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<br />- 3 - <br /> <br />environmental consequences from the action alternatives not be taken to restrict the range of <br />permissible responses under the Program's 151 Increment. <br /> <br />We believe that the framework and resource commitments in the Proposed Program provide <br />a reasonable approach for avoiding jeopardy and addressing species needs in the face of <br />scientific uncertainty, The DEIS fails to reflect that this jointly implemented program is <br />designed to react to trends to the species or habitat using a variety of management tools. The <br />DEIS and Service's biological opinion should evaluate the Program as a vehicle equipped to <br />work through future uncertainties and management options on the Platte with respect to <br />flows, sedimentation, habitat lands and other issues, and not unilaterally attempt to <br />predetermine the specific management actions that are today thought "acceptable." We <br />request that the Department of Interior analyze the Proposed Program as based upon <br />implementation of the 151 Increment Milestones and with specific recognition that it may <br />result in a range of permissible management strategies and responses, <br /> <br />4, The CWCB remains hopeful that we will be able to support the Proposed Program and the <br />Governance Committee Alternative. The CWCB does not support any ofthe "other action <br />alternatives" due to legal, technical, financial, and political issues associated with each of <br />these alternatives. <br /> <br />5, The DEIS contains extensive opinions which should be removed from the document. The <br />history of habitat use and trends for the target species and the impact analysis are not <br />objective and unbiased. The DEIS should be a factual summary of the no action and action <br />alternatives and a factual assessment of the outcome of the federal action. In addition, data <br />substantiating the positions or outcomes that are stated must be provided and referenced. <br /> <br />6, The DEIS should be revised to remove internal inconsistencies. <br /> <br />7. Reasonable, appropriate scientific methods are not used in the DEIS to evaluate present <br />conditions. The most recent species and habitat information is not used [i.e" whooping crane <br />and sediment investigations conducted during the Cooperative Agreement (CA), data <br />regarding tern and plover use of non-riverine habitat, and vegetation studies]. The <br />limitations of baseline data are also not disclosed. A technical review of the baseline data <br />(see CA Technical Committee comments dated October 22,1999, and subsequent comments <br />though 2003; see also John Nickum comments, United States Fish and Wildlife, April 2000 <br />Technical Committee minutes) reveled significant deficiencies, which previously lead the <br />Service to conclude that the information could not be used as a quantitative baseline, (see <br />above references). Yet the information is erroneously recreated in the DEIS. Examples of <br />deficiencies include: lack of defined methodologies for data collection, changed conditions <br />between observations and data collection, use of non-peered reviewed models and methods, <br />and use of models that have not been updated with current information. <br /> <br />The DEIS also establishes a present condition which does not reflect environmental and <br />ecological variability that has occurred over time. This is especially true in regard to climate <br />changes. The mid-1800s were a period of extreme drought followed by a wet period in the <br />early 1900s. The river channel configuration and land use cover used in the DEIS do not <br />reflect a "baseline condition", as the geomorphology and land cover were reacting to <br />dramatic climatic shifts and the impact of settlers moving west. <br />Flood Protection. Water Project Planning and Finance. Stream and Lake Protection <br />Water Supply Protection. Conservation Planning <br />