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. 2011 Dec;124(2):339-47.
doi: 10.1093/toxsci/kfr117. Epub 2011 May 11.

Halogenated phenolic contaminants inhibit the in vitro activity of the thyroid-regulating deiodinases in human liver

Craig M Butt  1 , Dongli Wang, Heather M Stapleton
Affiliations

Halogenated phenolic contaminants inhibit the in vitro activity of the thyroid-regulating deiodinases in human liver

Craig M Butt et al. Toxicol Sci. 2011 Dec.

Abstract

Halogenated contaminants, particularly brominated flame retardants, disrupt circulating levels of thyroid hormones (THs), potentially affecting growth and development. Disruption may be mediated by impacts on deiodinase (DI) activity, which regulate the levels of active hormones available to bind to nuclear receptors. The goal of this study was to develop a mass spectrometry-based method for measuring the activity of DIs in human liver microsomes and to examine the effect of halogenated phenolic contaminants on DI activity. Thyroxine (T4) and reverse triiodothyronine (rT3) deiodination kinetics were measured by incubating pooled human liver microsomes with T4 or rT3 and monitoring the production of T3, rT3, 3,3'-diiodothyronine, and 3-monoiodothyronine by liquid chromatography tandem mass spectrometry. Using this method, we examined the effects of several halogenated contaminants, including 2,2',4,4',5-pentabromodiphenyl ether (BDE 99), several hydroxylated polybrominated diphenyl ethers (OH-BDEs), tribromophenol, tetrabromobisphenol A, and triclosan, on DI activity. The Michaelis constants (K(M)) of rT3 and T4 deiodination were determined to be 3.2 ± 0.7 and 17.3 ± 2.3μM. The V(max) was 160 ± 5.8 and 2.8 ± 0.10 pmol/min.mg protein, respectively. All studied contaminants inhibited DI activity in a dose-response manner, with the exception of BDE 99 and two OH-BDEs. 5'-Hydroxy 2,2',4,4',5-pentabromodiphenyl ether was found to be the most potent inhibitor of DI activity, and phenolic structures containing iodine were generally more potent inhibitors of DI activity relative to brominated, chlorinated, and fluorinated analogues. This study suggests that some halogenated phenolics, including current use compounds such as plastic monomers, flame retardants, and their metabolites, may disrupt TH homeostasis through the inhibition of DI activity in vivo.

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Figures

FIG. 1.
FIG. 1.
Deiodinase reactions investigated in the present study. DI I, DI II, and DI III refer to specific isoforms of the DI enzyme.
FIG. 2.
FIG. 2.
Formation rate (pmol/min.mg protein) of T3 and 3,3′-T2 resulting from incubation of T4 (top panel) and rT3 (bottom panel), respectively. Michaelis constant (KM) and maximum reaction rate (Vmax) obtained from nonlinear regression analysis. Each data point represents the mean (n = 2), error bars represent 1 standard error.
FIG. 3.
FIG. 3.
Inhibition of T3, rT3, and 3,3′-T2 formation resulting from the incubation of human liver microsomes with 1μM T4 and various halogenated phenolic competitors. No relationship with 5′-OH BDE 99 and triclosan was found for the rT3 formation. Error bars represent 1 standard deviation.
FIG. 4.
FIG. 4.
Structure-activity relationships for the inhibition of DI activity in human liver microsomes. Figures show the inhibition of T3 formation, as a function of competitor concentration, resulting from the incubation of human liver microsomes with 1μM. Error bars represent 1 standard deviation.
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