Abstract

In 2016, we studied the occurrence of amphibians in 231 selected ponds in the city of Wrocław (Lower Silesia, Poland) and confirmed the occurrence of 10 species: Bombina bombina, Bufo bufo, Bufotes viridis, Hyla arborea, Pelobates fuscus, Pelophylax esculentus complex, Rana arvalis, Rana temporaria, Lissotriton vulgaris and Triturus cristatus. Among all studied sites, the most common were P. esculentus complex (146 occupied sites, 63.2%) and B. bufo (119, 51.5%), while the rarest was P. fuscus (8, 3.5%). The number of species at a single site varied from 0 (28 sites, 12.1%) to 9 (1 site, 0.4%). Frequency and mean amphibian species richness reached 87.9% and 2.7 ± 1.9, respectively. The composition of amphibian species did not change in comparison to previous studies conducted in the years 1997–2009, but declining trends in five species (B. bombina, B. viridis, H. arborea, P. esculentus complex, P. fuscus) were observed (28 compared sites). The results revealed that the permanency of ponds, their occurrence in the vicinity of river valleys, and a high ratio of watercourse length and green area around ponds are positively correlated and have a significant influence on amphibian species richness within the city. Thus, these identified factors should be considered in the course of sustainable urban planning in order to avoid potential conflicts between nature conservation and urban development.

Highlights

  • Urbanisation and progressive changes in land use are considered to exert some of the strongest influences on amphibian populations worldwide

  • In the case of 5 species (B. bombina, B. viridis, H. arborea, P. esculentus complex, P. fuscus) extinction events were more frequent than colonisation events, but in the remaining 5 species (B. bufo, R. arvalis, R. temporaria, L. vulgaris, T. cristatus) the trend was opposite

  • After comparison with data collected in the years 1997–2009 (Ogielska and Kierzkowski 2010), our study did not confirm the loss of any amphibian species; declining trends were observed in several species

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Summary

Introduction

Urbanisation and progressive changes in land use are considered to exert some of the strongest influences on amphibian populations worldwide. Amphibians are vulnerable to adverse changes in their habitats during both the aquatic and terrestrial life stages. Larvae, and tadpoles remain in streams, ponds, and wetlands for months or even a full year. Juveniles are often dispersed from their natal ponds Sinsch 1992), while adults of many frog, toad, and salamander species migrate seasonally between terrestrial (where they hide or hunt) and aquatic (where they breed) habitats (Vos and Stumpel 1996; Vos et al 2001; Semlitsch and Bodie 2003).

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