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<br />. <br /> <br />After sorting through drift samples and counting beads and larvae captured in the main <br /> <br />channel, these numbers were used to determine patterns of drift downstream from release sites. <br /> <br /> <br />Location of capture (left bank, right bank, or main channel) was noted, as was timing of capture <br /> <br /> <br />(relative to release), and numbers of beads and larvae captured within the breaches. The few fish <br /> <br /> <br />captured were identified and TC marked otoliths from early life stages of razorback sucker were <br /> <br />verified. However, we make only passing mention of the fish data collected in 2005 and 2006 <br /> <br />because preservation issues, especially in 2005, limited the number of fish recovered from <br /> <br />samples. Even though more fish were preserved and recovered from 2006 samples, we could not <br /> <br />establish which samples were well preserved and which were not, which made it difficult to <br /> <br />know if fish presence or abundance data were reliable. <br /> <br />In addition, it became clear upon reviewing sampling data that the GO Model 2030R <br /> <br />flow meters did not accurately measure velocities at lower flows in drift net samples. Without <br /> <br />backup flow velocity information such as Marsh-McBirney flow measurements in net mouths, <br /> <br />we had a number of gaps in data used to estimate the amount of flow sampled by nets. Because <br /> <br />of this, results from 2005 were used to calculate only the percent of released beads captured in <br /> <br />breach samples as well as to estimate the percent of flow entrained at various sites and at various <br /> <br />river stage levels. This data portrays the patterns of bead and flow entrainment over different <br /> <br />flow levels but not entrainment rates or densities of beads (e.g., beads per cubic meter of water <br /> <br />entrained), which would allow extrapolation of entrainment to the entire breach over the entire <br /> <br />sampling period. Because we were unable to extrapolate total bead entrainment, the best <br /> <br />measure of entrainment effectiveness then became calculating the percentage of beads entrained <br /> <br /> <br />into the breach over the different flows. In 2005, this value was calculated using the total <br /> <br /> <br />number of beads captured in breach samples divided by the total number of beads captured in all <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />25 <br /> <br />. <br />