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The shifting habitat mosaic of river ecosystems

机译:河流生态系统不断变化的栖息地马赛克

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The essence of ecology is to understand the distribution and abundance of biota ( Andre wartha & Birch 1954). In the same vein, a cornerstone of ecology is quantifying how and why organisms are dependent on specific biophysical space (habitat) to complete one stage or another in their life cycles (Southwood 1977). On the one hand, phenotypic plasticity promotes successful growth and reproduction in variable habitats, but on the other hand habitat fidelity over several to many generations may constrain (adapt) the species or life stage to a habitat with quite specific spatial or functional attributes. Conservation biologists sometimes refer to these locally adapted populations with habitat-specific life cycles as ecologically significant units. Such populations have been accorded special protection and management if they are rare or declining in numbers. However, habitat intrinsically is not static, owing to constantly changing successional (or gradient) states as landscape is mediated by interactive physical (e.g. flood, drought, fire) and biological (e.g. disease, predation, invasion) drivers. Thus, physical and biological attributes vary in time and space and interact to determine quantity and quality of specific habitat per life stage. Sufficient quality habitat is required to permit a positive life history energy balance to sustain a population over the long term, otherwise extinction occurs (Hall et al. 1992). Particular species, and even particular populations of species, either adapt to the dynamic nature of habitat or they fail to persist in that landscape. Of course, a given landscape is composed of n-dimensional gradients and species responses, and feedbacks are complex and nonlinear, making habitat per life stage of each species in the landscape very difficult to define. Nonetheless, quantifying habitat for species in very specific spatial and temporal terms is fundamental to conservation of biodiversity world wide.
机译:生态学的本质是了解生物区系的分布和丰富度(Andre wartha&Birch 1954)。同样,生态学的基石是量化生物如何以及为什么依赖于特定的生物物理空间(栖息地)来完成其生命周期中的一个或另一个阶段(Southwood 1977)。一方面,表型可塑性促进了可变栖息地的成功生长和繁殖,但另一方面,几代至多代的栖息地保真度可能会限制(适应)物种或生命阶段,使其具有特定的空间或功能属性。保护生物学家有时将这些具有当地栖息地特定生命周期的本地适应种群称为具有生态意义的单位。如果这类人口数量很少或正在下降,则应给予特别保护和管理。但是,由于景观是由交互的物理(例如洪水,干旱,火灾)和生物(例如疾病,掠食,入侵)驱动程序介导的,因此栖息地本质上不是静态的,这是因为不断变化的演替(或梯度)状态。因此,物理和生物学属性随时间和空间变化,并相互作用以确定每个生命阶段特定栖息地的数量和质量。需要足够的优质栖息地,以实现积极的生活史能量平衡以长期维持种群,否则会灭绝(Hall等人,1992)。特定物种,甚至特定物种种群,要么适应生境的动态特性,要么无法在该景观中持续存在。当然,给定的景观由n维梯度和物种响应组成,并且反馈是复杂且非线性的,这使得很难定义景观中每个物种每个生命阶段的栖息地。尽管如此,以非常具体的时空术语量化物种的栖息地对于保护全球生物多样性至关重要。

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