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Predicting species distributions from checklist data using site-occupancy models

(1) To increase awareness of the challenges induced by imperfect detection, which is a fundamental issue in species distribution modelling; (2) to emphasize the value of replicate observations for species distribution modelling; and (3) to show how 'cheap' checklist data in faunal/floral d...

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Published in:Journal of biogeography 2010-10, Vol.37 (10), p.1851-1862
Main Authors: Kéry, Marc, Gardner, Beth, Monnerat, Christian
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Gardner, Beth
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description (1) To increase awareness of the challenges induced by imperfect detection, which is a fundamental issue in species distribution modelling; (2) to emphasize the value of replicate observations for species distribution modelling; and (3) to show how 'cheap' checklist data in faunal/floral databases may be used for the rigorous modelling of distributions by site-occupancy models. Switzerland. We used checklist data collected by volunteers during 1999 and 2000 to analyse the distribution of the blue hawker, Aeshna cyanea (Odonata, Aeshnidae), a common dragonfly in Switzerland. We used data from repeated visits to 1-ha pixels to derive 'detection histories' and apply site-occupancy models to estimate the 'true' species distribution, i.e. corrected for imperfect detection. We modelled blue hawker distribution as a function of elevation and year and its detection probability of elevation, year and season. The best model contained cubic polynomial elevation effects for distribution and quadratic effects of elevation and season for detectability. We compared the site-occupancy model with a conventional distribution model based on a generalized linear model, which assumes perfect detectability (p = 1). The conventional distribution map looked very different from the distribution map obtained using site-occupancy models that accounted for the imperfect detection. The conventional model underestimated the species distribution by 60%, and the slope parameters of the occurrence-elevation relationship were also underestimated when assuming p = 1. Elevation was not only an important predictor of blue hawker occurrence, but also of the detection probability, with a bell-shaped relationship. Furthermore, detectability increased over the season. The average detection probability was estimated at only 0.19 per survey. Conventional species distribution models do not model species distributions per se but rather the apparent distribution, i.e. an unknown proportion of species distributions. That unknown proportion is equivalent to detectability. Imperfect detection in conventional species distribution models yields underestimates of the extent of distributions and covariate effects that are biased towards zero. In addition, patterns in detectability will erroneously be ascribed to species distributions. In contrast, site-occupancy models applied to replicated detection/non-detection data offer a powerful framework for making inferences about species distributions corrected for
doi_str_mv 10.1111/j.1365-2699.2010.02345.x
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Switzerland. We used checklist data collected by volunteers during 1999 and 2000 to analyse the distribution of the blue hawker, Aeshna cyanea (Odonata, Aeshnidae), a common dragonfly in Switzerland. We used data from repeated visits to 1-ha pixels to derive 'detection histories' and apply site-occupancy models to estimate the 'true' species distribution, i.e. corrected for imperfect detection. We modelled blue hawker distribution as a function of elevation and year and its detection probability of elevation, year and season. The best model contained cubic polynomial elevation effects for distribution and quadratic effects of elevation and season for detectability. We compared the site-occupancy model with a conventional distribution model based on a generalized linear model, which assumes perfect detectability (p = 1). The conventional distribution map looked very different from the distribution map obtained using site-occupancy models that accounted for the imperfect detection. The conventional model underestimated the species distribution by 60%, and the slope parameters of the occurrence-elevation relationship were also underestimated when assuming p = 1. Elevation was not only an important predictor of blue hawker occurrence, but also of the detection probability, with a bell-shaped relationship. Furthermore, detectability increased over the season. The average detection probability was estimated at only 0.19 per survey. Conventional species distribution models do not model species distributions per se but rather the apparent distribution, i.e. an unknown proportion of species distributions. That unknown proportion is equivalent to detectability. Imperfect detection in conventional species distribution models yields underestimates of the extent of distributions and covariate effects that are biased towards zero. In addition, patterns in detectability will erroneously be ascribed to species distributions. 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Switzerland. We used checklist data collected by volunteers during 1999 and 2000 to analyse the distribution of the blue hawker, Aeshna cyanea (Odonata, Aeshnidae), a common dragonfly in Switzerland. We used data from repeated visits to 1-ha pixels to derive 'detection histories' and apply site-occupancy models to estimate the 'true' species distribution, i.e. corrected for imperfect detection. We modelled blue hawker distribution as a function of elevation and year and its detection probability of elevation, year and season. The best model contained cubic polynomial elevation effects for distribution and quadratic effects of elevation and season for detectability. We compared the site-occupancy model with a conventional distribution model based on a generalized linear model, which assumes perfect detectability (p = 1). The conventional distribution map looked very different from the distribution map obtained using site-occupancy models that accounted for the imperfect detection. The conventional model underestimated the species distribution by 60%, and the slope parameters of the occurrence-elevation relationship were also underestimated when assuming p = 1. Elevation was not only an important predictor of blue hawker occurrence, but also of the detection probability, with a bell-shaped relationship. Furthermore, detectability increased over the season. The average detection probability was estimated at only 0.19 per survey. Conventional species distribution models do not model species distributions per se but rather the apparent distribution, i.e. an unknown proportion of species distributions. That unknown proportion is equivalent to detectability. Imperfect detection in conventional species distribution models yields underestimates of the extent of distributions and covariate effects that are biased towards zero. In addition, patterns in detectability will erroneously be ascribed to species distributions. 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Psychology</subject><subject>General aspects</subject><subject>generalized linear model</subject><subject>hierarchical model</subject><subject>Insecta</subject><subject>Invertebrates</subject><subject>Itinerant sales</subject><subject>Metapopulation ecology</subject><subject>Modeling</subject><subject>Odonata</subject><subject>Parametric models</subject><subject>Species</subject><subject>Species and community distributional modelling</subject><subject>species distribution model</subject><subject>Switzerland</subject><subject>Synecology</subject><subject>Topographical elevation</subject><issn>0305-0270</issn><issn>1365-2699</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2010</creationdate><recordtype>article</recordtype><recordid>eNqNkUtvEzEUhS0EEqHwExCzQawm9fuxYEEr6EMVFEHF0nLu2MXpJA72jEj-PZ5OlTXe2LrnO_faxwg1BC9JXafrJWFStFQas6S4VjFlXCz3z9DiKDxHC8ywaDFV-CV6VcoaY2wE4wt0e5t9F2GI2_um7DxEX5ouliHH1TjEtC1NyGnTwG8PD32tN50bXDOWRz4Ovk0A485t4dBsUuf78hq9CK4v_s3TfoLuvnz-eX7Z3ny7uDr_dNOCUKJea9UxEzTp-Ip4CVwwJ7UKnNEggDPhmATnPNZeOg8rEFp1oCmBwGoDadgJ-jD33eX0Z_RlsJtYwPe92_o0FquFVBJzKiupZxJyKiX7YHc5blw-WILtlKFd2ykqO0VlpwztY4Z2X63vn4a4Aq4PuT40lqOfMsq1obRyH2fub-z94b_72-uzq-lU_W9n_7oMKR_9HBuqjdZVb2e9_oDfH3WXH6xUTAn76-uFvcbftSJC2bPKv5v54JJ197ne-e5Hncww0YZQgtk_1wSnbw</recordid><startdate>201010</startdate><enddate>201010</enddate><creator>Kéry, Marc</creator><creator>Gardner, Beth</creator><creator>Monnerat, Christian</creator><general>Oxford, UK : Blackwell Publishing Ltd</general><general>Blackwell Publishing Ltd</general><general>Blackwell Publishing</general><general>Blackwell</general><scope>FBQ</scope><scope>BSCLL</scope><scope>IQODW</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7SN</scope><scope>7SS</scope><scope>7ST</scope><scope>7U6</scope><scope>C1K</scope><scope>F1W</scope><scope>H95</scope><scope>L.G</scope></search><sort><creationdate>201010</creationdate><title>Predicting species distributions from checklist data using site-occupancy models</title><author>Kéry, Marc ; Gardner, Beth ; Monnerat, Christian</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c5755-2bd39f81d4b1e6c453a687f432f5c435a36caae08e6aecbc587dc821cf3c57693</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2010</creationdate><topic>Aeshna cyanea</topic><topic>Aeshnidae</topic><topic>Animal and plant ecology</topic><topic>Animal, plant and microbial ecology</topic><topic>Applied ecology</topic><topic>Biogeography</topic><topic>Biological and medical sciences</topic><topic>checklists</topic><topic>citizen science</topic><topic>detection probability</topic><topic>dragonfly</topic><topic>Ecological modeling</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>General aspects</topic><topic>generalized linear model</topic><topic>hierarchical model</topic><topic>Insecta</topic><topic>Invertebrates</topic><topic>Itinerant sales</topic><topic>Metapopulation ecology</topic><topic>Modeling</topic><topic>Odonata</topic><topic>Parametric models</topic><topic>Species</topic><topic>Species and community distributional modelling</topic><topic>species distribution model</topic><topic>Switzerland</topic><topic>Synecology</topic><topic>Topographical elevation</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Kéry, Marc</creatorcontrib><creatorcontrib>Gardner, Beth</creatorcontrib><creatorcontrib>Monnerat, Christian</creatorcontrib><collection>AGRIS</collection><collection>Istex</collection><collection>Pascal-Francis</collection><collection>CrossRef</collection><collection>Ecology Abstracts</collection><collection>Entomology Abstracts (Full archive)</collection><collection>Environment Abstracts</collection><collection>Sustainability Science Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science &amp; Fisheries Abstracts (ASFA) 1: Biological Sciences &amp; Living Resources</collection><collection>Aquatic Science &amp; Fisheries Abstracts (ASFA) Professional</collection><jtitle>Journal of biogeography</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Kéry, Marc</au><au>Gardner, Beth</au><au>Monnerat, Christian</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Predicting species distributions from checklist data using site-occupancy models</atitle><jtitle>Journal of biogeography</jtitle><date>2010-10</date><risdate>2010</risdate><volume>37</volume><issue>10</issue><spage>1851</spage><epage>1862</epage><pages>1851-1862</pages><issn>0305-0270</issn><eissn>1365-2699</eissn><coden>JBIODN</coden><abstract>(1) To increase awareness of the challenges induced by imperfect detection, which is a fundamental issue in species distribution modelling; (2) to emphasize the value of replicate observations for species distribution modelling; and (3) to show how 'cheap' checklist data in faunal/floral databases may be used for the rigorous modelling of distributions by site-occupancy models. Switzerland. We used checklist data collected by volunteers during 1999 and 2000 to analyse the distribution of the blue hawker, Aeshna cyanea (Odonata, Aeshnidae), a common dragonfly in Switzerland. We used data from repeated visits to 1-ha pixels to derive 'detection histories' and apply site-occupancy models to estimate the 'true' species distribution, i.e. corrected for imperfect detection. We modelled blue hawker distribution as a function of elevation and year and its detection probability of elevation, year and season. The best model contained cubic polynomial elevation effects for distribution and quadratic effects of elevation and season for detectability. We compared the site-occupancy model with a conventional distribution model based on a generalized linear model, which assumes perfect detectability (p = 1). The conventional distribution map looked very different from the distribution map obtained using site-occupancy models that accounted for the imperfect detection. The conventional model underestimated the species distribution by 60%, and the slope parameters of the occurrence-elevation relationship were also underestimated when assuming p = 1. Elevation was not only an important predictor of blue hawker occurrence, but also of the detection probability, with a bell-shaped relationship. Furthermore, detectability increased over the season. The average detection probability was estimated at only 0.19 per survey. Conventional species distribution models do not model species distributions per se but rather the apparent distribution, i.e. an unknown proportion of species distributions. That unknown proportion is equivalent to detectability. Imperfect detection in conventional species distribution models yields underestimates of the extent of distributions and covariate effects that are biased towards zero. In addition, patterns in detectability will erroneously be ascribed to species distributions. In contrast, site-occupancy models applied to replicated detection/non-detection data offer a powerful framework for making inferences about species distributions corrected for imperfect detection. The use of 'cheap' checklist data greatly enhances the scope of applications of this useful class of models.</abstract><cop>Oxford, UK</cop><pub>Oxford, UK : Blackwell Publishing Ltd</pub><doi>10.1111/j.1365-2699.2010.02345.x</doi><tpages>12</tpages><oa>free_for_read</oa></addata></record>
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subjects Aeshna cyanea
Aeshnidae
Animal and plant ecology
Animal, plant and microbial ecology
Applied ecology
Biogeography
Biological and medical sciences
checklists
citizen science
detection probability
dragonfly
Ecological modeling
Fundamental and applied biological sciences. Psychology
General aspects
generalized linear model
hierarchical model
Insecta
Invertebrates
Itinerant sales
Metapopulation ecology
Modeling
Odonata
Parametric models
Species
Species and community distributional modelling
species distribution model
Switzerland
Synecology
Topographical elevation
title Predicting species distributions from checklist data using site-occupancy models
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