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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />RESULTS <br /> <br />SamDle Effort and Fish Captured <br /> <br />The following tables summarize the results of Trip No.2 Table 1 is a summary of sampling <br />effort by gear type; Table 2 presents the catch composition by species; Table 3 is a summary of <br />endangered fish; and Table 4 is a list of endangered fish captured. Table 5 presents the meristic <br />measurements taken on any Gila captured. <br /> <br />Endan2ered Fish Captured <br /> <br />A total of 99 Colorado squawfish and 2 humpback chub were captured during Trip No. 2 <br />(Table 3). The Colorado squawfish included 13 juveniles ranging in size from 61 - 336 mm TL, and <br />86 yay (1990 year class) ranging in size from 27 - 59 mm TL. <br /> <br />The majority of the yay Colorado squawfish (74 of 86) were found downstream of Ten Cent <br />Rapid (RM 200) in the former lake basin. This section of lake was riverine in character due to the <br />low pool elevation of Lake Powell. Discovery of this large number of yay Colorado squawfish in <br />this region is significant because it indicates that there is movement of yay into Lake Powell With <br />lakes levels higher in previous years (1985-1989) and with few backwater nurseries available, assessing <br />these numbers has been difficult. Now, we are able to say that, at least in 1990, significant numbers <br />of yay Colorado squawfish were transported into or moved into the Lake Powell basin. If this has <br />happened in other years when lake levels were higher, the absence of nursery backwaters and the <br />presence of large numbers of predators has prevented us from assessing the numbers of fish involved. <br />The numbers of Colorado sQuawfish, particularly yay, moving into T Jl1c-p P91.veY <1ftmJally CgYlEi Qe <br />~ 1!ecause of a lack of nursery habitHt and lar~e numbers of predators in the lake, their <br />chances of survival are probably minimal. ^ <br /> <br />Currently, riverine conditions exist to below Sheep Canyon (RM 176), including a well defined <br />channel and significant velocities. However, due to the unique channel morphology in this area <br />associated with the low lake level, habitat for yay and early juvenile Colorado squawfish may be <br />limited. Only 4 backwaters were counted in this area (RM 191-RM 177) where 10 were noted during <br />Trip No. 1. Lack of backwaters in this area is probably due to the river channel actively cutting into <br />large deposits of sediment laid down in the inflow area since 1983. In most areas the shorelines of <br />the river are characterized by high (10-20 foot), steep, actively eroding silt cutbanks. A few areas of <br />shear cliff, where the river has completely eroded the sediments from the canyon wall also exist in <br />this reach, particularly on the outside of bends in the river. Consequently, any yay or juvenile <br />Colorado squawfish that have moved or been transported into the inflow region during winter or <br />spring runoff would be forced to face rigors associated with the main channel in the inflow region, <br />including predation by the lake dwelling species. Electrofishing and netting below Ten Cent Rapid <br />(RM 200) produced large numbers of channel catfish, stripped bass, and walleye, indicating that the <br />inflow area continues to support large numbers of these predatory species despite the increasingly <br />riverine nature of the area. <br /> <br />The potential exists for more backwater habitat to be created in this area as thunderstorm <br />runoff flushes sediments from tnbutary canyons. This backwater habitat may become more prevalent <br />when lake levels rise to reflood the newly created channels. <br /> <br />3 <br />