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Air Quality Criteria for Lead Volume II of II - (NEPIS)(EPA) - US ...

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partition in sediment between acid-volatile sulfide, pore water, benthic organisms, and other<br />

sediment phases such as organic carbon. When the sum <strong>of</strong> the molar concentrations <strong>of</strong><br />

simultaneously extracted metal (∑SEM) minus the molar concentration <strong>of</strong> AVS is less than zero,<br />

it can accurately be predicted that sediments are not toxic because <strong>of</strong> these metals. Note that this<br />

approach can be used to predict the lack <strong>of</strong> toxicity, but not the presence <strong>of</strong> toxicity. It is<br />

important to emphasize that metals must be evaluated as a mixture using this approach.<br />

If individual metals, or just two or three metals, are measured in sediment, ∑SEM would be<br />

misleadingly small and it may inaccurately appear that ∑SEM / AVS is less than 1.0.<br />

If ∑SEM / AVS is normalized to the organic carbon fraction (i.e., (∑SEM / AVS)/fOC),<br />

mortality can be more reliably predicted by accounting <strong>for</strong> both the site-specific organic carbon<br />

and AVS concentrations. When evaluating a metal mixture containing cadmium, copper, Pb,<br />

nickel, silver, and zinc, the following predictions can be made (U.S. Environmental Protection<br />

Agency, 2005c):<br />

• A sediment with (SEM / AVS)/fOC < 130 µmol/gOC should pose low risk <strong>of</strong> adverse<br />

biological effects due to these metals.<br />

• A sediment with 130 µmol/gOC < (SEM / AVS)/fOC < 3000 µmol/gOC may have adverse<br />

biological effects due to these metals.<br />

• In a sediment with (SEM / AVS)/fOC > 3000 µmol/gOC, adverse biological effects may<br />

be expected.<br />

A third approach is to measure pore water concentrations <strong>of</strong> cadmium, copper, Pb, nickel,<br />

and zinc and then divide the concentrations by their respective FCVs. If the sum <strong>of</strong> these<br />

quotients is

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