© Entomologica Fennica. 11 October 2006

Ground assemblages of dolomitic grasslands in

Csaba Kutasi & Gyfizfi Szél

Kutasi, Cs. & Szél, Gy. 2006: assemblages of dolomitic grass- lands in Hungary. — Entomol. Fennica 17: 253—257.

The carabid assemblages of dolomitic grasslands were investigated in the Transdanubian Mountains in Central Hungary using pitfall trapping between 1988 and 2005. A total of25 1 5 indvidual adult carabids, belonging to 65 species were collected from five localities. The most abundant species were Calathus ambiguus (24.5%), C. cinctus (16.8%) and C.fusc1pes (8.4%). Rare species were Amara proxima, A. sollicita, axillaris, C. variolosa, Licinus cassideus and Masoreus wetterhallii. The seasonal activity ofadult hungaricus is given.

C. Kutasi, Department ofZoology, Natural History Museum ofBakony Moun— tains, H—8420 Zirc, Rakéczi tér 1, Hungary; E—mail.‘ entomologia@bak0ny— museum.koznet.hu G. Szél, Department ofZoology, Hungarian Natural History Museum, H—1088 Budapest, Baross u. 13, Hungary; E—mail.‘ [email protected] Received 14 December 2005, accepted 8 June 2006

1. Introduction acteristic and frequent carabids of dolomitic slopes of one locality, the Odvas-hegy (Buda The fauna of the dolomitic grasslands of Mountains) have been published (Szél & Adam the southern slopes of mountains in Hungary is 1992) important for the conservation of biodiversity, Since there are few papers dealing with the because this type of habitat is home to numerous fauna of dolomitic grasslands, the aim of our rare and/or relict species. The most valuable are studies was to explore the ground beetle fauna of the thermophilous species living in the Mediter- such grasslands in several areas of Hungary, to ranean and the Caucasus area and at the northern investigate the species composition and the domi- and western extent of range in Hungary. nance relations of assemblages. Pitfall trapping was carried out in the Transdanubian Mountains of Central Hungary. Former investigations in Buda Mountains were 2. Material and methods focused on the habitat selection of the ground during dolomitic succession (Baldi 1990, The samples were collected with pitfall traps at 10 Baldi & Adam 1991, Waliczky 1991), whilst ear- sites (5 localities, 2 sites at each) of dolomitic lier investigation in the Bakony Mountains was grasslands representing three regions ofHungary designed to monitor the carabid fauna (Kutasi et (Bakony Mountains, Vértes Mountains and Buda al. 2000). There are no comprehensive data about Mountains) between 1988 and 2005. Three local- the species composition of ground beetles of ities were investigated at the Bakony Mountains, dolomitic grassland in Hungary. The most char- Liter, Mogyoros-hegy (47°06’05” N, 18 °01 ’45” 254 Kutasi &Szél ' ENTOMOL. FENNICA Vol. 17

Table 1. Carabid catches, Berger-Parker dominance index values of the carabid assemblages, standardized abundance (n/ * trap year), and eight most abundant species of dolomitic grassland sites in Hungary. Samples sorted according to three moun- tain areas (Bakony, Vértes and Buda) and sampled habitats (Grass = grassland, Steppe = steppe meadow, Grass/mead = grassland/meadow habitat).

Bakony Vértes Buda

Mogyorés-hegy Ugri-hegy K'Lilso-hegy Bucka Odvas- Torok- hegy ugrato Grass Steppe Grass Steppe Grass Steppe Grass Steppe Grass/ Grass/ mead mead

Sampling period 1997—01 1997—01 1997—01 1997—01 1997—01 1997—01 2003—04 2003—04 1988 2005 No. of traps 15 15 15 15 15 15 20 8 108 27 No. individuals 174 75 340 202 530 604 65 203 281 41 No. species 18 16 27 26 33 37 13 12 27 7 Berger-Parker index 0.21 0.31 0.4 0.18 0.6 0.19 0.55 0.44 0.42 0.39 Standardized

no. individuals 2.32 1 4.53 2.7 7.06 8.05 1.62 12.7 2.6 1.52

Calathus ambiguus 17 — 40 2 60 19 4.6 1 0.4 17

Calathus cinctus 18 16 26 16 9.6 12 55 44 — 39

Calathus fuscipes 21 14 6.5 17 0.2 4 23 31 — 26.8 Carabus hungaricus 19 31 0.3 —— 5.4 —— 4.3 — Harpalus anxius — 1.3 3.5 18 7.7 14 3 ——— Harpalus subcylindricus —— 1.2 8.4 1.3 12 — 4 ——

Licinus cassideus 1.7 — 0.6 — 0.2 — 1.5 — 7.1 —

Zabrus spinipes — 2.7 ——— 0.5 —— 42 —

E), Kiralyszentistvan, Kulsd-hegy (47°05’57”N, number of traps). The traps (plastic cups of 8 cm 18°02’26” E) and Vilonya, Ugri-hegy (47° diameter and 12 cm depth, partly filled with 40% 07’47” N, 18°05’17” E). At the Vértes Moun- ethylene glycol) were placed 5 m from each other tains, Csakberény, Bucka (47°21’04” N, 18°21’ and covered with a square aluminium cover to 30” E) and in the Buda Mountains, two locations protect the trap content from rain, litter and dis- at Budaors, Odvas—hegy (47°28’05” N, 18°56’ turbance by small vertebrates. 48” E) and Torokugrato (47°27’30” N, 18°55’ The traps were checked and material col- 27” E) were studied. The main plant associations lected every two weeks between April and Octo- comprised open (Seselz' leucospermo—Festu— ber. The samples from each trap were handled cetum pallentis) or closed (Festuco pallenti— separately, stored at —18°C, sorted and identified Brometum pannonici) dolomitic grassland, and by the authors using Hfirka’s (1996) keys. The dolomitic steppe meadow (Chrysopogono— material is deposited in the collections ofthe Nat- Caricetum humilis). ural History Museum of Bakony Mountains The circumstances and intensity of collecting (Zirc, Hungary) and of the Hungarian Natural were different in the three regions. A total of 30 History Museum (Budapest). pitfall traps were used at each site in 1997—2001 Comparison ofthe carabid assemblages ofthe at the Bakony Mountains, 28 pitfall traps in investigated localities was made by hierarchical 2003—2004 at the Vértes Mountains, 108 pitfall clustering (Single-link) ofthe Jaccard Index. Cal- traps in 1988, and 27 pitfall traps in 2005 at the culations were made by the Syntax 2000 com- Buda Mountains The number ofthe traps was set puter package (Podani 1997). The chorological according to the length of the study period to en- types were used according to Hfirka (1996) and sure the maximum number of species from the the ecological characteristics were adopted from given area (the shorter the period, the higher the Kirschenhofer (1989). {CA VOL 17 a Carabids OfHungarian dOZOMiZ‘iC graSSiandS 255

(1.55 -

(1.411 '- 9.452 A total 0f2515 individuals belonging to 65 spe- 13.51): cies were collected. The percentage ofPalaearctic (1.55" 11.60; and Palaearctic species was relatively high (41.5%). The sampled species included 34 11.65 - 11.711- xerophflic (52.3%), 18 (18.5%), Similarity 0.75 - and 8 The assemm ophflic (12.3%) species. 0.8T); blage comprised 26% stenotopic species. 0.85; The bulk ofthe species belonged to the genera 0.90.3 Harpahzs (l4) and Amara (10). The most abunw 11.95: dant species were Caiaz‘has ambiguus (24.5%), 1.01) - C. CinCMS (17%) and C. fasapes (8.7%). Other Budai—hg. Vértes Bakony‘il . Bakony3. Bakony2. dominant species were-:— Cambus hangaricus, Fig. 1.. Dendrogram of similarity, based on the Jaccard Harpaias anxius, H. subcylindricas and Zabms index, of carabld assemblages in dolomitic grassland spinzpes. The species number collected in the inn Sites. Abbreviations: Budaiuhg: Budaérs, Vérles: dividual dolomitic grassland locations varied be“ Csékberény, Bakony’l: Kirélyszentlstvén, BakonyZ: tween 7 and 37, While the abundance of the Liter, BakcnyB: Vllonya. ground beetles was low. The average number of ’3‘ individuals per trap year varied between 1 and ofAugust to the end of October, is the main one. 12.7 (Table l). The dominant species ofthe study The highest number of specimens was observed sites are also presented in Table l. in the second. half of September. The assemblages of the different localities were compared using the Jaccard index (Fig 1). The hierarchical classification. showed that the carabids were divided into distinct regions. Ac»- cording to these results, the most frequent species The examinations were carried out in ten of the Bakony Mountains were Caiaihus amn- dolomitic grasslands in five localities represent- bigaas, C. Cincms and Harpaius anxms. C. cine-- ing the most extensive dolomitic regions ofHun- ms and C. fusczpes were the most frequent species gary (Bakony, Vértes and B ountains). it at the Vértes ountains, While C. cincms and can be concluded that the number of specimens Zabms spimjpes were most abundant at the B and species of carabid asssemblages are very low ountains. The species similarity ofcarabid assemblages in the different regions was low, with only eight ._ mm Liter. grasaland in all localities: Calathus species occurring —m- Liter. Steppe meadow

C. meadow ambiguus, Cincms, Cfusczpes, Hay/“pains pu- 1:3 __ mdmldilnnya. Steppe milas, H. mabah’, H. rubmpes, H. tardus and Licmus cassideus. A total of 23 carabid species individuaie EC! {if (35.4%) occurred only in one locality. ’ spe- cies found in the study area included Amara proxima, A. SOUicz’m, Cymmdis axfllaris, C. van Number wetter“ riaiasa, Licmus caSSideuS and 2%

i :3» a t a hailii. Cambus is one of the rarest hangaricus Li‘s; 7"". 33 in and seasonal of or; species dynamics [35.35]. [18.15. [37.15. Dram. [2! LP?! 113.15. 18311 this species has not previously been published Date 63" ad. C. has a (Turin 2003; Fig 2). hangaricas Fig. 2. Seasonal fluctuations of Carabus hungaricus in predominantly autu activity, although it can dolomitic grasslands of Bakony [1997—— curs in dolomitic grasslands from the begi ing 2001; 15 pitfall traps (total number of C. hungericus oflune. The second peak ofactivity, from the end catches per dates, all years and traps summed); 256 Kutasi & Szél ' ENTOMOL. FENNICA Vol. 17

in these habitats, and contains several rare spe- Calathus ambiguus is the qualitative indicator of cies. sandy soil type in Germany (Muller-Motzfeld Waliczky (1991) found 37 ground beetle spe- 1989), while C. fuscz'pes is significantly associ- cies from the Buda Mountains (Nagykovacsi) in ated with sandy soil in arable fields (Irmler, dolomitic rock swards and turkey oak forest. Of 2003). In addition to the two dominant species (C. these, 21 species were also found by us (these are ambiguus and C. fuselpes), almost halfofthe col- members of species communities of dry, open lected species are frequent in agricultural areas, steppes); the remaining 16 belong to forest com- including Agonum dorsale, Amara aenea, A. fa— munities. From the Bakony Mountains, nearby miliaris, Brachinus explodens, Calathus erratus, the area investigated by us, Kutasi (1998) men- Harpalus distinguendus, H. griseus, H. rufipes, tions 14 carabid species, of which all but Prero— H. serrl'pes, H. smaragdinus and Trechus quadri— stichus incommodus were found in our study. A striatus (Horvatovich & Szarukan 1986, Kutasi et number of species ofthe dolomitic regions do oc- al. 2004). The same phenomenon has earlier been cur in limestone rock sward, too (Horvatovich found in limestone rock sward and the neighbour- 1989, 2000). The faunistic overlap with the sandy ing agricultural fields (Horvatovich 1989, 2000). grasslands is also considerable: several species The carabid communities of the Hungarian occur in both areas. The faunistic similarity is at dolomitic steppes show similarity to those of least partly due to the good heat conductivity of other vegetation-poor, bare areas. The occurence the ground. of many thermophilous and xerotherm species Some rare species, such as Licinus cassideus can be explained by the good heat conductivity of and Amara sollicita, also occur in limestone rock the soil. Although a significant proportion of swards (Horvatovich 1989, 2000), while Cara— these species also occurs in agricultural/culti- bus hangaricus, L. cassideus, Masoreus wet— vated areas, we found several rarities with high terhalll'l' and Spim'pes are typical inhabit- protection value. In Hungary, the dolomitic rock ants of the sandy regions of the Great Hungarian swards are endangered by many activities, such Plain (Adam & Merkl 1986). These thermo- as mining, illegal trash deposits and motor sports. philous species are distributed mainly in the Our work underlines that the protection of these southern part of , in Asia Minor and/or in habitats is also important for entomological rea- North Africa. Carabus hangaricus, which proved sons. a dominant species in some samples, is strictly protected in Hungary since 2001 and a species of Ackowlea’gements. This research was supported by the Na— tional R&D “The and of the European community interest within Natura Programme: origin genesis fauna of the Carpathian Basin: diversity, biogeographical 2000. hotspots and nature conservation significance”, contract Of the we classified as species common, no: 3B023 —04. We thank two anonymous reviewers and G. Calathusfusczpes and Zabrus Spim'pes were also Lovei for comments on an earlier verison of this paper. common during an earlier study in the Buda Mountains (Waliczky 1991). oc- curs not only in sandy grasslands but also in parks References (Kutasi & Szél 2000) and humid areas (forest edges and depressions with reeds and willows) Adam, L. & Merkl, O. 1986. Adephaga of the Kiskunsag (Kutasi 1998, Szél & Kutasi 2003). National Park, I. Carabidae (Coleoptera). 7 In: Mahunka, S. (ed.): The fauna of the Kiskunsag Na- Ofthe rare species, Masoreus wetterhallii and tional Park, I: 1 197142. Akade'miai Kiado, Budapest. axillarz's were found in earlier studies Cymindis Baldi, A. 1990. Species richness, abundance and diversity on dolomitic rock sward (Waliczky 1991). of beetles (Coleoptera) in relation to ecological suc— The most abundant species have their activity cession. 7 Folia Entomologica Hungarica 51: 17724. peaks in autumn and two of these, viz. Calathus Baldi, A. & Adam, L. 1991. Habitat selection of ground— dwelling beetles during dolomitic succession. 7 An— ambiguus and C. fuscz'peS, can be found in great nales Historico-Naturales Musei Nationalis Hungarici numbers on arable land Lovei & (Thiele 1977, 83: 2457251. Sarospataki 1990), apple orchards (Kutasi et al. Horvatovich, S. 1989. A Villanyi-hegyse'g fiitobogarai 2004) and sandy areas (Szél & Kutasi 2005). (Coleoptera: Carabidae). (The Carabidae (Coleop- ENTOMOL. FENNICA Vol. 17 ° Carabids ofHungarian dolomitic grasslands 257

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