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RESULTS <br />Based on the timing and location of each sampling effort data collection was designed to <br />address one project objective at a time. In the context of the present study, the purpose behind <br />spring electrofishing in the vicinity of the San Rafael confluence and azeas upstream was to <br />collect adult razorback suckers. However, since there is a known population of Colorado <br />pikeminnow in this area (McAda et al. 1994), many pikeminnow were collected as result of this <br />project's efforts. The collections of pikeminnow from this portion of the river are reported <br />herein, but they have no bearing on the Millazd Canyon spawning investigations (Objective 5). <br />Similazly, larval pikeminnow were collected in and near the mouth of the San Rafael, in 1995. <br />These fish were likely produced upstream at the know spawning azea in Gray Canyon and <br />although important collections in their own regazd, are not relevant to this project's objective 6. <br />Congregations of adults at suspected spawning areas -razorback suckers <br />Electrofishing in 1994 and 1995 did not locate a concentration of adult razorback suckers <br />in the lower Green River. One adult was collected in related endeavors 69 km below the mouth <br />of the San Rafael River on 16 May 1995 (Table 1). In efforts prior to and since this study, <br />incidental collections of razorback sucker have been reported from the lower Green River since <br />1980 (Table 1). Most notable were two recent collections of adult razorback from the mouth of <br />the San Rafael River; one on 14 May 1996 collected during ISMP monitoring (McAda et al. <br />1997) and the other on 7 May 1997 collected as part of basin-wide razorback sucker monitoring <br />(Muth and Wick 1997). <br />In 1994, a total of 20.4 h of electrofishing effort was accumulated between the town of <br />Green River and the San Rafael River confluence azea (37 RK). Thirty-five juvenile to adult <br />Colorado pikeminnow were captured ranging from 164 mm to 567 mm TL. In 1995, 26.9 h of <br />effort again yielded no razorback sucker but 36 sub-adult/adult Colorado pikeminnow (206-759 <br />mm TL) were captured between RK 193.2 (RM 120.0) and RK 138.5 (RM 86.0). An additional <br />3.28 hours of electrofishing conducted throughout a 16 km stretch immediately upstream of <br />Green River, Utah, on 9 June 1995 amassed 16 subadult/adult Colorado pikeminnow ranging <br />from 371 mm to 595 mm TL. <br />Flannehnouth suckers (Catostomus latipinnis) were the most abundant species collected <br />via electrofishing both yeazs. Both flannelmouth sucker and bluehead sucker (Catostomus <br />discobolus) showed signs of sexual readiness. Other species collected via electrofishing <br />included: channel catfish (Ictalurus punctatus), common carp (Cyprinus carpio), and walleye <br />(Stizostedion vitreum) (Figure 3 and 4). <br />Congregations of adults at suspected spawning areas - Colorado pikeminnow <br />Sampling for Colorado pikeminnow adults in 1994 was limited to trammel netting due to <br />low flows and an inability to effectively sample the suspected spawning site with electrofishing <br />equipment. A total of 46.3 net hours were accumulated at the mouth of Millazd Canyon in 1994 <br />and no adult Colorado pikeminnow were captured. Channel catfish dominated the net catch in <br />1994 followed by flannelmouth sucker and common carp. <br />4 <br />