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• <br />Endangered and Threatened Species of the Platte River <br />Water - quality data are not integrated into knowledge about species responses to <br />reservoir and groundwater management and are not integrated into habitat suitability <br />guidelines. Different waters are not necessarily equal, either from a human or a wildlife <br />perspective, but there is little integration of water - quality data with physical or biological <br />understanding of the habitats along the Platte River. <br />The cost - effectiveness of conservation actions related to threatened and endangered <br />species on the central and lower Platte River is not well known. Neither the cost <br />effectiveness nor the equitable allocation of measures for the benefit of Platte River <br />species has been evaluated. The ESA does not impose or allow the implementing <br />agencies to impose a cost - benefit test. Listed species must be protected no matter what <br />the cost, unless the Endangered Species Committee grants an exemption. Cost <br />effectiveness, however, is another matter. The ESA permits consideration of relative <br />costs and benefits when choosing recovery actions, for example. USFWS has adopted a <br />policy that calls for minimizing the social and economic costs of recovery actions, that is, <br />of choosing actions that will provide the greatest benefit to the species at the lowest <br />societal cost (Fed. Regist. 59: 3472 [1994]). In addition, persons asked to make <br />economic sacrifices for the sake of listed species understandably want assurances that <br />their efforts will provide some tangible benefit. In the Platte, the direct economic costs of <br />measures taken for the benefit of species appear reasonably well understood. The <br />biological benefits are another matter. For example, the costs of channel - clearing and <br />other river - restoration measures are readily estimated. Their precise value for cranes is <br />more difficult to estimate, although their general use is fairly well established. <br />The allocation of conservation costs and responsibility also has not been <br />systematically evaluated. USFWS has concentrated its efforts to protect listed species in <br />the Platte system on federal actions, such as the operation of federal water projects. That <br />focus is understandable. Water projects with a federal nexus account for a large and <br />highly visible proportion of diversions from the system. In addition, those actions may <br />be more readily susceptible to regulatory control than others because they are subject to <br />ESA Section 7 consultation. But some nonfederal actions also affect the species. Water <br />users that depend on irrigation water from the federal projects may well feel that they are <br />being asked to bear an inordinate proportion of the costs of recovering the system. A <br />systematic inventory of all actions contributing to the decline of the species could help <br />the parties to the cooperative agreement channel their recovery efforts efficiently and <br />equitably. The National Research Council committee charged with evaluating ESA <br />actions in the Klamath River Basin recently reached a similar conclusion (NRC 2004). <br />The effects of prescribed flows on river morphology and riparian vegetation have not <br />been assessed. Adaptive- management principles require that the outcomes of a <br />management strategy be assessed and monitored and that the strategy be adjusted <br />accordingly, but there has been no reporting of the outcomes of the 2002 prescribed flow, <br />no analysis of vegetation effects of managed flows, no measurement of their geomorphic <br />effects, and no assessment of their economic costs or benefits. <br />The connections between surface water and groundwater are not well accounted for in <br />research or decision - making for the central and lower Platte River. The dynamics of and <br />12 <br />