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Last modified
7/14/2009 5:02:37 PM
Creation date
5/24/2009 7:30:42 AM
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UCREFRP
UCREFRP Catalog Number
9624
Author
Bauch, N. J. and J. B. Bails.
Title
Water-Quality Characteristics and Ground-Water Quantity of the Fraser River Watershed, Grand County, Colorado 1998-2001.
USFW Year
2004.
USFW - Doc Type
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Water Quality 21 <br />maximum discharge and is an indication of dilution of surface <br />water with snowmelt. Maximum values occurred during late <br />winter and early spring before the onset of snowmelt. <br />Dissolved-oxygen concentrations in the Fraser River at <br />Tabemash ranged from 8.0 to 11.5 mg/L, with a median of <br />9.6 mg/L (table 4). Dissolved-oxygen concentrations were <br />inversely related to stream temperature, which is a primary <br />factor controlling the solubility of oxygen in water. The State of <br />Colorado instream water-quality standard for dissolved-oxygen <br />concentration in the Fraser River is 6.0 mg/L except during <br />periods of fish spawning when the standard is raised to <br />7.0 mg/L (table 4) (Colorado Department of Public Health and <br />Environment, 2002). No dissolved-oxygen concentrations mea- <br />sured during this study were less than the standard. <br />Values for pH in the Fraser River ranged from 7.8 to 8.6 <br />(table 4). All measurements were within the State instream <br />water-quality standard of 6.5-9.0 (Colorado Department of <br />Public Health and Environment, 2002). <br />Dissolved Solids, Major Ions, and Trace Elements <br />The concentrations of dissolved solids in the Fraser River <br />were low, ranging from 53 to 93 mg/L (table 4). These concen- <br />trations reflected the high quality of the surface water and <br />indicate the suitability of the water for drinking, residential, <br />industrial, and irrigation purposes. <br />The surface water was a calcium-bicarbonate type water <br />throughout the study period (fig. 4). Samples from 10 of <br />11 ground-water wells were the same type water. During most <br />of the year, the surface water primarily is base flow from <br />ground-water discharge. The following discussion will only <br />focus on the major ions chloride and sulfate and the trace ele- <br />O <br />Z w <br />Q <br />W J <br />l- ZOc <br />LL w !L <br />0OQ <br />W = = <br />> U J <br />O <br />ments iron and manganese, all of which have State of Colorado <br />instream water-quality standards. <br />Chloride concentrations overall were low (less than or <br />equal to 9.0 mg/L.) in the Fraser River at Tabernash (table 4). <br />Maximum concentrations typically occurred during late winter <br />or early spring just prior to peak flow resulting from spring <br />snowmelt. Minimum concentrations occurred during snowmelt <br />runoff (fig. 9). It is likely that chloride in the river comes from <br />nonpoint sources, including salt and gravel applications during <br />winter, and discharges from wastewater-treatment facilities. All <br />chloride concentrations were substantially below the State <br />instream standard of 250 mg/L (Colorado Department of Public <br />Health and Environment, 2002). <br />Sulfate concentrations also were low (less than or equal to <br />4.5 mg/L) in the river. Like chloride, maximum concentrations <br />of sulfate typically occurred during late winter or early spring <br />just prior to peak flow resulting from spring snowmelt; mini- <br />mum concentrations occurred after snowmelt runoff in mid- <br />summer (fig. 9). All sulfate concentrations were substantially <br />below the State instream standard of 250 mg/L (Colorado <br />Department of Public Health and Environment, 2002). <br />Iron concentrations were relatively high at the site, ranging <br />from 73 to 354 µg/L, with a median concentration of 198 µg/L, <br />(table 4). The elevated iron concentrations may be related to <br />discharges of iron-rich ground water to the river in the vicinity <br />of Tabernash. A large amount of variability in the iron concen- <br />trations was present over the sampling period, but no seasonal <br />patterns were discernible. The State chronic instream iron stan- <br />dard of 300 Itg/L for the Fraser River site was exceeded in 1 of <br />19 samples (Colorado Department of Public Health and Envi- <br />ronment, 2002). For trace elements such as iron and manganese, <br />compliance with the State instream standard is met if the con- <br />centration of the 85th percentile of all representative data is less <br />12 <br />o- Dissolved sulfate <br />Dissolved chloride <br />10 Discharge <br />s A <br />6 / <br />4 / /A- I <br />2 <br />V 00 00 m Cr) O O O O O O <br />? ? ? ? ? ? O O O O O O O <br />O O O O O O O O O O O O O <br />OD N In W N In 00 N 0 00 <br />O ? O O O ? O O O ? O O O <br />TIME <br />300 <br />250 U 0 <br />mZ <br />UO <br />200 Z w <br />-U) <br />w <br />150 (D LU <br />Q ? <br />2 <br />100 LL <br />50 <br />Figure 9. Dissolved sulfate and chloride concentrations and discharge atthe <br />Fraser River below Crooked Creek at Tabernash, Colorado, 1998-2001.
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