Abstract

Intensive forest management has led to a population decline in many species, including those dependent on dead wood. Many lichens are known to depend on dead wood, but their habitat requirements have been little studied. In this study we investigated the habitat requirements of wood dependent lichens on coarse dead wood (diameter >10 cm) of Scots pine Pinus sylvestris in managed boreal forests in central Sweden. Twenty-one wood dependent lichen species were recorded, of which eleven were confined to old (estimated to be >120 years old) and hard dead wood. Almost all of this wood has emanated from kelo trees, i.e. decorticated and resin-impregnated standing pine trees that died long time ago. We found four red-listed species, of which two were exclusive and two highly associated with old and hard wood. Lichen species composition differed significantly among dead wood types (low stumps, snags, logs), wood hardness, wood age and occurrence of fire scars. Snags had higher number of species per dead wood area than logs and low stumps, and old snags had higher number of species per dead wood area than young ones. Since wood from kelo trees harbours a specialized lichen flora, conservation of wood dependent lichens requires management strategies ensuring the future presence of this wood type. Besides preserving available kelo wood, the formation of this substratum should be supported by setting aside P. sylvestris forests and subject these to prescribed burnings as well as to allow wild fires in some of these forests.

Highlights

  • The boreal forest has an extension of 14.3 million km2 (Kasischke et al 1995) and is one of the largest biomes on the planet

  • In this study we investigated the habitat requirements of wood dependent lichens on coarse dead wood

  • The highest number of wood dependent species was found on old dead wood ([120 years)

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Summary

Introduction

The boreal forest has an extension of 14.3 million km (Kasischke et al 1995) and is one of the largest biomes on the planet. Intensive forest management has led to a decrease of structural diversity (Östlund et al 1997), including a decrease in the amount of dead wood (Green and Peterken 1997). In old-growth boreal forests, dead wood is mainly created by self-thinning, pathogens and disturbances such as storms, fire, and insect outbreaks (Esseen et al 1997; Niklasson and Granström 2000; Stokland et al 2012). In managed forests trees are harvested before natural processes creating larger quantities of dead wood take effect. The volume of coarse woody debris (CWD, i.e. wood with a diameter[10 cm) in managed boreal forests has been estimated to be only 2–10% of the amount in natural forests (Siitonen 2001). A large proportion of forest-dwelling species requires dead wood (Jonsson et al.2005). The loss of habitat has led to population declines in many of these species

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