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WSP02139
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Last modified
1/26/2010 12:34:49 PM
Creation date
10/11/2006 10:56:33 PM
Metadata
Fields
Template:
Water Supply Protection
File Number
8170
Description
Arkansas Basin Water Quality Issues
State
CO
Basin
Arkansas
Water Division
2
Date
1/1/1990
Author
USGS
Title
Water Quality of Fountain and Monument Creeks - South-Central Colorado - with emphasis on Relation of Water Quality to Stream Classifications
Water Supply Pro - Doc Type
Report/Study
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<br />0091 <br /> <br />Dissolved Oxygen <br /> <br />When considerable oxygen demand is present in a stream such as Fountain <br />Creek, dissolved oxygen may be substantially depleted while digestive proces- <br />ses are occurring. However, the dissolved-oxygen concentrations, which were <br />measured in Fountain Creek during the daylight hours and, therefore, are <br />likely to be somewhat larger than the minimum daily dissolved-oxygen concen- <br />tration, indicate that the stream generally is well oxygenated (fig, 16), <br />Since 1975, only four dissolved-oxygen measurements were less than the recom- <br />mended standard of 5,0 mg/L for Lower Fountain Creek. The stream remains well <br />oxygenated probably because of large reaeration rates that result from large <br />velocities and shallow depths in Fountain Creek, <br /> <br />Monthly variations in dissolved-oxygen concentrations of Fountain Creek <br />at sites F12, F17, and F36 are summarized in figure 17, Because dissolved- <br />oxygen concentration is inversely related to water temperature, the smallest <br />dissolved-oxygen concentrations of Fountain Creek occur during July and August <br />when water temperatures are warmest and biological decomposition is greatest <br />(fig, 11); the largest dissolved-oxygen concentrations occur during December <br />and January when water temperatures are coldest and biological decomposition <br />is least, <br /> <br />Suspended Solids <br /> <br />The suspended-solids concentrations at nine sites along Fountain Creek <br />from 1975 through 1983 are summarized in figure l8A, and suspended-solids <br />concentrations from 1980 through 1983 are summarized in figure l8B, Down- <br />stream variations in suspended-solids concentrations are better represented <br />in figure l8B because the period of record and the number of measurements are <br />more similar between sites. <br /> <br />The suspended-solids concentrations measured on Fountain Creek upstream <br />from the confluence with Monument Creek have been small because of the pres- <br />ence of nonerosive igneous and metamorphic rocks, the cobbled-bed channel, <br />and the shallow soils in the Upper Fountain Creek basin, The small concen- <br />trations of suspended solids result in a clear stream, which adds to the <br />aesthetic quality, However, suspended-solids concentrations rapidly increase <br />downstream from the confluence with Monument Creek primarily as the result of <br />Monument Creek inflow, as indicated by data collected at site F17, Suspended- <br />solids concentrations decreased from site F17 to site FI9 because of dilution <br />from the Colorado Springs Wastewater Treatement Plant effluent, The median <br />suspended-solids concentration (1980-83) decreased from 156 mg/L at site F17 <br />to 89 mg/L at site FI9 (fig. l8B), which is located about 2 mi downstream from <br />the wastewater-treatment plant outfall. However, the resulting increase in <br />streamflow from the effluent re-entrains sediments that have been deposited <br />in the stream channel downstream as the result of tributary inflows, which <br />increases the suspended-solids concentrations downstream from site F20 <br />(fig, l8B) , <br /> <br />29 <br />
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