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<br />calculated bankfull flow. The very high flows of September and October 1997 were an <br /> <br />obstacle for cross section work, and because of the short window when flows were below <br /> <br />600 cfs some of the field work was modified or abandoned. <br /> <br />METHODS <br /> <br />Cross Section Profiles <br /> <br />Cross section methods are frequently used to determine minimal flows for <br /> <br />maintaining habitats required by members of the aquatic community. These methods <br /> <br />operate by determining a stage-discharge relationship, usually across a riffle, and using <br /> <br />that relationship to find a flow that provides adequate depths and velocities for fish <br /> <br />habitat maintenance. This study used a total of 110 cross sectional profiles spread over a <br /> <br />distance of 64 river miles. Sample sites were selected in strata 6 and 8, described above <br /> <br /> <br />(Miller et al.I982), and their river mile location is given in Table 1. Sampling sites were <br /> <br /> <br />randomly selected by dividing the strata into 0.5 mile segments (called clusters), which <br /> <br /> <br />were meant to include two run/riffle sequences. Twelve clusters were randomly selected <br /> <br /> <br />from Strata 6 and 13 clusters were randomly selected from Strata 8. <br /> <br />Only one stage-discharge measurement was taken at each cross section. The <br /> <br />concern was for habitat availability during the base flow period, when flow typically <br /> <br />ranges from 100 to 300 cfs. Since a few cross sections were done at flows of about 600 <br /> <br />cfs, model runs were compared using the calculated and a higher roughness value to <br /> <br />determine if calculated mannings n values were suitable for extrapolating beyond 40% of <br />the measured flow. <br /> <br />Cross sectional measurements were made during the base flow period in August <br /> <br />and September in 1996 and in September and October 1997. The bed profile was <br /> <br />surveyed between head pins set at or above the grassline on both sides of the channel. <br /> <br />10 <br />