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11/23/2009 1:22:00 PM
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10/4/2006 9:09:52 PM
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Floodplain Documents
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State of Colorado
Stream Name
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Title
Stream, Riparian, and Wetland Ecology - Class material, Volume 1 of 2
Date
9/1/1987
Prepared For
Students
Prepared By
Professor Windell
Floodplain - Doc Type
Educational/Technical/Reference Information
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<br />It <br /> <br />\ <br /> <br />77 <br /> <br />processing rates. For example, loss rates of less than 0.5 percent per day <br />are characteristic of .slow. leaf litter such as hemlock and oak, whereas <br />ash and alder leaves may be converted at greater than 1.5 percent per day <br />(Peterson and Cummins 1974, Sedell et al. 1975). <br /> <br />~1;~ :f?' <br /> <br />The River Continuum Concept <br /> <br />\ <br />I <br />; <br /> <br />The River Continuum Concept proposes that natural stream ecosystems <br />may be characterized as extending from theIr headwater beginnings (i.e., <br />first order tributaries) to mouth or estuary and that these ecosystems <br />provide a continuous gradient of physical conditions >rhich affect organic <br />matter storage and transport and the response of biotIc communitiE!s <br />(Vannote et at. 1980). The stream order system, although not perfect, <br />provides a convenient structural framework upon which community structure <br />and function can be related to stream width and length. A hypothetical <br />drainage system is used to illustrate biotIc communit)r structure and <br />function in a downstream direction along a longitudinally linked twelfth <br />order stream system. The stream system provides a gradient of ch,mging <br />physical, chemical, and biological conditions (Figure 2). Longitudinally, <br />the stream system is divided into three major ecological zones based on <br />small headwater feeder streams (orders 1, 2, 3), medium-size streams <br />(orders 4, 5, 6), and large streams (orders 7 to 12). The boundaries <br />between the three zones are not intended to be rigidl)r fixed and may vary <br />from drainage to drainage by shifting the "ones upstrE!am or downsl:ream <br />depending on a number of factors including climate, longitude, lal:itude, <br />altitude, geomorphology, number of inflowing tributarIes and the "ature of <br />the riparian zone. These factors are superimposed on the overall tendency <br />for the physical conditions to change progressively and predictably with <br />increasing stream size. Significant differences in the downstream gradient <br />of changing physical conditions (abiotic component) is related to <br />significant changes in the biotic components such as producers, <br />microconsumers, and macroconsumers. Thus the coalesc:lng network of <br />within a drainage basin represents a longitudinally LLnked gradient <br />physical habitat conditions that support a continuum ()f communities <br />ecosystem material processes. <br /> <br />I <br />, <br />, <br /> <br />< <br /> <br />1 <br />i <br />, <br /> <br />streams <br />of <br />and <br /> <br />, <br />J' <br /> <br />Headwater Feeding Streams <br /> <br />Headwater feeder streams constitute a massive feeder network within <br />watersheds that collect and channel materials from the landscape to <br />downstream reaches. When evaluated on the basis of stream length, first <br />and second order streams collectively exceed 75 percent of the total length <br />of U.S. streams. Addition of the third order segments increases the <br />collective length to 85 percent of the total national stream milage. The <br />first, second and third order streams form critically important links <br />between themselves, the surrounding landscape and downstream reaches <br />(Figure 2). <br /> <br />The most distinctive characteristics of headwater feeder streams <br />include smallness, narrowness, a gradient (i.e., decreasing slope) greater <br />
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