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Received for publication December 21, 2005.
Revised February 22, 2006.
Accepted for publication February 23, 2006.
Exposure to the organochlorine pesticide methoxychlor is associated with endocrine disruption in several species, through biotransformation to mono-desmethyl-MXC (OH-MXC) and bis-desmethyl-MXC (HPTE), which interact with estrogen receptors. The biotransformation of [14C]-methoxychlor was examined in channel catfish (Ictalurus punctatus), a freshwater species found in the southern United States. Hepatic microsomes formed OH-MXC and HPTE, assessed by co-migration with authentic standards. The Km for OH-MXC formation by control liver microsomes was 3.8 ± 1.3 mM (mean ± S.D., n = 4) and Vmax was 131 ± 53 pmol/min/mg protein. These values were similar to those of catfish pretreated with 2 mg methoxychlor /kg ip, for 6 days (Km 3.3 ± 0.8 mM and Vmax 99 ± 17 pmol/min/mg), but lower (p<0.05) than the kinetic parameters for catfish treated with 3-methylcholanthrene (3-MC), which had Km of 6.0 ± 1.1 µM and Vmax 246 ± 6 pmol/min/mg protein. Liver microsomes from 3-MC-treated fish produced significantly more of the secondary metabolite and more potent estrogen, HPTE. Intestinal microsomes formed OH-MXC at lower rates than liver. Methoxychlor pretreatment significantly reduced intestinal metabolite formation from 32 ± 4 to 15 ± 6 pmol/min/mg (mean ± S.D., n=4) while 3-MC treatment significantly raised OH-MXC production to 72 ± 22 pmol/min/mg. Ketoconazole, clotrimazole and
-naphthoflavone all decreased the production of OH-MXC in liver microsomes, while
-naphthoflavone stimulated HPTE formation, suggesting CYP1 and CYP3 family isozymes demethylated methoxychlor. The results suggest that the formation of estrogenic metabolites from methoxychlor would be more rapid in catfish co-exposed to CYP1 inducers.
Key words:
cytochrome P450 catalyzed oxidations, environmental toxicology, fish cytochrome P450, insecticides, monooxygenases
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