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1 <br />1 <br /> <br /> <br />downstream areas. Water development in the Yampa River could alter the <br />natural flow/sediment transport-deposition dynamics of the entire upper Green <br />River system. <br />Several workers have evaluated relationships between discharge, sediment <br />1 <br />1 <br />1 <br /> <br /> <br /> <br />1 <br /> <br /> <br />1 <br /> <br /> <br /> <br />load, and maintenance of spawning habitat for fishes in the Yampa Canyon <br />(reviewed by Butler 1988). The results of those studies suggested that <br />sediment transport equilibria in the spawning reach can be attained under <br />reduced Elow regimens. However, attainment of such equilibria would not <br />preclude downstream changes (Butler 1988) ,and the accompanying chan;a_s in <br />sediment load and channel morphometry would permanently modify existing fish <br />habitat. Reductions in sediment load resulting from water withdrawal may cause <br />downstream erosion of shoreline areas, and destabilization of riparian <br />communities. For example, sediment depletion due to closure of Flaming Gorge <br />Dam has reduced 'sank width of the Green River between Flaming Gorge and Ouray, <br />Utah, by 10%, and this stretch has not yet attained its new dynamic <br />equilibrium (Andrews 198b). <br />Butler (19$8) evaluated different scenarios Following completion of <br />water development projects in the Yampa River. pie Found that sediment load in <br />sipper Green River system would be robbed of about 626,800 tons of sediment on <br />an annual basis (a 24°o sediment reduction), following completion of Juniper <br />Project. Thus, the lower Yampa River (downstream from Little Snake River) <br />would become an aggrading system due to loss of scouring spring flows. <br />Hydrology of Little Snake River also warrants study because 77% of the <br />sediment delivered to the lower Yampa River is derived from the Little Snake <br />River (O'Brien 1984). Further losses are implicated as potential effects of <br />38 <br />ii <br />