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hatchery origin and exchanges) might provide information on questions of fitness and genetics as <br /> they may influence body condition. <br /> Further and more detailed analyses of the kinds suggested above might help to clarify whether a <br /> systemic or localized deterioration of body condition in pallid sturgeon is occurring in the <br /> Missouri River and, if so, where it is occurring. Additional analyses could allow the investigators <br /> to answer the first question posed to the team. Do note that the relevance of the second question <br /> is contingent on the answer to the first question. Following further analysis, if a"skinny fish" <br /> phenomenon is merely an artifact of the Shuman et al. formula, subsequent efforts that speculate <br /> on causal mechanisms are unnecessary. However, if additional analyses demonstrate that the <br /> condition of pallid sturgeon is declining in the lower Missouri River, inferences about the <br /> influence of habitat quality need to be drawn from data beyond point measures of hydrodynamics <br /> and bed elevation as developed in the current document. Useful characterization of pallid <br /> sturgeon habitat requires a more comprehensive consideration of resources (and resource <br /> conditions) used by the fish. Such analysis of habitat conditions using an ecosystem-based <br /> approach that addresses, for example food resources using an energetics-based food web <br /> analysis, appears beyond the scope and intent of the current examination of pallid sturgeon <br /> condition in the Missouri River and is likely constrained by available data. However, any <br /> discussion of habitat quality as a potential cause of low body condition based on limited <br /> hydrology data(as in the current document) remains highly speculative—unless river <br /> hydrodynamics can be shown to serve as a valid proxy measure in lieu of a more realistic, multi- <br /> dimensional description of habitat. <br /> The purpose of the Randall et al. report was to assess new information that might prove essential <br /> to managing pallid sturgeon in an adaptive framework. Accordingly,the report could benefit <br /> from an introductory discussion of how the body condition of pallid sturgeon relates to or <br /> influences the metrics outlined in the Adaptive Management Plan. It is important for river <br /> managers to consider any new information pertaining to trends in the body condition of pallid <br /> sturgeon with reference to the Effects Analysis (EA), specifically the Conceptual Ecological <br /> Models(CEMs), and to determine how information on body condition fits into the ecological <br /> state of the MRRP action area,the primary management hypotheses for pallid sturgeon, and the <br /> larger-scale programmatic components of the AMP. While there is some discussion of the effects <br /> of body condition on recruitment at the end of the Randall et al. report, it is not clear how the <br /> new information would (or should) influence the metrics outlined in the AMP. Ultimately, any <br /> new information on body condition should be evaluated in relation to the critical issue of pallid <br /> sturgeon recruitment in the Missouri River. <br /> The lack of a clearly stated connection between new information(here the report by Randall et <br /> al.) and the data-driven efforts already undertaken under the MRRP suggests that a revised <br /> approach to vetting and conveying new information into the MRRP is advisable. The following <br /> paragraphs offer some guidance for addressing new information in the context of CEMs,the EA, <br /> and the program's hypothesis testing framework: <br /> Any concerned party is encouraged to bring to the MRRP new data or other information on the <br /> ecology and behavior of the listed species, resources and habitat attributes that affect those <br /> species including environmental stressors, ecosystem processes that are known or suspected to <br /> ISAP Comments on Draft Pallid Sturgeon Condition Assessment Page 3 of 4 <br />