RED LIST OF , BUSH-CRICKETS AND CRICKETS () OF THE CARPATHIAN MOUNTAINS

Anton Krištín () & Iorgu Ionuț Ștefan (Romania) (eds) Data and assessment process contributors and authors of relevant and cited publications: Anton Krištín (Slovakia), Iorgu Ionuț Ștefan (Romania), Miklós Heltai, Barnabas Nagy (Hungary), Jevhen Lyushenko, Vasil Chumak (Ukraine), Jaroslav Holuša, Petr Kočárek (), Axel Hochkirch ()

Introduction pathian region: Data was collected from the literature, from sources given by BioREGIO project partners in Orthoptera are among the most important bio-indicators particular countries (see data contributors above) and of the status of integrity of natural habitats, especially own published and unpublished data (see literature for habitats with small plot sizes. Therefore, Orthoptera section, unpublished records only by KRIŠTÍN A. & assemblages provide valuable information on habitat con- IORGU I. Ş.). ditions and status of sites (MARINI et al. 2009). 2. Data was entered in the online database platform of Global assessments of the conservation status of ca. 1000 the project BioREGIO Carpathians as well as into a European species of grasshoppers, crickets and bush-c- Microsoft Excel database. rickets for the IUCN Red List of Threatened SpeciesTM 3. All 142 Orthoptera species present in the Carpathian started in 2011. The Red List status of 60 species has been orographic units (excluding Serbia due to missing data) published in 2012. Altogether, the global Red List status were evaluated according to the IUCN Red List criteria of 236 Orthoptera species has been assessed (IUCN (IUCN 2001). Only one species (not native and intro- 2013), 14 of which occur in the Carpathians (Chorthippus duced, meridionale) could not be assessed and acroleucus VU, glabra LC, Isophya harzi VU, Metri- was included in the category “Not Applicable” (NA). optera domogledi VU, irena VU, non- The other 141 species were classifi ed to the categories tana VU, VU, Onconotus servillei VU, Critically Endangered (CR), Endangered (EN), Vul- Poecilimon affi nis LC, Poecilimon ampliatus LC, Saga pedo VU, nerable (VU), Near Threatened (NT), Least Concern eurasius VU, Uvarovitettix transylvanicus VU and (LC) and Data defi cient (DD). Altogether 80 out of Zubovskia banatica VU). 141 species were not listed in the Bioregio database Red Lists of Orthoptera have been published in several due to technical reasons (fi lling the occurrence, loca- Carpathian countries (however, based upon different cri- tions, habitats, threats in all orographic units in very teria): (LIANA 1992, LIANA 2002, GŁOWACIŃSKI & common and abundant species), but they fulfi l the ge- NOWACKI 2004), former Czechoslovakia (GULIČKA 1992), neral criteria for the category LC. Red List assessments Hungary (NAGY 1999), Slovakia (KRIŠTÍN 2001), Czech Re- from particular countries were also considered, based public (HOLUŠA & KOČÁREK 2005), Ukraine (AKIMOV 2009, on the proposals of project partners and considering МАTELESHKO & POTISH 2011). A European Red List is not the extinction risk in surrounding Carpathian countries available yet and there is only one Carpathian Red List or adjacent Non-Carpathian territories. No assessment prepared ten years ago, based on unknown criteria, which was done for the small part of the Carpathians located includes fi ve Orthoptera species (WITKOWSKI et al. 2003). in Serbia, due to the absence of a partner. Assessment Method Our purpose was to collect and process all existing data For processing the existing data on grasshoppers, crickets on Orthoptera species from six Carpathian countries and bush-crickets in the Carpathian region of Slovakia, (Czech Republic, Hungary, Poland, Romania, Slovakia, Czech Republic, Poland, Ukraine and Romania the fol- and Ukraine) and enter them into a database developed lowing three steps were used: by the State Nature Conservancy of the Slovak Republic 1. Documentation on the Orthoptera fauna in the Car- in order to assess the Red List status.

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zzbornik_cervenebornik_cervene zzoznamy.inddoznamy.indd 118686 227.8.20147.8.2014 222:36:272:36:27 Results (Summary) References Altogether 142 Orthoptera species (ca 10.3% of the Carpathians & Red Lists 1382 European species) were recorded in the Carpathian GULIČKA, J. (1992). Orthoptera. Pp. 69-73. In: Škapec, Mountains, in six Carpathian countries (CZ, SK, PL, UA, L. (ed): Červená kniha ohrožených a vzácných druhů HU, RO; Table 1). The number of species ranged from rostlin a živočichů ČSFR 3 - Bezobratlí. [Red data book 55 (Poland) to 133 (Romania) taxa, following the tempe- of endangered and rare plant and species of the rature gradient along this region and illustrating the strong ČSFR 3 - Invertebrates]. Príroda, Bratislava, 160 pp. (in impact on thermophilous as well as the proporti- Czech). onal size of Carpathians in the particular countries. In these countries, the number of species listed in national HARZ, K. (1969). Die Orthopteren Europas - The Or- Red Lists ranged from 12 (Poland, one threatened speci- thoptera of Europe. Vol. I. - The Hague, Dr.W. Junk es) to 33 (Romania, 20 threatened species) and 37 species B.V., 749 pp. (Slovakia, 13 threatened species). HARZ, K. (1975). Die Orthopteren Europas - The Or- Altogether, 61 of the 141 assessed species were included thoptera of Europe. Vol. II. - The Hague, Dr. W. Junk in Carpathian Red List, but only 20 of them are listed as B.V., 939 pp. threatened. Ten species were assessed as EN (Isophya har- zi, Isophya ciucasi, Isophya nagyi, Saga pedo, Gampsocleis glabra, IUCN (2013). IUCN Red List of Threatened Species. Metrioptera domogledi, Zubovskia banatica, Chorthippus acroleu- Version 2013.2. . Downloaded cus, Paracaloptenus caloptenoides, Podismopsis transsylvanica) and on 31 January 2014. ten as VU (Isophya costata, I. sicula, I. dochia, Poecilimon inter- KRIŠTÍN, A. & KAŇUCH, P. (2013). A review of distribu- medius, Onconotus servillei, Uvarovitettix transsylvanicus, Mira- tion and ecology of three Orthoptera species of Euro- mella irena, Odontopodisma decipiens, Odontopodisma montana, pean importance with contributions from their recent Stenobothrus eurasius, Table 1). Most of EN species are also north-western range. Journal of North Western Zoo- included on the global IUCN Red List. logy 9: 185-190. A total of 16 species was endemic to the Carpathians (11.3% of 142) and further six species sub-endemic MARINI, L., FONTANA, P., BATTISTI A. & GASTON K.J. (Table 1), meaning that they also occur at a few sites in (2009). Response of orthopteran diversity to abandon- the area surrounding the Carpathians. ment of seminatural meadows. Agric. Ecosyst. Envi- ron. 132: 232–236.

Main threats NAGY, B. (2005). Orthoptera fauna of the Carpathian The major threats detected in most red-listed species are: basin – recent status of knowledge and a revised che- i) Habitat loss/degradation, abandonment of traditio- cklist. - Entomofauna carpathica 17: 14-22.

nal management, of grass cutting and grazing and fol- WITKOWSKI, Z.J., KRÓL, W. & SOLARZ, W. (eds) (2003). lowing succession leading to overgrowing by shrubs Carpathian List Of Endangered Species. WWF and and trees (e.g. Saga pedo, Gampsocleis glabra, Metrioptera Institute of Nature Conservation, Polish Academy of domogledi, Paracaloptenus caloptenoides, Odontopodisma deci- Sciences, Vienna-Krakow. piens, Miramella irena, Stenobothrus eurasius). ii) Human settlement expansion, use of insecticides, Czech Republic overgrazing (e.g. Isophya harzi, I. ciucasi, I. nagyi, I. sicula, HOLUŠA, J. (1995). Orthoptera náplavových šterkovišť I. dochia, Paracaloptenus caloptenoides, Saga pedo, Chorthip- řeky Ostravice a Morávky. Klapalekiana 31: 91-99. pus acroleucus, Podismopsis transsylvanica). iii) Afforestation of non-forest habitats (e.g. Saga pedo, HOLUŠA, J. (1996). Výskyt saranče Stethophyma grossum Paracaloptenus caloptenoides, Stenobothrus eurasius). (, ) na severní Moravě a v českém iv) Restricted range, low densities, limited dispersal with Slezsku. Čas. Slez. Muz. Opava (A), 45: 285-286. combination with above mentioned threats: (e.g. most HOLUŠA, J. (1997). Druhové spektrum sarančí (Caelife- of brachypterous species Isophya harzi, I. ciucasi, I. nagyi, ra) a kobylek () údolí potoka Dinotice (Vsetín- I. sicula, I. dochia, Poecilimon intermedius, Onconotus servillei, ské vrchy). Klapalekiana 33: 11-16. Gampsocleis glabra, Uvarovitettix transsylvanicus, Miramella irena, Zubovskia banatica, Chorthippus acroleucus, Podismop- HOLUŠA, J. (2000). K poznání sarančí (Caelifera) a ko- sis transsylvanica). bylek (Ensifera) Moravsko slezských Beskyd. Klapale- kiana 36: 41-70.

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Table 1: Orthoptera in the Carpathians (Car) and their IUCN regional Red List categories (RL) and criteria (Crit) in particular Carpa- thian countries and for entire Carpathian region. (* = present) SK CZ HU Taxa RL Crit RL Crit RL Crit

Ephippiger (Fiebig, 1784) * Conocephalus discolor Thunberg, 1815 / * =fuscus (Fabricius, 1793)/ Conocephalus dorsalis (Latreille, 1804) LC * Conocephalus hastatus (Charpentier, 1825) Ruspolia nitidula (Scopoli, 1786) LC A. Costa, 1860 * (De Geer, 1773) * constrictus Brunner von Wattenwyl, 1878 * Barbitistes ocskayi (Charpentier, 1850) Barbitistes serricauda (Fabricius, 1798) NT * NT Isophya beybienkoi Maran, 1958 DD Isophya camptoxypha Fieber, 1853 * Isophya costata Brunner von Wattenwyl, 1878 VU B1 a+c Isophya harzi Kis, 1960 Isophya kraussii kraussii Brunner von Wattenwyl, 1878 * * Isophya kraussii moldavica Iorgu & Heller, 2013 Isophya modestior Brunner von Wattenwyl, 1882 * Isophya pienensis Maran, 1954 NT * Isophya ciucasi Iorgu & Iorgu, 2010 Isophya sicula Orci, Szovenyi & Nagy, 2010 Isophya dochia Iorgu, 2012 Isophya nagyi Szovenyi, Puskas & Orci, 2012 Isophya posthumoidalis Bazyluk, 1971 DD Isophya speciosa (Frivaldszky, 1867) Isophya stysi Cejchan, 1957 NT NT Isophya modesta (Frivaldszky, 1867) VU B1 a+c VU B1 a+c

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zzbornik_cervenebornik_cervene zzoznamy.inddoznamy.indd 119090 227.8.20147.8.2014 222:36:272:36:27 KRIŠTÍN, A., P. KAŇUCH, B. JARČUŠKA, E. I. IORGU & I. S. RAMME, W. (1951). Zur Systematik Faunistik und Biolo- IORGU (2013): Notes on Orthoptera (Insecta) and their gie der Orthopteren von Sudost-Europa und Vordera- assemblages in the Romanian Carpathians. Travaux du sien, Mitteilungen Aus Dem Zoologischen Museum zu Muséum National d’Histoire Naturelle “Grigore Anti- Berlin, 27: 383-385. pa” LVI (1): 19-32. SANGHELI, A. (1978). Date noi privind distributia spe- NAGY, B., B. KIS & L. NAGY (1983). Saga pedo Pall. (Or- ciei Saga pedo (Pall), (Sagidae-Orthoptera) in Muntii thoptera, Tettigoniidae): Verbreitung und ökologische Banatului. Muzeul Banatului Tibiscus: 133-140. (in Ro- Regelmassigkeiten des Vorkommes in SO-Mitteleuro- manian) pa. Verh. SIEEC X: 190-192. SZÖVÉNY, G. & K. M. ORCI (2008). Contributions to the ORCI, K. M., G. SZÖVÉNYI & B. NAGY (2010a): A cha- Orthoptera fauna of Maramureş county with the fi rst racterization of the pair forming acoustic signals of record of Isophya posthumoidalis Bazyluk 1971 in Roma- Isophya harzi (Orthoptera, Tettigonioidea, Phaneropte- nia. Studia Universitatis “Vasile Goldiş”, Seria Ştiinţele ridae). Acta Zoologica Academiae Scientiarum Hunga- Vieţii 19: 235-241. ricae 56(1): 43-53. SZÖVÉNY, G., G. PUSKÁS & K. M. ORCI (2012): Isophya ORCI, K. M., G. SZÖVÉNYI & B. NAGY (2010b). Isophya si- nagyi, a new phaneropterid bush-cricket (Orthoptera: cula sp. n. (Orthoptera: Tettigonioidea), a new, morpho- Tettigonioidea) from the Eastern Carpathians (Caliman logically cryptic bush-cricket species from the Eastern Mountains, North Romania). Zootaxa 3521: 67-79. Carpathians (Romania) recognized from its peculiar male calling song. Zootaxa 2627: 57-68.

PL UA RO Carpathians Endemic, or RL Crit RL Crit RL Crit RL Crit Subendemic in Carpathians

* * * * * *

* * * LC * * * * LC NA * * * * * * * * * * * NT DD E * * * * E * VU B1a, b(iv, v) EN B2a+b iii iv v EN B2a+b iii iv v E DD * * * * * * * NT * * LC E EN B1a+b ii iii EN B1a+b ii iii E VU B2a+b iii VU B2a+b iii E VU B2a+b iii VU B2a+b iii E EN B2a+b iii EN B2a+b iii E DD * LC LC E LC LC DD NT * LC E * DD SE

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Isophya rectipennis Brunner von Wattenwyl, 1878 Isophya zubowskii Bei-Bienko, 1954 Leptophyes albovittata (Kollar, 1833) * * Leptophyes discoidalis (Frivaldszky, 1867) NT NT Leptophyes laticauda (Frivaldszky, 1867) Leptophyes punctatissima (Bosc, 1792) * Phaneroptera falcata (Poda, 1761) * * Phaneroptera nana Fieber, 1853 DD * Poecilimon affi nis (Frivaldszky, 1867) Poecilimon ampliatus Brunner von Wattenwyl, 1878 Poecilimon brunneri (Frivaldszky, 1867) * Poecilimon fussii Brunner von Wattenwyl, 1878 CR B1 a+c VU B1 a+c Poecilimon intermedius (Fieber, 1853) EN B1 a+c; D VU B1 a+c VU B1 a+c Poecilimon schmidtii (Fieber, 1853) LC LC Poecilimon thoracicus (Fieber, 1853) Polysarcus denticauda (Charpentier, 1825) LC CR B1 a+b+c * Onconotus servillei Fischer de Waldheim, 1846 Saga pedo (Pallas, 1771) CR B1 a+b+c CR B1 a+b+c EN B1 a+b+c Decticus verrucivorus (Linnaeus, 1758) * * * Gampsocleis glabra (Herbst, 1786) Metrioptera (M.) bicolor (Philippi, 1830) * * * Metrioptera (M.) brachyptera (Linnaeus, 1761) * * * Metrioptera (Broughtonia) domogledi Brunner v. Wattenwyl, 1882 Metrioptera (M.) roeselii roeselii (Hagenbach, 1822) * * * Pachytrachis gracilis (Brunner von Wattenwyl, 1861) CR B1 a+b+c EN B1 a+c Pholidoptera aptera (Fabricius, 1793) * * * Pholidoptera fallax (Fischer, 1853) * * * Pholidoptera frivaldskyi (Herman, 1871) EN B1 a+c Pholidoptera griseoaptera (De Geer, 1773) * * * Pholidoptera littoralis similis (Brunner von Wattenwyl, 1861) Pholidoptera transsylvanica (Fischer, 1853) NT NT Platycleis (P.) albopunctata (Goeze, 1778) Platycleis (Platycleis) albopunctata grisea (Fabricius, 1781) * * * Platycleis (Montana) striata (Thunberg, 1815) Platycleis (Montana) montana (Kollar, 1833) NT Platycleis (Tesselana) veyseli (Kocak, 1984) * * Pterolepis germanica (Herrich-Schäffer, 1840) VU B1 a+c * Tettigonia cantans (Füssli, 1775) * * * Tettigonia caudata (Charpentier, 1842) NT * NT Tettigonia viridissima Linnaeus, 1758 * * * Acheta domesticus (Linnaeus, 1758) * * * Eumodicogryllus bordigalensis (Latreille, 1804) DD * * Gryllus campestris Linnaeus, 1758 * * * Melanogryllus desertus (Pallas, 1771) * * *

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LC LC LC LC SE * * * * NT * DD SE DD DD * * * * * * * DD NT NT DD DD DD DD * DD DD VU B1a, b(ii,iii,iv, v) NT * LC NT NT DD LC * LC VU B2a+b iii; D1 VU B2a+b iii; D1 EN B2a+b i ii iii; D EN B2a+b i ii iii; D * * * * EN B2a+b; D EN B2a+b; D * * * * * * * * EN B2a+b EN B2a+b; D E

* * * * EN B1 a+c * DD * * * * * DD LC DD SE * * * * * *

NT LC LC SE * * * * * * * * NT NT * LC DD * * * * * * * * * * * * * * * * * * * * * * * *

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Modicogryllus frontalis (Fieber, 1844) * * * Nemobius sylvestris (Bosc, 1792) * * Pteronemobius heydenii (Fischer, 1853) Oecanthus pellucens (Scopoli, 1763) * * * Gryllotalpa gryllotalpa (Linnaeus, 1758) * * * Myrmecophilus acervorum (Panzer, [1799]) * * * Tetrix bipunctata (Linnaeus, 1758) * * * Tetrix ceperoi (Bolívar, 1887) * Tetrix subulata (Linnaeus, 1758) * * * Tetrix tenuicornis Sahlberg, 1893 * * * Tetrix tuerki (Krauss, 1876) LC CR B1 a+b+c Tetrix undulata (Sowerby, 1806) * * * Uvarovitettix transsylvanicus (Bazyluk et Kis, 1960) Acrida ungarica (Herbst, 1786) Calliptamus italicus (Linnaeus, 1758) * NT * Paracaloptenus caloptenoides (Brunner v. Wattenwyl, 1861) CR B1 a+b+c CR B1 a+b+c (Kollar, 1833) * * Miramella ebneri ebneri (Galvagni, 1953) Miramella ebneri carpathica Cejchan, 1958 * Miramella irena (Fruhstorfer, 1921) Odontopodisma acuminata Kis, 1962 Odontopodisma carpathica Kis, 1962 Odontopodisma decipiens Ramme, 1951 VU B2 a+c Odontopodisma montana Kis, 1962 Odontopodisma rubripes Ramme, 1931 VU B1 a+c Pezotettix giornae (Rossi, 1794) VU B1 a+c * pedestris (Linnaeus, 1758) * RE * Pseudopodisma fi eberi (Scudder, 1897) Pseudopodisma nagyi Galvagni & Fontana, 1996 LC LC Pseudopodisma transilvanica Galvagni & Fontana, 1993 * Zubovskya banatica Kis, 1965 Arcyptera fusca (Pallas, 1773) NT RE VU B1 a+c Chorthippus acroleucus (Müller, 1924) Chorthippus albomarginatus (De Geer, 1773) * * * Chorthippus apricarius (Linnaeus, 1758) * * * Chorthippus biguttulus (Linnaeus, 1758) * * * Chorthippus brunneus (Thunberg, 1815) * * * Chorthippus dichrous (Eversmann, 1859) DD * * Chorthippus dorsatus (Zetterstedt, 1821) * * * Chorthippus mollis (Charpentier, 1825) * * * Chorthippus montanus (Charpentier, 1825) * * * Chorthippus oschei Helversen, 1985 * * Chorthippus parallelus (Zetterstedt, 1821) * * * Chorthippus pullus (Philippi, 1830) NT NT Chorthippus tatrae (Harz, 1971) * Chorthippus vagans (Eversmann, 1848) * * *

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* * * * * * * * * * * * * * * * * * * * * * * * * * * * * NT LC LC LC * * * * VU B2a,bII,IV VU B2a,bII,IV E * * * * * * EN B2a+b; D EN B2a+b; D * * * * * LC NT * LC VU B2a+b iii; D1 VU B2a+b iii; D1 E? * * * * VU B2a+c VU B1a+b iii iv v VU B1a+b iii iv v NT NT NT SE * LC LC * LC * * LC DD * LC EN B2a+b iii iv v EN B2a+b iii iv v E * NT EN B2a+b iii iv v EN B2a+b iii iv v E * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * DD NT * NT * * * *

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Chrysochraon dispar (Germar, [1834]) * * * Dociostaurus brevicollis (Eversmann, 1848) * * Dociostaurus maroccanus (Thunberg, 1815) * declivus (Brisout de Barneville, 1849) * * * Euchorthippus pulvinatus (Fischer de Waldheim, 1846) * * (Ocskay, 1826) * * * Gomphocerippus rufus (Linnaeus, 1758) * * * Myrmeleotettix maculatus (Thunberg, 1815) * * * Omocestus haemorrhoidalis (Charpentier, 1825) * * * Omocestus petraeus (Brisout de Barneville, 1856) * Omocestus rufi pes (Zetterstedt, 1821) * * * Omocestus viridulus (Linnaeus, 1758) * * * Podismopsis transsylvanica Ramme, 1951 Stauroderus scalaris (Fischer de Waldheim, 1846) NT * Stenobothrus crassipes (Charpentier, 1825) * * * Stenobothrus eurasius Zubovskii, 1898 VU B2 a+c VU B2 a+c Stenobothrus lineatus (Panzer, 1796) * * * Stenobothrus nigromaculatus (Herrich-Schäffer, 1840) * * * Stenobothrus rubicundulus Kruseman et Jeekel, 1967 Stenobothrus stigmaticus (Rambur, 1838) * * * Aiolopus strepens (Latreille, 1804) Aiolopus thalassinus (Fabricius, 1781) LC * Mecostethus parapleurus (Hagenbach, 1822) NT NT * Oedaleus decorus (Germar, 1826) * * Oedipoda caerulescens (Linnaeus, 1758) * * * Bryodemella tuberculatum (Fabricius, 1775) Psophus stridulus (Linnaeus, 1758) * NT NT Sphingonotus caerulans (Linnaeus, 1767) NT * * Stethophyma grossum (Linnaeus, 1758) LC NT * Total species 37 11 17 RE 2 CR 4 3 1 EN 2 2 VU 7 1 6 NT 11 5 6 LC 8 2 DD 5

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* * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * EN B2a+b iii EN B2a+b iii E * * * * * VU B2a+c VU B2a+c * * * * * * * * * * * * * * DD * * LC DD NT * LC * * * * * DD DD VU B1, B2a+b iv+v NT * LC * LC * * * LC 12 14 33 61

1 10 10 1 10 10 2 9 4 7 2 2 8 22 7 3 4 12

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Taxa Criteria in detail for Carpathians Meconema meridionale A. Costa, 1860 not native in Carpathians, known only from 2009 there Barbitistes serricauda (Fabricius, 1798) NT close to VU: B. 2. AOO: approx. 3000 km2; (a) severely fragmented; (b) II. continuing decline in area / quality of habitat Isophya costata Brunner von Wattenwyl, 1878 B. 1. EOO cca. 10 000-15 000 km2; (a) severely fragmented; (b) continuing decline in area, quality of habitat (due to overgrazing), number of locations; number of mature individuals. Isophya harzi Kis, 1960 B. 2. AOO cca. 150 km2; (a) only one known location; (b) continuing decline in area, quality of habitat (due to overgrazing), number of subpopulations; number of mature individuals Isophya ciucasi Iorgu & Iorgu, 2010 B. 1. EOO cca. 3000 km2; (a) only two locations; (b) continuing decline in area of occupancy and area / quality of habitat (due to overgrazing) Isophya sicula Orci, Szovenyi & Nagy, 2010 B. 2. AOO cca. 1000 km2; (a) only two locations; (b) continuing decline in area / quality of habitat (due to overgrazing and human settlement expansion) Isophya dochia Iorgu, 2012 B. 2. AOO cca. 1000 km2; (a) only three locations; (b) continuing decline in area / quality of habitat (due to overgrazing) Isophya nagyi Szovenyi, Puskas & Orci, 2012 B. 2. AOO cca. 300 km2; (a) only two locations; (b) continuing decline in area / quality of habitat (due to overgrazing) Poecilimon affi nis (Frivaldszky, 1867) NT close to VU: B. 1. EOO: approx. 20 000 km2; (a) only 25 locations; (b) II. continuing decline in area / quality of habitat (due to overgrazing). Poecilimon intermedius (Fieber, 1853) B. 1. EOO cca. 10 000 km2; (a) severely fragmented; (b) continuing decline in area of occupancy, quality of habitat (due to overgrazing), number of locations; number of mature individuals. Poecilimon thoracicus (Fieber, 1853) NT close to VU: B. 1. EOO: approx. 10 000 km2; (a) only 11 locations; (b) II. continuing decline in area / quality of habitat (due to overgrazing). Onconotus servillei Fischer de Waldheim, 1846 B. 2. AOO cca. 1000 km2; (a) only one location; (b) continuing decline in area / quality of habitat; D. 1. Population size: 500-800 individuals. Saga pedo (Pallas, 1771) B. 2. AOO cca. 300 km2; (a) only fi ve locations; (b) continuing decline in extent of occurrence, area of occupancy and area / quality of habitat; D. population size estimated to be less than 200 mature individuals Gampsocleis glabra (Herbst, 1786) B2. AOO: approx. 200 km2; (a) only one location; (b) continuing decline in area of occupancy and number of mature individuals; D. Population size: approx. 150-200 mature individuals. Metrioptera (Broughtonia) domogledi B2. AOO: approx. 200 km2; (a) only one location; (b) continuing decline in Brunner v. Wattenwyl, 1882 area of occupancy and number of mature individuals. In Serbia 4 oro units (VU, Pavičevič D, in litt.) Pachytrachis gracilis (Brunner von Wattenwyl, 1861) NT close to VU: B. 1. EOO: approx. 25 000 km2; (a) especially in the northern countries severely fragmented; (b) II. continuing decline in area / quality of habitat. Platycleis (Montana) montana (Kollar, 1833) NT close to VU: B. 2. AOO: approx. 2100 km2; (a) only 4 locations; (b) II. continuing decline in area / quality of habitat (due to overgrazing and human settlement expansion). Uvarovitettix transsylvanicus (Bazyluk et Kis, 1960) B. 2. AOO: approx. 1800-2000 km2; (a) only four locations; (b) continuing decline in (II) area of occupancy and (IV) number of locations Paracaloptenus caloptenoides B. 2. AOO: approx. 380-450 km2; (a) severely fragmented, only 11 (Brunner v. Wattenwyl, 1861) locations; (b) continuing decline in area of occupancy, number of mature individuals; D. Population size: approx. 200-250 mature individuals. Miramella irena (Fruhstorfer, 1921) B. 2. AOO cca. 1000 km2; (a) only one location; (b) continuing decline in area / quality of habitat; D. 1. Population size: 800-1000 mature individuals.

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zzbornik_cervenebornik_cervene zzoznamy.inddoznamy.indd 119898 227.8.20147.8.2014 222:36:272:36:27 Odontopodisma decipiens Ramme, 1951 B. 2. AOO: approx. 800-1000 km2; (a) only 8 locations; (c) extreme fl uctuations in number of mature individuals Odontopodisma montana Kis, 1962 B. 1. EOO cca. 15000 km2; (a) only six locations; (b) continuing decline in: area and quality of habitat; number of locations; number of mature individuals Odontopodisma rubripes Ramme, 1931 NT close to VU: B. 1. EOO: approx. 20 000 km2; (a) severely fragmented; (b) continuing decline in area / quality of habitat. Zubovskya banatica Kis, 1965 B. 2. AOO cca. 200 km2; (a) only one location; (b) continuing decline in area, quality of habitat; number of subpopulations; number of mature individuals Arcyptera fusca (Pallas, 1773) NT close to VU: B. 2. AOO: approx. 2 000-3 000 km2; (a) severely fragmented; (b) continuing decline in area / quality of habitat (aforestation, lost of pastures). Chorthippus acroleucus (Müller, 1924) B. 2. AOO cca. 150 km2; (a) only one location; (b) continuing decline in area, quality of habitat (due to overgrazing), number of subpopulations; number of mature individuals Chorthippus pullus (Philippi, 1830) NT close to VU: B. 2. AOO: approx. 2 000-3 000 km2; (a) severely fragmented; (b) continuing decline in area / quality of habitat. Podismopsis transsylvanica Ramme, 1951 B. 2. AOO cca. 200 km2; (a) only one location; should be: (b) continuing decline in area / quality of habitat (due to overgrazing) Stenobothrus eurasius Zubovskii, 1898 B. 2. AOO: approx. 2000 km2; (a) only 7 locations; (c) extreme fl uctuations in number of mature individuals.

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