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EPA's Vessel General Permit and Small Vessel General

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PAH <strong>and</strong> MAH<br />

Because MAHs <strong>and</strong> PAHs are Type I narcotic compounds, the toxicity of these compounds in<br />

water (<strong>and</strong> sediments) is most easily assessed using what is called the target lipid model or TLM<br />

(DiToro <strong>and</strong> McGrath, 2000). Under the TLM, acute <strong>and</strong> chronic toxicity of MAHs <strong>and</strong> PAHs<br />

to aquatic animals is predicted as single pollutants <strong>and</strong> as mixtures by calculating the critical<br />

body burden in the target lipid of an organism. EPA used the critical body burden of<br />

benzo(a)pyene <strong>and</strong> benzene in lipid to develop its response thresholds against which modeled<br />

environmental concentrations would be compared. Under EPAs estuarine harbor model, average<br />

post permit PAH <strong>and</strong> MAH concentrations were unchanged for all analytes but benzene, which<br />

was reduced between 17 <strong>and</strong> 53 percent under worst case <strong>and</strong> best case conditions, respectively.<br />

For the river harbor model, average post permit PAH <strong>and</strong> MAH concentrations were unchanged<br />

for all but benzene, which was reduced between 6 <strong>and</strong> 9 percent, depending on scenario.<br />

The TLM guidelines proposed by McGrath <strong>and</strong> DiToro (2009) are equivalent to a HC5, which is<br />

the hazard concentration considered to protect 95% of the tested species. Thresholds for<br />

individual analytes ranged from 0.286 ug/L for bezo(a)pyrene to 2,433 for benzene ug/L.<br />

Average RQs calculated by EPA for individual analytes in modeled estuarine/marine harbors<br />

ranged from

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