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<br />EXECUTIVE SUMMARY <br /> <br />The San Juan River is historic habitat for seven native fish species <br />including three rare fish species: the Colorado squawfish (Ptvchocheilus <br />lucius), razorback sucker (Xvrauchen texanus), and roundtail chub (Gila <br />robusta). In 1991 and 1992, the U.S. Fish and Wildlife Service's Colorado <br />River Fisheries Project (CRFP) office in Grand Junction, Colorado, in <br />cooperation with other state and federal agencies conducted electrofishing <br />surveys on the lower mainstem San Juan River. The primary responsibility of <br />the CRFP office is to monitor the adult fish community in the river's main <br />channel habitat. <br />The river was electrofished from river mile (RM) 158.6 (Hogback <br />Diversion, New Mexico) to Mexican Hat, Utah (RM 53.0) in 1991, during three <br />sampling trips. Three trips in 1992 sampled from Farmington, New Mexico (RM <br />179.0) to Mexican Hat, Utah (RM 53.0). The most abundant species collected in <br />1991 was flannelmouth sucker (Catostomus latipinnis), followed, in descending <br />order, by common carp (Cvorinus caroio), channel catfish (Ictalurus <br />Dunctatus), and bluehead sucker (~discobolus). In 1992 the most abundant <br />species was flannelmouth sucker, followed by bluehead sucker, channel catfish, <br />and common carp. <br />Fish community composition did not change markedly between the two years. <br />Common carp and channel catfish accounted for 20% of the total catch in the <br />first two years, while all other introduced species composed only 3% of the <br />total catch. Native species, mostly flannelmouth sucker and bluehead sucker, <br />composed 77% of all fish collected in 1991 and 1992. Colorado squawfish and <br />roundtail chub combined composed less than 1% of the total catch in the first <br />two years. Electrofishing capture rates were highest for flannelmouth sucker, <br />bluehead sucker and speckled dace (Rhinichthvs osculus) in the reach of river <br />from Hogback Diversion, New Mexico (RM 158.6) to Four Corners Bridge (RM <br />119.2). Catch rates for most species showed a downward trend as sampling <br />proceeded downriver from Hogback Diversion. <br />Twelve Colorado squawfish and five roundtail chub were collected in two <br />years. No razorback sucker were collected. All Colorado squawfish were <br />captured between RM 142.0 and 117.0. Four of five roundtail chub captures <br />occurred between RM 147.9 and 135.3. <br />Nine Colorado squawfish were surgically implanted with radio tags and <br />tracked year-round from the air and ground. One hundred and thirteen radio <br />contacts were made with these fish between June 1991 and January 1993. All <br />radio contacts occurred between RM 142.0 and 117.0. During pre-spawn periods, <br />May and early June, Colorado squawfish demonstrate an affinity for the section <br />of river in and around the Mancos River confluence (RM 122.6). During <br />estimated spawning periods, 79 percent of radio contacts with Colorado <br />squawfish were made within the "Mixer" area (RM 133.4 to 129.8). The highest <br />percentage of ground contacts (34.3%) were made with Colorado squawfish using <br />run habitat. Mean maximum displacement (7.4 miles) and mean final <br />displacement (3.99 miles) were very close to that of Colorado squawfish in the <br />illS-mile reach" of the Colorado River near Grand Junction, Colorado. Total <br />longitudinal movement averaged 8.94 miles. All of the above information <br />suggests that the river reach between Hogback Diversion and Four Corners <br />Bridge (RM 158.6-119.2) is important to the native fish of the San Juan River. <br />Information to date is insufficient to assess the impacts of existing <br />instream water diversion structures on rare fish movement. <br /> <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 />