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<br />Biological Data <br /> <br />The Division of Wildlife has conducted surveys of the fishery resources on this stream and have <br />found a natural environment that can be preserved. As reported for this reach of stream in the <br />BLM letter to the CWCB " The existence of a natural environment and cold water salmonid <br />fishery was established in Case No 3-76W3645. For reference we have. attached a fishery <br />survey from the Division of Wildlife, which profiles the brown trout fishery" (See BLM Fish <br />Survey in Appendix B). <br /> <br />Field Survey Data <br /> <br />BLM staff used the R2Cross methodology to quantify the amount of water required to preserve <br />the natural environment to a reasonable degree. The R2Cross method requires that stream <br />discharge and channel profile data be collected in a riffle stream habitat type. Riffles are most <br />easily visualized, as the stream habitat types that would dry up first should streamflow cease. <br />This type of hydraulic data collection consists of setting up a transect, surveying the stream <br />channel geometry, and measuring the stream discharge. Appendix B contains copies of field <br />data collected for this proposed segment. <br /> <br />Biological Flow Recommendation <br /> <br />The CWCB staff relied upon the biological expertise of the cooperating agencies to interpret <br />output from the R2Cross data collected to develop the initial, biologic instream flow <br />recommendation. This initial recommendation is designed to address the unique biologic <br />requirements of each stream without regard to water availability. Three instream flow hydraulic <br />parameters, average depth, percent wetted perimeter, and average velocity are used to develop <br />biologic instream flow recommendations. The CD OW has determined that maintaining these <br />three hydraulic parameters at adequate levels across riffle habitat types, aquatic habitat in pools <br />and runs will also be maintained for most life stages of fish and aquatic invertebrates (Nehring <br />1979; Espegren 1996). <br /> <br />For this segment of stream, 5 data sets were collected with the results shown in Table 1 below. <br />Table 1 shows who collected the data (Party), the date the data was collected (Date), the <br />measured discharge at the time of the survey (Q), the accuracy range of the predicted flows <br />based on Manning Equation (240% and 40% of Q), the summer flow recommendation based on <br />meeting 3 of 3 hydraulic criteria and the winter flow recommendation based upon 2 of 3 <br />hydraulic criteria. <br /> <br />Table 1: Data <br /> <br />Party Date Q 250%-40% Summer (3/3) Winter (2/3) <br />BLM 8/2312001 9.48 23.7 -3.8 3.1 tl) 2.7U) <br />BLM 5/3012002 3.08 7.7 - 1.2 5.4 1.0t!) <br />BLM 5/3012002 3.19 8.0 - 1.3 3.6 0.6P) <br />BLM 8/0812002 1.73 4.3 -0.7 2.5 2.5 <br />BLM 8/08/2002 1.95 4.9 - 0.8 2.4 1.7 <br /> <br />BLM = Bureau of Land Management DOW = Division of Wildlife <br />(I) Predicted flow outside of the accuracy range of Manning's Equation. ? = Criteria never met in R2CROSS Staging Table. <br /> <br />Biologic Flow Recommendation <br />The summer flow recommendations, which met 3 of 3 criteria and are within the accuracy range <br />of the R2CROSS model range from 5.4 cfs to 2.4 cfs (See Table 1). The winter flow <br />recommendations, which met 2 of 3 criteria and are within the accuracy range of the R2CROSS <br />model range from 2.5 cfs to 1.7 cfs (See Table 1). Averaging the four summer flow <br />- 3 - <br />