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Chemical and toxicological properties of coal fly ash - University of ...

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steady state conditions in the disposal pond, they may have longresidence times in the <strong>ash</strong> effluent, thus increasing the probability <strong>of</strong>bioaccumulation by aquatic organisms.13. Of the 12 <strong>fly</strong> <strong>ash</strong> samples evaluated, five were selected for toxicitytesting on the basis <strong>of</strong> the diversity <strong>of</strong> extract pH values observed.All five extracts were acutely toxic to fathead minnow fry.14. Physicochemical components probably responsible for the acute toxicity<strong>of</strong> the <strong>fly</strong> <strong>ash</strong> extracts to fish were pH, Al, ionic strength, <strong>and</strong> Zn.Because <strong>of</strong> the complex composition <strong>of</strong> some extracts <strong>and</strong> the unknownsynergistic <strong>and</strong> antagonistic effects <strong>of</strong> the chemical constituents <strong>of</strong>the extracts, it was not possible from these experiments to determinewhich chemical constituents specifically were responsible for theobserved mortality.15. The <strong>fly</strong> <strong>ash</strong> extracts were diluted to levels presumed subacutely toxicfor use in bioaccu~nul at ion experiments. The growth <strong>of</strong> fathead minnows<strong>and</strong> green sunfish exposed to these diluted <strong>fly</strong> <strong>ash</strong> extracts was notsignificantly different from that <strong>of</strong> control test organisms exposed t<strong>of</strong>iltered tap water under similar conditions.16. The fathead minnows <strong>and</strong> green sunfish accumulated similar elements fromthe <strong>fly</strong> <strong>ash</strong> extracts; the six chemical constituents most commonlyaccumulated from <strong>fly</strong> <strong>ash</strong> extracts were Al, B, Cd, Mn, Mo, <strong>and</strong> Ni. Ofthese six chemical constituents, Cd appeared to be <strong>of</strong> greatestimportance because <strong>of</strong> its highly toxic nature.1. An apparent relationship was observed between the initial pHcharacter <strong>of</strong> a <strong>fly</strong> <strong>ash</strong> leachate <strong>and</strong> its color <strong>and</strong> the matrixCaO/S03 ratio in the solid waste. Further study <strong>of</strong> the less commonlyproduced acidic high-iron <strong>fly</strong> <strong>ash</strong>es should be done.2. The long-term equilibration (LTE) extraction procedure was designed tosimulate equilibrated <strong>ash</strong> ponds. Although obtaining representative pondsamples is difficult, such field work should be done to assess theaccuracy <strong>of</strong> the LTE procedure.3. Fly <strong>ash</strong> laboratory extracts <strong>of</strong>ten undergo complex changes in chemistrywith time <strong>and</strong> should be studied to determine which mineral phasescontrol the aqueous solubility <strong>of</strong> the components. The chemistry <strong>of</strong>slurry water <strong>and</strong> disposal ponds should also be studied <strong>and</strong> modeled todetermine whether the same types <strong>of</strong> changes that occur in laboratoryextracts occur in the field,4. Grab samples were collected from only nine power plants, seven <strong>of</strong> whichwere in Illinois. To provide a more complete picture <strong>of</strong> <strong>fly</strong> <strong>ash</strong>composition <strong>and</strong> variability, samples from other Illinois power plants<strong>and</strong> from other states should be studied.5. The scope <strong>of</strong> the ecological analyses <strong>of</strong> <strong>fly</strong> <strong>ash</strong> in this study consisted<strong>of</strong> acute static bioassays using fathead minnow fry <strong>and</strong> bioaccumulation

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