Alkylated polycyclic aromatic hydrocarbons, such as retene (7-isopropyl-1-methylphenanthrene), induce cytochrome P450 1A (CYP1A) enzymes and produce dioxin-like toxicity in the embryo–lar
val stages of fish characterized by the signs of blue sac disease (BSD). The signs of toxicity are well characterized; howe
ver, the mechanism is not well understood. To elucidate the role of CYP1A in retene toxicity, lar
val rainbow trout (
Oncorhynchus mykiss) were co-treated with a range of concentrations of
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-naphthofla
vone (ANF), a known CYP1A inhibitor. The co-treatment produced synergistic toxicity at 3.2–100 μg/L ANF, after which toxicity at 180 μg/L ANF dropped to le
vels typical of retene-only. At 320 μg/L ANF, toxicity increased with or without retene, indicating that ANF alone was capable of inducing BSD. In addition, the additi
ve toxicity of retene-only and 320 μg/L ANF-only approximately equalled that of the co-exposed lar
vae (100 μg/L retene + 320 μg/L ANF), indicating response addition. Thus, two mechanisms of action occurred in co-exposed lar
vae at different concentrations of ANF. In trout lar
vae, there was a correlation between toxicity and CYP1A protein concentrations, and in ju
venile trout, ANF produced a concentration-dependent inhibition of ethoxyresorufin-
O-deethylase (EROD) acti
vity without a measurable drop in CYP1A protein. Taken together, the mechanism underlying the synergistic toxicity is EROD-independent and may be AhR-dependent. This study demonstrated that multiple, exposure-dependent mechanisms can occur in mixture toxicity, suggesting that current risk assessment models may drastically underestimate toxicity, particularly of mixtures containing both CYP1A inducers and inhibitors.