Responses of benthic fish exposed to contaminants in outdoor microcosms--examining the ecological relevance of previous laboratory toxicity tests.
Previous laboratory studies indicate that coal combustion wastes (a mixture composed of fly ash and other lower volume wastes such as bottom ash; hereafter collectively referred to as ash) adversely affect the health of benthic fish (Erimyzon sucetta; lake chubsucker), but fish in these studies were provided with ample uncontaminated food resources. Because aquatic disposal of ash can also adversely affect food resources for benthic fish, we hypothesized that changes in resources might exacerbate the effects of ash on fish observed in laboratory studies. We exposed juvenile E. sucetta in outdoor microcosms to water, sediment, and benthic resources from an ash-contaminated site or a reference site for 45 days and compared our findings to previous laboratory studies. Benthic invertebrate biomass was nearly three times greater in controls compared to ash microcosms. Total organic content of control sediment (41%) was also greater than in ash sediments (17%), suggesting that additional benthic resources may have also been limited in ash microcosms. Benthic invertebrates isolated from the ash microcosms had trace element concentrations (As, Cd, Co, Cr, Cs, Se, Sr, and V) up to 18 times higher than in weathered ash used in laboratory studies. The concentrations of trace elements accumulated by fish reflected the high dietary concentrations encountered in the ash microcosms and were associated with reduced growth (final mass = 0.07 g) and survival (25%) compared to controls (0.37 g and 67%, respectively). Accumulation of trace elements, as well as reductions in growth and survival, were more pronounced than in previous laboratory studies, suggesting that resource conditions may be important in mediating ash toxicity. Taken together, our studies suggest that ash discharge into aquatic systems is a more serious threat to the health of benthic fish than previously predicted based upon laboratory toxicity tests.
Hopkins
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WA
Savannah River Ecology Laboratory, University of Georgia, Drawer E, Aiken, SC 29802, USA. hopkins@srel.edu
Staub
B P
BP
Snodgrass
J W
JW
Taylor
B E
BE
DeBiase
A E
AE
Roe
J H
JH
Jackson
B P
BP
Congdon
J D
JD
D000704:Analysis of Variance; D000818:Animals; D002244:Carbon / Q000633:toxicity*; D060729:Coal Ash; D003531:Cypriniformes / Q000254:growth & development / Q000378:metabolism*; D019015:Geologic Sediments / Q000032:analysis; D006128:Growth / Q000187:drug effects*; D007448:Invertebrates / Q000378:metabolism; D052638:Particulate Matter; D012037:Refuse Disposal; D013022:South Carolina; D014131:Trace Elements / Q000032:analysis / Q000493:pharmacokinetics; D014874:Water Pollutants, Chemical / Q000633:toxicity*
D060729:Coal Ash; D052638:Particulate Matter; D014131:Trace Elements; D014874:Water Pollutants, Chemical; D002244:Carbon