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<br />quite substantial and can even exceed the estimated <br />value of nb' Main-channel vegetation for this site, <br />however, can be removed by flow magnitudes <br />slightly larger than the 2-year flow (Garrett and <br />Gellenbeck, 1991, p. 578, and table I), which <br />makes the selection of n4 for this site difficult. Use <br />of the relation presented in this report, however, <br />can dramatically decrease the uncertainty <br />associated with the selection of n4 for sites where <br />vegetation conditions may be altered by flow. <br /> <br />Table 9. Estimated preflow and postflow roughness <br />coefficients and computed changes in water-surface <br />elevations <br /> <br />Estimated <br />preflow <br />Site roughness <br />number coefficient <br /> <br />10 <br /> <br />Ib <br />Ie <br />20 <br /> <br />2b <br /> <br />3 <br /> <br />4 <br /> <br />5a <br /> <br />5b <br />6 <br />7 <br />8 <br />9a <br />9b <br />ge <br />to <br />II <br /> <br />t2 <br />t3 <br />t4 <br /> <br />15 <br />16 <br />17 <br />18 <br />190 <br />19b <br /> <br />0.030 <br />.035 <br />.045 <br />.048 <br />.038 <br />.030 <br />.00t <br />.041 <br />.038 <br />.034 <br />.040 <br />.050 <br />.040 <br />.050 <br />.035 <br />.075 <br />.034 <br />.080 <br />.040 <br />.200 <br />.040 <br />.050 <br />.046 <br />.045 <br />.035 <br />.048 <br />.035 <br />.045 <br /> <br />Estimated <br />poslflow <br />roughness <br />coefficient <br /> <br />'0.030 <br />.032 <br />.037 <br />1048 <br />1035 <br />'.026 <br />'.041 <br />.026 <br />M~- <br />.029 <br />.033 <br />.035 <br />.025 <br />.025 <br />.032 <br />.060 <br />.029 <br />.080 <br />.035 <br />.200 <br />.030 <br />.050 <br />.041 <br />.040 <br />.033 <br />.043 <br />.025 <br />.025 <br /> <br />IVerified n values (Phillips and Ingersoll, 1998). <br /> <br />Change in <br />water-surface <br />elevation, <br />In feel <br /> <br />0.00 <br />.34 <br />2.17 <br /> <br />o <br /> <br />.t2 <br />.55 <br /> <br />o <br />I.7t <br />.20 <br />1.32 <br />.45 <br />1.00 <br />2.5t <br />2.60 <br />.22 <br />1.73 <br />1.22 <br />o <br />.43 <br />o <br />2.63 <br />o <br />.36 <br />.43 <br />.04 <br />1.23 <br />1.13 <br />1.18 <br /> <br />Example case.--Consider a rectangular <br />channel where computation of the flood elevation <br />of the 100-year flow is needed. The channel reach <br />is uniform in shape and bed-material composition. <br />The bed material is dominated by cobbles with a <br />d50 of 0.30 ft. Brush and willow are present <br />throughout the study reach and distributed <br />randomly in the channel. The average height of the <br />brush is 3.0 ft, and the average height of the willow <br />is lOft. The percentage of cross-section area of <br />flow that is blocked by each vegetation type is <br />about 30 percent (table 10). These component <br />values are in the range of data used to develop the <br />relation in this report. <br /> <br />Table 10. Channel and vegetation components for the <br />example case <br /> <br />Vege- <br />tation <br />type <br /> <br />Brush <br />Willow <br /> <br />Median <br />diam- <br />eter <br />dso, <br />in feet <br /> <br />Aver- <br />age <br />vege- <br />tation <br />height, <br />in feet <br /> <br />Vege- <br />tation- <br />flexi- <br />bility <br />factor, <br />In toot <br />pounds <br /> <br />8.85 <br />63.2 <br /> <br />Amount <br />otllow <br />blocked <br />by vege- <br />tation, <br />in percent <br /> <br />Vege- <br />tation <br />distri- <br />bution <br /> <br />3 <br />to <br /> <br />30 <br />30 <br /> <br />Random <br />Random <br /> <br />0.3 <br />.3 <br /> <br />Use of the relation (fig. 9) presented in this <br />report to estimate the effect of flow on vegetation <br />conditions requires quantification of the stream <br />power as well as the vegetation-susceptibility <br />index. Information obtained from a detailed <br />description of the channel and vegetation <br />conditions in the reach as well as a survey of the <br />study reach can be used to compute the <br />vegetation-susceptibility index. For the hydraulic <br />computations, the standard-step method <br />(Shearman, 1990) is used. This method requires <br />solution of the energy equation, continuity <br />equation, and Manning's equation. Components <br />required to compute stream power are obtained <br />from the standard-step computational results. <br /> <br />A stepwise procedure is suggested for using <br />the information presented in this report. For <br />the purposes of this example case, discharges that <br />correspond to the 2-, 10-, 50-, and 100-year <br />flows will be used. The magnitude of these <br />discharges were determined arbitrarily (table II). <br /> <br />, <br /> <br />, <br /> <br />22 Method to Estimate Effects of Flow-Induced Vegetation Changes on Channel Conveyances ot Streams in Central Arizona <br /> <br />--'-'- - <br />