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The lake landscape-context framework: linking aquatic connections, terrestrial features and human effects at multiple spatial scales

机译:湖泊景观 - 背景框架:在多个空间尺度上连接水生连接,地面特征和人类效果

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The principles of landscape ecology provide a powerful means to develop a more robust conceptual understanding of human and hydrogeomorphic controls of lake heterogeneity across space and time (MAGNUSON & KRATZ 2000; WIENS 2002; KRATZ et al. 2005). Using a landscape perspective, lakes can be con-ceptualized as patches (a fundamental unit of a landscape) that are hierarchically organized in a complex terrestrial and aquatic matrix of natural and human-influenced features that interact at multiple spatial scales. WIENS (2002) identified four properties of landscape structure that apply effectively to lakes when treated as patches: (1) patch quality describes the physical features of the patch (e.g., lake morphometry, sediment characteristics), (2) boundaries mark sharp transitions at patch edges (e.g., lake shorelines), (3)patch context describes nearby features (e.g., soils and geology), and (4) connectivity defines the degree to which materials and organisms move across the landscape through aquatic connections ( e.g. streams, groundwater and wetlands). Because the context for lake patches is hierarchical, a multiscale view that considers both spatial extent (i.e. the size of the study area that contains interacting features, such as lakes, geology, climate, etc.) and spatial grain (i.e. the resolution that features are characterized, such as ecoregion or lake district) is required to link aquatic, terrestrial, and human components into a practical framework.Such a framework empowers us to more explicitly integrate the myriad of landscape components that we know influence lake ecosystems at different spatial scales and to identify the factors contributing to the spatial structure of variation among lakes.Existing landscape frameworks have proven to be effective for understanding spatial heterogeneity across lakes (Toms 1990, KRATZ et al. 1997). For example, a combination of bio-geographic barriers, abiotic constraints (determined largely by a lake's morphometry and surface water connections) and biotic interactions can help to understand the presence/absence of aquatic species from fish to plants and invertebrates (Toms 1990; HERSHEY et al. 1999, LEWIS & MAGNUSON 2000, HRABIK et al. 2005, RAHEL 2007). In addition, a lake's position in the regional groundwater and surface flow system (i.e. landscapeposition) is strongly related to lake water chemistry, clarity, biological measures, and human use of lakes (KRATZ et al. 1997, SORANNO et al. 1999, RIERA et al. 2000, QUINLAN et al. 2003, LEAVITT et al. 2006, PATOINE et al. 2006). Finally, the hy-drogeomorphic setting generates large variation among lakes in their response to disturbance (WEBSTER et al. 2000, CH ERUVELIL 2004).Despite these examples and calls for a more explicit land-scape perspective for lakes (MAGNUSON & KRATZ 2000, WIENS 2002, KRATZ et al. 2005), we lack a formalization of these ideas into an integrated conceptual framework that is broadly applicable to a range of lakes and regions. Many existing lake frameworks have been developed for a particular hydrologic setting or omitted humans as important drivers of variation. Interestingly, stream ecologists have a rich history of considering stream ecosystems from landscape perspectives that integrate hydrogeomorphology with ecology (HYNES 1975, VAN-NOTE et al. 1980, FRISSELL et al. 1986, WILEY et al. 1997, POFF 1997). If the valley rules the stream, what rules the lake?
机译:景观生态学原则提供了一种强大的方法,可以在空间和时间(MagnuSon&Kratz 2000; Wiens 2002; Kratz等,2005)中制定更强大的概念性对人类和水力术语的概念性控制。使用景观透视图,湖泊可以被视为斑块(横向的基本单元),其在复杂的陆地和水生矩阵的分层组织,其自然和人类影响的特征在多个空间尺度处相互作用。 Wiens(2002)确定了景观结构的四个性能,当被视为贴片时有效适用于湖泊:(1)补丁质量描述了贴片的物理特征(例如,湖流格术,沉积物特征),(2)边界标志着急剧转变贴片边缘(例如,湖岸),(3)贴片上下文描述了附近的特征(例如,土壤和地质),(4)连接定义了通过水生连接在景观中移动的程度(例如流,地下水和湿地)。因为Lake补丁的上下文是分层的,所以多尺度视图,其考虑空间范围(即,研究区域的大小,其中包含湖泊,地质,气候等)和空间谷物(即,特征的分辨率被特征在于,如eCoregion或湖区)需要将水生,陆地和人类组成部分链接到一个实用的框架中。框架授权授权我们更明确地整合我们知道在不同的空间尺度下影响湖泊生态系统的景观组件并确定湖泊之间变异空间结构的因素。证明景观框架已被证明是为了理解湖泊的空间异质性有效(汤姆斯1990,Kratz等,1997)。例如,生物地理障碍,非生物约束(主要由湖的形态学和地表水连接确定)和生物相互作用的组合可以有助于了解从鱼到植物和无脊椎动物的水生物种(Toms 1990; Hershey等人。1999,Lewis&Magnuson 2000,Hrabik等,2005,Rahel 2007)。此外,湖泊在区域地下水和地表流动系统(即景观)中的位置与湖水化学,清晰度,生物措施和湖泊的人类使用强烈相关(Kratz等,1997,Soranno等,1999,Riera等人。2000,Quinlan等人2003,Leavitt等人2006,Patoine等人。2006)。最后,Hy-Drogeomorphic设置在对干扰的响应中产生大的变化(Webster等,2000,Ch Eruvelil 2004)。这些示例和呼吁为湖泊提供更明确的土地Scape视角(Magnuson&Kratz 2000, Wiens 2002,Kratz等人2005),我们缺乏这些想法的形式化,以综合概念框架,广泛适用于一系列湖泊和地区。许多现有的湖框架已经为特定的水文环境或省略了人类作为变异的重要驱动因素。有趣的是,流的生态学家具有富裕的历史,历史悠久的历史悠久地考虑与生态学的景观视角,整合水文晶体(Hynes 1975,Van-Note等1980,Frissell等人1986,Wiley等,1997,Poff 1997)。如果山谷统治流,那么湖的规则是什么?

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