Abstract

Loss of biodiversity caused by impact of elephants (Loxodonta africana) on African woodlands may require a management response, but any action should be based on an understanding of why elephants choose to utilise trees destructively. Comprehension of elephant feeding behaviour requires consideration of the relative value of the plant groups they may potentially consume. Profitability of available food is partly determined by the time to locate a food patch and, therefore, as a foundation for understanding the influence of food availability on diet selection, key controls on the density of grass, forb, and browse patches were investigated across space and time in a semi-arid African savanna. Density of food patches changed seasonally because plant life-forms required different volumes of soil water to produce green forage; and woody plants and forbs responded to long-term changes in soil moisture, while grasses responded to short-term moisture pulses. Soil texture, structure of woody vegetation and fire added further complexity by altering the soil water thresholds required for production of green forage. Interpolating between regularly-timed, ground-based measurements of food density by using modelled soil water as the predictor in regression equations may be a feasible method of quantifying food available to elephants in complex savanna environments.

Highlights

  • African savannas are characterised by a predominance of woody plants and grasses (Huntley, 1982), but they support a richness of herbaceous dicotyledons

  • Density of herbaceous forage patches was successfully modelled from soil water using the sigmoidal functions (Fig. 3)

  • Food availability for elephants changed seasonally primarily because grasses, forbs and woody plants required different volumes of soil water for development and maintenance of green foliage, and they responded to fluctuations in soil moisture over different time gforbs gleaves 45

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Summary

Introduction

African savannas are characterised by a predominance of woody plants and grasses (Huntley, 1982), but they support a richness of herbaceous dicotyledons (forbs). Savanna elephants (Loxodonta africana) harvest food from all these plant types (Barnes, 1982; Field, 1971; Kabigumila, 1993), but their conspicuous impact on woody plants has the greatest potential to cause long-term vegetation change (Lamprey et al, 1967; Laws, 1970b; Leuthold, 1977). Over time, this behaviour may simplify the structure and composition of woodlands (O’Connor & Page, 2014), jeopardising the persistence of impacted species (Lombard et al, 2001; O’Connor, Goodman & Clegg, 2007) and the biota that are dependent. The threat of local extirpation of some impacted woody species (O’Connor, Goodman & Clegg, 2007) begs a management response, but any action should be founded upon an understanding of why elephants choose to use woody plants in a destructive manner

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