Scaritini | 15. | Scarites basiplicatus Heyden, 1884 | |
16. | Scarites procerus Fischer von Waldheim, 1828 | ||
17. | Scarites subcylindricus Chaudoir, 1843 | ||
18. | Scarites terricola Bonelli, 1813 | ||
Broscinae | Broscini | 19. | Broscus asiaticus Ballion, 1871 |
20. | Broscus punctatus Dejean, 1828 | ||
21. | Craspedonotus margellanicus Kraatz, 1884 | ||
Trechinae | Bembidiini | 22. | Asaphidion flavicorne Solsky, 1874 |
23. | Bembidion abbreviatum Solsky, 1874 | ||
24. | Bembidion almum J. Sahlberg, 1900 | ||
25. | Bembidion insidiosum Solsky, 1874 | ||
26. | Bembidiоn kirgisorum Netolitzky, 1934 | ||
27. | Bembidion lampros (Herbst 1784) | ||
28. | Bembidion luridicorne Solsky, 1874 | ||
29. | Bembidion quadrimaculatum Linnaeus, 1761 | ||
30. | Bembidion quadripustulatum Audinet-Serville, 1821 | ||
31. | Bembidion piceocyaneum Solsky, 1874 | ||
32. | Bembidion saxatile flavipalpe Netolitzky, 1930 | ||
Tachyini | 33. | Elaphropus tetraspilus (Solsky, 1874) | |
34. | Tachyura euphratica Reitter, 1885 | ||
35. | Tachys turkestanicus Csiki, 1928 | ||
Trechini | 36. | Trechus quadristriatus Schrank, 1781 | |
37. | Chlaenius circumscriptus (Duftschmid, 1812) | ||
38. | Chlaenius festivus Panzer, 1796 | ||
39. | Chlaenius flavicornis Fischer, 1842 | ||
40. | Chlaenius extensus Mannerheim, 1825 | ||
41. | Chlaenius semicyaneus Solsky, 1874 | ||
42. | Chlaenius tenuilimbatus Ballion, 1871 | ||
Harpalini | 43. | Acinopus laevigatus Menetries,1832 | |
44. | Acinopus striolatus Zoubkoff, 1833 | ||
45. | Acupalpus parvulus (Sturm, 1825) | ||
46. | Anisodactylus binotatus Fabricius, 1787 | ||
47. | Carenochyrus titanus Solsky,1874 | ||
48. | Chilotomus usgentensis Schauberger, 1932 | ||
49. | Ditomus calydonius Rossi, 1790 | ||
50. | Dixus eremita Dejean, 1825 | ||
51. | Dixus semicylindricus Piochard de la Brûlerie, 1872 | ||
52. | Eocarterus chodshenticus Ballion, 1871 | ||
53. | Harpalus distinguendus Duftschmid, 1812 | ||
54. | Harpalus griseus Panzer, 1796 | ||
55. | Harpalus rufipes De Geer, 1774 | ||
56. | Harpulus rubripes Duftschmid, 1812 | ||
57. | Harpalus tenebrosus Dejean 1829 | ||
58. | Parophonus hirsutulus (Dejean, 1829) | ||
59. | Stenolophus abdominalis Mannerheim, 1844 | ||
Lebiini | 60. | Cymindis andreae Ménétriés, 1832 | |
61. | Cymindis quadrisignata Menetries, 1848 | ||
62. | Lebia cyonocephala Linnaeus, 1758 | ||
63. | Lebia festiva Faldermann, 1836 | ||
64. | Lebia scapularis (Geoffroy, 1785) | ||
Platynini | 65. | Agonum viridicupreum Goeze, 1777 | |
66. | Anchomenus dorsalis Pontoppidan, 1763 | ||
Pterostichini | 67. | Poecilus cupreus Linnaeus,1758 | |
68. | Poecilus liosomus Сhaudoir, 1876 | ||
69. | Poecilus longiventris Solsky, 1874 | ||
70. | Poecilus sp. | ||
71. | Pterostichus niger Schaller, 1783 | ||
Sphodrini | 72. | Calathus ambiguus Paykull, 1790 | |
73. | Calathus melanocephalus Linnaeus, 1758 | ||
74. | Calathus peltatus Kolenati, 1845 | ||
75. | Dolichus halensis Schaller, 1783 | ||
76. | Pseudotaphoxenus juvencus (Ballion, 1871) | ||
77. | Taphoxenus goliath Faldermann, 1836 | ||
Zabrini | 78. | Amara aenea De Geer,1774 | |
79. | Amara ovata Fabricius, 1792 | ||
80. | Amara similata Gyllenhal, 1810 | ||
81. | Zabrus morio Mandrias, 1832 |
The most representative in terms of the number of species is the subfamily Harpalinae, which includes 45 species (55.6% of the total species diversity). In terms of the number of individuals, the subfamily Harpalinae accounts for 79.3% of all collected ground beetles. Among the representatives of this subfamily, the tribe Harpalini has the largest number of species, which is represented by 17 species from 11 genera. Among them, Acinopus laevigatus, Eocarterus chodshenticus, Harpalus rufipes and Harpalus griseus are numerous.
The tribe Sphodrini is represented by six species from four genera, the most numerous of which are Calathus ambiguus and Pseudotaphoxenus juvencus. The tribe Pterostichini is represented by five species from two genera (Pterostichus niger and four species from the genus Poecilus).
Six species from the tribe Chlaeniini belonging to the genus Chlaenius were identified. The most common are Chlaenius extensus. The tribe Lebiini is represented by five species and the tribe Zabrini by four species (three species from the genus Amara and one species from the genus Zabrus). Amara aenea and Zabrus morio are the dominant species of carabid fauna.
In the Karabidocomplex of the Zerafshan Range, 15 species belonging to three tribes and five genera are found from the subfamily Trechinae. The tribe Trechini is represented by a single species, Trechus quadristriatus, and the tribe Tachyini by three species. The tribe Bembidiini includes 11 species (genus Asaphidion – one species, genus Bembidion – ten species). Although these species are widespread and numerous in agrolandscapes, their abundance in the studied ridge is low. In general, representatives of the subfamily Trechinae account for 10.46% of all ground beetles and 18.5% of the total species diversity.
Five species of beetles from the subfamily Scaritinae belonging to the genera Scarites (four species) and Clivina (one species) were identified. The subfamilies Carabinae and Brachininae are represented by four species each (the genus Carabus and Calosoma each have two species, three species from the genus Brachinus and one species from the genus Mastax). The subfamily Broscinae is represented by three species from the genera Broscus and Craspedonotus.
In the complex of ground beetles of the studied territories, two representatives each have the subfamilies Nebriinae and Cicindelinae, and the only species is the subfamily Omophroninae.
The dominant species of the carabid fauna of the Zerafshan Range are Anchomenus dorsalis (10.46%), Calathus ambiguus (8.23%), Amara aenea (7.48%), Harpalus rufipes (6.03%). The habitats of subdominant species are rich in Zabrus morio (4.77%), Eocarterus chodshenticus (4.54%), Pseudotaphoxenus juvencus (4.47%), and Harpalus griseus(4.36%).
Very few are Brachinus bayardi, Broscus punctatus, Chlaenius circumscriptus, Chlaenius tenuilimbatus, Chilotomus usgentensis, Craspedonotus margellanicus, Ditomus calydonius, Notiophilus sublaevis and Taphoxenus goliath, whose dominance is less than 0.1% (Table 2).
№ | Species name | Chakil- kalyan | Karatepa | Zirabulak- Ziadin | Total | Degree of dominance, % |
---|---|---|---|---|---|---|
1. | Acinopus laevigatus | 32 | 53 | 16 | 101 | 3.76 |
2. | Acinopus striolatus | 12 | 6 | 4 | 22 | 0.82 |
3. | Acupalpus parvulus | 3 | 2 | - | 5 | 0.19 |
4. | Agonum viridicupreum | - | 4 | 2 | 6 | 0.22 |
5. | Amara aenea | 65 | 112 | 24 | 201 | 7.48 |
6. | Amara ovata | 1 | 4 | 2 | 7 | 0.26 |
7. | Amara similata | 2 | 4 | 6 | 12 | 0.45 |
8. | Anchomenus dorsalis | 94 | 119 | 68 | 281 | 10.46 |
9. | Anisodactylus binotatus | - | 4 | - | 4 | 0.15 |
10. | Asaphidion flavicorne | 9 | 12 | 9 | 30 | 1.12 |
11. | Bembidion abbreviatum | 3 | 2 | 1 | 6 | 0.22 |
12. | Bembidion almum | 5 | 3 | 2 | 10 | 0.37 |
13. | Bembidion insidiosum | 6 | 4 | - | 10 | 0.37 |
14. | Bembidion lampros | 7 | 5 | - | 12 | 0.45 |
15. | Bembidion luridicorne | 13 | 9 | 9 | 31 | 1.15 |
16. | Bembidion piceocyaneum | 2 | 2 | 1 | 5 | 0.19 |
17. | Bembidion quadrimaculatum | 6 | 7 | 5 | 18 | 0.67 |
18. | Bembidion quadripustulatum | 2 | 3 | 1 | 6 | 0.22 |
19. | Bembidion saxatile flavipalpe | 12 | 7 | 2 | 21 | 0.78 |
20. | Bembidiоn kirgisorum | 3 | 1 | 2 | 6 | 0.22 |
21. | Brachinus brevicollis | 8 | 10 | 12 | 30 | 1.12 |
22. | Brachinus explodens | 19 | 38 | 12 | 69 | 2.57 |
23. | Brachinus bayardi | 2 | - | - | 2 | 0.07 |
24. | Broscus asiaticus | 15 | 6 | 3 | 24 | 0.89 |
25. | Broscus punctatus | 1 | 1 | - | 2 | 0.07 |
26. | Calathus ambiguus | 121 | 60 | 40 | 221 | 8.23 |
27. | Calathus melanocephalus | 7 | 11 | 4 | 22 | 0.82 |
28. | Calathus peltatus | 14 | 12 | 8 | 34 | 1.27 |
29. | Calosoma auropunctatum | 5 | 7 | - | 12 | 0.45 |
30. | Calosoma sycophanta | 2 | 2 | - | 4 | 0.15 |
31. | Carabus fedtschenkoi | 9 | 11 | - | 20 | 0.74 |
32. | Carabus staudingeri | 1 | 3 | - | 4 | 0.15 |
33. | Carenochyrus titanus | 4 | 2 | 2 | 8 | 0.30 |
34. | Chilotomus usgentensis | - | 2 | - | 2 | 0.07 |
35. | Chlaenius festivus | 4 | 2 | 2 | 8 | 0.30 |
36. | Chlaenius circumscriptus | - | 2 | - | 2 | 0.07 |
37. | Chlaenius flavicornis | 12 | 7 | 5 | 24 | 0.89 |
38. | Chlaenius semicyaneus | 1 | 2 | - | 3 | 0.11 |
39. | Chlaenius tenuilimbatus | 1 | 1 | - | 2 | 0.07 |
40. | Chlaenius extensus | 29 | 10 | 21 | 60 | 2.23 |
41. | Cicindela turkestanica | 9 | 10 | 7 | 26 | 0.97 |
42. | Cicindela fischeri | - | 4 | - | 4 | 0.15 |
43. | Clivina collaris | 8 | 9 | 3 | 20 | 0.74 |
44. | Craspedonotus margellanicus | - | 1 | - | 1 | 0.04 |
45. | Cymindis quadrisignata | 9 | 17 | 26 | 52 | 1.94 |
46. | Cymindis andreae | 3 | 4 | 3 | 10 | 0.37 |
47. | Ditomus calydonius | - | - | 2 | 2 | 0.07 |
48. | Dixus eremita | 15 | 19 | 8 | 42 | 1.56 |
49. | Dixus semicylindricus | 3 | 3 | - | 6 | 0.22 |
50. | Dolichus halensis | 11 | 9 | 9 | 29 | 1.08 |
51. | Eocarterus chodshenticus | 37 | 54 | 31 | 122 | 4.54 |
52. | Harpalus distinguendus | 14 | 13 | 23 | 50 | 1.86 |
53. | Harpalus griseus | 42 | 21 | 54 | 117 | 4.36 |
54. | Harpalus rufipes | 40 | 64 | 58 | 162 | 6.03 |
55. | Harpulus rubripes | 11 | 10 | 4 | 25 | 0.93 |
56. | Harpalus tenebrosus | 3 | - | - | 3 | 0.11 |
57. | Lebia cyonocephala | 6 | 14 | - | 20 | 0.74 |
58. | Lebia scapularis | - | 8 | - | 8 | 0.30 |
59. | Lebia festiva | 3 | - | - | 3 | 0.11 |
60. | Mastax thermarum | - | 2 | 2 | 4 | 0.15 |
61. | Nebria psammophila | 5 | 3 | - | 8 | 0.30 |
62. | Notiophilus sublaevis | 2 | - | - | 2 | 0.07 |
63. | Omophron rotundatum | - | - | 3 | 3 | 0.11 |
64. | Parophonus hirsutulus | - | 5 | 3 | 8 | 0.30 |
65. | Poecilus cupreus | 7 | 7 | 6 | 20 | 0.74 |
66. | Poecilus liosomus | 14 | 16 | 10 | 40 | 1.49 |
67. | Poecilus longiventris | 14 | 17 | 11 | 42 | 1.56 |
68. | Poecilus sp. | 4 | 8 | 1 | 13 | 0.48 |
69. | Pseudotaphoxenus juvencus | 44 | 58 | 18 | 120 | 4.47 |
70. | Pterostichus niger | 17 | 12 | 11 | 40 | 1.49 |
71. | Scarites basiplicatus | 4 | 8 | - | 12 | 0.45 |
72. | Scarites procerus | - | - | 11 | 11 | 0.41 |
73. | Scarites subcylindricus | - | 3 | - | 3 | 0.11 |
74. | Scarites terricola | 6 | 3 | 4 | 13 | 0.48 |
75. | Stenolophus abdominalis | 22 | 17 | 3 | 42 | 1.56 |
76. | Tachys turkestanicus | 4 | 3 | 5 | 12 | 0.45 |
77. | Tachyura euphratica | - | 3 | 1 | 4 | 0.15 |
78. | Tachyura tetraspila | 4 | 4 | - | 8 | 0.30 |
79. | Taphoxenus goliath | - | 2 | - | 2 | 0.07 |
80. | Trechus quadristriatus | 35 | 21 | 46 | 102 | 3.80 |
81. | Zabrus morio | 45 | 59 | 24 | 128 | 4.77 |
Number of individuals | 973 | 1063 | 650 | 2686 | 100.00 | |
Number of species | 66 | 74 | 54 | 81 | - | |
Species richness, DMg | 9.45 | 10.47 | 8.18 | 10.13 | - | |
Species richness, DMn | 2.12 | 2.27 | 2.12 | 1.56 | - | |
Diversity indicator Shannon, H | 3.54 | 3.55 | 3.39 | 3.60 | - | |
Shannon equitability index, EH | 0.84 | 0.83 | 0.85 | 0.82 | - | |
Simpson’s Diversity Index, D (Sλ) | 0.045 | 0.046 | 0.047 | 0.043 | - | |
Berger – Parker dominance index, d | 0.124 | 0.112 | 0.10 | 0.105 | - |
As noted above, the Zeravshan Range is divided into the Chakilkalyan, Karatepa, Zirabulak and Ziadin mountains. The greatest diversity of ground beetles was noted on the Karatepa mountains (74 species), and the least on the Zirabulak and Ziadin mountains (54 species). The Chakilkalyan mountains occupies an intermediate position (66 species). However, there were no significant differences in the indices of ecological diversity of the beetle fauna in these territories (Table 2).
An analysis of the similarity of the fauna of the studied territories shows that the fauna of the ground beetles of the Chakalikalyan and Karatepa mountains are closer to each other (Jaccard index – 0.79, Chekanovsky-Sørensen coefficient – 0.89) (Table 3). The lowest value of the similarity coefficients was noted between the Chakalikalyan and Zirabulak-Ziadin mountains (0.64; 0.78).
Mountains | Karatepa | Chakilkalyan | Zirabulak-Ziadin |
---|---|---|---|
Karatepa | - | 0.89 | 0.8 |
Chakilkalyan | 0.79 | - | 0.78 |
Zirabulak-Ziadin | 0.66 | 0.64 | - |
The species Ditomus calydonius, Omophron rotundatum and Scarites procerus are unique for the Zirabulok-Ziyadin Mountains and are found only in this part of the Zerafshan Range. Eight species of ground beetles were found only in the Karatepa Mountains (Anisodactylus binotatus, Chilotomus usgentensis, Chlaenius circumscriptus, Cicindela fischeri, Craspedonotus margellanicus, Lebia scapularis, Scarites subcylindricus and Taphoxenus goliath). Brachinus bayardi, Harpalus tenebrosus, Lebia festiva and Notiophilus sublaevis were found only in the Chakalikalyan Mountains.
In these three areas of the Zeravshan Range, the degree of dominance of individual species can vary significantly. Thus, Calathus ambiguus (12.44%) is the most numerous in the Chakalikalyan Mountains. The habitats of dominant species are also Anchomenus dorsalis (9.66%) and Amara aenea (6.68%). Subdominants also have a high degree of dominance: Zabrus morio (4.62%), Pseudotaphoxenus juvencus (4.52%), Harpalus griseus (4.32%) and Harpalus rufipes (4.11%).
In the Karatepa Mountains, the dominant species are located in the following order: Anchomenus dorsalis (11.19%), Amara aenea (10.54%), Harpalus rufipes (6.02%), Calathus ambiguus (5.64%), Zabrus morio (5.55%), Pseudotaphoxenus juvencus (5.46% ), Eocarterus chodshenticus (5.08%) and Acinopus laevigatus (4.99%). Thus, Eocarterus chodshenticus and Acinopus laevigatus join the dominant species, and Harpalus rufipes is excluded from the dominant species.
And on the Zirabulak-Ziadin mountains, the dominant species are located in the following order: Anchomenus dorsalis (10.46%), Harpalus rufipes (8.92%), Harpalus griseus (8.31%), Trechus quadristriatus (7.08), Calathus ambiguus (6.15%), Eocarterus chodshenticus (4.77%) and Cymindis quadrisignata (4.0%). Here, there are no dominant species of Zabrus morio and Pseudotaphoxenus juvencus, but Trechus quadristriatus and Cymindis quadrisignata appear among the dominant species. However, in this section of the Zeravshan Range, the number of ground beetles, which are widely distributed in the agricultural landscapes Harpalus rufipes, Harpalus griseus and Trechus quadristriatus, is increasing.
The number of dominant species can vary significantly at different points within the same mountain, depending on the height of the area. So, as the height of the area increases, the abundance of Pseudotaphoxenus juvencus and Eocarterus chodshenticus increases, while the other dominant species show an opposite trend, that is, as the height increases, a decrease in abundance is observed. It should be noted that altitudinal belts affect not only the diversity and abundance of ground beetles, but also the morphometric features of individual species (Zokirova and Khalimov 2022).
Conclusion
For the first time, a list of ground beetles of the Zeravshan Range was compiled, including 81 species. A comparative analysis of the ecological diversity of the carabid fauna of the Chakaliyan, Karatepa and Zirabulak mountains, which are part of the ridge, was carried out. Dominant and rare species were identified. Among rare beetle species in need of protection are Brachinus bayardi, Broscus punctatus, Chlaenius circumscriptus, Chlaenius tenuilimbatus, Chilotomus usgentensis, Craspedonotus margellanicus, Ditomus calydonius, Notiophilus sublaevis and Taphoxenus goliath. However, further research is required to fully understand the state of the populations of these species.
Acknowledgements
The author expresses his sincere gratitude to I. Kabak (St. Petersburgh) and R. Dudko (Novosibirsk) for their help in species identification.
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