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Operation of the Aspinall Unit as proposed under Alternatives A and B would result in decreased <br />Blue Mesa storage levels, particularly over a dry period such as occurred between the fall of <br />1988 to the spring of 1991. However, in all but very dry conditions (for example, in 1977), <br />Alternatives A and B would meet or exceed supplies to existing users as compared to historic <br />conditions while providing desired fish flows below Redlands. In very dry years, such as 1977, <br />water supply shortages would be shared by both fish and water users. <br />All alternatives for the interim agreement would be implemented under Colorado water law, <br />would not interfere with the purposes of the Aspinall Unit, and would help meet purposes of the <br />Recovery Program -- to recover the endangered fish while allowing water use and development <br />to continue under the "Law of the River." <br />River Flows, Water Rights and Water Uses -- Review of past hydrologic records indicates that <br />flows of at least 300 cfs are in the river below the Redlands Diversion Dam during July through <br />October in most years already. However, in certain below average runoff years, special <br />releases would need to be made because flows would be too low to meet the needs of both the <br />fish and the senior water rights. Under the originally proposed Alternative C, such senior water <br />rights could request a call on the river. This would cause upstream junior diversions (for <br />example in the Upper Gunnison Basin or along the North Fork of the Gunnison) to be reduced <br />or shtit down to increase the supply to the Redlands Diversion. While such calls have occurred <br />during dry years under existing conditions, they would occur more frequently with the interim <br />flow agreement as presented in Alternative C. One purpose of Alternatives A and B is to see <br />that junior water users are better protected from such calls. <br />To show the effects of the agreement alternatives on river flows, water rights, and river <br />administration, data from Appendix E was used for 4 representative water years: wet (1985), <br />normal (1987), dry (1990), and very dry (1977). The monthly information is shown to allow <br />comparison among all the alternatives: No Action and Alternatives A, B, and C. Data for No <br />Action represents the baseline against which anticipated conditions under the interim agreement <br />alternatives are compared. Alternatives A and B are shown together because the water supply <br />requirements are the same for both alternatives. Tables 1 through 3 show monthly average <br />Gunnison river flows for the representative years at three locations on the river near Whitewater, <br />below Redlands, and below the Gunnison Tunnel. <br />Table 1 shows that average monthly flows near Whitewater are nearly the same for all <br />alternatives during wet, normal, and very dry years, but they change in a dry year such as 1990. <br />When flows of at least 1,095 cfs occur at Whitewater, the needs of both the fish and water users <br />are met (750 cfs for the Redlands Diversion, 45 cfs for the absolute water rights between <br />Redlands and Whitewater, and 300 cfs for endangered fish). Figure 3 illustrates the 1990 <br />information from Table 1 in a bar graph format. The graph shows flows were often less than <br />1,095 cfs in the winter and summer months for No Action and Alternative C. <br />Figure 3 shows that Alternative C does not provide sufficient flow for both fish and water users <br />under dry year (for example, 1990) conditions. Shortages to water users would occur during <br />20