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<br />There <br />resources.8 <br />themes. <br /> <br />are numerous variations of <br />This section presented <br /> <br />strategies <br />what seem <br /> <br />for protection of instream <br />to be the most important <br /> <br />IV. CONCLUSION <br /> <br />In Section I we presented data concerning the collocation of high quality <br />instream resources and energy projects and indicated generally the reaches <br />where conflicts might occur. Can we say anything specific about the conse- <br />quences for either the energy industry or fish and wildlife? <br />Numerous water supply and demand alternatives are available to the energy <br />industry. The most expensive of these--dry cooling--reduces water require- <br />ments for electric plants to 1,000 acre-ft per year/IOOO MW at an incremental <br />cost of less than 10% and for coal gas plants to as little as 2000 acre-ft/250 <br />million ft3/day plant at an incremental cost of 1.5% (see Abbey, 1979 a and <br />b). Supply alternatives to streamflows include groundwater, municipal and <br />other wastewater, and transfers from present users. <br />Fish and wildlife management is less flexible. Numerous studies stress <br />the susceptibility of freshwater ecosystems to habitat modification, the most <br />pervasive influence being reduced flow. When depletion is gradual and cumula- <br />tive, mitigation is especially difficult. <br />The issue, then, is not whether streamflow reservations will constrain <br />energy development but whether the increased costs of water conservation are <br />worthwhile. That requires specific information concerning the effects of <br />development on streamflows and water quality. Getting that information <br />requires application of such a technique as the Incremental Methodology as <br />well as basic ecological research. <br /> <br />, <br /> <br />81n 1978 the US Fish and Wildlife Service published a series of reports <br />discussing streamflow protection in each of 13 Western states. <br /> <br />7 <br />