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<br />An example of a two-dimensional matrix (depth, <br />and velocity) is given in Table 2. In each cell of the <br />matrix, the upper numeral refers to the surface area of <br />stream having a certain depth-velocity combination. <br />The numerals in parenthesis refer to the weighted <br />usable area. Due to the large number of calculations <br />required for each reach matrix, a computer program <br />has been developed by the Cooperative Instream Flow <br />Service Group to make all calculations for as many <br />species as desired from a single set of hydraulic unput <br />data (Main, 1978b). <br /> <br />For each species and life stage, weighted usable <br />area may be plotted against discharge and various <br />flow regimes, such as median monthly flows or l-in-l0 <br />year monthly low flows (Figure 3). Such plots can <br />show critical time periods for a given life stage, <br />limiting habitat availability for each life stage (i.e., <br />physical carrying capacity), and limiting habitat <br />availability for different species. Since changes in <br />hydraulic characteristics will initiate differential <br />species reactions, the incremental method is <br />particularly useful in evaluating changes in species <br />composition as inferred from changes in habitat <br />usability. <br /> <br />The quality of the physical habitat for a specific <br />instream use is a deterministic function of the flows, <br />and can be described as a stochastic process by <br />converting the flows to some habitat index associated <br />with the flows. <br /> <br />In most controlled river systems a "minimum" flow <br />is established for certain stream reaches and the <br />system operated with this "minimum" flow as a <br />constraint which is often violated under certain <br />conditions such as low water yield (drought). Rarely <br />are system operating criteria developed considering <br />the stochastic variation of the production of benefits <br />from use of the water instream (Milhous and Bovee, <br />1978). The IFG incremental methodology is designed <br />to allow this stochastic approach. <br /> <br />The IFG incremental methodology has been <br />developed to quantify the impact on fish habitat <br />resulting from incremental or alternative <br />modifications in stream flow. Listed below are 12 most <br />commonly asked questions of the IFG methodology <br />which are also applicable to anticipated assessments <br />of eastern streams impacted by coal developments. <br /> <br />1. What does the IFG incremental methodology <br />do which previous in stream flow methodol- <br />ogies could not do? <br /> <br />Most instream flow methodologies in the past have <br />specified minimum flow requirements for fishes. The <br />IFG incremental methodology examines what will <br /> <br />happen to the fish habitat with an increase or decrease <br />in the amount of flow by any given increment. <br />Further, it makes these predictions for each of <br />several species of fish, each life history stage of those <br />species, and for each month of the year. Thus, the IFG <br />incremental methodology is no longer restricted to <br />single value minimum flows. It is useful for predicting <br />and quantifying impacts and establishing instream <br />flow regimes for specified management objective <br />(habitat maintenance). <br /> <br />2. What information does the IFG Incremental <br />Methodology provide? <br /> <br />The methodology provides information on physical <br />impacts of altered stream flow on fish habitat. These <br />impacts are expressed as an index of surface area of <br />usable habitat for each reach of stream considered. <br />The index relates a particular stream reach with <br />optimal habitat of the same surface area. The <br />methodology predicts the suitability of the stream <br />habitat for fish of a given species and life stage as <br />defined by combinations of depth, velocity and <br />su bstrate for specified stream discharges. <br /> <br />Based on information about a species and its habitat, <br />an index termed "weighted usable area" is calculated. <br />The index displays the optimal square feet equivalent <br />of stream that provides suitable fish habitat, <br />compared to the total square feet of surface area. <br />Computer programs are available to calculate <br />weighted usable area for each of several stream flows. <br />Thus, the "best" str-eam flow for any desired <br />management objective can be determined. <br /> <br />These results help the fishery manager determine <br />the potential impact of incremental changes in stream <br />flow on fish habitat. This information can be used to <br />make judgements about which stream flow quantities <br />meet his management objectives. It can also be used to <br />predict the environmental impact of water <br />development activities on fishes by identifying life <br />stages and times of the year which may become <br />limiting to the continued well-being of a fish species. <br /> <br />3. Why is an instream flow methodology <br />important? <br /> <br />Under various laws (for example, the Fish and <br />Wildlife Coordination Act), fish and wildlife agencies <br />have made stream flow recommendations to water <br />development agencies. Usually, the recommendation <br />is for a minimum flow. A minimum flow is that stream <br />flow below which there will be disastrous effects on <br />fish. The minimum flow concept has not been very <br />useful for predicting the impacton fish from modifica- <br />tions in stream flow levels, such as reducing the flow <br />from 200 to 150 cubic feet per second. The IFG <br />incremental methodology, which allows such <br />predictions, represents a breakthrough in water <br />management by placing instream use of water on an <br />equal status with offstream or consumptive uses. <br /> <br />5 <br />