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does require that two or more parties agree on what the status quo is, The <br />methodology described here is designed to define a starting condition, and <br />then provide data on incremental changes so that professionals can evaluate <br />new conditions. It is quite possible that a solution arrived at through <br />incrementalism would have been considered radical had it been proposed at the <br />outset. <br />The Instream Flow Incremental Methodology (IFIM) adheres to the principle <br />of incrementalism. In one sense, the IFIM can be thought of as a collection <br />of computer models and analytical procedures designed to predict changes in <br />fish habitat due to increments of flow change. Indeed, this methodology does <br />enable such predictions. It can also be used to evaluate such diverse impacts <br />as changes in channel structure or alterations in waste loading from a pollu- <br />tion source. In fact, it can be used to translate changes in land use to <br />changes in the stream environment, if the user follows it that far. However, <br />the IFIM is much more than a collection of computer models. It is, in fact, a <br />thought process that begins with the structuring of the study design and <br />carries through to the final negotiation of a problem solution. Several of <br />the underlying principles of the methodology are presented and discussed <br />below. <br />The first, and probably most important principle, is that implementation <br />of an instream flow regime is inseparable from water management. Therefore, <br />the IFIM should be thought of as a water management tool. It is not intended <br />to be an ecosystem model. However, it is designed to have environmental and <br />ecological applications. The IFIM will not ensure against ecological blunders, <br />as is true with other decision systems, including ecosystem models. Ecological <br />blunders can be prevented only insofar as we are able to foresee the conse- <br />quences of our actions and adapt our management accordingly. The IFIM does <br />allow a systematic evaluation of different management options, providing <br />quantitative estimates of fish habitat available under each option. <br />The second principle is that the method is not intended to generate a <br />single solution, but to predict the impacts of different alternatives. Users <br />seeking a mechanistic solution to a problem may find this methodology difficult <br />to understand. The methodology has been specifically designed to provide <br />multiple solutions. Therefore, the user must embrace the philosophy of incre- <br />mentalism and iterative problem solving before the methodology can be used to <br />its full advantage. Following this philosophy, the methodology best lends <br />itself to a systems approach. Such an approach opens a wider variety of <br />options and water management alternatives to an application of the methodology. <br />The third principle is that the objectives of any application must be <br />rigorously defined. It is quite possible for two identical applications of <br />the methodology to result in vastly different solutions, due solely to the <br />objectives of the analysts. For example, two groups may have as their <br />objective, "the design of a flow regime to maintain a fishery at a minimally <br />acceptable level." To one group this really means, "To maximize fish habitat <br />within the constraints of the available water supply." To the other group, <br />the same objective means, "To maximize out-of-channel water use without elimin- <br />ating the fishery." <br />2