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Water Quality of Fountain and Monument Creeks
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Water Quality of Fountain and Monument Creeks
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Last modified
7/20/2010 3:28:51 PM
Creation date
6/28/2010 4:38:34 PM
Metadata
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Template:
Water Supply Protection
Description
ARCA
State
CO
KS
Basin
Arkansas
Water Division
2
Date
1/1/1990
Author
U.S. Department of the Interior, U.S. Geologic Survey, Colorado Springs Department of Utilities, Lower Fountain Water-Quality Management Association, Patrick Edelmann
Title
Water Quality of Fountain and Monument Creeks
Water Supply Pro - Doc Type
Report/Study
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009 <br />Monthly variations in <br />M10 and M28 are summarized <br />smaller during April, May, <br />occurs during August and Si <br />ever, the largest specific <br />on the sources of flow. <br />the specific conductance of Monument Creek at sites <br />in figure 22. Median specific conductance is <br />and June. The largest median specific conductance <br />�ptember at site M10 and in August at site M28; how - <br />conductance may occur during any season depending <br />pH <br />The pH of Monument Creek varies considerably at each of the four sites <br />where measurements have been made; however, all measurements were within the <br />acceptable range of 6.5 to 9.0 (fig. 23). The median pH increased from 7.5 <br />at site M10 to 8.0 at site M34, which is located about 2 mi upstream from the <br />confluence with Fountain Creek. The increase may result from ground -water <br />discharge or drainage of alkaline materials that enter the stream from urban- <br />ized areas. At the measured levels of pH, most trace elements are relatively <br />insoluble in this well- oxygenated stream. However, manganese, selenium, and <br />zinc are fairly soluble at the pH levels measured on Monument Creek. <br />Five -Day Biochemical Oxygen Demand <br />Except for site M35, the BOD5 measured on Monument Creek was less than <br />4 mg /L for more than 50 percent of the time samples were collected, indicating <br />that small quantities of biochemically oxidizable material were present in the <br />stream. The BOD measured on Monument Creek is summarized in figures 24 and <br />25. Between 1975 and 1983, B0D generally increased downstream (fig. 24) <br />because more oxidizable material was present in the stream, probably because <br />of discharge from wastewater - treatment plants and from nonpoint sources trans- <br />ported to the stream by runoff. <br />A slight increase in median BOD5 occurred from 1975 through 1979, between <br />sites M28 and M34 and, from 1980 through 1983, between sites M28 and M35 <br />(fig. 25). In addition, the B0D5 measured from 1980 through 1983 was consid- <br />erably larger than concentrations measured from 1975 through 1979, indicating <br />there was more biochemically oxidizable material in the stream from 1980 <br />through 1983 than from 1975 through 1979 (fig. 25). <br />Dissolved Oxygen <br />Dissolved - oxygen concentrations were measured in Monument Creek during <br />the daylight hours. Dissolved - oxygen concentrations frequently exhibit diel <br />variations, and the largest concentrations occur during daylight as a result <br />of photosynthesis. Thus, the dissolved- oxygen concentrations measured in <br />Monument Creek are likely to be greater than the minimum daily dissolved - <br />oxygen-concentration (fig. 26). Since 1975, all dissolved- oxygen measurements <br />made on Monument Creek, except for one measurement at site M34, have been <br />greater than the recommended standard of 5.0 mg /L. The large velocities and <br />shallow depths keep the stream well oxygenated. <br />37 <br />
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