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Last modified
7/14/2009 5:02:31 PM
Creation date
5/20/2009 2:54:44 PM
Metadata
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Template:
UCREFRP
UCREFRP Catalog Number
7806
Author
U.S. Department of the Interior.
Title
Quality of Water, Colorado River Basin.
USFW Year
1997.
USFW - Doc Type
Progress Report No. 18,
Copyright Material
NO
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<br />Chapter 3 <br /> <br />Energy Exploration and Development <br /> <br />Many of the geologic formations of the Colorado River Basin were deposited in marine (salt <br />water) or brackish water environments. Sulfates and sodium chloride are prevalent salts in most of <br />these formations. Many of the formations were deposited in drier periods and are capable of <br />transmitting w.ater, but these aquifers are frequently sandwiched between hundreds or even <br />. thousands of feet of impermeable shales (aquicIudes). These aquifers are, therefore, static and <br />often saline. Many static and saline aquifers are present in the Basin. When a path of flow is <br />provided by drilling or mining, these aquifers are mobilized, and brackish or saline waters flow <br />back to the surface. <br /> <br />The development of energy resources, specifically coal, oil and gas, and oil shale, in the Colorado <br />River Basin may contribute significant quantities of salt to the Colorado River. Salinity of surface <br />waters can be increased either by mineral dissolution and uptake in surface runoff, mobilization of <br />brackish ground water, or by consumption of good quality water. The location of fossil fuels is <br />associated with marine-derived formations. Any disturbance of these saline materials will increase <br />the contact surfaces, allowing for the dissolutions of previously unavailable soluble minerals. <br /> <br />Salinity increases associated with the mining of coal can be attributed to leaching of coal spoil <br />materials, discharge of saline ground waters, and increased erosion resulting from surface <br />disturbing activities. Spoil materials have a greater permeability than undisturbed overburden, <br />allowing most of the rain falling on the spoils to infiltrate instead of running off. The water <br />percolates through the spoils, dissolving soluble minerals. <br /> <br />Studies[5-7] conducted on mining spoils in northwestern Colorado indicate that the resulting <br />salinity of spoil-derived waters ranges from approximately 3,000 mg/L to 3,900 mg/L. The <br />variability in concentration depends on water residence time and the chemical and physical <br />properties of the spoil. <br /> <br />Saline water is also a byproduct of oil and gas production in the Basin. It is not uncommon to <br />produce several times the amount of saline waters as oil. Oil and gas operators in Colorado <br />produced approximately 25,000,000 barrels of saline water during December 1985. The salinity of <br />production waters varies greatly from location to location and is dependent upon the producing <br />formation. Common disposal techniques include evaporation, injection, and discharge to local <br />drainages. <br /> <br />The future development of the oil shale resources in Colorado, Utah, and Wyoming has the <br />potential to increase salt loading to the Colorado River. Salt increases can be attributed to the <br />consumptive use of good quality water, mine dewatering, and, if surface retorting is used, the <br />leaching of spoil materials similar to that of surface coal mining. <br /> <br />Reclamation and others are attempting to identify abandoned exploration wells that are leaking and <br />develop plans to control the leaks. The Meeker Dome Salinity Control Unit identified and <br />plugged several abandoned wells along the White River to prevent a salt dome (a geologic <br />formation) from discharging saline water into the river. <br /> <br />12 <br />
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