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Last modified
1/26/2010 2:49:28 PM
Creation date
10/12/2006 3:14:26 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8170
Description
Arkansas Basin Water Quality Issues
State
CO
Basin
Arkansas
Water Division
2
Date
1/1/1993
Author
USGS
Title
Reconnaissance of Water Quality of Lake Henry and Lake Meredith Reservior - Crowley County - Southeastern Colorado - April-October 1987
Water Supply Pro - Doc Type
Report/Study
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<br /> 0053 <br /> Table 10. Light-transparency measurements lor all sites at <br /> Lake Meredith <br /> Samplng site Sampling date, Secchl- <br /> disk depth' <br /> <Ilg.3) 1987 (leel) <br />" <br /> M2Bl 05-01 1.5 <br /> 06-30 .5 <br />. 08-20 .5 <br /> 10-06 .5 <br /> MIB 05-01 1.5 <br /> 06-30 .5 <br /> 08-20 1.0 <br /> M4B 05-01 1.0 <br />I 06-30 .5 <br /> 08-21 .5 <br /> MIA 06-30 .5 <br /> 08.20 1.0 <br /> MIC 06-30 .5 <br /> 08-20 1.0 <br /> M2A 06-30 .5 <br /> 08-20 1.0 <br /> M2C 06-30 .5 <br /> 08-20 1.0 <br /> M3A 06-30 .5 <br /> 08-21 1.0 <br /> M3B 06-30 .5 <br /> 08-21 1.0 <br /> M4A 06-30 .5 <br /> 08-21 .5 <br /> ILight transparency represents lhe depth to the nearest <br /> 0.5 fool at which the Secchi disk was not visible. <br /> 2M2B was the only site measured on October 6. 1987. <br /> <br />Chemical Constituents <br /> <br />I <br />i) <br /> <br />l <br /> <br />During the sampling period, concentrations of <br />total nitrogen al sile M2B ranged from less than <br />1.3 mgIL to less than 2.0 mgIL and averaged less than <br />about 1.6 mgIL (table 19). The principal nitrogen form <br />was organic nitrogen, which averaged about 90 percent <br />of the total nitrogen. The concentrations of total- <br />inorganic nitrogen were less than 0.2 mgIL throughout <br />the sampling period. <br />The Colorado Department of Health (1987) has <br />established water-quality standards for aquatic life of <br />0.5 mgfL of total nitrite and 0.06 mgIL of un-ionized <br />ammonia for Lake Meredith. Concentrations of total <br />nitrite at sites M2B, M I B, and M4B ranged from 0.001 <br />to 0.022 mgfL (tables 19-21). Un-ionized ammonia is <br />calculated as a percentage of total ammonia, given <br /> <br />water temperature and pH (Willingham, 1976), and <br />concentrations ranged from 0.003 to 0.031 mgfL at <br />sites M2B, M1B, and M4B. <br /> <br />Concentrations of total phosphorus at sites M2B. <br />M 1 B, and M4B ranged from 0.062 to 0.148 mgfL and <br />averaged 0.106 mg!I... Orthophosphate as phosphorus <br />(the biologically available form of phosphorus) aver- <br />aged about 14 percent of the total phosphorus. <br /> <br />During the sampling period, concentrations of <br />dissolved-inorganic nitrogen at site M2B were greater <br />than 0.02 mg!I.. indicating nitrogen was not a limiting <br />nutrient (Ryding, 1988). Concentrations of dissolved <br />orthophosphate as phosphorus at site M2B were less <br />than 0.010 mg!I.. on May I, June 30, and August 20 <br />indicating potential phosphorus limitation (Ryding. <br />1988). On October 6, the average dissolved orthophos- <br />phate as phosphorus concentration was 0.022 mgfL <br />indicating phosphorus was not a limiting nutrient. <br /> <br />The mass ratio of dissolved-inorganic nitrogen to <br />dissolved orthophosphate as phosphorus was greater <br />than 7; I on the May, June, and August sampling dates <br />(table II) indicating potential phosphorus limitation <br />(Ryding, 1988). On the October sampling date, the <br />mass ratio of dissolved-inorganic nitrogen to dissolved <br />orthophosphate as phosphorus was less than 7; I indi- <br />cating potential nitrogen limitation (Ryding. 1988). <br /> <br />Dissolved-solids concentrations at site M2B <br />ranged from 1,870 to 2,370 mgIL and were smallest on <br />June 30 and largest on October 6 (table 19). As indi- <br />cated by samples collected at site M2B near the lake <br />surface and near the lake bottom and from specific- <br />conduclance measurements made at the other sites in <br />Lake Meredith, no substantial vertical or areal varia- <br />tions in dissolved solids occurred on the sampling <br />dates. Dissolved-solids concentrations (in mgIL) in <br />Lake Meredith can be approximated from specific- <br />conductance measurements, as indicated from eight <br />samples collected at site M2B during the sampling <br />period, by multiplying the specific-conductance mea- <br />surement by 0.76. <br /> <br />Based on analysis of eight water samples col- <br />lected at site M2B, the predominant cation in Lake <br />Meredith is sodium and the predominant anion is sul- <br />fate. Sodium averaged about 47 percent of the cations. <br />and sulfate averaged about 83 percent of the anions (as <br />milliequivalents per liter). <br /> <br />The Colorado Department of Health has not <br />eSlablished water-quality standards for the major <br />chemical constituents for water use from Lake <br />Meredith. However. dissolved-solids concentrations <br />and the percentage of individual cations and anions are <br />important factors in water used for agricultural pur- <br />poses as discussed for Lake Henry. <br /> <br />WATER-QUALlTY CHARACTERISTtCS OF LAKE MEREDITH AND COMPARtSON TO WATER.QUALITY STANDARDS 25 <br />
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