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dc.contributor.authorMair, Louise
dc.contributor.authorHarrison, Philip J.
dc.contributor.authorJönsson, Mari
dc.contributor.authorLöbel, Swantje
dc.contributor.authorNordén, Jenni
dc.contributor.authorSiitonen, Juha
dc.contributor.authorLãmås, Tomas
dc.contributor.authorLundström, Anders
dc.contributor.authorSnäll, Tord
dc.date.accessioned2017-01-02T09:47:27Z
dc.date.available2017-01-02T09:47:27Z
dc.date.created2016-12-22T09:45:14Z
dc.date.issued2016
dc.identifier.issn2045-7758
dc.identifier.urihttp://hdl.handle.net/11250/2425948
dc.description.abstractThe extensive spatial and temporal coverage of many citizen science datasets (CSD) makes them appealing for use in species distribution modeling and forecasting. However, a frequent limitation is the inability to validate results. Here, we aim to assess the reliability of CSD for forecasting species occurrence in response to national forest management projections (representing 160,366 km2) by comparison against forecasts from a model based on systematically collected colonization–extinction data. We fitted species distribution models using citizen science observations of an old-forest indicator fungus Phellinus ferrugineofuscus. We applied five modeling approaches (generalized linear model, Poisson process model, Bayesian occupancy model, and two MaxEnt models). Models were used to forecast changes in occurrence in response to national forest management for 2020-2110. Forecasts of species occurrence from models based on CSD were congruent with forecasts made using the colonization–extinction model based on systematically collected data, although different modeling methods indicated different levels of change. All models projected increased occurrence in set-aside forest from 2020 to 2110: the projected increase varied between 125% and 195% among models based on CSD, in comparison with an increase of 129% according to the colonization–extinction model. All but one model based on CSD projected a decline in production forest, which varied between 11% and 49%, compared to a decline of 41% using the colonization–extinction model. All models thus highlighted the importance of protected old forest for P. ferrugineofuscus persistence. We conclude that models based on CSD can reproduce forecasts from models based on systematically collected colonization–extinction data and so lead to the same forest management conclusions. Our results show that the use of a suite of models allows CSD to be reliably applied to land management and conservation decision making, demonstrating that widely available CSD can be a valuable forecasting resource. deadwood-dependent fungi, forestry, global biodiversity information facility, habitat change, land use change, opportunistic data, volunteer recordingnb_NO
dc.language.isoengnb_NO
dc.subjectdeadwood-dependent funginb_NO
dc.subjectforestrynb_NO
dc.subjectglobal biodiversity information facilitynb_NO
dc.subjecthabitat changenb_NO
dc.subjectland use changenb_NO
dc.subjectopportunistic datanb_NO
dc.subjectvolunteer recordingnb_NO
dc.titleEvaluating citizen science data for forecasting species responses to national forest managementnb_NO
dc.typeJournal articlenb_NO
dc.typePeer reviewednb_NO
dc.rights.holder© 2016 The Authors. Ecology and Evolution published by John Wiley & Sons Ltd.nb_NO
dc.subject.nsiVDP::Matematikk og Naturvitenskap: 400::Basale biofag: 470nb_NO
dc.source.journalEcology and Evolutionnb_NO
dc.identifier.doi10.1002/ece3.2601
dc.identifier.cristin1416560
dc.relation.projectEU/242093nb_NO
cristin.unitcode7511,6,0,0
cristin.unitnameOslo
cristin.ispublishedtrue
cristin.fulltextoriginal
cristin.qualitycode1


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