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Cerna K. et al.<br />
Lepidoptera in Sudetes Mts.: effect of area and isolation<br />
The aim of this paper is (a) to quantify the differences in species composition of<br />
the alpine islands in the High Sudetes Mts., (b) to test the effects of isolation and area on<br />
species richness and (c) to propose conservation priorities concerning selected alpine<br />
sites.<br />
2. Materials and methods<br />
The High Sudetes Mts. consist of three disjunct mountain systems, the Krkonose Mts.<br />
(Riesengebirge/Giant Mts.), the Hruby Jesenik Mts. (Altvatergebirge) and the Kralicky<br />
Sneznik Mts. (Glatzer Schneegebirges), and shape a natural border between the Czech<br />
Republic and Poland. Geologically, their surface is rather uniform, build by granite,<br />
gneiss, and mica schist (Treml and Banas, 2000). The alpine timberline is formed by<br />
Norway spruce (Picea abies) and dwarf pine (Pinus mugo), which is however artificially<br />
planted in the Hruby Jesenik Mts. and slowly overgrowing alpine grasslands dominated<br />
by Calluna vulgaris, Vaccinium myrtillus, Vaccinium vitis-idaea, Avenella flexuosa,<br />
Nardus stricta, Festuca supine and Molinia coerullea.<br />
All available sources (Table 1) related to these mountain ranges were critically<br />
reviewed and list of Lepidoptera species was compiled for each alpine site of the High<br />
Sudetes Mts. (Table 2): Krkonose-West (Kotel Mt. – 1435 m), Krkonose-East<br />
(Snezka/Schneekoppe – 1602 m), Kralicky Sneznik (1424 m), Serak (1351 m), Keprnik<br />
(1423 m), Cervena hora (1337 m), Maly Ded (1355 m), Mravenecnik-Vresnik (1343 m),<br />
Praded (1491 m) and Vysoka hole (1464 m); the last 7 alpine sites are parts of the Hruby<br />
Jesenik Mts. (Fig. 1). The examined list (Table 2) includes only “diagnostic species”, i.e.,<br />
species with an exclusive affinity for alpine habitats of the High Sudetes Mts. or<br />
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