23The most appropriate strategy for preserving fragmented populations depends on a species' 24 ability to colonise distant habitat patches. Insects associated with early decay stages of dead 25 wood are expected to have a high capacity to colonise new habitat patches. To study the 26 dispersal ranges of beetles (Coleoptera) and flat bugs (Hemiptera: Aradidae) dependent on 27 recently dead aspen (Populus tremula) wood in Finland, we set out 58 piles of recently cut 28 aspen logs at various distances up to 1.6 km from forests that contained a high density of old 29 aspen trees. We captured insects by trunk window-traps, and counted beetles' exit holes.
30Habitat connectivity was measured in terms of the amount of suitable aspen-wood in the 31 surrounding environment, with the closest dead wood items up-weighted by a negative-32 exponential function.
33The log-piles attracted many saproxylic insects including four red-listed aspen-34 specialist species. The exposure of log-piles to the sun, and high levels of habitat 35 connectivity increased the species richness of aspen-specialists, whereas bark peeling by 36 moose decreased richness. The spatial scale at which species richness had its strongest habitat by re-locating logs may be useful at localities with a rich and specialised fauna but 42 which have too low rate of formation of dead wood by natural processes.
Introduction
48Many organisms associated with dead wood are thought to be threatened as a result of 49 habitat loss and fragmentation (Berg et al. 1995; Nieto and Alexander 2010). The most 50 effective conservation strategy for preserving this fauna and flora depends to some extent on 51 species' dispersal ranges. For species with a limited dispersal range, it is important that 52 conservation efforts are directed within, or close to, sites where the target species are present 53 (Huxel and Hastings 1999), while to protect species that are able to colonise over long 54 3 distances, efforts can be directed at more distant sites where restoration efforts may be less 55 expensive and where they may improve habitat quality quickly (Ranius and Kindvall 2006). should be promoted in forest landscapes for enhancing biodiversity (Gustafsson et al. 2010).
80The efficiency of such conservation measures depends on the ability of aspen-associated 81 species to colonize patches. Several beetle species that specialise on dead aspen wood occur 82 in a larger proportion of items of dead wood where these are present in large aspen stands 83 than in smaller stands (Sahlin and Schroeder 2010 We set out 58 piles of aspen logs in a way that generated a high variability in habitat 114 connectivity among log-piles. They were set out along six forest roads, starting from was approximately 0.6 m 3 , which corresponds to a medium-sized aspen-tree.
131All experimental aspen logs were sourced from managed forests outside the study area. (Table 1). Aspen specialists were defined as species for which we estimate that > and then we observed that this bark stripping took p...