Abstract

There is still considerable debate about the relative importance of resource heterogeneity and resource quantity in the maintenance of species diversity in a community. The resource heterogeneity hypothesis proposes that spatial heterogeneity of limiting resources and inter-specific differences in resource requirements will determine species richness. In contrast, the resource quantity hypothesis predicts that average resource supply rates contribute to species richness by their effects on plant density and stochastic population dynamics. However, the evaluation of the two hypotheses in observational studies is associated with a major methodological challenge as average resource supply rate often covaries with resource heterogeneity. Using a novel approach derived from the relationships between average resource supply rate, resource heterogeneity (calculated as the standard deviation of environmental factors) and plant density in the resource hypotheses, we evaluated the relative importance of resource quantity and resource heterogeneity with a variation partitioning model in Gutianshan (GTS) forest plot, China and Barro Colorado Island (BCI) forest plot, central Panama. We found that resource quantity explained much less of the variation in species richness than resource heterogeneity in both of GTS and BCI (44.5% vs 4.9% in GTS and 20.4% vs 0.8% in BCI at the 20×20 m scale, 57.5% vs 3.4% in GTS at the 40×40 m scale and 34.5% vs 2.6% in BCI at the 50×50 m scale). We also found that resource heterogeneity governed species richness in GTS, whereas spatial processes dominated species diversity in BCI. Moreover, most of the effect of resource heterogeneity and resource quantity on species richness overlapped with that of spatial processes. This result indicates that most effects of resources could also be explained by spatial processes, such as dispersal limitation. Therefore, resource heterogeneity and spatial processes, but not resource quantity played an important role in determining species diversity in these two old-growth forests. This is in contrast to the results of several manipulative studies, which found that resource quantity governed species diversity when one or a limited number of resources were considered. This suggests that the processes determining species richness along ecological gradients are complicated and determined by the interaction of various processes.

Highlights

  • Disentangling the importance of different processes in determining the species diversity of biotic communities has been an enduring challenge for ecologists (Ricklefs and Schluter, 1993; Abrams, 1995; Barot, 2004)

  • The present work asked a central question: what is the relative contribution of resource quantity and resource heterogeneity to species diversity maintenance? We first addressed this question by partitioning the variation in species richness at GTS and Barro Colorado Island (BCI) into fractions explained by resource heterogeneity, resource quantity, and plant density (Figures 2A,B and Table 1)

  • In GTS only 4.9% of the variation in species richness was explained by resource quantity, which contrasted markedly with 44.5% of the variation explained by resource heterogeneity at the 20 × 20 m scale (Figure 2A and Table 1)

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Summary

Introduction

Disentangling the importance of different processes in determining the species diversity of biotic communities has been an enduring challenge for ecologists (Ricklefs and Schluter, 1993; Abrams, 1995; Barot, 2004). At opposite ends of a spectrum, the resource quantity hypothesis proposes that the species richness is determined by the average supply rates of limiting resources, through stochastic population dynamics (Wright, 1983; Stevens and Carson, 2002), while the resource heterogeneity hypothesis suggests that species richness is a function of the spatial heterogeneity in resource supply and inter-specific differences in resource requirements (Ricklefs, 1977; Huston, 1979; Stein et al, 2014). The close spatial covariation of resource quantity and resource heterogeneity has presented an enduring challenge in measuring their separate effects on species diversity (Stevens and Carson, 2002) and has hampered our ability to draw general conclusions regarding the mechanisms of diversity maintenance

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