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<br />. <br /> <br />. <br /> <br />. <br /> <br />Miguel River near Ames. Dissolved levels of heavy metals in the Howard's Fork continue to be <br />a problem for the river's fishery but conditions may be improving. Protection of the high quality <br />water in the headwaters and all of the tributaries of the Howard's Fork is vital to the continued '- <br />improvements we are seeing in both water quality and fish populations. <br /> <br />Field Survey Data <br /> <br />CDOW and CWCB staff used the R2Cross methodology to quantify the amount of water <br />required to preserve the natural environment to a reasonable degree. The R2Cross method <br />requires that stream discharge and channel profile data be collected in a riffle stream habitat type. <br />Riffles are most easily visualized as the stream habitat types that would dry up first should <br />streamflow cease. This type of hydraulic data collection consists of setting up a transect, <br />surveying the stream channel geometry, and measuring the stream discharge. Appendix B <br />contains copies of field data collected for this proposed segment. <br /> <br />Biological Flow Recommendations <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 CDOW 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 these segments of stream, three data sets were collected with the results shown in Table 1 <br />below. 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 />DOW ICWCB 10109/96 2.22 5.5 -0.9 5.6 1.5 <br />DOW/CWCB 10/09/96 14.8 37.0 - 5.9 4.6~1) 2.5~I) <br />DOW/CWCB 10/09/96 11.2 28.0- 4.5 8.3 3.5(1) <br /> . . <br /> <br />BLM = Bureau of Land Management DOW = DIVISIOn of WIldhfe <br />(I) Predicted flow outside of the accuracy range of Manning's Equation. <br /> <br />CWCB = Colorado Water ConservatIOn Board <br />? = Criteria never met in R2CROSS Staging Table. <br /> <br />Biologic Flow Recommendations . <br />The CD OW recommended a 5.6 cfs summer flow and a 1.5 cfs winter flow for the upper <br />segment and a 8.3 cfs summer flow and a 3.0 cfs winter flow for the lower segment based on the <br />October 9th, 1996, data collection efforts. Staff reviewed the data collected by the CDOW. The <br />summer flow recommendation for the upper reach, which meets 3 of 3 criteria and is within the <br />accuracy range of the R2CROSS model is 5.6 cfs. The winter flow recommendation for the <br />upper reach which meets 2 of 3 criteria and is within the accuracy range of the R2CROSS model <br />is 1.5 cfs (See Table 1). The summer flow recommendation for the lower reach, which meets 3 of <br />3 criteria and is within the accuracy range of the R2CROSS model is 8.3 cfs. The winter flow <br />recommendations which meet 2 of 3 criteria both fall outside of the accuracy range of the <br /> <br />- 5 - <br />