<br />nl.,{"
<br />
<br />Toxicity of Shale Oil to Fish and Food Chain Organisms
<br />
<br />.ln 01 I,
<br />cnll,lt.,
<br />
<br />many of the same genera sampled in baseline
<br />studies of the oil-shale regions in Colorado (Erman
<br />1981; Pollard and Kinney 1979). The taxa common
<br />to all studies were the Chironomidae and the genera
<br />Ephemerella, Baetis, Rithrogena, Isoperla, Hy-
<br />dropsyche, and Hydroptila, Among these, Chirono-
<br />midae, Baetis, and Isoperla were selected for study
<br />because of their ubiquitous occurrence in field plate
<br />samples and their sensitivity to low concentrations
<br />of oil. Inasmuch as Baetis and Isoperla were the
<br />most sensitive genera, their absence could provide
<br />an early warning in the field of the occurrence of
<br />low levels (0.5-1.0 mg/L) of shale oil contamina-
<br />tion. Although fish mortality would be unlikely at
<br />these concentrations, impaired swimming perfor-
<br />mance and decreased predator success might be
<br />expected. Thus, the use of aquatic insects and fish
<br />behavior in this manner may provide a meaningful
<br />and realistic means of relating laboratory results to
<br />environmental effects monitored in the field.
<br />Actual concentrations of hydrocarbon contami-
<br />nants in a stream after a pipeline break or acci-
<br />dental spill depend on many factors. Under a simu-
<br />lated oil spill of 100 mg/L and the conditions
<br />presented in this study, an impact on aquatic or-
<br />ganisms was observed. The database needs to be
<br />expanded, but combined field and laboratory ap-
<br />proaches used in the present study provide a tech-
<br />nique useful in the field assessment of biological
<br />damage from shale oil spills. Benthic organisms
<br />avoid stress by drifting; and their relatively slow
<br />rate ofrecolonization after stress, gives this assess-
<br />lIent technique the advantage of being applicable
<br />days after contamination has occurred. A measure
<br />''or the degree of contamination could be estimated
<br />from the insect species affected, and contaminant
<br />stress to higher organisms of more economic or
<br />aesthetic value could be predicted.
<br />
<br />DIICh
<br />01
<br />
<br />[;1\',
<br />
<br />~.q
<br />
<br />" -
<br />
<br />.' ..:
<br />
<br />1, ,-
<br />
<br />~,'
<br />I'
<br />
<br />',r
<br />
<br />, '
<br />
<br />~ . f.
<br />
<br />, ,
<br />
<br />:' :
<br />
<br />S I!\ ..
<br />
<br />,till \ \"
<br />
<br />)r'_' ,
<br />
<br />1I1+:
<br />
<br />~ C!'It;...
<br />
<br />11l1lLT,
<br />
<br />lent... I
<br />
<br />:~
<br />
<br />cnl II
<br />
<br />,Ii
<br />
<br />Acknowledgments. We thank Jim Johnson and Bob Knowlton
<br />'ilr their respective assistance in chemical analysis and toxicity
<br />5ludies of the shale oils,
<br />
<br />l'~d .: ~ "-
<br />
<br />:ll"<)k"
<br />cd I:
<br />)lilL: '
<br />II) \\,
<br />It:: !
<br />I k,'<I
<br />
<br />~"I;.:: ;
<br />'3
<br />
<br />References
<br />'''l(:
<br />
<br />:,.,-
<br />American Society for Testing and Materials (1980) Standard
<br />practice for conducting acute toxicity tests with fishes, mac-
<br />, roinvertebrates, and amphibians, American Society for
<br />- Testing Materials Report E-729, Philadelphia, PA, 25 pp
<br />,Cada GC, Kenna M (1985) Effectiveness of hydrotreatment in
<br />reducing the toxicity of a coal liquefaction product to juve-
<br />nile channel catfish, Bull Environ Con tam Toxicol 34:746-
<br />. 753
<br />
<br />:toleman WE, Munch JW, Streicher RP, Ringhand HP, Kopfer
<br />FC (1984) Identification and measurement of components in
<br />
<br />J Ii ~ '
<br />
<br />)::'-~ " ,:
<br />s;tlln, '
<br />
<br />
<br />al \..'\:'
<br />
<br />i d;illt"
<br />'\)11,,1\
<br />lrd , :
<br />\,
<br />Ire'" I','
<br />
<br />
<br />245
<br />
<br />gasoline, kerosene. and No.2 fuel oil that partition into the
<br />aqueous phase after mixing. Arch Environ Contam Toxicol
<br />13:171-178
<br />Erman DC (1981) Stream macroinvertebrate baseline surveys: A
<br />comparative analysis from the oil-shale regions of Colorado,
<br />USA. Environ Manage 5:531-536
<br />Finger SE, Little EE, Henry MG, Fairchild JF, Boyle TP (1985)
<br />Comparison of laboratory and field assessment of fluorine.
<br />Part I: Effects of fluorine on the survival, growth, reproduc-
<br />tion, and behavior of aquatic organisms in laboratory tests.
<br />In: Boyle TP (ed) Validation and predictability of laboratory
<br />methods for assessing the fate and effects of contaminants in
<br />aquatic ecosystems. ASTM STP 865, American Society for
<br />Testing and Materials, Philadelphia, PA, pp 120-133
<br />Fisher JW, Hunt TP, Putnam ME, Livingston MJ (1985) Toxic
<br />effects of petroleum and shale JP-4 and JP-8 aviation fuels
<br />on fathead minnows, Water Resour Bull 21 :49-52
<br />Folmar LC, Graddock DR, Blackwell JW, Joyce G, Hodgins HO
<br />(1981) Effects of petroleum exposure on predatory behavior
<br />of coho salmon (Oncorhynchus kisutch). Bull Environ
<br />Con tam Toxicol 27:458-465
<br />Ghassemi M, Panahloo A (1984) Comparison of physical and
<br />chemical characteristics of shale oil fuels and analogous pe-
<br />troleum products. Environ Toxicol Chern 3:511-535
<br />Giddings JM, Washington IN (1981) Coal liquefaction products,
<br />shale oil, and petroleum. Acute toxicity to freshwater algae.
<br />Environ Sci Technol15: 106-108
<br />Griest WH, Guerin MR, Yeatts LB Jr, Clark BR (1981) Sample
<br />management and chemical characterization of the Paraho/
<br />Sohio/U,S. Navy crude and refined shale oil suite. In: Griest
<br />WH, Guerin MR, Coffin DL (eds) Health Effects Investiga-
<br />tion of Oil Shale Development, Ann Arbor Science Pub-
<br />lishers, Ann Arbor, MI, pp 17-44
<br />Howard TE (1975) Swimming performance of juvenile coho
<br />salmon (Oncorhynchus kisutch) exposed to bleached kraft
<br />pulpmill effluent. J Fish Res Board Can 32:789-793
<br />Ingram LL, Ellis J, Crisp PT, Cook AC (1983) Comparative
<br />study of oil shales and shale oils from the Mahogany Zone,
<br />Green River formation (USA) and Kerosene Creek seam,
<br />Rundle formation (Australia). Chern GeoI38:185-212
<br />Klein SA, Jenkins D (1977) Environmental Quality Research:
<br />Fish and Aufwuchs Bioassay, Air Force Aerospace Medical
<br />Research Laboratory Report No. AMRL-TR-77-54. Wright-
<br />Patterson Air Force Base, OH, 58 pp
<br />Lee DS, Gilbert CR, Hocutt CH, Jenkins RE, McAllister DE,
<br />Stauffer JR Jr (1980) Atlas of North American Freshwater
<br />Fishes, North Carolina State Museum of Natural History,
<br />Raleigh, NC, 854 pp
<br />Litchfield JT Jr, Wilcoxon F (1949) A simplified method of eval-
<br />uating dose-effect experiments. J Pharmacol Exp Ther
<br />96:99-113
<br />Little EE, Flerov BA, Ruzhinskaya NN (1985) Behavioral ap-
<br />proaches in aquatic toxicity: A review. In: Mehrle PM, Gray
<br />RH, Kendall RL (eds) Toxic substances in the aquatic envi-
<br />ronment: An international perspective, American Fisheries
<br />Society, Water Quality Section, Bethesda. MD, pp 92-98
<br />Merritt RW, Cummings KW (1978) An Introduction to the
<br />Aquatic Insects of North America, Kendall/Hunt, Dubuque,
<br />lA, 441 pp
<br />Pielou, EC (1975) Ecological Diversity, John Wiley & Sons, New
<br />York, 165 pp
<br />Pollard JE, Kinney WL (1979) Assessment of macroinvertebrate
<br />monitoring techniques in an energy development area. U.S.
<br />
<br /><0"*"
<br />
|