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<br />ranged from 8.110 8.6 during the sampling period. Dis- <br />solved-oxygen concentrations and pH were largest <br />near the lake surface as a result of photosynthesis and <br />smallest near the lake bottom, where respiration <br />occurs. Specific conductance in Lake Henry ranged <br />from 8891IS/cm on June 29 to 1,010 lIS/cm on October <br />6 but did not vary vertically and areally in the lake. Sec- <br />chi-disk measurements indicated unifonn light trans- <br />parency throughout the lake. On May I, Secchi-disk <br />depths were 1.5 ft, and during the remainder of the <br />study period Secchi-disk depths were 0.5 ft. Light <br />transparency in Lake Henry is affected by phytoplank- <br />ton biomass and nonalgal suspended material. <br />Total-nitrogen concentrations ranged from 0.86 <br />to 1.4 mgIL, and total-phosphorus concentrations <br />ranged from 0.030 to 0.106 mg/L during the sampling <br />period. Dissolved-solids concentrations ranged from <br />598 to 704 mg/L, and calcium and sulfate comprised <br />the largest percentage of the major chemical constitu- <br />ents. At site HEW2, concentrations of total- <br />recoverable iron occasionally exceeded the Colorado <br />Department of Health water-quality standard of <br />1.000 IJgIL. On August 19, total-recoverable iron con- <br />centrations were 1,000 1Ig/L near the lake surface and <br />6,300 IJgIL near the lake bottom; on October 6, concen- <br />trations of total-recoverable iron were 1,900 1Ig/L near <br />the lake surface and 2,500 lIglL near the lake bollom. <br />Concentrations of other trace elements were less than <br />the water-quality standards or less than the detection <br />limits for the analysis. <br />The groups of phytoplankton sampled in Lake <br />Henry during the sampling period were diatoms, green <br />algae, golden-brown algae, cryptomonads, blue-green <br />algae, and euglenoids. The concentrations of phy- <br />toplankton collected at site HEW2 ranged from 33,000 <br />cells/mLon June 29to 930,OOOcells/mL on August 19. <br />On each sampling date, blue-green algae accounted for <br />the greatest percentage of the phytoplankton density. <br />The trophic status of Lake Henry is eutrophic as indi- <br />cated by the trophic-state index and the fixed-boundary <br />system. <br />During the sampling period, water temperatures <br />in Lake Meredith ranged from 15.3 to 27.90C. The lake <br />was thermally stratified on May I and was not stratified <br />on June 30. Concentrations of dissolved oxygen <br />ranged from 1.4 to 10.3 mgIL. CDncentrations of dis- <br />solved oxygen less than the 5.0 mg/L water-quality <br />standard were measured near the lake bollom on <br />May I, June 30, and August 20 and 21. The pH of the <br />water in Lake Meredith ranged from 7.9 tD 8.7. Dis- <br />solved-Dxygen cDncentrations and pH in Lake <br />Meredith were largest near the lake surface as a result <br />of photosynthesis and smallest near the lake bollom <br /> <br />where respiratiDn occurs. Specific cDnductance in the <br />lake ranged from 2,520 lIS/cm on June 30 tD 3,040 lIS/ <br />cmon August21 but did not vary vertically and areally. <br />Secchi-disk measurements ranged frDm 0.5 to 1.5 ft <br />and were largest on May I. Light transparency in Lake <br />Meredith is affected by phytoplankton biomass and <br />nonalgal suspended material. <br />Concentrations of total nitrogen at site M2B <br />ranged from less than 1.3 mg/L to less than 2.0 mgIL <br />during the sampling period. At sites M2B, M1B, and <br />M4B, concentrations of total phosphorus ranged from <br />0.062 to 0.148 mg/L. Dissolved-solids concentrations <br />at site M2B ranged from 1,870 tD 2.370 mg/L, and <br />sDdium and sulfate comprised the largest percentage of <br />the major chemical constituents. At sites M1B and <br />M4B on June 30 and August 21, concentrations Df <br />total-recDverable iron ranged frDm 1,300 to <br />1,800 lIglL, which exceeded the 1,000 1Ig/L Colorado <br />Department of Health water-quality standard. Concen- <br />trations of total-recoverable boron at site M2B on <br />August 20 and October 6 ranged from 770 to 810 lIg/L, <br />which exceeded the 750 1Ig/L water-quality standard. <br />Concentrations of other trace elements were less than <br />the water-quality standards or less than the detection <br />limits for the analysis. <br />The groups of phytoplankton sampled at site <br />M2B during the sampling period were diatoms, green <br />algae, golden-brown algae, cryptomonads, blue-green <br />algae, euglenoids, and dinoflagellates. The concentra- <br />tions of phytoplankton collected at site M2B ranged <br />from 58,000 cells/mL on May 1 to 3,900,000 cells/mL <br />on October 6. On each sampling date, blue-green algae <br />comprised the largest percentage of the phytDplankton <br />density. The trophic status of Lake Meredith as deter- <br />mined using the trophic-state index and the fixed- <br />boundary system indicates Lake Meredith is a <br />eutrophic lake. <br />During the sampling period, the thennal proper- <br />ties of Lake Henry and Lake Meredith were similar. <br />Dissolved-oxygen concentrations and pH values in <br />Lake Henry and in Lake Meredith were larger near the <br />lake surface and smaller near the lake bollom because <br />of the effect of photosynthesis and respiration by phy- <br />toplankton. Average specific conductance in Lake <br />Henry was about one-third the average specific con- <br />ductance in Lake Meredith. <br />Nutrient concentrations varied between Lake <br />Henry and Lake Meredith. Nutrient concentrations <br />were generally smaller in Lake Henry than in Lake <br />Meredith. The predominant chemical constituents <br />were calcium and sulfate in Lake Henry and sodium <br />and sulfate in Lake Meredith. Concentrations of total- <br />recoverable iron in Lake Henry and total-recoverable <br />iron and total-recoverable boron in Lake Meredith <br /> <br />30 Reconnaissance of Water Quality of Lake Henry and Lake Meredith Reservoir, Crowley County, Southeastern <br />Colorado, April-October 1987 <br />