Abstract

The rich species pool in semi-natural grasslands is associated with high spatial and temporal heterogeneity. This empirical study is one of the first to jointly analyze the response of orders, individual species and functional richness of arthropods to particular management practices and to linear landscape features, such as strips of grass and belts of trees. Mostly it was the less mobile, flightless taxa that were negatively affected by immediate disturbance caused by mowing. At a larger time-scale, grasslands managed by mow- ing once every year, and especially by a combined regime of mowing and grazing, supported the highest species richness of butterflies and beetles. Most functional diversity measures reached maximum values soon after mowing. Both strips of grass and belts of trees substantially affected the invertebrate community structure as the majority of taxa were positively associated with these linear features. Based on our results, we propose postponing mowing to later in the year, mowing in gradual stages, maintaining uncut strips primar - ily along permanent landscape features and establishing both strips of grass and belts of trees in submontane grassland environments.

Highlights

  • A substantial proportion of the Central European biodiversity occurs in semi-natural grasslands

  • In this study we evaluate the association of invertebrate communities in submontane meadows and pastures in the Czech Republic with agricultural management and local landscape structure

  • We evaluated the association of the community structure of invertebrates with various types of grassland management, with particular reference to both the immediate effects of mowing and grazing and the long-term effects of each management treatment

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Summary

Introduction

A substantial proportion of the Central European biodiversity occurs in semi-natural grasslands. Existence of this widespread type of open habitat is dependent on disturbance, which prevents succession towards forest. Nonforest areas were traditionally maintained by grazing and hay-making (Duffey et al, 1974) Both types of land use differed in terms of intensity of use, which often fluctuated in space and time, creating a wide spectrum of microhabitats and promoting high species richness and diversity (Benton et al, 2003; Davies et al, 2005). The 20th century brought two interrelated trends, both of which led to the loss of spatial and temporal heterogeneity This resulted in a depletion of originally diverse communities of grasslands. Semi-natural grasslands still play a key role in the preservation of a considerable part of non-forest biodiversity associated with the cultural landscape in Europe (Poschlod & WallisDeVries, 2002; Woodcock et al, 2005; Baur et al, 2006)

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