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<br />:.1 <br />'. <br />! 0 <br />.j C.' <br />N <br />iJ ~,; <br />..". '.. <br />) ".J <br />") <br />..~ <br />., <br />~) <br />'} <br />., <br />,.r <br />" <br />.J <br />, <br />...., <br />, <br />:..';: <br />:~'t <br />.P <br /> <br />" <br /> <br />.':', <br /> <br />., <br /> <br />., <br /> <br />..Eo <br /> <br />EXECUTIVE SUMMARY <br /> <br />As part of the San Juan River Basin Recovery Implementation Program (SJRIP), investigations <br />of non. native fishes were conducted during 1991.1997 to characterize interactions with native <br />fishes. The impacts of non-native fish species on natives has often been identified as a key <br />impact, along with habitat alteration, that facilitates loss of native biological diversity, In the San <br />Juan River, the endangered Colorado pikeminnow Ptychocheilus lucius and razorback sucker <br />Xyrauchen texanus, as well as the other members of the native fish community, are the focus of <br />the SJRIP. A major component of native fish recovery efforts in the San Juan River is the <br />mimicry of the natural hydrograph, and SJRIP studies were designed to assess the response of the <br />resident fish community to variable flow conditions affected the releases from upstream Navajo <br />Dam. Section 5.4 of the SJRIP Long Range Plan identified several informational and action <br />needs regarding non. native fish species: 1) characterize distribution and abundance patters of <br />non.native fishes, 2) characterize habitats used by non-native fishes, 3) describe the food habits <br />of non-native fishes. 4) characterize the response of non-native fishes to varying flow regimes, 5) <br />develop a non-native fish stocking policy, 6) develop regulations to restrict bait-fish species <br />harvest, 7) develop regulations to control importation of non.native fishes, and 8) monitor and <br />evaluate non-native fishes control actions implemented as part of the SJRIP. This report presents <br />results of non. native fishes investigations that address items 1-4 and 8 above. <br /> <br />The distribution and abundance patterns oflarge.bodied non.native fishes were studied to <br />determine responses to varying flow regimes, Sampling was primarily by raft.mounted <br />electrofishing. but also included limited hoop and trammel netting. Main and secondary channel <br />sampling collected 18 species of non.native fish, Channel catfish !ctalurus punctatus and <br />common carp Cyprinus carpio were the most abundant and the most widely distributed species, <br />Seasonal movements of striped bass Marone saxatilis and walleye Stizostedion vitreum out of <br />Lake Powell and upstream into the San Juan River as far as Shiprock, New Mexico were <br />documented. Mark and recapture studies of channel catfish and common carp were used to <br />estimate abundance and to evaluate movement patterns lor the entire reach of the San Juan River <br />sampled, Farmington, New Mexico downstream to Clay Hills, Utah. Schnabel population <br />estimates (95% C.L) for channel catfish ranged from 131,768 (72,]43 . 219,393) in 1992 to <br />274,484 (115,7]2.563,162) in 1995 and for common carp were 26,576 (14,2]3.45,019) in <br />1992 to 107,268 (61,438 - 172,692) in 1995, The proportional abundance of non-native species <br />sampled during electro fishing surveys in main and secondary channel habitats increased during . <br />1994-1997, after initial declines observed during1991.1994. Implementation of high spring <br />releases from Navajo Dam did not appear to negatively impact non-native species distribution or <br />abundance, <br /> <br />Recapture rates for 3,878 channel catfish and 3,034 common carp tagged with numbered Floy <br />tags were 5,8% and 10.8%, respectively, Neither species exhibited strong movement patterns to <br />or affinities for specific areas of the San Juan River as has been documented in other river <br />systems. The mean distance moved between recapture and original or last capture locations was <br /> <br />San Juan River Non-native Species Interactions. Final Report, I February 2000 <br /> <br />11 <br />