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<br />12 BIOLOGICAL REpORT 29 <br /> <br />Wetted Perimeter Method <br /> <br />VVV'V <br />1 iU-/4 <br /> <br />E .' Inflexion point <br />'C .' <br />!. ' <br />'tl <br />i / <br />;> l <br /> <br /> <br />Discharge (cfs) <br /> <br />Bao 1991). Additional methods are described by <br />Wesche and Rechard (1980). <br /> <br />Multiple Attribute Standard-Setting <br />Methods <br /> <br />All of the methods previously discussed result in <br />a single stream flow value, recommended for a <br />defined period in individual streams. These meth- <br />ods have given rise to the term 'minimum flow.' <br />Such standard-setting recommendations are hard <br />to use in negotiation because too little information <br />is available to allow an informed compromise. <br />Much more must be done to answer the hard ques- <br />tions during negotiation (Wilds 1985). Answering <br />these hard questions requires moving away from <br />tools leading only to minimum flows. Techniques <br />need to show the relation between the amount of <br />habitat and stream flow. Such approaches allow the <br />analyst to display impacts on the resource of inter- <br />est for any given flow. <br />Tools that can be used to achieve this result fall <br />into two groups. The fIrst uses statistical analyses <br />to correlate environmental features of a stream <br />with fIsh population size. An example of this type <br />of analysis is Wyoming's Habitat Quality Index <br />(HQI), described by Binns (1982). An HQI is devel- <br />oped by regressing several habitat variables <br />against the standing crop of fIsh. This procedure is <br />stream-specific, and the recommendations are re- <br />lated to critical low flows. The second group of tools <br />link open channel hydraulics with known elements <br />of fish behavior. Examples include the Physical <br />Habitat Simulation System (PHABSIM), as first <br />presented by Bovee and Milhous (1978) and dis- <br />cussed again by Bovee (1982; also see Milhous et al. <br /> <br />Fig. 2.1. Use of the wetted perimeter <br />method to estimate instream flows. <br /> <br />1984). An important explicit element of PHABSIM <br />and HQI is an analysis of water supply. A water <br />supply analysis should accompany any standard- <br />setting technique to answer the question: What is <br />the likelihood that water will be available to meet <br />the standard? <br />Many people confuse IFIM with the Physical <br />HABitat SIMulation System (PHABSIM). <br />Whereas IFIM is a general problem-solving ap- <br />proach employing systems analysis techniques, <br />PHABSIM is a specific model designed to calculate <br />an index to the amount of microhabitat available <br />for different life stages at different flow levels. <br />Developed from techniques used in the Pacific <br />Northwest, PHABSIM requires the collection of <br />fIeld data on stream cross sections and habitat <br />features, hydraulic simulation to evaluate habitat <br />variables at different flows, and species suitability <br />criteria to calculate stream characteristics with <br />available habitat at alternate flows. Depending on <br />the complexity of the proposed project and the <br />complexity of the stream under study, the collec- <br />tion of fIeld data ranges from inexpensive and <br />quick to costly and time consuming. <br />Using PHABSIM enables the investigator to in- <br />form decision makers about the impacts on fIsh <br />habitat of different flows for different life stages. <br />Attention is typically given to the life stages of fIsh <br />species that are of special concern for management <br />or that are thought to be most sensitive to change. <br />The resulting relation between flow and habitat, <br />generated by linking species criteria with flow-de- <br />pendent stream channel characteristics, aids in <br />negotiation by more clearly depicting the effect that <br />less-than-optimum flow will have on habitat (Geer <br />1980). Figure 2.2 is an example ofa typical habitat <br />