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Dual roles of the 90-kDa heat shock protein hsp90 in modulating functional activities of the dioxin receptor. Evidence that the dioxin receptor functionally belongs to a subclass of nuclear receptors which require hsp90 both for ligand binding activity and repression of intrinsic DNA binding activity.

Signal transduction by dioxin (2,3,7,8-tetrachloro-dibenzo-p-dioxin) is mediated by the intracellular dioxin receptor which, in its dioxin-activated state, regulates transcription of target genes encoding drug metabolizing enzymes such as cytochrome P-450IA1 and glutathione S-transferase Ya. Upon binding of dioxin the receptor translocates from the cytoplasm to the nucleus in vivo and is converted from a latent non-DNA binding form to a species which binds to dioxin-responsive positive control elements in vitro. The latent receptor form is associated with an inhibitory protein (the 90-kDa heat shock protein, hsp90), the release of which is necessary to unmask the DNA binding activity of the receptor. Here we have established a protocol to disrupt the hsp90-receptor complex in the absence of ligand. We show that it was possible to covalently cross-link with dioxin only the hsp90-associated form of dioxin receptor. In contrast, the disrupted hsp90-free form of receptor did not form a stable complex with dioxin but bound DNA constitutively. Moreover, we could partially reconstitute the ligand binding activity of the salt-disrupted hsp90-free dioxin receptor by incubation with hsp90-containing reticulocyte lysate but not by incubation with wheat germ lysate which lacks immuno-detectable levels of hsp90. Thus, we demonstrate that the dioxin receptor loses its high affinity ligand binding activity following release of hsp90 and that it is possible to reverse this process. In conclusion, hsp90 appears to play dual roles in the modulation of functional activities of the dioxin receptor: (i) it represses the intrinsic DNA binding activity of the receptor and (ii) it appears to determine the ability of the receptor to assume and/or maintain a ligand binding conformation.

Affinity Labels

Carcinogenic bioassay of the herbicide, 2,4,5-trichlorophenoxyethanol (TCPE) with different 2,3,7,8-tetrachlorodibenzo-p-dioxin (dioxin) content in Swiss mice.

The carcinogenic effect of a herbicide trichlorophenoxyethanol (TCPE) was investigated. The substance always contains 2,3,7,8-tetrachlorodibenzo-p-dioxin (dioxin) as a trace contaminant. Outbred Swiss-H/Riop mice were treated for 1 year with different doses of the various admixtures of the two compounds and those of dioxin alone to determine whether their carcinogenic effects are dose-dependent. Observation time after TCPE treatment was 1 and 2 years. The maximum tolerable dose of TCPE (70 mg/kg) with a dioxin concentration of 7.10(-6) mg/kg doubled the number of liver tumours as compared to the controls. The occurrence of liver tumours decreased at the administration of lower doses of the two compounds. No change in tumour frequency could be detected when the level of dioxin as a trace contaminant was raised, either (10 ppm). According to our preliminary results, dioxin has a more toxic than carcinogenic effect. The use of TCPE as a herbicide in accordance with the proper factory regulations and the consumption of products treated with it does not seem to bear a carcinogenic risk for the consumer.

2,4,5-Trichlorophenoxyacetic Acid

Disposition of 2,3,7,8-tetrabromodibenzo-p-dioxin and 2,3,7,8-tetrachlorodibenzo-p-dioxin in the rat: biliary excretion and induction of cytochromes CYP1A1 and CYP1A2.

The biologic activity and pharmacokinetic properties of 2,3,7,8-tetrabromodibenzo-p-dioxin (TBDD) are similar to those of the chlorinated congener, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Metabolism of both compounds appears to be rate-limiting for excretion, which is primarily via the feces. Therefore, the biliary elimination of TBDD and TCDD was examined as an indirect assessment of metabolism. Male F344 rats were anesthetized with pentobarbital, and 1 nmol/kg [3H]TBDD or [3H]TCDD was administered iv. Bile was collected for up to 8 hr while rats were maintained under anesthesia. The rate of biliary excretion of radioactivity was slightly greater for TCDD than TBDD (10% vs 7% in 5 hr). All biliary radioactivity was attributable to metabolites. High pressure liquid chromatographic (HPLC) profiles of biliary radioactivity were similar for [3H]TBDD and [3H]TCDD. To determine if pretreatment altered elimination kinetics, a single dose of 100 nmol/kg TBDD or TCDD was administered to rats by oral gavage 3 days prior to iv injection of 1 nmol/kg [3H]TBDD or [3H]TCDD, respectively. Biliary excretion of the radiolabeled dose was quantitatively and qualitatively unaffected by pretreatment despite a twofold increase in hepatic levels of radiolabel in the pretreated animals. Therefore, under these experimental conditions, autoinduction of TCDD and TBDD metabolism did not occur in the rat in vivo at doses which elicited enhanced hepatic uptake. In a second set of studies, the dose-response profiles for induction of cytochromes CYP1A1 and CYP1A2 by TBDD were characterized. The ED50 value for CYP1A1 induction (measured by ethoxyresorufin O-deethylase activity and radioimmunoassay (RIA) was estimated to be 0.8-1.0 nmol/kg, similar to what has been reported for TCDD. Induction of CYP1A2 (RIA) by TBDD appeared to be a more sensitive response over the dose range studied. Finally, comparison of hepatic CYP1A2 induction vs hepatic concentrations of TBDD 3 days following treatment with 10 vs 1 nmol/kg TBDD suggested that induction of CYP1A2 alone may not account for nonlinearities in dioxin disposition exemplified by dose-related increases in the ratio of dioxin concentrations in liver and adipose tissue.

Animals

Factors affecting the toxicity of dioxin-like toxicants: a molecular approach to risk assessment of dioxins.

The numerous toxic responses of dioxin-like compounds are mediated by the intracellular Ah (aryl hydrocarbon) receptor. It has been suggested that the regulation of dioxins and similar substances could be placed on a molecular foundation by considering the proportion of Ah-receptor sites occupied by toxicant molecules. The present work has shown that the following formation not yet available would be needed in order to develop this approach: correlation between dioxin exposure and human tissue levels; accurate determination of the association constants for human Ah-receptor with toxicant, and for human receptor-ligand complex with DNA; and knowledge of the intracellular concentrations of both receptor binding sites and DNA binding sites. Furthermore, since not all dioxin-like substances behave identically, this information would need to be gathered for a wide variety of substances.

Animals

Persistent brominated and chlorinated dioxin blood levels in a chemist. 35 years after dioxin exposure.

This is the first report on occupational health hazards to dioxin chemists associated with laboratory exposure to 2,3,7,8-tetrabromodibenzodioxin (TBrDD), and further characterizes the human response to 2,3,7,8 tetrachlorodibenzodioxin (TCDD). In this case study the chemist was exposed on two separate occasions. In March 1956, after synthesizing 10 g of TBrDD, the chemist suffered from mild and transient chloracne of the neck and wrists; in September 1956, after synthesizing 16 g of TCDD, he suffered severe chloracne of the entire body, headaches, backache, and leg pain on exertion. His measured 2,3,7,8-TBrDD in 1991 was 625 parts per trillion (ppt) in whole blood lipid, 35 years after initial exposure and 18 ppt TCDD, an elevated level in comparison with the mean 2,3,7,8-TCDD level of 5 ppt in the US population. This is the first reported detection of a brominated dioxin in human tissue. The total halogenated dioxin body burden in September 1956 is estimated to have been between 13,005 ppt and 146,726 ppt. This amount can be considered to be, at least in this person, a strong chloracnegenic dose, and a dose causing human nervous system and muscular or circulatory system responses. This uptake demonstrates an occupational hazard to chemists and chemical workers, and the usefulness of human tissue dioxin measurements to document absorption.

Adult

Phorbol esters inhibit the dioxin receptor-mediated transcriptional activation of the mouse Cyp1a-1 and Cyp1a-2 genes by 2,3,7,8-tetrachlorodibenzo-p-dioxin.

Tetradecanoyl phorbol acetate (TPA) has been shown to inhibit 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-induced mouse P450IA1 benzo[a]pyrene hydroxylase activity (Raunio, H., and Pelkonen, O. (1983) Cancer Res. 43, 782-786). When we co-administered TPA and TCDD to C57BL/6 mice, the accumulation of TCDD-inducible liver P450IA1 and P450IA2 mRNA, as well as kidney P450IA1 mRNA, was greatly inhibited. When nuclear run-on assays were conducted, maximal levels of transcriptional activation were achieved for both liver Cyp1a-1 and Cyp1a-2 with 1 micrograms/kg (approximately equal to 3.0 nmol/kg) TCDD. TCDD elicited a dose-dependent increase in the rates of gene transcription, which paralleled the induction of P450IA1 and P450IA2 mRNA. Only Cyp1a-1 gene transcription was elevated in kidney. When these experiments were repeated following the co-administration of TPA with TCDD, the levels of TCDD-mediated transcriptional increases in liver Cyp1a-1 and Cyp1a-2 and P450IA1 and P450IA2 mRNAs were dramatically inhibited. The reduction in Cyp1a gene transcription by TPA could be accounted for by reduced DNA binding of the dioxin receptor to the xenobiotic-responsive element (XRE) sequences, as measured by gel-retardation analysis. Analysis of nuclear [3H]TCDD dioxin receptor by sucrose density gradients demonstrated that the inhibition of Cyp1a gene transcription and DNA binding by TPA resulted from a reduction in nuclear dioxin receptor concentration.

Animals

A histochemical study of the liver lesion induced by 2,3,7,8-tetrachlorodibenzo-p-dioxin (dioxin) in rats.

A histochemical study of plasma-membrane associated enzymes in rat liver demonstrated a significant lesion 3 days after a single oral dose of 2,3,7,8-tetrachlorodibenzo-p-dioxin (dioxin). The complete loss of canalicular ATPase reaction in the parenchymal cells of the centrilobular zone remained the prominent feature of the liver throughout the 6-wk period studied. Involvement of the periportal and midzonal regions occurred in moribund animals and improvement in the health of two surviving animals at 9 mth was associated with a normal distribution of ATPase in the liver. Qualitative changes in 5-nucleotidase and acid phosphatase were secondary to the parenchymal cell damage. This lesion supports the morphological evidence, reported previously, that the parenchymal cell plasma-membrane is a specific subcellular site of the toxic action of dioxin.

Acid Phosphatase

Decreased hepatic phosphoenolpyruvate carboxykinase gene expression after 2,3,7,8-tetrachlorodibenzo-p-dioxin treatment: implications for the acute toxicity of chlorinated dibenzo-p-dioxins in the rat.

Decreased activity of the rate limiting gluconeogenic enzyme, phosphoenolpyruvate carboxykinase (PEPCK), has been recently suggested to be the critical lesion in the acute toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). We now show that other toxicologically relevant chlorinated dibenzo-p-dioxins (CDDs), with chlorine substituents in the crucial 2-,3-,7-, and 8-positions, exert the same effect on PEPCK activity. The doses required to cause this enzyme inhibition are within the acutely toxic range for each homologue, suggesting the same mechanism of action for these compounds. To further investigate the mechanism whereby dioxins decrease PEPCK activity, Northern analysis was performed using a cDNA probe complementary to a portion of the PEPCK mRNA. We could demonstrate that after TCDD treatment hepatic PEPCK mRNA was decreased by as much as 90% compared to pair-fed control animals (day 8 after dosing). This decrease in PEPCK mRNA was paralleled by a decrease of the amount of PEPCK protein and enzymatic activity. These results indicate that the physiological changes which occur in TCDD-treated animals (decreased feed consumption, low plasma insulin and elevated plasma corticosterone levels) which under normal conditions increase PEPCK gene expression and enzyme activity, are not effective in stimulating PEPCK synthesis in TCDD-treated animals.

Animals

Placental transport of dioxins from mother to fetus. II. PCBs, dioxins and furans and vitamin K metabolism.

Placental transport of dioxins and furans from mother to fetus takes place. It is probably related to the fatty acid transport. Between 10 and 20% of fatty acids in a full-term baby are of maternal origin. In adipose tissue of children that died in the early neonatal period concentrations of +/- 25% were found of three dioxin and furan congeners 12378 P5CDD, 123678 H6CDD, and 23478 P5CDF in relation to a mean concentration of these congeners in the fat of 14 breastmilk samples. Data of concentrations are given as measured in liver and adipose tissue. In the placenta of a Dutch woman an accumulation of dioxins and furans is found in relation to blood. Animal studies support the hypothesis that polychlorobifenyls play a role in the cause of the late hemorrhagic disease in the newborn, in particular the 2, 4, 5, 2, 4, 5-hexachlorobifenyl that is present in relatively high concentrations in breastmilk.

Dioxins

Long-term carcinogenesis studies on 2,3,7,8-tetrachlorodibenzo-p-dioxin and hexachlorodibenzo-p-dioxins.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) and 1,2,3,6,7,8- and 1,2,3,7,8,9-hexachlorodibenzo-p-dioxins (HCDDs) are among the most toxic and carcinogenic of "man-made" chemicals. These "dioxins," as well as many of the other polychlorinated dibenzodioxins (PCDDs) and dibenzofuran (PCDFs) derivatives, are chlorinated aromatic compounds which are chemically stable, insoluble in water, and highly soluble in fats and oils. TCDD acts as a complete carcinogen in several species, causing both common and uncommon tumors at multiple sites. It is a highly potent chemical carcinogen in chronic animal studies, producing carcinogenic effects in laboratory animals with doses as low as 0.001 micrograms/kg/day. In rats, TCDD induces neoplasms in the lung, oral/nasal cavities, thyroid and adrenal glands, and liver. In mice, TCDD induces neoplasms in the liver and subcutaneous tissue, thyroid gland, and thymic lymphomas. In hamsters, it induces squamous cell carcinomas of the facial skin. Tumors of the integumentary system are reported after oral (mice and rats), intraperitoneal (hamsters), and dermal (mice) administration. A mixture of HCDDS (defined as the mixture of the 1,2,3,6,7,8- and 1,2,3,7,8,9 isomers used in the NTP experiments) are potent liver carcinogens in mice and rats. Pharmacokinetic studies in laboratory animals indicate that 50-90% of dietary TCDD is absorbed. It concentrates in adipose tissue and the liver. In mammals, the TCDD present in the liver is slowly redistributed and stored in fatty tissue. Elimination of TCDD occurs via excretion of metabolites in the bile and urine and passively through the gut wall. Metabolism is slow: the biological half-life of TCDD varies from weeks (rodents) to years (humans), and is strongly dependent upon the rate of TCDD metabolism. Many of the toxic effects of TCDD, including teratogenicity, may arise by receptor-mediated mechanisms. The induction of cytochrome P-448 and related enzymes by TCDD occurs by such a mechanism, and is related to the binding of TCDD to the Ah receptor. The specific mechanism(s) by which TCDD exerts its carcinogenic effects is unclear: receptor-binding may be part of the story. The role of the Ah receptor has been indicated in a skin promotion assay. The evidence for mutagenicity is inconclusive. TCDD did not induce lethal mutations, chromosomal aberrations, micronuclei or sister chromatid exchanges in rodents treated in vivo, nor was it mutagenic to bacteria, but it did enhance transformation of mouse C3H 10T1/2 cells by N-methyl-N'-nitro-N-nitrosoguanidine and was mutagenic to mouse lymphoma cells.(ABSTRACT TRUNCATED AT 400 WORDS)

Animals

[Similarities in the biochemical effects of tetrachloro 2,3,7,8 dibenzo-p-dioxin and tetrabromo-2,3,7,8 dibenzo-p-dioxin on rats].

Screening tests for the study of carcinogenic compounds showed that 2,3,7,8-tetrabromodibenzo-p-dioxin was at least as active as 2,3,7,8-tetrachlorodibenzo-p-dioxin in regard to its effect on the in vivo synthesis of zoxanzolamine hydroxylase and on the arginase activity of the liver. The biological properties of these compounds seem to be due to the symmetry of their m molecular structure.

Animals

Arachidonic acid metabolism by dioxin-induced cytochrome P-450: a new hypothesis on the role of P-450 in dioxin toxicity.

Dioxin (2,3,7,8-tetrachlorodibenzo-p-dioxin, TCDD) is a highly potent inducer of cytochrome P-450. The role of the induced P-450 in TCDD toxicity has been obscure as P-450 neither detoxifies TCDD nor activates it to genotoxic or cytotoxic metabolites. We show, using a chick embryo model, that TCDD causes major increases in the NADPH dependent metabolism of arachidonic acid (AA), a predominant cell membrane fatty acid, that it does so with extremely high potency (ED50, 6.3 pmol per egg) and that this metabolism is catalyzed by TCDD-induced cytochrome P-450 species. Thus, TCDD treatment increased by six to ten fold the P-450 mediated hepatic microsomal metabolism of AA to epoxides and monohydroxyeicosatetraenoic acids, products whose diverse biological activities suggest links to TCDD's toxic effects. In contrast only x and x-1 hydroxy AA, inactive products, were significantly formed by the controls. These findings open a new perspective on how P-450 induction could be related to the diverse toxic effects of TCDD. They lead to the novel hypothesis that TCDD-induced cytochrome P-450 metabolizes an endogenous fatty acid to reactive products that in turn mediate or modulate varied manifestations of TCDD toxicity.

Animals

Swedish dioxin survey: evaluation of the H-4-II E bioassay for screening environmental samples for dioxin-like enzyme induction.

The H-4-II E enzyme induction bioassay was used for testing both pure reference substances and extracts of wildlife samples. Polychlorinated naphthalenes were found to be as active as enzyme inducers as certain coplanar polychlorinated biphenyls (PCBs). Also a mixture of polybrominated diphenyl ethers (Bromkal 70-5DE) was shown to induce enzyme activity. In extracts of herring, containing polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs), bioassay and chemically derived TCDD-equivalents (TEQs) were nearly identical. When extracts containing other types of dioxin-like compounds as well were tested, the bioassay TEQs for most of them agreed well with chemical TEQs calculated for PCDDs, PCDFs and non-ortho PCBs. However, for ringed seal and whitefish, TEQs obtained from the bioassay were higher than those from the chemical analysis. Our results indicate that this bioassay is an excellent complement to chemical residue analysis and a useful tool in understanding the complex interactions of halogenated hydrocarbons. For risk assessment, such results should, however, be used most carefully as they are measured in vitro.

Animals

Polyhalogenated dibenzo-p-dioxins and dibenzofurans and the immune system. 4. Effects of multiple-dose treatment with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on peripheral lymphocyte subpopulations of a non-human primate (Callithrix jacchus).

Non-human primates (Callithrix jacchus) were treated with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) over a period of 30 weeks, and lymphocyte subpopulations of venous blood were monitored using monoclonal antibodies and flow cytometry (FACScan). There was no clear-cut change in the total lymphocyte population during this study. In the first part of the study the new-world monkeys (marmosets) were treated for 24 weeks with a weekly dose of 0.3 ng TCDD/kg body wt. At the end of this treatment period a level corresponding to an actual cumulative dose of about 2.5-2.7 ng TCDD/kg body wt was expected. The percentage and the absolute number of the CD4+CDw29+ cells ("helper inducer" or "memory" cells) surmounted the physiologically occurring increase. Concomitantly the percentage of the CD4+CD45RA+ cells ("suppressor-inducer" or "naive" cells) decreased. There was, at the same period, no change in the total T cell population (CD2+ cells) or in the cells carrying the CD8 or the CD4 epitope. When increasing the weekly dose to 1.5 ng TCDD/kg body wt, a transient increase in the percentage and the absolute number of the CD8+CD56+ cell population ("cytotoxic T cells") was observed 3 weeks after the increase in dosing. At this time the expected decrease in the percentage or the absolute number of CD4+CDw29+ cells was just detectable and this decline was at its maximum 6 weeks after switching to the higher weekly doses. The reduction in the percentage and the absolute number of CD4+CDw29+ cells persisted 5 weeks after discontinuation of the dosing, but this cell population was again within normal limits 7 weeks later. Because the two subpopulations are changed in opposite directions, the ratio CD4+CDw29+/CD4+CD45RA+ is a very sensitive measure of the effect induced by TCDD. There was a pronounced decrease in the percentage of the CD20+ cells (B1 cells), but their percentage and number rapidly normalized, in contrast to the CD4+CDw29+ cells, when the dosing was discontinued. At the end of the treatment period the apparent body burden was calculated to correspond to an actual dose of about 9-10 ng TCDD/kg body wt. Such an actual dose level might be assumed to be reached under steady-state conditions in chronic experiments with daily doses of about 135 pg TCDD/kg body wt (assuming a half-life for TCDD in the marmoset of 6-8 weeks). Extrapolations of the results obtained at higher doses to very low exposures is not justified with respect to the effects induced by TCDD on the immune system of marmosets. At lower doses the effect is clearly reversed.

Animals

Polyhalogenated dibenzo-p-dioxins and dibenzofurans and the immune system. 2. In vitro effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on lymphocytes of venous blood from man and a non-human primate (Callithrix jacchus).

The effect of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on poke weed mitogen-stimulated proliferation and differentiation of peripheral lymphocytes was studied in vitro with cells from a non-human primate (marmoset monkey, Callithrix jacchus) and from man. Monoclonal antibodies and flow cytometry (FACScan) were used for analysis. The extent of the overall mitogen-stimulated proliferation of isolated lymphocytes in vitro from marmoset blood was only slightly reduced in the presence of TCDD compared to the solvent control (0.01% DMSO). However, incubation with TCDD in the culture medium together with the mitogen led to a pronounced decrease in the percentage of the lymphocyte subset with the surface marker CD4, and a concomitant increase in the percentage of CD8+ cells. The lowest concentration found to be effective in vitro was 1 x 10(-13) M TCDD (25 fg TCDD/ml). When culturing lymphocytes from human blood of different donors under identical conditions in the presence of TCDD and the mitogen, corresponding effects were observed to those seen with marmoset cells. A closer analysis of the T lymphocyte subsets affected revealed the CD4+ CDw29+ (helper-inducer cells) to be the main target for the action of TCDD. A clear-cut change in the percentage of this subpopulation was induced at concentrations as low as 1 x 10(-13) M TCDD. The development of the IL-2-marker in culture was only slightly affected by TCDD, and concentrations of 1 x 10(-12) M were required to slightly reduce the number of CD2+CD25+ cells.(ABSTRACT TRUNCATED AT 250 WORDS)

Animals

2,3,7,8-Tetrachlorodibenzo-p-dioxin increases reliance on fats as a fuel source independently of diet: evidence that diminished carbohydrate supply contributes to dioxin lethality.

The environmental toxin, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) causes a wasting syndrome marked by hypophagia, loss of body fat, changes in intermediary metabolism and death. Use of conventional laboratory animals has not resolved whether or not TCDD affects intermediary metabolism independently of hypophagia. We used the chick embryo, which does not require an exogenous food supply for energy, to answer this question. Our results show that TCDD treatment increases dependence on fats as a fuel source independently of changes in food intake and therefore can affect intermediary metabolism independently of hypophagia. Results of experiments using aminocarnitine to inhibit fatty acid oxidation suggest that TCDD treatment impairs carbohydrate production rather than its utilization and that the former effect contributes to TCDD lethality.

Animals