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levels in the tank were within 10 mg/L of the release site. The fish were then placed within <br />live cars secured in the LCR, monitored, and allowed to acclimate overnight until their <br />release the following morning. Throughout this trip the water at the LCR capture and <br />release sites and in the holding tank were periodically tested for dissolved oxygen, <br />conductivity, temperature, and pH using a Surveyor 3 Hydrolab (Hydrolab Corp., Austin, <br />Texas); CO2 levels were measured using the previously described titration technique. <br />Fall Monitoring trip <br />We conducted a fall monitoring trip from October 31-November 4, 2003 to survey the area <br />above Chute Falls for the presence of any previously translocated humpback chub. We <br />deployed twenty-two baited hoopnets from 14.2 to 16.74 RKM for three --24 hour hauls. <br />We also deployed two gill nets and one trammel net. We measured (TL) speckled dace, <br />Rhinichthys osculus, captured in the first eleven nets of the first haul, and then tallied <br />thereafter. We measured all other fishes for total length (TL) . Each humpback chub was <br />examined for an elastomer tag, held overnight in an aerated tank (so ingested bait could be <br />digested), inserted with a passive integrated transponder tag (Biomark, Inc.), and released. <br />We examined the digestive tracts of all large-bodied predatory fish for fish remains. In <br />addition, we instructed all personnel from prior downstream LCR and Colorado River <br />monitoring trips (i.e., July-November 2003) to examine humpback chub for yellow <br />elastomer tags to detect any translocated fish that may have migrated downriver. <br />Statistical Analyses and Comparisons <br />We compared numbers and proportions of fishes captured in hoopnets between the <br />reconnaissance and monitoring trips. Independent sample T-tests were used to examine <br />for significant intraspecific length differences of various species. Precursory Levene's Test <br />for Equality of Variances validated the use of pooled- vs. separate-variances T-tests. We <br />used pooled-variances T-tests to examine for significant humpback chub and fathead <br />minnow, Pimephales promelas, length differences between the two trips, and between <br />those humpback chub with and without visible elastomer tags captured during the <br />monitoring trip. Separate-variances T-tests were used to examine the length differences of <br />both speckled dace and common carp, Cyprinus carpio, between trips. The sample sizes <br />of speckled dace were sufficient to graphically compare the mean catch per unit effort <br />(CPUE) ± 2 standard error between trips; nonoverlapping error bars were considered <br />significantly different. We constructed length frequency histograms of humpback chub from <br />the July 2003 translocation and November 2003 monitoring trips. To examine for <br />concurrence over time, we compiled and overlaid by location the mean CO2 levels from the <br />July 2003 reconnaissance trip, along with those collected in July 1993 by Mattes (1993) <br />and in June 1994 by Robinson et al. (1996). Because "RKM" accuracy has improved with <br />newer technology, we updated the historical locations to concur with those from this study. <br />The names and descriptions of known sites given by Mattes (1993) and location map <br />detailed in Robinson et al. (1996) made this possible. Discharge data from U.S. Geological <br />Survey gage 09402300, located above the mouth of the LCR, allowed for an inspection of <br />flow conditions in the Colorado River since humpback chub were first translocated above <br />Chute Falls. <br />8