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<br />Throughout the basin, uses of water for domestic <br />purposes are assigned the highest priority under State <br />law. This is not the case in some States with respect to a <br />preferential status for livestock water. Quantities with- <br />drawn and consumed for both of these purposes are <br />relatively small. However, the storage of surface waters <br />for livestock use results in depletions due to evaporation <br />losses in the arid portions of the basin and could result <br />in competitive demands for scarce supplies. <br />The economic and social necessity for livestock water <br />use dictated action to provide for such use in plan <br />formulation. The great variance in, and localized nature <br />of, the problem required general treatment after con- <br />sideration of the available supply of ground and surface <br />water, water quality, climatic conditions, and distribu- <br />tion of electric power supplies. <br />The projected future water requirements for livestock <br />use are dependent on base projections. These projections <br />indicate a significant increase in livestock production. <br />From a regional standpoint, economic and social objec- <br />tives are aimed at dampening, to some extent, the loss of <br />farm population and intensifying agricultural produc- <br />tion. The initial projections are, therefore, adequate for <br />planning purposes, but will have to be reviewed, and <br />adjusted as necessary, taking into account the effects of <br />a long-range plan. <br /> <br />Electric Power Water Supply <br /> <br />Studies to project the future electric power needs of <br />the basin were conducted as an integral part of the <br />Federal Power Commission's National Power Survey. <br />With minor exceptions, the power study area coincided <br />with the externai boundarIes of the Missouri River Basin. <br />However, the subbasin boundaries and population dis- <br />aggregations used in the comprehensive framework study <br />did not lend themselves conveniently to power analysis. <br />Therefore, projected electric power requirements were <br />based on the FPC Power Supply Areas (PSA's). Each <br />PSA represen ts essentially the service areas of related <br />groups of major electric utilities. The projected PSA <br />power requirements and consumptive water use were <br />then disaggregated to the subbasins. <br />Power studies covered hydroelectric and thermal <br />sources as well as private and public sources and <br />distribution systems. While the location of fuel reserves <br />was reported, the study is not in sufficient detail to <br />permit a firm location of future generating plants or <br />distribu tion lines. <br />Water requirements for hydropower production are <br />non-consumptive and are limited by the existing pattern <br />of operation and the few remaining structural sites <br />suitable for development. Cooling water requirements <br />for thermal-electric plants were determined for each <br />subbasin in terms of condenser cooling water require- <br /> <br />58 <br /> <br />ments, required streamflow diversions, and cooling water <br />losses. This degree of estimating is adequate for the <br />purposes of this study. It does reveal that each future <br />proposal for locating thermal-electric power plants must <br />seriously consider the effect of withdrawal and con- <br />sumptive use of water, and the temperature effect on <br />other wa ter uses, both locally and regionally. <br /> <br />Although the projections of future water require- <br />ments are documented, the demands for cooling water <br />are not susceptible to simple evaluation. The complexity <br />of the evaluation can be traced to the alternatives <br />available for cooling purposes. The cheapest cooling <br />form is a flow-through system with a very small part of <br />the water lost through consumption, but with significant <br />temperature rises in the return flow. As an indication of <br />the magnitude of such future cooling water require- <br />ments, a summation of projected gross withdrawals <br />approach 4.9 million acre-feet annually by the year <br />2020, which allows for the use of supplemental type <br />cooling systems. By introducing closed systems and <br />cooling towers, problems such as temperature increases <br />and water quantity are minimized, but this can be <br />achieved only through additional cost. Within the plan <br />formula tion process, therefore, it was necessary to <br />weigh all factors in order to determine the best possible <br />course of action. These included recognition of bene- <br />ficial as well as detrimental effects, the costs involved, <br />and the probable reaction of the consumer and his <br />willingness to pay for maintaining certain economic and <br />social values that may otherwise be lost. <br /> <br />Water Supply for Mineral Development <br /> <br />Additional water required for future mineral develop- <br />ment and processing is projected for all subbasins. Gross <br />water withdrawal requirements for metals, non-metals, <br />fuels, and sand and gravel approach 538,000 acre-feet <br />annually by year 2020. Of this amount, 346,000 <br />acre-feet are for sand and gravel processing. <br /> <br />FISH AND WILDLIFE <br /> <br />The demands and desires for fish and wildlife in the <br />Missouri Basin and its subbasins were determined by the <br />several State fish and wildlife agencies and the Bureaus <br />of Sport Fisheries and Wildlife and Commercial Fisher- <br />ies. The study included an inventory of lands and water <br />dedicated primarily to fishing and hunting, and areas <br />where fish and wildlife is an ancillary use. The single- <br />purpose category includes lands owned or controlled by <br />State fish and game agencies and the Bureau of Sport <br />Fisheries and Wildlife. Primary use lands are public and <br />private lands where fish and wildlife is one of the <br />principal multi-purpose uses. Identified also were the <br />areas of habitat or range for select fish and game species <br />