Effect of thyroidectomy and thyroxine on 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) induced toxicity

From dioxin to drug lead--the development of 2,3,7,8-tetrachlorophenothiazine

Polychlorinated dibenzo-p-dioxins are persistent environmental pollutants. The most potent congener, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), causes a wasting syndrome and is a potent carcinogen and immunosuppressant in the rat at high doses. However, low doses cause opposite effects to some of those observed at higher doses, resulting in chemoprevention, stimulation of the immune system, and longevity in experimental animals. The new TCDD analogue, 2,3,7,8-tetrachlorophenothiazine (TCPT), was developed to take advantage of the low-dose effects of dioxins that have potential application as therapeutics. Its development marked a deviation from the traditional scope of phenothiazine drug design by deriving biological effects from aryl substituents. TCPT was synthesized in three steps. The key ring-closing step was performed utilizing a Buchwald-Hartwig amination to provide TCPT in 37% yield. Its potency to induce CYP1A1 activity over 24 h was 370 times lower than that of TCDD in vitro. The elimination half-life of the parent compound in serum was 5.4 h in the rat and 2.7 h in the guinea pig, compared to 11 and 30 days, respectively, for TCDD. These initial findings clearly differentiate TCPT from TCDD and provide the basis for further studies of its potential as a drug lead.

Altered Retinoid Metabolism in Female Long-Evans and Han/Wistar Rats following Long-Term 2,3,7,8-Tetrachlorodibenzo-p-Dioxin (TCDD)-Treatment

This study investigated the effects of long-term low-dose 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) exposure on retinoid, thyroid hormone, and vitamin D homeostasis in Long-Evans and Han/Wistar rats using a tumor promotion exposure protocol. Female rats (ten/group) were partially hepatectomized, initiated with nitrosodiethylamine (NDEA), and given TCDD once per week by sc injection for 20 weeks at calculated daily doses of 0, 1, 10, 100, or 1000 ng/kg bw/day. Groups of nonhepatectomized/uninitiated rats (five/group) were identically maintained. After 20 weeks, the rats were killed, and apolar retinoid levels were determined in the liver and kidneys. No consistent differences were seen between partially hepatectomized/initiated and nonhepatectomized/uninitiated animals with respect to apolar retinoid levels or hepatic TCDD concentration. Further analyses of polar and apolar retinoid levels in liver, plasma, and kidney, as well as free thyroxine (FT4) and vitamin D (25-OH-D(3)) concentrations were carried out in partially hepatectomized/inititated animals. In Long-Evans rats, TCDD exposure dose-dependently decreased hepatic retinyl ester concentrations at doses of 1-100 ng/kg bw/day. Likewise, hepatic all-trans-retinoic acid (all-trans-RA) concentration was decreased 39 and 54% at 10 and 100 ng/kg bw/day respectively, whereas 9-cis-4-oxo-13,14-dihydro-retinoic acid (9-cis-4-oxo-13,14-dihydro-RA), a recently discovered retinoic acid metabolite, was decreased approximately 60% in the liver at 1 ng/kg bw/day. TCDD dose-dependently increased plasma retinol and kidney retinol concentrations, whereas all-trans-RA concentration was also increased in the plasma and kidney at 10 and 100 ng/kg bw/day. Plasma 9-cis-4-oxo-13,14-dihydro-RA was decreased to below detection limits from doses of 1 ng/kg bw/day TCDD. A qualitatively similar pattern of retinoid disruption was observed in the Han/Wistar rat strain following TCDD exposure. FT4 was decreased to a similar extent in both strains, whereas 25-OH-D(3) was decreased only at 100 ng/kg bw/day in Long-Evans rats. Together these results show that TCDD disrupts both retinoid storage and metabolism of retinoic acid and retinoic acid metabolites in liver, kidney, and plasma from doses as low as 1 ng/kg bw/day. Furthermore, 9-cis-4-oxo-13,14-dihydro-RA was identified as a novel and sensitive indicator of TCDD exposure, in a resistant and sensitive rat strain, thereby extending the database of low-dose TCDD effects.

2,3,7,8-tetrachlorodibenzo-p-dioxin augments the modulation of gene expression mediated by the thyroid hormone receptor

Previously, we reported on genes whose expression was highly modulated by T3 in the HeLaTR cells that stably expressed the thyroid hormone receptor (TR). In this study, we examined the effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on TR-mediated gene expression. In the HeLaTR cells, T3 induced the expression of the reporter gene in a thyroid hormone responsible element (TRE)-dependent manner. When the cells were cultured in the presence of T3, the addition of TCDD but not 4-hydroxy-2',3,4',5,6'-pentachlorobiphenyl (PCB-OH), bisphenol A (BPA), or di(2-ethylhexyl)phthalate (DEHP) to the culture media further enhanced the T3-induced expression of the reporter gene. RT-PCR revealed that mRNA levels of 4-1BB, fmfc, PSCA, PSG7, RANTES, and TRAF1, which were highly increased by T3, were further elevated in cells exposed to T3 and TCDD. Also, the mRNA level of BMP6, which was decreased by T3, further declined in the cells exposed to both T3 and TCDD. In contrast to the effect of TCDD, PCB-OH suppressed the modulation of these gene expressions by T3. Neither TCDD nor PCB-OH alone affected the expression of 4-1BB, fmfc, PSCA, PSG7, RANTES, TRAF1, or BMP6. These results indicate that TCDD augments the cellular responses to T3 by hyperactivating TR-mediated gene expression, whereas PCB-OH suppresses cellular responses to T3 by negatively regulating it. Based on these findings, enzyme-linked immunosorbent assay (ELISA) for the PSCA protein in the HeLaTR cells was established. Such assays will be useful to monitor the effects of endocrine disrupting chemicals (EDCs) on TR-mediated gene expression.

Pentachlorophenol exposure in women with gynecological and endocrine dysfunction

Exposure to wood preservatives containing pentachlorophenol (PCP) was detected in 65 women who consulted the Endocrinological Department of the University Hospital of Obstetrics and Gynecology, Heidelberg, Germany, because of gynecological problems. Blood PCP levels ranged from 20.7 to 133 microg per liter of serum. One hundred and six women with similar clinical conditions, corresponding age and body weight, no PCP exposure in history, and PCP levels below 20 microg per liter of serum served as control group. Significant associations were found between serum PCP concentrations, age, and different parameters of the endocrine system. PCP may act centrally on a hypothalamic or suprahypothalamic level which may result in mild ovarian and adrenal insufficiency. PCP may, therefore, play a role in the increasing infertility problem.

Effects of environmental synthetic chemicals on thyroid function

Synthetic chemicals are released into the environment by design (pesticides) or as a result of industrial activity. It is well known that natural environmental chemicals can cause goiter or thyroid imbalance. However, the effects of synthetic chemicals on thyroid function have received little attention, and there is much controversy over their potential clinical impact, because few studies have been conducted in humans. This article reviews the literature on possible thyroid disruption in wildlife, humans, and experimental animals and focuses on the most studied chemicals: the pesticides DDT, amitrole, and the thiocarbamate family, including ethylenethiourea, and the industrial chemicals polyhalogenated hydrocarbons, phenol derivatives, and phthalates. Wildlife observations in polluted areas clearly demonstrate a significant incidence of goiter and/or thyroid imbalance in several species. Experimental evidence in rodents, fish, and primates confirms the potentiality for thyroid disruption of several chemicals and illustrates the mechanisms involved. In adult humans, however, exposure to background levels of chemicals does not seem to have a significant negative effect on thyroid function, while exposure at higher levels, occupational or accidental, may produce mild thyroid changes. The impact of transgenerational, background exposure in utero on fetal neurodevelopment and later childhood cognitive function is now under scrutiny. There are several studies linking a lack of optimal neurological function in infants and children with high background levels of exposure to polychlorinated biphenyls (PCBs), dioxins, and/or co-contaminants, but it is unclear if the effects are caused by thyroid disruption in utero or direct neurotoxicity.

Modulating effects of thyroid state on the induction of biotransformation enzymes by 2,3,7,8-tetrachlorodibenzo-p-dioxin

In this study we investigated to what extent the induction of detoxification enzymes by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) is modulated by concomitant TCDD-induced changes in thyroid state. Euthyroid (Eu) male Sprague-Dawley rats, surgically thyroidectomized (Tx) rats and Tx rats receiving substitution doses of 3,3',5-triiodothyronine (Tx+T3) or thyroxine (Tx+T4) by osmotic minipumps were treated with a single ip injection of 10 μg TCDD/kg/bwt or with vehicle (corn oil). Three days after TCDD administration, rats were sacrificed and blood and livers were collected for analysis. Total hepatic cytochrome P450 (CYP) content was increased by ≈50% by TCDD in all groups but was not affected by thyroid state. In Eu rats, TCDD increased CYP1A1/1A2 activity 90-fold, CYP1A1 protein content 52-fold and CYP1A1 mRNA levels ≈5.8-fold. Similar findings were obtained in Tx, Tx+T3 and Tx+T4 rats except that TCDD-induced CYP1A1 activity was significantly decreased in Tx rats. NADPH cytochrome P450 reductase activity was not affected by TCDD but was decreased in Tx rats, which may explain the diminished TCDD-induced CYP1A1 activity in Tx rats. Hepatic p-nitrophenol UDP-glucuronyltransferase (UGT) activity was induced ≈4-fold by TCDD in Eu rats. Similar basal and TCDD-induced activities were observed in Tx+T3 and Tx+T4 rats, but TCDD-induced activities were significantly lower in Tx rats. TCDD did not have a significant effect on overall glutathione-S-transferase (GST) activity or hepatic GST 2-2, 3-3 or 4-4 protein levels but produced a marked increase in GST 1-1 protein levels. Thyroid state did not affect basal or TCDD-induced GST activity or subunit pattern. Iodothyronine sulfotransferase (ST) activity was not affected by TCDD treatment and was slightly but not significantly lower in Tx rats than in Eu, Tx+T3 and Tx+T4 rats. These results suggest that the changes in thyroid hormone levels associated with TCDD treatment have little modulating effects on the induction of hepatic detoxification enzymes in Sprague-Dawley rats exposed to this compound.

Regulation by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) of the DNA binding activity of transcriptional factors via nuclear protein phosphorylation in guinea pig adipose tissue

2,3,7,8-Tetrachloro-p-dioxin (TCDD) induced a modest stimulation of nuclear protein phosphorylation in explant tissue cultures in 10 min, followed by a substantial decrease in the level of total protein phosphorylation activity in the nucleus. Curiously, this TCDD-induced decline in nuclear protein phosphorylation was accompanied by an increase in cytosolic and extranuclear protein phosphorylation activity. One of the main causes for such a decrease in the protein phosphorylation activity in the nucleus appears to be related to some increase in protein phosphatase activities as judged by the counteractions of okadaic acid and Na3VO4 to the above effect. In addition, TCDD induced changes in nuclear protein kinase activities as well. Manganese-stimulated protein kinase was found to be the predominant type of nuclear protein phosphorylating activity affected by TCDD, with 60% of the total activity due to heparin-sensitive casein kinase II (CK II), a major nuclear protein kinase. The level of CK II activity in the nuclear protein preparation from adipose tissue of TCDD-treated guinea pigs (1 microgram/kg) in the presence of 100 nM heparin was only 35% of the control value after 24 hr. In addition, TCDD was found to increase the protein kinase C and microtubule-associated protein 2 kinase activities as early as 15 min after treatment in isolated adipose tissues in culture. Under in situ incubation conditions with explant tissues in culture, TCDD rapidly enhanced the DNA binding activity of the transcriptional factor AP-1, whereas the same treatment reduced c-Myc DNA binding activity. Genistein, a specific protein tyrosine kinase inhibitor, abolished the stimulatory effect of TCDD on AP-1 binding activity, but not on DNA binding activity of c-Myc. Phorbol ester (TPA) increased the binding activity of AP-1 and c-Myc, as expected. However, TCDD in combination with TPA caused a slight reduction in binding activity of both transcriptional factors. On the other hand, in the presence of forskolin, the stimulatory effect of TCDD on AP-1 binding activity and the inhibitory effect on c-Myc were still apparent. Okadaic acid almost abolished the binding activity of c-Myc, whereas in combination with TCDD a stimulatory effect was found. These observations are consistent with the idea that TCDD regulates the DNA binding activity of AP-1 and c-Myc mainly through modulating their states of phosphorylation by altering protein kinase and phosphatase activities.

Modulation of gene expression and endocrine response pathways by 2,3,7,8-tetrachlorodibenzo-p-dioxin and related compounds

The aryl hydrocarbon (Ah) receptor binds several different structural classes of chemicals, including halogenated aromatics, typified by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), polynuclear aromatic and heteropolynuclear aromatic hydrocarbons. TCDD induces expression of several genes including CYP1A1, and molecular biology studies show that the Ah receptor acts as a nuclear ligand-induced transcription factor that interacts with xenobiotic or dioxin responsive elements located in 5'-flanking regions of responsive genes. TCDD also elicits diverse toxic effects, modulates endocrine pathways and inhibits a broad spectrum of estrogen (17 beta-estradiol)-induced responses in rodents and human breast cancer cell lines. Molecular biology studies show that TCDD inhibited 17 beta-estradiol-induced cathepsin D gene expression by targeted interaction of the nuclear Ah receptor with imperfect dioxin responsive elements strategically located within the estrogen receptor-Sp1 enhancer sequence of this gene.

Effect of thyroidectomy and thyroxine on hexachlorobenzene induced porphyria

The role of thyroid status in hexachlorobenzene (HBC) induced porphyria was studied in normal, thyroidectomized and thyroxine (T4) treated rats. Female Wistar rats were treated with HCB for different periods of time. Serum T4 levels were depressed after 8 days of HCB administration whereas levels of triiodothyronine (T3) were not altered. T4 administered simultaneously with HCB resulted in hyperthyroxinemia. The time course of porphyrinogen carboxy-lyase (PCL) activity in the three HBC treated groups was studied. A rapid and significant decrease of PCL activity was found after 8 days of HCB treatment in T4 treated rats with respect to untreated animals. In contrast, HCB treatment of normal and thyroidectomized rats elicited a significant decrease of PCL activity after 21 and 30 days, respectively. This study shows that thyroid hormone plays an important role in the early establishment of HCB induced porphyria.

Aryl hydrocarbon or dioxin receptor: biologic and toxic responses

1. The AhR represents a ligand-activated transcription factor. Receptor agonists include planar aromatic compounds, a variety of heterocyclic plant constituents, and PCDD/PCDF. The latter lead to persistent activation of the receptor due to their strong binding affinity and long biologic half-life of over 10 years in human blood and fat. Practically every person on earth is exposed to these compounds via the diet (> 90%) and by high concentrations in mother's milk. PCDD/PCDF produced toxic responses in exposed people (primarily chloracne and immunosuppression) in the past. However, the present PCDD/PCDF levels (basal levels) in the general population are below those warranting toxicologic concern. 2. The AhR has been characterized as a helix-loop-helix transcription factor related to the Drosophila developmental genes sim and per. The cytosolic form of the receptor is present as an inactive complex with two subunits of HSP90. After ligand binding HSP90 is released and the receptor enters the nucleus as a heterodimer together with a related protein ARNT. It binds with high affinity to certain enhancer elements in the upstream region of several genes such as cytochrome P4501A1 (CYP1A1). The AhR transcriptionally activates several drug-metabolizing enzymes and proteins involved in growth/differentiation, such as the plasminogen activator inhibitor PAI-2 and IL-1 beta. In addition, it modulates the action of a number of other nuclear transcription factors such as receptors of the steroid hormone receptor superfamily and of cell surface receptors such as EGF. With the exception of CYP1A1 induction, little is known about the mechanism of transcriptional activation of the AhR-controlled genes. Many AhR-modulated biologic responses (such as modulation of the estrogen and EGF receptor) appear to be indirect. 3. Persistent activation of the AhR is probably responsible for toxic responses in experimental animals and humans. They are markedly tissue and species specific. In rodents a wasting syndrome, immunosuppression, teratogenicity, chloracne, and carcinogenicity/tumor promotion have been well studied. There is good evidence for an involvement for the AhR in these responses. However, the chain of events from receptor activation to the diverse toxic endpoints is largely unknown. Alteration of growth and differentiation of epithelial tissues may underlie most of the toxic responses. A lot has already been achieved, mostly by characterizing the AhR and transcriptional activation of CYP1A1. Still more work lies ahead of us, for example, elucidation of the physiologic roles of the AhR and of the chains of events from receptor activation to the various biologic and toxic endpoints.

The interaction of L-triiodothyronine and 2,3,7,8-tetrachlorodibenzo-p-dioxin on Ah-receptor-mediated hepatic Phase I and Phase II enzymes and iodothyronine 5'-deiodinase in thyroidectomized rats

Across all levels of L-triiodothyronine (L-T3) treatment, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) resulted in increased hepatic cytochrome P-450-associated activities of 7-ethoxycoumarin O-deethylase (ECOD), 7-ethoxyresorufin O-dealkylase (EROD) and aryl hydrocarbon hydroxylase (AHH). The treatment of thyroidectomized rats with L-T3 at physiologic replacement levels in concert with TCDD produced an increase in ECOD, EROD and AHH activity above that seen with only TCDD. TCDD as well as L-T3 enhanced the activity of hepatic 1-naphthol glucuronyl transferase (NGT). In addition, the combined effect of L-T3 and TCDD resulted in similar levels of induction of NGT at both physiologic and supraphysiologic doses of L-T3. TCDD treatment resulted in elevated serum T3 levels at both physiologic and supraphysiologic levels of L-T3. One TCDD dose inhibited hepatic microsomal 3,3',5'-triiodothyronine (reverse T3) 5'-deiodinase activity by 61% in thyroidectomized, T3-untreated rats. The inhibition of 5'-deiodinase activity was partially overcome by increasing the T3 dose.

Alterations of hepatic acetyl-CoA carboxylase by 2,3,7,8-tetrachlorodibenzo-p-dioxin

The effect of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on acetyl-CoA carboxylase (ACC) activity and synthesis was examined. Male Wistar rats received a single i.p. injection of TCDD (53 micrograms/kg), and nine days later body weight, liver weight, hepatic lipid, ACC activity and mass were determined and compared to pair-fed controls. Body weights of TCDD-treated animals decreased, while liver weights increased resulting in an increase in liver to body weight ratios. ACC activity was decreased by 65%, however sodium dodecyl sulfate-polyacrylamide gel electrophoresis (SDS-PAGE) and Western analysis using a biotin specific probe revealed that ACC protein levels were not appreciably changed. In addition, there was a large increase in exogenous lipid material in TCDD-treated livers as determined by osmium tetroxide staining. These data suggest that the decrease in ACC activity may be due to direct inhibition of the enzyme by negative allosteric interactions with free fatty acids released from adipose tissue that subsequently accumulate in liver.

Vaginal cyclicity, sexual receptivity, and eating behavior of the female rat following treatment with chlordecone

The effects of 25, 50, or 75 mg/kg chlordecone on vaginal and behavioral estrus were examined following treatment of intact rats during estrus, diestrus 1, or diestrus 2. Chlordecone accelerated vaginal estrus, but sexual behavior was eliminated, delayed, or reduced. Chlordecone treatment led to the presence of vaginal estrus within 2 days, but reduced or eliminated sexual behavior on the evening of predicted proestrus. Of the females that received chlordecone, 20% to 50% showed some behavior on the day after the evening of predicted proestrus and 20% to 35% never showed behavior during the 8-day observation period. Although the lordosis to mount ratio was still reduced, the occurrence of behavior a day late suggested that the pesticide had delayed behavioral estrus. Chlordecone also rapidly suppressed food intake and led to a significant decline in body weight; these nutritional factors could have contributed to the disrupted estrous cycle. Some support for this possibility was derived from a reduced sexual receptivity on the evening of proestrus when the caloric intake of untreated female rats was matched to that of the chlordecone treated animals. However, the effects of caloric reduction on proestrous lordosis behavior were less robust than seen following chlordecone. Chlordecone treatment on diestrus 2 reduced the number of progesterone receptors in uterine tissue of females on the predicted day of proestrus. This suggested that the tissue sensitivity to circulating levels of progesterone would be reduced within 2 days after chlordecone treatment.(ABSTRACT TRUNCATED AT 250 WORDS)

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.

Learning in monkeys exposed perinatally to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)

TCDD is an extremely toxic chemical pollutant which bioaccumulates in maternal adipose tissue, and is transferred to the developing organism during gestation and lactation. Long-term cognitive deficits have been reported following perinatal exposure to polychlorinated biphenyls, which are structurally and toxicologically similar to TCDD. In the current study, monkeys exposed to TCDD perinatally were later tested in two cognitive paradigms, discrimination-reversal learning (RL) and delayed spatial alternation (DSA). RL detected effects; whereas DSA, as analyzed, did not. RL consisted of a series of simple spatial reversals, followed by spatial reversals with color and shape as irrelevant cues, then by color reversals and finally by shape reversals. TCDD-exposed monkeys exhibited retarded learning of the shape reversals. The deficit was most pronounced on the first reversal following overtraining. There were no group differences on the spatial or color reversals. However, the number of trials the TCDD-exposed monkeys individually took to learn the spatial reversals was positively correlated with TCDD concentration in body fat. Conversely, the number of trials they took to learn the color reversals was negatively correlated with TCDD in body fat.

Biochemical and functional effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on the heart of female rats

Biochemical, functional and morphologic effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on the hearts of female rats were examined. Six days after the treatment of rats with TCDD, the blood pressures and resting heart rates were significantly less than in control animals. Treated animals were also less responsive to the effects of the beta-1 agonist, (-)isoproterenol. No histopathologic changes were observed in the heart although extensive centrilobular necrosis occurred in the liver after TCDD administration. Serum levels of thyroxine were 66% less than in control animals. Marked lipid peroxidation was produced in the liver with small but significant increases occurring in the heart. TCDD administration had no effect on catalase activity in the heart, but produced a 20% decrease in superoxide dismutase activity relative to control animals. The effects of TCDD on cardiac function do not appear to be due to a direct action of the xenobiotic on the heart but possibly to a down-regulation of beta-receptors in the heart as a result of the hypothyroid state.

Corticosterone decreases toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in hypophysectomized rats

Male Sprague-Dawley rats were hypophysectomized by an established surgical technique. Hypophysectomy aggravated the toxicity (mortality and mean time to death) of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD; 125 micrograms/kg ip) when compared to sham-operated rats (100% mortality with 9 +/- 1 d mean time to death vs. 90% mortality with 32 +/- 6 d mean time to death, respectively). However, administration of corticosterone (25 micrograms/ml in drinking water) to hypophysectomized rats resulted in an attenuation of the toxicity (40-60% mortality with 40-90 d mean time to death) to a range of TCDD doses (125, 250, 500 micrograms/kg) much higher than the LD50 (about 60 micrograms/kg TCDD) in nonhypophysectomized rats (about 30 d mean time to death). Furthermore, thyroid hormone supplementation in hypophysectomized rats dosed with 125 micrograms/kg TCDD restored the toxicity of TCDD to approximately "normal." Based on these data it is concluded that one or more as yet unknown key factors that are important in the modulation of the toxicity of TCDD reside in the pituitary.

Effects of 3,4,3',4'-tetrachlorobiphenyl on thyroid function and histology in marmoset monkeys

Marmoset monkeys were treated with oral doses of 0.1, 1 or 3 mg 3,4,3',4'-tetrachlorobiphenyl (TCB) per kg body weight 2 times a week for 18-23 weeks. Histological examination of the thyroid gland revealed a dose-dependent follicular cell hyperplasia. The morphological changes were associated with various disturbances of thyroid function. The average serum thyroxine (T4) levels during the treatment period were reduced by more than 99% in monkeys receiving 3 mg TCB/kg, by 81% in marmosets on a dose of 1 mg TCB/kg, and by 35% with 0.1 mg TCB/kg. The reduction in serum T4 levels was established from the earliest time point (2 weeks) throughout the whole dosing period (18-23 weeks). The reduction in serum T4 levels was reflected in decreased free thyroxine (FT4) index in the 1 and 3 mg TCB/kg dose groups. Serum triiodothyronine (T3) levels were lowered in the 3 mg/kg dose group already after 2 weeks. Evidence for decreased binding to carrier proteins is suggested by increased T3 resin uptake in the highest dose group. Levels of thyrotropin (TSH) were increased in the highest dose group as a feedback response to the dramatically reduced serum T4 levels.

Tissue-specific alterations of de novo fatty acid synthesis in 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-treated rats

De novo fatty acid synthesis was determined by the 3H2O method in numerous tissues and organs of TCDD-treated (125 micrograms/kg), pair-fed and free-fed male Sprague-Dawley rats to investigate if this important pathway of intermediary metabolism is altered by TCDD. Of the 12 tissues and organs examined, liver showed an increased, and interscapular brown adipose tissue (IBAT) a decreased de novo fatty acid synthesis when comparing TCDD-treated to pair-fed or free-fed control rats. De novo fatty acid synthesis was unaffected in other organs and tissues examined, with the exception that the concentration of 3H-fatty acids in plasma reflected the increased rate of synthesis seen in the liver of TCDD-treated animals. Increased de novo fatty acid synthesis in liver coincided with increased plasma triiodothyronine (T3) concentrations, whereas decreased de novo fatty acid synthesis in IBAT parallelled decreased plasma thyroxine (T4) levels. Thyroidectomy decreased de novo fatty acid synthesis, as expected, in both liver and IBAT. However, TCDD elicited no response in either of these organs in thyroidectomized rats. This finding suggests that changes observed in non-thyroidectomized rats are probably secondary effects. Indeed, known tissue-specific effects of T3 on liver and T4 on IBAT provide a likely explanation for the altered de novo fatty acid synthesis of these organs. It is suggested that increased de novo fatty acid synthesis in the liver of TCDD-treated rats might be responsible for the additional wasting away observable in these animals as compared to pair-fed controls.

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.

Effects of TCDD-estradiol interactions in three strains of mice

Interactions of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and estradiol were studied in three strains of mice: CD-1 and C57B/6 (TCDD sensitive) and DBA/2 (TCDD resistant at lower doses). Immature females were injected with 0-200 ng/kg/day estradiol for 2 weeks, s.c. On days 7, 9, 11, and 13, mice received 10 micrograms TCDD/kg by gavage. Relative uterine weight increased in mice of all three strains treated with estradiol alone. Uterine imbibition was suppressed by TCDD treatment, although this effect was antagonized in a saturable manner by coadministration of estradiol. TCDD induced aryl hydrocarbon hydroxylase (AHH) in liver microsomes of treated mice independent of estradiol dose and strain of mice (the dose of TCDD used was high enough to cause AHH induction in the resistant DBA/2 mice). Treatment of CD-1 mice, but not other strains, with TCDD and estradiol resulted in a decrease in the electrophoretic band of hepatic microsomal proteins comigrating with cytochrome P-450a and epoxide hydrase.

Do residue levels of polychlorinated biphenyls (PCBs) in human blood produce mild hypothyroidism?

PCBs are nearly ubiquitous environmental contaminants, occurring in most human adipose tissue and blood samples. It has recently been recognized that PCBs and related compounds share important structural properties with thyroid hormones and can bind thyroid hormone binding proteins. It is reasonable that such specific binding interactions can modulate the distribution of these compounds in the body and alter hormone-protein interactions that are responsible for the maintenance of normal thyroid status. Most of the available evidence indicates that the levels of free thyroid hormones in plasma are a reflection of the maintenance of normal thyroid status in any individual. A theoretical model for the transport of thyroid hormones in blood has been extended to estimate the modulating effects of PCBs on free thyroid hormones. Using conservative assumptions based on experimental data, our calculations indicate that PCB concentrations normally found in humans can effect significant increases in free thyroxine levels in serum by competing with serum thyroid hormone binding proteins. Experimental data are discussed which support the proposal that antagonist binding of PCBs to thyroid hormone binding proteins in serum could produce varying degrees of hypothyroidism. The biological result is compatible with the "equilibrium hypothesis" in which thyroid hormone redistributes between specific and nonspecific binding proteins rather than emphasizing the importance of free hormone as the active moiety.

Toxic effects in C57B1/6 and DBA/2 mice following consumption of halogenated aromatic hydrocarbon-contaminated Great Lakes coho salmon (Oncorhynchus kisutch Walbaum)

Diets containing coho salmon (Oncorhynchus kisutch Walbaum) from the Pacific Ocean or from Lakes Erie, Michigan, and Ontario [containing a gradation from low to high of halogenated aromatic hydrocarbons, (HAHs)] were fed to C57B1/6 and DBA/2 mice. Following a 4-month dietary exposure to Lake Ontario salmon, both strains of mice demonstrated hepatomegaly. The ethoxyresorufin-O-deethylase (ERR) enzyme levels were elevated in livers of C57B1/6 mice fed diets of salmon from all of the Great Lakes studied, with exceptionally high levels detected in C57B1/6 mice fed Lake Ontario salmon. Induction of ERR enzyme levels was detected in DBA/2 mice only following dietary exposure to Lake Ontario salmon. Serum levels of L-thyroxine (T4) and triiodo-L-thryonine (T3) were suppressed in C57B1/6 mice following consumption of Lake Ontario coho salmon, but T3 and T4 levels remained unchanged in DBA/2 mice. In general, pathobiological effects correlated with both dietary HAH exposure level and Ah receptor status.

Effects of vitamin A and/or thyroidectomy on liver microsomal enzymes and their induction in 2,3,7,8-tetrachlorodibenzo-p-dioxin-treated rats

Vitamin A and thyroid hormone status have been shown previously to alter the toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in rats. In the present study, we have examined the effects of a vitamin A-excess and a vitamin A-deficient diet on thyroid hormone levels, on selected drug-metabolizing enzymes in liver microsomes, and on their inducibility by TCDD in male Sprague-Dawley rats. Except for a slight increase in serum T3 levels, none of these end points was affected by feeding rats the vitamin A-deficient diet. In contrast, excess dietary vitamin A caused a decrease in serum thyroxine (T4) and triiodothyronine (T3) levels, although the levels of T3 remained in the euthyroid range (60-80 ng/dl). The concentration of liver microsomal cytochromes P-450 and b5 and the basal activity of benzo[a]pyrene hydroxylase and 7-ethoxyresorufin O-de-ethylase were unaffected by excess dietary vitamin A. This result is consistent with our previous observation that the basal activity of these enzymes is dependent more on T3 than on T4 levels. Vitamin A excess markedly suppressed the activity of liver microsomal UDP-glucuronosyl transferase toward 1-naphthol. However, no such enzyme suppression was observed in thyroidectomized rats. This suggests that the suppressive effect of vitamin A on UDP-glucuronosyl transferase activity may be dependent on T3. Neither vitamin A nor thyroid status had any major effect on the inducibility of UDP-glucuronosyl transferase and cytochrome P-450-dependent enzyme activities by TCDD. However, vitamin A and TCDD had a nearly additive effect on suppression of serum T4. It is concluded that liver microsomal enzyme induction is not associated with the modulatory effect of vitamin A and thyroid hormones on the toxicity of TCDD.

Composition of diet modifies toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in cold-adapted rats

The effect of a high carbohydrate, high fat or high protein diet was studied on the acute toxicity of TCDD (125 micrograms/kg) in cold-adapted (4 +/- 1 degrees C) rats. Within 10 days after dosing, TCDD-treated rats fed a high carbohydrate or a high protein diet reduced their caloric intake by 25% whereas those fed a high fat diet consumed only 15% fewer kcal/MBS (metabolic body size). TCDD-treated rats fed a high protein diet lost body weight at the same rate as their pair-fed controls, whereas body weight loss in high fat-fed rats was significantly higher than in their pair-fed controls. In contrast, TCDD-treated rats fed a high carbohydrate diet effectively maintained their body weight in the 4 days immediately after TCDD dosage, whereas their pair-fed controls lost weight. Mortality in TCDD-treated animals was 100% irrespective of the diet; all pair-fed control rats (except one fed a high protein diet) were terminated on days corresponding to the spontaneous death of their TCDD-treated pairs. Mean time to 50% mortality and mean time to death were significantly longer in TCDD-treated rats fed a high carbohydrate diet in comparison with the other two TCDD-treated groups (p less than 0.05), although caloric intake was comparable. Serum triiodothyronine (T3) was reduced in TCDD-treated animals fed a high fat or a high carbohydrate diet but not in those fed a high protein diet; serum thyroxine (T4) was reduced in all the treated groups, irrespective of diet.(ABSTRACT TRUNCATED AT 250 WORDS)

Evidence that 2,3,7,8-tetrachlorodibenzo-p-dioxin and thyroid hormones act through different mechanisms in human keratinocytes

It has been proposed [J. D. McKinney, J. Fawkes, S. Jordan, K. Chae, S. Oatley, R. E. Coleman, and W. Briner (1985). Environ. Health Perspect. 61, 41-53] that 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) produces toxic responses through persistent occupancy of nuclear thyroxine (T4) receptors, and that maintenance of receptor occupancy by supraphysiologic concentrations of thyroid hormones mimics TCDD toxicity [L. H. Hong, J. D. McKinney, and M. I. Luster (1987). Biochem. Pharmacol., 36, 1361-1365]. TCDD induces hyperkeratinization in cultured normal human epidermal cells and the human keratinocyte line, SCC-12F. This response is associated with a decrease in high-affinity epidermal growth factor (EGF) receptors. These cell systems were used as models to compare the actions of TCDD with those of triiodothyronine (T3) and T4 on human target cells. Keratinocytes were treated simultaneously with T3 and T4 in a 4:1 molar ratio (T3/T4; Hong et al., 1987) and levels of EGF binding and 7-ethoxycoumarin O-deethylase activity (a marker for cytochrome P1-450 induction) were measured. T3/T4 (at concentrations up to 10 microM T3/2.5 microM T4) and T3 or T4 alone (0.1 to 10 microM) did not produce the hyperkeratinization, the decrease in EGF binding, or the increase in ECOD activity that are characteristic of TCDD exposure. Nonresponsiveness to T3/T4 was not due to metabolism of these hormones by the keratinocytes. T3 and T4 did not compete with [3H]TCDD for binding to cytosolic Ah receptor from C57BL6 mouse liver, SCC-12F, or normal human epidermal cells. TCDD and an active stereoisomer, 2,3,7,8-tetrachlorodibenzofuran, did not compete with [125I]T3 or [125I]T4 for binding to nuclear receptors from SCC-12F cells or C57BL6 mouse liver. Taken together, these data demonstrate that the actions of TCDD and thyroid hormones are mediated by distinct mechanisms in human keratinocytes.

Goitre and wasting induced in hamsters by hexachlorobenzene

Male Syrian hamsters were treated with hexachlorobenzene (HCB) in their diet at levels of 100 ppm for 28 weeks, 200 ppm for 18 and 28 weeks, and 500 ppm for 6 weeks. All treatments caused at least a 2.5- to 3-fold increase in thyroid size, mainly by enlargement of some follicles. Serum thyroxine (T4) levels were unchanged, whereas levels of triiodothyronine (T3) eventually became depressed by greater than 60%. Uptake of 131I into thyroids was induced approximately 3-fold when estimated after feeding HCB (500 ppm) for 3 or 6 weeks. Hamsters also lost weight by depletion of adipose tissue, leading to 50% mortality in longer experiments. Results were distinct from the effects of the known antithyroid agent 3-aminotriazole or amitrole (200 ppm for 28 weeks), which did not affect survival and although causing thyroid enlargement depressed serum T4 and significantly elevated T3. The effects of HCB in hamsters were also different from those in rats (500 ppm HCB for 6 weeks) in which there was only a small increase in thyroid size (1.3-fold), serum levels of T3 were only slightly depressed but T4 levels were reduced by 74%. These studies are discussed with reference to the effects of other polyhalogenated aromatic chemicals on the thyroid, serum thyroid hormone levels and lethality.

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.

Modulation of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-mediated myelotoxicity by thyroid hormones

Although binding by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) to the Ah receptor is a prerequisite for toxicity, the events responsible for subsequent TCDD effects are essentially unknown. Several lines of evidence have indicated that thyroid hormones share common molecular properties with TCDD and can modulate its toxicity. In the present studies we employed suppression of murine bone marrow hematopoiesis by TCDD as an in vitro model to study the relationship between thyroid hormones and TCDD toxicity. Supraphysiological levels of thyroid hormone mimicked TCDD myelotoxicity, in that both were inhibited by a common antagonist, 1-NH2-3,7,8-trichlorodibenzo-p-dioxin. Furthermore, myelotoxicity by both TCDD and thyroid hormone segregated with the Ah locus in congenic mice. These data provide evidence of a relationship between TCDD and thyroid hormones in that hormonal activity may help regulate TCDD toxicity.

Toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin in cold-adapted rats

The toxicity of 60 micrograms/kg 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) given IP in corn oil/5% acetone was examined in male Sprague-Dawley rats adapted to 25 degrees C or 4 degrees C ambient temperature. Cold exposure significantly reduced mean time to death and tended to increase mortality. Body weight at the time of death was reduced at both ambient temperatures to about the same extent. Thus, the rate of body weight loss was about twice as fast in non-survivors at 4 degrees C than at 25 degrees C. There was a continuous decrease in feed intake of the non-survivors at 25 degrees C until death. However, no reduction in feed intake occurred in any of the rats at 4 degrees C ambient temperature. At 14 days after dosing all TCDD-dosed animals were hypothyroid in terms of T4 but essentially euthyroid in terms of T3. Oxygen consumption at 10 days after dosing was reduced to the same extent in all TCDD-dosed rats without regard to survival status. By day 20 after TCDD dosage, survivors increased their oxygen consumption at both ambient temperatures to nearly control levels whereas non-survivors were unable to do so. Body temperature of all animals remained within normal range except for the non-survivors, which showed reduced rectal temperature shortly before death.(ABSTRACT TRUNCATED AT 250 WORDS)

Effects of thyroidectomy on the Ah receptor and enzyme inducibility by 2,3,7,8-tetrachlorodibenzo-p-dioxin in the rat liver

Thyroidectomy of rats confers some protection, by an unknown mechanism, from the weight loss, immunotoxicity, and mortality induced by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Since at least some of the many effects of TCDD appear to be mediated by the Ah receptor, perhaps the thyroid plays a role in regulation of this receptor, thereby modifying the toxicity of TCDD. We tested this hypothesis by comparing TCDD-binding characteristics of the receptor and hepatic enzyme inducibility by TCDD (a receptor-mediated response) in thyroidectomized (ThX) and euthyroid rats. There were no significant differences in levels of TCDD binding in vitro in hepatic cytosol, in receptor affinity, nor in the molecular size of the TCDD-bound receptor in untreated ThX rats compared to controls fed ad libitum or pair-fed. Total hepatic cytochrome P-450 (P-450) levels and NADPH-menadione oxidoreductase (NMOR) activity were unaffected by thyroid status, whereas 7-ethoxycoumarin O-deethylase (ECOD) activity was approx. 50% lower in ThX animals than in ad libitum or pair-fed controls. At 3 and 10 days after TCDD administration (10 micrograms/kg, i.p.), P-450 concentrations and NMOR and ECOD activities were induced by approximately the same proportions in ThX and pair-fed intact rats; however, the absolute levels of the induced activities were lower in ThX than in pair-fed controls. It was concluded that hypothyroidism does not regulate Ah receptor concentration or function in the liver. Therefore, the modulation of TCDD toxicity by hypothyroidism appears not to involve changes in the hepatic Ah receptor.

Toxicity and evidence for metabolic alterations in 2,3,7,8-tetrachlorodibenzo-p-dioxin-treated guinea pigs fed by total parenteral nutrition

The effect of total parenteral nutrition (TPN) on the toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in male, Hartley-strain guinea pigs was determined. At a single dose of 2 micrograms TCDD/kg, TPN-fed guinea pigs maintained body weight at a level which was slightly, but consistently, below that of the TPN-fed control animals. However, despite the sustenance of body weight, TCDD-treated animals died or were sacrificed due to morbidity between Days 8 and 24 following treatment. Approximately 50% of this group demonstrated a profound loss of body weight within a few days prior to death or sacrifice. With the exception of the pattern of weight loss, the signs of toxicity in the TPN-fed, TCDD-treated animals were strikingly similar to those observed in TCDD-treated guinea pigs fed ad libitum. Although livers from TCDD-treated, TPN-fed animals demonstrated increased content of lipid and cytochrome P-450, this tissue appeared to be morphologically and functionally comparable to that from TPN-fed controls. Of the blood chemistry examined, only the serum concentrations of 3,5,3'-triiodothyronine were significantly decreased in the treated animals fed by TPN. Results were also compared to TCDD-treated guinea pigs fed ad libitum and respective pair-fed controls. Many of the physiological and biochemical responses observed in animals fed ad libitum following TCDD treatment could be explained by a decrease in food consumption. This study demonstrated that although food consumption clearly accounts for the major effect of TCDD on body weight loss in guinea pigs fed ad libitum, additional physiological and/or biochemical alterations occurred which also contribute to body weight loss, other signs of toxicity, and subsequent lethality.

Effects of thyroid hormones on the induction of cleft palate by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in C57BL/6N mice

The induction of cleft palate by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) administered with thyroid hormones triiodothyronine (T3) or thyroxine (T4) was investigated in C57BL/6N mice. Timed-pregnant mice were treated with vehicle, TCDD, T3, T4, TCDD plus T3, or TCDD plus T4 on Days 10 to 13 of gestation. No cleft palates were observed in any control fetuses in this study, nor have there been any cleft palates in 1193 fetuses or 154 control litters in the past 24 months. TCDD (3 micrograms/kg/day) caused about 8% cleft palates per litter, while T3 (120, 240, 480 micrograms/kg/day) and T4 (625, 1250, 2500 micrograms/kg/day) resulted in no more than 1.2% cleft palates per litter in any of the treatment groups and the incidence was not dose related. The combination of TCDD (3 micrograms/kg/day) plus T3 at 120, 240, and 480 micrograms/kg/day resulted in 15.9, 20.6, and 31.4% cleft palates per litter, respectively. TCDD plus T4 at 625, 1250 and 2500 micrograms/kg/day caused 15.1, 22.9, and 27.2% cleft palates per litter. No cleft palates were observed when large doses of T3 were given in combination with T4. These data demonstrated that coadministration of T3 or T4 with TCDD increased the incidence of cleft palate to incidences greater than expected from the separate administration of the hormones plus TCDD.

Thyroid status and thermogenesis in rats treated with 2,3,7,8-tetrachlorodibenzo-p-dioxin

Several key aspects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) toxicity resemble the effects of hypothyroidism, while in other ways the toxic responses are characteristics of hyperthyroidism. Whether thyroid dysfunction plays a role in TCDD toxicity remained unknown, however. We therefore determined the dose-related effects of TCDD treatment on plasma concentrations of L-thyroxine (T4), 3,5,3'-triiodo-L-thyronine (T3), and thyroid-stimulating hormone (TSH), and compared these changes with signs of TCDD toxicity. We also determined whether indices of functional thyroid status (and thermogenesis) were altered in response to TCDD treatment. Young adult male Sprague-Dawley rats were given single oral doses of TCDD (6.25-100 micrograms/kg) and evaluated 1 week later. Toxicity, measured by decreases in feed intake and body weight, ranged from minimal to severe. Plasma concentrations of T4 were greatly reduced at all doses tested, while T3 was increased in a dose-related fashion (up to 35%). TSH was elevated but was inversely proportional to dose. Thyroid histology was unremarkable, and TCCD treatment had little effect on the ability of rats to raise serum T4, T3, and TSH concentrations in response to acute cold stress. TCDD treatment caused a slight (8%) decrease in basal metabolic rate, yet comparable decreases were seen in pair-fed control animals. Thermogenesis, as measured by O2 consumption and colonic temperatures in rats exposed to various ambient temperatures, was only marginally affected. In summary, although thyroid hormone concentrations were markedly altered, rats given doses of TCDD sufficient to cause overt toxicity appeared to be essentially euthyroid. These results do not support proposals by other researchers that altered thyroid status is a major contributor to TCDD toxicity and/or a key response to TCDD exposure.

Histopathology of interscapular brown adipose tissue, thyroid, and pancreas in 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-treated rats

The time course of histological changes was studied in rats lethally intoxicated (150 micrograms/kg) with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). In addition to TCDD-caused tissue damage described by others, the thyroid, pancreas, and interscapular brown adipose tissue (IBAT) were identified as tissues affected by TCDD. Because histological changes in the thyroid and pancreas occurred late (7 days after dosing), these effects are viewed as secondary due to altered hormonal homeostases. Both light and electron microscopic examination of IBAT identified this tissue as a target in TCDD toxicity. Histological changes in IBAT are characterized by three phases: (1) "fatty" IBAT (Days 1 to 3 after dosing); (2) fat depletion accompanied by glycogen accumulation (Days 4 to 7 after dosing); and (3) complete fat and glycogen depletion together with massive cellular damage (Days 8 to 14), particularly affecting the mitochondria. It is concluded that brown adipose tissue is a primary target in TCDD toxicity. It seems that destruction of brown adipose tissue by TCDD leads to an energy imbalance resulting in reduced oxygen consumption which forces animals to contribute a greater proportion of energy to the maintenance of their body temperature by anaerobic pathways. It is suggested that this less efficient energy utilization is the cause of a wasting syndrome.

Synergistic interaction of 2,3,7,8,-tetrachlorodibenzo-p-dioxin and hydrocortisone in the induction of cleft palate in mice

Glucocorticoids cause cleft palate in sensitive mouse strains by interfering with the proliferation of mesenchymal cells in the palatal shelves; 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) also causes cleft palate, but its effects involve the epithelial cells. The purpose of this study was to examine the interaction of TCDD and the glucocorticoid hydrocortisone in the induction of malformations. Pregnant C57BL/6N mice were treated on gestation days 10-13 with TCDD (0 or 3 micrograms/kg, p.o.), hydrocortisone (0, 25, 50, or 100 mg/kg, s.c.) or a combination of TCDD and hydrocortisone. The dams were killed on gestation day 18 and the mice were analyzed for maternal and fetal toxicity and soft tissue malformations. TCDD alone had no effect on litter size, fetal weight or viability, or maternal weight gain. This dose of TCDD is essentially a threshold dose and it did not produce cleft palate in this study, but all the TCDD-treated fetuses had hydronephrosis, the most sensitive indicator of TCDD teratogenicity. Hydrocortisone alone caused dose-related decreases in fetal weight and maternal liver/body weight ratios, and dose-related increases in cleft palate (0, 5, 10, and 30%). No effects of hydrocortisone were detected on litter size or fetal viability, but maternal weights were affected. Combination of all doses of hydrocortisone with TCDD resulted in a 100% incidence of cleft palate, accompanied by a decrease in litter size and fetal weight and an increase in fetal mortality related to the dose of hydrocortisone. TCDD tended to reverse the decrease in liver/body weight ratio seen with hydrocortisone alone.(ABSTRACT TRUNCATED AT 250 WORDS)

Effect of thyroid hormones on liver microsomal enzyme induction in rats exposed to 2,3,7,8,-tetrachlorodibenzo-p-dioxin

The effect of thyroidectomy and thyroid hormone replacement therapy on liver microsomal enzyme induction was studied in 2,3,7,8,-tetrachlorodibenzo-p-dioxin (TCDD)-treated rats (100 micrograms/kg). Treatment of non-thyroidectomized rats with TCDD had no effect on the concentration of liver microsomal cytochrome b5. In contrast, cytochrome b5 content was increased by TCDD treatment of thyroidectomized rats, regardless of replacement therapy with either T3 or T4. TCDD treatment increased the concentration of cytochrome P-450 (2-3-fold) and the activities of benzo[a]pyrene hydroxylase (4-7-fold), ethoxyresorufin O-de-ethylase (50-70-fold) and UDP-glucuronosyltransferase (5-7-fold) in non-thyroidectomized and thyroidectomized as well as thyroidectomized thyroid hormone treated rats; indicating the induction of these liver microsomal enzyme activities is independent of thyroid status. Because thyroid status alters the toxicity of TCDD but does not alter the ability of TCDD to induce microsomal enzymes, it appears that TCDD toxicity may not be directly related to microsomal enzyme induction.

Delayed wasting syndrome and alterations of liver gluconeogenic enzymes in rats exposed to the TCDD congener 3,3', 4,4'-tetrachloroazoxybenzene

A delayed wasting syndrome similar to that induced by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was observed in male Sprague-Dawley rats exposed to 3,3', 4,4'-tetrachloroazoxybenzene (TCAOB) and 3,3',4,4'-tetrachloroazobenzene (TCAB). After a slow growth period, all treatment animals (25 mg/kg, i.p., 2 doses per week) exhibited a starvation-like syndrome characterized by reduced food intake, dramatic loss of body weight and subsequent death. Although the growth of all major organs in the treatment animals was affected, the thymus appeared severely atrophied. The growth kinetics during the earlier phase were further analyzed using serially-killed rats receiving TCAOB. In addition, TCAOB was found to markedly depress the specific activity (mumol/min/g wet liver) of glucose-6-phosphatase, fructose-1,6-bisphosphatase, phosphoenolpyruvate carboxykinase, and pyruvate kinase in the liver. Significant changes in the levels of cytochrome P-450, glutamic-pyruvic transaminase and malic enzyme in the liver were also observed.

Effect of thyroidectomy and thyroxine on 2,3,7,8-tetrachlorodibenzo-p-dioxin-induced immunotoxicity

Radiothyroidectomy protected against 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-induced immunotoxicity in rats as assessed by the spleen anti-SRBC plaque-forming cell assay. Thyroxine (T4) replacement therapy partially reversed the effects of thyroidectomy on T4 and triiodothyronine (T3) serum levels, body weight and immune function as well as restored TCDD-induced immunotoxicity. Thus, hypothyroidism induced by TCDD exposure can be viewed as a protective response of the organism to reduce the insult caused by TCDD.

Thyroid hormones modulate the toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)

These experiments examine the role of thyroxine (T4) and triiodothyronine (T3) on the toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). The first experiment is continuation of a study reported previously (Rozman et al., 1984). In this experiment, 60 male Sprague-Dawley rats were divided into 6 equal groups. Four groups of rats were thyroidectomized by 3 mCi Na131 l/kg rat. Five weeks later 2 of the thyroidectomized and 1 of the nonthyroidectomized groups of rats received ip 100 micrograms TCDD/kg body weight in corn oil/acetone, whereas 3 corresponding groups of rats served as vehicle controls. Two days after dosing and every 7 d thereafter, 1 thyroidectomized control group and 1 thyroidectomized TCDD-dosed group were given ip 105 micrograms T4/kg body weight. Mortality and body weight were monitored. The course of TCDD toxicity was similar in nonthyroidectomized and thyroidectomized T4-treated rats but was different in thyroidectomized animals without T4 replacement therapy. At d 90 after TCDD dosage, mortality was still lower and the mean time to death was increased (p less than 0.01) in this group of rats compared to nonthyroidectomized or thyroidectomized T4-treated rats. However, administration of T4 starting at d 91 after dosing with TCDD resulted within 2 wk in the same final mortality in thyroidectomized rats as in nonthyroidectomized or thyroidectomized T4-treated animals, indicating that thyroid hormones modulate the time course of the wasting syndrome but do not affect the ultimate mortality figure. Body weight loss was much slower in thyroidectomized (approximately 1 g/d) than in nonthyroidectomized or thyroidectomized T4-treated rats (approximately 8 g/d). In the second experiment the three vehicle control groups of the first experiment were used. Nonthyroidectomized vehicle controls and thyroidectomized T4-treated controls were maintained as before, whereas thyroidectomized controls received T3 at 5 micrograms/kg daily. One month later each rat was dosed with TCDD at 100 micrograms/kg in corn oil/acetone. Toxicity of TCDD was similar in nonthyroidectomized, thyroidectomized T4-treated, and thyroidectomized T3-treated rats as judged by mortality, body weight, and food intake, indicating no difference between T3 and T4 in the modulation of TCDD toxicity.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD)-induced immunotoxicity

The selective toxicity of TCDD (2,3,7,8-tetrachlorodibenzo-p-dioxin) for the thymus, consisting primarily of immature T-cells, led us to search for an analogous selective toxicity for the immature B-lymphocytes in the bone marrow. In the dose-response study C57B1/6 male mice were injected with either vehicle alone (corn oil), 30, 60, or 120 micrograms/kg of TCDD i.p. The mice were killed by cervical dislocation 7 days later. In the time-response study, mice were injected with either saline or 120 micrograms/kg i.p. TCDD, 3, 7, 14, or 21 days before killing. In both studies, the following were analyzed: change in body weight, thymus weight, spleen and bone marrow cellularity, and spleen and marrow B-lymphocyte function, measured using the in vitro B-lymphocyte colony forming unit in culture assay, with the mitogen lipopolysaccharide (LPS) from Salmonella typhosa, and the in vitro plaque forming cell assay, with the thymus independent antigen, TNP-LPS. In the dose-response study there was a reduction in thymic weight, spleen B-cell functional response (per spleen), and bone marrow B-cell functional response to 14%, 35-54%, and 20-32% of control, respectively, at a dosage of 120 micrograms/kg. In the time-response study, thymic weight and bone marrow B-cell functional response (per femur) were reduced to 6% and 18% of control, respectively, at day 21. The results indicate that TCDD was selectively more toxic to the immature B-cells in the bone marrow than the more mature B-cells in the spleen. This immunotoxicity was dose-dependent.

Hexadecane increases the toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD): is brown adipose tissue the primary target in TCDD-induced wasting syndrome?

Addition of 5% hexadecane to the diet of rats increased fecal excretion of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) from 14 to 39% of an LD50 dose (60 micrograms/kg) during 10 days after dosing. This enhanced elimination did not result in reduced toxicity. On the contrary, the treatment has increased mortality from 60% in controls to 100% in hexadecane treated animals. Body weight changes were good indicators for predicting survival or nonsurvival after the LD50 dose but thymus weights were depressed without regard to survival status. The mechanism by which hexadecane potentiates the toxicity of TCDD is unknown but it is likely to be due to effects altering the disposition of TCDD. Based on similarities in the disposition of TCDD and hexachlorobenzene (HCB), it is suggested that the lethality causing target of TCDD is part of the peripheral compartment. The only site in the peripheral compartment that is compatible with the many thousand-fold species differences observed in TCDD toxicity is brown adipose tissue. The hypothesis is advanced that interaction between thyroid hormones and brown adipose tissue are responsible for the species differences in TCDD toxicity.

Separation of wasting syndrome and lethality caused by 2,3,7,8-tetrachlorodibenzo-p-dioxin

Twenty rats were administered LD50 doses of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) i.p. (60 micrograms/kg). Two days later 10 rats were started and maintained on a diet containing 5% hexadecane, whereas the other 10 rats continued receiving basal diet. Dietary hexadecane increased the mortality rate of rats from 60 to 100%. All animals destined to die showed a biphasic body weight and food intake pattern. The first 16 days after dosing were characterized by progressive weight loss which went hand in hand with increasing appetite suppression. No animal died during this initial phase. After day 16, rats overcame their loss of appetite, started eating and stabilized their body weight. During this second phase, lasting from day 16 to day 40, mortality progressed to 60 and 100% in the controls and hexadecane-treated rats, respectively. No body weight loss or change in food intake was observed in any of the surviving animals. Data indicate that TCDD-induced wasting syndrome is due to appetite suppression. However, wasting syndrome does not seem to be the ultimate cause of lethality.

Health implications of 2,3,7,8-tetrachlorodibenzodioxin (TCDD) contamination of residential soil

Extrapolations from animal toxicity experiments (including carcinogenicity and reproductive effects) to possible human heath effects can be used to estimate a reasonable level of risk for 2,3,7,8-tetrachlorodibenzodioxin (2,3,7,8-TCDD). Extrapolations are derived from: (1) review of published studies, (2) a complex set of assumptions related to human exposure to contaminated soil, and (3) estimates of (a) a dose response curve, (b) appropriate margins of safety, and/or (c) applicable mechanisms of action. One ppb of 2,3,7,8-TCDD in soil is a reasonable level at which to begin consideration of action to limit human exposure for contaminated soil.