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<br />SleD 7a <br /> <br />The power associated with the 2-year flow is <br />not substantial enough to significantly affect <br />either the brush or the willow (fig. I I). Go back <br />to STEP 1 using the 10-year flow (step Ib), <br /> <br />SleD 7b <br /> <br />Plotting position for the brush now indicates <br />that it probably will be laid over as a result <br />of the IO-year flow. The willow, however, <br />plots just below the vegetation-susceptibility <br />threshold, and the effect of flow on it <br />is questionable (fig. I I). Consequently, com- <br />putations are made again but now only the <br />effect of flow on the willow is evaluated. Go <br />, back to STEP 1 using the 50-year flow (step <br />Ic). <br /> <br />SleD 7c <br /> <br />As indicated by the plotted position of willow, <br />there is a high probability that it will be laid <br />over as a consequence of the 50-year flow <br />(fig. II). At this discharge, the flow-retarding <br />effects associated with the brush and willow <br />will diminish greatly, and depending on the <br />amount of proneness, the retarding effects <br />associated with the vegetation may become <br />negligible. No further steps are required. <br /> <br />Because it was determined that a 50-year flow <br />is adequate to layover vegetation growing in this <br />channel, it is assumed that the vegetation will be <br />laid over on the rising limb of the hydrograph for <br />the lOO-year flow. The resultant effect would be a <br />dynamic decrease of flow resistance and increase <br />in channel conveyance compared to conveyance <br />computations made on the basis of preflow- <br />vegetation conditions. <br /> <br />For determination of the water-surface <br />elevations of the 100-year flow in this example <br />case, selection of Manning's n should only account <br />for the flow-retarding effects associated with the <br />bed material and any residual effects of laid-over <br />vegetation. Because the residual effects were <br />considered minor, for this example, a Manning's n <br />of 0.035 would be recommended for design- <br />discharge computations for the 100-year flow. The <br /> <br />result is a substantial reduction in n compared to <br />estimates made on the basis of preflow-vegetation <br />conditions using current guidelines and techniques. <br />By comparing computed water-surface elevations <br />for n values equal to 0.035 and 0.070, the potential <br />error in water-surface elevation computations <br />resulting from incorrect assessment of peak-flow <br />vegetation conditions for this example case for the <br />100-year flow is 3.58 ft. As discussed previously in <br />this report, a sufficient amount of information was <br />not available in this study to develop a substantive <br />relation for the removal of vegetation and, <br />therefore, the removal of the vegetation for the <br />example case was not considered. <br /> <br />ASSUMPTIONS AND LIMITATIONS <br /> <br />Although not documented in this study, the <br />possibiilty of laid-over vegetation springing back <br />to an upright position when the power and forces <br />of flow subside is a concern. An assumption <br />required for analysis of data gathered for this <br />report demands that the flow-affected vegetation <br />remain in a position following flow similar to that <br />during peak flow. For example, if vegetation was <br />laid over during peak flow, it is assumed to remain <br />in this position when flow subsides, Additionally, <br />caution should be taken when transferring the <br />results from this study to other sites especially if <br />the channel and vegetation conditions of the other <br />sites are substantially different from the channel <br />and vegetation conditions used to derive the <br />relation in this report. <br /> <br />For the simple semiempirical relation <br />presented in this report (fig. 9), stream power was <br />used to describe the flow-induced changes to <br />vegetation; however, some important inherent <br />uncertainties exist. For example, peak-flow <br />velocity was required for use in the stream-power <br />equation, and barring a direct current-meter <br />measurement, peak-flow velocities were primarily <br />obtained by use of Manning's equation. Estimates <br />of peak-flow n values made after the flow subsided <br />were based on the assumption that any noticeable <br />change in roughness elements (vegetation for <br />example) occurred before peak flow, and postflow- <br />vegetation conditions were assumed identical to <br />those at peak flow. This assumption may be <br /> <br />26 Method to Estimate Effects 01 Flow-Induced Vegetation Changes on Channel Conveyances 01 Streams In Central Arizona <br />