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In 1995, 23.1 net hours produced six sub-adult Colorado pikeminnow ranging in size <br />from 230-250 mm TL. Flannelmouth sucker dominated the net catch in 1995, however, <br />nonnative channel catfish and common carp were also abundant (Figure 5). Electrofishing, in <br />1995, for pikeminnow between RK 56.4 and 40.7 (RM 35.0-25.3) resulted in the collection of 16 <br />juveniles/subadults (100-321 mm TL); no adults. Common carp dominated that electrofishing <br />catch and again flannehnouth sucker and channel catfish were abundant. <br />Larval sampling: razorback sucker <br />The first project objective was to review the Larval Fish Laboratory's examination of past <br />collections ofsmall-bodied fish from the lower Green River to determine the presence of any <br />previously unidentified larval or young razorback sucker. This activity was identified in the <br />FY93 recovery program work plan. No larval oryoung-of--year (YOY) razorback suckers were <br />found as reported in subsequent LFL sample processing reports to the Recovery Program (R. <br />Muth, pers. comm.). <br />A total of 333.2 and 458.71arval light trap hours were accumulated in 1994 and 1995, <br />respectively. In 1994, a total of 441arval razorback suckers were collected between the mouth of <br />the San Rafael River (RK 155.0; RM 97.0) and just below Red Wash (RK 152.8; RM 94.9) with <br />the majority of those (n=36, 82.8%) collected on O1 June (Table 2). Collection dates ranged <br />from 17 May to 16 June 1994 and total lengths ranged from 10 mm to 14.2 mm (Figure 6). Only <br />four larval razorback suckers were collected in the lower Green River in 1995, two near the San <br />Rafael confluence (RK 155; RM 97.0), and two near Anderson Bottom (RK 53.6; RM 33.5). <br />Collection dates of these four individuals ranged from 31 May to 30 June, with total lengths <br />ranging from 11.3-12.8 mm (see Table 2 and Figure 6). Four sympatric native species were <br />collected: flannehnouth suckers, bluehead suckers, speckled dace (Rhinichthys osculus) and Gila <br />spp., in decreasing order of abundance. Red shiner was the most abundant species in the 1994 <br />collections, accounting for 53.7% of the total catch (N= 2041). Nonnative cyprinids also <br />dominated the 1995 light trap samples, eventually comprising 80% of the annual total catch <br />(N=1206). Nonnative cyprinid collections generally increased through the sampling period <br />during both years of study. <br />Seine collections were conducted simultaneously with light trapping. All of the 1994 <br />seine collections occurred between RK 156.2-95.3. Nonnative cyprinids comprised 89% of the <br />total catch collected in 20 seine hauls (encompassing a total of 637 m2 of low velocity habitat). <br />Small numbers of flannelmouth sucker, bluehead sucker, speckled dace, channel catfish, <br />common carp, and Gila spp. were captured. The most abundant native fish captured were ninety- <br />fourjuvenile Colorado pikeminnow ranging in size from 40-118 mm TL. In 1995, 41 seine <br />hauls covered 324 m2 between RK 156.2 and 152.2. Nonnative cyprinids accounted for 95% of <br />the catch, along with small numbers of previously mentioned species and two Colorado <br />pikeminnow juveniles (86 and 111 mm TL). <br />Larval sampling: Colorado pikeminnow near Millard Canyon <br />No sampling for larval or YOY Colorado pikeminnow occurred near Millard Canyon in <br />1994. Specific efforts to locate early life stages of pikeminnow were conducted in 1995 between <br />RK 53.9-40.6 (RM 33.5-25.2). On 28-30 June 19951ow velocity habitats immediately <br />5 <br />