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FEASIBILITY OF DEVELOPING AND MAINTAINING A SPORT FISHERY IN THE SALT RIVER PROJECT CANALS <br />Table 5. Mean catch-per-unit-effort (CPUE; fish/hr) by site for selected resident fish species <br />electrofished from the Arizona Canal, October 1992 through July 1994. See Table 2 for fish species <br />codes. <br /> Mean Mean <br />Species Site CPUE SD n" Species Site CPUE SD n* <br />CAIN 1 13.56 8.76 23 CTID 1 6.28 4.71 23 <br />2 20.13 16.44 21 2 1.24 2.48 21 <br />3 101.64 97.22 29 3 1.10 1.57 30 <br />5 53.06 36.54 21 5 0.74 0.66 21 <br />7 40.07 44.23 18 7 0.32 0.77 18 <br />CACL 1 2.10 2.61 23 MISA 1 1.55 1.67 23 <br />2 6.73 7.07 21 2 1.33 2.03 21 <br />3 111.27 144.38 30 3 2.83 4.61 29 <br />5 38.14 28.19 21 5 1.34 1.91 21 <br />7 11.69 20.61 18 7 0.06 0.26 18 <br />CYLU 1 14.82 20.88 23 ICPU 1 0.50 0.89 23 <br />2 42.16 46.34 21 2 1.60 2.41 21 <br />3 9.46 21.91 30 3 2.49 4.35 29 <br />5 11.62 21.25 21 5 0.11 0.30 21 <br />7 15.63 27.39 18 7 1.24 1.99 18 <br />DOPE 1 76.81 91.26 23 ONMY 1 0.30 1.42 23 <br />2 7.47 13.97 21 2 0.02 0.10 21 <br />3 21.56 76.26 30 3 0.00 0.00 29 <br />5 4.45 6.96 21 5 0.08 0.25 21 <br />7 2.26 3.46 18 7 0.08 0.34 18 <br />umber (n) of sample days for each site during this project <br />distributions were generated for roundtail chubs <br />and yellow bass. <br />Throughout our study, largemouth bass total <br />lengths were highly variable (Fig. 10). In Summer <br />1993 and Fall 1993, we identified 2 largemouth <br />bass cohorts. During Spring 1994 and Summer <br />1994, we identified a single cohort; however, <br />during these 2 seasons our sample size of <br />largemouth bass with TL >_240 mm was <br />primarily the result of biased sampling due to <br />repeated-effort electrofishing. <br />No gaps were found in the length frequency <br />distribution to separate threadfin shad into <br />separate cohorts (Fig. 11). Threadfin shad <br />exhibited some degree of growth over time <br />because TL measurements shifted upward. In <br />Winter 1993-1994, threadfin shad (TL <_90 mm) <br />were absent from our collections. This trend <br />continued in Spring 1994 (TL <_ 100 mm) and <br />Summer 1994 (TL <_ 110 mm). <br />The number of red shiners declined <br />dramatically during the last 3 seasons (i.e., Winter <br />1993-1994, Spring 1994, and Summer 1994) of this <br />study. We found no distinct breaks in the length <br />frequency distribution to separate red shiners into <br />specific cohorts (Fig. 12). <br />Sonora suckers exhibited a bimodal length <br />frequency distribution during most of our study <br />(Fig. 13). To a lesser degree, a third cohort of <br />young fish (TL 5120 mm) appeared in Summer <br />1993 through Winter 1993-1994, and again in <br />Summer 1994. However, by Summer 1994 a <br />bimodal length distribution had returned. <br />Desert suckers exhibited a bimodal length <br />frequency distribution throughout most of our <br />study, except in Summer 1993 when a third <br />cohort appeared (Fig. 14). The length ranges <br />within the 2 cohorts remained stable during the <br />first 3 seasons. The same 2 cohorts also remained <br />stable during Fall 1993 through Spring 1994. By <br />Summer 1994, the bimodal distribution shifted <br />downward towards smaller fish. <br />22 ARIZONA GAME & FISH DEPARTMENT, TECH. REP. 18 B. R. WRIGHT AND J. A. SORENSEN 1995