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404 <br />PERSONS AND BULKLEY <br />ervoir filled to maximum elevation (1,128 m <br />above mean sea level) for the first time during <br />1980. <br />During the 1981 sampling period, the reser- <br />voir level was about 1,122 m and the river flow <br />averaged less than 380 m3/sec. As a result of the <br />lower reservoir level and reduced river flow, the <br />mixing zone was greatly altered: mud and silt <br />bars that formed during 1980 were exposed in <br />1981; the river channel was narrower and shal- <br />lower, current velocity was greatly reduced; and <br />there were fewer and smaller side eddies (Persons <br />et at. 1981). <br />The second sampling site, Spanish Bottom <br />(river km 343), lies above the upper rapid of <br />Cataract Canyon and just below the confluence <br />of the Green and Colorado rivers. The river is <br />narrow and relatively straight for 5.6 km from <br />the confluence to Spanish Bottom. Cataract Can- <br />yon consists of a series of relatively short rapids. <br />At Rapid 23 or Big Drop, the most severe in the <br />canyon, the rate of fall is 7 m/km (Baars and <br />Molenaar 1971). <br />METHODS <br />Fish were collected at Gypsum Canyon during <br />the period April 26-June 18, 1980 and May 24- <br />July 22, 1981 with multifilament nylon gill nets <br />31 in long x 3 m deep and with 6.4-cm mesh <br />(bar measure). One end of the net was attached <br />by rope to the shore and the net was fished in <br />water 1-15 m deep. Nets were checked every 4- <br />5 hours during 1980 and every 0.5-3 hours in <br />1981. Catch per gill-net hour is reported in terms <br />of ore 31-,,. net. Nets also we.;, fisl.ed near Span- <br />ish Bottom on May 7-21, 1980, and on May 26- <br />June 2, 1981, to determine if striped bass moved <br />upriver through the Cataract Canyon rapids. <br />All striped bass captured were weighed and, <br />measured (total length). Stomachs of most adult <br />striped bass collected in 1980 were preserved in <br />10% buffered formalin. Stomachs were examined <br />in the field during 1981. Gonads also were exam- <br />ined to determine stage of maturity and were <br />preserved for later study when maturity was <br />questionable. Gonads were classified as imma- <br />ture, maturing, mature, or spent-based partly <br />on work by Scruggs (1957) and Persons et al. <br />(1981). <br />Other workers have effectively collected eggs <br />in plankton nets to determine striped bass repro- <br />ductive success (Johnson and Koo 1975; Turner <br />1976; Combs 1979). Plankton nets (0.5-m diam- <br />eter mouth, 0.565-mm mesh) were fished daily <br />in the main river channel at bottom, middle, and <br />sub-surface depths for 3-5 minutes at each depth. <br />Nets became clogged with debris if towed for a <br />longer period. Tows also were made in quiet water <br />and slow back eddies near Gypsum Canyon. Ich- <br />thyoplankton samples were preserved in 5-8% <br />buffered formalin containing rose bengal dye for <br />later examination for the presence of fish eggs or <br />larvae. <br />River discharge in the sampling area was esti- <br />mated to be the sum of the discharge of Green <br />River measured at Green River, Utah, 188 km <br />upstream from the confluence, and the discharge <br />of the Colorado River measured at Cisco, Utah, <br />156 km upstream from the confluence (Unpub- <br />lished data from the U.S. Geological Survey, 1980 <br />and 1981). Surface temperature was recorded <br />daily at the sampling sites. <br />RESULTS <br />During the 1980 sampling season, the river <br />discharge ranged from 680 to 1,800 (average, <br />1,280) m'/sec. Discharge during the same period <br />in 1981 ranged from 200 to 650 (average 380) <br />m-1/sec (Fig. 1). <br />Water Temperatures <br />Surface water temperature at Gypsum Canyon <br />varied from 12.8 to 17.2 C during the 1980 sam- <br />pling period (Fig. 1), and was within the range <br />of temperatures normally present during striped <br />bass spawning (16-18 C) during May 54, May <br />20-24, and after June 9, 1980. Water tempera- <br />tuue at Gypsum Canyon ...IS -W-Ilth::c or above he <br />range suitable for spawning throughout the 1981 <br />sampling period. Temperatures at Spanish Bot- <br />tom were suitable for spawning during the 1981 <br />sampling period but not during that of 1980. <br />Catches <br />Common carp (Cyprinus carpio), striped bass, <br />walleyes (Stizostedion vitreum), and channel cat- <br />fish (Ictalurus punctatus) were the most fre- <br />quently captured species during about 8,200 hours <br />of sampling with gill nets in 1980 and 1981 (Per- <br />sons et al. 1981). The striped bass was the most- <br />frequently collected species in 1980; common <br />carp and walleyes were most abundant in 1981. <br />Specimens of two endangered species were cap- <br />tured: 6 razorback suckers in 1980 and 10 in <br />1981; 45 Colorado squawfish in 1980 and 6 in <br />1981. <br />GYPS <br />U 25- <br />Z_ SPAN <br />W <br />m <br />20 <br />w <br />g 15?.. <br />W <br />I- <br />0` <br />w 20 <br />15- <br />I V <br />? <br />O 5 <br />u_ 0 <br />30 <br />APRIL <br />Figure 1. F <br />.water temp <br />1981. <br />Catches of <br />the same ge <br />temperature <br />early May, a <br />mid-June (F <br />two peaks, o <br />June. Other <br />four peaks <br />fated with <br />levels (Hare <br />Peak strip <br />0.2 fish per <br />per unit of <br />1980 (Fig. 2 <br />during 1981 <br />ing populati? <br />of an additi <br />Records ind: <br />brood stock <br />higher in 19 <br />1981). <br />Although <br />1980, and N <br />Bottom, no <br />bass eggs wr <br />striped bass <br />Cataract Ca;