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<br />Mlt~~ <br /> <br />Affected Environment & Consequences <br /> <br />3-16 <br /> <br />. Widening, where the river widens so that fluid shear stress acting on the bed drops to <br />or below the critical level. <br /> <br />The point at which flow can initiate bed material movement is called incipient motion, <br />and was defined in two ways for this study. The first defines the critical particle size as <br />the size at which any material is mobilized. This value is based upon a Shields value ('tc) <br />of 0.03. A second definition assumed a Shields value of 0.045, which is typically used to <br />define the level at which measurable bed-material movement begins. Table 3-11 <br />indicates the percentage of time these values would be exceeded for the No Action and <br />Development alternatives. <br /> <br />Table 3.11. Percent of Time Incipient Motion Occurs <br /> <br />Alternative <br />E-l E-2 <br />48.2% 47.8% <br />0,6% 0.6% <br /> <br />Shields Value <br />0.03 <br />0.045 <br /> <br />Critical flow <br />614 <br />2028 <br /> <br />A <br />7.3% <br />0,0% <br /> <br />E.3 <br />47.3% <br />0.4% <br /> <br />The values shown in Table 3-11 indicate that critical flows are exceeded under all <br />alternatives, and stream adjustment is likely to occur. The Sponsors then determined how <br />this adjustment would occur. For gravel bed rivers with easily erodible banks such as the <br />Uncompahgre, channel adjustment is more likely to result in widening than in bed <br />lowering (degradation). However, comments expressed the concern that the introduction <br />of Project-related flows would result in massive channel degradation. Therefore, the <br />Sponsors evaluated the ability of the river to degrade if there was no bank erosion and no <br />channel widening (j.e, all stream energy was directed towards degradation). <br /> <br />This evaluation was done using a sediment continuity model.3 This model uses the <br />Parker bedload function, which is the current state of the art model for gravel bed rivers, <br />to assess bedload movement (Sigma, 1995b), Bed-level changes were calculated on a reach <br />by-reach basis, with the model moving sediment through the river based upon each <br />reach's transport capacity. The location of the reaches is shown in Figures 3-2 and 3-3. <br /> <br />The continuity model indicated that the potential for bed degradation is minimal even <br />assuming all energy is directed at the stream bottom instead of the banks. In two of the <br />14 reaches (representing 2.5 of 27 total miles), the bed could degrade slightly. These <br />reaches are immediately downstream of the Selig and Garnet Diversion Dams. Initial <br />degradation would be 2.5 to 3 inches per year (1.5 to 2 inches per year for the 750-cfs <br />alternative). Because of the nature of the bed material, an armor layer can be expected to <br />develop very quickly, which would lirnit such degradation (ME! 1995b). In reality, the <br />effect will be less or not occur at all, since the river will tend to widen rather than degrade <br />(see below). <br /> <br />3 <br /> <br />Development of the continuity model was coordinated with representatives from the Corps of <br />Engineers. <br /> <br />AB Lateral Hydropower Project <br /> <br />July 2000 <br /> <br />" <br /> <br />,; i <br /> <br />. ",. <br /> <br />1h .0 .;;,l ~,~ <br /> <br />,1 <br />.,~_.3i0ii <br />