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TABLE 1 <br />Mean Annual Streamflow and Computed Sediment Yield <br />(Andrews, 1978) <br />Station/Site Area Mean Mean Annual Sediment Load <br />(sq mi) Annual (tons/year) <br />Discharge Suspended Bedload Total <br />(cfs) <br />Little Snake River 3,730 575 1,300,000 70,000 1,400,000 <br />River near Lily, CO <br />Yampa River near 3,410 1,550 <br />Maybell, CO <br />420,000 120,000 540,000 <br />Yampa River at -- 2,125 <br />Deerlodge Park, CO <br />-- -- 2,000,000 <br />The above table shows that the Little Snake and Yampa River sub-basins are <br />roughly equal in drainage area, but the distribution of sediment and water <br />yield is very different. The Little Snake River sub-basin supplies 270 of the <br />annual runoff to Deerlodge Park and 707. of the sediment load. In contrast, the <br />Yampa River sub-basin supplies 73% of the annual runoff at Deerlodge Park but <br />only 27% of the sediment load. <br />Andrews (1980) selected 15 gaging stations <br />computed the effective discharge at each s <br />as the increment of discharge that transpo <br />annual sediment load over a period of year <br />were used; again developed using measured <br />bedload transport. <br />in the Yampa River basin and <br />ite. Effective discharge is defined <br />its the largest fraction of the <br />s. Total sediment transport curves <br />suspended sediment data and estimated <br />The effective discharges were equaled or exceeded on the average of between 1.5 <br />days/year and 11 days/year (0.4% to 3.0%, respectively). Recurrence intervals <br />of the effective discharges ranged from 1.18 to 3.26 years. Variation in the <br />duration of effective discharge between stations is explained, in part (about <br />50%), by the skewness of the distribution of daily streamflows. As drainage <br />area increased, the relative abundance of high flows or skew of the <br />distribution of streamflow increases. As a result, the effective discharge <br />becomes less frequent as drainage area decreases.