Skip to main content
Drug Metabolism and Disposition logoLink to Drug Metabolism and Disposition
. 2012 Mar;40(3):588–595. doi: 10.1124/dmd.111.042796

Polychlorinated Biphenyl Congeners that Increase the Glucuronidation and Biliary Excretion of Thyroxine Are Distinct from the Congeners that Enhance the Serum Disappearance of Thyroxine

L A Martin 1, D T Wilson 1, K R Reuhl 1, M A Gallo 1, C D Klaassen 1,
PMCID: PMC3286271  PMID: 22187485

Abstract

Polychlorinated biphenyl (PCB) congeners differentially reduce serum thyroxine (T4) in rats, but little is known about their ability to affect biliary excretion of T4. Thus, male Sprague-Dawley rats were orally administered Aroclor-1254, Aroclor-1242 (32 mg/kg per day), PCB-95, PCB-99, PCB-118 (16 mg/kg per day), PCB-126 (40 μg/kg per day), 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) (3.9 μg/kg per day), or corn oil for 7 days. Twenty-four hours after the last dose, [125I]T4 was administered intravenously, and blood, bile, and urine samples were collected for quantifying [125I]T4 and in bile [125I]T4 metabolites. Serum T4 concentrations were reduced by all treatments, but dramatic reductions occurred in response to Aroclor-1254, PCB-99 [phenobarbital (PB)-type congener], and PCB-118 (mixed-type congener). None of the treatments increased urinary excretion of [125I]T4. Aroclor-1254, PCB-118, TCDD, and PCB-126 (TCDD-type congener) increased biliary excretion of T4-glucuronide by 850, 756, 710, and 573%, respectively, corresponding to marked induction of hepatic UDP-glucuronosyltransferase (UGT) activity toward T4. PCB-95 and PCB-99 did not induce UGT activity; therefore, the increased biliary excretion of T4-glucuronide was related to the affinity of congeners for the aryl hydrocarbon receptor. The disappearance of [125I]T4 from serum was rapid (within 15-min) and was increased by Aroclor-1254, PCB-99 and PCB-118. Thus, reductions in serum T4 in response to PCBs did not always correspond with UGT activity toward T4 or with increased biliary excretion of T4-glucuronide. The rapid disappearance of [125I]T4 from the serum of rats treated with PB-like PCBs suggests that increased tissue uptake of T4 is an additional mechanism by which PCBs may reduce serum T4.

Introduction

Glucuronidation plays an essential role in thyroid hormone homeostasis not only by facilitating excretion, but also by providing the first step in enterohepatic recycling of triiodothyronine (T3) and thyroxine (T4) (Visser, 1990; Vansell and Klaassen, 2001, 2002). Reductions in serum T4 and corresponding increases in T4 glucuronidation occur in rats in response to the anticonvulsant phenobarbital (PB) (McClain et al., 1989), the selective antagonist of corticotropin-releasing factor receptor-1 DMP 904 (Wong et al., 2005; Lecureux et al., 2009), the synthetic steroids spironolactone and pregnenolone-16α-carbonitrile (PCN) (Semler et al., 1989; Liu et al., 1995), and the polycyclic aromatic hydrocarbons 3-methylcholanthrene (3-MC), tetrachlorodibenzo-p-dioxin (TCDD), and polychlorinated biphenyls (Hood and Klaassen, 2000; Craft et al., 2002).

Polychlorinated biphenyl (PCB) mixtures such as Aroclor-1254 are especially effective in reducing circulating levels of T4 in rats (Collins and Capen, 1980; Liu et al., 1995). Although there are a number of theories regarding the mechanisms by which PCBs exert their effects on thyroid hormones, including direct effects on the gland itself and interference with serum transport proteins (Capen, 1994; Li and Hansen, 1997), the major focus has been on increased biotransformation. As early as the 1970s, increased glucuronidation of T4 and increased biliary excretion of T4-glucuronide after exposure to Aroclor-1254 were demonstrated (Bastomsky, 1974). Subsequently, studies with thyroidectomized rats demonstrated that this effect produced by PCBs or TCDD was due to an extrathyroidal mechanism, most likely increased glucuronidation (Barter and Klaassen, 1992; Schuur et al., 1997).

PCB mixtures are produced by random chlorination of the biphenyl molecule, which can theoretically produce 209 different congeners with varying degrees of chlorination and patterns of toxicity (De Voogt and Brinkman, 1989; Li and Hansen, 1997). The congeners are commonly divided into three types. The coplanar PCB congeners, which have no chlorine substitutions in the ortho positions, have affinity for the aryl hydrocarbon receptor (AhR), induce CYP1A, and are referred to as TCDD-type inducers. The noncoplanar PCB congeners, which have at least two chlorine substitutions in the ortho positions, have low affinity for the AhR (Murk et al., 1996), induce CYP2B, and are referred to as PB-type inducers. The mono-ortho coplanar PCB congeners have one chlorine substitution in an ortho position, which reduces but does not abolish affinity for the AhR. These congeners induce both CYP1A and CYP2B in rats and are referred to as mixed-type inducers (Safe et al., 1985).

We have previously shown that individual PCB congeners differentially reduce serum T4 levels, with the PB-type and mixed-type PCBs being most effective (Martin and Klaassen, 2010). However, little is known about their ability to affect biliary excretion of T4-glucuronide. Thus, the present study was designed to test the hypothesis that the reduction of serum T4 by these PCBs corresponds with their ability to induce the glucuronidation of T4 and increase the biliary excretion of T4-glucuronide. PCB-126 (3,3′4,4′,5-pentachlorobiphenyl, a coplanar TCDD-type congener), PCB-95 (2,2′,3,5′,6-pentachlorobiphenyl, noncoplanar PB-type congener), PCB-99 (2,2′,4,4′,5-pentachlorobiphenyl, noncoplanar PB-type congener), and PCB-118 (2,3′,4,4′,5-pentachlorobiphenyl, a mono-ortho coplanar mixed-type congener) were examined. Aroclor-1254 was used to compare the effects of the mixture with those of the congeners. Aroclor-1242 was used to compare the effects of a PCB mixture with a lower (42% by weight) degree of chlorination. TCDD was included as the prototypical AhR ligand for comparison with PCB-126. After a 7-day administration period, radiolabeled T4 was administered intravenously to the rats, the disappearance of [125I]T4 from the plasma and excretion into bile was quantified, the radioactive metabolites in bile were separated by high-performance liquid chromatography (HPLC), and the induction of hepatic UDP-glucuronosyltransferase (UGT) activity toward T4 was determined.

Materials and Methods

Chemicals and Reagents.

Aroclor-1254 and Aroclor-1242 were donated by Dr. Lawrence Hansen (University of Illinois at Urbana). TCDD was a gift from Dr. Karl Rozman (University of Kansas Medical Center, Kansas City, KS). PCB-95, PCB-99, PCB-118, and PCB-126 were obtained from AccuStandard (New Haven, CT). Radioimmunoassay kits for assay of serum thyroid hormones were obtained from Diagnostics Products (Los Angeles, CA). [125I]T4, radiolabeled on both outer-ring positions, was obtained from PerkinElmer Life and Analytical Sciences (Waltham, MA). Heparin was purchased from Elkins-Sinn, Inc. (Cherry Hill, NJ). Ultima Flo-M Scintillant was purchased from PerkinElmer Life and Analytical Sciences. All other reagents were obtained from Thermo Fisher Scientific (Waltham, MA).

Animals and Treatments.

The Institutional Animal Care and Use Committee approved all protocols before initiation. Male Sprague-Dawley rats (Sasco, Omaha, NE), weighing 225 to 250 g, were individually housed in hanging wire-bottomed cages and were maintained at approximately 70°F on a 12-h light/dark cycle. All compounds were dissolved in corn oil (Mazola, Best Foods, Englewood Cliffs, NJ). Rats (six per group) were administered the corn oil solutions of Aroclor-1254, Aroclor-1242 (32 mg/kg per day), PCB-95, PCB-99, PCB-118 (16 mg/kg per day), PCB-126 (40 μg/kg per day), or TCDD (3.9 μg/kg per day) via gavage for 7 consecutive days at a dose volume of 5 ml/kg. The dose selection was based on our dose-response studies of these PCBs (Martin and Klaassen, 2010). Control rats were administered corn oil (5 ml/kg). All rats had ad libitum access to feed (Purina Rodent Chow, 5001; Purina, St. Louis, MO) and water. Body weights were recorded daily. Twenty-four hours after the last dose, animals were anesthetized with sodium pentobarbital (50 mg/ml), combined with 1:1 potassium iodide (1 mg/ml) at 2 ml/kg to prevent uptake of 125I into the thyroid. The femoral vein and artery were cannulated (PE 50) and primed with saline or heparinized saline (33 units/ml), respectively. Approximately 1 ml of blood was sampled from the artery from which serum was prepared and stored at −70°C for further assay. The bile duct was cannulated (PE 10), and the body temperature of each animal was maintained at 37°C using a heat lamp with a rectal thermometer. Ten minutes later, each rat was given 1 ml of [125I]T4 i.v. at 15 μCi/ml in 10 mM NaOH saline + 1% normal rat serum, and bile was collected on ice at 30-min intervals for 2 h. Fifteen minutes after the start of bile collection and three more times at 30-min intervals, approximately 300-μl aliquots of blood were collected from the femoral artery. At the end of the 2-h collection period, the urinary bladder was exposed, and urine was collected by puncture with needle and syringe. The liver was removed, weighed and snap frozen, and stored at −70°C. Bile and urine volumes were determined gravimetrically. Blood samples were centrifuged for 5 min to collect serum. Two aliquots (20 μl each) were taken from the bile, serum, and urine samples for gamma spectroscopy. After the addition of methanol (1:2) and storage at −20°C for 1 h to precipitate protein, bile was centrifuged at 12,000g (4°C) for 10 min, and the supernatant was collected for analysis by HPLC.

HPLC Analysis.

Beckman System Gold equipment and software (version 8.1) consisting of an Autosampler 507, Programmable Solvent Module 126, Radioisotope Detector 171 and 110B Solvent Delivery Module for pumping scintillation cocktail were used for HPLC (Beckman Coulter, Fullerton, CA). Reverse-phase HPLC was performed on a 10 × 0.3 cm ChromSpher C18 column in combination with both a ChromSep 10 × 2 mm reverse-phase guard column (Chrompack, Inc., Raritan, NJ) and a 7.5 × 4.6 mm Adsorbosphere C18 reverse-phase guard column (Alltech Associates, Inc., Deerfield, IL) with a 16 to 45% stepwise linear gradient of acetonitrile run against 0.02 M ammonium acetate, pH 4 for 1 h (Visser et al., 1993b). The sample volume injected was 20 μl. To determine the amount of T4-glucuronide present, the percent total area of the T4-glucuronide peak was multiplied by the total biliary radioactivity.

Determination of Serum T4 and T3.

The concentrations of total (representing free and protein-bound) T4 and T3 in serum were determined by radioimmunoassay. The limits of detection of these kits were 0.25 μg/dl and 7 ng/dl, respectively.

Microsome Preparation.

UGT activity toward T4 was determined in liver microsomes. Liver microsomes were prepared as described previously (Hood and Klaassen, 2000). In brief, liver tissue was homogenized in 2 volumes of ice-cold buffer containing 50 mM Tris and 150 mM potassium chloride (pH 7.5). Homogenates were centrifuged at 860g for 15 min, and the pellet was discarded. The supernatant was centrifuged at 23,300g for 25 min at 4°C, and the pellet was discarded. This second supernatant was decanted into ultracentrifuge tubes and was centrifuged at 105,000g for 1 h at 4°C. The resulting pellet was removed and homogenized in 1.15% potassium chloride containing 10 mM neutralized EDTA. The homogenate was centrifuged at 105,000g for 1 h at 4°C. The supernatant was discarded, and the microsomal pellet was homogenized in 0.4 ml/g tissue of 0.25 M sucrose. The homogenate was stored at −70°C until analysis. Protein concentrations in microsomes were determined according to the bicinchoninic acid method using a commercial assay kit with bovine serum albumin as the standard.

Purification of [125I]T4.

Free 125I label was removed from the stock [125I]T4 before use in the UGT activity assay (Vansell and Klaassen, 2001). Stock [125I]T4 was applied to a Sephadex LH-20 (Sigma-Aldrich, St. Louis, MO) column (0.5-ml bed volume), equilibrated with 0.1 N HCl. Free [125I]T4 was eluted from the column with 4 ml of 0.1 N HCl. The column was then rinsed with 4 ml of deionized water. Purified [125I]T4 was eluted by rinsing the column with 1.5 ml of an ethanol/ammonium hydroxide (98:2%) solution. The volume of the [125I]T4 was reduced to approximately 200 μl using a stream of nitrogen gas.

UGT Activity Toward T4.

UGT activity toward T4 in liver microsomes was evaluated by determining the amount of [125I]T4-glucuronide produced (Beetstra et al., 1991). All reactions contained 150 μl of reaction mixture with 75 mM Tris-HCl, 7.5 mM MgCl2, 30 mM UDP-glucuronic acid, 1 μM nonradioactive T4, approximately 100,000 counts per minute of [125I]T4, and 0.1 mM propylthiouracil to inhibit outer-ring deiodinases. Reactions were initiated by adding 50 μl of microsomal protein (final concentration, 250 μg/ml) before incubation for 1 h in a 37°C water bath. The reaction was terminated by placing the samples on ice and adding 200 μl of ice-cold methanol. The samples were centrifuged at 12,000g (4°C) for 45 min. The supernatant (200 μl) was poured over a Sephadex LH-20 column (1-ml bed volume) that had been equilibrated with 6 ml of 0.1 N HCl. Free 125I was eluted by rinsing the column with 2 ml of 0.1 N HCl. Columns were subsequently rinsed with 2 ml of deionized water. The [125I]T4-glucuronide was eluted by rinsing with 3 ml of deionized water, and to ensure complete elution of the glucuronide, the columns were rinsed with an additional 3 ml of deionized water. The [125I]T4 that remained unconjugated was eluted from the columns using 3 ml of ethanol: 0.1 N NaOH (1:1 v/v). The amount of [125I]T4 in the eluates was determined by gamma spectroscopy.

Statistics.

Differences between control and treated animals were determined using analysis of variance followed by the Duncan's multiple range post hoc test. Significant differences between treated and control groups (p < 0.05) are indicated by asterisks in the figures. Statistical analyses were performed using STATISTICA 4.5 (StatSoft, Inc., Tulsa, OK).

Results

No significant changes in body weight were produced by administration of PCBs or TCDD (data not shown). With the exception of PCB-95, all of the treatments produced significant increases in liver/body weight ratios (Fig. 1). Aroclor-1254 produced the greatest increase of 78%. PCB-99, PCB-118, and TCDD caused roughly equal increases in liver/body weight ratios of 42, 47, and 44%, respectively. Aroclor-1242 and PCB-126 produced more moderate, but still significant, increases in liver/body weight ratios of 33 and 25%, respectively.

Fig. 1.

Fig. 1.

Effects of PCBs and TCDD on liver/body weight ratios. Values represent the mean ± S.E.M. of six rats. *, significantly different from the control group (p < 0.05).

The effects of the PCBs on serum thyroid hormone concentrations after the 7-day dosage period are shown in Fig. 2. Each of the seven treatments produced significant reductions in serum total T4 (Fig, 2, top). The most dramatic reductions in serum T4 occurred in response to treatment with Aroclor-1254, PCB-99, and PCB-118 (95, 87, and 93%, respectively). Aroclor-1242, PCB-95, PCB-126, and TCDD caused nearly equal decreases of 73, 64, 74, and 71%, respectively. Serum total T3 levels were also significantly reduced by each of the compounds (Fig. 2, bottom). As with T4, the largest decreases in T3 occurred in response to treatment with Aroclor-1254, PCB-99, or PCB-118. These decreases were 53, 41, and 52%, respectively. Aroclor-1242, PCB-95, PCB-126, and TCDD caused decreases of 37, 36, 32, and 17%, respectively.

Fig. 2.

Fig. 2.

Effects of PCBs and TCDD on serum total T4 (top) and total T3 (bottom). Values represent the mean ± S.E.M. of six rats. *, significantly different from the control group (p < 0.05).

After the intravenous administration of radiolabeled T4 ([125I]T4), the concentration of [125I]T4 in serum was determined at 30-min intervals, beginning at 15 min after injection (Fig. 3). Each of the treatments significantly enhanced the disappearance of [125I]T4 from serum. Aroclor-1254, PCB-99, and PCB-118 decreased the serum concentration of [125I]T4 by more than 70% within 15 min of administration. Serum concentrations of [125I]T4 in these PCB-treated rats continued to be significantly lower, compared with the control group values, over the entire 2-h collection period by an average of 77%. Aroclor-1242, PCB-95, and PCB-126 also significantly enhanced the disappearance of [125I]T4 from serum within 15 min and continuing over the entire collection period; the reductions in serum concentrations of [125I]T4 caused by these three treatments were less dramatic than those caused by Aroclor-1254, PCB-99, and PCB-118, averaging approximately 45%. In contrast, TCDD did not significantly reduce serum [125I]T4 until the 45-min time point. The average reduction caused by TCDD was only 25% (9, 23, 32, and 39% at the 15, 45, 75, and 105-min time points, respectively).

Fig. 3.

Fig. 3.

Effects of PCBs and TCDD on the disappearance of [125I]T4 from serum. Values represent the mean ± S.E.M. of six rats. *, significantly different from the control group (p < 0.05).

The effect of PCBs and TCDD on bile flow was not appreciable (data not shown). Only Aroclor-1242 significantly increased bile flow and only at the 30- and 60-min time points. These increases were 36 and 37%, respectively.

The biliary excretion rate for total [125I]T4 (T4 and all metabolites) was significantly increased by Aroclor-1254, PCB-118, PCB-126, and TCDD (Fig. 4). Aroclor-1254 had the greatest effect, increasing the biliary excretion rate above the control rate by 558, 679, 444, and 334% at the 30, 60, 90, and 120-min time points, respectively. PCB-118 was nearly as effective as Aroclor-1254 in increasing the rate of biliary excretion of [125I]T4, causing 421, 452, 430, and 386% increases, compared with the control rate, at the 30, 60, 90, and 120-min time points, respectively. PCB-126 and TCDD were somewhat less effective, causing average increases in the rate of biliary excretion of 280 and 373%, respectively, over the 2-h collection period. Aroclor-1242, PCB-95, and PCB-99 did not significantly increase the rate of biliary excretion of [125I]T4.

Fig. 4.

Fig. 4.

Effects of PCBs and TCDD on the rate (top) and amount (bottom) of biliary excretion of [125I]T4. Values represent the mean ± S.E.M. of six rats. *, significantly different from the control group (p < 0.05).

The cumulative biliary excretion of [125I]T4 is shown in the bottom of Fig. 4. Consistent with the increases in the rate of excretion, Aroclor-1254, PCB-118, PCB-126, and TCDD produced significant increases in the amount of [125I]T4 excreted into bile over the 2-h collection period. As with the excretion rate, Aroclor-1254 was most effective in significantly increasing the cumulative amount of [125I]T4 present in bile at each of the time points, compared with the control group values. These increases were 561, 616, 565, and 508% at the 30-, 60-, 90-, and 120-min time points, respectively (average increase of 563%). PCB-118 caused similar increases, with an average increase of 456% over the 2-h collection period. PCB-126 and TCDD also significantly increased the cumulative amount of [125I]T4 present in bile, compared with the control, with average increases of 277 and 372%, respectively. Aroclor-1242, PCB-95, and PCB-99 did not significantly increase the amount of biliary excretion of [125I]T4.

HPLC analysis of bile samples revealed the predominant T4 metabolite to be T4-glucuronide (a representative chromatogram is depicted in Fig. 5). In control animals, the T4-glucuronide represented, on average, 86% of the radiolabeled iodothyronines present in bile. Figure 6 shows both the rate (top) and the cumulative amount (bottom) of biliary excretion of T4-glucuronide after pretreatment of the rats with the various polychlorinated biphenyls. The effects on the rate of excretion of T4-glucuronide were consistent with the effects on the overall rate of excretion of [125I]T4 (Fig. 4, top). The rate of biliary excretion of T4-glucuronide was significantly increased by Aroclor-1254, PCB-118, PCB-126, and TCDD. Aroclor-1254 was the most effective, causing an average increase of 850% over the 2-h collection period. PCB-118, PCB-126, and TCDD also markedly increased the rate of biliary excretion of T4-glucuronide, with increases over the 2-h collection period averaging 756, 573, and 710%, respectively. These four compounds consistently increased the amount of T4-glucuronide excreted into bile at 30, 60, 90, and 120 min: Aroclor-1254 by 992, 1100, 1000, and 938%; PCB-118 by 734, 848, 820, and 784%; PCB-126 by 525, 652, 664, and 614%; and TCDD by 602, 758, 769, and 705%, respectively. Aroclor-1242, PCB-95, and PCB-99 did not significantly increase the rate or amount of biliary excretion of T4-glucuronide. No other T4 metabolites were present in sufficient quantities to analyze.

Fig. 5.

Fig. 5.

A representative chromatogram of HPLC analysis of bile samples. T4-glucuronide was eluted at 19.14 min as a predominant T4 metabolite.

Fig. 6.

Fig. 6.

Effects of PCBs and TCDD on the rate (top) and amount (bottom) of biliary excretion of [125I]T4-glucuronide. Values represent the mean ± S.E.M. of six rats. *, significantly different from the control group (p < 0.05).

The amount of [125I]T4 and its metabolites excreted in urine during the 2-h collection period was only a small percentage (0.8 to 27%) of that present in bile (data not shown). Administration of PCBs and TCDD did not result in significant differences in urinary excretion of [125I]T4.

The effect of PCBs and TCDD on the activity of UGTs toward T4 was evaluated in liver microsomes and is shown in Fig. 7. Aroclor-1254, PCB-126, and TCDD were the most effective inducers of UGT activity toward T4, causing 789, 709, and 824% increases, respectively, in UGT activity compared with the control group value. Aroclor-1242 and PCB-118 were slightly less effective, producing increases in activity of 307 and 514%, respectively. PCB-95 and PCB-99 did not significantly increase the activity of UGTs toward T4.

Fig. 7.

Fig. 7.

Effects of PCBs and TCDD on the activity of hepatic UDP-UGTs toward T4. Values represent the mean ± S.E.M. of six rats. *, significantly different from the control group (p < 0.05).

Discussion

It is generally thought that the reduction in serum T4 produced by PCBs is due to increased glucuronidation of T4 followed by increased biliary excretion of T4-glucuronide (Bastomsky, 1974; Hood and Klaassen, 2000; Vansell and Klaassen, 2001; Craft et al., 2002). However, the present study demonstrates that at least one additional mechanism might be responsible for the reduction in serum T4 on the basis of the observations that PCB mixtures and congeners used in this study significantly reduced serum levels of T4 (Fig. 2), but not all of them significantly increased the in vivo excretion of T4-glucuronide into bile (Fig. 4) or increased the UGT activity toward T4 in vitro (Fig. 7).

We were not surprised that Aroclor-1254 and TCDD significantly increased the biliary excretion of T4-glucuronide in vivo, because it has been reported previously (Bastomsky, 1974; Vansell and Klaassen, 2001). However, we were surprised that only the PCB congeners with TCDD-like activity, namely PCB-118 and PCB-126, significantly increased the biliary excretion of T4-glucuronide in vivo, whereas the PB-type congeners, PCB-95 and PCB-99, did not. We have shown that PCB-118 and PCB-126 significantly increased CYP1A2 activity [as quantified by ethoxyresorufin-O-deethylase (EROD) activity], whereas PCB-95 and PCB-99 increased CYP1B2 activity [as quantified by pentoxyresorufin-O-deethylase (PROD) activity] (Martin and Klaassen, 2010).

The effects of PCB congeners on UGT activity toward T4 in vitro were consistent with the in vivo excretion results. Aroclor-1254, PCB-118, PCB-126, and TCDD were the most effective inducers of UGT activity toward T4 in vitro. PCB-95 and PCB-99 (PB-type) had no effect on UGT activity toward T4. These results are supported by the observation that PCB-110 (a PB-type congener) did not induce hepatic UGT activity unless it was contaminated with PCB-126 (Li et al., 1998). When a PCB-contaminated soil sample is filtered with charcoal to remove the coplanar (TCDD-like) congeners, induction of UGT activity is abolished (Li and Hansen, 1997). These data suggest that the ability of the PCBs to induce UGT activity toward T4 is related to the level of TCDD-like activity of these compounds.

The mechanism by which TCDD induces gene transcription begins by interaction with a soluble cytoplasmic receptor known as the AhR. The ligand (TCDD) and the receptor are then translocated to the nucleus where the heterodimerization with the AhR nuclear translocator occurs. The receptor–ligand complex then interacts with xenobiotic response elements, which are cis-acting DNA sequences that induce transcription of genes (Whitlock, 1993). Transcriptional regulation of the genes encoding UGT1A6 in rat liver is mediated by xenobiotic response elements, and this gene is inducible by the AhR ligands 3-MC and TCDD (Emi et al., 1996; Masmoudi et al., 1997). It is currently thought that this UGT isoform is at least partially responsible for glucuronidation of T4. Evidence for this includes impaired T4 glucuronidation in Gunn rats, which have a genetic defect in all UGT1 gene products (Visser et al., 1993a). In addition, induction of UGT activity toward p-nitrophenol (a specific substrate of UGT1A6) by 3-MC, PCBs, and TCDD also increased the glucuronidation of T4 but not T3 (Beetstra et al., 1991; Visser et al., 1993b; van Raaij et al., 1993). In regard to PCBs, these data support the theory that induction of UGT activity toward T4 is mediated by the TCDD-like activity of these compounds. This also explains the lack of induction of UGT activity toward T4 by the PB-type congeners, which do not bind to the AhR (Safe et al., 1985).

Whereas there appears to be a good correlation between the ability of these PCBs to increase UGT activity toward T4 in vitro and to increase the excretion of T4-glucuronide in vivo, there is not a good correlation with this ability to lower serum T4 levels. The AhR ligands, Aroclor-1254, PCB-118, PCB-126, and TCDD, were the most effective inducers of UGT activity toward T4 in vitro and produced the greatest increases in biliary excretion of T4-glucuronide in vivo. The PB-type congeners (PCB-95 and PCB-99) did not induce UGT activity toward T4 in vitro or increase the biliary excretion of T4-glucuronide in vivo. According to present theory, one would anticipate that the TCDD-type congeners would decrease serum T4 the most and the PB-type congeners would not be as effective. However, this hypothesis is not supported by the results of the current study. PCB-99, which was one of the most effective congeners at reducing serum levels of T4, did not induce UGT activity toward T4 or increase the biliary excretion of T4-glucuronide. In addition, two of the compounds that increased UGT activity the most (TCDD and PCB-126) were less effective at reducing serum levels of T4 than PCB-99. This suggests that the PB-like activity of the mixtures and congeners is responsible for perturbation of pathways that are not related to UGT induction.

The reductions in circulating levels of T4 seem to correlate with the disappearance of [125I]T4 from the serum of these PCB-treated rats. Within 15 min of administration of [125I]T4, the serum level of [125I]T4 in the rats administered Aroclor-1254, PCB-99, or PCB-118 was less than 30% of that of controls (Fig. 3). PCB-95, Aroclor-1242, PCB-126, and TCDD also significantly increased the disappearance of [125I]T4 from serum, but much less dramatically. These results mirror those observed for circulating levels of T4. The rapid disappearance of [125I]T4 from the plasma of rats treated with Aroclor-1254, PCB-99, or PCB-118 suggests that the PB-like activity of these compounds must be important for increased T4 clearance. It is hypothesized that these compounds may increase tissue uptake of T4 by increasing thyroid hormone transport across cell membranes.

Thyroid hormones most likely do not diffuse but are actively transported across cell membranes (Hennemann et al., 2001). Several transport proteins have been identified and cloned from rat liver that are thought to mediate the transport of thyroid hormones, including the organic anion-transporting polypeptides Oatp1a1, Oatp1a4, and Oatp1b2, as well as the sodium taurocholate cotransporting polypeptide Ntcp (Docter et al., 1997; Abe et al., 1998; Friesema et al., 1999; Fujiwara et al., 2001). Treatment of male Sprague-Dawley rats with PB increased Oatp1a4 protein levels in liver and enhanced the uptake of digoxin (substrate for Oatp1a4) (Hagenbuch et al., 2001). Another study reported the induction of Oatp1a4 protein by PB and PCN (Rausch-Derra et al., 2001). These reports reinforce findings in previous studies that pretreatment with PCN and PB increased the hepatic uptake and biliary excretion of cardiac glycosides (Klaassen, 1974) and suggest that the increased hepatic uptake of cardiac glycosides may be due, at least in part, to up-regulation of Oatp1a4.

It is conceivable that PCB-99, PCB-118, and Aroclor-1254, which have PB-like activity (induction of CYP2B) (Martin and Klaassen, 2010), may also induce Oatp1a4 and increase hepatic uptake of T4. In fact, it has been shown that Oatp1a4 protein was increased 130% by PCB-99 but was decreased 72% by PCB-126 (Guo et al., 2002). If hepatic uptake of T4 is increased by PCB-99 and decreased in response to PCB-126, this may, at least in part, explain the differential effects of PCB-99 and PCB-126 on serum T4. PCB-99 effectively reduces serum T4 without inducing UGT activity toward T4 or increasing the biliary excretion of T4-glucuronide, whereas PCB-126 is less effective at reducing serum levels of T4 while significantly inducing UGT activity toward T4. The other PB-type congener, PCB-95, also significantly increased the disappearance of [125I]T4 without inducing UGT activity or increasing the biliary excretion of T4-glucuronide. However, PCB-95 was less effective than PCB-99 in decreasing plasma T4 levels, which probably reflects the more labile, metabolizable structure of PCB-95 (Matthews and Dedrick, 1984).

The selective antagonist of corticotropin-releasing factor receptor-1, DMP 904, dramatically increased the biliary clearance of unconjugated [125I]T4 in rats, at least in part by enhanced hepatic uptake of [125I]T4 through induction of Oatp1a1 and Oatp1a4 (Wong et al., 2005). DMP 904 also induced a canalicular transporter, namely the multidrug resistance protein-2 (Mrp2) (Wong et al., 2005). Further study demonstrated that DMP 904 increased plasma clearance and hepatic uptake of [125I]T4 in Wistar but not in Mrp2-deficient TR(−) rats, suggesting that Mrp2 is responsible for biliary excretion of T4-glucuronide and contributes in part to the excretion of T4 (Lecureux et al., 2009). Sulfation is another pathway for thyroid hormone metabolism (Wu et al., 2005) and contributes a small part to the biliary excretion of T3, which was increased by PCN but not by PCB (Vansell and Klaassen, 2002).

In conclusion, the present study provides evidence that the effects of PCB mixtures and congeners on serum levels of T4 cannot be explained solely by induction of UGT activity toward T4 and enhanced excretion of T4-glucuronide. There appear to be two major effects of PCBs on serum T4. One is increased glucuronidation and increased biliary excretion, which is associated with binding to the AhR, and the second is enhanced tissue uptake, which is associated with the PB-like characteristics of the congeners. Increased glucuronidation facilitates biliary excretion of T4-glucuronide; however, it appears that reductions in serum T4 are more dependent on uptake, probably through transport proteins such as Oatp1a4.

This work was supported by the National Institutes of Health National Institute of Environmental Health Sciences [Grants ES013714, ES09716] [Training Grants ES07079, ES05022, ES07148]; the National Institutes of Health National Institute of Diabetes and Digestive and Kidney Diseases [Grant DK-081461]; and the National Institutes of Health National Center for Research Resources [Grant RR021940].

Article, publication date, and citation information can be found at http://dmd.aspetjournals.org.

http://dx.doi.org/10.1124/dmd.111.042796.

ABBREVIATIONS:
T3
triiodothyronine
T4
thyroxine
PCN
pregnenolone-16α-carbonitrile
TCDD
2,3,7,8-tetrachlorodibenzo-p-dioxin
PCB
polychlorinated biphenyl
AhR
aryl hydrocarbon receptor
PB
phenobarbital
PCB-126
3,3′4,4′,5-pentachlorobiphenyl
PCB-95
2,2′,3,5′,6-pentachlorobiphenyl
PCB-99
2,2′,4,4′,5-pentachlorobiphenyl
PCB-118
2,3′,4,4′,5-pentachlorobiphenyl
HPLC
high-performance liquid chromatography
UGT
UDP-glucuronosyltransferase
EROD
ethoxyresorufin-O-deethylase
PROD
pentoxyresorufin-O-deethylase
3-MC
3-methylcholanthrene
Mrp2
multidrug resistance protein-2.

Authorship Contributions

Participated in research design: Martin and Klaassen.

Conducted experiments: Martin and Wilson.

Performed data analysis: Martin and Wilson.

Wrote or contributed to the writing of the manuscript: Martin, Reuhl, Gallo, and Klaassen.

References

  1. Abe T, Kakyo M, Sakagami H, Tokui T, Nishio T, Tanemoto M, Nomura H, Hebert SC, Matsuno S, Kondo H, et al. (1998) Molecular characterization and tissue distribution of a new organic anion transporter subtype (oatp3) that transports thyroid hormones and taurocholate and comparison with oatp2. J Biol Chem 273:22395–22401 [DOI] [PubMed] [Google Scholar]
  2. Barter RA, Klaassen CD. (1992) UDP-glucuronosyltransferase inducers reduce thyroid hormone levels in rats by an extrathyroidal mechanism. Toxicol Appl Pharmacol 113:36–42 [DOI] [PubMed] [Google Scholar]
  3. Bastomsky CH. (1974) Effects of a polychlorinated biphenyl mixture (aroclor 1254) and DDT on biliary thyroxine excretion in rats. Endocrinology 95:1150–1155 [DOI] [PubMed] [Google Scholar]
  4. Beetstra JB, van Engelen JG, Karels P, van der Hoek HJ, de Jong M, Docter R, Krenning EP, Hennemann G, Brouwer A, Visser TJ. (1991) Thyroxine and 3,3′,5-triiodothyronine are glucuronidated in rat liver by different uridine diphosphate-glucuronyltransferases. Endocrinology 128:741–746 [DOI] [PubMed] [Google Scholar]
  5. Capen CC. (1994) Mechanisms of chemical injury of thyroid gland. Prog Clin Biol Res 387:173–191 [PubMed] [Google Scholar]
  6. Collins WT, Jr, Capen CC. (1980) Biliary excretion of 125I-thyroxine and fine structural alterations in the thyroid glands of Gunn rats fed polychlorinated biphenyls (PCB). Lab Invest 43:158–164 [PubMed] [Google Scholar]
  7. Craft ES, DeVito MJ, Crofton KM. (2002) Comparative responsiveness of hypothyroxinemia and hepatic enzyme induction in Long-Evans rats versus C57BL/6J mice exposed to TCDD-like and phenobarbital-like polychlorinated biphenyl congeners. Toxicol Sci 68:372–380 [DOI] [PubMed] [Google Scholar]
  8. De Voogt P, Brinkman AT. (1989). Production properties and usage of polychlorinated biphenyls, in Halogenated Biphenyls, Terphenyls, Naphthalenes and Dibenzodioxins and Related Products (Kimbrough RD, Jensen AA. eds), Elsevier, New York [Google Scholar]
  9. Docter R, Friesema EC, van Stralen PG, Krenning EP, Everts ME, Visser TJ, Hennemann G. (1997) Expression of rat liver cell membrane transporters for thyroid hormone in Xenopus laevis oocytes. Endocrinology 138:1841–1846 [DOI] [PubMed] [Google Scholar]
  10. Emi Y, Ikushiro S, Iyanagi T. (1996) Xenobiotic responsive element-mediated transcriptional activation in the UDP-glucuronosyltransferase family 1 gene complex. J Biol Chem 271:3952–3958 [DOI] [PubMed] [Google Scholar]
  11. Friesema EC, Docter R, Moerings EP, Stieger B, Hagenbuch B, Meier PJ, Krenning EP, Hennemann G, Visser TJ. (1999) Identification of thyroid hormone transporters. Biochem Biophys Res Commun 254:497–501 [DOI] [PubMed] [Google Scholar]
  12. Fujiwara K, Adachi H, Nishio T, Unno M, Tokui T, Okabe M, Onogawa T, Suzuki T, Asano N, Tanemoto M, et al. (2001) Identification of thyroid hormone transporters in humans: different molecules are involved in a tissue-specific manner. Endocrinology 142:2005–2012 [DOI] [PubMed] [Google Scholar]
  13. Guo GL, Choudhuri S, Klaassen CD. (2002) Induction profile of rat organic anion transporting polypeptide 2 (oatp2) by prototypical drug-metabolizing enzyme inducers that activate gene expression through ligand-activated transcription factor pathways. J Pharmacol Exp Ther 300:206–212 [DOI] [PubMed] [Google Scholar]
  14. Hagenbuch B. (2007) Cellular entry of thyroid hormones by organic anion transporting polypeptides. Best Pract Res Clin Endocrinol Metab 21:209–221 [DOI] [PubMed] [Google Scholar]
  15. Hagenbuch N, Reichel C, Stieger B, Cattori V, Fattinger KE, Landmann L, Meier PJ, Kullak-Ublick GA. (2001) Effect of phenobarbital on the expression of bile salt and organic anion transporters of rat liver. J Hepatol 34:881–887 [DOI] [PubMed] [Google Scholar]
  16. Hennemann G, Docter R, Friesema EC, de Jong M, Krenning EP, Visser TJ. (2001) Plasma membrane transport of thyroid hormones and its role in thyroid hormone metabolism and bioavailability. Endocr Rev 22:451–476 [DOI] [PubMed] [Google Scholar]
  17. Hood A, Klaassen CD. (2000) Differential effects of microsomal enzyme inducers on in vitro thyroxine (T(4)) and triiodothyronine (T(3)) glucuronidation. Toxicol Sci 55:78–84 [DOI] [PubMed] [Google Scholar]
  18. Klaassen CD. (1974) Effect of microsomal enzyme inducers on the biliary excretion of cardiac glycosides. J Pharmacol Exp Ther 191:201–211 [PubMed] [Google Scholar]
  19. Lecureux L, Dieter MZ, Nelson DM, Watson L, Wong H, Gemzik B, Klaassen CD, Lehman-McKeeman LD. (2009) Hepatobiliary disposition of thyroid hormone in Mrp2-deficient TR- rats: reduced biliary excretion of thyroxine glucuronide does not prevent xenobiotic-induced hypothyroidism. Toxicol Sci 108:482–491 [DOI] [PubMed] [Google Scholar]
  20. Li MH, Hansen LG. (1997) Consideration of enzyme and endocrine interactions in the risk assessment of PCBs. Rev Toxicol 1:71–156 [Google Scholar]
  21. Li M, Rhine C, Hansen LG. (1998) Hepatic enzyme induction and acute endocrine effects of 2,3,3′,4′,6-pentachlorobiphenyl in prepubertal female rats. Arch Environ Contam Toxicol 35:97–103 [DOI] [PubMed] [Google Scholar]
  22. Liu J, Liu Y, Barter RA, Klaassen CD. (1995) Alteration of thyroid homeostasis by UDP-glucuronosyltransferase inducers in rats: a dose-response study. J Pharmacol Exp Ther 273:977–985 [PubMed] [Google Scholar]
  23. Martin L, Klaassen CD. (2010) Differential effects of polychlorinated biphenyl congeners on serum thyroid hormone levels in rats. Toxicol Sci 117:36–44 [DOI] [PMC free article] [PubMed] [Google Scholar]
  24. Masmoudi T, Hihi AK, Vázquez M, Artur Y, Desvergne B, Wahli W, Goudonnet H. (1997) Transcriptional regulation by triiodothyronine of the UDP-glucuronosyltransferase family 1 gene complex in rat liver. Comparison with induction by 3-methylcholanthrene. J Biol Chem 272:17171–17175 [DOI] [PubMed] [Google Scholar]
  25. Matthews HB, Dedrick RL. (1984) Pharmacokinetics of PCBs. Annu Rev Pharmacol Toxicol 24:85–103 [DOI] [PubMed] [Google Scholar]
  26. McClain RM, Levin AA, Posch R, Downing JC. (1989) The effect of phenobarbital on the metabolism and excretion of thyroxine in rats. Toxicol Appl Pharmacol 99:216–228 [DOI] [PubMed] [Google Scholar]
  27. Murk AJ, Legler J, Denison MS, Giesy JP, van de Guchte C, Brouwer A. (1996) Chemical-activated luciferase gene expression (CALUX): a novel in vitro bioassay for Ah receptor active compounds in sediments and pore water. Fundam Appl Toxicol. 33:149–160 [DOI] [PubMed] [Google Scholar]
  28. Rausch-Derra LC, Hartley DP, Meier PJ, Klaassen CD. (2001) Differential effects of microsomal enzyme-inducing chemicals on the hepatic expression of rat organic anion transporters, OATP1 and OATP2. Hepatology 33:1469–1478 [DOI] [PubMed] [Google Scholar]
  29. Safe S, Bandiera S, Sawyer T, Robertson L, Safe L, Parkinson A, Thomas PE, Ryan DE, Reik LM, Levin W. (1985) PCBs: structure-function relationships and mechanism of action. Environ Health Perspect 60:47–56 [DOI] [PMC free article] [PubMed] [Google Scholar]
  30. Schuur AG, Boekhorst FM, Brouwer A, Visser TJ. (1997) Extrathyroidal effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin on thyroid hormone turnover in male Sprague-Dawley rats. Endocrinology 138:3727–3734 [DOI] [PubMed] [Google Scholar]
  31. Semler DE, Chengelis CP, Radzialowski FM. (1989) The effects of chronic ingestion of spironolactone on serum thyrotropin and thyroid hormones in the male rat. Toxicol Appl Pharmacol 98:263–268 [DOI] [PubMed] [Google Scholar]
  32. van Raaij JA, Kaptein E, Visser TJ, van den Berg KJ. (1993) Increased glucuronidation of thyroid hormone in hexachlorobenzene-treated rats. Biochem Pharmacol 45:627-631 [DOI] [PubMed] [Google Scholar]
  33. Vansell NR, Klaassen CD. (2001) Increased biliary excretion of thyroxine by microsomal enzyme inducers. Toxicol Appl Pharmacol 176:187–194 [DOI] [PubMed] [Google Scholar]
  34. Vansell NR, Klaassen CD. (2002) Effect of microsomal enzyme inducers on the biliary excretion of triiodothyronine (T(3)) and its metabolites. Toxicol Sci 65:184–191 [DOI] [PubMed] [Google Scholar]
  35. Visser TJ. (1990) Importance of deiodination and conjugation in the hepatic metabolism of thyroid hormone, in The Thyroid Gland (Greer MA. ed) pp 255–283, Raven Press Ltd, New York [Google Scholar]
  36. Visser TJ, Kaptein E, van Raaij JA, Joe CT, Ebner T, Burchell B. (1993a) Multiple UDP-glucuronyltransferases for the glucuronidation of thyroid hormone with preference for 3,3′,5′-triiodothyronine (reverse T3). FEBS Lett 315:65–68 [DOI] [PubMed] [Google Scholar]
  37. Visser TJ, Kaptein E, van Toor H, van Raaij JA, van den Berg KJ, Joe CT, van Engelen JG, Brouwer A. (1993b) Glucuronidation of thyroid hormone in rat liver: effects of in vivo treatment with microsomal enzyme inducers and in vitro assay conditions. Endocrinology 133:2177–2186 [DOI] [PubMed] [Google Scholar]
  38. Whitlock JP., Jr (1993) Mechanistic aspects of dioxin action. Chem Res Toxicol 6:754–763 [DOI] [PubMed] [Google Scholar]
  39. Wong H, Lehman-McKeeman LD, Grubb MF, Grossman SJ, Bhaskaran VM, Solon EG, Shen HS, Gerson RJ, Car BD, Zhao B, et al. (2005) Increased hepatobiliary clearance of unconjugated thyroxine determines DMP 904-induced alterations in thyroid hormone homeostasis in rats. Toxicol Sci 84:232–242 [DOI] [PubMed] [Google Scholar]
  40. Wu SY, Green WL, Huang WS, Hays MT, Chopra IJ. (2005) Alternate pathways of thyroid hormone metabolism. Thyroid 15:943–958 [DOI] [PubMed] [Google Scholar]

Articles from Drug Metabolism and Disposition are provided here courtesy of American Society for Pharmacology and Experimental Therapeutics

RESOURCES