Кавказский энтомологический бюллетень 15(1): 135–146 © Caucasian Entomological Bulletin 2019
Süleyman Demirel University, Isparta, Turkey. E-mail: aligok32@gmail.com, ergin_859_taurus@hotmail.com Университет Сулеймана Демиреля, Ыспарта, Турция
Key words: Coleoptera, Chrysomelidae, species composition, Hatila Valley National Park, Artvin, Turkey.
Ключевые слова: Coleoptera, Chrysomelidae, видовой состав, национальный парк «Долина Хатилы», Артвин, Турция.
Abstract. The first detailed data on species composition of leaf beetles of Hatila Valley National Park, Artvin, Turkey are presented. During the field surveys conducted in 2015, in total 49 species of Chrysomelidae from 26 genera belonging to 7 subfamilies were registered. Among them, 30 species are recorded for the first time from Artvin Province. The subfamily Galerucinae is the most diverse and includes 23 species in the park (18 – Alticini, 4 – Galerucini and 1 – Luperini), however two subfamilies, Criocerinae and Eumolpinae, are represented by only one species each. The genus Cryptocephalus Geoffrey, 1762 is the most diverse (7 species), followed by Cassida Linnaeus, 1758 (6),
Chrysolina Motschulsky, 1860 (5), Altica Geoffrey, 1762 (4),
Longitarsus Latreille, 1829 (4), Phyllotreta Chevrolet,
1836 (2) and Batophila Foudras, 1860 (2). The remaining genera are represented by only one species.
The brief information on activity periods, host plant preferences and distribution of each species collected from the area is given and discussed in detail. The results based on our material showed that Hatila Valley National Park has a low species composition in terms of leaf beetles and the faunal structure of leaf beetles was not as high as expected.
Резюме. Приведены первые подробные сведения о видовом составе листоедов национального парка
«Долина Хатила», провинция Артвин, Турция. Результаты наших исследований, проведенных в 2015 году, показали, что видовой состав листоедов национального парка «Долина Хатилы» характеризуется невысоким разнообразием: было зарегистрировано 49 видов Chrysomelidae из 26 родов, принадлежащих к 7 подсемействам. Среди них
30 видов впервые указаны для провинции Артвин. Наибольшим количеством видов (23) представлено подсемейство Galerucinae (18 – Alticini, 4 – Galerucini
Research Article / Научная статья
DOI: 10.23885/181433262019151-135146
и 1 – Luperini), наименьшим (по одному виду) – подсемейства Criocerinae и Eumolpinae. Род с самым большим количеством видов – Cryptocephalus Geoffrey, 1762 (7 видов), за ним следуют Cassida Linnaeus, 1758
(6 видов), Chrysolina Motschulsky, 1860 (5 видов),
Altica Geoffrey, 1762 (4 вида), Longitarsus Latreille, 1829
(4 вида), Phyllotreta Chevrolet, 1836 (2 вида) и Batophila Foudras, 1860 (2 вида). Остальные роды представлены одним видом каждый.
Дана краткая информация о периодах активности жуков, кормовых растениях и распространении каждого вида.
Hatila Valley National Park (HVNP) is located in Artvin Province in northestern Turkey and is one of the most popular national parks in Turkey. It was declared a national park in 1994 due to unusual geomorphological structure and geology, which has created a distinctive landscape. The park covers an area of about 16944 hectare and represents all features of Colchic flora. The altitude of the area varies from 140 to 3241 m a.s.l. [Milliparklar, 2017]. The lower parts of the valley are dry and warm but the higher parts are cool and humid with snow cover in winter. The area is close to the Black Sea and has a Mediterranean climate with warm summers, cool winters and plentiful rainfall throughout the year. The valley is densely vegetated, especially in its middle and lower sections and therefore provides various habitats for a wide variety of plant and animal species [National Parks..., 2017].
Although the area is in European-Siberian flora region, plant species of Mediterranean flora can be seen at the lower parts by the help of microclimate formed by Çoruh valley. This situation leads to an increase in the biological
diversity of the valley [Milliparklar, 2017]. The park and its close environs are represented by 769 plant taxa belonging to 374 genera and 95 families [Eminağaoğlu, Anşin, 2003]. The forests in the park consist of both deciduous and coniferous tree species. These include sessile oak, eastern spruce, monumental spruce, fir, chesnut and linden, such as hornbeam, alder, beech, willow, birch and common apsen [Milliparklar, 2017].
Leaf beetles (Coleoptera: Chrysomelidae) is one of the most conspicuous groups of phytophagous beetles due to their food habits on the plants. Many species are quite host- specific, feeding only on a single plant species or on several closely related plants. However, others are generalists that feed on a wide variety of plants. Adult leaf beetles consume plants in a great variety of ways, but frequently by direct eating of the living foliage [Jolivet, Verma, 2002; Clark et al., 2004].
There is no work on the leaf beetle fauna of HVNP until now. Our knowledge on the beetle species in this park is limited to very scattered and incomplete collections. Therefore, it is necessary to determine the species of this group which is very closely related to the plants. The objectives of the present paper are to investigate the fauna and species composition, provide detailed distributional and some ecological data (host plant, phenology etc.) on the leaf beetles of HVNP.
Field surveys were conducted in May – September 2015. The sampling areas which are represented different habitat types in HVNP were selected and the samplings were performed in fine weather (at approximately 9:00 to 16:00 h). Adults were collected from various plants, shrubs and trees by means of sweep net and aspirator. Collected specimens were killed with ethyl acetate in poison bottles. The specimens were taken to the laboratory for dissection and identification. The prepared specimens were deposited at the Biology Department of Süleyman Demirel University (Isparta, Turkey). Plants showing feeding marks on the leaves by the adults were considered as a host plant. The species recorded for the first time in Artvin Province are given with the asterisk (*) in Table 1.
Identification was performed mainly based on the keys of Mohr [1966] and Warchałowski [2003, 2010]. The subfamilies and genera are listed according to the Catalogue of the Palaearctic Coleoptera [2010].
Oulema obscura (Stephens, 1831)
Material. 1♂, 1.09.2015.
Cassida bella Falderman, 1837
Material. 2♂, 19.05.2015; 1♀, 20.06.2015; 9♂, 13♀, 2.07.2015; 1♀,
20.07.2015; 1♂, 21.08.2015; 1♀, 27.08.2015.
Cassida inquinata Brullé, 1832
Material. 3♂, 16.05.2015.
Cassida prasina Illiger, 1798
Material. 1♀, 1.06.2015; 1♂, 2.06.2015; 1♂, 2♀, 10.06.2015; 1♀,
20.06.2015.
Cassida rubiginosa Müller, 1776
Material. 1♂, 23.05.2015; 1♂, 2♀, 2.07.2015; 1♂, 8.07.2015.
Cassida vibex Linnaeus, 1767
Material. 1♂, 1♀, 1.06.2015; 2♂, 1♀, 2.07.2015; 1♂, 2♀, 21.08.2015; 1♂, 1♀, 22.08.2015; 1♂, 1.09.2015.
Table 1. Leaf beetle species of Hatila Valley National Park: activity periods, altitude distribution, number of collected specimens and distribution in Turkey.
Таблица 1. Листоеды национального парка «Долина Хатилы»: периоды активности, высотное распределение, количество найденных особей и распространение в Турции.
Species Вид | Activity period (months) / Период активности (месяцы) | Altitude distribution / Высотное распределение | Number of specimens / Количество экземпляров | Distribution in Turkey Распространение в Турции |
CRIOCERINAE | ||||
Lemini | ||||
Oulema obscura* | September сентябрь | I | 1 | CAR, EAR, EBS, WBS |
CASSIDINAE | ||||
Cassida bella | May – August май – август | III | 28 | AEG, MAR, MED, EBS, WBS |
C. inquinata* | May май | I, II | 3 | AEG, CAR, MAR, CBS, EBS |
C. prasina* | June июнь | II | 6 | AEG, CAR, EAR, SAR, MAR, MED, WBS, EBS |
C. rubiginosa* | May, July май, июль | II | 5 | AEG, CAR, EAR, MAR, MED, WBS, CBS, EBS |
C. vibex* | June – September июнь – сентябрь | II | 11 | AEG, CAR, MED, WBS, CBS, EBS |
C. viridis* | May – August май – август | II | 11 | AEG, CAR, EAR, SAR, MAR, MED, WBS, CBS, EBS |
Hypocassida cornea* | June июнь | I | 2 | EBS |
CHRYSOMELINAE | ||||
Chrysomelini | ||||
Chrysolina adzharica heinzi | May – September май – сентябрь | II | 33 | EBS |
Ch. chalcites | June июнь | II | 1 | AEG, CAR, SAR, MAR, MED, WBS, CBS, EBS |
Ch. coerulans angelica | July – September июль – сентябрь | III | 38 | AEG, EAR, SAR, MED, EBS |
Ch. herbacea | May – September май – сентябрь | II, III | 75 | AEG, CAR, EAR, MAR, MED, WBS, CBS, EBS |
Ch. polita | May, August май, август | I, II | 3 | CAR, EAR, SAR, MAR, MED, WBS, CBS, EBS |
Gastrophysa viridula | September сентябрь | IV | 3 | EAR, EBS |
Leptinotarsa decemlineata | June июнь | I, II | 7 | AEG, CAR, EAR, MAR, MED, WBS, CBS, EBS |
Phratora coerulescens* | May, August – September май, август – сентябрь | III | 54 | EAR, MED, EBS |
Timarchini | ||||
Timarcha hummeli | August август | III | 1 | EBS |
GALERUCINAE | ||||
Alticini | ||||
Altica carduorum | May – July, September май – июль, сентябрь | I | 38 | CAR, EAR, MAR, CBS, EBS |
A. impressicollis | May – June, September май – июнь, сентябрь | I | 14 | CAR, EAR, MAR, MED, CBS, EBS |
A. oleracea* | May – September май –сентябрь | I | 59 | CAR, EAR, MAR, MED WBS, CBS, EBS |
A. quercetorum* | May – June, August – September май – июнь, август – сентябрь | I | 10 | AEG, MAR, MED, EBS |
Aphthona rugipennis* | July июль | III | 4 | EAR, EBS |
Table 1 (continuation).
Таблица 1 (продолжение).
Species Вид | Activity period (months) / Период активности (месяцы) | Altitude distribution / Высотное распределение | Number of specimens / Количество экземпляров | Distribution in Turkey Распространение в Турции |
Batophila fallax | May – June, September май – июнь, сентябрь | III | 19 | CAR, EAR, MAR, MED, WBS, CBS, EBS |
B. rubi* | May, August – September май, август – сентябрь | III | 16 | EBS |
Chaetocnema scheffleri* | June июнь | III | 1 | AEG, EAR, CAR, MAR, MED, EBS |
Crepidodera aurea* | May, July – September май, июль – сентябрь | III | 9 | CAR, EAR, MAR, MED, WBS, CBS, EBS |
Epitrix pubescens* | May, September май, сентябрь | III | 3 | AEG, CAR, EAR, MAR, WBS, EBS |
Longitarsus anchusae* | May, September май, сентябрь | III | 17 | EAR, MAR, MED, WBS, EBS |
L. aramaicus* | May – June, August – September май – июнь, август – сентябрь | III | 20 | CAR, MED, EBS |
L. luridus | May, July – September май, июль – сентябрь | III | 107 | CAR, EAR, MAR, MED, EBS |
L. nasturtii* | July – August июль – август | III | 80 | AEG, MED, EBS |
Neocrepidodera ferruginea* | June – July, September июнь – июль, сентябрь | III | 10 | CAR, EAR, MAR, MED, EBS |
Phyllotreta cruciferae* | May май | III | 2 | AEG, CAR, EAR, MAR, MED, CBS, EBS |
P. undulata* | June – July июнь – июль | III | 18 | CAR, EAR, MAR, EBS |
Psylliodes napi* | May – June, August – September май – июнь, август – сентябрь | IV | 8 | AEG, CAR, EAR, MED, EBS |
Galerucini | ||||
Agelastica alni | May – August май – август | II | 33 | AEG, CAR, EAR, MAR, MED, WBS, EBS |
Galeruca circassica* | June, August – September июнь, август – сентябрь | IV | 32 | CAR, EAR, MAR, MED, WBS, CBS, EBS |
Lochmaea caprea* | May, August май, август | IV | 11 | AEG, CAR, EAR, MAR, MED, CBS, EBS |
Xanthogaleruca luteola* | May май | I | 1 | AEG, CAR, EAR, MAR, MED, WBS, CBS, EBS |
Luperini | ||||
Phyllobrotica elegans* | June июнь | III | 1 | MAR, MED, WBS, EBS |
CRYPTOCEPHALINAE | ||||
Clytrini | ||||
Smaragdina vaulogeri* | May – July май – июль | I | 39 | MED, SAR, EBS |
Cryptocephalini | ||||
Cryptocephalus transcaucasicus | June – August июнь – август | III | 43 | AEG, CAR, EAR, MAR, MED, WBS, EBS |
C. duplicatus | September сентябрь | III | 1 | AEG, CAR, EAR, SAR, MAR, MED, WBS, CBS, EBS |
C. elegantulus* | June июнь | III | 4 | CAR, EBS |
C. moraei | May – September май – сентябрь | III | 39 | AEG, CAR, EAR, SAR, MAR, MED, WBS, CBS, EBS |
C. ocellatus | May – July, September май – июнь, сентябрь | III | 4 | AEG, CAR, EAR, SAR, MAR, MED, WBS, CBS, EBS |
C. praticola | June – August июнь – август | III | 57 | EAR, MAR, CBS, EBS |
Table 1 (completion).
Таблица 1 (окончание).
Species Вид | Activity period (months) / Период активности (месяцы) | Altitude distribution / Высотное распределение | Number of specimens / Количество экземпляров | Distribution in Turkey Распространение в Турции |
C. sexpunctatus* | May, September май, сентябрь | I | 3 | EAR, CBS, EBS |
EUMOLPINAE | ||||
Bromiini | ||||
Bromius obscurus* | September сентябрь | III | 1 | MED, EBS |
2013]. It is known that this species has a distribution in western and central parts of Turkey up to now. It is recorded for the first time from Artvin Province.
Cassida viridis Linnaeus, 1758
Material. 1♀, 18.05.2015; 1♂, 1♀, 21.05.2015; 2♀, 10.06.2015; 1♂,
20.06.2015; 1♀, 2.07.2015; 2♂, 2♀, 21.08.2015.
regions of Turkey [Ekiz et al., 2013]. It is recorded for the first time from Artvin Province.
Hypocassida cornea (Marseul, 1868)
Material. 1♂, 1♀, 20.06.2015.
Chrysolina adzharica heinzi Kippenberg, 2012
Material. 1♂, 18.05.2015; 1♂, 1♀, 21.05.2015; 8♂, 5♀, 10.06.2015; 8♂, 5♀, 2.07.2015; 1♂, 6.08.2015; 1♀, 21.08.2015; 1♂, 1♀, 1.09.2015.
Chrysolina chalcites (Germar, 1823)
Material. 1♂, 1.06.2015.
Chrysolina coerulans angelica (Reiche et Saulcy, 1858)
Material. 8♂, 3♀, 2.07.2015; 4♂, 1♀, 21.08.2015; 1♀, 25.08.2015; 9♂, 11♀, 30.08.2015; 1♀, 1.09.2015.
Özdikmen, 2014] and Israel [Friedman, 2016]. According to Ekiz et al. [2013], in Turkey it has been recorded from İzmir, Antalya, Ankara, Mersin, Hatay, Kahramanmaraş, Erzincan, Erzurum, Artvin and Kars provinces.
Chrysolina herbacea (Duftschmid, 1825)
Material. 1♀, 23.05.2015; 12♂, 16♀, 10.06.2015; 7♂, 15♀, 2.07.2015;
6♂, 6♀, 21.08.2015; 1♂, 22.08.2015; 2♂, 25.08.2015; 1♂, 1♀, 30.08.2015; 7♀,
1.09.2015.
longifolia and Urtica sp., which grow in moist areas in stream banks at 750–1600 m elevations.
Distribution. It is an Eurasian species widely distributed in Europe, Asia Minor, Caucasian countries, North Iran and Central Asia [Rozner, Rozner, 2014]. The species has a very wide distribution in Turkey including almost all Anatolia [Ekiz et al., 2013]. It is probably the most widespread species of Chrysolina Motschulsky, 1860 in Turkey.
Chrysolina polita (Linnaeus, 1758)
Material. 1♂, 1♀, 21.05.2015; 1♂, 26.08.2015.
Gastrophysa viridula (De Geer, 1775)
Material. 1♂, 2♀, 1.09.2015.
Leptinotarsa decemlineata (Say, 1824)
Material. 1♂, 6♀, 10.06.2015.
Phratora coerulescens Küster, 1848
= Phratora horioni (Mohr, 1966): Kippenberg, 2018: 20.
Material. 27♂, 18♀, 23.05.2015; 1♂, 1♀, 21.08.2015; 1♀, 22.08.2015;
3♂, 3♀, 1.09.2015.
Timarcha hummeli Faldermann, 1837
Material. 1♂, 26.08.2015.
Altica carduorum Guérin-Meneville, 1858
Material. 1♂, 1♀, 16.05.2015; 1♂, 2♀, 18.05.2015; 1♂, 3♀, 21.05.2015; 4♂, 8♀, 23.05.2015; 1♀, 2.06.2015; 3♀, 10.06.2015; 1♀, 20.06.2015; 1♀,
2.07.2015; 3♂, 8♀, 1.09.2015.
Altica impressicollis (Reiche, 1862)
Material. 1♀, 23.05.2015; 4♂, 6♀, 4.06.2015; 1♂, 2♀, 1.09.2015.
Isparta, Antalya, Samsun, Kayseri, Erzurum and Artvin provinces.
Altica oleracea (Linnaeus, 1758)
Material. 3♂, 5♀, 16.05.2015; 4♂, 6♀, 18.05.2015; 1♀, 19.05.2015;
4♂, 7♀, 26.05.2015; 1♀, 10.06.2015; 1♀, 20.06.2015; 1♀, 7.07.2015; 1♂, 2♀,
22.08.2015; 1♀, 27.08.2015; 1♀, 30.08.2015; 9♂, 12♀, 1.09.2015.
Altica quercetorum Foudras, 1860
Material. 1♂, 2♀, 23.05.2015; 1♀, 10.06.2015; 2♀, 21.08.2015; 1♂, 3♀, 1.09.2015.
1997]. This species has been reported from İzmir, İstanbul,
Isparta, Antalya, and Osmaniye provinces of Turkey [Ekiz et al., 2013]. It is recorded for the first time from Artvin Province.
Aphthona rugipennis Oglogbin, 1926
Material. 4♀, 8.07.2015.
Batophila fallax Weise, 1888
Material. 1♂, 1♀, 19.05.2015; 1♀, 20.06.2015; 7♂, 9♀, 1.09.2015.
from Sakarya, Bolu, Eskişehir, Isparta, Ordu, Giresun, Rize, Artvin and Erzurum provinces [Ekiz et al., 2013].
Batophila rubi (Paykull, 1799)
Material. 1♂, 1♀, 19.05.2015; 2♂, 3♀, 23.08.2015; 4♂, 5♀, 1.09.2015.
Chaetocnema scheffleri (Kutschera, 1864)
Material. 1♀, 4.06.2015.
Crepidodera aurea (Geoffroy, 1785)
Material. 1♀, 26.05.2015; 3♂, 1♀, 2.07.2015; 1♀, 23.08.2015; 3♀,
1.09.2015.
Epitrix pubescens (Koch, 1803)
Material. 1♀, 21.05.2015; 2♀, 1.09.2015.
Longitarsus anchusae (Paykull 1799)
Material. 2♀, 18.05.2015; 6♂, 9♀, 1.09.2015.
Longitarsus aramaicus Leonardi, 1979
Material. 1♀, 21.05.2015; 2♀, 18.06.2015; 6♂, 8♀, 21.08.2015; 1♂, 1♀, 22.08.2015; 1♀, 1.09.2015.
Longitarsus luridus (Scopoli 1763)
Material. 1♂, 21.05.2015; 1♀, 2.07.2015; 3♂, 1♀, 7.07.2015; 1♂, 3♀, 21.08.2015; 20♂, 37♀, 23.08.2015; 1♂, 25.08.2015; 1♂, 27.08.2015; 1♂,
30.08.2015; 14♂, 23♀, 1.09.2015.
Rozner, Rozner, 2008, 2014; Baviera, Biondi, 2015]. Similarly, it is a very common and widespread species in Turkey [Ekiz et al., 2013].
Longitarsus nasturtii Fabricius, 1792
Material. 21♂, 41♀, 7.07.2015; 5♂, 8♀, 22.08.2015; 2♂, 3♀, 25.08.2015.
Province).
Neocrepidodera ferruginea (Scopoli, 1763)
Material. 1♂, 20.06.2015; 4♀, 2.07.2015; 1♀, 7.07.2015; 1♂, 3♀,
1.09.2015.
recently [LeSage, Savard, 2012]. The species is known from Sakarya, Isparta, Antalya, Ankara, Konya, Kayseri and Erzurum provinces of Turkey [Ekiz et al., 2013]. It is recorded for the first time from Artvin Province.
Phyllotreta cruciferae (Goeze, 1777)
Material. 1♀, 16.05.2015; 1♀, 26.05.2015.
from Artvin Province.
Phyllotreta undulata (Kutschera, 1860)
Material. 4♂, 8♀, 10.06.2015; 2♂, 4♀, 2.07.2015.
Erzurum provinces of Turkey [Ekiz et al., 2013] and is recorded for the first time from Artvin Province.
Psylliodes napi (Fabricius, 1792)
Material. 1♀, 26.05.2015; 3♂, 2♀, 18.06.2015; 1♀, 25.08.2015; 1♀,
1.09.2015.
2013, 2014]. This species is also known from North America [Clark et al., 2004]. Its range in Turkey includes Manisa, Isparta, Antalya, Ankara, Kayseri, Adana and Erzurum provinces [Ekiz et al., 2013], and it is recorded for the first time from Artvin Province.
Agelastica alni (Linnaeus, 1758)
Material. 6♂, 15♀, 18.05.2015; 1♂, 4♀, 24.05.2015; 2♀, 26.05.2015;
1♂, 10.06.2015; 1♀, 2.07.2015; 2♂, 1♀, 30.08.2015.
Galeruca circassica Reitter, 1899
Material. 3♂, 4.06.2015; 2♀, 10.06.2015; 2♂, 20.06.2015; 6♂, 9♀,
22.08.2015; 2♂, 8♀, 1.09.2015.
Lochmaea caprea (Linnaeus, 1758)
Material. 2♂, 3♀, 23.05.2015; 1♂, 5♀, 21.08.2015.
Xanthogaleruca luteola (Müller, 1766)
Material. 1♀, 18.05.2015.
Phyllobrotica elegans Kraatz, 1866
Material. 1♀, 20.06.2015.
Armenia, Azerbaijan, Turkey, Syria, Lebanon and Israel [Bezděk, 2010]. It has been reported from İstanbul, Bursa, Bolu, Isparta, İçel, Osmaniye and Erzurum provinces of Turkey [Ekiz et al., 2013] and is recorded for the first time from Artvin Province.
Material. 1♀, 18.05.2015; 1♀, 1.06.2015; 1♂, 2.06.2015; 15♂, 17♀,
20.06.2015; 2♂, 2♀, 2.07.2015.
Cryptocephalus transcaucasicus Jakopson, 1898
Material. 4♂, 8♀, 20.06.2015; 9♂, 7♀, 2.07.2015; 8♂, 7♀, 25.08.2015.
Azerbaijan, European Russia, Georgia, Armenia, Turkey, Jordan, Iran [Sassi, 2014]. Similarly, it is a common and widespread species especially in northern Turkey [Ekiz et al., 2013].
Cryptocephalus duplicatus Suffrian, 1847
Material. 1♂, 1.09.2015.
Cryptocephalus elegantulus Gravenhorst, 1807
Material. 2♂, 2♀, 20.06.2015.
and Giresun provinces [Ekiz et al., 2013] and the species is recorded for the first time from Artvin Province in this study.
Cryptocephalus moraei (Linnaeus, 1758)
Material. 1♂, 23.05.2015; 5♂, 3♀, 20.06.2015; 6♂, 13♀, 2.07.2015; 1♂, 1♀, 7.07.2015; 2♂, 2♀, 21.08.2015; 1♀, 22.08.2015; 3♂, 1♀, 1.09.2015.
Cryptocephalus ocellatus Drapiez, 1819
Material. 1♀, 21.05.2015; 1♀, 20.06.2015; 1♂, 2.07.2015; 1♀,
1.09.2015.
Cryptocephalus praticola Weise, 1889
Material. 8♂, 12♀, 20.06.2015; 25♂, 11♀, 2.07.2015; 1♂, 21.08.2015.
northern parts of Turkey [Sassi, 2014]. In Turkey, its range includes Kırklareli, Samsun, Rize, Artvin, Erzurum and Kars provinces [Ekiz et al., 2013].
Cryptocephalus sexpunctatus (Linnaeus, 1758)
Material. 1♀, 18.05.2015; 2♀, 1.09.2015.
[Gruev, 2004]. Its distribution in Turkey is very limited, and the species is only known from Tokat and Erzurum provinces [Ekiz et al., 2013] and is recorded for the first time from Artvin Province in this study.
Bromius obscurus (Linnaeus, 1758)
Material. 1♀, 1.09.2015.
common in Europe and North America [An et al., 2014]. However, this species shows a very limited distribution in Turkey and only known from Osmaniye up to now [Ekiz et al., 2013] and is recorded for the first time from Artvin Province in this study.
Faunistic composition of leaf beetles of HVNP. In total 49 leaf beetle species from 26 genera representing 7 subfamilies were collected from HVNP during May – September 2015 (Table 1). It was found that the subfamily Galerucinae has the largest number of species and is represented by 23 species (18 – Alticini, 4 – Galerucini and 1 – Luperini) in the park, however the Criocerinae and Eumolpinae subfamilies are represented by only one species each. The genus with the highest number of species was Cryptocephalus Geoffrey, 1762 (7 species),
Fig. 1. Species numbers by months in 2015. Рис. 1. Число видов по месяцам в 2015 году.
followed by Cassida Linnaeus, 1758 (6), Chrysolina (5),
Altica Geoffrey, 1762 (4), Longitarsus Latreille, 1829 (4), Phyllotreta Chevrolet, 1836 (2) and Batophila Foudras, 1860 (2). The remaining genera are represented by only one species.
Phenologic properties of leaf beetles of HVNP. The highest number of species (28) was collected in May and the least (20) in July (Fig. 1). It was found that the species with the longest activity period are Chrysolina adzharica heinzi, Ch. coerulans angelica, Ch. herbacea, Altica oleracea, Cryptocephalus aureolus and C. praticola, collected from May to September (Table 1). This results indicate that some of the most abundant species in the area have the longest activity.
Host plant preferences of leaf beetles of HVNP. It was observed that the leaf beetles are mainly associated with various herbaceous vegetations belonging to Lamiaceae, Asteraceae, Fabaceae, Hypericaceae and Polygonaceae, and also the woody vegetations of Salicaceae, Fagaceae and Betulaceae. The host plant of 16 species collected in the studied area were precisely determined. Among them, the host plant of Chrysolina adzharica heinzi, which is described recently, is reported for the first time in this study and thus were contributed to the information about the host plant of the subspecies. Also, it was found that the species belonging to the genus Mentha, which grow on the edge of the stream, were the most preferred host plants by five leaf betle species. While the host plants of 16 leaf beetle species were precisely detected, host plants of the remaining species were not identified.
Zoogeographical composition of leaf beetles of HVNP. It was determined that the leaf beetles collected from HVNP are primarily associated with the fauna of two major areas: Europe and Central Asia. Also, it was found that a large part of the species obtained in the study are widely distributed species especially in Europe. Other species are distributed across the Caucasus, Anatolia and Middle East (Table 1).
The results indicate that numerous species collected during this study typically occur in central and southern parts of Europe and the Mediterranean region. Also, four species with the Caucasian and northern Anatolian distribution were found in the area (Cassida bella, Phratora coerulescens, Timarcha hummeli and Galeruca circassica); two species with Middle Eastern distribution (Longitarsus aramaicus and Smaragdina vaulogeri); only one species with Pontic distribution (Batophila fallax).
So far, the leaf beetles of Hatila Valley National Park has not been systematically studied, especially lacking knowledge about detailed fauna and species composition, activity period, host plant preference and zoogeographic composition information. This paper is the first detailed study on the species composition and some ecological features of leaf beetles in HVNP.
In the study presented here, 49 species in 26 genera and 7 subfamilies (982 specimens) were recorded. It was observed that many of the species found in the field are quite widespread and common species in Turkey. The others (8 species) have a relatively narrow distribution area or are known only from this region.
Results presented here establish baseline data for faunistic composition and some ecological characteristics of leaf beetles of HVNP and can serve as a reference study for future work and can offer supporting data for future research.
This study was supported by Scientific Research Project Management of Süleyman Demirel University (SDÜBAP) with project number 4270-YL1-15.
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Received / Поступила: 10.12.2018 Accepted / Принята: 12.02.2019