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<br />GREEN RIVER LIGHT TRAPS: 1994 and 1995 <br />NNC (0.39%) <br />CP (0.05%) RZ (2.1696) <br /> <br /> BH (5.29%) <br />FH (21.71 %) C'' (0'0096) <br /> CH (0.93%) <br /> 1994 SD (1.76%) <br />n 2041 ' <br /> RS (53.65%) <br /> RZ (0.33%) <br /> FM (15.51%) <br /> BH (2.9096) <br /> <br />1995 CS (0.91 %) <br /> CH (0.00%) <br /> ~t=1Z06 SD (0.33%) <br />NNC (58.04%) RS (14.93%) <br /> FH ro.oo%) <br /> ss (7.os%) <br /> cP (o.oo%) <br />Figure 6. Relative abundance offish collected in larval light traps in the Green River, 1994 and <br />1995. Summarizes collections near the mouth of the San Rafael and near Millard Canyon. RZ = <br />razorback sucker„ FM = flannelmouth sucker, BHS = bluehead sucker, CS =Colorado <br />squawfish, CH = Gila spp., SD =speckled dace, RS =red shiner, FH=fathead minnow, SS = <br />sand shiner, CP =common carp, and NNC =non-native cyprinid. <br />In 1995, larval-production as indexed by light trap catch was down for all species. A total of four <br />(4) larval razorback suckers were collected in the lower Green River, two near the San Rafael <br />confluence (RM 97.0), and two near Anderson Bottom (RM 33.5). Collection dates ranged from <br />May 31st to June 30th, and total lengths ranged from 11.3 mm to 12.8 mm (see Table 1 and <br />Figure 4 and 5). Flannelmouth suckers (n=187) comprised 15.5% of the catch with the bulk of <br />them collected early in the sampling period (peak date May 03). Non-native cyprinids did not <br />become abundant in the samples until relatively late in the year, July 11 and 19. <br />DRAFT' 13 <br />