Laserfiche WebLink
<br />T <br />" <br /> <br /> <br />ltl <br /> <br />TOXICITY OF LEACHATES FROM RETORTED OIL SHALE <br /> <br />increase in these variables could result in reduced <br />survival and growth of fishes and food-chain or- <br />ganisms. However, it would take 50 oil shale <br />developments, each producing 117,182 m3 per <br />year ofIeachate (Stollenwert and Runnells 1981), <br />to increase the TDS in the White River (USGS <br />1981 b) to concentrations measured in our 3% <br />exposure. This would amount to 1 % of the av- <br />erage annual discharge from the White River. <br />Due to reduced dilution and less flushing, smaller <br />feeder streams and backwater areas are likely to <br />" have higher concentrations ofleachates than the <br />main channel of the river system. Because these <br />I, habitats are important fish food-producing and <br />I nursery areas for young-of-the-year fishes, es- <br />~, pecially Colorado squawfish (Tyus et al. 1982), <br />protection of water quality in these habitats is <br />essential. <br />Discharge of retorted shale leachate into the <br />upper Colorado River system should take into <br />consideration the high concentration of in organ- <br />ic ions in the leachate, the already high level of <br />dissolved solids in the river system, and the di- <br />lution factor between quantity of leachate dis- <br />charged and volume of receiving stream, Prelim- <br />" inary findings in this study indicate a safe ratio <br />l of leachate discharge to surface water discharge <br />I might be I :99 or 1 %. Site-specific studies would <br />; need to be conducted on particular spent shale <br />: types and receiving waters, Special emphasis <br />t should be placed on the flow characteristics of <br />1'",baCkwater habitats to prevent an increased res- <br />idence time of leachate in these areas. <br /> <br />, Acknowledgments <br /> <br />t Wi thank D. Chester, J,~. Coyle, E, K. Henry, <br />~, R. L. Knowlton, L. C. Nell, K. M. McFadden, <br />i D. A. Sanchez, and B. L. Thomas for their ex- <br />J ceIlent technical assistance in conducting this <br />~",', study. The U.S. Department of Energy supported <br />the University of Wyoming under Contract DE- <br />AC02-82ER60071 and Battelle Pacific North- <br />- est Laboratories under Contract DE-AC06- <br />76LRO 1830. <br /> <br /> <br />I References <br /> <br />AMY, G. L., A. L. HINES, J. F. THOMAS, AND R. E. <br />SELLECK, 1980, Groundwater leaching of organic <br />I- po11ntan" from in-"'n retorted on ,bw,_ A =" <br />I transfer analysis, Environmental Science and <br />, Technology 14:831-835, <br />,; APHA (AMERICAN PUBLIC HEALTH ASSOCIATION) <br />I AMERICAN WATERWORKS ASSOCIATION, AND WA- <br /> <br /> <br />f <br />~ <br />f <br /> <br /> <br />TER POLLUTION CONTROL FEDERATION. 1980, <br />Standard methods for the examination of water <br />and wastewater, 15th edition. American Public <br />Health Association, Washington, DC, USA. <br />ASTM (AMERICAN SOCIETY FOR TESTING MATERIALS). <br />1980, Standard methods for conducting acute <br />toxicity tests with fishes, macroinvertebrates, and <br />amphibians. Protocol E729-80 in Annual book of <br />ASTM standards. American Society for Testing <br />and Materials, Philadelphia, PA, USA. <br />BEHNKE, R. J" AND D. E. BENSON, 1980. Endangered <br />and threatened fishes of the upper Colorado River <br />Basin, Colorado State University Cooperative Ex- <br />tension Service Bulletin 503A, Fort Collins, CO, <br />USA. <br />BUIKEMA, A. L., JR., J, G, GEIGER, AND D. R. LEE. <br />1980. Daphnia toxicity tests, American Society <br />for Testing and Materials, Special Technical Pub- <br />lication 715:48-69. <br />Fox, J. P. 1980, Water-related impacts of in-situ oil <br />shale processing, University of California, Law- <br />rence Berkeley Lab Report LBL-6300, Berkeley, <br />CA, USA, <br />FRANSWAY, D, F" AND R. J. WAGENET. 1981. Salt <br />release and movement in processed oil shale. Jour- <br />nal of Environmental Quality 10: 107-113. <br />FREMLING, C. R., AND W, L. MAUCK. 1980, Methods <br />for using nymphs of burrowing mayflies (Ephem- <br />eroptera, Hexagenia) as toxicity test organisms, <br />American Society for Testing and Materials Spe- <br />cial Technical Publication 715:81-97. <br />GEIGER, J. G" AND A, L. BUIKEMA, JR, 1982. Hy- <br />drocarbons depress growth and reproduction of <br />Daphnia pulex (Cladocera), Canadian Journal of <br />Fisheries and Aquatic Sciences 39:830-836, <br />HAMILTON, M, A. R" R. C, Russo, AND R, V. <br />THURSTON. 1977. Trimmed Spearman-Karber <br />method for estimating median lethal concentra- <br />tions in toxicity bioassays, Environmental Science <br />and Technology 12:714-719. <br />HARBERT, H, p" III, W. A. BERG, AND D. B. Mc- <br />WHORTER, 1979. Lysimeter disposal of Paraho <br />retorted oil shale, U,S, Environmental Protection <br />Agency, EP A-60017179-188, Cincinnati, OH, USA. <br />HOLDEN, p, B. 1977. Habitat requirements of juve- <br />nile Colorado River squawfish. U,S, Fish and <br />Wildlife Service Biological Services Program FWS/ <br />OBS-77/65, <br />KILKELLY, M. K., H, P. HARBERT III, AND W, A. BERG. <br />1981. Field studies on Paraho retorted oil shale <br />Iysimeters: leachate, vegetation, moisture, salini- <br />ty, and runoff, 1977-1980. United States Envi- <br />ronmental Protection Agency Report EP A-60017/ <br />81-131, Cincinnati, OH, USA, <br />LOWMAN, F. G., AND THIRTEEN CO-AUTHORS. 1970, <br />Bioenvironmental and radiological-safety feasi- <br />bility studies, Atlantic-Pacific interoceanic canal. <br />Estuarine and marine ecology, volumes I-IV, U .S, <br />Atomic Energy Commission, Puerto Rico Nuclear <br />Center, Mayaguez, Puerto Rico, <br />MARTIN, H. W. 1967, A method of measuring lengths <br /> <br />893 <br />