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fine sediment at the mouths of backwaters in the Grand Valley. The deposited sediment <br />was not displaced during several consecutive years of low flow and backwater mouths <br />progressively filled until fish access was blocked. When vegetation encroaches into the <br />channel during periods of low flow, deposited sediments become stabilized. It then <br />becomes increasingly difficult to scour sediments from these habitats (Pitlick and Van <br />Steeter 1998). Over time, this process leads to a loss of channel complexity and a <br />concomitant loss of the preferred habitats associated with complex sites. Comparing <br />historic with recent aerial photographs of the river, Van Steeter and Pitlick (1998) <br />calculated that 25% of the historic side channel and backwater area in the Grand Valley was <br />lost from this channelization process during the preceding 50 years. Similar analyses by <br />Pitlick and Cress (2000) indicate a 31 % loss of side channel and backwater area in the 45- <br />km De Beque-to-Rifle reach. <br />After the channel is shaped by the high flows of spring, the quantity (total area) of <br />preferred mesohabitats is affected by river stage. In the 15-mile reach, weighted area of <br />mesohabitats preferred by adult Colorado pikeminnow in summer (eddies, pools and <br />backwaters) was 291/o higher at a discharge of 1,630 cfs than it was at 1,240 cfs, and 42% <br />higher than at 2,870 cfs (Osmundson et al. 1995). <br />In 1983, a year of very high spring flows, Carter et al. (1985) mapped Colorado <br />River habitats near Parachute, Colorado at flows ranging from 1,710 to 28,300 cfs <br />(measured at the USGS gage near De Beque). Their 3.2-km (2-mile) study area, judged to <br />be representative of the De Beque-to-Rifle reach, was mapped once in March and then <br />weekly from 18 June to 3 September (12 mapping dates). Wetted area was broken into 12 <br />categories, or mesohabitats. Results revealed that at flows less than 10,000 cfs total area of <br />both pools and backwaters was highest at 1,710 cfs, the lowest flow studied (Fig. 4 and 5). <br />Eddies, however, did not appear until mapping occurred at the next higher discharge, 3,840 <br />cfs. To determine which of these two flow levels provided the greatest area of preferred <br />habitat for adult Colorado pikeminnow, I multiplied the preference rating for each of the <br />three preferred habitat types (derived from Osmundson et al. 1995) by the total area of the <br />corresponding habitat type and summed the values to provide weighted area of preferred <br />habitat at each flow level (see Osmundson et al. 1995 for methods). At 1,710 cfs, the <br />23