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      Discrepancies in occupancy and abundance approaches to identifying and protecting habitat for an at‐risk species

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          Abstract

          Predicting how environmental factors affect the distribution of species is a fundamental goal of conservation biology. Conservation biologists rely on species distribution and abundance models to identify key habitat characteristics for species. Occupancy modeling is frequently promoted as a practical alternative to use of abundance in identifying habitat quality. While occupancy and abundance are potentially governed by different limiting factors operating at different scales, few studies have directly compared predictive models for these approaches in the same system. We evaluated how much occupancy and abundance are driven by the same environmental factors for a species of conservation concern, the greater short‐horned lizard ( Phrynosoma hernandesi). Occupancy was most strongly dictated by precipitation, temperature, and density of ant mounds. While these factors were also in the best‐supported predictive models for lizard abundance, the magnitude of the effects varied, with the sign of the effect changing for temperature and precipitation. These discrepancies show that while occupancy modeling can be an efficient approach for conservation planning, predictors of occupancy probability should not automatically be equated with predictors of population abundance. Understanding the differences in factors that control occupancy versus abundance can help us to identify habitat requirements and mitigate the loss of threatened species.

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          ESTIMATING SITE OCCUPANCY RATES WHEN DETECTION PROBABILITIES ARE LESS THAN ONE

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            Global biodiversity scenarios for the year 2100.

            Scenarios of changes in biodiversity for the year 2100 can now be developed based on scenarios of changes in atmospheric carbon dioxide, climate, vegetation, and land use and the known sensitivity of biodiversity to these changes. This study identified a ranking of the importance of drivers of change, a ranking of the biomes with respect to expected changes, and the major sources of uncertainties. For terrestrial ecosystems, land-use change probably will have the largest effect, followed by climate change, nitrogen deposition, biotic exchange, and elevated carbon dioxide concentration. For freshwater ecosystems, biotic exchange is much more important. Mediterranean climate and grassland ecosystems likely will experience the greatest proportional change in biodiversity because of the substantial influence of all drivers of biodiversity change. Northern temperate ecosystems are estimated to experience the least biodiversity change because major land-use change has already occurred. Plausible changes in biodiversity in other biomes depend on interactions among the causes of biodiversity change. These interactions represent one of the largest uncertainties in projections of future biodiversity change.
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              Evolution and Ecology of Species Range Limits

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                Author and article information

                Contributors
                rdibner@uwyo.edu
                Journal
                Ecol Evol
                Ecol Evol
                10.1002/(ISSN)2045-7758
                ECE3
                Ecology and Evolution
                John Wiley and Sons Inc. (Hoboken )
                2045-7758
                15 June 2017
                August 2017
                : 7
                : 15 ( doiID: 10.1002/ece3.2017.7.issue-15 )
                : 5692-5702
                Affiliations
                [ 1 ] Program in Ecology University of Wyoming Laramie WY USA
                [ 2 ] Environmental Studies Program University of Colorado, Boulder Boulder CO USA
                [ 3 ] Department of Ecosystem Science and Management Program in Ecology University of Wyoming Laramie WY USA
                Author notes
                [*] [* ] Correspondence

                Reilly R. Dibner, Haub School of Environment and Natural Resources, University of Wyoming, Laramie, WY, USA.

                Email: rdibner@ 123456uwyo.edu

                Author information
                http://orcid.org/0000-0001-9197-5986
                Article
                ECE33131
                10.1002/ece3.3131
                5655793
                29085621
                ffa5f3f7-417a-4df7-8402-86e429179b30
                © 2017 The Authors. Ecology and Evolution published by John Wiley & Sons Ltd.

                This is an open access article under the terms of the Creative Commons Attribution License, which permits use, distribution and reproduction in any medium, provided the original work is properly cited.

                History
                : 14 September 2016
                : 18 April 2017
                : 25 April 2017
                Page count
                Figures: 5, Tables: 2, Pages: 11, Words: 8500
                Funding
                Funded by: Wyoming NASA Space Grant Consortium Grant
                Award ID: #NNX10AO95H
                Funded by: Wyoming Governor's Big Game License Coalition
                Award ID: #NNX10AO95H
                Funded by: Dr. George E. Menkens Memorial Scholarship
                Funded by: L. Floyd Clarke Fellowship
                Funded by: Reed W. Fautin Memorial Scholarship
                Funded by: Horned Lizard Conservation Society
                Categories
                Original Research
                Original Research
                Custom metadata
                2.0
                ece33131
                August 2017
                Converter:WILEY_ML3GV2_TO_NLMPMC version:5.2.1 mode:remove_FC converted:25.10.2017

                Evolutionary Biology
                abundance,conservation,environmental limits,horned lizard,occupancy,phrynosoma hernandesi

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