Abstract

Hunting and logging, ubiquitous human disturbances in tropical forests, have the potential to alter the ecological processes that govern population recruitment and community composition. Hunting-induced declines in populations of seed-dispersing animals are expected to reduce dispersal of the tree species that rely on them, resulting in potentially greater distance- and density-dependent mortality. At the same time, selective logging may alter competitive interactions among tree species, releasing remaining trees from light, nutrient or space limitations. Taken together, these disturbances may alter the community composition of tropical forests, with implications for carbon storage, biodiversity conservation and ecosystem function. To evaluate the effects of hunting and logging on tree fecundity and seed dispersal, we use 3 years of seed rain data from a large-scale observational experiment in previously logged, hunted and protected forests in northern Republic of Congo (Brazzaville). We find that low-intensity logging had a meaningful long-term effect on species-specific seed dispersal distances, though the direction and magnitude varied and was not congruent within dispersal vector. Tree fecundity increased with tree diameter, but did not differ appreciably across disturbance regimes. The species-specific dispersal responses to logging in this study point towards the long-lasting toll of disturbance on ecological function and highlight the necessity of conserving intact forest.

Highlights

  • Logging concessions cover almost 56 million ha of forest in West and Central Africa (FAO 2016)

  • Two-thirds of all species (22/33) in disturbed forests had 95 % credible intervals (CIs) for dispersal parameters that did not overlap with estimates from protected plots, indicating a role of disturbance

  • Of the 22 species affected by disturbance, 17 species showed an effect of logging alone: nine species had higher dispersal estimates in logged compared to protected forest (Celtis mildbraedii, Diospyros canaliculata, Erythrophleum suaveolens, Greenwayodendron suaveolens, Lannea welwitschii, Pausinystalia macroceras, Rinorea oblongifolia, Staudtia kamerunensis, Strombosia nigropunctata), and eight species had lower dispersal estimates (Cleistopholis patens, Grossera macrantha, Myrianthus arboreus, Macaranga barteri, Nesogordonia kabingaensis, Strombosiopsis tetrandra, Thomandersia hensii, Terminalia superba)

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Summary

Introduction

Logging concessions cover almost 56 million ha of forest in West and Central Africa (FAO 2016). Tropical trees respond to environmental disturbance on timescales that usually surpass the duration of ecological studies (Gourlet-Fleury et al 2013; Edwards et al 2014; Berdanier and Clark 2015) and changes in tree fecundity and seed dispersal may persist long after disturbance has ended, potentially altering ecosystem function. Logging directly disturbs tropical forest communities through the extraction of large trees (Laurance et al 2000), residual damage to remaining trees (Kasenene and Murphy 1991) and disruption of seed-dispersing animal communities (Gutiérrez-Granados 2011; Haurez et al 2016; Rosin and Poulsen 2016). Reductions in vertebrate dispersers may affect the approximately two-thirds of all woody plants that rely on animals for seed dispersal (Willson and Traveset 2000; Muller-Landau and Hardesty 2005; Beaune et al 2013). Dispersal failure has consequences for community composition through density-dependent recruitment (Cannon et al 1994; Bleher and Böhning-Gaese 2001) and competition at later life stages (Nathan and Muller-Landau 2000)

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