Abstract

AbstractUnderstanding how species are non‐randomly distributed in space and how the resulting spatial structure responds to ecological, biogeographic, and anthropogenic drivers is a critical piece of the biodiversity puzzle. However, most metrics that quantify the spatial structure of diversity (i.e., community differentiation), such as Whittaker’s β‐diversity, depend on sampling effort and are influenced by species pool size, species abundance distributions, and numbers of individuals. Null models are useful for identifying the degree of differentiation among communities due to spatial structuring relative to that expected from sampling effects, but do not accommodate the influence of sample completeness (i.e., the proportion of the species pool in a given sample). Here, we develop an approach that makes use of individual‐ and coverage‐based rarefaction and extrapolation, to derive a metric, βC, which captures changes in intraspecific aggregation independently of changes in the species pool size. We illustrate the metric using spatially explicit simulations and two case studies: (1) a re‐analysis of the “Gentry” plot data set consisting of small forest plots spanning a latitudinal gradient from North to South America and (2) comparing a large plot in high diversity tropical forests of Barro Colorado Island, Panama, with a plot in a lower diversity temperate forest in Harvard Forest, Massachusetts, USA. We find no evidence for systematic changes in spatial structure with latitude in these data sets. As it is rooted in biodiversity sampling theory and explicitly controls for sample completeness, our approach represents an important advance over existing null models for spatial aggregation. Potential applications range from better descriptors of biogeographic diversity patterns to the consolidation of local and regional diversity trends in the current biodiversity crisis.

Highlights

  • Species are non-randomly distributed across the globe, and understanding spatial patterns of species diversity from ecological samples remains a central challenge (Gaston 2000, McGill 2011, Worm and Tittensor 2018)

  • This and other measures of β-diversity are influenced by the size and number of samples, the size of the regional species pool, the shape of the regional species abundance distribution (SAD), and the number of individuals captured by the samples (McGill 2011, Chase and Knight 2013, Chase et al 2018)

  • Building on previous work using rarefaction and coverage-based approaches (Chao and Jost 2012, Chao et al 2014, Chase et al 2018, McGlinn et al 2019), we developed a metric standardized by sample coverage to quantify the degree of intraspecific spatial aggregation, independent of changes in the size of the species pool and the regional SAD

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Summary

INTRODUCTION

Species are non-randomly distributed across the globe, and understanding spatial patterns of species diversity from ecological samples remains a central challenge (Gaston 2000, McGill 2011, Worm and Tittensor 2018). Chase et al (2018) suggested that when calculated at a common number of individuals (n), the ratio of rarefied richness (Sn) calculated between the γ- and α-scales, termed βSn , could provide an indication of the degree of intraspecific aggregation, or non-randomness in the distribution of species in the assemblage, independent of any sampling effect (see McGlinn et al 2019). As we will illustrate below, βSn is biased when comparing the degree of aggregation among regions where species pools and shapes of the γ-scale IBRE curves change (e.g., along biogeographical gradients) To visualize this problem, consider two assemblages each composed of two patches, but which differ in the size of their regional species pool (500 vs 100 species Fig. 2A, B, respectively). Let Ctarget be the smallest of the Cn values across all assemblages

Calculate βC
Findings
DISCUSSION AND CONCLUSIONS
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