Abstract

Functional Diversity is considered an important driver of community assembly in environmental and successional gradients. To understand tree assembly processes in a semideciduous tropical forest, we analyzed the variation of Functional Richness (FRic), Functional Divergence (FDiv), and Functional Evenness (FEve) of small vs. large trees in relation to fallow age after slash-and-burn agriculture and topographical position (flat sites vs. hills). FRic of small trees was lower than null model predicted values across the successional gradient, and decreased unexpectedly in older successional ages. FRic of large trees was higher than null model predictions early in succession and lower in late-successional stands on hills. Dominant species were more similar (low FDiv) in early and intermediate successional stands for small trees, and on hills for large trees, suggesting that species that are best adapted to harsh conditions share similar traits. We also found evidence of competitive exclusion among similar species (high FEve) for small trees in early successional stands. Overall, our results indicate that community assembly of small trees is strongly affected by the changing biotic and abiotic conditions along the successional and topographical gradient. For large trees, hills may represent the most stressful conditions in this landscape.

Highlights

  • Tropical dry forests (TDF), characterized by a dry period of several months, a mean annual rainfall between 400 and 1700 mm, and a ratio of rainfall to potential evapotranspiration greater than unity, is one of the most extensive ecosystems in the tropics [1,2]

  • Our results suggest a thorough use of resources by large trees in early successional and intermediate forests (3 to 25 years old) on flat sites, reflecting maximum variation in ecological strategies and positive Functional Richness (FRic) values (Figure 2b), probably due to the coexistence of pioneers, generalists and old-growth forest specialists

  • We found that FRic differed significantly from null model expected values in all successional ages and topographic positions, while Functional Divergence (FDiv) differed from the null model only in successional ages 1 and 2 and Functional Evenness (FEve) only in age 1 (Table 3)

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Summary

Introduction

Tropical dry forests (TDF), characterized by a dry period of several months, a mean annual rainfall between 400 and 1700 mm, and a ratio of rainfall to potential evapotranspiration greater than unity, is one of the most extensive ecosystems in the tropics [1,2]. Because the severe dry season facilitates vegetation removal with fire and the suppression of pests and weeds [2,3,4] it is one of the ecosystems most threatened by land conversion. This land use change has produced a mosaic of tropical dry forest patches of different successional ages, which may offer an opportunity to further our understanding of assembly patterns and processes during secondary succession in this human-modified system [5]. Young successional forest stands are dry, sunny, and hot, because early plant communities have small stature and offer little cover, have small basal area and a small leaf area index [6,7,8,9,10].

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