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<br />. <br /> <br />DRAFT <br /> <br />. <br /> <br />24-hour period. Maps of the river stretch utilized by the fish as described <br />above were completed for each 24-hour monitoring period. <br /> <br />3.2.3 Crepuscular Monitoring <br /> <br />. <br /> <br />Each fish during year 2 of this investigation was monitored for 2 hours during <br />dawn or dusk; beginning 1 hour before and ending 1 hour after sunrise or <br />sunset. Movement and habitat use of each fish was recorded during this period <br />to determine if different behavior occurs during these crepuscular periods. <br />Habitat measurements were taken at sites occupied by a fish for longer than 15 <br />minutes. <br /> <br />3.2.4 Test Flow Monitoring <br /> <br />. <br /> <br />Selected fish were monitored for daylight periods of 8 to 12 hours to determine <br />if scheduled flow releases from Flaming Gorge Dam had any effect on fish <br />position and movement. The fish were monitoring during either an increase in <br />flow of 800 to 4,000 cfs or a decrease of 4,000 to 800 cfs. A full description <br />of arrival times and resultant stage flow levels at different sites downstream <br />of Flaming Gorge Dam is presented later in this report. Detailed maps of <br />habitats were drawn over recent aerial photographs of the Rainbow Park area in <br />an effort to assess aereal habitat changes. <br /> <br />. <br /> <br />3.3 HABITAT ME'ASUREMENl'S <br /> <br />. <br /> <br />Upon completion of a 2-hour, 24-hour, or crepuscular monitoring period, habitat <br />measurements were taken to include water depth, water veloci ty, water <br />temperature, cover, and dominant and secondary substrate at each location where <br />a fish was stationary for 15 minutes or longer. Measurements were taken from <br />either a boat, by wading, or through a hole in the ice at three points relative <br />to the fish; the point of triangulation ('point' measurement), one meter toward <br />the river channel ('out' measurement), and one meter toward the shore (' in' <br />measurement) . <br /> <br />. <br /> <br />. <br /> <br />The 'point' measurements included water depth; water velocity at the river <br />bottom, at 0.2, 0.6, and 0.8 of the water depth; dominant and secondary <br />substrate; and water temperature. Measurements at one meter on either side of <br />the fish ('in' and 'out') were the same except that velocity was recorded only <br />a 0.6 depth. Velocities were measured using a Marsh-McBirney current meter and <br />an 6 to 12-foot wading rod. Where the measurement was taken in a <br />countercurrent (i.e. an eddy) greater than 90 degrees from the main directional <br />flow, velocity was recorded as negative. Substrates was assessed as one of six <br />categories (silt, sand, gravel, cobble, boulder, or bedrock) by probing with <br />the hand, foot, or wading rod, depending on water depth. Features providing <br />cover (i.e. large boulders, overhanging banks, sand ridges) at each location <br />were also recorded. <br /> <br />. <br /> <br />. <br /> <br />10 <br /> <br />. <br />