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Hansen Et Al. Edge Effects Across Ecosystem Types 1 Ecosystem Hansen et al. Edge effects across ecosystem types Ecosystem Biomass as a Framework for Predicting Habitat Fragmentation Effects Running Head: Edge effects across ecosystem types Key Words: biomass, conservation principles, edge effects, forest interior species, habitat fragmentation, microclimate Word Count: 7150 Andrew James Hansen, Ecology Department, Montana State University, Bozeman, MT 59717-3460 Lisa Baril, Ecology Department, Montana State University, Bozeman, MT 59717-3460 Jennifer Watts, Land Resources and Environmental Sciences Department, Montana State University, Bozeman, MT 59717-3460 Fletcher Kasmer, Montana State University, Bozeman, MT 59717-3460 Toni Ipolyi, Montana State University, Bozeman, MT 59717-3460 Ross Winton, Entomology Department, Montana State University, Bozeman, MT 59717- 3460 Corresponding Author: Andrew Hansen, Ecology Department, 310 Lewis Hall, Montana State University, Bozeman, MT 59717-3460. [email protected] 25 February 2008 1 Hansen et al. Edge effects across ecosystem types Abstract: Past studies of the consequences of human-induced edge effects on native biodiversity have had mixed results leading to confusion on if and how to manage to avoid negative edge effects in different forested ecosystem types. The purpose of this paper is to evaluate if forest ecosystems differ predictably in response to edge effects based on forest structure and density. The Biomass Accumulation Hypothesis (Hansen & Rotella 2000) asserts that edge effects have the highest magnitude of influence in ecosystems that accumulate high levels of standing aboveground vegetation biomass. We test two predictions of this hypothesis: 1) The dense vegetation in mid to late seral habitats within high-biomass ecosystems buffers microclimate, resulting in large differences in average microclimate between disturbance patch edges and forest interiors; 2) In high biomass ecosystems the sharp gradient in vegetation and microclimate results in finer habitat partitioning by organisms and more forest interior specialists than is the case in lower biomass ecosystems. These predictions were tested by statistical analysis of the results of published studies in several of the major forest biomes. We found that magnitude of edge influence of microclimate was significantly related to forest biomass for light intensity and relative humidity. Trends for air temperature, soil temperature, vapor pressure deficit, and soil moisture were as predicted, but not statistically significant. A model including all microclimate samples and controlling for microclimate variable type was significant. The percent of species that specialized on forest interiors was significantly related to biomass for mammals and birds, and nearly significant for beetles. The results suggest that forest fragmentation is most likely to negatively influence forest species in high biomass ecosystems such as tropical and temperate rainforests, but may have little influence on forest species in low-biomass ecosystems such as boreal or subalpine forests. These finding 2 Hansen et al. Edge effects across ecosystem types provides a basis for prioritizing the management of habitat fragmentation appropriately across the world’s forest ecosystems. 3 Hansen et al. Edge effects across ecosystem types Introduction The emerging discipline of conservation biology has increasingly converged on principles dealing with how humans influence ecological systems and strategies for mitigating negative effects (Grumbine 1994; Groom et al. 2006). Resource managers are drawing on these strategies to retain ecosystem function and biodiversity in the face of human expansion. A necessary step in the maturation of conservation biology is to understand which conservation strategies are best employed in a particular ecosystem, including those pertaining to human habitat fragmentation (Saunders et al. 1991). The vast body of research on edge effects, a consequence of fragmentation, has shown conflicting results (Paton 1994; Murcia 1995; Harper et al. 2005) leading to confusion concerning management. A major review by Matlack & Litvaitis (1999) concluded, “The negative repercussions of edge habitats have prompted changes in forestry practices, especially regulation regarding the size, distribution, and configuration of clearcuts. Yet there is considerable variability in edge response among forest sites and species, which makes it difficult to formulate a consistent edge management policy. The most productive approach is probably to consider the impact of edges on forest communities on a case-by- case basis.” (pg. 222). In a more recent review, Fahrig (2003) concluded that there is strong evidence that loss of habitat area negatively impacts biodiversity. However, change in spatial configuration of habitat (e.g., patch size, edge density, patch isolation), independent of habitat loss, “… has rather weak effects on biodiversity, which are as likely to be positive as negative.” (pg. 508). She states with regards management, “The fact that effects of 4 Hansen et al. Edge effects across ecosystem types fragmentation per se [habitat configuration] are usually small and at least as likely to be positive as negative suggests that conservation actions that attempt to minimize fragmentation (for a given habitat amount) may often be ineffectual.” (pg., 508). A caution is offered, however, that evidence suggests that negative edge effects on biodiversity are much stronger in tropical than in temperate systems. But, “This prediction remains to be tested.” (pg 508). Thus, substantial uncertainty remains on which ecosystem types are sensitive to changes in spatial configuration of fragmented habitats and ecosystem-specific guidelines for managers are generally not available. Edge effects are the result of the interaction between two adjacent ecosystems that are separated by an abrupt transition (Murcia 1995). Three categories of edge effects have been identified: abiotic effects, direct biological effects, and indirect biological effects (Harper et al. 2005). Abiotic effects include the alteration of microclimate and nutrients from patch exterior to interior. Changes in species abundances are examples of a direct biological effect. Edge conditions might lead to indirect biological effects seen in alterations of species interactions, such as predation, herbivory, pollination, and seed dispersal. 5 Hansen et al. Edge effects across ecosystem types Introduction Human expansion has led to fragmentation of many natural ecosystems (Saunders et al. 1991). Habitat fragmentation results in both a reduction in total area of habitat and change in spatial configuration of remaining habitat patches (Wilcove et al. 1986). Change in habitat patch size and number lead to increases in abrupt edges between remaining habitat patches and the expanding matrix as fragmentation proceeds. While some native species thrive at habitat edges, others are adapted to habitat interiors and may become extinct in landscapes where habitat is dominated by edge effects (Noss et al. 2006a). The vast body of research on the consequences of human-induced habitat edge effects on native biodiversity, however, has shown conflicting results (Paton 1994; Murcia 1995; Harper et al. 2005) leading to confusion concerning management. A major review by Matlack & Litvaitis (1999) concluded, “The negative repercussions of edge habitats have prompted changes in forestry practices, especially regulation regarding the size, distribution, and configuration of clearcuts. Yet there is considerable variability in edge response among forest sites and species, which makes it difficult to formulate a consistent edge management policy.” (pg. 222). More recently, Fahrig (2003) concluded that change in spatial configuration of habitat (including edges), independent of habitat loss, “… has rather weak effects on biodiversity, which are as likely to be positive as negative.” (pg. 508). She states regarding management, “… conservation actions that attempt to minimize fragmentation (for a given habitat amount) may often be ineffectual.” (pg., 508). A caution is offered, however, that that negative edge effects may be much stronger in tropical than in temperate systems, but, “This prediction remains to be tested.” (pg 508). Thus, substantial uncertainty remains 6 Hansen et al. Edge effects across ecosystem types on which ecosystem types are sensitive to edge effects and which management strategies are most effective for maintaining native biodiversity in a given ecosystem. The purpose of this paper is to evaluate if forest ecosystems differ predictably in response to edge effects based on forest structure and density. The Biomass Accumulation Hypothesis (Hansen & Rotella 2000) asserts that edge effects have the highest magnitude of influence in ecosystems that accumulate high levels of standing aboveground vegetation biomass. We examine how well the predictions of this hypothesis are supported by published studies from a range of forest ecosystem types. The abrupt edge transition comprising human-induced edges in forest systems is typically in vegetation structure, from patches with lower density vegetation to forest stands with higher vegetation density. This sharp gradient in vegetation structure across forest edges is the primary mechanism driving abiotic effects such as changes in microclimate, direct biological effects such as changes in plant and animal composition, and indirect biological effects such as responses herbivory and predation (Matlack & Litvaitis 1999; Kremester
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