4-06CW230 Anthracite Creek Supplemental Data

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Land Status Review Upper Terminus Lower Terminus Total Length (miles) Land Ownership % Private % Public Ruby Anthracite Creek Coal Creek 8.0 49% 51 % 51% of the reach is located on public lands and 49% of the reach is located on private lands. Biological Data The CDOW has conducted field surveys of the fishery resources on this stream and have found a natural environment that can be preserved. As reported in the letter from the CDOW to the CWCB "Anthracite Creek is classified as a river (between 60 to 99 feet wide) and fishery surveys indicate the stream environment of Anthracite Creek supports a self - sustaining brown and rainbow trout fishery. Anthracite Creek also supports populations of mottled sculpins, dace and bluehead suckers" (See CDOW Fish Survey in Appendix B). Field Survey Data CDOW staff used the R2CROSS methodology to quantify the amount of water required to preserve the natural environment to a reasonable degree. The R2CROSS method requires that stream discharge and channel profile data be collected in a riffle stream habitat type. Riffles are most easily visualized, as the stream habitat types that would dry up first should streamflow cease. This type of hydraulic data collection consists of setting up a transect, surveying the stream channel geometry, and measuring the stream discharge. Appendix B contains copies of field data collected for this proposed segment. Biological Flow Recommendation The CWCB staff relied upon the biological expertise of the cooperating agencies to interpret output from the R2CROSS data collected to develop the initial, biologic instream flow recommendation. This initial recommendation is designed to address the unique biologic requirements of each stream without regard to water availability. Three instream flow hydraulic parameters, average depth, percent wetted perimeter, and average velocity are used to develop biologic instream flow recommendations. The CDOW has determined that maintaining these three hydraulic parameters at adequate levels across riffle habitat types, aquatic habitat in pools and runs will also be maintained for most life stages of fish and aquatic invertebrates (Nehring 1979; Espegren 1996). For this segment of stream, three data sets were collected with the results shown in Table 1 below. Table 1 shows who collected the data (Party), the date the data was collected (Date), the measured discharge at the time of the survey (Q), the accuracy range of the predicted flows based on Manning's Equation (240% and 40% of Q), the summer flow recommendation based on meeting 3 of 3 hydraulic criteria and the winter flow recommendation based upon 2 of 3 hydraulic criteria.