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FEASIBILITY OF DEVELOPING AND MAINTAINING A SPORT FISHERY IN THE SALT RIVER PROJECT CANALS <br />Figure 16. Overall length-frequency distributions of <br />yellow bass in the Arizona Canal (October 1992-July <br />1994). <br />Figure 17. Overall length-frequency distributions (across <br />seasons) of roundtail chub in the Arizona Canal <br />(October 1992-July 1994). <br />Granite Reef Electrical Barrier Monitoring <br />To estimate fish immigration into the <br />Arizona Canal, we looked at fish collection data <br />from surveys (Jakle and Riley, unpubl. data) taken <br />between Granite Reef Dam and the electric fish <br />barrier. From 1991 to 1995, 17 fish species were <br />collected above the barrier (Table 9). Species <br />richness remained relatively stable, with a low of <br />9 species collected in 1991 and a high of 13 species <br />in 1992 and 1995. Percent species composition <br />varied across years. The most abundant species (n <br />700) collected above the barrier for the 5-yr <br />period were: desert sucker (29.70/6), tilapia (Tilapia <br />spp.; 16.5%), Sonora sucker (14.10/6), channel <br />catfish (13.0%), and common carp (12.4%). The <br />least abundant species (n < 50) were: roundtail <br />chub, walleye, threadfin shad, bluegill, yellow <br />bullhead, white amur, and bigmoutlr buffalo <br />(Ictiobus cyprinellus). <br />Percent species composition of tilapia and <br />common carp were highly variable between years. <br />In 1991, tilapia was the most common species <br />collected (n = 748) but they were absent from the <br />1995 survey. However, tilapia still ranked second <br />in overall relative abundance during this 5-yr <br />period. Common carp above the barrier were <br />rare to nonexistent between 1991 and 1993, but <br />their numbers increased in 1994 (n = 526) ranking <br />them highest in abundance. In the 1995 survey, <br />carp numbers again declined, but they still ranked <br />fifth in total abundance for the 5-yrs. The <br />abundance of both species above the barrier was <br />unusual when compared to our electrofishing <br />sampling downstream where carp were rare (n = <br />19) and tilapia were absent. <br />Experimental Fish Stockings <br />Channel Catfish (June-Stocking). Most June- <br />stocked catfish sampled were recovered within the <br />first 5 weeks after stocking (Fig.18). We sampled <br />161 (10.7%) fish from June 1993 through July <br />1994. Monthly and repeated-effort electrofishing <br />surveys captured 44 June-stocked channel catfish. <br />Twenty of these fish were collected during our <br />repeated-effort sampling (CPUE = 1.7 fish/hr). <br />We sampled 69 June-stocked channel catfish by <br />angling (CPUE = 1.1 fish/hr) and 1 fish by gill <br />net (CPUE = 0.1 fish/hr). We documented an <br />additional 41 fish harvested by public anglers, but <br />were unable to estimate the catch rate due to <br />60 <br />cn <br />................. <br />L <br />40 <br />LL <br />0 <br />= 20 <br />Z <br />o <br />1 4 <br />10 13 16 19 22 25 26 31 34 <br />Weeks After Stocking 3i 4u 43 49 52 55 <br />Figure 18. Recapture frequency of June-stocked channel <br />catfish across weeks after stocking for all sampling <br />methods (June 1993 - July 1994). <br />32 ARIZONA GAME & FISH DEPARTMENT, TECH. REP. 18 B. R. WRIGHT AND I. A. SORENSEN.1995