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<br />... ------..->".>.~c-'h,~""'".".C<o.,..,',..'>.,d;'".=;'''''<C.,','"" '""'."","~'>""-"'f'-n/'''''';'''''''''''''V''H''fL \1W'!'!._tla'i"'~. ...Vll. .IIIIR~ <br />< - - ..~, "", --'~""""",-","""" -U_..-......~Wti'j.'iI-~~;Wi;p~j_~~,f'"il;i~~~J.;;.-i-$cF'Ji*-~~ - _ --;;) '--~''" . ",' . <br />. .. <br /> <br />methodology does not consider chemical or water <br />quality changes. <br /> <br />10. What important assumptions are part of the <br />IFG incremental methodology? <br /> <br />As with any analytical approach using the scientific <br />method, certain assumptions are made which define <br />those conditions under which the approach is valid. <br />The assumptions in the IFG incremental methodology <br />must be explicit, so that the limitations of the <br />methodology can be recognized. All present methods <br />assume that if habitat is maintained at some given <br />level, the fish population will be maintained. <br /> <br />The IFG incremental methodology is based on the <br />following primary assumptions: <br /> <br />A. The physical variable of depth, velocity and <br />temperature as associated with substrate are <br />assumed to be the most important fish habitat <br />variables when considering changes in stream <br />flow regimes or channel geometry. Water <br />chemistry, light and other variables known to be <br />extremely important in determining the level of <br /> <br />fish production, standing crop, and yields ar:~ qssl1p1eci <br />not to change significantly, and are thus considered as <br />constants in the instream flow analysis. Of course, <br />there are many cases in which significant changes in <br />water chemistry may occur with a proposed water <br />development. In such cases, conventional water <br />quality models must be used in addition to the IFG <br />incremental method to adequately display the <br />environmental impacts. <br /> <br />B. The structure of the stream channel is not altered <br />by changes in flow regime. Of course, periodic <br />flooding as well as long periods of low flow will <br />mod ify -the shape of any stream channel. To a lesser <br />extent, incremental modifications of flow may <br />change the size and shape of the stream channel. <br />Nevertheless, this methodology is based on the <br />assumption that the shape of the stream channel <br />and associated boulders, trees, and other features <br />will remain the same when assessing different dis- <br />charges. The user should exercise judgement in <br />assessing the range of flows under which this <br />assumption is valid in any particular stream. <br />Known or predicted changes in channel shape <br />must be treated as new input to the model. <br /> <br /> <br />~i <br /> <br />. ~~1!~~"'~~~~D11' <br />~ \]--- <br />a~ / ~ <br /> <br />Hr11ft.I_i!'''''' <br /> <br />~___<_''''' _,,",__,,'Y~;" <br /> <br />~L~}{.~.--.. <br /> <br />_ ,;:;__,-_>"",~~~ r-::i: <br /> <br /> <br />8 <br />