Abstract

In production forests, a common silvicultural objective is enhancing tree growth rates. The growth rate influences both mechanical and biochemical properties of wood, which may have an impact on dead wood inhabiting (i.e. saproxylic) species. In this study, we tested for the first time whether tree growth rates affect dead-wood associated assemblages in general and the occurrence of red-listed species in particular. We sampled saproxylic beetles (eclector traps) and fungi (DNA metabarcoding of wood samples) in dead trunks of Norway spruce (Picea abies), which had different growth rates within the same hemiboreal forests in Sweden. A high proportion of fungi showed a positive association to increasing tree growth. This resulted in higher fungal richness in fast-grown trees both at the trunk scale and across multiple studied trunks. Such patterns were not observed for saproxylic beetles. However, a set of species (both beetles and fungi) preferred slow-grown wood. Moreover, the total number of red-listed species was highest in slow-grown trunks. We conclude that dead wood from slow-grown trees hosts relatively fewer saproxylic species, but a part of these may be vulnerable to production forestry. It implies that slow-grown trees should be a target in nature conservation. However, where slow-grown trees are absent, for instance in forests managed for a high biomass production, increasing the volumes of dead wood from fast-grown trees may support many species.

Highlights

  • Production forestry is globally transforming and homogenizing forest structure, which profoundly affects biodiversity (Noble and Dirzo 1997)

  • Some possible pathways of how tree growth rate can affect wood-inhabiting assemblages are revealed by ecological theory, laboratory experiments and wood technology studies

  • Our study provides partial support to the expected pattern that slow-grown trees have fewer species, but a part of these are specialists and potentially vulnerable to production forestry

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Summary

Introduction

Production forestry is globally transforming and homogenizing forest structure, which profoundly affects biodiversity (Noble and Dirzo 1997). Slow-grown wood of many tree species is denser, has thicker cell walls and contains more lignin (Mäkinen et al 2002; Saranpää 2003; Sarén et al 2004; Novaes et al 2010); these properties inhibit the development of decayer assemblages (Stokland et al 2012) This may end up in a slower decay rate, which may benefit rare species due to an extended time-window for colonization (Edman et al 2006; Venugopal et al 2016). Tree growth rate can affect wood-inhabiting assemblages through the combined influences of cambium growth and morphology to produce specific bark structure of slow-grown trees (Whitmore 1963; MacFarlane and Luo 2009; Villari et al 2014). Casual observations suggest an association of several saproxylic beetle species with slow-grown trees (Ehnström 2001; Ehnström and Axelsson 2002), but this has never been tested

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