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Selenium 1/1 9 <br />All iron excursions were the result of high suspended solids. None of <br />the iron excursions were at a NPDES site. <br />One sample from NPDES8 exceeded the chronic selenium standard, 4.6 ug/1, <br />with a value of 7.1 ug/l, but not the acute standard, 18.4 ug/1. <br />In September 2003, the CDPHE resegmented Grassy Creek from Yampa Segment <br />12 to Segment 13e. Regulation 33 was further revised in December 2005 <br />and August 2008. Table 15 shows the new CDPHE receiving stream standards <br />for Grassy Creek. Table 16 provides a comparison of those standards to <br />water quality data collected this year from NPDES and stream sites in <br />the Grassy Creek basin. Standards that were exceeded are: <br />Parameter # of Sites / # of Excursions <br />Iron, Total Rec. 3/4 <br />Nitrite 1/1 <br />Selenium 1/1 <br />Sulfide 2/4 <br />All iron excursions were the result of high suspended solids. None of <br />the iron excursions were at a NPDES site. The two stream sites that <br />experienced excursions are upstream of Seneca's discharges. <br />One stream site, SSLG5, exceeded the nitrite standard. This site is <br />upstream of the Seneca II mining area. Nitrites are unstable in aerated <br />water and will oxidize into nitrates (Hem, 1989). This same site <br />exceeded the chronic selenium standard. <br />Three samples from NPDES3 experienced exceedances of the sulfide <br />standard (0.002 mg/l un-ionized), as well as one sample from Site SSG2. <br />i <br />The analytical method available to SCC detects both dissolved sulfides <br />and acid-soluble metallic sulfides present in suspended matter. It is <br />suspected that a large portion of the sulfides detected is of the latter <br />i20 <br /> <br />