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iForest -Biogeosciences and Forestry
IntroductionComprehensive knowledge of how forest structure develops in response to natural disturbances is essential to evaluate current forest conditions and to promote sustainable silviculture and conservation systems in the future (McCarthy 2001). In Mediterranean montane forests, disturbances killing or removing small groups of trees are important drivers that create habitat heterogeneity and trigger successional dynamics (Dubé et al. 2005, Linares & Carreira 2009). This process may culminate in the replacement of the original dominant canopy species by individuals of different tree species at the stand scale. In such cases, gap disturbance would promotes the coexistence of species with different resource-use strategies, dispersal and competitive abilities (Veblen 1992). Implementation and exploitation of these natural succession processes in forest management is a desirable approach for threatened or endangered tree species. Therefore, detailed knowledge of how various tree species establish within gaps could be an efficient way to introduce ecological mechanisms into current silvicultural systems (Veblen 1992, Beckage et al. 2000.The Spanish fir (Abies pinsapo Boiss.) is a relict fir species endemic to southern Spain and northern Morocco. It has been hypothesized that A. pinsapo populations remained isolated throughout the Quaternary (AlbaSánchez et al. 2010). Such historical isolation caused significant morphological, genetic and ecological differentiation from other circum-Mediterranean fir species (Martín et al. 2010, Linares 2011. A. pinsapo forests were subjected to intense human use (e.g., grazing and logging for timber, firewood, and charcoal) until the mid-20 th century. As a result, the current structure and tree species composition of A. pinsapo forests reflect their past use and management (Linares et al. 2010a, Esteban et al. 2010. Previous research on A. pinsapo regeneration has mainly focused on several reproductive stages of the species such as cone and seed production as well as seedling abundance (Arista et al. 1997). Nevertheless, there is scarce information on A. pinsapo seedling and sapling abundance as related to gap dynamics.Many studies on the role of gap formation in tree regeneration have been conducted in montane or temperate forests (Runkle 1985, Degen et al. 2005, Sapkota & Odén 2009). However, little attention has been paid to the role of gaps as regeneration foci in Mediterranean conifer forests. Most studies on forest gap regeneration in mesic fir forests have been performed in continuous forests with large tree-fall gaps that greatly differ in size (Dobrowolska & Veblen 2008). Yet, few studies have addressed how pest-related canopy gaps drive regeneration dynamics in Mediterranean fir forests. At the landscape scale, the natural disturbance regime of A. pinsapo forests in Spain is driven by fire, drought and fungal infection (Arista 1995, Linares & Carreira 2009). In the absence of fire or pest outbreaks, the creation of small canopy g...