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Last modified
7/14/2009 5:02:34 PM
Creation date
5/20/2009 10:25:48 AM
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UCREFRP
UCREFRP Catalog Number
8274
Author
Pitlick, J. and R. Cress.
Title
Longitudinal Trends in Channel Characteristics of the Colorado River and Implications for Food-Web Dynamics.
USFW Year
2000.
USFW - Doc Type
Recovery Implementation Program Project 48-C,
Copyright Material
NO
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The 1937 and 1995 aerial photographs are slightly different in scale (1:32,000 and 1:20,000, <br />respectively), and were taken when the river was flowing at different discharges (55 m3/s in 1937 <br />and 79 m3/s in 1995). The higher discharge in the more recent photographs complicates the <br />analysis slightly because, at higher flows, the channel would appear larger than it would for an <br />equivalent or lower flow. However, the error introduced by different flow levels is very small in this <br />case- probably much less than 5% (Van Steeter, 1996)- and even so, the higher discharge occurs in <br />the more recent set of photographs. This means that changes in planform area since 1937 are <br />probably underestimated by a small amount. Further details of the procedures involved in <br />developing similar GIS data bases are discussed in detail by Pitlick et al. (1999). <br />Sediment Loads <br />Annual suspended sediment loads were estimated for various time periods using streamflow and <br />sediment data from the following USGS gauging stations: Colorado River at Glenwood Springs, <br />CO (station 9072500), Colorado River near Cameo, CO (station 9095500), Colorado River near <br />CO-UT state line (station 9163500), and Colorado River near Cisco, UT (station 9180500). We <br />recognize that Glenwood Springs is well upstream of the study area, but we include this station in <br />the analysis because it illustrates how abruptly the sediment load of the Colorado River increases <br />downstream. The hydrologic data from these four gauging stations are of high quality, with record <br />lengths varying from 45 to 100 years. The streamflow record from the Glenwood Springs gauge is <br />the longest, beginning in 1898, but complicated by the fact that in 1966 the gauge was moved to a <br />point downstream of the Roaring Fork River. The records for these two gauges were combined by <br />subtracting daily discharges of the Roaring Fork River, which is also gauged, from the same-day <br />discharges of the Colorado River. The flow record at the Cameo gauge (at RKM 322) begins in <br />1934 and is continuous through the present. There is another gauge near the town of DeBeque <br />(station 9093700, at RKM 343); however, since this gauge is only 20 km away from the Cameo <br />gauge, and there are few tributaries in between, we have not used these data. The State Line gauge <br />has been in operation since 1951; this gauge was initially located at RKM 224 in Ruby Canyon, but <br />in 1979 it was moved to its present location at RKM 216. The Cisco gauge was established near <br />the Dewy Bridge (RKM 152) in 1914; the record from this gauge is continuous from 1922 through <br />the present. <br />Suspended sediment samples have been taken at each of these gauging stations, however, reliable <br />data are available only since about 1950, and the amount of data collected at individual stations <br />varies considerably. Approximately 80 suspended sediment samples were taken at the Glenwood <br />Springs gauge from 1951-1965 (Iorns et al., 1964). To our knowledge no additional samples have <br />been taken since then. About 50 suspended sediment samples were taken at the Cameo gauge <br />between 1951 and 1954 (Iorns et al., 1964), and several hundred more samples have been taken <br />since 1983 (USGS Water Supply Papers). Over 100 suspended sediment samples have been taken <br />at the State Line gauge since 1977 (USGS Water Supply Papers). Sediment sampling began at the <br />Cisco gauge in 1930 (Iorns et al., 1964), however, there is some question about the representative- <br />ness of samples taken prior to 1950, when a different type of suspended sediment sampler was in <br />use (Topping et al., 1996). Given this concern, we limited our analysis of the Cisco sediment data <br />to samples taken after 1950; since then, several hundred suspended sediment samples have been <br />taken at the Cisco gauge. <br />Suspended sediment loads were estimated for each of these gauging stations by developing a series <br />of sediment rating curves, or empirical relations between water discharge and suspended sediment <br />load. Such curves allow us to estimate daily suspended sediment loads (which are measured only <br />intermittently) from daily discharges (which are measured continuously). The rating curves were <br />10
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