Abstract

Quantifying and assessing changes in biological diversity are central aspects of many ecological studies, yet accurate methods of estimating biological diversity from sampling data have been elusive. Hill numbers, or the effective number of species, are increasingly used to characterize the taxonomic, phylogenetic, or functional diversity of an assemblage. However, empirical estimates of Hill numbers, including species richness, tend to be an increasing function of sampling effort and, thus, tend to increase with sample completeness. Integrated curves based on sampling theory that smoothly link rarefaction (interpolation) and prediction (extrapolation) standardize samples on the basis of sample size or sample completeness and facilitate the comparison of biodiversity data. Here we extended previous rarefaction and extrapolation models for species richness (Hill number qD, where q = 0) to measures of taxon diversity incorporating relative abundance (i.e., for any Hill number qD, q > 0) and present a unified approach for both individual‐based (abundance) data and sample‐based (incidence) data. Using this unified sampling framework, we derive both theoretical formulas and analytic estimators for seamless rarefaction and extrapolation based on Hill numbers. Detailed examples are provided for the first three Hill numbers: q = 0 (species richness), q = 1 (the exponential of Shannon's entropy index), and q = 2 (the inverse of Simpson's concentration index). We developed a bootstrap method for constructing confidence intervals around Hill numbers, facilitating the comparison of multiple assemblages of both rarefied and extrapolated samples. The proposed estimators are accurate for both rarefaction and short‐range extrapolation. For long‐range extrapolation, the performance of the estimators depends on both the value of q and on the extrapolation range. We tested our methods on simulated data generated from species abundance models and on data from large species inventories. We also illustrate the formulas and estimators using empirical data sets from biodiversity surveys of temperate forest spiders and tropical ants.

Highlights

  • The measurement and assessment of biological diversity is an active research focus of ecology (Magurran 2004, Magurran and McGill 2011) and a central objective of many monitoring and management projects (Groom et al 2005, CBD 2012)

  • To compare diversities between the Girdled and Logged treatments, we show in Fig. 3b, for each fixed value of q (q = 0, 1, and 2), the sample-size-based rarefaction and extrapolation of these two plots with 95% confidence intervals up to a base sample size

  • We have developed a new, comprehensive statistical framework for the analysis of biodiversity data based on Hill numbers

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Summary

Introduction

The measurement and assessment of biological diversity (biodiversity) is an active research focus of ecology (Magurran 2004, Magurran and McGill 2011) and a central objective of many monitoring and management projects (Groom et al 2005, CBD 2012). The simplest and still the most frequently used measure of biodiversity is the species richness of an assemblage. Observed species richness is highly sensitive to sample size (the sampling problem). Because most species in an assemblage are rare, biodiversity samples are usually incomplete, and undetected species are a common problem. The observed number of species in a well-defined biodiversity sample (species density, sensu Gotelli and Colwell 2001) is known to be a biased underestimate of true species richness, and is highly sensitive to the area surveyed, the number of individuals counted, and the number of samples scored for species occurrence (incidence; Colwell and Coddington 1994). A second problem with species richness as a measure of biodiversity is that it does not incorporate any information about the relative abundance of species (the abundance problem)

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