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<br />SUPPLEMENTAL WATER SUPPLY <br /> <br />In Nebraska both surface water and groundwater are <br />potential sources of supply for supplemental water. <br />Total outflow from the state's streams averages from <br />about 5 million acre-feet in dry years to more than 15 <br />million acre-feet in wet years. The fact that close to half <br />of this flow originates in the generally lower elevation <br />eastern third of the state and that areas with higher <br />economic potential generally occur in upstream areas <br />to the west presents definite economic, technologic, <br />and environmental constraints to its use. However, <br />some of this supply could be stored and/or diverted for <br />use at other times and in other places. Groundwater <br />reservoirs which are recharged by losing reaches of <br />streams represent a unique source of surface water that <br />has become groundwater. <br />Even with a projection of 200 years of maximum <br />development of groundwater for irrigation on overlying <br />land, there would be groundwater in portions of cen- <br />tral and northwest Nebraska available for supplemen- <br />tal supplies. Additionally, the mounding of groundwater <br />south of the Platte River in central Nebraska is another <br />source for such supply. <br />In addition to a supply, most supplemental water <br />development requires that the water be transferred over <br />or under the ground. In Nebraska there still is limited <br />potential for gravity transfer systems. Because much <br />of the remaining source of supply is at the lower eleva- <br />tions in the eastern portion of the state, many sup- <br />plemental water developments in the future will require <br />pumping and lifts. These methods of transfer may in- <br />troduce many technological, economic, and en- <br />vironmental constraints. <br />There are potential sites across the state for the <br />storage of water on the surface. Over 200 sites which <br />would have a normal capacity of 1,000 acre-feet or <br />more have been studied previously by others. The <br />facilities which might be built on these sites could not <br />only directly supply water, but in many cases have the <br />potential to recharge the groundwater reservoir. In <br />some cases they could also serve such uses as flood <br />control, power generation, or fish, wildlife and <br />recreation. <br />Underground storage of water in many areas of the <br />state represents an important potential for the future <br />development of supplemental water systems. These <br />areas include locations where there have been water- <br />level declines in the groundwater reservoir and where <br />there are layers of unsaturated materials which could <br />contain and release \AJater. <br /> <br />IMPACTS AND CONSTRAINTS <br /> <br />When an impact from a supplemental water develop- <br />ment is proven, or is perceived to be a hindrance to <br />development, then the impact is considered a con- <br />straint. Impacts and constraints can result from a varie- <br /> <br />XII <br /> <br />ty of environmental, technological, social, legal, institu- <br />tional, or economic factors. <br />The results of this study seem to indicate that often <br />there are net environmental impacts which would be <br />considered negative in the area where groundwater is <br />withdrawn for use as a supplemental water supply. By <br />contrast, the net environmental impacts would usually <br />be positive in areas where the groundwater reservoir <br />might be used for storage purposes. Both surface <br />storage and transfer of water could face environ- <br />mental constraints or have positive environmental im- <br />pacts, depending on the site and management of the <br />development. The debate over which effect might oc- <br />cur is most often a result of the evaluator's perspec- <br />tive and of a lack of environmental data for a specific <br />instance or site. <br />Most technological factors which are obstacles to the <br />development of supplemental water supply systems <br />can be overcome. However, overcoming the <br />technological obstacles may be very costly - beyond <br />the benefits of the development. <br />Social constraints to supplemental water develop- <br />ment are many, varied and closely dependent on the <br />type of development and its specific location(s). The <br />attitudes of people become the major social constraint. <br />Their attitude may be formed in reaction to social im- <br />pacts on land use, population or the local economy. <br />These attitudes also may be in relation to how tax <br />dollars are spent and who receives benefits. Or, their <br />attitudes may be related to traditions and mores. In any <br />event, the expression of peoples' attitudes in a <br />democratic society through social pressures, the <br />political process and the legal system can present a <br />constraint that cannot be ignored in developing <br />supplemental water supplies. <br />The two aspects of Nebraska surface and ground- <br />water law most constraining supplemental water-supply <br />development are: (1) the preference for junior natural- <br />flow appropriators over senior storage appropriators <br />during the irrigation season, and (2) the absence of <br />clear agricultural groundwater-transfer authorities. <br />The major federal institutional constraints to <br />supplemental water project development are en- <br />vironmental and financial. One major federal environ- <br />ment constraint is that many proposed projects could <br />cause environmental problems and thus may be <br />politically challenged because of material contained in <br />the environmental impact statement or legally challeng- <br />ed because some parties may not believe the statement <br />is adequate. Another instance where institutional pro- <br />tection of the environment may constrain project <br />development in Nebraska is the Platte Whooping Crane <br />Critical Habitat designation by the Federal Government. <br />A major state environmental constraint is the require- <br />ment that state actions not jeopardize the continued <br />existence of threatened or endangered species or their <br />critical habitat. The major financial constraints seem <br />to be (1) the availability of federal water resources <br />