Abstract:ABSTRACT. Given escalating concern worldwide about the loss of biodiversity, and given biodiversity's centrality to quality of life, it is imperative that current ecological knowledge fully informs societal decision making. Over the past two decades, ecological science has undergone many significant shifts in emphasis and perspective, which have important implications for how we manage ecosystems and species. In particular, a shift has occurred from the equilibrium paradigm to one that recognizes the dynamic, … Show more
“…The prevailing static focus of aquatic ecosystem management requires little or no understanding of ecological processes (Wallington et al 2005). In contrast, managing for environmental change requires extensive knowledge of ecological processes and the functional response of species.…”
Section: Discussionmentioning
confidence: 99%
“…At the same time, the scientific view of the behavior of ecosystems, and the landscapes in which they are embedded, is shifting from an equilibrium perspective to one that recognizes dynamics and non-equilibrium conditions over time (Wallington et al 2005). The latter perspective views successional processes as much less deterministic than does the former (Pahl-Worstl 1995).…”
“…Scale considerations are paramount to understanding cumulative effects. The problem is exacerbated when temporal and spatial variability interact in ways that are complex and not well understood (Wallington et al 2005).…”
Section: Background: Historical Range Of Variabilitymentioning
ABSTRACT. The emerging perspective of ecosystems as both non-equilibrium and dynamic fits aquatic ecosystems as well as terrestrial systems. It is increasingly recognized that watersheds historically passed through different conditions over time. Habitat conditions varied in quantity and quality, primarily as a function of the time since the last major disturbance and the legacy of that disturbance. Thus, to match the effects of historical processes, we would expect a variety of conditions to exist across the watersheds in a region at any time. Additionally, watersheds have different potentials to provide habitat for given fish species because of variation in physical features. This developing ecological understanding is often preempted by social desires to bring all watersheds to a "healthy" condition, which in turn is reflected in a common regulatory approach mandating a single condition as the long-term goal for all watersheds. Matching perceptions and regulations to the way aquatic systems actually change and evolve through time will be a major challenge in the future.
“…The prevailing static focus of aquatic ecosystem management requires little or no understanding of ecological processes (Wallington et al 2005). In contrast, managing for environmental change requires extensive knowledge of ecological processes and the functional response of species.…”
Section: Discussionmentioning
confidence: 99%
“…At the same time, the scientific view of the behavior of ecosystems, and the landscapes in which they are embedded, is shifting from an equilibrium perspective to one that recognizes dynamics and non-equilibrium conditions over time (Wallington et al 2005). The latter perspective views successional processes as much less deterministic than does the former (Pahl-Worstl 1995).…”
“…Scale considerations are paramount to understanding cumulative effects. The problem is exacerbated when temporal and spatial variability interact in ways that are complex and not well understood (Wallington et al 2005).…”
Section: Background: Historical Range Of Variabilitymentioning
ABSTRACT. The emerging perspective of ecosystems as both non-equilibrium and dynamic fits aquatic ecosystems as well as terrestrial systems. It is increasingly recognized that watersheds historically passed through different conditions over time. Habitat conditions varied in quantity and quality, primarily as a function of the time since the last major disturbance and the legacy of that disturbance. Thus, to match the effects of historical processes, we would expect a variety of conditions to exist across the watersheds in a region at any time. Additionally, watersheds have different potentials to provide habitat for given fish species because of variation in physical features. This developing ecological understanding is often preempted by social desires to bring all watersheds to a "healthy" condition, which in turn is reflected in a common regulatory approach mandating a single condition as the long-term goal for all watersheds. Matching perceptions and regulations to the way aquatic systems actually change and evolve through time will be a major challenge in the future.
“…The unprecedented level of native habitat perturbation and the concomitant loss of biodiversity demand that ecologists fill the gap between restoration science and practice [1,2]. This means that ecological restoration will be a key process for the conservation of biodiversity, which can benefit from the fast-growing body of knowledge acquired among disciplines such as community ecology or evolutionary ecology.…”
Biotic interactions assembling plant communities can be positive (facilitation) or negative (competition) and operate simultaneously. Facilitative interactions and posterior competition are among the mechanisms triggering succession, thus representing a good scenario for ecological restoration. As distantly related species tend to have different phenotypes, and therefore different ecological requirements, they can coexist, maximizing facilitation and minimizing competition. We suggest including phylogenetic relatedness together with phenotypic information as a predictor for the net effects of the balance between facilitation and competition in nurse-based restoration experiments. We quantify, by means of a Bayesian meta-analysis of nurse-based restoration experiments performed worldwide, the importance of phylogenetic relatedness and life-form disparity in the survival, growth and density of facilitated plants. We find that the more similar the life forms of neighbouring plants are the greater the positive effect of phylogenetic distance is on survival and density. This result suggests that other characteristics beyond life form are also contained in the phylogeny, and the larger the phylogenetic distance, the less is the niche overlap, and therefore the less is the competition. As a general rule, we can maximize the success of the nurse-based practices by increasing life-form disparity and phylogenetic distances between the neighbour and the facilitated plant.
“…Essential to the assessment of conservation programs are appropriate monitoring and understanding of the ecological drivers of landscape heterogeneity (Eyre et al, 2011, Wallington et al, 2005. Heterogeneity results from variation in the extent, frequency, and intensity of abiotic and biotic processes, including disturbance (Fraterrigo andRusak, 2008, Pickett andWhite, 1985).…”
Winter, Stephen L.; Miller, James R.; and Debinski, Diane M., "Inconsistent outcomes of heterogeneity-based management underscore importance of matching evaluation to conservation objectives" (2013
AbstractConservation policy often incentivizes managers of human-impacted areas to create landscape heterogeneity to maximize biodiversity. In rangeland, patchy disturbance regimes create landscape heterogeneity (patch contrast), but outcomes of heterogeneity-based management are rarely tested for a universal response. We analyzed four habitat variables-vegetation structure, plant functional group composition, litter cover, and bare ground-from five experimental rangelands in Oklahoma and Iowa, USA. We tested for response consistency to heterogeneity-based management across and within locations. We calculated effect sizes for each variable to compare patch contrast on pastures managed for heterogeneity (patch burn-grazing) and pastures managed for homogeneity (grazing with homogeneous fire regimes). Effects varied considerably across and within locations. Effects of heterogeneity-based management were positive for all variables at only three of five experimental rangeland locations. No location showed a consistent pattern of positive effect across all four variables, although one location showed no effect for any variable. At another location, we found a positive effect of heterogeneity-based management on litter cover and bare ground, but no effect on vegetation structure and plant functional group composition. We discuss effect variability and how the fire-grazing interaction applies to rangeland management and conservation. Although it is accepted practice to use heterogeneity-based management to increase rangeland habitat diversity, managers should also confirm that evaluation metrics match desired conservation outcomes.
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