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<br />. <br /> <br />. <br /> <br />~:;':;-;';.r~-:;~ <br />~I Mr. A. Jack Garner <br /> <br />~ <br />~ <br /> <br />2 <br /> <br />July through September 10, while still supplying sufficient water for <br />conservation of endangered fish habitat as recommended in the June 15, 1987 <br />USFWS biological opinion. <br /> <br />Under the Preferred Alternative with Conservation Measures, the Bureau <br />would withhold 5,000 AF of water from the volume previously anticipated for <br />sale to industrial users for conservation of endangered fish habitat. As part <br />of this alternative, and additional 5,000'AF would be made available from Ruedi <br />in the months of July through September. With the Green Mountain mitigation <br />scenario described in Section 5.2, Ruedi would "maintain higher reservoir water <br />elevation in nearly all months for all conditions." However, paragraphs <br />depicted in Sections 5.3 and 5.4 do not seem to accurately reflect numbers <br />developed in Table 2.1, which describe changes in elevation and volume at <br />Rued i. <br /> <br />With Green Mountain Reservoir prov iding 5,000 AF out of the 10,000 AF <br />required for conservation of endangered fish habitat, it appears that adverse <br />impacts to recreation would be lessened. This measure and its relationship to <br />Ruedi Reservoir is not adequately addressed in the FSES. <br /> <br />We believe the most significant impact to recreation at Ruedi Reservoir <br />will occur from the sale of 46,500 AF of water with a peak demand period from <br />July through October. Our primary objection to the FSES is based on the <br />inadequate disclosure of this impact by emphasizing adverse impacts associated <br />with conservation releases which will be partially mitigated through releases <br />from Green Mountain Reservoir. This provides an all or nothing scenario which <br />does not balance the need for marketing water to meet construction/operation <br />costs of the reservoir with the economic value of recreation to the Forest <br />Service and local economy. <br /> <br />2. Fish Habitat <br /> <br />a. Ruedi Reservoir <br /> <br />Reduction in water elevation during late summer/early fall as <br />described in the FSES will adversely impact aquatic communities and would be <br />the most critical in the shallow bays along the north shore. This area is <br />important as rearing and feeding areas for trout as benthic macroinvertegrates <br />and macrophyte communities are more abundant than in the deeper areas of the <br />reservoir. In a dry year almost one-third of the littoral zone would be <br />eliminated, but in all years there would be a reduction of at least 10 percent. <br />In the long-term, abundance and size of resident fish species would be reduced. <br />No long-term monitoring plan and mitigation measures have been provided in the <br />FSES to offset impacts to fishery resources in Ruedi Reservoir. We recommend <br />that mitigation measures be identified which enhance the dewatered areas <br />through planting of appropriate vegetation to enhance fish and wildlife <br />productivity of this area. <br /> <br />b. Fryingpan River <br /> <br />The construction of Ruedi Reservoir eliminated approximately <br />seven miles of trout spawning and rearing habitat. We question whether <br />adequate compensation/mitigation has, to date, been provided by the Bureau. <br /> <br />Caring for the Land and Serving People <br /> <br />FS.6200.2817-621 <br />