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<br />indicate that the actual flow forces are more <br />directly controlled by the magnitude of hydraulic <br />conditions, such as channel slope and flow depth, <br />and probably not the absolute discharge. <br />The absolute magnitude of peak discharge is <br />not used directly in the derivation ofthe relation in <br />this report; however, discharge data are presented <br />for comparative purposes (table I). Discharge data <br />were' obtained by direct current-meter measure- <br />ment (Rantz and others, 1982), at a nearby USGS <br />streamflow-gaging station that had a well defined <br />stage-discharge relation, or by indirect peak-flow <br />measurement (Dalrymple and Benson, 1967). <br /> <br />Stream Power and Shear Stress <br /> <br />A fundamental assumption of this <br />investigation is that a critical stream power exists <br />for specific vegetation conditions, and that <br />vegetation will begin to bend when this critical <br />stream power value is exceeded. Stream power is a <br />measure of energy transfer in an open channel and, <br />according to Simons and Richardson (1966), <br />stream power is defined as: <br /> <br />SP = 62.4RS V, <br />w <br /> <br />where <br /> <br />SP = stream power, in foot-pounds per <br />second per foot squared, <br />62.4 = specific weight of water, in pounds per <br />cubic foot, <br />R = hydraulic radius, in feet, <br />Sw = slope of the water-surface profile, in <br />feet per foot, and <br />V = average velocity, in feet per second. <br /> <br />Boundary shear stress (shear stress) is the force <br />exerted on the bed by the moving water and is the <br />hydraulic component most related to substrate or <br />bedload movement (Vanoni, 1975; Carson and <br />Griffiths, 1985). Shear stress is used instead of <br />stream power to describe the potential for a flow to <br />degrade the channel substrate. Consequently, shear <br />stress is considered the predominant mechanism <br />that potentially can expose and weaken root <br />systems and remove vegetation. Shear stress, to' is <br /> <br />the force per unit area exerted on the bed by the <br />moving water and is defined (Davidian and Cahal, <br />1963) as: <br /> <br />to = 62.4RSo' <br /> <br />(2) <br /> <br />where <br /> <br />62.4 = specific weight of water, in pounds per <br />cubic foot; <br />R = hydraulic radius, in feet; and <br />So = bed slope, in feet per foot. <br /> <br />, <br /> <br />Vegetation Data <br /> <br />(I) <br /> <br />Adequately describing all the physical <br />components that collectively characterize <br />vegetation conditions in streams in Arizona is <br />complex and difficult. In the study by Phillips and <br />Hjalmarson (1994), the average height of <br />vegetation measured before flow was the only <br />component used to characterize vegetation <br />conditions. Their simplified approach required <br />various assumptions that ignored several important <br />factors such as the variable flexural strength of <br />different vegetation species. <br /> <br />In the course of this investigation, it was <br />determined that additional physical components <br />could more effectively model the effects of <br />flow-induced changes to vegetation. The physical <br />components include four vegetation attributes------{I) <br />the flexural strength of specific types and sizes of <br />vegetation, (2) the percent of flow blocked by <br />vegetation, (3) the distribution of the vegetation, <br />and (4) the depth of flow relative to the vegetation <br />height (table 2). <br /> <br />Vegetation-Susceptibility Index <br /> <br />The vegetation attributes that were determined <br />for each site (table 2) are incorporated into a single <br />parameter called the vegetation-susceptibility <br />index. The vegetation-susceptibility index is <br />defined by <br /> <br />Kv = Vj/exCblockingCdistCdepth' (3) <br /> <br />6 Method to Estimate Effects ot Flow-Induced Vegetation Changes on Channel Conveyancea of Streams in Central Arizona <br />