2015
DOI: 10.1007/s10980-015-0221-5
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Relative importance of habitat characteristics at multiple spatial scales for wood-dependent beetles in boreal forest

Abstract: Methods: Saproxylic beetles were sampled under the bark of dead wood in a managed forest 7 landscape in central Sweden. We modelled the occurrence probability in dead wood items of 44 8 species (all species occurring in >2% of the items), based on dead wood item characteristics, 9 forest stand characteristics, and habitat connectivity (i.e. area of potentially suitable forest stands 10 in the surrounding of each stand), using hierarchical Bayesian regression. 11Results: For the majority of species, dead wood i… Show more

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Cited by 28 publications
(20 citation statements)
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References 55 publications
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“…Availability of deadwood resources was measured as the total volume of deadwood (m 3 ) multiplied by the diversity of 20 deadwood types (20 combinations of four tree species (Scots pine Pinus sylvestris , Norway spruce Picea abies and two species of birch, Betula pendula and Betula pubescens ) and five decay stages; decay stages from Mäkinen et al [40]). We accounted for deadwood diversity in the measure as it has been suggested to be of key importance for species occurrence [32,41]. The diversity of deadwood types was measured with Simpson’s index of diversity.…”
Section: Methodsmentioning
confidence: 99%
See 1 more Smart Citation
“…Availability of deadwood resources was measured as the total volume of deadwood (m 3 ) multiplied by the diversity of 20 deadwood types (20 combinations of four tree species (Scots pine Pinus sylvestris , Norway spruce Picea abies and two species of birch, Betula pendula and Betula pubescens ) and five decay stages; decay stages from Mäkinen et al [40]). We accounted for deadwood diversity in the measure as it has been suggested to be of key importance for species occurrence [32,41]. The diversity of deadwood types was measured with Simpson’s index of diversity.…”
Section: Methodsmentioning
confidence: 99%
“…refraining from thinnings) [22,30]. Increasing the amount and diversity of deadwood resources in forests is the first step towards promoting deadwood-dependent biodiversity [31,32]. Landscape-level planning has been widely utilized in land-use optimization to maximize conservation benefits while minimizing economic or opportunity costs [16,18,33,34].…”
Section: Introductionmentioning
confidence: 99%
“…In a boreal forest landscape in central Sweden, we surveyed dead wood in all main types of forest stands. In this landscape, there is no sign of dispersal constraints in the distribution pattern of the great majority of all dead-wood-dependent beetle species and characteristics of dead-wood items have been found to explain beetle species’ occurrence patterns to a much higher extent than stand characteristics (Ranius et al 2015). We relate species pool size to habitat extent in unmanaged forests, since they reflect historical conditions better than the managed forest stands that are currently dominant in the region.…”
Section: Introductionmentioning
confidence: 91%
“…Intensive forestry may decrease the volume of logs and snags to only a tenth of natural volumes (Siitonen 2001), and therefore, the amount of dead wood has to be maintained or restored to preserve forest biodiversity. Species in dead wood have been shown to be associated with characteristics of individual dead-wood items, such as tree species, diameter, and position (standing/downed) (fungi: Berglund et al 2011; Junninen and Komonen 2011; lichens: Humphrey et al 2002; beetles: Ranius et al 2015). For dead-wood habitats, the evolutionary species pool hypothesis suggests that dead-wood types utilized by most species are those formed by tree mortality factors that were most abundant under pre-human conditions, while dead-wood types to a higher extent created by forestry operations are used by fewer species, since such types have only recently become abundant.…”
Section: Introductionmentioning
confidence: 99%
“…The effects of the species composition of overstory trees and/or their age (Heyborne et al, 2003;Wiezik et al, 2007;Samu et al, 2014;Stašiov et al, 2017), quality and amount of leaf litter and coarse woody debris (Castro & Wise, 2010;Ranius et al, 2015), canopy closure and/or deer density (Spitzer et al, 2008;Isaia et al, 2015;Košulič et al, 2016) on spatial distribution of invertebrates, species richness, abundance and composition have been documented in many studies.…”
mentioning
confidence: 99%