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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 />009~ <br /> <br />Monthly variations in the specific conductance of Monument Creek at sites <br />M10 and M28 are summarized in figure 22. Median specific conductance is <br />smaller during April, May, and June. The largest median specific conductance <br />Occurs during August and September at site M]O and in August at site M28; how- <br />ever, the largest specific conductance may Occur during any season depending <br />on the sources of flow. <br /> <br />pH <br /> <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 M]O 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 /> <br />Five-Day Biochemical Oxygen Demand <br /> <br />Except for site M35, the BODs 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 BODs measured on Monument Creek is summarized in figures 24 and <br />25. Between ]975 and ]983, BODs 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 /> <br />A slight increase in median BODs occurred from ]975 through 1979, between <br />sites M28 and M34 and, from ]980 through ]983, between sites M28 and M35 <br />(fig. 25). ln addition, the BODs measured from ]980 through ]983 was consid- <br />erably larger than concentrations measured from 1975 through ]979, indicating <br />there was more biochemically oxidizable material in the stream from ]980 <br />through ]983 than from ]975 through ]979 (fig. 25). <br /> <br />Dissolved Oxygen <br /> <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 ]975, 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 /> <br />37 <br />
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