Abstract

Summary The size spectrum of an ecological community characterizes how a property, such as abundance or biomass, varies with body size. Size spectra are often used as ecosystem indicators of marine systems. They have been fitted to data from various sources, including groundfish trawl surveys, visual surveys of fish in kelp forests and coral reefs, sediment samples of benthic invertebrates and satellite remote sensing of chlorophyll. Over the past decades, several methods have been used to fit size spectra to data. We document eight such methods, demonstrating their commonalities and differences. Seven methods use linear regression (of which six require binning of data), while the eighth uses maximum likelihood estimation. We test the accuracy of the methods on simulated data. We demonstrate that estimated size‐spectrum slopes are not always comparable between the seven regression‐based methods because such methods are not estimating the same parameter. We find that four of the eight tested methods can sometimes give reasonably accurate estimates of the exponent of the individual size distribution (which is related to the slope of the size spectrum). However, sensitivity analyses find that maximum likelihood estimation is the only method that is consistently accurate, and the only one that yields reliable confidence intervals for the exponent. We therefore recommend the use of maximum likelihood estimation when fitting size spectra. To facilitate this, we provide documented R code for fitting and plotting results. This should provide consistency in future studies and improve the quality of any resulting advice to ecosystem managers. In particular, the calculation of reliable confidence intervals will allow proper consideration of uncertainty when making management decisions.

Highlights

  • For aquatic ecosystems, size-based indicators are tools for understanding food-web structure and enabling cost-effective monitoring (Shin et al 2005)

  • We find that four of the eight tested methods can sometimes give reasonably accurate estimates of the exponent of the individual size distribution

  • Ecological surveys are often designed to sample a specific range of body sizes, leading to size spectra being fit across a finite range (e.g. Dulvy et al 2004; Trebilco et al 2015), so a bounded distribution is being implicitly assumed

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Summary

Introduction

Size-based indicators are tools for understanding food-web structure and enabling cost-effective monitoring (Shin et al 2005). For a fish community, Rice & Gislason (1996) define size spectra as generally being ‘the variation in a community property across the size range of fish in the community’. If the same data set (e.g. individual body masses of fish in a community) is given to two researchers, under current practices it is not clear that they would obtain the same value for the slope of the size spectrum. This is because there are usually choices to be made in determining the slope: (i) how to define the size classes to bin the data, and (ii) how to plot the binned data

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