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Pseudoscorpions (Arachnida: Pseudoscorpiones) of Malá Fatra National Park, Strážovské Vrchy Protected Landscape Area and Žilinská Kotlina Basin (Slovakia)

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Pseudoscorpions (Arachnida: Pseudoscorpiones) of Malá Fatra National Park, Strážovské Vrchy Protected Landscape Area and Žilinská Kotlina Basin (Slovakia) Folia faunistica Slovaca 21 (1) 2016: 1–7 www.ffs.sk PSEUDOSCORPIONS (ARACHNIDA: PSEUDOSCORPIONES) OF MALÁ FATRA NATIONAL PARK, STRÁŽOVSKÉ VRCHY PROTECTED LANDSCAPE AREA AND ŽILINSKÁ KOTLINA BASIN (SLOVAKIA) 1 2 2 3 Katarína Krajčovičová , Erika Igondová , Oto Majzlan 1 & Radomír Blažek 2 Department of Zoology, Faculty of Natural Sciences, Comenius University, Mlynská dolina, Ilkovičova 6, SK–842 15 Bratislava, Slovakia [[email protected]] Department of Environmental studies, Faculty of Natural Sciences, Comenius University,3 Mlynská dolina, Ilkovičova 6, SK–842 15 Bratislava, Slovakia [[email protected], [email protected]] Mestské Múzeum v Rajci, Hviezdoslavova 1070, SK–015 01 Rajec, Slovakia [[email protected]] Abstract: Faunistic data on pseudoscorpions from Malá Fatra National Park, Strážovské vrchy Protected Landscape Area and Žilinská kotlina Basin were summarized for the first time. A total of 11 species from four families were found during 2004–2015. Pseudoscorpions from Chthoniidae and Neobisiidae families were sifted from organic material or collected using pitfall traps. Only one species of the family Cheliferidae, collected by beating branches,Neobisium was found. erythrodacty Chernetid- lumpseudoscorpions were mostly sifted from compost heaps, garden waste and rotten hay. The most abundant was epigean species Lamprochernes(L. Koch, 1873), nodosus majority of specimens were collected using pitfall traps in wetland area in Šujské rašelinisko Nature Reserve. In the study area, species (Schrank, 1803) occurred in high abundance as well, all specimensKey words: were found in composts and rotten hay. Central Europe, faunistics, peatbog, Pseudoscorpiones, Slovakia, wetland. INTRODUCTION C heterodactylus C dioph- thalmus - - . Tömösváry, 1882 with . Pseudoscorpions are small arachnids inhabit Daday, 1888. Taken this revision into ac- ing almost all terrestrial habitats (Beier 1963). count, the Slovak pseudoscorpion fauna currently includes 54 species from eight families. More in According to Christophoryová et al. (2011a, c;- tensive research of this arachnid order began in 2012a, b) the Slovak pseudoscorpion faunaChtho was- - niusrepresented heterodactylus by 55 species belonging to eight fami Slovakia in the latter half of the 20th century. For lies. Gardini (2014) in his latest revision of that reason, the knowledge of pseudoscorpion di group synonymized species versity and distribution is still fragmentary. Only Krajčovičová K, Igondová E, Majzlan O & Blažek R, 2016: Pseudoscorpions (Arachnida: Pseu- doscorpiones) of Malá Fatra National Park, Strážovské vrchy Protected Landscape Area and Žilinská kotlina Basin (Slovakia). Folia faunistica Slovaca, 21 (1): 1–7. [in Slovak, with English abstract] Received 29 June 2015 ~ Accepted 12 December 2015 ~ Published 5 February 2016 © Faunima, Bratislava, 2016 e–ISSN 1336–4529 ISSN 1335–7522 2 Krajčovičová K et al.: Pseudoscorpions of Malá Fatra, Strážovské vrchy and Žilinská kotlina - Neobisium Pselaphochernes - - a few areas have been systematically investigat sp. and Neobisium beieri sp. listed in (ed: Gaderská dolina Valley of Veľká Fatra Nation- the paper were never identified on species lev al Park (Krumpál 1980), Poloniny National Park el. The rare species Verner, 1958 Krumpál & Krumpálová 2003), Cerová vrchovi- describedN. from beieri Veľká Fatra NP was confirmed by na Protected Landscape Area (Christophoryová Krumpál (1980). Studničková (1968) mentioned 2009) and Burda Nature Reserve (Christophory record of C. heterodactylusin her thesis from Malá Fatra NP- ová et al. 2014). Malé Karpaty Protected Landscape as well, but this record has never been published. Area and Trnavská pahorkatina Hills represent the The findings of represent the on best-documented regions in Slovakia, through the- ly published data about pseudoscorpions from Malá- systematic long-term research (Christophoryová Fatra NP (Krumpál & Kiefer 1981, Ducháč 1989). & Krumpál 2005, 2007; Christophoryová & Hole- There are no published records about pseudoscor cová 2012; Christophoryová 2013). The attention pions from Strážovské vrchy Protected Landscape was also paid to the pseudoscorpion fauna of small- Area and Žilinská kotlina Basin. er areas: a several years accumulated material - Each faunistic study of a new area could improve from Šúr Nature Reserve was published by Chris the knowledge about pseudoscorpion diversity in tophoryová & Krumpál (2010) and pseudoscor Slovakia. The aim of the current paper was to give- pion material from Malaise traps and pitfall traps new report of pseudoscorpion species from Malá from Ostrov Kopáč Nature Reserve was published Fatra NP, Strážovské vrchy PLA and Žilinská kotli by Krumpál & Christophoryová (2007). During na Basin. the years 1974–1976 Krumpál (1980) carried out- MATERIAL AND METHODS the research in Gaderská dolina, valley of Veľká- Fatra NP, which is closest to the current studied ar ea (Veľká Fatra NP borders Malá Fatra NP). Alto- The study area is located in northern Slovakia gether 13 species from three families were found in (Fig. 1). The altitude varies from 371 to 840 m above NeobisiumGaderská dolina brevidigitatum using pitfall traps, siftingN andcarpati indi- sea level. Malá Fatra NP forests are represented- cumvidual collecting. NFourmacrodactylum species of them, concretely mainly by mixed beech forests at higher elevations Chernes similis (Beier, 1928), . by fir and spruce. Limestone beech forests domi Beier, 1935, . (Daday, 1888) nate in the whole area of Strážovské vrchy PLA. and (Beier, 1932) were recorded The material presented in this paper was collected for the first time in Slovakia. The pseudoscorpions during 2004 – 2015. The majority of specimens was Figure 1. Map of localities situated in Malá Fatra National Park, Strážovské vrchy Protected Landscape Area and Žilinská kotlina Basin (Slovakia); with locality codes listed in list of localities (see Material and Methods). Folia faunistica Slovaca 21 (1) 2016: 1–7 3 - Martinské hole: collected randomly by different collectors. System [12A]48°58’44” Rajec: N, 18°36’43” W, 656 m atic research was carried out in Šujské rašelinisko a.s.l., meadow, sifting under the hazel vegetation, Nature Reserve, where formaldehyde pitfall traps leg. R. Blažek; [12B] Rajec: 49°04’58” N, 18°37’42” with two weeks sampling intervals were exposed W, 494 m a.s.l., city gardens, sifting of garden waste,- during 2013 – 2015; exposure time: 14. 4. – 1. 11.- leg. R. Blažek; 49°04’02”[13] Rokoš N, 18°36’18” Nature 2013, 24. 3. – 5. 10. 2014, in 2015 the pitfall traps- Reserve:W, 500 m a.s.l., stream bank, sifting under the al- were exposed randomly. Šujské rašelinisko NR lo der vegetation, leg. R. Blažek; cated in Malá Fatra NP is an importantth wetland ar [14A] Súľov-Hradná:48°46’20” N, 18°26’43” W, 747 m a.s.l., de ea of Slovakia classified to the 4 level of nature ciduous forest, sifting of leaf litter, leg. Ľ. Černecká;- protection. 49°08’20” N, 18°35’30”[14B] W, - 444 m a.s.l., stream bank, sifting of compost con A part of the pseudoscorpion material was studied Súľov-Hradná: taining mainly garden waste, leg. R. Blažek; - as permanent slide mounts using Leica DM1000 mi- 49°08’12” N, 18°35’14” W, 444 croscope. A part of the material was deposited in [15A] m a.s.l., stream bank, sifting of compost contain ethanol and studied using Zeiss Stemi 2000-C ster Šujské rašelinisko Nature Reserve: ing mainly garden waste, leg. R. Blažek; eomicroscope. All specimens were identified using- 49°03’40” N, identification keys Christophoryová et al. (2011d) [15B] Šujské rašelinisko 18°37’05” W, 479 m a.s.l., peatbog, pitfall trap, leg. and Gardini (2013, 2014) (det. Jana Frisová Chris NR: - E. Igondová, O. Majzlan; tophoryová, K. Krajčovičová). Nomenclature for all - 49°03’37” N, 18°37’02” W, 480 m a.s.l., play taxa follows Harvey (2013) and Gardini (2014). [15C] Šujské rašelinisko NR: ground (mowed meadow), pitfall trap, leg. E. Ig The whole material is deposited in the zoological - collectionList of studied of the localities Comenius including University, sampling Bratislava. ondová, O. Majzlan; [15D] methods (alphabetized list): Šujské49°03’40” rašelinisko N, 18°36’57” NR: W, 493 m a.s.l., dry pine for [1A] Čičmany: est, pitfall trap, leg. E. Igondová, O. Majzlan; (Fig. 1) [15E] 49°03’44”Šujské rašelinisko N, 18°37’05” NR: [1B] Čičmany:48°57’07” N, 18°30’36” W, 665 m W, 479 m a.s.l., reed, Phragmites australis,Salix pitfallRu- a.s.l., marsh, sifting of organic material, leg. R. bustrap, leg. O. Majzlan; Blažek; 1C] Čičmany: 48°57’09” N, 18°30’51” W, 49°03’46” N, 18°37’09” W,[15F] 479 Šujském a.s.l., rašelinisko sp., 658 m a.s.l., marsh, sifting under the willows, leg. NR: sp. vegetation in peat area, pitfall trap, leg. E. R. Blažek;[2A] [ Dolná Tižina:48°57’54” N, 18°32’31” W, Igondová, O. Majzlan; [15G] 731 m a.s.l., marsh, sifting under the willows, leg. R.- Šujské49°03’42” rašelinisko N, 18°37’05” NR: W, 478 m a.s.l., gravel Blažek; 49°13’19” N, 18°54’45”[2B] bars, pitfall trap, leg. E. Igondová, O. Majzlan; DolnáW, 420 Tižina:m a.s.l., stream bank with willow vegeta 49°03’36” [15H]N, 18°37’18” Šujské tion, sifting of organic material, leg. R. Blažek; rašeliniskoW, 477 m a.s.l., NR: meadow–arable field edge, pitfall [3] Domaniža: 49°12’38” N, 18°55’17” W, 474 m trap, leg. E. Igondová, O. Majzlan; a.s.l., stream bank, sifting of moss, leg. R. Blažek; [16] Višňové:49°03’48” N, 18°37’19” W, 474 m 49°02’47” N, 18°33’04”[4] W,Ďurčiná: 371 m a.s.l., river bank, pitfall trap, leg. E. Igondová, O. a.s.l., stream bank, sifting of compost containing Majzlan;[17A] Vojtová dolina 49°08’57” Valley: N, 18°48’14” W, mainly garden waste, leg. R. Blažek; - 578 m a.s.l., spruce forest, sifting of moss, leg.
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