Ábrahám Levente (szerk.): Válogatott tanulmányok VII. - Natura Somogyiensis 22. (Kaposvár, 2012)

Winkler D. - Erdő Á.: A comparative study of breeding bird communities in representative habitats of the Sárosfő Nature Reserve area

Winkler D. & Erdő Á.: Breeding bird communities 219 Table 3: Comparison of Shannon diversities using Hutcheson's t-test (t-values, ***P=0.01; **P=0.05; *P=0.1; ns - not significant) reedbed meadow oak afforestation oak forest meadow 0.0323 ns oak afforestation 6.0413" 4.7602" oak forest 5.4661" 4.3086" 0.7881 ns ash-aldcr forest 9.2026'" 7.0226"' 3.9198"' 4.8414'" pine forest 1.9473 ns 1.7179 ns 2.7483' 2.2712' ash-aldcr forest 5.0552"' allochthonous Scots pine forest. Nevertheless, this habitat was responsible for the occur­rence and nesting of species connected to coniferous forest, such as the Coal Tit (Parus ater) or the Crested Tit (Parus cristatus), thus increasing the summarized species rich­ness of the whole study area. Shannon diversity showed a similar trend (Fig. 2b) expressed in species richness. Its numerical value was the highest (3.013) in the riverine ash-alder woodland area while the lowest (1.205) in the reed habitat. Breeding pair density was the highest (64.54 pairs/10 ha) in the riverine ash-alder for­est, but it was also considerable (~44 pairs/10 ha) in the low pole oak stand (Fig. 2c). Total density of bird community was fairly low (~6 pairs/10 ha) in the reed and meadow habitats. The community dominance index is a simple characteristic calculated as the percent­age of the total abundance of all species in the community that is contributed by the two most abundant species (Fig. 2d). It can therefore be an appropriate characteristic for evaluating the dominance structure of bird communities. Its value was considerably high in the reedbed and meadow habitats that can be explained with the low number of spe­4» 4X 0 96 1 92 2 44» alpha Fig. 3: Diversity profiles of breeding bird communities in the different habitats

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