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Beyond the Fragmentation Threshold Hypothesis: Regime Shifts in Biodiversity Across Fragmented Landscapes

机译:超越碎片化阈值假说:碎片化景观中生物多样性的制度转变

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摘要

Ecological systems are vulnerable to irreversible change when key system properties are pushed over thresholds, resulting in the loss of resilience and the precipitation of a regime shift. Perhaps the most important of such properties in human-modified landscapes is the total amount of remnant native vegetation. In a seminal study Andrén proposed the existence of a fragmentation threshold in the total amount of remnant vegetation, below which landscape-scale connectivity is eroded and local species richness and abundance become dependent on patch size. Despite the fact that species patch-area effects have been a mainstay of conservation science there has yet to be a robust empirical evaluation of this hypothesis. Here we present and test a new conceptual model describing the mechanisms and consequences of biodiversity change in fragmented landscapes, identifying the fragmentation threshold as a first step in a positive feedback mechanism that has the capacity to impair ecological resilience, and drive a regime shift in biodiversity. The model considers that local extinction risk is defined by patch size, and immigration rates by landscape vegetation cover, and that the recovery from local species losses depends upon the landscape species pool. Using a unique dataset on the distribution of non-volant small mammals across replicate landscapes in the Atlantic forest of Brazil, we found strong evidence for our model predictions - that patch-area effects are evident only at intermediate levels of total forest cover, where landscape diversity is still high and opportunities for enhancing biodiversity through local management are greatest. Furthermore, high levels of forest loss can push native biota through an extinction filter, and result in the abrupt, landscape-wide loss of forest-specialist taxa, ecological resilience and management effectiveness. The proposed model links hitherto distinct theoretical approaches within a single framework, providing a powerful tool for analysing the potential effectiveness of management interventions.
机译:当关键的系统属性超过阈值时,生态系统很容易发生不可逆转的变化,从而导致弹性丧失和政权转移。在人为修改的景观中,此类特性中最重要的也许是残留的原生植被的总量。在一项开创性的研究中,安德烈(Andrén)提出了残余植被总量中存在破碎阈值的问题,在该阈值以下,景观尺度的连通性受到侵蚀,当地物种的丰富度和丰度变得取决于斑块的大小。尽管物种斑块区域效应一直是保护科学的主要内容,但对这一假说尚缺乏可靠的经验评估。在这里,我们介绍并测试了一个新的概念模型,该模型描述了破碎景观中生物多样性变化的机制和后果,确定了破碎阈值是积极反馈机制的第一步,该机制具有削弱生态适应力并推动生物多样性制度转移的能力。该模型认为局部灭绝的风险由斑块大小确定,移民率由景观植被覆盖率确定,从本地物种损失中恢复的能力取决于景观物种库。通过使用关于巴西大西洋森林中非挥发性小哺乳动物跨复制景观分布的独特数据集,我们为模型预测找到了有力的证据-斑块区域效应仅在森林总覆盖率的中间水平才明显多样性仍然很高,通过地方管理加强生物多样性的机会最大。此外,大量的森林流失会使原生生物群落通过灭绝过滤器,并导致整个森林范围内的森林专科分类单元,生态适应力和管理有效性突然丧失。所提出的模型在一个框架内链接了迄今为止截然不同的理论方法,为分析管理干预措施的潜在有效性提供了强大的工具。

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