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<br />~ <br />c-:.~ <br />1'-' <br /> <br />EXECUTIVE SUMMARY <br /> <br />i-Ol.'- <br />t,,) <br />.:> <br /> <br />Between Shiprock, New Mexico and Chinle Creek, Utah, secondary channels are <br />a common feature of the San Juan River. Prior to initiation of the San Juan River Seven- <br />Year Research Program no studies specific to secondary channels had been conducted, <br />As part of the Seven-Year Research Program, research was initiated in 1991 to <br />characterize the fish fauna of San Juan River secondary channels, to discern seasonal-use <br />patterns of secondary channels by common fishes, to evaluate the effects of different flow <br />regimes on common fish species, and to characterize use of secondary channels by rare <br />fishes (roundtail chub, Colorado pikeminnow, and razorback sucker). Summer <br />inventories of secondary channels were iniliated in 1991 and spring and autumn <br />invenlories began in 1993. Research on secondary channels occurred in Geomorphic <br />Reaches 5, 4, and 3. Flows of 1500 cfs wetted most secondary channels and flows of <br />2500 cfs inundaled almost all. <br /> <br />During spring, when flows were alleast 2500 cfs, native flannelmoulh sucker and <br />bluehead sucker and nonnative common carp and channel catfish numerically dominated <br />secondary channel fish collections, Small-bodied fishes such as native speckled dace and <br />nonnative red shiner and fathead minnow, were uncommon in spring collections. The <br />sampling technique, raft-mounted electrofishing, was not an effective means of collccting <br />small-bodied fishes. Abundance of flannel mouth sucker was less in 1997 than 1993 in all <br />reaches, but the decline was most apparent in Reach 4, Allhough abundance evidently <br />declined, mean tolallength, mean biomass, size-struclure, and age-structure were not <br />markedly differenl in 1997 from that found in 1993, Bluehead sucker abundance was <br />least in 1995 in all Reaches and second greatest in 1997. Neither mean total length nor <br />biomass was appreciably different in 1997 than that found in 1993, In Reach 5, where <br />bluehead was typically most common, lhere was little change in size- or age-structure, <br />but in Reach 3 (where least common), there was considerable variation in these <br />populalion attribules among years. [n all years in all Reaches, most common carp <br />captured were 2: 400 mm 10lallength and lhus adults. Common carp were slightly more <br />common in all reaches in 1997 lhan 1993, bul mean total length and biomass did nol <br />change, Abundance of channel catfish in Reaches 5 and 4 was slightly grealer in 1997 <br />lhan 1993, but was considerably greater in Reach 3 in 1997 than 1993. Total biomass, <br />however, was greater in 1993 lhan 1997 in Reaches 5 and 4, [n Reach 3, total biomass <br />was least in 1993, but froml995 through 1997 did not change. Mean total length and <br />biomass declined from 1993 lhrough 1997 in all reaches, but most dramatically in <br />Reaches 5 and 4. Changes in size- and age-struclure of channel catfish were also noted; <br />smaller and younger fish were more common in collections in 1997 than 1993. In most <br />years (1994 lhrough 1997) and Reaches flannelmoulh sucker was slightly more abundant <br />in secondary channels lhan the primary channel. Bluehead sucker, however, tended 10 be <br />more common in the primary than secondary channels. In Reach 5, common carp were <br />more common in secondary channels lhan primary chalmel in all years and usually so in <br />