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reports. The frequency column on Table 10 indicates the number of <br />exceedences out of the total number of samples (i.e., 1/2 indicates one <br />exceedence out of two samples). Below is a summary of standards that <br />were exceeded. Given in parenthesis is the source and use of each <br />standard. Although the CDOH does not indicate between livestock and <br />irrigation uses in their surface water agricultural standards, they have <br />done so in their similar ground water agricultural standards (see Table <br />5). For the sake of discussion, SCC chooses to use those ground water <br />use standards classifications (livestock or irrigation) for surface <br />water use evaluation. Of all the surface water sites downstream of <br />Seneca II-W, only Sites WSDS (Dry Creek), WSSF3 (Sage Creek), WSH7 (mid- <br />Hubberson Gulch) and WSHF1 {lower Hubberson Gulch) have their waters <br />used for irrigation. Following is a list of standards exceeded this <br />year. <br />Parameter # of Sites / # of Excursions <br />manganese (CDOH, SW, irrigation) 5/8 <br />Review of this list indicates that only one CDOH surface water <br />agricultural use standards was exceeded. The manganese standard was <br />exceeded at five sites. However, as noted previously in the ground water <br />discussion, the relatively low CDOH standard o£ 0.2 mg/1, according to <br />the EPA, applies to plants grown in acidic soils. In alkaline soils, as <br />are found in the Seneca II-W region, a more appropriate (EPA) standard <br />would be 10 mg/1. The maximum manganese value for any surface water site <br />observed this year was 1.22 mg/I. Premining manganese values often <br />exceeded the 0.2 mg/1 standard. <br />Table 11 shows the CDOH receiving stream standards for Sage and Dry <br />Creeks (Yampa Segment 13d). Table 12 provides a comparison of those <br />standards to water quality data collected this year from NPDES and <br />stream sites in those basins. Standards that were exceeded (excluding <br />ammonia and sulfide) are: <br />r'1 <br />LJ <br /> <br />I <br />20 <br />