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<br />. <br /> <br />. <br /> <br />We can not explain why more water was entrained into Thunder Ranch in 2006 than <br /> <br />2005; the increase in beads entrained in 2006 is likely due to increased flow entrained, but may <br /> <br />be due to the release location being so close to the sample site. Even though only Breach 3 was <br /> <br />sampled in 2005, comparisons showed that more than twice as much flow was entrained into that <br /> <br />single breach in 2006 than 2005. It is possible that breach elevation was higher in 2005 and <br /> <br />inhibited flow entrainment, but we have no means to evaluate this hypothesis. Measurement <br /> <br />error is also possible but seems unlikely, given the magnitude ofthe differences and that many of <br /> <br />the same personnel were on hand to estimate flow entrainment in a consistent fashion between <br /> <br />years. Another possible explanation for vagaries in flows and entrainment rates at this and other <br /> <br />sites, is that flow levels fluctuate, sometimes dramatically, within a day. Our use of mean daily <br /> <br />flow values would mask effects of those flow variations, which may in fact be responsible for <br /> <br />some of the anomalous values we observed. <br /> <br />We also have some evidence that bead entrainment reflects larval fish entrainment as <br /> <br />well, because we recovered some fish from Thunder Ranch samples in 2006. For example, on <br /> <br />21 May, the first two samples (29 and 50 min samples, respectively) collected from Net 1 in <br /> <br />Breach 3 after release of particles contained 129 beads and one bead, respectively. Those same <br /> <br />samples contained 82 and one razorback sucker larvae, respectively. However, there were <br /> <br />obvious inconsistencies in fish captures, based on numbers of larvae captured in samples <br /> <br />collected side by side at similar times. Such inconsistencies made us cautious and prevented <br /> <br />further interpretation of any fish entrainment data. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />46 <br /> <br />. <br />