Review Article |
Corresponding author: Lola Gandjaeva ( tulipa_83@mail.ru ) Academic editor: Jader Oliveira
© 2023 Lola Gandjaeva, Ikram Abdullaev, Abdulla Iskandarov, Komila Allabergenova, Saodat Yusupova, Gulkhayo Narimanova, Erkinboy Yusupboev, Sohiba Ibragimova , Sanjar Begliev, Khulkar Bobojonova.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Gandjaeva L, Abdullaev I, Iskandarov A, Allabergenova K, Yusupova S, Narimanova G, Yusupboev E, Ibragimova S, Begliev S, Bobojonova K (2023) A zoogeographical analysis of true bugs (Insecta, Heteroptera) from Uzbekistan. ZooKeys 1163: 121-142. https://doi.org/10.3897/zookeys.1163.99414
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The purpose of this study is to perform a zoogeographic analysis of terrestrial true bugs (Heteroptera) in the Lower Amudarya Territory, Uzbekistan. According to the findings of a literature review, there are 149 species of terrestrial hemipterans in the Territory. All hemipteran species, with the possible exception of five, have most likely been misidentified. Until now, reliable information on the zoogeography of true bug species in Uzbekistan’s north-western region has not been published. The composition of species, diversity, and the proportion of endemism vary greatly across the country’s zoogeographic regions. The Heteroptera fauna of the Khorezm and Karakalpakstan can be divided into four groups: most species belonging to the Palaearctic region, with 125 species constituting 83.89% of the fauna; the second group of Holarctic origin is characterized by no more than ten species, which constitutes 6.71%; the third consists of endemics, 13 species or 8.72%; and one species (0.67%) is cosmopolitan. Much more research is needed to investigate distributions in a more northern climate. The introduction of invasive Heteroptera to the north-western part of Uzbekistan will increase and deserves further consideration.
Abundance, distribution, faunistics, geography range, Karakalpakstan, Khorezm, Lower Amudarya, occurrence
Heteroptera or true bugs are a large group with more than 40,000 species in approximately 50 families distributed across the world (
The study of the fauna of true bugs by Central Asia region has been occurring for more than 170 years (
The geographical distribution of Heteroptera from around the world has always been of interest to researchers (
Since the second half of the 19th century, new descriptions of Central Asian species have been published regularly in the works of
The literature on the fauna of terrestrial true bugs in different habitats of the Republic of Uzbekistan is meager. This lack of study also includes true bugs of Central Asia, mainly in the southern regions, which cover the territories of Samarkand, Bukhara, Tashkent, Andijan, Fergana, Kashkadarya, and Surkhandarya.
The purpose of the current paper is to explain database entries for the Lower Amudarya Heteroptera species, including brief geographic histories and original references. Every database should be a living document, with the ability to track changes regularly. Additional information on newly studied species is being added continuously (
The goals of this study include classifying species ranges and conducting a zoogeographical analysis of the nation’s actual true bug fauna, as well as determining species compositions and distributions in various belts of the Khorezm region and Karakalpakstan Republic.
The study was conducted in a lowland area in the northwestern part of Uzbekistan along the lower sections of the Amudarya River: between 60' and 61' longitude and 41' and 42' latitude, at an altitude of 113–138 m above sea level. The vegetative cycle of plants lasts 200–210 days. The climate is continental, with an average annual precipitation of 80–90 mm, and average temperature ranges from -5 °C in January to 40 °C in July. The climate has been changing, and the temperature has risen in summer, reaching 50 °C in July (
For the analysis, we used zoogeographical categories of the heteropteran species that had been recorded earlier. Approximately 180 specimens of Heteroptera indexed in the territory of the Lower Amudarya River and were identified to 149 species in 89 genera, and two infraorders. These species were deposited in the Zoological collections of the Zoology Institute (ZIN) of the Academy of Sciences of the Republic of Uzbekistan.
The study was carried out between 2007 and 2020 (see
The zoogeographic analysis of identified species in the Lower Amudarya was based on zoogeographical nomenclature by
The descriptive area nomenclature utilized in this work uses the concepts of physical geography and applies two axis coordinates: the latitudinal axis runs from north to south and is critical because it is used to determine climatic conditions of the distributed species, especially temperature; the longitudinal axis runs from west to east. In some species, the range coincides with the boundaries of the landscape zone and is labeled as Arctic (polar deserts, tundra), boreal (taiga), subboreal (broad-leaved forests), subtropical and tropical (evergreen forests) (
We used the basic data on the geographic distribution of these species from the Catalogue “Heteroptera of the Palaearctic” Volumes I–VI, published by the
Netherlands Entomological Society, Amsterdam (NES)
(1995–2013) (
An analysis of the occurrence and abundance of species on cultivated and wild plants were carried out by observing 50–100 plant specimens every day along the diagonal of the fields. The number of adult bugs, larvae of all ages, and egg clutches was recorded (
The number of species and their occurrence was calculated using the formula devised by
F(%) = 100 × (Pi/P)
where Pi refers to the species that was found; P is an absolute number.
Species are divided into four groups based on their frequency of occurrence:
Constantly occurring species: F ≥ 50%
Often occurring species: 25% < F < 50%
Additional occurring species: 5% ≤ F < 25%
Rarely occurring species: F < 5%
The dynamics of the abundance of species was calculated using the formula of
Ar(%) = 100 × (Ni/N)
where Ni is the coefficient of special observable species; N is the absolute number of all observable species.
The analyses of the dynamics of the numbers of species are also divided into four groups:
Abundant: Ar ≥ 10
Frequent: 5 ≤ Ar < 10
Some: 1 ≤ Ar < 5
Few: Ar < 1
Checklists of Heteroptera for the Khorezm region and Karakalpakstan Republic were published more than 20 years ago.
We carried out a comparative analysis of the lists of regional faunas using the data from
Checklist of the terrestrial Heteroptera from the Lower Amudarya (2007–2020).
Taxon | Family | Occurrence | Abundance | Distribution | Zoogeographic categories | References | |
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1 | Anthocoris pilosus (Jakovlev, 1877) | Anthocoridae Fieber, 1837 | + | F | *** | SA |
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2 | Orius niger (Wolff, 1811) | ++ | FR | 0 | TP |
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3 | Orius ribauti (Wagner, 1952) | + | F | *** | P |
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4 | Orius albidipennis (Reuter, 1884) | + | S | ** | TP |
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5 | Nabis ferus (Linnaeus, 1758) | Nabidae Costa, 1852 | ++ | FR | 0 | TP |
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6 | Nabis palifer (Seidenstücker, 1954) | + | F | *** | TS |
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7 | Nabis viridis (Brullé, 1839) | + | F | *** | SA |
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8 | Nabis rugosus (Linnaeus, 1758) | ++ | FR | *** | SA |
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9 | Nabis remanei (Kerzhner, 1962) | + | F | ** | ChCA |
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10 | Nabis sareptanus (Dohrn, 1862) | + | F | *** | TP |
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11 | Prostemma sanguineum (Rossi, 1790) | + | F | ** | PA |
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12 | Deraeocoris punctulatus (Fallén, 1807) | Miridae Hahn, 1833 | ++ | FR | 0 | P |
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13 | Deraeocoris serenus (Douglas & Scott, 1868) | ++ | FR | ** ** | W |
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14 | Adelphocoris lineolatus (Coeze, 1778) | +++ | A | 0 | TP |
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15 | Adelphocoris seticornis (Fabricius, 1775) | +++ | A | ** ** | W |
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16 | Agnocoris rubicundus (Fallen, 1807) | ++ | FR | *** | TP |
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17 | Brachycoleus decolor (Reuter, 1887) | ++ | FR | *** | W |
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18 | Lygus pratensis (Linnaeus, 1758) | +++ | A | 0 | SA |
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19 | Lygus gemellatus (Herrich-Schäffer, 1835) | +++ | A | 0 | TP |
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20 | Lygus pachycnemis (Reuter, 1879) | +++ | A | *** | TNT |
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21 | Lygus rugulipennis (Poppius, 1911) | +++ | A | ** ** | TP |
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22 | Lygus punctatus (Zetterstedt, 1838) | +++ | A | ** ** | TP |
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23 | Megacoelum brevirostre (Reuter, 1879) | ++ | FR | *** | TS |
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24 | Orthops basalis (Costa, 1853) | ++ | FR | *** | SA |
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25 | Orthops kalmi (Linnaeus, 1758) | ++ | FR | 0 | SA |
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26 | Polymerus vulneratus (Panzer, 1806) | +++ | A | 0 | TP |
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27 | Polymerus cognatus (Fieber, 1858) | +++ | A | ** | TP |
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28 | Notostira elongata (Geoffroy, 1785) | ++ | FR | ** ** | SA |
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29 | Megaloceroea recticornis (Geoffroy, 1785) | ++ | FR | ** ** | W |
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30 | Stenodema calcaratum (Fallen, 1807) | +++ | A | 0 | TP |
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31 | Stenodema tripsinosa (Reuter, 1904) | +++ | A | *** | TP |
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32 | Stenodema laevigata (Linnaeus, 1758) | +++ | A | *** | PA |
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33 | Stenodema turanica (Reuter, 1904) | ++ | FR | 0 | NC |
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34 | Trigonotylus ruficornis (Geoffroy, 1785) | ++ | FR | 0 | PA |
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35 | Trigonotylus pulchellus (Hahn, 1834) | ++ | FR | ** ** | P |
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36 | Orthotylus eleagni (Jakovlev, 1881) | ++ | FR | *** | TS |
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37 | Orthotylus flavosparsus (Sahlberg, 1841) | Miridae Hahn, 1833 | ++ | FR | *** | TP |
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38 | Campylomma annulicorne (Signoret, 1865) | ++ | FR | ** | P |
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39 | Campylomma diversicornis (Reuter, 1878) | +++ | A | *** | NS |
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40 | Campylomma verbasci (Meyer-Dur, 1843) | +++ | A | ** | PA |
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41 | Camptotylidea alba (Reuter, 1879) | ++ | FR | *** | TNT |
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42 | Camptotylus meyeri (Frey-Gessner, 1863) | ++ | FR | *** | NS |
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43 | Europiella alpina (Reuter, 1875) | ++ | FR | ** ** | TP |
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44 | Heterocapillus tigripes (Meyer & Dur, 1852) | + | F | * | SA |
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45 | Macrotylus herrichi (Reuter, 1873) | + | F | * | SA |
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46 | Tuponia elegans (Jakovlev, 1867) | ++ | FR | *** | SA |
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47 | Tuponia pallida (Jakovlev, 1867) | ++ | FR | *** |
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48 | Tuponia roseipennis (Reuter, 1889) | ++ | FR | *** | ChCA |
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49 | Tarajala brevicornis (Reuter, 1879) | – | – | – | – |
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50 | Monosteira discoidalis (Jakovlev, 1883) | Tingidae Laporte, 1832 | + | F | 0 | SA |
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51 | Stephanitis pyri (Fabricius, 1775) | + | F | ** ** | P |
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52 | Tingis leptochila (Horvath, 1906) | + | F | *** | ITCA |
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53 | Stenolemus bogdanovi (Oshanin, 1896) | Reduviidae Latreille, 1807 | + | F | *** | TS |
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54 | Coranus aegyptius (Fabricius, 1775) | ++ | FR | *** | SA |
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55 | Coranus subapterus (De Geer, 1773) | ++ | FR | ** | NS |
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56 | Rhynocoris monticola (Oshanin, 1870) | ++ | FR | *** | TS |
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57 | Rhinocoris nigronitens Reuter, 1881 | ++ | FR | *** | TS |
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58 | Vachiria deserta (Becker,1867) | + | F | ** ** | ITCA |
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59 | Ectomocoris ululans (Rossi, 1807) | + | F | *** | ETPE |
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60 | Reduvius testaceus (Herrich-Schäffer, 1845) | + | S | *** | TS |
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61 | Reduvius disciger (Horváth, 1896) | + | F | *** | TS |
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62 | Reduvius christophi (Jakovlev, 1874) | + | S | 0 | TS |
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63 | Reduvius fedtschenkianus (Oshanin, 1871) | + | F | 0 | TNT |
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64 | Reduvius semenovi (Jakovlev, 1885) | Reduviidae Latreille, 1807 | + | F | *** | TNT |
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65 | Reduvius elegans (Jakovlev, 1885) | ++ | FR | *** | TNT |
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66 | Oncocephalus brachymerus (Reuter, 1882) | ++ | FR | *** | TS |
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67 | Oncocephalus termezanus (Kiritshenko, 1914) | ++ | FR | ** | ITCA |
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68 | Camptopus lateralis (German, 1817) | Alydidae Amyot & Serville, 1843 | + | F | 0 | SA |
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69 | Megalotomus ornaticeps (Stål, 1858) | + | F | ** | NS |
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70 | Centrocoris volxemi (Puton, 1878) | Coreidae Leach, 1815 | + | F | *** | TS |
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71 | Coreus marginatus (Linnaeus, 1758) | + | S | *** | TP |
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72 | Enoplops eversmanni (Jakovlev, 1881) | + | F | *** | T |
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73 | Bathysolen nubilus (Fallen, 1807) | + | F | ** | TS |
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74 | Bothrostethus annulipes (Herrich-Schäffer, 1835) | + | S | ** | TS |
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75 | Coriomeris vitticollis (Reuter, 1900) | + | F | 0 | TS |
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76 | Brachycarenus tigrinus (Schilling, 1829) | Rhopalidae Amyot & Serville, 1843 | ++ | FR | 0 | TP |
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77 | Chorosoma schillingi (Schilling, 1829) | ++ | FR | *** | SA |
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78 | Corizus limbatus (Rey, 1887) | +++ | A | 0 | SA |
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79 | Corizus tetraspilus (Horvath, 1917) | +++ | A | ** | NS |
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80 | Corizus hyoscyami (Linnaeus, 1758) | +++ | A | *** | TP |
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81 | Maccevethus persicus (Jakovlev, 1882) | ++ | FR | *** | TS |
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82 | Liorhyssus hyalinus (Fabricius, 1794) | ++ | FR | 0 | C |
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83 | Rhopalus parumpunctatus (Schilling, 1829) | ++ | FR | *** | TP |
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84 | Rhopalus distinctus (Signoret, 1859) | ++ | FR | *** | TS |
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85 | Stictopleurus unicolor (Jakovlev, 1873) | ++ | FR | *** | W |
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86 | Dicranocephalus marginatus (Ferrari, 1874) | Stenocephalidae Dallas, 1852 | + | F | 0 | TS |
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87 | Dicranocephalus ferghanensis (Horváth, 1887) | + | F | 0 | TS |
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88 | Artheneis alutacea (Fieber, 1861) | Artheneidae Stål, 1872 | + | S | *** | W |
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89 | Geocoris ater (Fabricius, 1787) | Geocoridae Baerensprung, 1860 | ++ | FR | ** | TP |
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90 | Geocoris arenarius (Jakovlev, 1867) | + | F | ** | NS |
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91 | Geocoris dispar (Waga, 1839) | ++ | FR | ** | W |
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92 | Geocoris lapponicus (Zetterstedt, 1838) | + | F | ** ** | P |
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93 | Geocoris fedtschenkoi (Reuter, 1885) | + | F | *** | NS |
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94 | Geocoris scutellatus (Montandon, 1907) | + | F | *** | KNTIT |
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95 | Engistus salinus (Jakovlev, 1874) | + | F | *** | TS |
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96 | Engistus exsanguis (Stál, 1872) | ++ | FR | *** | TS |
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97 | Henestaris halophilus (Burmeister, 1835) | + | F | *** | W |
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98 | Lygaeus equestris (Linnaeus, 1758) | Lygaeidae Schilling, 1829 | ++ | FR | 0 | TP |
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99 | Spilostethus rubriceps (Horvath, 1899) | + | F | 0 | TS |
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100 | Spilostethus pandurus (Scopoli, 1763) | + | F | ** | TS |
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101 | Nysius graminicola (Kolenati, F.A., 1845) | ++ | FR | *** | SA |
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102 | Oxycarenus pallens (Herrich-Schäffer, 1850) | + | S | *** | SA |
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103 | Ortholomus punctipennis (Herrich-Schäffer, 1850) | ++ | FR | *** | P |
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104 | Beosus quadripunctatus (Muller, 1766) | Rhyparochromidae Amyot & Serville, 1843 | ++ | FR | ** | SA |
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105 | Bleteogonus beckeri (Frey-Gessner, 1863) | + | F | ** | TS |
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106 | Emblethis griseus (Wolff, 1802) | + | F | 0 | SA |
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107 | Emblethis verbasci (Fabricius, 1803) | + | F | 0 | SA |
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108 | Emblethis ciliatus (Horváth, 1875) | + | F | 0 | SA |
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109 | Emblethis denticollis (Horváth, 1878) | + | F | *** | P |
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110 | Emblethis dilaticollis (Jakovlev, 1874) | – | – | – | – |
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111 | Hyalocoris pilicornis (Jakovlev, 1874) | + | S | 0 | TS |
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112 | Lamprodema maura (Fabricius, 1803) | ++ | FR | 0 | W |
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113 | Aethus pilosulus (Klug, 1845) | Cydnidae Billberg, 1820 | + | F | 0 | TS |
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114 | Aethus nigronervosus (Melichar, 1906) | – | – | – | – |
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115 | Byrsinus fossor (Mulsant & Rey, 1866) | + | F | 0 | TP |
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116 | Microporus virgata (Fabricius, 1794) | – | – | – | – |
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117 | Microporus nigrita (Fabricius, 1794) | + | F | ** | ETPE |
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118 | Stibaropus hohlbecki (Kiritshenko, 1912) | + | F | ** | TNT |
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119 | Sehirus morio (Linnaeus, 1761) | + | F | *** | W |
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120 | Amaurocoris candidus (Horváth, 1889) | + | F | *** | TS |
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121 | Aelia acuminata (Linnaeus, 1758) | Pentatomidae Leach, 1815 | +++ | A | ** | W |
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122 | Aelia furcula (Fieber, 1868) | +++ | A | *** | TS |
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123 | Aelia melanota (Fieber, 1868) | +++ | A | ** | TS |
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124 | Brachynema germari (Kalenati, 1846) | ++ | FR | 0 | TP |
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125 | Carpocoris pudicus (Poda, 1761) | ++ | FR | *** | P |
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126 | Carpocoris fuscispinus (Boheman, 1851) | ++ | FR | 0 | W |
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127 | Palomena prasina (Linnaeus, 1761) | +++ | A | ** ** | SA |
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128 | Dolycoris penicillatus (Horváth, 1904) | +++ | A | 0 | TS |
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129 | Desertomenida quadrimaculata (Horváth, 1892) | +++ | A | *** | NS |
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130 | Desertomenida albula (Kiritshenko, 1914) | +++ | A | *** | TS |
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131 | Derula longipennis (Oshanin, 1871) | + | F | ** ** | TP |
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132 | Apodiphus integriceps (Horváth, 1888) | +++ | A | 0 | TS |
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133 | Cellobius abdominalis (Jakovlev, 1885) | ++ | FR | *** | NS |
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134 | Codophila varia (Fabricius, 1787) | ++ | FR | *** | SA |
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135 | Holcostethus nitidus (Kiritshenko, 1914) | ++ | FR | *** | TNT |
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136 | Holcostethus strictus vernalis (Wolff, 1804) | Pentatomidae Leach, 1815 | ++ | FR | ** | P |
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137 | Menaccarus deserticola (Jakovlev, 1900) | ++ | FR | *** | TS |
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138 | Eurydema ornata (Linnaeus, 1758) | +++ | A | *** | SA |
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139 | Eurydema oleracae (Linnaeus, 1758) | +++ | A | ** ** | SA |
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140 | Eurydema wilkinsi (Distant, 1879) | +++ | A | * | NS |
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141 | Eurydema ventralis (Kolenati, 1846) | +++ | A | ** ** | SA |
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142 | Eurydema maracandica (Oshanin, 1871) | +++ | A | ** | NS |
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143 | Graphosoma lineatum (Linnaeus, 1758) | ++ | FR | *** | SA |
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144 | Graphosoma consimile (Horvath, 1903) | ++ | FR | *** | TS |
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145 | Tarisa elevata (Reuter, 1901) | ++ | FR | *** | TS |
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146 | Tarisa subspinosa (Germar, 1839) | ++ | FR | *** | TP |
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147 | Tarisa virescens (Herrich-Schäffer, 1851) | ++ | FR | *** | NS |
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148 | Tarisa pallescens (Jakovlev, 1871) | ++ | FR | *** | TS |
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149 | Sciocoris helferi (Fieber, 1851) | – | – | – | – |
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150 | Eurygaster integriceps (Puton, 1881) | Scutelleridae Leach, 1815 | ++ | FR | 0 | P |
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151 | Odontotarsus impictus (Jakovlev, 1886) | + | F | 0 | TS |
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152 | Odontotarsus angustatus (Jakovlev 1883) | + | F | *** | TS |
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153 | Scantius aegyptius (Linnaeus, 1758) | Pyrrhocoridae Amyot & Serville, 1843 | + | F | 0 | NS |
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154 | Pyrrhocoris apterus (Linnaeus, 1758) | ++ | FR | 0 | W |
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Total number of species: 154 |
Entomologists (
The analysis of terrestrial Heteroptera in the Lower Amudarya by Gandjaeva (2007–
During 2007–2020, 149 species of terrestrial heteropterans were recorded in the Lower Amudarya territory as represented in Table
From the surveys, it has been established that approximately 30 species are abundant and numerous. Sixty-two species are frequent, eight are sometimes encountered, and 49 were recorded as few. They belong to 17 families, 89 genera and the most numerous are Miridae – 37 species and Pentatomidae – 28 species, followed by Reduviidae – 15; Rhopalidae – 10; Geocoridae – 9; Rhyparochromidae – 8; Nabidae – 7; Coreidae, Lygaeidae, Cydnidae – 6, Anthocoridae – 4. Other families are represented by not more than two or three species (Table
Distribution of the number of genera, species within families, as well as their percentage (%) in the fauna of terrestrial heteropterans.
Family | Number of genera | % | Number of species | % |
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Anthocoridae | 2 | 2.27 | 4 | 2.68 |
Nabidae | 2 | 2.27 | 7 | 4.70 |
Miridae | 20 | 21.59 | 37 | 24.16 |
Tingidae | 3 | 3.41 | 3 | 2.01 |
Reduviidae | 7 | 7.95 | 15 | 10.07 |
Alydidae | 2 | 2.27 | 2 | 1.34 |
Coreidae | 6 | 6.82 | 6 | 4.03 |
Rhopalidae | 7 | 7.95 | 10 | 6.71 |
Stenocephalidae | 1 | 1.14 | 2 | 1.34 |
Artheneidae | 1 | 1.14 | 1 | 0.67 |
Geocoridae | 3 | 3.41 | 9 | 6.04 |
Lygaeidae | 5 | 5.68 | 6 | 4.70 |
Rhyparochromidae | 5 | 5.68 | 8 | 5.37 |
Cydnidae | 6 | 6.82 | 6 | 4.03 |
Pentatomidae | 15 | 17.05 | 28 | 18.79 |
Scutelleridae | 2 | 2.27 | 3 | 2.01 |
Pyrrhocoridae | 2 | 2.27 | 2 | 1.34 |
Total: | 89 | 100 | 149 | 100 |
Recorded species belong to 11 types according to sector ranges, and 28 groups of areas according to belt ranges (Table
Type area | The sector and belt range | Number of species | Species | Percentage |
---|---|---|---|---|
I. Groups of wide areas | I.1. Cosmopolitan | 1 | Liorhyssus hyalinus; | 0.67 |
II. Holarctic | II.1. Trans-Palaearctic | 9 | 6.04 | |
a) Extratropical, Nearctic | 3 | Lygus rugulipennis, Orius albidipennis, Derula longipennis; | 2.01 | |
b) Boreal-subtropical, Nearctic | 3 | Agnocoris rubicundus, Lygus punctatus, Polymerus cognatus; | 2.01 | |
c) Boreal-subtropical | 2 | Polymerus vulneratus, Orthotylus flavosparsus; | 1.34 | |
d) Boreal – subboreal | 1 | Stenodema tripsinosa; | 0.67 | |
II.2. Pancontinental | 1 | 0.67 | ||
a) Extratropical | 1 | Deraeocoris punctulatus; | 0.67 | |
III. Palaearctic | III.1. Ethiopia – Trans-Palaearctic – Eastern | 2 | 1.34 | |
a) Southern | 2 | Ectomocoris ululans, Microporus nigrita; | 1.34 | |
III.2. Trans-Palaearctic | 16 | 10.74 | ||
a) Extratropical | 1 | Europiella alpina; | 0.67 | |
b) Arctic | 3 | Brachynema germari, Byrsinus fossor, Tarisa fraudatrix; | 2.01 | |
c) Boreal | 2 | Nabis ferus, Nabis sareptanus; | 1.34 | |
d) Boreal-subtropical | 9 | Orius niger, Adelphocoris lineolatus, Lygus gemellatus gemellatus, Stenodema calcaratum, Geocoris ater, Coreus marginatus, Brachycarenus tigrinus, Corizus hyoscyami hyoscyami, Rhopalus parumpunctatus; | 6.04 | |
e) Boreal-subboreal | 1 | Lygaeus equestris; | 0.67 | |
III.3. Super-Atlantic | 28 | 18.79 | ||
a) Arcto-Subboreal | 7 | Tuponia elegans, Tuponia pallida, Coranus aegyptius, Nysius graminicola graminicola, Emblethis griseus, Emblethis verbasci, Corizus limbatus; | 4.70 | |
b) Boreal-subboreal | 1 | Orthops basalis; | 0.67 | |
c) Boreal-subtropical | 7 | Lygus pratensis, Notostira elongata, Eurydema ornata, Eurydema oleracae, Palomena prasina, Orthops kalmi, Chorosoma schillingi; | 4.70 | |
d) Subboreal | 8 | Nabis rugosus, Nabis viridis Brullé, Heterocapillus tigripes, Macrotylus herrichi, Monosteira discoidalis, Beosus quadripunctatus, Codophila varia, Camptopus lateralis; | 5.37 | |
e) Subboreal-subtropical | 2 | Eurydema ventralis, Graphosoma lineatum; | 1.34 | |
f) Southern | 3 | Anthocoris pilosus, Oxycarenus pallens, Emblethis ciliatus; | 2.01 | |
III. 4. The Western | 13 | 8.72 | ||
a) Boreal | 2 | Deraeocoris serenus, Adelphocoris seticornis; | 1.34 | |
b) Boreal-subtropical | 5 | Lamprodema maura, Stictopleurus unicolor, Sehirus morio, Aelia acuminata, Carpocoris fuscispinus; | 3.36 | |
c) Boreal-subboreal | 2 | Pyrrhocoris apterus, Megaloceroea recticornis; | 1.34 | |
d) Subboreal | 3 | Artheneis alutacea, Brachycoleus decolor, Geocoris dispar; | 2.01 | |
e) Southern | 1 | Henestaris halophilus; | 0.67 | |
III. 5. Pan-Atlantic | 4 | 2.68 | ||
a) Boreal-subtropical | 2 | Stenodema laevigata, Campylomma verbasci; | 1.34 | |
b) Boreal-subboreal | 1 | Trigonotylus ruficornis; | 0.67 | |
c) Subboreal-subtropical | 1 | Prostemma sanguineum; | 0.67 | |
III. 6. Pancontinental | 10 | 6.71 | ||
a) Northern | 1 | Geocoris lapponicus; | 0.67 | |
b) Boreal-subtropical | 5 | Ortholomus punctipennis, Emblethis denticollis, Holcostethus strictus vernalis, Carpocoris pudicus, Trigonotylus pulchellus; | 3.36 | |
c) Subboreal | 1 | Orius ribauti; | 0.67 | |
d) Subboreal-subtropical | 1 | Eurygaster integriceps; | 0.67 | |
e) Southern | 2 | Campylomma annulicorne, Stephanitis pyri; | 1.34 | |
III. 7. Narrow Continental | 2 | 1.34 | ||
a) Eastern Mediterranean Gobian | 1 | Stenodema turanica; | 0.67 | |
b) Mediterranean-Irano-Turanian | 1 | Geocoris fedtschenkoi; | 0.67 | |
III. 8. The North Setian | 12 | 8.05 | ||
a) Trans-Scythian | 1 | Geocoris arenarius; | 0.67 | |
b) Western Scythian | 3 | Coranus subapterus, Campylomma diversicorne, Camptotylus meyeri; | 2.01 | |
c) Eastern Scythian | 8 | Corizus tetraspilus, Megalotomus ornaticeps, Desertomenida quadrimaculata, Cellobius abdominalis, Eurydema wilkinsi, Eurydema maracandica, Tarisa virescens, Scantius aegyptius; | 5.37 | |
III. 9. Tethyan-Siberian | 38 | 25.50 | ||
a) Western-Scythian-Saharo-Gobian | 1 | Stenolemus bogdanovi; | 0.67 | |
b) Euro-Mediterranean – Turanian | 10 | Spilostethus pandurus, Tarisa pallescens, Reduvius testaceus, Centrocoris volxemi, Bathysolen nubilus, Coriomeris vitticollis, Rhopalus distinctus, Engistus exsanguis, Aelia furcula, Graphosoma consimile; | 6.71 | |
c) Irano-Turanian-Gobian | 4 | Megacoelum brevirostre, Orthotylus eleagni, Oncocephalus brachymerus, Bothrostethus annulipes; | 2.68 | |
d) Irano-Turanian | 15 | Reduvius disciger, Reduvius christophi, Engistus salinus, Tarisa elevata, Desertomenida albula, Odontotarsus impictus, Odontotarsus angustatus, Amaurocoris candidus, Aelia melanota, Dolycoris penicillatus, Apodiphus integriceps, Menaccarus deserticola, Maccevethus corsicus persicus, Dicranomerus marginatus, Dicranomerus ferghanensis; | 10.07 | |
e) Kazakh-Northern Turanian, Irano-Turanian | 6 | Nabis palifer, Rhynocoris monticola monticola, Rhynocoris nigronitens, Spilostethus rubriceps, Bleteogonus beckeri, Geocoris scutellatus; | 4.03 | |
f) Tethys-Ethiopian | 2 | Hyalocoris pilicornis, Aethus pilosulus; | 1.34 | |
IV. Endemics | IV. Endemics | 13 | 8.72 | |
a) Chinese-Central Asian | 2 | Nabis remanei, Tuponia roseipennis; | 1.34 | |
b) Chinese-Irano-Central Asian | 1 | Reduvius fedtschenkianus; | 0.67 | |
c) Turkestanian-Northern Turanian | 6 | Stibaropus hohlbecki, Holcostethus nitidus, Lygus pachycnemis, Camptotylidea alba, Reduvius semenovi, Reduvius elegans; | 4.03 | |
d) Irano-Turanian-Central Asian | 3 | Vachiria deserta, Tingis leptochila, Oncocephalus termezanus; | 2.01 | |
e) Turanian | 1 | Enoplops eversmanni; | 0.67 | |
Total: | 149 | 100 |
In the northern part of Uzbekistan, only one species (0.67%) is cosmopolitan. The group of the Holarctic range is characterized by no more than ten species, which constitutes 6.71% of the total, and most species belong to the Palaearctic group, which is most diverse. The group contains 125 species (83.89%), with 38 from the Tethyan-Siberian type constituting 25.50%. Approximately 15 species account for 10.07% of the Irano-Turanian range, while ten species constitute 6.71% of the Euro-Mediterranean-Turanian range. In the Super-Atlantic range, 28 species account for 18.79%, with eight species making up 5.37% of subboreal and seven species accounting for 4.70% of boreal-subtropical species recorded. Sixteen Trans-Palaearctic species (10.74%) have been recorded, followed by 13 Western (8.72%), 12 North Setian (8.05%), ten Pancontinental (6.71%), and four Pan-Atlantic (2.68%) species. The number of species with Ethiopia-Trans-Palaearctic-Eastern distributions and Narrow Continental is only two for each area or 1.34%. It can be seen that the prevailing part of the group,125 species (83.89%), were found in wider areas of the Holarctic, and 13 are endemic species (8.72%).
The endemics are divided into Chinese-Central Asian, Chinese-Irano-Central Asian, Turkestanian-Northern Turanian, Irano-Turanian-Central Asian, and Turanian (found in Central Asia only). For the assessment of any territory, endemics have a high conservation value since they indicate the distinctive nature of the fauna.
In this study, we collected new 39 species for the Khorezm region and 87 species for the Republic of Karakalpakstan during 2007–2020. In addition, we compare our collections with reports of
The Heteroptera fauna of Khorezm and Karakalpakstan can be divided into four groups: Cosmopolitan with one species (0.67%); Holarctic, with no more than ten species, or 6.71%; Palaearctic, with most of species (125 species, or 83.89%); and endemic with 13 species, or 8.72%.
An understanding of the fauna is important, as the productivity of crops is currently being negatively impacted by invasive species from neighboring countries. For example, recently we recorded (
The authors express their warm gratitude to Dr. M. Ahmed for checking the English version of the manuscript, to Dr. M. Sultonov for producing the map of the study area and sampling locations, and to the team from the Zoology Institute (ZIN) of the Uzbekistan Academy of Sciences (UAS) for their assistance.