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The model uses a regression, based on the relationship between concentrations of
PAHs in interstitial water and toxicity to estuarine amphipods in spiked sediment
bioassays, to determine toxic units for PAHs. Toxic units for each compound,
which are equal to the concentration in the interstitial water of the contaminated
sediment divided by the interstitial water 10-d LC50, are summed. The sum of the
toxic units is used to predict the probability of significant acute sediment toxicity
to marine and estuarine amphipods, where significant mortality was defined as
>24 percent mean mortality in field-collected sediments. The model was verified
by comparison to mortality observed in sediment toxicity tests in field-collected
samples from 13 investigations. The Sum-PAH-PAH) level of acute toxicity
(Sum of Toxic Units = 3.291, p of >24% mortality = 1.0) was determined as the
toxic-unit concentration above which acute toxicity is always expected to occur.
The Σ-PAH threshold of acute toxicity (Sum of Toxic units = 0.186, p of >24%
mortality = 0.05) is the toxic unit concentration below which mixtures of PAHs
are unlikely to contribute to sediment toxicity above background. The 50 percent
probability of acute toxicity (sum of toxic units = 0.725, p>0.050) is the
concentration expected to cause acute toxicity in 50 percent of the cases.
Narcosis
Narcosis due to organic contaminants in aquatic organisms is defined as a
nonspecific reversible disturbance in the functioning of the membrane, caused by
the accumulation of contaminants in the hydrophobic (lipid) phases of the
organism (van Wezel and Opperhuizen 1995). Experimental work has
demonstrated that the critical body residue (CBR) for the acute lethal effect of
nonpolar narcotic chemicals is fairly constant at 2 to 8 mmol chemical/kg wet wt
tissue (McCarty et al. 1992). In addition, the effects of mixtures of nonpolar
chemicals that act by a narcotic mode of action appear to be generally additive
(McCarty and Mackay 1993).
B4
Appendix B Food Chain and Toxicity Models

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