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<br />. 1611 <br /> <br />WATERSHED MANAGEMENT <br /> <br />ESTIMATING EROSION <br /> <br />169 <br /> <br />where S = sediment yield (t/mi2/yr) <br />Q = annual runoff (in.l <br />A= watershed area (mil). <br /> <br />Because of widely varying .local factors the au:thors may not have intend- <br />ed for this equation to be used for 'a specific location. However,_ the <br />equation does express a rational relationship for sediment yield that I <br />think is realistic for conditions encountered in the. southwest. <br />To estim~te the average annual runoff for a watershed, I used the <br />relationship developed 'by Renard (10) for the Walnut Gulch Experimental <br />Watershed: . <br /> <br />southwestern United States, and it uses a deterministic sediment trans- <br />port relationship (8). Sediment yield is then computed by simulatin9 <br />individual hydrographs and computing the ~ediment transport for the sim- <br />ulated hydraulic conditions. Annual yield is the sum of the yield of <br />individual runoff events. Thus sediment yield is a function of runoff, <br />hydrograph peale. Manning's roughness. slope. hydraulic radius and the <br />size distribution of the sediment in the streambed. The method was <br />applied and calibrated with sample data for several of the larger water- <br />sheds on Walnut Gulch in. southeastern Arizona. With the roodel. a sim- <br />pI Hied relationshi_p was developed which relates the annual sediment <br />yield to watershed drainage area in the form <br /> <br />Q = 0.4501 A-0.1449 <br /> <br />(2) <br /> <br />Y = 0.001846 Aa-.1187 <br /> <br />(5) <br /> <br />where the terms are as defined above. SUbstituting Eq. 2 into Eq. 1 <br />gives <br /> <br />where <br /> <br />Y =-average annual sediment yi~ld in ac-ft/ac/yr <br />Aa = drainage area in acres <br /> <br />S = 887 A-.0667 (1.43 - 0.26 log A) <br /> <br />(3) <br /> <br />Thus. because of transmission losses (abstractions from runoff by <br />the alluvial channels) in the watershed. water yield decreases with in- <br />creasi n9 drai nage area and this same trend is reflected ,in the sediment <br />yield reJationship. Conversions are required to produce the units com- <br />parable to the other methods. <br /> <br />To convert the annual sediment yield to ac-ft/mi2/yr, I assumed the <br />sediment deposited weighed 90 lbs/ft3, <br /> <br />Fl axman Method: <br /> <br />where <br /> <br />log tY + 100) = 6.21301 - 2.19113 log (XI + 100) <br /> <br />+ 0.06034 log (X2 + 100) - 0.01644 log (X3 + 100} <br /> <br />+ 0.04250 log (X4 + 100) (4) <br /> <br /> <br />Y = antilog of [log (Y + 100)) - 100. <br />Y = average annual sediri1ent yield (ac-ft/mi2/yr) <br />Xl = ratio of average annual precipitatio~ (in) to ave~age an- <br />l1Ja 1 temperature <br />X2 . average watershed slope (~) <br /> <br />X3 x soil particles greater than 1.0 mm (~) <br /> <br />X4 = soil aggregation Index <br /> <br />WATERSHEOS CONSIDERED <br /> <br />The Walnut Gulch Experimental Watershed is a 58 mil drainage in <br />southeastern Arizona operated by -the Science and Education Admi nistra- <br />tion of USDA- to evaluate the effect of land use and conservation prac,- <br />tices on water and sediment yield of arid and semiarid r.angelands. The <br />watershed in the Southeastern Arizona Basin and Range land resource area <br />(1.) is typical of the intermountai n alluvial areas of the southwest. <br />Elevations in the watershed range from 4200 to 6000 feet above nean sea <br />level. ,Cover in the watershed is a mixture of brush and grasses with <br />vegetation basal areas less than 10%. Soi Is are typically calcareous <br />with large amounts of gravel and larger material. A gravel pavement <br />develOps with erosion on the land surface. and in some areas it repre- <br />sents nearly a 100% cover. <br />Precipitation in the area. 'fCtlich averages about 14 in/yr. is domi- <br />nated by sunmer rainfall (about two-thirds of the annual) consisting of <br />high-i ntensity. short-duration thunderstorms of limited areal extent. <br />'Wi nter storms are generally of greater areal extent and of low intensity <br />so that runoff is rot corrmon. The sumner ai r-mass thunderstorms result <br />in high peak flows that generally have high sediment loads. <br />Withi n the watershed, a number of small earthen. dams (stock pondS) <br />provide water .for the grazing animals. Periodic topographic. surveys of <br />the pond storage area have been made to determine sediment accUlllIla- <br />tions. The. nine ponds for which such infonnation was available are <br />shown in Table 2 along with data on the characteristics of the watershed <br />area. The ponds generally have enough storage space that discharge <br />through the emergency spillway is infrequent. .Pond 223 spilled more of- <br />ten than the others. <br /> <br />Flaxman (4) developed a regression equation for reservoir design <br />on rangeland watersheds in the western U.S. relatinq sediment yield to <br />four parameters. His expression is <br /> <br />The parameters are eKpressions of cHmate and also reflect vegetative <br />growth (Xl ), topography (X2) and soil properties (X3 and X4). The equa- <br />tion explained about 911 of the variance in average anra1 sediment <br />yield from 27 watersheds ranging in size from 12 to 54 mi in 10 west- <br />ern states. <br /> <br />Renard Method: <br /> <br />A method for estimating sediment yield was developed by Renard <br />(12) and Renard and Laursen (11). This method uses a stochastic runoff <br />model (3), which generates hydrographs for semiarid watersheds in the <br /> <br />2~lO <br /> <br />. <br />