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<br />~~,~~.,. <br />tiJ ..)_v....' <br />Affected Envifonment & Consequences <br /> <br />3-25 <br /> <br />quality would primarily occur downstream from the North Fork. This condition is <br />unchanged from that described in the PElS, and a more detailed discussion is presented in <br />that report. <br /> <br />3.6.2.3 Uncompahgre River <br /> <br />Development of the proposed Project would result in widening of the active channel in <br />response to increased magnitude and duration of in-channel flows. Channel widening <br />would increase the amount of sediment in the river, which could subsequently reduce <br />water quality, The Sponsors evaluated this issue using a sediment continuity model, <br />described in Section 3.4.3. Based on an ultimate average width/depth (W /0) ratio of 35 <br />with a minimum dimensionless shear stress of 0.03 (Shields value 'tc = 0.03), channel <br />widening and estimated total volume of material eroded are shown in Table 3-15. <br /> <br />Table 3.15. Total Material Eroded Over Life of Project <br /> <br />Average Volume Eroded, Total Material Eroded, <br />Alternative Widening, First Year, over 40 years, <br />feet cubic yards cubic yards <br />E-I 30 76,000 278,000 <br />E-2 26 64,200 224,000 <br />E-3 23 45,800 176,000 <br />Source: Mussetter Engineering, Inc, Uncompahgre River Channel Stability Study, Final Report, <br />February 1995; modified December, 1997, <br /> <br />The estimates shown in Table 3-15 account for the relative width between the flood plain <br />limits (average height 4,1 feet) and the height of the bars along the active channel <br />(average height of approximately 2 feet). Based on the proposed bank protection plan <br />(see Section 2.4.4) it was assumed that none of the terraced surfaces would be affected by <br />the channel widening. The estimates also exclude those areas where the channel is <br />currently protected on both banks and thus cannot widen. <br /> <br />The impact of introducing this volume of material into the Uncompahgre River, and <br />ultimately the Gunnison River, depends primarily on the rate at which it is introduced. <br />After the Uncompahgre River has adjusted to the new flow regime, the total sediment <br />load delivered to the Gunnison River would not exceed the current sediment load. In <br />fact, the sediment load after channel adjustment would most likely be less because the <br />introduced water from the proposed Project would be sediment free and the coarse <br />grained Uncompahgre River would achieve a threshold condition (Mussetter Engineering, <br />1995). <br /> <br />MEI (1995b) converted the eroded volumes to sediment loads. For the 850-cfs <br />Alternative, the maximum (first-year) increase in sediment load would be 127 parts per <br />million (ppm) to 190 ppm. Of this, approximately 8 ppm to 13 pprn would be silt and <br />clays, with the balance being larger particles. For comparison, the total existing summer <br /> <br />AS Lateral Hydropower Project <br /> <br />July 2000 <br /> <br /> <br />. <br />