Abstract

AbstractSecondary forests dominate some human‐modified tropical biomes, and this is expected to increase via both abandonment of marginal agricultural land as well as forest and landscape restoration programmes. A key question is whether promoting the recovery and protection of secondary tropical forests will return invertebrate functional diversity and associated functional traits. Dung beetles are ideal for assessing functional diversity as they play vital roles in several ecosystem functions, including seed dispersal, nutrient cycling and bioturbation. We examined how taxonomic and functional diversity, and the functional trait composition of native dung beetle species recovers in naturally regenerating secondary forests in comparison to both cattle pastures and primary forest in the Colombian Choco‐Andes, a global hotspot of threatened biodiversity. Using a space‐for‐time approach, we found that taxonomic and functional diversity recovered to levels comparable to primary forest within approximately 30 years of secondary forest regrowth. Functional richness and FD, measures of the diversity of traits present in a community, were similar in secondary and primary forest, but significantly lower in pasture. Rolling dung beetle species were positively associated with forest habitats, particularly primary, while dwelling species were more common in pasture. Thus, the functional trait composition of secondary forests was more similar to primary forest than to pasture. The ability of secondary forests to rapidly accumulate primary‐forest dung beetle functional diversity, and a representative suite of functional traits, provides an opportunity to protect biodiversity and ecosystem functioning, especially in regions where marginal agricultural land allows cost‐effective conservation actions.

Highlights

  • Agricultural expansion is driving tropical land-use change, resulting in the conversion of over 150 million hectares of tropical forest between 1980 and 2012 (Gibbs et al, 2010; Hansen et al, 2013)

  • Primary forest had the greatest abundance of individuals (9750), followed by secondary forest (7351), with cattle pasture having the lowest number of individuals (585)

  • Secondary forest taxonomic diversity and evenness did not differ from primary forest, but was significantly greater than in pasture (Fig. 1; X2 = 13.738, d.f. = 2, P < 0.01; evenness, X2 = 15.236, d.f. = 2, P < 0.001)

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Summary

Introduction

Agricultural expansion is driving tropical land-use change, resulting in the conversion of over 150 million hectares of tropical forest between 1980 and 2012 (Gibbs et al, 2010; Hansen et al, 2013). This habitat loss and subsequent fragmentation effects are the leading cause of tropical biodiversity decline (Laurance et al, 2014). For example 36.2 million hectares of secondary forest regrew between 2000 and 2010 in Latin America and the Caribbean (Aide et al, 2013), especially in the tropical Andes, Brazilian Caatinga and Costa Rica (Nanni et al, 2019). Farmland is abandoned due to complex socioeconomic and biophysical drivers, especially steep topography and related agricultural marginality, climate, declining rural populations and urbanization (Lambin & Meyfroidt, 2010; Nanni et al, 2019), allowing secondary forests to naturally regenerate

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