Abstract

There is renewed interest in implementing surrogate species approaches in conservation planning due to the large number of species in need of management but limited resources and data. One type of surrogate approach involves selection of one or a few species to represent a larger group of species requiring similar management actions, so that protection and persistence of the selected species would result in conservation of the group of species. However, among the criticisms of surrogate approaches is the need to test underlying assumptions, which remain rarely examined. In this study, we tested one of the fundamental assumptions underlying use of surrogate species in recovery planning: that there exist groups of threatened and endangered species that are sufficiently similar to warrant similar management or recovery criteria. Using a comprehensive database of all plant species listed under the U.S. Endangered Species Act and tree-based random forest analysis, we found no evidence of species groups based on a set of distributional and biological traits or by abundances and patterns of decline. Our results suggested that application of surrogate approaches for endangered species recovery would be unjustified. Thus, conservation planning focused on individual species and their patterns of decline will likely be required to recover listed species.

Highlights

  • Policy makers and conservation managers strive to use the best available science to determine strategies for species conservation

  • Use of surrogate species for conservation planning employs the assumption that species sharing biological traits or relationships will be similar in terms of their distribution, abundance, or response to management

  • Biological Traits as Grouping Variables We found no evidence of grouping among listed plant species based on distributional and biological traits: OOB error was 50.0% for the model including only traits and 50.2% for the model including traits, listing status, and plan year (Table 2)

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Summary

Introduction

Policy makers and conservation managers strive to use the best available science to determine strategies for species conservation. They may overlap with target species in terms of ecological requirements or geographical ranges (indicator and focal species; [2,9]), control target species abundance through trophic interactions (keystone species; [10,11]), have close phylogenetic relationships with targets (species groups; [12]), or have broad ecological requirements that encompass those of many species (umbrella species; [2,13,14]) Based on these biological relationships and similarities, benefits from protection or management of surrogates are inferred to extend to target species. Use of surrogate species for conservation planning employs the assumption that species sharing biological traits or relationships will be similar in terms of their distribution, abundance, or response to management

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