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Last modified
7/14/2009 5:02:29 PM
Creation date
5/22/2009 6:45:31 PM
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UCREFRP
UCREFRP Catalog Number
7087
Author
Elliot, J. G., J. E. Kircher and P. V. Guerard.
Title
Sediment Transport in the Lower Yampa River, Northwestern Colorado.
USFW Year
1984.
USFW - Doc Type
Denver, CO.
Copyright Material
NO
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Deerlodge Park was 16,500 ft~/s and the 1983 instantaneous peak discharge was <br />23,400 ft3/s. In 1983, the flood plain at Deerlodge Park was inundated by <br />floodwater for several days during the peak runoff. Recurrence intervals of <br />annual maximum daily mean discharges were estimated for the 1982 and 1983 <br />streamflows at Deerlodge Park using the 43 years of streamflow record, and a <br />Log Pearson Type III analysis (U.S. Water Resources Council, 1981). The 1982 <br />peak daily mean discharge had a recurrence interval of about 3 years, and the <br />1983 peak daily mean discharge had a recurrence interval of about 20 to 25 <br />years. The combined long-term mean annual streamflow of the Yampa River near <br />Maybell and the Little Snake River near Lily is 1.5 million acre-ft/yr (U. S. <br />Geological Survey, 1982). In 1982, the combined annual streamflow of the <br />Yampa River near Maybell and the Little Snake River near Lily was 1.9 million <br />acre-ft, and in 1983 it was 2.3 million acre-ft. <br />A flow-duration curve is a cumulative frequency curve that shows the <br />percentages of time specified discharges are equaled or exceeded during a <br />given period. It combines into one curve the flow characteristics of a stream <br />throughout a range of discharge, without regard to the sequence of occurrence <br />(Searcy, 1959). Historical streamflows at station 09251000 Yampa River near <br />Maybell and station D9260000 Little Snake River- near Lily were examined to <br />determine an appropriate period of record for estimating the long-term <br />flow-duration curve at station 09260050 Yampa River at Deerlodge Park. <br />Flow-duration curves calculated from 10-year increments were compared for each <br />site. In the decade of the 1920's, days when discharge was very low occurred <br />much less frequently than in other decades. By contrast, in the decade of the <br />I930's, days when discharge was very low occurred much more frequently than in <br />other decades. streamflow of the decades since 1940 has been relatively <br />uniform and has had a greater effect on the present channel morphology than <br />has streamflow from earlier in the century; therefore, only discharge data <br />recorded since 1940 was used in streamflow analysis. Along-term (1941-1983) <br />flow-duration curve for Deerlodge Park was computed from the daily sums of <br />daily mean discharges recorded at the Maybell and Lily gaging stations. This <br />curve is presented in figure 6. <br />SEDIMENT TRANSPORT AT DEERLODGE PARK <br />The relation between water discharge and sediment discharge at Deerlodge <br />Park was used to quantify the amount of sediment entering the Yampa River <br />Canyon. The total sediment load of a river can be divided into two compo- <br />nents: (1) Suspended-sediment, which is the relatively fine material (clay, <br />silt, and some sand-size material) transported in suspension; and (2) bedload <br />which is coarser material (sand, gravel, and cobble sizes) that moves by <br />rolling or bouncing along the bed. Measurements of both suspended sediment <br />discharge and bedload discharge were made at the Deerlodge Park study reach <br />during the spring and summer of 19$2 and 1983. Supplemental streamflow and <br />sediment data were collected in 1983 at two additional sites (fig. 3). <br />Suspended-sediment measurements were made at station 09260000 Little Snake <br />River near Lily to provide additional information an sediment entering the <br />Yampa River. Also, discharge measurements were made and sediment samples were <br />11 <br />
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