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<br />\ <br /> <br />002833 <br /> <br />etation, influences the form and condition <br />of a stream system and valley, We can <br />broadly describe watershed changes that <br />occur when fluvial processes are altered by <br />reducing natural flood flows: (1) valley <br />floors no longer flood; (2) local water tables <br />are no longer recharged; (3) stream bar and <br />channel areas no longer become inundated <br />and scoured; (4) sediment accretes on bars <br />and channel edges and forms lower, nar- <br />rower stream banks; (5) side channels and <br />backwater areas become disconnected from <br />the main channel or abandoned by the <br />mainstream as they fill in; (6) tributary <br />channel confluences with main stems lo- <br />cally aggrade and push out into the main <br />channel; and (7) the ratio of pools to riffles <br />is significantly altered (Morisawa 1968; <br />Platts 1979; Leopold and Emmett 1983), <br />These factors need to be considered in any <br />analysis of flow alteration because biotic <br />conditions such as riparian habitat or long- <br />term fish community structure and !ish <br />populations may depend on them, <br />Streams generally go through an aging <br />process, They are seldom at equilibrium <br />because they adjust to a wide range of fac- <br />tors and processes within the watershed <br />(Kellerhals and Church 1989), Once a <br />stream approaches an equilibrium condi- <br />tion, the controlling factors may change, <br />Such adjustments may occur daily. season- <br />ally, or over long periods. Nevertheless, <br />over time a channel and associated stream- <br />side vegetation will develop characteristics <br />and features that balance the effects of a <br />varied flow and sediment regime (Platts et <br />at 1985), <br />Channel adjustments are a natural com- <br />ponent of the channel-forming processes <br />in all valley bottom types (Lotspeich and <br />Platts 1982), Hence, local channel dimen- <br />sions and characteristics will change as a <br />result of natural or altered flow regimes, <br />For example, the removal of all peak flows <br />will cause near-term channel adjustments, <br />but over the long term reduced peak flows <br />will impair floodplain functions, which in <br />turn alter streamside vegetation and chan- <br />nel conditions (Platts 1979) that provide <br />habitat for fish, <br /> <br />The morphology of streams, especially al- <br />luvial ones, is controlled by the interaction <br />of flow regime with streamside vegetation <br />and sediment input (Hynes 1970). The <br />magnitude and duration of the bankfull <br />flows (and larger) are particularly impor- <br />tant, Geology, climate, and resulting sed- <br />iment supply (including quality and quan- <br />tity) and size of channel bed materials, <br />within the geomorphic setting, also pro- <br />vide form control (Beschta and Platts 1986), <br />In sand-bed streams, bedload transport <br />generally occurs over a wide range of flows <br />(Leopold et at 1964), However, in gravel- <br />bed streams the channel materials are usu- <br />ally stable except during relatively high <br />flows (Beschta 1987). Therefore, if fine sed- <br />iments that have become deposited be- <br />tween the gravels are to be removed by <br />flowing water, sufficiently high flows must <br />periodically occur to cause local scour and <br />transport of bed materials (Beschta and <br />Jackson 1979; Beschta 1987), Natural high <br />flow events normally provide the neces- <br />sary level of streambed mobilization to <br />flush fine sediments from both the bed and <br />the gravel and rubble (Rosgen et at 1986), <br />Regulated flows that occur downstream <br />from water diversion and storage facilities <br />can have both a positive and a negative <br />effect on channel substrates. For example, <br />a positive effect is the reduction in avail- <br />ability of fine sediments from upstream <br />sources that may deposit in spawning <br />gravels, A negative effect is the reduction <br />in gravel recruitment and loss of fines for <br />bank-building processes, <br />Stream bank form depends on a balance <br />between erosive forces of flowing water <br />and resisting forces of the bed, bank, and <br />streamside vegetation (Platts 1979), Vege- <br />tation buffers the stream bank from flowing <br />water, and flowing water in turn keeps <br />vegetation from occupying the channel <br />(Rosgen et at 1986). The duration of over- <br />bankfull flow is also important to channel <br />and floodplain characteristics. Flow dura- <br />tion determines the amount of time avail- <br />able for deposition of sediments, recharge <br />of subsurface moisture. and other main- <br />tenance processes. <br /> <br />FLOODPLAIN PROCESSES <br /> <br />Except in under-fit or deeply entrenched <br />streams, floodplain size is generally related <br /> <br />tlJ 200 <br /> <br />to the discharge of the stream and slope of <br />valley bottom (Hack 1957). Surface erosion <br /> <br />Rivers' Volume 2, Number 3 <br /> <br />July 1991 I <br /> <br />