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<br />, .. '~ <br />Porcella [16] compared with information that was obtained <br />from various sources by the U.S. Fish and Wildlife Service <br />(FWS). Of importance here is not whether the figures are <br />exact, but rather the trend that is depicted. Much of the <br />water being sold to the energy development companies was <br />~re~iously used for a~ricultural purposes. El-Ashry (17) <br />1nd1cated that the Sh1ft of water use from agriculture to <br />energy development would have adverse impacts on surface and <br />ground water and, consequently, on fish and wildlife. This <br />would happen through an increased depletion of available <br />ground w~ter resources which, in some areas, depends on deep <br />~ercolat1on of excess water from irrigation runoff. Streams, <br />1n many areas, are also sustained by excess water draining <br />from irrigated lands. <br /> <br />I t is also possible that another factor could cause a <br />n~t increase in water use when ,there is a shift from irriga- <br />t10n to energy development. There are many situations where <br />the full allotment of water owned for the purpose of agri- <br />cultural u~e ~s not c~mpletely utilized during a given year; <br />however, 1t 1S Poss~ble that this may change and energy <br />developers may cons1stently utilize the majority of the <br />allotted water. This is a result of the different demands <br />for water between the agriculture uses and energy development <br />uses. <br /> <br />One study estimated that only 5% [about 0.1 x 109 m3 <br />(90,000 AF)J of current agricultural water supplies 1n <br />Colorado and Utah will have been converted to energy use by <br />the year 200~ [18J. However, several of the energy develop- <br />ment compan1es purchased water righ ts (many of which had <br />previously been used for agricultural purposes) during the <br />1950's and 60's, and may not have been included in the above <br />study. For example, a group of energy development companies <br />have proposed removing a maximum of 0.45 x 109 m3 <362,000 <br />AF) of water annually from the Colorado River near the town <br />of DeBeque, Colorado. Most of these water rights are senior <br />and were purchased 15-30 years ago. This is just one example. <br />The FWS has worked with several energy development companies <br />that have proposed project s that would require significant <br />amounts of water that has already beer. purchased, some having <br />purchased the water several years ago. It is assumed that <br />much of this water was used for agricultural purposes or is <br />still being used for agricultural purposes (via leases, <br />etc.) until it is needed for energy development. <br /> <br />PROSPECTS FOR THE FUTURE <br /> <br />The continued existence of the endangered Colorado River <br />fishes will require cooperation an~ communication among <br /> <br />546 <br /> <br />........- <br /> <br />diverse interest groups. As demonstrated in the snail darter <br />vs Telico Dam case, all future development will not likely <br />come to a halt because of unique fishes such as the bony tail <br />chub, humpback chub, and Colorado squawfish. Probably <br />several proposed dams and water diversion projects will have <br />to be abandoned. Other projects must expect some delay, <br />compromises, and modifications in pr?jects to, mai,ntain <br />certain environmental conditions and avo1d the ext1nct1on of <br />these rare fishes [1]. However, this rationale is not new, <br />Wheelwright [19J pointed out that the majority of nearly 150 <br />conflicts between the provisions of Section 7 of the 1973 <br />Endangered Species Act and planned, federally involved <br />projects between 1973 and 1977, ha~ ~een resolv~d through <br />negotiation and compromise. The ma]Or1ty of Sect10n 7 work <br />in Colorado and Utah, dealing with fish that the FWS ha~ b7en <br />involved in, has also resulted in some form of negot1at1on <br />and compromise. In the future we will have to be even <br />increasingly selective with respect to projects a~l~wed <br />to proceed and even more demanding with respect to,mod1f1ca- <br />tions and constraints to minimize undesirable env1ronmental <br />alterations. <br /> <br />Since the demand for water appears to be the issue <br />concerning the future survival of the native upper basin <br />fish, we must reduce this demand or face the fact that <br />extinction of some unique fish and additional loss and <br />modification of natural riverine ecosystems will occur. <br />Perhaps we should look more to moderating or minimizing <br />our demands for still more water. We cannot afford to be <br />extravagant. The following is a list of some potential means <br />for reducing our future water demands. <br /> <br />1. Use of energy alternatives (solar, etc.). <br />2. Conservation methods (less water use for domestic <br />purposes, more efficient irrigation systems like <br />those used in some arid countries, etc.). <br />3. Reduce the level of planned activities. <br />4. Development of new technologies (where cost/benefit <br />ratios usually prohibit this aspect, the future <br />price tags on water might make them more feasible). <br />5. Use of ground water that has little or no effect on <br />surface water (Spofford [20J, estimated that the <br />recoverable reserve of ground water in the upper <br />30.5 m (100 ft) of saturated rocks may be as much as <br />142 x 109 m3 (115 MAF). However, about 99 x 109 m3 <br />(80 MAF) (70%) is saline). Care is required if <br />ground water is used because ground w~ter s?urces <br />can be easily polluted and lost, espec1ally 1f not <br />readily recharged. <br />6. Weather modifications (cloud seeding). <br />