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2013-04-18_PERMIT FILE - C2009087A
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2013-04-18_PERMIT FILE - C2009087A
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Last modified
11/30/2016 9:55:16 AM
Creation date
5/1/2013 12:34:12 PM
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Template:
DRMS Permit Index
Permit No
C2009087A
IBM Index Class Name
Permit File
Doc Date
4/18/2013
Doc Name
Hydrology Description
Section_Exhibit Name
2.04.7 Hydrology Description
Media Type
D
Archive
Yes
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RULE 2 - PERMITS <br />• CDPHE surface water agricultural use standard of 0.2 mg/L at sites SSG1 (0.32 mg/L), SSG2 (0.25 <br />mg/L), YSG5 (0.24 mg/L), and YSGF5 (0.25 mg/L). Peak concentrations additionally exceeded the <br />agricultural standard at all three NPDES outfalls, and NPDES3's average concentration (0.68 mg/L) <br />exceeded the standard. However, as stated previously, this standard does not apply, since soil pH's in <br />this area are generally above 6.0. The trend of increasing manganese concentration in Grassy Creek <br />from upstream (YSGF5) to just above the Little Grassy Creek confluence (SSG1), followed by a <br />decrease at SSG2, located below Little Grassy Creek and NPDES3, suggests that naturally elevated <br />levels in Grassy Creek are diluted by those in Little Grassy Creek, despite the additional load from the <br />existing NPDES outfalls. <br />Little Grassy Creek, at site SSLG5, exhibited slightly elevated levels of nitrite and selenium not <br />observed at other monitoring sites. These are due to natural conditions. Average nitrite concentrations <br />exceeded the 0.05 mg/L CDPHE Yampa River Segment Be (Grassy Creek) aquatic life standard at <br />SSLG5 (0.06 mg/L average, 0.09 mg/L peak), peak concentrations slightly exceeded the standard once <br />at SSG1 (0.06 mg/L). Exceedances at SSLG5 are suspected to be due to naturally occurring upstream <br />conditions. The effects were diluted at SSG2, which had uniformly low levels. Peak selenium <br />concentrations (8.1 ug/L) were also elevated above the Segment Be (Grassy Creek) aquatic life <br />chronic standard (4.6 ug/L) at SSLG5, but did not exceed the acute (18.4 ug/L) or agricultural use (20 <br />ug/L) standards. <br />Average sulfide concentrations reported in the tables are influenced by the use of the detection limit <br />(0.02 mg/L) in cases where the laboratory reported (<0.02 mg/L). Hence, any apparent exceedance of <br />Yampa River water quality standards (0.002 mg/L un- ionized; set to the 0.02 mg/L detection limit) is <br />• spurious when comparing average values. In addition, values up to 0.06 mg/L, while reported at some <br />stations, were flagged by the laboratory as uncertain. The only elevated sulfide measurements <br />considered reliable were two at NPDES4, measured as 0.12 and 0.33 mg/L. The analytical method <br />available to Seneca Coal Company detects both dissolved sulfides and acid - soluble metallic sulfides <br />present in suspended matter. It is suspected that a large portion of the sulfides detected are of the latter <br />type, which would bias the un- ionized results high. Any dissolved sulfides present in surface water <br />should eventually oxidize to sulfates. <br />Mercury levels were influenced by detection limits in a similar fashion to sulfide. While the Yampa <br />River standard is 0.01 ug/L, the detection limit used in this report is 0.2 ug/L or greater for springs and <br />streams. All stream samples were reported as less than 0.2 ug/L, except for 4/5/07 sample at SSG2, <br />which was reported as less than 1.0 ug/L, and the 4/23/09 sample at YSGF5, which was reported as <br />less than 0.4 ug/L. Thus, all of the reported mercury concentrations are spurious for stream sampling <br />points. Impoundments are subject to different, and lower, detection limits. Like streams, all but one of <br />the reported impoundment mercury concentrations were "less than" values, and thus do not actually <br />represent exceedance of a standard. One sample, 2/5/07 at NPDES4, was reported as 0.023 ug/L, <br />which does represent a single exceedance. <br />The trilinear diagrams for Grassy Creek and Little Grassy Creek are shown on Figures 2.04.7 -F16 <br />through Figure 2.04.7 -F19.1 YSG5 was historically only monitored for TDS, field params and <br />occasionally for iron, but has recently (3 samples) been sampled for the full suite of water quality <br />params. YSG5 therefore has a limited period of record as compared to the other stations. Three of the <br />• five sites (SSG1, SSG2, and SSLG5) are of a calcium- sodium cation type, with high magnesium and <br />mixed anions (chloride - sulfate- bicarbonate). Water at YSGF5, the most upstream station on Grassy <br />Creek, and at YSG5, the most downstream station on Grassy Creek, alternates between <br />PSCM Permit App. 2.04 -76 Revision 12/17/09 <br />
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