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WSP10317
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Last modified
1/26/2010 2:58:17 PM
Creation date
10/12/2006 4:15:59 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8200.760
Description
Yampa River General
State
CO
Basin
Yampa/White
Water Division
6
Date
12/5/1976
Author
USGS
Title
Surface-Water Quality in the Yampa River Basin - Colorado and Wyoming - An Area of Accelerated Coal Development
Water Supply Pro - Doc Type
Report/Study
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<br />002850 <br /> <br />from the entire Yampa River basin was estimated at nearly 406,000 tons <br />(368,000 t) per year. Recent calculations by the authors indicate that the <br />historical long-term load during the 1951-74 water years was approximately <br />450,000 tons (404,000 t) annually, or perhaps 10 percent higher than the esti- <br />mates of Iorns, Hembree, and Oakland (1965). In either case, about 5 percent <br />of the dissolved-solids load of the upper Colorado River basin is contributed <br />by the Yampa River basin (Iorns and others, 1965, fig. 8). <br /> <br />. <br /> <br />TRACE ELEMENTS AND PH <br /> <br />During the August-September 1975 reconnaissance, water samples were col- <br />lected at all sites for determination of selected trace elements in dissolved <br />and total phases (Steele and others, 1976a, p.13). Bottom-sediment samples <br />for trace-element determinations were obtained at only 48 of the 82 sites, <br />because bed materials were prohibitively large at the remaining sites. Se- <br />lected results of trace-element and pH determinations are discussed in this <br />paper; a more detailed discussion is given in the expanded technical report. <br /> <br />Frequency distributions of dissolved and total trace elements in streams <br />of the Yampa River basin were typically positively skewed as shown by the to- <br />tal Se example in figure 9A. This is the case for all except dissolved Cu <br />and total Zn, which are more symmetrical (see, for example, fig. 9B). <br /> <br />Stream sites with one or more anomalous water-quality characteristics were <br />determined by analyzing the various frequency distributions and separating the <br />outliers (indicating perturbed areas) from the distributions representative of <br />ambient or unperturbed conditions. For example, the concentrations of 71 ~g/L <br />total Se in figure 9A and 550 ~g/L dissolved Cu in figure 9B were found by <br />this analysis to be outliers. <br /> <br />Using the above techniques, four sites were found to have anomalously <br />high total or dissolved trace-element concentrations. These sites are Y-26 <br />(5 outliers), Y-46 (4 outliers), Y-54 (2 outliers), and Y-68 (7 outliers) <br />(see fig. 1). If Fe and Mn are deleted from the outlier analysis, three <br />sites remain; these are Y-26 (5 outliers), Y-46 (4 outliers), and Y-68 (3 out- <br />liers). The rationale for deleting Fe and Mn is discussed in the expanded <br />technical report. <br /> <br />Site Y-68 (known also as the Oak Creek Drain) appears to be an abandoned <br />drainage tunnel and is the only known site in Colorado affected by the oxida- <br />tion of pyritic materials associated with coal (Wentz, 1974a). Water issuing <br />from the drain deposits a bright-orange coating of ferric hydroxide (yellow <br />boy) on the channel bottom between the tunnel and Oak Creek. In addition to <br />total and dissolved Fe and Mn, total Cd and dissolved Co and Ni were found to <br />be present at anomalously high concentrations in August-September 1975. <br />There appears to have been enough dilution from Oak Creek so that the latter <br />three constituents are not a problem at Y-67, the next site downstream on Oak <br />Creek. Previous chemical data reported by Wentz (1974a) and Moran and Wentz <br />(1974) indicate that Cu, Pb, and V also may occur at relatively high concen- <br />trations in the drain at certain times of the year, but that downstream <br />effects on Oak Creek are minima~. <br /> <br />16 <br /> <br />, <br />Ii <br /> <br />11. ~ <br />
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