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<br />4 <br /> <br />I <br />I <br />I <br />,I <br />I <br />I <br />,I <br />" <br />il <br />" <br />I <br />I <br />I <br />I <br />I <br />II <br />I <br />I <br />i <br /> <br />METHODS <br /> <br />Discharge, water temperature, and water quality <br /> <br />Discharge records during the sampling period were obtained from U.S. <br />Geological Survey gaging station, named "near Lily, Colorado", #09260000 at <br />RK 15 (Crowfoot et al. 1996). Water quality was measured on four occasions <br />during runoff and baseflow. Conductivity was measured with a Cole Parmer@, <br />model TDSTestr 3 meter lrange 1-1990 jJS), pH with a Cole Parmer@, model <br />pHTestr 2 meter, total hardness with a HACH@ model HA-DT test kit, alkalinity with <br />a HACH@ model AL-DT test kit, dissolved oxygen with a HACH@ model AL-DT test <br />kit using a modified Winkler titration method, and light penetration with Secchi <br />disk. <br /> <br />Water temperature was collected hourly by Ryan data loggers on the Little <br />Snake River at RK 15 from May 5 through October 28 and on the Yampa River at <br />Moffat County Road-25 bridge, 2.5 km upstream of the Little Snake River <br />confluence, from May 5 through October 1. Loggers were checked bi-weekly to <br />insure they remained submerged as water levels dropped. <br /> <br />Fish community sampling <br /> <br />Fish were collected on six occasions from May 16 to October 1, 1995 using <br />techniques similar to those employed the previous year IHawkins et al. 1997). <br />Sampling occurred in the spring and summer during the ascending and descending <br />limbs of runoff and in autumn during base flow. Sample dates were May 15-18, <br />June 1-6, June 21-23, July 1-7, July 16-18, and September 27- October 1 <br />(Figure 2). Sampling gear and methods targeted larvae, juveniles, and adults of both <br />