<strong>Red</strong> <strong>Book</strong> <strong>of</strong> <strong>Butterflies</strong> <strong>in</strong> <strong>Turkey</strong> Taxonomic notes Despite the recent proposal for the use <strong>of</strong> the senior synonym Phengaris for all recognised Macul<strong>in</strong>ea taxa, an appeal for the precedence <strong>of</strong> the name Macul<strong>in</strong>ea over Phengaris was submitted to the International Commission on Zoological Nomencalature <strong>in</strong> mid 2010, and published <strong>in</strong> the Bullet<strong>in</strong> <strong>of</strong> Zoological Nomenclature (Balletto et al. 2010). A decision is awaited. Habitat and Ecology The Dusky Large Blue occurs on damp, moderately nutrient-rich grassland and rough vegetation where its larval foodplant Great Burnet (Sanguisorba <strong>of</strong>fic<strong>in</strong>alis) grows. The butterflies are usually found on or near the larval foodplant, which is also the ma<strong>in</strong> nectar source for the adults. Females preferably deposit the eggs on large flowerheads <strong>of</strong> large plants. The egg load per flowerhead can exceed 20 which leads to high resource competition, and usually not more than three to four caterpillars per flowerhead successfully reach their f<strong>in</strong>al larval <strong>in</strong>star. After about three weeks they move out <strong>of</strong> the flowerheads to the ground <strong>in</strong> order to be carried by workers <strong>of</strong> the ant genus Myrmica to an ant nest. There, they feed on ant grubs and ant regurgitations, hibernate and pupate early the follow<strong>in</strong>g summer. As soon as they emerge from the chrysalis, the butterflies leave the nest. The Dusky Large Blue is one <strong>of</strong> the most specialised <strong>of</strong> all the obligate myrmecophilous blues: its life cycle be<strong>in</strong>g adapted to only one species <strong>of</strong> host ant <strong>in</strong> most <strong>of</strong> its range. While <strong>in</strong> most <strong>of</strong> Europe Myrmica rubra is the ma<strong>in</strong> and <strong>of</strong>ten only host ant, some populations at the edge <strong>of</strong> the range are adapted to Myrmica scabr<strong>in</strong>odis but these are very rare (Tartally et al. 2008, Settele et al. 2008c). The Myrmica species used <strong>in</strong> <strong>Turkey</strong> is not known. This butterfly species usually has one generation a year from mid-July to mid-August (Hesselbarth et al. 1995) but it may also happen that caterpillars <strong>in</strong> the ant nest take two years to fully develop (Witek et al. 2006). Population trend Increas<strong>in</strong>g Decreas<strong>in</strong>g Stable Unknown Population This is a local species, restricted to (semi-) natural areas (van Swaay et al. 2009c). The populations <strong>in</strong> <strong>Turkey</strong> are considered fragmented. The areas <strong>of</strong> suitable habitat are small and isolated and unlikely to be connected as the longest migration so far documented for this species is 5 km (B<strong>in</strong>zenhöfer and Settele 2000) with most displacements hardly exceed<strong>in</strong>g 500 m (van Langevelde and Wynh<strong>of</strong>f 2009). For the same reason, exchange <strong>of</strong> <strong>in</strong>dividuals with the nearest populations <strong>in</strong> Georgia is uncerta<strong>in</strong>. Small and isolated patches have a lower probability <strong>of</strong> occupancy (Nowicki et al. 2007). However, it is known that very small populations <strong>of</strong> this species can survive for some time (Wynh<strong>of</strong>f 2001). In Europe, this species is listed on the regional European <strong>Red</strong> List as Near Threatened due to a strong decl<strong>in</strong>e <strong>in</strong> distribution or population size <strong>of</strong> more than 30% <strong>in</strong> Romania, the Netherlands and Ukra<strong>in</strong>e, and a decl<strong>in</strong>e <strong>of</strong> between 6-30% <strong>in</strong> Austria, France, Germany, Hungary, Slovenia and Switzerland (van Swaay et al. 2009c). Although there is no monitor<strong>in</strong>g data available for <strong>Turkey</strong>, the decl<strong>in</strong>e observed <strong>in</strong> Europe may also be occurr<strong>in</strong>g <strong>in</strong> <strong>Turkey</strong> as habitat management changes and other threats are similar. 50 Phengaris nausithous Threats The management <strong>of</strong> the hay meadows where the larval foodplant grows is critical. Best is traditional cutt<strong>in</strong>g by scythe <strong>in</strong> small blocks, with some areas cut late, or left uncut for one year, to provide flowerheads where the larvae can complete their development. However, mow<strong>in</strong>g large areas with a tractor <strong>in</strong> the middle <strong>of</strong> the season (as seen <strong>in</strong> Kılıçkaya, Artv<strong>in</strong>, <strong>in</strong> 2009), destroys the structural diversity, removes the foodplant while the caterpillars are <strong>in</strong> the flowerheads and damages the larger ant nests which are most valuable to the butterflies. Mechanisation at Kılıçkaya was also facilitat<strong>in</strong>g dra<strong>in</strong>age and plough<strong>in</strong>g <strong>of</strong> the marg<strong>in</strong>al habitats which provide important refuges for this butterfly. In the long-term, abandonment is also a problem (van Swaay et al. 2009c) although <strong>in</strong>itially abandoned meadows can support very high population densities <strong>of</strong> this butterfly. But, after 10-20 years the grassland turns to forest and populations face ext<strong>in</strong>ction. In the long-term this species may be vulnerable to climate change as its distribution is well expla<strong>in</strong>ed by climate variables (Settele et al. 2008c) and <strong>Turkey</strong> is a long way south <strong>of</strong> the ma<strong>in</strong> area <strong>of</strong> distribution. Recommended conservation action This species is listed <strong>in</strong> the EU Habitats Directive Annexes 2 and 4, and the Bern Convention Annex 2. Careful control <strong>of</strong> the implementation <strong>of</strong> habitat management is needed on a site by site basis. For example, damage done by mow<strong>in</strong>g with tractors can be reduced if it takes place early enough, generally before mid June to allow sufficient regrowth <strong>of</strong> the foodplant, or after mid September when the caterpillars have left the flowerheads. However, mechanisation can have a negative effect on the ant nests and this should be monitored. Selected References Balletto, E., Bonelli, S., Settele, J., Thomas, J., Verovnik, R. and Wahlberg, N. (2010) Case 3508: Macul<strong>in</strong>ea van Eecke, 1915 (Lepidoptera:Lycaenidae): proposed precedence over Phengaris Doherty, 1891. BNZ 67(2), pp.129-132. B<strong>in</strong>zenhöfer B. and Settele J. (2000) Vergleichende autökologische Untersuchungen an Glaucopsyche (Macul<strong>in</strong>ea) nausithous Bergstr. und G. (M.) teleius Bergstr. (Lepidoptera, Lycaenidae) im nördlichen Steigerwald. In: Settele, J & Kle<strong>in</strong>ewietfeld S (eds) Populationsökologische Studien an Tagfaltern 2. UFZ- Bericht 2/2000, pp.1-98. Nowicki, P., Pepkowska, A., Kudlek, J., Skorka, P., Witek, M., Settele, J. and Woyciechowski, M. (2007) From metapopulation theory to conservation recommendations: lessons from spatial occurrence and abundance patterns <strong>of</strong> Macul<strong>in</strong>ea butterflies. Biol. Conservation, 140, pp.119–129. Settele, J., Kudrna, O., Harpke, A., Kühn, I., van Swaay, C.A.M., Verovnik, R., Warren, M., Wiemers, M., Haspanch, J., Hickler, T., Kühn, E., van Halder, I., Vell<strong>in</strong>g, K., Vliegenthart, A., Wynh<strong>of</strong>f, I. and Schweiger, O. (2008g) Phengaris nausithous IN: Climatic Risk Atlas <strong>of</strong> European <strong>Butterflies</strong>. S<strong>of</strong>ia, Moscow: Pens<strong>of</strong>t, pp.272-273. Tartally, A., Rákosy, L., Vizauer, T.C., Goia, M. and Varga, Z. (2008) Macul<strong>in</strong>ea nausithous exploits Myrmica scabr<strong>in</strong>odis <strong>in</strong> Transylvania: Unusual Host Ant Species <strong>of</strong> a Myrmecophilous Butterfly <strong>in</strong> an Isolated Region (Lepidoptera:Lycaenidae; Hymenoptera: Formicidae). Sociobiology, 51(2), pp.373-380. van Langevelde, F. and Wynh<strong>of</strong>f, I. (2009) What limits the spread <strong>of</strong> two congeneric butterfly species after their re<strong>in</strong>troduction: quality or spatial arrangement <strong>of</strong> habitat? Animal Conservation, 12, pp.540-548. van Swaay, C., Wynh<strong>of</strong>f, I., Verovnik, R., Wiemers, M., López Munguira, M.,Maes, D., Šašic, M., Verstrael, T., Warren, M. and Settele, J. (2009c) Phengaris nausithous IN: IUCN <strong>Red</strong> List <strong>of</strong> Threatened Species. IUCN 2010. Version 2010.3. [Onl<strong>in</strong>e]. Available from: www.iucnredlist.org. [Downloaded 12 October 2010]. Witek, M., Sliw<strong>in</strong>ska, E.B., Skórka, P., Nowicki, P., Settele, J. and Woyciechowski, M. (2006) Polymorphic growth <strong>in</strong> larvae <strong>of</strong> Macul<strong>in</strong>ea butterflies, as an example <strong>of</strong> biennialism <strong>in</strong> myrmecophilous <strong>in</strong>sects. Oecologia, 148, pp.729–733. Wynh<strong>of</strong>f, I. (2001) At home on foreign meadows. Dissertatie Departement Omgev<strong>in</strong>gswetenschappen, Wagen<strong>in</strong>gen Universiteit en Research Centrum. Assessment date 11.08.2009 Assessors Karaçet<strong>in</strong>, E., Welch, H.J., Sáfián, S., Wynh<strong>of</strong>f, I. & <strong>Red</strong> List Work<strong>in</strong>g Group participants, Ankara 10-12.08.2009 Karaçet<strong>in</strong>, E. and Welch, H.J. (2011). <strong>Red</strong> <strong>Book</strong> <strong>of</strong> <strong>Butterflies</strong> <strong>in</strong> <strong>Turkey</strong>. Ankara, <strong>Turkey</strong>: Doğa Koruma Merkezi. Available from: [www.dkm.org.tr]
001310 Order: LEPIDOPTERA Family: LYCAENIDAE Aricia teberd<strong>in</strong>a (Sheljuzhko, 1934) IUCN Global <strong>Red</strong> List category IUCN Global <strong>Red</strong> List criteria - - RECENT SYNONYMS Scientific: Plebeius teberd<strong>in</strong>us, Polyommatus (Aricia) teberd<strong>in</strong>a English: Georgian False Argus, Caucasian Silvery Argus Turkish: Teberda Çokgözlüsü DISTRIBUTION - Global: Northern slopes <strong>of</strong> the central Greater Caucasus and <strong>Turkey</strong> (Tuzov et al. 2000). In the Russian Caucasus there are two localities; the type locality at Teberda <strong>in</strong> the Chatipara Mts. at 2,200-2,300 m (Sheljuzhko 1934) and Itkol <strong>in</strong> the Elbrus Mts. (Eckweiler 1978). <strong>Red</strong> <strong>Book</strong> <strong>of</strong> <strong>Butterflies</strong> <strong>in</strong> <strong>Turkey</strong> EN Endangered B1ab(iii)+2ab(iii) <strong>Turkey</strong>: Extent Of Occurrence (EOO) post 1980 (km2 )
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Bibliography Abadjiev, S. and Beshk
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van Swaay, C., Wynhoff, I., Verovni
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