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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

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

[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

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

A review of the genetic toxicology of chlorinated dibenzo-p-dioxins.

Information from both published and unpublished sources considered relevant to the understanding of the genetic toxicology of chlorinated dibenzo-p-dioxins is summarized in this review. Interest in writing this paper was stimulated by the fact that this class of compounds, particularly 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), has gained notoriety as an extreme environmental and industrial hazard. The potential for human exposure occurs in the work place when dioxins are formed during the synthesis of a number of commercially important compounds such as 2,4,5-trichlorophenoxyacetic acid, hexachlorophene, and pentachlorophenol. Environmental contamination may result from manufacturing processes and from dioxin contaminants in marketed products. Research on dioxins as potential mutagens was initiated because of their structural similarity to acridines, a class of known intercalating agents. To date, only 4 dioxin compounds have been evaluated for mutagenicity: the di-, tetra-, and octa-chlorinated derivatives and the unsubstituted dibenzo-p-dioxin. Since only a few of the many possible structural forms of dioxins have been tested, no definite conclusions can be made about their potential mutagenicity. Furthermore, the positive mutagenicity and cytological effects reported thus far with the few dioxin isomers examined seems to depend on the position of chlorine substitution. The most active form of the molecule is the 2,3,7,8-derivative (TCDD). Data available for assessing the mutagenic potential of TCDD are conflicting and scarce. Differences in testing results reported in these studies could be attributed to solubility problems with the test chemical, treatment protocols, purity of test samples, or toxicity. Because there are conflicting data, additional experiments are needed before the mutagenic potential of TCDD and other dioxins can be determined. Studies exploring the promoting effect of dioxins on the mutagenicity of other compounds are also recommended because experiments have shown TCDD to be an extremely active liver enzyme inducing agent that enhances the mutagenicity of certain polycyclic hydrocarbons such as 3-methylcholanthrene in vitro. The importance of discerning the hazards to human health from dioxin compounds became apparent after an accidental release of TCDD from a chemical plant contaminated the Seveso, Italy area in July 1976. This accident revealed that insufficient data were available to properly evaluate the long-term health risks posed by dioxin compounds. Several research projects were therefore initiated after the Seveso incident; it is hoped that many of the questions concerning the mutagenicity of TCDD and possibly of other dioxin congeners will be answered as a result of this work.

Acridines

Comparative molecular field analysis of polyhalogenated dibenzo-p-dioxins, dibenzofurans, and biphenyls.

Comparative molecular field analysis (CoMFA) was performed on polyhalogenated dibenzo-p-dioxins, dibenzofurans, and biphenyls for Ah (dioxin) receptor binding and associated enzyme inducing activities determined by others using in vitro assays. Since various members of all three classes of compounds have been shown to produce qualitatively similar toxicities, a separate CoMFA was performed on each class of compounds and combinations of the different classes for each bioactivity which included combining all three classes of molecules in one CoMFA study. For the Ah receptor binding, the CoMFA-derived QSARs for all three classes of compounds and combinations thereof showed strong crossvalidated correlations indicating that they are highly predictive. For enzyme induction, the CoMFA-derived QSARs were highly predictive for the dibenzofurans but were only partially successful for the dioxins. For the biphenyls, the results were clearly unpredictive. The overall results of these CoMFA studies which include both steric and electrostatic considerations are compared and contrasted to other SAR models that have met with some success in making qualitative predictions about the potential for receptor binding and associated toxicity in these classes of compounds. The CoMFA-derived QSAR for the dioxin series of molecules in most cases significantly overestimates the enzyme inducing ability of the ortho-substituted biphenyls. This weak inducing activity of the o-biphenyls is, however, consistent with their relatively low dioxin-like toxicity as measured in other biological systems. Fundamentally different mechanisms may be operating in the expression of dioxin-like toxic responses for the o-biphenyls, and their direct, dioxin-like toxic equivalency perhaps needs to be reconsidered in this light.

Aryl Hydrocarbon Hydroxylases

Comparative toxicity of four chlorinated dibenzo-p-dioxins (CDDs) and their mixture. Part I: Acute toxicity and toxic equivalency factors (TEFs).

There is presently no scientifically proven method to assess the toxicity of environmental samples containing complex mixtures of chlorinated dibenzo-p-dioxins (CDDs) of known composition. Their risk assessment is currently based on the interim concept of toxicity equivalency factors (TEFs), with the unproven assumption that all interactions of CDDs are additive. To address this problem we conducted acute toxicity studies with four different CDDs, viz 2,3,7,8-tetrachlorodibenzo-p-dioxin (tetra-CDD), 1,2,3,7,8-pentachlorodibenzo-p-dioxin (penta-CDD), 1,2,3,4,7,8-hexachlorodibenzo-p-dioxin (hexa-CDD) and 1,2,3,4,6,7,8-heptachlorodibenzo-p-dioxin (hepta-CDD), all containing chlorine substituents in the crucial 2,3,7,8-positions. The homologues, dissolved in corn oil/acetone, were administered to groups of five male Sprague Dawley rats at several doses (at least three) by gastric intubation. The obtained mortality data were employed to calculate the LD20,50 and 80 for each homologue. These data were subsequently used to prepare equipotent doses (expected mortality of 20, 50 and 80%) of a mixture containing all four homologues, each of them contributing one fourth of the toxicity, under the assumption of additive toxicity. The obtained LD50 value and (TEF) was for tetra-CDD 43 micrograms/kg (1), penta-CDD 206 micrograms/kg (0.2) hexa-CDD 887 micrograms/kg (0.05) and hepta-CDD 6325 micrograms/kg (0.007), respectively. The dose-response to the mixture confirmed the hypothesis of strict additivity in the acute toxicity of the four CDD homologues.

Animals

Polychlorinated dibenzo-p-dioxins. Separation and identification of isomers by gas chromatography-mas spectrometry.

Attempts were made to synthesize all polychlorinated dibenzo-p-dioxin isomers containing six to eight chlorine atoms by micro-scale pyrolysis of different polychlorophenates. Eight of the ten possible hexachlorodibenzo-p-dioxins, the two hepta- and the octachlorodibenzo-p-dioxin were observed and separated by gas chromatography using glass capillary columns. Without actual isolation of these toxic materials, isomers were characterized by gas chromatography and mass spectrometry. Commercial chlorinate phenols were analyzed for the presence of these isomers. The major hexachlorodibenzo-p-dioxin observed in two commerical products was the unexpected 1,2,3,7,8,9-substituted isomer, which was not formed as the main dioxin component in any of the pyrolysis experiments. The same isomer was reported to be isolated from toxic fat and identified by X-ray crystallography.

Chlorobenzenes