Evaluation of land disposal and underground injection of shale oil wastewaters [electronic resource]
Results indicate that the salinity of retort water, the principal wastewater generated by shale oil recovery operations, will be too high in most cases for irrigation of cover crops needed for effective stabilization by land disposal. Furthermore, large storage lagoons would be required to hold the...
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Online Access: |
Online Access |
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Corporate Authors: | , |
Format: | Government Document Electronic eBook |
Language: | English |
Published: |
Richland, Wash. : Oak Ridge, Tenn. :
Pacific Northwest National Laboratory (U.S.) ; distributed by the Office of Scientific and Technical Information, U.S. Dept. of Energy,
1979.
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Subjects: |
MARC
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245 | 0 | 0 | |a Evaluation of land disposal and underground injection of shale oil wastewaters |h [electronic resource] |
260 | |a Richland, Wash. : |b Pacific Northwest National Laboratory (U.S.) ; |a Oak Ridge, Tenn. : |b distributed by the Office of Scientific and Technical Information, U.S. Dept. of Energy, |c 1979. | ||
300 | |a Pages: 59 : |b digital, PDF file. | ||
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500 | |a 05/01/1979. | ||
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500 | |a Mercer, B.W.; Campbell, A.C.; Wakamiya, W. | ||
520 | 3 | |a Results indicate that the salinity of retort water, the principal wastewater generated by shale oil recovery operations, will be too high in most cases for irrigation of cover crops needed for effective stabilization by land disposal. Furthermore, large storage lagoons would be required to hold the retort water during the long winters encountered in the oil shale regions of Colorado, Wyoming and Utah. Land disposal cannot be carried out during prolonged periods of freezing weather. Additional problems which may arise with land disposal include air pollution from volatile constituents and groundwater pollution from refractory organics and dissolved salts in the retort water. Pretreatment requirements include the removal of ammonia which is present at toxic concentrations in retort water. Underground injection of retort water may be permitted in regions possessing favorable geological characteristics. It is anticipated that this method would be used as a last resort where effective or resonably priced treatment technology is not available. Regulatory restraints are expected to limit the use of underground injection for disposal of highly polluted shale oil wastewaters. Proving the confinement of injected wastes, a frequently difficult and expensive task, will be required to assure protection of drinking water resources. | |
536 | |b EY-76-C-06-1830. | ||
650 | 7 | |a Management. |2 local. | |
650 | 7 | |a Organic Compounds. |2 local. | |
650 | 7 | |a Other Organic Compounds. |2 local. | |
650 | 7 | |a Mineral Oils. |2 local. | |
650 | 7 | |a Industry. |2 local. | |
650 | 7 | |a Wastes. |2 local. | |
650 | 7 | |a Synthetic Fuels. |2 local. | |
650 | 7 | |a Water. |2 local. | |
650 | 7 | |a Waste Management. |2 local. | |
650 | 7 | |a Synthetic Petroleum. |2 local. | |
650 | 7 | |a Oxygen Compounds. |2 local. | |
650 | 7 | |a Waste Disposal. |2 local. | |
650 | 7 | |a Fossil Fuels. |2 local. | |
650 | 7 | |a Oils. |2 local. | |
650 | 7 | |a Fuels. |2 local. | |
650 | 7 | |a Shale Oil. |2 local. | |
650 | 7 | |a Waste Water. |2 local. | |
650 | 7 | |a Oil Shale Industry. |2 local. | |
650 | 7 | |a Salinity. |2 local. | |
650 | 7 | |a Underground Disposal. |2 local. | |
650 | 7 | |a Hydrogen Compounds. |2 local. | |
650 | 7 | |a Energy Sources. |2 local. | |
650 | 7 | |a Liquid Wastes. |2 local. | |
650 | 7 | |a Oil Shales And Tar Sands. |2 edbsc. | |
710 | 2 | |a Pacific Northwest Laboratory. |4 res. | |
710 | 2 | |a Pacific Northwest National Laboratory (U.S.). |4 res. | |
710 | 1 | |a United States. |b Department of Energy. |b Office of Scientific and Technical Information. |4 dst. | |
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