Activity of thyroid hormone-inducible enzymes following treatment with 2,3,7,8-tetrachlorodibenzo-p-dioxin

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) caused a depletion of serum thyroxine, but paradoxically did not change L-3,5,3'-triiodothyronine (T3) levels in serum of rats. The activities of the thyroid-regulated enzymes alpha-glycerol phosphate dehydrogenase (GPD) and malic enzyme (ME) were determined in livers of normal and thyroidectomized (THX) rats treated with 0.1 to 100 nmol TCDD/kg body weight. Mitochondrial GPD activity did not change significantly as a function of TCDD dose in either normal or THX rats. ME activity was induced by TCDD in a dose-dependent fashion, but only in non-THX animals. The absence of ME induction in THX rats treated with TCDD indicates that TCDD is not intrinsically thyromimetic. The dependence of ME induction on thyroid hormones is much like the thyroid-hormone-dependent, multihormonal induction of ME by insulin and glucocorticoids. However, TCDD had no additive or synergistic effects on induction of ME activity in THX rats fed T3. A 30% decrease in steady-state plasma T3 levels of T3-fed animals treated with TCDD relative to T3-fed controls suggested that T3 catabolism was more rapid in TCDD-treated rats than controls. Thus a thyroid-hormone-dependent, multihormonal interaction is suggested as the basis for induction of ME by TCDD, but a strictly T3-dependent process has not been ruled out.     

Effect of 2,3,7,8-tetrachlorodibenzo-p-dioxin on the hepatic metabolism of testosterone in the rat

A dose of 20 micrograms/kg of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was given to adult male rats intragastrically and the metabolism of [4-14C]-testosterone by liver homogenate was examined 1 week later. The overall catabolism of testosterone was significantly reduced by the TCDD treatment. Dihydroxysteroids (intermediate reduced metabolites) were increased, while the production of polar non-conjugated metabolites (end products) was diminished.     

Effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin treatment on mechanical function of the rat heart

Mechanical responses of isolated atria to (-)-isoproterenol and activities of myocardial pyruvate kinase and citrate synthase, enzymes involved in energy metabolism, were assessed in rats 7 days after 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) treatment. Basal tension development by electrically paced left atria was significantly elevated by all doses of TCDD (6.25, 25, or 100 micrograms/kg) when compared to that of vehicle-treated rats with unlimited access to feed. The basal rate of spontaneously beating right atria was significantly depressed in rats receiving 100 micrograms/kg TCDD. In left atria from rats treated with 100 micrograms/kg TCDD, maximal inotropic responses to (-)-isoproterenol and 1-methyl-3-isobutylxanthine were enhanced to the same degree. Right and left atria from rats receiving 100 micrograms/kg TCDD had an increased sensitivity to the chronotropic and inotropic effects of (-)-isoproterenol, respectively. The augmented atrial effects caused by TCDD were not secondary to loss of body weight because pair-fed animals that lost the same amount of weight did not display the responses. The ratio of heart ventricular mass to body weight and the activities of pyruvate kinase and citrate synthase in homogenates of heart ventricular muscle were not affected by TCDD treatment. Thus, overtly toxic doses of TCDD in the rat did not depress mechanical function of the heart.     

Hepatic metabolism of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in the rat and guinea pig

Marked interspecies variability exists in the acute toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), with the rat having an LD50 about 25-fold greater than the guinea pig. The metabolism of TCDD was examined by incubating hepatocytes isolated from these animals with purified [14C]TCDD (2.2 microM) for 8 hr. Over the 8-hr incubation, cytochrome P-450 content and ethoxyresorufin O-deethylase and benzphetamine N-demethylase activities were well maintained, indicating the functional viability of the hepatocytes. Quantitative differences were observed in the rate of [14C]TCDD metabolism, with hepatocytes from control rats metabolizing TCDD at a rate 2.8-fold greater than hepatocytes from control guinea pigs. The role of the hepatic cytochrome P-450-448-dependent monooxygenase system in the metabolism of TCDD was examined through the use of hepatocytes isolated from animals pretreated with either TCDD (5 micrograms/kg, ip; 72 hr prior to hepatocyte isolation) or phenobarbital (80 mg/kg, ip X 3 days; 24 hr prior to isolation). The rate of [14C]TCDD metabolite formation in hepatocytes from TCDD pretreated guinea pigs (0.26 +/- 0.14 pmol mg cell protein-1 hr-1) was unchanged from the control rate (0.25 +/- 0.07), while the rate in hepatocytes from TCDD pretreated rats (2.26 +/- 0.43 pmol mg-1 hr-1) was 3.2-fold greater than control (0.70 +/- 0.10) and nine times greater than in hepatocytes from TCDD-pretreated guinea pigs. In addition, significant differences were observed in the profiles of the metabolites formed by hepatocytes from TCDD-pretreated rats and guinea pigs. On the other hand, phenobarbital pretreatment produced little change in the rate of [14C]TCDD metabolism in rat hepatocytes (0.98 +/- 0.13 pmol mg-1 hr-1). These results suggest that TCDD may be metabolized by a TCDD inducible form of cytochrome P-448 which is expressed in the rat but not in the guinea pig. Furthermore, the differences in the hepatic metabolism of TCDD in the rat and guinea pig and in the ability of TCDD to induce its own rate of metabolism may play a major role in explaining the varying susceptibility of these species to the acute toxicity of TCDD.     

Hepatocarcinogenesis in female Sprague-Dawley rats following discontinuous treatment with 2,3,7,8-tetrachlorodibenzo-p-dioxin.

In this study, we investigated the time course of promotion of tumors and putatively preneoplastic altered hepatic foci in the livers of diethylnitrosamine (DEN)-initiated female Sprague-Dawley rats. These rats had been treated with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) under different dosing regimens, but we used the same administered biweekly dose of 1.75 microg/kg of body weight. Animals were treated continuously for up to 60 weeks, or continuously for 30 weeks, followed by cessation of treatment for up to 30 weeks. In addition, TCDD treatment in these groups was begun either 2 or 18 weeks after initiation with DEN. Liver tumors were only observed in animals after 60 weeks on the study and were increased by continuous TCDD treatment, relative to controls. The incidence of hepatocellular adenoma and carcinoma combined, in animals treated with TCDD for 30 weeks followed by no TCDD treatment for 30 weeks (17%), was lower than in animals receiving either TCDD (79%) or vehicle control (corn oil) alone (55%) for 60 weeks. The lower liver-tumor incidence after cessation of TCDD treatment paralleled time-dependent decreases in the volume fraction occupied by placental glutathione S-transferase-positive altered hepatic foci and the number of foci per unit volume, but not the mean focus volume that exhibited a time-dependent increase after cessation of TCDD treatment. Cessation of TCDD treatment led to reductions in liver TCDD levels, and these changes were reflected in a cessation of reduced body weight because of TCDD treatment. These data indicate that liver-tumor promotion by TCDD in female rats is dependent upon continuous exposure to TCDD, and that alterations in patterns of TCDD exposure can have significant effects on tumor incidence not reflected by standard measures of dioxin exposure.     

The fate of 2,3,7,8-tetrachlorodibenzo-p-dioxin following single and repeated oral doses to the rat.

Rats were given a single oral dose of 1.0 μg of [¹⁴C]-2,3,7,8-Tetrachlorodibenzo-p-dioxin ([¹⁴C]TCDD)/kg/day, or repeated oral doses of 0.01, 0.1, or 1.0 μg of [¹⁴C]TCDD/kg/day Monday through Friday for 7 weeks. Following a single oral dose of 1.0 μg of [¹⁴C]TCDD/kg, ¹⁴C activity could be detected only in feces, but not in urine. The half-life of ¹⁴C activity in the body was 31 ± 6 days. Twenty-two days after the single oral dose, concentrations of ¹⁴C activity were located principally in liver and fat. Following repeated oral doses the major route of excretion was via the feces; urine contained 3–18% of the cumulative dose of ¹⁴C activity by 7 weeks. The half-life of ¹⁴C activity in the body of these rats was 23.7 days. Assuming a one compartment open model, 76.2% of steady-state concentrations were achieved in the whole body after 7 weeks. ¹⁴C activity in liver and fat approached steady-state values at a rate similar to the whole body. Radioactivity in the liver was identified as TCDD by gas chromatography-mass spectrometry and could be extracted from liver tissue with organic solvents. The results of this study in rats indicate that TCDD approaches steady-state concentrations in the body within 13 weeks, and the rate constant defining the approach to steady-state concentrations is independent of the dosage of TCDD over the dose range of 0.01?1.0 μg of TCDD/kg/day.     

Effect of monooxygenase inducers and inhibitors on the hepatic metabolism of 2,3,7,8-tetrachlorodibenzo-p-dioxin in the rat and hamster

The rat and hamster exhibit about a 100-fold difference in sensitivity to the acute toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), with the hamster representing the most resistant species examined to date. The present study compared the induction and inhibition of hepatic TCDD metabolism in these species using suspensions of isolated hepatocytes. Purified 14C-TCDD or 3H-TCDD (2.2 microM) was incubated for 2-6 hr with hepatocytes isolated from untreated, TCDD-pretreated (5 micrograms/kg, ip), 3-methylcholanthrene-pretreated (3-MC, 50 mg/kg, ip, x 3 days), isosafrole-pretreated (ISO, 150 mg/kg, ip, x 3 days), or phenobarbital-pretreated (PB, 80 mg/kg, ip, x 3 days) rats and hamsters. Untreated rat and hamster hepatocytes metabolized TCDD at a similar rate (0.20 and 0.18 pmol/hr/mg, respectively). In both species, TCDD and 3-MC pretreatments elevated the rate of TCDD metabolism by 5-6-fold, while PB pretreatment had no effect. isosafrole modestly increased (1.8-2.5-fold) TCDD metabolism in each species. Analysis by high performance liquid chromatography indicated similarities in the TCDD-metabolite profiles formed by hepatocytes from both species, with two major metabolite peaks detected following induction by TCDD and 3-MC. The in vitro metabolism of TCDD in hepatocytes from TCDD-pretreated rats and hamsters was inhibited by 7,8-benzoflavone (100 microM), but not by metyrapone (100 microM). The effect of these cytochrome P-450 inducers and inhibitors on the metabolism of 3H-benzo(a)pyrene (BaP) in rat hepatocytes was similar to their effect on TCDD metabolism. However, marked differences were observed in their effects on the metabolism of BaP and TCDD in hamster hepatocytes.(ABSTRACT TRUNCATED AT 250 WORDS)     

Lymphocyte stem cell alterations following perinatal exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin

Perinatal exposure of experimental animals to the environmental contaminant 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) leads to thymic atrophy and a suppression of cell-mediated immunity that is more severe and persistent than that caused by adult exposure, suggesting that events involved in the maturation of the immune system are particularly sensitive to TCDD. We report here that perinatal TCDD exposure produces an alteration in the lymphocyte stem cell population in the fetus and neonate, as evidenced by a significant reduction in the lymphocyte stem cell-specific enzyme terminal deoxynucleotidyl transferase (TdT). After maternal treatment with a single dose of TCDD (10 micrograms/kg of body weight) on gestational day (gd) 14, TdT biosynthesis and TdT-specific mRNA were reduced more than 50% in fetal liver lymphoid cells on gd 18. An even more extensive reduction was seen in neonatal bone marrow through postnatal day 18. In contrast, thymic TdT synthesis appeared to be relatively unaffected on a per cell basis by perinatal TCDD exposure, although the actual number of TdT-synthesizing thymocytes was diminished due to extensive thymic atrophy. These effects occurred at concentrations of 1-31 fg of TCDD/mg of thymus. Flow cytometric analysis of thymocyte surface marker expression revealed a slight decrease in the percentage of Lyt-2+L3T4+ thymocytes on gd 18 and postnatal day 4. This alteration was no longer apparent by postnatal day 11, when marrow TdT biosynthesis was most suppressed. These results suggest that TCDD-induced thymic atrophy during the perinatal period may be due, in part, to an effect on the prothymocyte.     

Relationship between acute toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and disturbance of intermediary metabolism in the Long-Evans rat

The effects of the non-steroidal anti-inflammatory drugs fenbufen and ibuprofen on hepatic cytochrome P450 activities and peroxisomal proliferation were investigated in the rat, following intraperitoneal administration at three dose levels. At the two highest doses, 30 and 150 mg/kg, ibuprofen stimulated lauric acid hydroxylase activity but no other dose-dependent effects on cytochrome P450 activities were evident. Fenbufen, at the highest dose of 150 mg/kg, decreased cytochrome P450 content and related activities, and this effect was attributed to the toxicity of the drug at this dose. Immunoblot studies employing solubilized microsomes from ibuprofen-treated rats revealed that ibuprofen increased the apoprotein levels of CYP4A1, at the two higher doses. The same treatment with ibuprofen, at the highest dose only, increased the β-oxidation of palmitoyl CoA, determined in liver homogenates, and immunoblott analysis showed an increase in the apoprotein levels of therans-2-enyol CoA hydratase trifunctional protein. Fenbufen did not influence palmitoyl β-oxidation. Computer graphic overlays with clofibric acid showed that ibuprofen, when compared with fenbufen, displayed a better overall fit to clofibric acid. Finally, interaction energies between the two drugs and the putative peroxisome proliferator-activated receptor lignad domain revealed that ibuprofen had a higher affinity for the receptor than fenbufen, but the difference was modes. It is concluded that ibuprofen, at doses far exceeding those employed clinically, is a weak inducer of both CYP4A1 activity and peroxisomal proliferation and these effects may be attributed to the presence of an aryl propionic acid moiety. These results are discussed with reference to the role of CYP4A induction and peroxisomal proliferation in the hepatotoxicity of this class od drugs.     

Response of the antral mucosa of the rat stomach to 2,3,7,8-tetrachlorodibenzo-p-dioxin.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) produces a striking hypergastrinemia in rats that is thought to mediate the antiatrophy effect of TCDD on the oxyntic gland mucosa of the stomach. However, effects of TCDD on the antral mucosa, which is the origin of most physiologically released gastrin and is not a target for the trophic action of gastrin, has yet to be thoroughly investigated. Also gastrin release from gastrin-containing cells (i.e., G-cells) in the antral mucosa is inhibited by the paracrine secretion of somatostatin from D-cells in the antrum. Our purpose was to determine if the antral mucosa is affected by the trophic influence of TCDD and if alterations in antral mucosa levels of gastrin or somatostatin cause the hypergastrinemia. TCDD (100 micrograms/kg, Day 14 post-treatment) had a trophic effect on the antral mucosa. This was demonstrated histologically and by significant increases in antral wet weight and antral mucosa height. In contrast, pair-fed control rats that lost the same amount of body weight developed antral mucosa atrophy. With respect to serum and antral levels of gastrointestinal hormones, TCDD produced a 7- to 10-fold increase in serum gastrin concentrations that was not detected until Day 14 post-treatment. In contrast, serum gastrin concentrations in pair-fed control rats were comparable to those of control rats. The number of G-cells in the antral mucosa was not affected by either TCDD treatment or paired-feed restriction. These findings demonstrate that hypergastrinemia in TCDD-treated rats is not caused by reduced feed intake or antral G-cell hyperplasia. A major finding was that antral mucosa levels of both gastrin and somatostatin were decreased significantly in TCDD-treated rats. However, the temporal development and dose-dependence of these TCDD effects on antral hormone levels were quite different than those for hypergastrinemia. TCDD-induced decreases in antral levels of gastrin and somatostatin were detected 1 week earlier than hypergastrinemia. Also, the ED50 of TCDD on Day 14 post-treatment for the decrease in antral mucosa content and concentration of gastrin (29 and 22 micrograms/kg, respectively) and somatostatin (24 and 19 micrograms/kg, respectively) was less than that for hypergastrinemia (46 micrograms/kg). These time- and dose-dependent differences demonstrate that hypergastrinemia in TCDD-treated rats is not a consequence of reduced antral levels of gastrin or somatostatin. We conclude that the antral mucosa, an epithelial tissue not responsive to the proliferative effect of gastrin, is nevertheless a target for the trophic influence and gastrointestinal hormone-altering effects of TCDD.     

Persistent abnormalities in the rat mammary gland following gestational and lactational exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD).

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) exposure during gestation has revealed reproductive anomalies in rat offspring, including inconclusive reports of stunted mammary development in females (Brown et al., 1998, Carcinogenesis 19, 1623-1629; Lewis et al., 2001, TOXICOL: Sci. 62, 46-53). The current studies were designed to examine mammary-gland development in female offspring exposed in utero and lactationally to TCDD, and to determine a critical exposure period and cellular source of these effects. Long-Evans rats were exposed to 1 microg TCDD/kg body weight (bw) or vehicle on gestation day (GD) 15. TCDD-exposed females sacrificed on postnatal days (PND) 4, 25, 33, 37, 45, and 68 weighed significantly less than control litter mates, and peripubertal animals exhibited delayed vaginal opening and persistent vaginal threads, yet did not display altered estrous cyclicity. Mammary glands taken from TCDD-exposed animals on PND 4 demonstrated reduced primary branches, decreased epithelial elongation, and significantly fewer alveolar buds and lateral branches. This phenomenon persisted through PND 68 when, unlike fully developed glands of controls, TCDD-exposed rats retained undifferentiated terminal structures. Glands of offspring exposed to TCDD or oil on gestation days 15 and 20 or lactation days 1, 3, 5, and 10 were examined on PND 4 or 25 to discern that GD 15 was a critical period for consistent inhibition of epithelial development. Experiments using mammary epithelial transplantation between control and TCDD-exposed females suggested that the stroma plays a major role in the retarded development of the mammary gland following TCDD exposure. Our data suggest that exposure to TCDD prior to migration of the mammary bud into the fat pad permanently alters mammary epithelial development in female rat offspring.     

Induction of benzo[a]pyrene metabolism by 2,3,7,8-tetrachlorodibenzo-p-dioxin in primary cultures of adult rat hepatocytes

Primary hepatocyte cultures prepared from adult male Sprague-Dawley rats were extremely sensitive to induction of benzo[a]pyrene (BaP) metabolism by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), added to the cells in culture. A 48-hr exposure to 1 pmol TCDD/10⁶ cells resulted in a 4-fold induction of BaP metabolism. Significant induction was produced by a 48-hr exposure to a dose as low as 0.01 pmol (3 pg) TCDD/10⁶ cells. Cells exposed to TCDD from 7 to 55 hr in culture and then assayed for BaP metabolism responded to much lower doses of TCDD than did cells assayed at 36 hr in culture after being exposed to TCDD from 7 to 36 hr in culture. The doses of TCDD required for half-maximal induction of BaP metabolism were 24.8 and 164 fmol TCDD/10⁶ cells for cells assayed at 55 and 36 hr, respectively. Hepatocytes treated with TCDD starting at later times in culture showed a much more rapid time course of induction than did cells treated at earlier times in culture. A 2.6-fold induction occurred in cells treated from 49 to 55 hr in culture, compared to a 1.2-fold induction from 31 to 37 hr in culture. In contrast to cells exposed to TCDD from 7 to 55 hr in culture, cells exposed from 49 to 55 hr in culture were nearly as sensitive to inhibition of BaP metabolism by SKF 525-A as were uninduced control cells. An apparent derepression of the induction of BaP metabolism is occurring in primary hepatocyte cultures, resulting in an increase in the intitial rate of induction by TCDD and a decrease in the dose of TCDD required to obtain the half-maximum response.     

Hepatic gene downregulation following acute and subchronic exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin.

Chronic exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) has been shown to lead to the development of hepatotoxicity and carcinogenicity in the liver of female rats. In this study, we investigated hepatic gene downregulation in response to acute and subchronic TCDD exposure. We identified 61 probes which exhibited a downregulation of twofold or greater following subchronic (13 weeks) exposure to TCDD. Comparative analysis of the hepatic expression of these 61 probes was conducted with rats subchronically exposed to PeCDF, PCB126, PCB153, and a mixture of PCB126 and PCB153. PCB153 produced little or no alteration in these probes, while the binary mixture mimicked most closely the downregulation observed with TCDD. To discern if the repression of genes within this probe set occur as a primary response to TCDD exposure, we analyzed the early responsiveness of 11 genes at 6, 24, and 72 h following a single exposure to TCDD. We observed early repression of the 11 genes within this early time course, indicating that the repression of this subset of genes occurs as a primary response to TCDD exposure and not as a secondary response to 13 weeks of subchronic treatment. In addition, the gender, species, and AhR dependence of these responses were also investigated. Gender- and species-dependent repression was observed within this subset of genes. Furthermore, utilizing AhR knockout mice, we were able to determine the AhR-dependent downregulation of seven of 11 genes. Together these results assist efforts to understand the multitude of effects imposed by TCDD and AhR ligands on gene expression.     

Mode of metabolism is altered in 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-treated rats

Male Sprague-Dawley rats were fed either a high-fat (HF) or a high-carbohydrate (HC) diet and subsequently injected with either 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) (125 micrograms/kg) or vehicle (pair-fed controls). In all TCDD-treated animals, a reduction in caloric intake was evident as early as 1 day after dosage. Respiratory quotients (RQ) were determined at 5-day intervals. Their pattern for the HC-fed but not for the HF-fed TCDD-treated rats was different from that of the corresponding pair-fed controls. After an initial parallel decrease the RQ values remained low for TCDD-treated rats whereas they increased again for pair-fed controls. Serum total thyroxine (T4) was significantly lower in TCDD-treated animals and this reduction was not influenced by the composition of the diet. Serum triiodothyronine (T3) was neither altered by diet nor by TCDD. Thymic atrophy was as severe in pair-fed as in TCDD-treated rats fed the HC diet but not in rats fed the HF diet. Our results suggest that TCDD-treated rats are in a different mode of metabolism from pair-fed rats and that this difference is related to gluconeogenesis.     

The in vivo biotransformation of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in the rat

This study presents evidence for the in vivo biotransformation of TCDD in the rat. Three male rats with indwelling bile loop cannulas were given repeated daily po doses of 15 μg [¹⁴C]TCDD/kg body weight. After either two, four, or six doses, the total output of bile from one rat was collected for 24 hr following the last dose. Biliary ¹⁴C activity was excreted at a rate similar to the excretion of ¹⁴C activity in the feces of normal (noncannulated) rats given po doses of [¹⁴C]TCDD. Therefore it is not likely that enterohepatic recycling plays a significant role in the retention of ¹⁴C activity following a dose of [¹⁴C]TCDD. High-pressure liquid chromatography of the bile from these rats showed the presence of at least eight radioactive peaks and very little, if any, unchanged TCDD. These metabolites were all more polar than TCDD, and the chromatographic profile was altered following incubation of the bile with β-glucuronidase. These data, in conjunction with previous studies, indicate that the metabolic transformation of TCDD in the liver may be the rate-limiting step in the elimination of TCDD from the body.     

Relationship between the murine Ah phenotype and the hepatic uptake and metabolism of 2,3,7,8-tetrachlorodibenzo-p-dioxin

The influence of the Ah locus on the hepatic uptake and metabolism of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was studied using isolated hepatocytes from Ah responsive C57BL/6J (C57) and nonresponsive DBA/2J (DBA) mice. Hepatocytes from control and TCDD-pretreated C57 and DBA mice were incubated with purified [14C] TCDD (2.2 microM) for 8 hr in the metabolism studies or 2 hr in the uptake studies. Mice were pretreated 7 days prior to hepatocyte isolation with TCDD at doses that maximally induce aryl hydrocarbon hydroxylase activity (C57: 3 micrograms/kg, ip; DBA: 30 micrograms/kg, ip) or at doses approaching the LD50 value (C57: 150 micrograms/kg, ip; DBA: 600 micrograms/kg, ip). Hepatocytes isolated from untreated C57 and DBA mice had similar uptake of [14C]TCDD, and, at all doses, TCDD pretreatment increased [14C]TCDD uptake. The rates of hepatic TCDD metabolism over the first 2 hr of incubation were similar for control C57 and DBA mice, although some qualitative differences in metabolites were detected by HPLC. TCDD pretreatment at doses of 3 and 30 micrograms/kg for C57 and DBA mice, respectively, produced no detectable quantitative or qualitative changes in TCDD metabolism, despite increases in cytochrome P-450 content, 7-ethoxyresorufin O-deethylase (EROD) activity, and benzo[a]pyrene (BaP) metabolism. Pretreatment of C57 and DBA mice with the respective LD50 doses of TCDD decreased the rate of TCDD metabolism by hepatocytes, although cytochrome P-450 content, EROD activity, and BaP metabolism were increased. These results suggest that the uptake and the rate of hepatic metabolism of TCDD do not correlate with genetic differences at the murine Ah locus.     

Changes in thyroid hormones and thyroxine glucuronidation in hamsters compared with rats following treatment with 2,3,7,8-tetrachlorodibenzo-p-dioxin

In rats exposed to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and related compounds, serum thyroxine (T4) is depressed. Since hamsters are relatively insensitive to TCDD-induced lethality, the effects of TCDD on several parameters of thyroid status were measured in hamsters as a comparison with the more sensitive rat. At 7 days after ip injection of TCDD, there was a dose-dependent increase in serum 3,5,3'-triiodothyronine (T3) and T4 in hamsters to a maximum level 200% of control; the ED50 was approximately 10 micrograms/kg. Hamsters receiving 100 micrograms/kg lost up to 4% of their body weight but began to recover after about 3 weeks. Serum T4 in these animals was elevated compared to pair-fed and ad libitum controls throughout the 53-day experiment, although it also began to recover after Day 21. This was in direct contrast to the marked reduction of T4 in rats exposed to lower doses of TCDD. T3 was significantly higher in TCDD-treated hamsters than in pair-fed controls on Days 2-7, and TSH was also elevated on Days 2-21. Reverse T3, like T4, was increased by TCDD in hamsters whereas it was decreased in rats. Hepatic microsomal UDP-glucuronosyltransferase (GT) activity was measured using T4 as substrate (T4-GT). On a whole liver basis, T4-GT was induced by TCDD by the same proportion in both rats and hamsters (170-180% of controls) although absolute activities in rats were 3- to 4-fold higher than in hamsters. This similarity in T4-GT inducibility by TCDD suggests that there are likely mechanisms in addition to T4-GT induction which account for the species-specific alterations in T4. Thus, while the response of thyroid hormones to TCDD differed qualitatively, effective doses in hamsters were higher than in rats, suggesting that these changes, although secondary, may correlate more directly with toxicity than does enzyme induction (whose ED50s are similar in both species). An understanding of the mechanism of this species difference may be helpful in unravelling the primary mechanisms of TCDD toxicity.     

Impaired cued delayed alternation behavior in adult rat offspring following exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin on gestation day 15

This investigation used random ratio (RR) and cued delayed alternation procedures to examine the operant behavior of adult male and female rats following prenatal 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Offspring were exposed to a single maternal dose of 0.0, 0.06, 0.18 or 0.54 microg/kg po of TCDD on gestation day (GD) 15. For RR, adult subjects were trained to respond on one lever in a two-lever chamber for food reinforcement. The response requirement was increased across sessions. Male offspring responded at higher rates than females regardless of RR value and prenatal exposure history. For delayed alternation, animals were required to alternate responses on both apparatus levers and to inhibit responding during randomly interpolated delay intervals. The performance of male and female offspring exposed to 0.18-microg/kg TCDD was significantly less accurate and this group committed more errors by responding during the delay intervals than the other exposure groups. A similar trend was observed in the 0.54- microg/kg group. Overall, response accuracy during the delayed alternation procedure was inversely related to delay length and tended to improve with experience. Interpretations of these outcomes include the possibility that TCDD interfered with the development of attentional processes, impaired response inhibition or promoted response perseveration despite the presence of cues, indicating changes in reinforcement contingencies.