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dc.contributor.authorAndersson, Anastasia
dc.contributor.authorKarlsson, Sten
dc.contributor.authorRyman, Nils
dc.contributor.authorLaikre, Linda
dc.date.accessioned2023-02-27T14:49:43Z
dc.date.available2023-02-27T14:49:43Z
dc.date.created2022-11-15T13:48:38Z
dc.date.issued2022
dc.identifier.citationMolecular Ecology. 2022, .en_US
dc.identifier.issn0962-1083
dc.identifier.urihttps://hdl.handle.net/11250/3054373
dc.description.abstractGenetic diversity is the basis for population adaptation and long-term survival, yet rarely considered in biodiversity monitoring. One key issue is the need for useful and straightforward indicators of genetic diversity. We monitored genetic diversity over 40 years (1970–2010) in metapopulations of brown trout (Salmo trutta) inhabiting 27 small mountain lakes representing 10 lake systems in central Sweden using >1200 fish per time point. We tested six newly proposed indicators; three were designed for broad, international use in the UN Convention on Biological Diversity (CBD) and are currently applied in several countries. The other three were recently elaborated for national use by a Swedish science- management effort and applied for the first time here. The Swedish indicators use molecular genetic data to monitor genetic diversity within and between populations (indicators ΔH and ΔFST, respectively) and assess the effective population size (Ne- indicator). We identified 29 genetically distinct popula-tions, all retained over time. Twelve of the 27 lakes harboured more than one popula-tion indicating that brown trout biodiversity hidden as cryptic, sympatric populations are more common than recognized. The Ne indicator showed values below the thresh-old (Ne ≤ 500) in 20 populations with five showing Ne< 100. Statistically significant ge-netic diversity reductions occurred in several populations. Metapopulation structure appears to buffer against diversity loss; applying the indicators to metapopulations suggest mostly acceptable rates of change in all but one system. The CBD indicators agreed with the Swedish ones but provided less detail. All these indicators are appro-priate for managers to initiate monitoring of genetic biodiversityen_US
dc.language.isoengen_US
dc.rightsAttribution-NonCommercial-NoDerivatives 4.0 Internasjonal*
dc.rights.urihttp://creativecommons.org/licenses/by-nc-nd/4.0/deed.no*
dc.subjectcryptic sympatryen_US
dc.subjecthidden biodiversityen_US
dc.subjectintraspecific biodiversityen_US
dc.subjectprotected areaen_US
dc.subjectsympatric populationsen_US
dc.titleMonitoring genetic diversity with new indicators applied to an alpine freshwater top predatoren_US
dc.title.alternativeMonitoring genetic diversity with new indicators applied to an alpine freshwater top predatoren_US
dc.typePeer revieweden_US
dc.typeJournal articleen_US
dc.description.versionpublishedVersionen_US
dc.rights.holder© 2022 The Authorsen_US
dc.subject.nsiVDP::Zoologiske og botaniske fag: 480en_US
dc.subject.nsiVDP::Zoology and botany: 480en_US
dc.source.pagenumber18en_US
dc.source.journalMolecular Ecologyen_US
dc.identifier.doi10.1111/mec.16710
dc.identifier.cristin2074287
dc.relation.projectAndre: Carl Trygger Foundationen_US
dc.relation.projectAndre: Swedish Research Council Formasen_US
dc.relation.projectAndre: Swedish Research Councilen_US
dc.relation.projectAndre: Erik Philip-Sörensen Foundationen_US
dc.relation.projectAndre: Swedish Agency for Marine and Water Managementen_US
cristin.ispublishedtrue
cristin.fulltextoriginal
cristin.qualitycode2


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Attribution-NonCommercial-NoDerivatives 4.0 Internasjonal
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