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<br />0042 <br /> <br />2.14 <br /> <br />2.4 Summary of Impacts for Alternatives ,Considered in Detail <br /> <br /> <br />The following tables summarize the impacts and issues associated with the <br /> <br />alternatives. Table 2.2 contains both quantitative and qualitative data <br /> <br /> <br />derived from the text in Chapter IV, Environmental Consequences, and from <br /> <br /> <br />appendix material. Table 2.3 presents a qualitative assessment of whether, <br /> <br /> <br />and how well, the public issues and concerns are addressed by the <br /> <br /> <br />alternatives. <br /> <br />~}. <br /> <br />~ <br /> <br />The various environmental effects of the different alternatives are due <br /> <br />to differences in the amount of water sold from Ruedi, and differences in the <br /> <br /> <br />timing of the release of water from the reservoir. Alternatives 2 and 3 would <br /> <br /> <br />produce contracts for the largest amounts of water (over 70,000 acre-feet), <br /> <br /> <br />followed by Alternatives 4, 5 and the preferred (over 50,000 acre-feet) and <br /> <br /> <br />then Alternatives 6 through 10 (from 39,000 to 45,000 acre-feet). Even with <br /> <br /> <br />the largest volumes of water sales, there would not be any effects on erosion <br /> <br /> <br />or scour of stream channels because flow rates would never exceed the <br /> <br /> <br />threshold necessary to move bed materials in the rock and cobble controlled <br /> <br /> <br />stream channels. Significant flow changes greater than + 10 percent occur for <br /> <br /> <br />several months under all alternatives, but Alternatives 4 and 5 have the most <br /> <br /> <br />months of altered stream flows, followed by Alternatives 2, 3, 7 and the <br /> <br /> <br />Preferred, and then by Alternatives 6, 8, 9 and 10, which have the fewest <br /> <br />number of months with significantly altered stream flows. <br /> <br /> <br />The encouragement of water deliveries in the winter in order to avoid <br /> <br /> <br />significant reservoir drawdown in the summer recreation season, is best accom- <br /> <br /> <br />plished by Alternatives 3, 5, 6, 8, 9 and 10, and less so by Alternatives 2, <br /> <br />4, 7 and the Preferred. The capability to deliver water in the winter in <br /> <br /> <br />spite of possible icing conditions was judged adequate for all Alternatives <br /> <br /> <br />except 2 and 4, which have winter flow rates low enough that icing might pose <br /> <br /> <br />a problem in dry years. <br /> <br />The effects of the alternatives on fisheries were evaluated largely by <br /> <br /> <br />the amount and duration of habitat losses, with the alternatives falling into <br /> <br /> <br />three groups; one, Alternatives 2, 4, and 5 showed the greatest number of <br /> <br />months with significant trout habitat losses (more than 10 percent), followed <br /> <br /> <br />by Alternatives 7 and the Preferred, followed by Alternatives 3, 6, 8, 9 and <br /> <br /> <br />10 with the fewest months of habitat loss. <br /> <br />. <br />