Laserfiche WebLink
<br />'.( . <br /> <br />r? . <br />;.. ~ <br />... <br />-'or; <br /> <br />001556 <br /> <br />. <br /> <br />. <br /> <br />. . <br />'fraction.(Fig;4) were typical of all size classes and indicated that: <br />transport capacity was 1-2 orders of magnitude greater than supply. <br /> <br />The. next step was to evaluate how much the discharge could be reduced <br />under post-project conditions without occurrence of aggradation. It was <br />assumed that the reservoir would trap all particles in the gravel size <br />fraction. AdditionalLy, based on Andrews' conclusions and lack of signifi- <br />cant tributary sediment sources below the reservoir (within the forest <br />boundary), it was assumed that there would be an insignificant supply of <br />the gravel size fraction below the reservoir. Using the calibrated trans- <br />port relationships, the discharge required to move the remaining sediment <br />supply was, then evaluated for both sites A and B. Results indicated that <br />85 cfs would be required below Site A to move all the pre-project supply of <br />sediment . finer than gravel, while 10 cfs would be required below Site B. <br />To move all pre-project sediment supply (including gravels) would require <br />30 cfs below Site B, a value that is considered a very conservative main- <br />tenance flow requirement.:: :Channel. stability under these flow conditions <br />was not considered. to be impacted since the existing channel:. Jsupply. .- <br />limited) is stable,.probabli due to armoring by coarse particles. <br /> <br />VEGETATION ENCROACHMENT <br /> <br />The above results suggested that a relatively small discharge would <br />adequately prevent sediment deposition in the channel downstream of the <br />project. Therefore, the flows required to minimize vegetation encroachment <br />became the controlling factor in. defining required bypass flows. It is <br />generally accepted that established vegetation cannot survive long periods <br />of submergence or mean velocities higher than 5-6 fps. Under pre-project <br />bankfull conditions (190 cfs), the mean velocity was 3.7 fps; therefore, it <br />was concluded that a 16-day bypass time period (calculated from strict <br />application of the Chapter 30 procedure) provided an adequate length of <br />submergence to minimize vegetation encroachment. Under the post-project 85 <br />cfs flow necessary to prevent aggradation below Site A, the velocity is <br />only 2.5 fps. Therefore, this flow would also be required for 16 days to <br />minimize vegetation encroachment below the waterline. The 85 cfs flow <br />covers 98 percent of. the pre-proj ect bankfull wetted perimeter; conse- . <br />'.'._quently, it can be.. concluded that a post-project flow of 85 cfs below Site. <br />A is as effective as a channel maintenance flow as 190 cfs was for the <br />pre-project condition. <br /> <br />For Site B the 10 cfs flow required .to prevent aggradation leaves a <br />large portion of the channel bed exposed which could be encroached on by <br />vegetation. Under the 30 cfs flow required to transport all the pre-project <br />sediment supply, 74 percent of the pre-project wetted perimeter is covered. <br />To provide a more significant submergence factor would require about 50 <br />cfs, for which 89 percent of the pre-project wetted perimeter is covered. <br />Based on these results, a 50 cfs bypass for 16 days was considered neces- <br />sary to control a majority of the vegetation encroachment below Site B. <br />