Abstract

Land‐use change may alter both species diversity and species functional diversity patterns. To test the idea that species diversity and functional diversity changes respond in differing ways to land‐use changes, we characterize the form of the change in bird assemblages and species functional traits along an intensifying gradient of land use in the savanna biome in a historically homogeneous vegetation type in Phalaborwa, South Africa. A section of this vegetation type has been untransformed, and the remainder is now mainly characterized by urban and subsistence agricultural areas. Using morphometric, foraging and breeding functional traits of birds, we estimate functional diversity changes. Bird species richness and abundance are generally higher in urban and subsistence agricultural land uses, as well as in the habitat matrix connecting these regions, than in the untransformed area, a pattern mainly driven through species replacement. Functionally unique species, particularly ground nesters of large body size, were, however, less abundant in more utilized land uses. For a previously homogenous vegetation type, declines in the seasonality of energy availability under land‐use change have led to an increase in local avian diversity, promoting the turnover of species, but reduced the abundance of functionally unique species. Although there is no simple relationship between land‐use and diversity change, land‐use change may suit some species, but such change may also involve functional homogenization.

Highlights

  • Human population expansion is unlikely to stabilize in the 21st century (Gerland et al 2014)

  • We focus our study on an exemplar African savanna ecosystem in and around the Kruger National Park (KNP), South Africa

  • We examined the changes in the body size of species assemblages between land uses with body size frequency distribution (BSFD) histograms using body mass in grams for all species (Coetzee et al 2013)

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Summary

Introduction

Human population expansion is unlikely to stabilize in the 21st century (Gerland et al 2014). Understanding the impact of urban and agricultural intensification on biodiversity is of particular importance, as they form a substantial component of human land-use activities. From 1700 to 2000, agriculture and urban settlement increased from 5% to 39% of the earth’s total ice-free terrestrial surface (Ellis et al 2010). Both urbanization (Evans et al 2011) and agriculture (Tilman 1999) continue to expand rapidly, with a concomitant expected decrease in biodiversity (Vitousek et al 1997; Foley et al 2005; Dobrovolski et al 2013)

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