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/ Classification of streams and stream habitats is useful for research involving establishment of monitoring stations, determination of local impacts of land-use practices, generalization from site-specific data, and assessment of basin-wide, cumulative impacts of human activities on streams and their biota. This article presents a framework for a hierarchical classification system, entailing an organized view of spatial and temporal variation among and within stream systems. Stream habitat systems, defined and classified on several spatiotemporal scales, are associated with watershed geomorphic features and events. Variables selected for classification define relative long-term capacities of systems, not simply short-term states. Streams and their watershed environments are classified within the context of a regional biogeoclimatic landscape classification. The framework is a perspective that should allow more systematic interpretation and description of watershed-stream relationships.Managers of streams and their associated resources face problems of understanding and managing nonpoint source pollution, evaluating the complex, cumulative impacts of changing land use on stream habitats and biological communities, and assessing the effectiveness of fish habitat improvement projects and other mitigation procedures. Scientists have developed few generally applicable perspectives or procedures to address such needs. Present approaches to these problems typically involve paired watershed studies, long-term before-and-after monitoring programs, or upstream-downstream comparisons. Yet there exists no integrative, systematic approach for understanding the considerable natural variability within and among stream systems and stream communities (Hall and Knight 1981). How do we select representative or comparable sampling sites in such diverse environments? How can we interpret in a broader context, or how far can we reasonably extrapolate, information gathered at specific sites? How do we assess past and possible future states of a stream?This article articulates a general approach for classifying stream systems in the context of the watersheds that surround them. The stream classification
/ Classification of streams and stream habitats is useful for research involving establishment of monitoring stations, determination of local impacts of land-use practices, generalization from site-specific data, and assessment of basin-wide, cumulative impacts of human activities on streams and their biota. This article presents a framework for a hierarchical classification system, entailing an organized view of spatial and temporal variation among and within stream systems. Stream habitat systems, defined and classified on several spatiotemporal scales, are associated with watershed geomorphic features and events. Variables selected for classification define relative long-term capacities of systems, not simply short-term states. Streams and their watershed environments are classified within the context of a regional biogeoclimatic landscape classification. The framework is a perspective that should allow more systematic interpretation and description of watershed-stream relationships.Managers of streams and their associated resources face problems of understanding and managing nonpoint source pollution, evaluating the complex, cumulative impacts of changing land use on stream habitats and biological communities, and assessing the effectiveness of fish habitat improvement projects and other mitigation procedures. Scientists have developed few generally applicable perspectives or procedures to address such needs. Present approaches to these problems typically involve paired watershed studies, long-term before-and-after monitoring programs, or upstream-downstream comparisons. Yet there exists no integrative, systematic approach for understanding the considerable natural variability within and among stream systems and stream communities (Hall and Knight 1981). How do we select representative or comparable sampling sites in such diverse environments? How can we interpret in a broader context, or how far can we reasonably extrapolate, information gathered at specific sites? How do we assess past and possible future states of a stream?This article articulates a general approach for classifying stream systems in the context of the watersheds that surround them. The stream classification
/ Laboratory stream microcosms have been used to study transport, fate, and effects of toxic substances in stream ecosystems. Several general concerns exist in utilizing laboratory streams in this way. We summarize some of the most important and difficult of these problems and endeavor to provide theoretical understanding, evaluation, and empirical approaches necessary for making laboratory stream ecosystem studies more useful in solving problems of toxic substance behavior in natural stream ecosystems. Welldesigned laboratory streams and other microcosms are complex dynamic systems that can contribute to our understanding of the behavior of toxic substances. But such systems are far too complex and dynamic to be employed as bioassay, monitoring, or predictive tools, as individual organisms have been.Our culture is faced with the unprecedented task of evaluation and control of toxicants entering the environment as a result of human activities. The problem is of such technical, social, and natural complexity that one may well wonder by what means and how adequately it can be managed. While questions concerning the transport, fates, and effects of toxic substances in the environment are by no means only scientific in nature, scientific evaluation and understanding of the overall problem and its particulars are necessary.There is a serious need for general approaches to the study of transport, fates, and effects of toxic substances in natural ecosystems (Levin and others 1984, Herricks andSchaeffer 1985). Recently, there has been increased interest in the use of laboratory microcosms of various designs to evaluate the behavior and effects of toxic substances in ecosystems (Draggen 1976, Witt and Gillett 1979, Clark and others 1980, Coats 1980, Giesy 1980, Sanders 1982, Shriner and Gregory 1984, Lynch and others 1985, Ribeyre 1985, Warren and others 1987. Although much microcosm and laboratory stream work has been done, several general problems remain. Shriner and Gregory (1984) believe it is necessary to know how processes in artificial microcosms differ from those in natural situations. Levin and others (1984) state that the criteria important in assessing the applicability of microcosms to natural systems are accuracy, replicability, reproducibility, KEY WORDS: Laboratory streams; Toxic substances; Classification; Theory; Ecosystems *Author to whom correspondence should be addressed.and simplicity. Herricks and Schaeffer (1985) regard microcosms as biomonitoring test systems of great complexity producing qualitative data differing in variability, sensitivity, and validity. Swartzman and Rose (1984) propose a strategy for studying toxic effects in aquatic ecosystems that combines the use of microcosms with single species bioassays, mesocosm studies, and simulation models, yet they remain uncertain about applying microcosm results to natural systems. King (1980) addresses some concerns in applying the results of simple microcosm experiments to complex natural systems. Perhaps the most important constrain...
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