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capturing additional adult Colorado squawfish for implantation of <br />radio tags prior to the 1993 spawning season. July 1993 sampling <br />will cover the river reach between Farmington, New Mexico and <br />Hogback Diversion, RM 179.0 to 158.6 (a stretch of river sampled <br />only once during 1991-1992 adult monitoring trips), and also from <br />Mexican Hat, Utah to Clay Hills, Utah, RM 53.0 to 2.0, a river <br />reach previously unsampled for adult fish during our study. <br />October 1993 sampling will be conducted from Hogback Diversion to <br />Mexican Hat, Utah. <br />Early Lifestage - Low-velocity habitats were sampled between the <br />Hogback Diversion, New Mexico, and Clay Hills Crossing, Utah, <br />during summer and fall 1991 and spring, summer, and fall 1992 to <br />determine the early life stage fish community in the San Juan <br />River. In addition, two larval drift stations were operated in <br />summer 1991 and three in summer 1992 to determine larval drift <br />patterns. Fish communities in tributaries to the San Juan River, <br />Utah, were also surveyed in fall 1992. <br />Four young-of-the-year sampling trips were made in the San Juan <br />River in 1991 and five in 1992. Low-velocity habitats targeting <br />backwaters were sampled using seines. A total of 26,099 native and <br />96,802 non-native fish specimens were collected in 1991 and 21,911 <br />native and 75,759 non-native specimens were collected in 1992. <br />Non-native red shiner and fathead minnow were the most abundant <br />species found in low-velocity habitats during both years. Native <br />species commonly found were flannelmouth sucker, bluehead sucker, <br />and speckled dace. Five specimens of roundtail chub were collected <br />in 1991 and eighteen specimens were collected in 1992. No other <br />rare fish (Colorado squawfish or razorback sucker) were collected <br />in low-velocity habitats in 1991 or 1992. <br />Fish community structure differed temporally and spatially by catch <br />rate and species composition in 1991 and 1992. Non-native red <br />shiner and fathead minnow were the most abundant species in late <br />summer and fall during both years. Native flannelmouth sucker, <br />bluehead sucker, and speckled dace were most abundant in mid-summer <br />during both years. In addition, native species were most commonly <br />found upstream of Chinle Creek. <br />A total of 716 native and 1,723 non-native fish specimens were <br />collected at the Four Corners and Mexican Hat larval drift sites in <br />1991 and 638 native and 432 non-native specimens were collected in <br />1992. Non-native red shiner was the most abundant species in <br />larval drift collections at the Four Corners larval drift site in <br />1991 and native flannelmouth sucker was most abundant in 1992. <br />Non-native channel catfish was the most abundant species at the <br />Mexican Hat larval drift site in both 1991 and 1992. Few fish <br />(N=50), mostly speckled dace and flannelmouth sucker, were <br />collected at the Mixer larval drift site in 1992. No rare fish <br />(Colorado squawfish, roundtail chub, or razorback sucker) were <br />found in larval drift collections in 1991 or 1992. <br />9 <br />