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1 100 MODDE ET AL. <br /> 70 670 <br /> 60 discharge 1995 sss <br /> 50 453 <br /> 40 340 <br /> 30 <br />- <br /> 20 - <br />E 10 <br />?i00plankton 113 ?? <br />E <br />Z <br />p 0 <br />10 20 30 10 20 30 10 20 30 90 20 30 <br />10 20 30 10 20 0 <br />pt <br />Y <br /> <br />70 <br />670 t11 <br />V <br />y <br />0 60 discharge <br />1996 <br />s6s <br />0 <br />0 <br />N <br />50 <br />453 <br /> 40 $40 <br /> 30 ~ <br />227 <br /> 20 <br /> 10 zooplankton 113 <br /> 0 - <br />1o 20 30 10 20 30 10 20 30 10 20 30 <br />10 20 30 10 20 0 <br /> May Jun Jul Aug Sep Oct <br />FIGURE 3.-Green River discharge (solid line; right scale) and zooplankton density (broken li ne; left scale) in <br />Old Charley Wash d uring 1995 and 1996. <br />during the high-flow period. Pucherelli et al. <br />(1988) reported that most channel backwaters do <br />not exist in the middle Green River until flows <br />recede to approximately 109 m3/s, well after ra- <br />zorback sucker larvae were collected in the Green <br />River (Muth et al. 1998). Solar radiation increases <br />temperature in the relatively shallow, no-velocity <br />floodplain, providing a more favorable environ- <br />ment for age-0 fishes. The temperature preferen- <br />dum for 6-year-old hatchery reared razorback <br />suckers (150-300 mm) is between 22.9°C and <br />24.8°C (Bulkley and Pimental 1983). Tempera- <br />tures were either at or just above this preferendum <br />during most of the summer in Old Charley Wash, <br />exceeding 25°C in August 1995 and July 1996. <br />Because the temperature tolerance and preference <br />of younger fish are higher than those of adults <br />(Boehlert 1981), the temperatures observed in Old <br />Charley Wash were probably nearly optimal for <br />the growth of razorback sucker juveniles. <br />Throughout spring and summer, water tempera- <br />tures in the wetland were warmer than those in the <br />main channel. Dissolved oxygen concentrations <br />and water depth were sufficient to support fish <br />through the warmwater months. Dissolved oxygen <br />concentrations were rarely below 5.0 mg/L, the <br />concentration suggested by Boyd (1979) as opti- <br />mal for warmwater pond fishes. <br />This favorable physical environment was com- <br />plemented by high prey densities. High zooplank- <br />ton densities in Old Charley Wash coincided with <br />access by larval razorback suckers to floodplains <br />in the Green River. Mabey (1993) reported zoo- <br />plankton densities of 7.1/L and 1-5/L (using a 63- <br />µm mesh) in riverine backwaters near Ouray in <br />July and August, respectively, compared with <br />311.4/1- and 690.2/L during the same time in Old <br />Charley Wash. In high-velocity main-channel hab- <br />TABLE L-Time periods when larval razorback suckers were collected in the Green River, Utah, and the number of <br />days larvae had access to floodplains in the Ouray National Wildlife Refuge wetland complex (i.e., flows above 575 <br />m3/s) in the presence (regulated) and absence (unregulated) of the Flaming Gorge Dam. <br /> Days larvae had <br /> access to floodplain <br /> Duration wetlands <br /> Number (d) of <br /> Dates larvae of larvae larval Un- <br />Year present collected collections Regulated regulated <br />1993 19 May-8 Jul 292 52 0 17 <br />1994 15 May-15 Jun 1,277 32 0 0 <br />1995 13 Jun-21 Jul 32 39 0 10 <br />1996 3 Jun-27 Jun 174 25 0 5