Abstract

Lantana camara L. (Verbenaceae) originates from tropical Central and South America and has become invasive in about 50 countries. It causes problems when invading rangelands due to its toxicity to livestock and its tendency to form dense, monotonous thickets. Its invasiveness can partly be explained by the high tannin content largely protecting the species from being browsed, its tolerance to a wide range of environmental conditions, as well as its general preference for anthropogenically disturbed habitats. The dispersal of L. camara is facilitated by birds and other animals consuming its drupes (endozoochory), and so both wild and domestic ungulates could contribute to its spread. In our study, we investigated the distribution of L. camara in the Mutara rangelands of north-eastern Rwanda, an area that faced dramatic landscape changes in recent decades. We assessed 23 ecological factors and factors related to land-use and conservation-political history. Major effects on the local abundance of L. camara were found in that the relative canopy cover of L. camara was negatively correlated with the occurrence of other shrubs (suggesting competition for space and nutrients), while encounter rates of houses, ‘living fences’ (Euphorbia tirucalli L.) and cattle tracks were positively correlated with L. camara cover. Hence, the spread of non-native L. camara in the Mutara rangelands appears to be linked to landscape alterations arising from the transformation of rangelands supporting traditional pastoralist communities to other agricultural land-use forms.

Highlights

  • One of the major threats to global biodiversity is the spread of invasive species [1,2,3]

  • In the case of Lantana camara and Cymbopogon nardus, we found significant effects of environmental variables, condensed into six principal components (PCs) (Table 1), while percentage cover of Dichrostachys cinerea was not affected by any PC (Table 2)

  • ANCOVAs (General Linear Models, GLM) revealed that percentage cover of L. camara and C. nardus were significantly affected by PC2, which received axis loadings (>|0.50|)

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Summary

Introduction

One of the major threats to global biodiversity is the spread of invasive species [1,2,3]. This applies usually to exotic (non-native) species that—once introduced and established in a new area—increase rapidly in local abundance and have negative impacts on the native flora or fauna [4]. Hybridization between native and introduced species can occur; e.g., invasive Spartina alterniflora Loisel. Biological invasions can impact human livelihoods through environmental and economic costs arising from the uncontrolled spread of invasive species (e.g., in the United States of America an estimated 137 billion USD annually [15,21])

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