Abstract

Understanding how land-use change affects biodiversity is a fundamental step to develop effective conservation strategies in human-modified tropical landscapes. Here, we analyzed how land-use change through tropical small-scale agriculture affects endemic, exotic, and non-endemic native ant communities, focusing on vanilla landscapes in north-eastern Madagascar, a global biodiversity hotspot. First, we compared ant species richness and species composition across seven land-use types: old-growth forest, forest fragment, forest-derived vanilla agroforest, fallow-derived vanilla agroforest, woody fallow, herbaceous fallow, and rice paddy. Second, we assessed how environmental factors drive ant species richness in the agricultural matrix to identify management options that promote endemic and non-endemic native while controlling exotic ant species. We found that old-growth forest, forest fragment, and forest-derived vanilla agroforest supported the highest endemic ant species richness. Exotic ant species richness, by contrast, was lowest in old-growth forest but highest in herbaceous fallows, woody fallows, and rice paddy. Rice paddy had the lowest non-endemic native ant species richness. Ant species composition differed among land-use types, highlighting the uniqueness of old-growth forest in harboring endemic ant species which are more sensitive to disturbance. In the agricultural matrix, higher canopy closure and landscape forest cover were associated with an increase of endemic ant species richness but a decrease of exotic ant species richness. We conclude that preserving remnant forest fragments and promoting vanilla agroforests with a greater canopy closure in the agricultural matrix are important management strategies to complement the role of old-growth forests for endemic ant conservation in north-eastern Madagascar.

Highlights

  • Tropical forests harbor the highest proportion of biodiversity worldwide (Myers et al 2000)

  • Rice paddy had significantly lower non-endemic native ant species richness compared to forest fragment (p < 0.01), forest-derived vanilla agroforest species richness a a (a) endemic (b) exotic a b bc cd d c c c c ab bc a (c) non−endemic

  • We found a significant gradient in the endemic (PERMANOVA, df = 6, F = 2.96, R­ 2 = 0.23, p = 0.001), exotic (PERMANOVA, df = 6, F = 8.88, ­R2 = 0.42, p = 0.001), and non-endemic native (PERMANOVA, df = 6, F = 5.93, ­R2 = 0.35, p = 0.001) ant species composition across land-use types (Fig. 3)

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Summary

Introduction

Tropical forests harbor the highest proportion of biodiversity worldwide (Myers et al 2000) They are decimated and fragmented due to human land use, often resulting in a mosaic landscape consisting of forest patches and various agricultural land-use systems (Grass et al 2020). The structure of ant community may be driven by environmental factors such as canopy openness, vegetation structure, deadwood volume, and landscape forest cover (Luke et al 2014; Solar et al 2016). Analyzing how these factors influence species richness can help identify land-use management options that result in few exotic species to efficiently preserve the native (endemic) ant community

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