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<br />>, <br /> <br />Differing Methodologies and the Role of "Professional Judgment" <br />Because I was specifically asked to review the methods that were used by the U.S. Fish and <br />Wildlife Service for assessing instream flows, it appears that the efficacy of the various instream <br />flow methodologies was not fully understood while studies leading to the recommendw flows were <br />being conducted. Heavy investment in IFIM was made, and it clearly was not warranted. The <br />method as currently formulated should not be used in the future in the potamon reaches of the <br />Upper Colorado River Basin, owing to the problems I detailed above. Weaknesses in the IFIM <br />approach were recognized as flow recommendations were developed and IFIM analyses were not <br />used to support the flow recommendations on the Green and Yampa Rivers. Rather, ecological data <br />and interpretations were couched in terms of "professional judgement" to provide rationale for the <br />recommendations. On the Colorado River, IFIM analyses were used explicitly, along with reference <br />to other studies which I summarized above (e.g., squawfish need clean gravel scoured by spring <br />runoff and 180 - 220 C temperatures that usually occur on the declining limb of the runoff to spawn <br />successfully). Use of IFIM on the Colorado River and discarding of it on the Green River raised <br />doubts about the recommended regimes, which undermined the clear inference from the ecological <br />studies that higher amplitude peak to baseflow regimes were needed. <br />Moreover, emphasis on on "professional judgment" was overemphasized, given the general <br />high quality of the ecological studies that were available. I agree with Tyus (1992) that <br />considerations of in stream flow provisions were based on ecological information obtained in <br />suboptimal habitats of these fishes. And, perhaps, the "biological opinion" process overshadowed <br />the science. <br />The recommendations should have been based entirely on inferences from long-term <br />quantifications of energetics, habitat preferences, recruitment, channel geomorphology and food <br />web composition and stability and simple correlations with the highly variable flows that eventuated <br />over the decade of the 1980s. Had that been done, I think the flow amplitude recommended by the <br />U.S. Fish and Wildlife Service on the Green River would have been higher (higher spring peaks, <br />lower baseflows) and more consistent with my synthesis of the existing information. The Colorado <br /> <br />62 <br />