Abstract

Organismal distributions in human-modified landscapes largely depend on the capacity of any given species to adapt to changes in habitat structure and quality. The golden-headed lion tamarin (GHLT; Leontopithecus chrysomelas) is an Endangered primate from the Brazilian Atlantic Forest whose remaining populations occupy heterogeneous landscapes consisting primarily of shade cacao (Theobroma cacao) agroforestry, locally known as cabrucas. This cash crop can coexist with high densities of native tree species and holds a significant proportion of the native fauna, but its widely extolled wildlife-friendly status is increasingly threatened by management intensification. Although this potentially threatens to reduce the distribution of GHLTs, the main determinants of tamarin's occupancy of cabrucas remain unknown, thereby limiting our ability to design and implement appropriate conservation practices. We surveyed 16 cabruca patches in southern Bahia, Brazil, and used occupancy modeling to identify the best predictors of GHLT patch occupancy. Key explanatory variables included vegetation structure, critical resources, landscape context, human disturbance, and predation pressure. We found a negative relationship between GHLT occupancy and the prevalence of jackfruit trees (Artocarpus heterophylus), which is likely associated with the low representation of other key food species for GHLTs. Conversely, cabrucas retaining large-diameter canopy trees have a higher probability of GHLT occupancy, likely because these trees provide preferred sleeping sites. Thus, key large tree resources (food and shelter) are currently the main drivers of GHLT occupancy within cabruca agroecosystems. Since both factors can be directly affected by crop management practices, intensification of cabrucas may induce significant habitat impacts on GHLT populations over much of their remaining range-wide distribution.

Highlights

  • As a result of burgeoning human demands on Earth's natural resources, human‐modified landscapes have expanded relentlessly, in species‐rich biomes (Watson et al, 2016)

  • Several features of the habitat structure and management of cabruca were sampled within seven 200 m2 plots (Figure 3) at each site in the same period of golden‐headed lion tamarin (GHLT) surveys to assess 15 variables (Table S4): (a) density of shade trees; (b) canopy height; (c) canopy connectivity; (d) vertical stratification; (e) species richness of shade trees; (f) equitability of shade tree species; (g) Importance Value Index (IVI; Curtis & McIntosh, 1951) of key resource trees; (h) IVI of jackfruit trees; (i) mean diameter at breast height (DBH) of shade trees; (j) abundance of woody lianas; (k) abundance of bromeliads; (l) abundance of banana trees; (m) management intensity; (n) density of cacao trees; (o) percentage of shading

  • We investigated the determinants of GHLT occupancy within cabrucas of southern Bahia, Brazil, focusing on the specific influence of vegetation structure, habitat quality, agroforestry management intensity, landscape context, and predation pressure

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Summary

| INTRODUCTION

As a result of burgeoning human demands on Earth's natural resources, human‐modified landscapes have expanded relentlessly, in species‐rich biomes (Watson et al, 2016). According to the Executive Committee of the Cacao Cropland Plan (CEPLAC), cabrucas should retain between 25 and 30 shade trees/ha (Mandarino, 1981), but traditional cabrucas of this region usually retain a much higher tree density: an average of 197 (70–480) shade trees/ha of which ~63% (18–100%) are native species (Schroth et al, 2015) These cabrucas maintain a vegetation complexity that enables a significant proportion of native fauna to use them as habitat, supplementary resources, and/or dispersal corridors between forest patches (Faria, Paciencia, Dixo, Laps, & Baumgarten, 2007). Patch occupancy should be negatively related to (d) predation risk (i.e., an abundance of potential predators); and (e) management intensification of shade‐cacao plantations (i.e. high frequency of weeding, high density of cacao trees, and low shade cover)

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