Polychlorinated dibenzofurans (PCDFs): correlation between in vivo and in vitro structure-activity relationships

Feed materials - Levels and characteristic profiles of dioxins and PCBs

Dioxins (PCDD/PCDF) are toxic compounds that are ubiquitous in the environment; although present in low concentrations, they are persistent and highly toxic and they bioaccumulate in food chains. Therefore, it is very important that feed is free of these types of contaminants, because otherwise they can become a source that can negatively affect animal health and the safety of food of animal origin. The aim of the study was to comprehensively assess the concentrations of dioxins and polychlorinated biphenyls (PCBs) in a variety of feed materials available on the Polish market. In addition, characteristic profiles of congeners for given categories of feeds were investigated and defined. Approximately 95 % of the 523 samples of various feed materials tested over seven years (2013-2018 and 2022) met the requirements of European Union feed law (Commission Regulation 277/2012/EU). The highest average PCDD/PCDF/dl-PCB concentrations were found in fish oils and meal and were respectively 1.17 ± 0.78 and 5.51 ± 4.51 ng WHO-TEQ/kg of feed at 12 % moisture. Median and background level concentrations of PCDD/PCDFs, dl-PCBs, PCDD/PCDF/dl-PCBs, and ndl-PCBs were significantly lower than their average concentrations for each individual feed material category. The WHO-TEQ profiles enabled the identification of three different characteristic profiles in feed materials.

QSARs for congener-specific toxicity of polyhalogenated dibenzo-p-dioxins with DFT and WHIM theory

Polyhalogenated dibenzo-p-dioxins (PHDDs) have become the most notorious pollutants in the environment. However, the origin of their congener-specific toxicity is not well understood. For explaining the difference in toxicity between PHDDs as well as their potencies of aryl hydrocarbon hydroxylase (AHH) and 7-ethoxyresorufin O-deethylase (EROD) induction, quantitative structure-activity relationships (QSARs) were constructed through the combined application of DFT (density functional theory) and WHIM (weighted holistic invariant molecular) theory. Results from the QSAR analyses suggest that dispersion interaction along the lateral sites of PHDDs should interpret the vast majority of variance of binding affinities as well as the consequent toxicity. Although electrostatic interaction is comparatively less influential, it should not be negligible. Long-range dispersion interaction is also described in QSARs with minute influence. Quadrupole moment tensor perpendicular to the ring plane, i.e., Q(zz) and its implicated electrostatic interaction plays an important role in the contribution to induction potencies.

The search for endogenous activators of the aryl hydrocarbon receptor

The primary design of this perspective is to describe the major ligand classes of the aryl hydrocarbon receptor (AHR). A grander objective is to provide models that may help define the physiological activator or "endogenous ligand" of the AHR. We present evidence supporting a developmental role for the AHR and propose mechanisms by which an endogenous ligand and consequent AHR activation might be important during normal physiology and development. From this vista, we survey the known xenobiotic, endogenous, dietary, and "unconventional" activators of the AHR, including, when possible, information about their induction potency, receptor binding affinity, and potential for exposure. In light of the essential function of the AHR in embryonic development, we discuss the candidacy of each of these compounds as physiologically important activators.

DFT study on the structure-toxicity relationship of dioxin compounds using PLS analysis

Density functional theory (DFT) at B3LYP/6-311G** level was employed to optimise the dioxin compounds, i.e., 25 polychlorinated or brominated dibenzo-p-dioxins (PCDDs or PBDDs) and 34 polychlorinated dibenzofurans (PCDFs) involved in this investigation. Three groups of descriptors mainly related to chemical reactivity, molecular overall charge distribution and thermochemical property were calculated. With partial least squares (PLS) analysis and variable importance in the projection (VIP), the least significant descriptors were removed from the quantitative structure-activity relationship (QSAR), which was focused on exploring the influential factors responsible for the variance of binding affinities of dioxins to aryl hydrocarbon receptor (AhR). With better-improved and predictive QSAR (Q(2)(cum) = 0.827), further understanding of the nature of toxicity was available. Both dispersion interaction and electrostatic interaction were considered to be important and together capable of accounting for the most part of the total binding affinities, though the former could make more contribution than the latter. Comparatively, the long-range dispersion interaction should be very small.

QSARs for the toxicity of polychlorinated dibenzofurans through DFT-calculated descriptors of polarizabilities, hyperpolarizabilities and hyper-order electric moments

DFT-B3LYP method with 6-31G(**) basis set was employed to fully optimize the electronic structures of 135 polychlorinated dibenzofurans and parent compound, namely dibenzofuran. It was demonstrated that polarizability anisotropy and mean polarizability could change sensitively and systematically with chlorine number and substitution pattern. And new quantitative structure-activity relationships (QSARs) focused on the binding affinities of aryl hydrocarbon receptor (AhR), aryl hydrocarbon hydroxylase (AHH) and 7-ethoxyresorufin O-deethylase (EROD) induction potencies of PCDFs were developed. It was concluded that polarizability anisotropy in conjunction with hyperpolarizabilties and hyper-order electric moments, e.g. octupole moments could well interpret the variation of toxicity of different congeners and dispersion interaction should be the leading form among various interactions. Although the terms of hyperpolarizabilities and hyper-order electric moments were not the same significant ones as polarizability anisotropy, the long-range interactions characterized by them should not be ignored in explaining the toxicity.

Combining NMR spectral and structural data to form models of polychlorinated dibenzodioxins, dibenzofurans, and biphenyls binding to the AhR

A three-dimensional quantitative spectrometric data-activity relationship (3D-QSDAR) modeling technique which uses NMR spectral and structural information that is combined in a 3D-connectivity matrix has been developed. A 3D-connectivity matrix was built by displaying all possible assigned carbon NMR chemical shifts, carbon-to-carbon connections, and distances between the carbons. Two-dimensional 13C-13C COSY and 2D slices from the distance dimension of the 3D-connectivity matrix were used to produce a relationship among the 2D spectral patterns for polychlorinated dibenzofurans, dibenzodioxins, and biphenyls (PCDFs, PCDDs, and PCBs respectively) binding to the aryl hydrocarbon receptor (AhR). We refer to this technique as comparative structural connectivity spectral analysis (CoSCoSA) modeling. All CoSCoSA models were developed using forward multiple linear regression analysis of the predicted 13C NMR structure-connectivity spectral bins. A CoSCoSA model for 26 PCDFs had an explained variance (r2) of 0.93 and an average leave-four-out cross-validated variance (q(2)4) of 0.89. A CoSCoSA model for 14 PCDDs produced an r2 of 0.90 and an average leave-two-out cross-validated variance (q(2)2) of 0.79. One CoSCoSA model for 12 PCBs gave an r2 of 0.91 and an average q(2)2 of 0.80. Another CoSCoSA model for all 52 compounds had an r2 of 0.85 and an average q(2)2 of 0.52. Major benefits of CoSCoSA modeling include ease of development since the technique does not use molecular docking routines.

Disposition of polychlorinated dibenzo-p-dioxins, dibenzofurans, and non-ortho polychlorinated biphenyls in pregnant long evans rats and the transfer to offspring

Pharmacokinetic properties of polychlorinated dibenzo-p-dioxins, dibenzofurans (PCDFs), and non-ortho biphenyls (PCBs) play a critical role in their relative toxicity. The present study examined the transfer of these chemicals to offspring and placenta. Pregnant Long Evans rats received 0.0 (control), 0.05, 0.2, 0.8, and 1.0 microg/kg of dioxin toxic equivalence (TEQ) by oral gavage on the 15th gestational day (GD 15), using a dosing mixture that contained 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 2,3,7,8-tetrachlorodibenzofuran (TCDF), 1,2,3,7,8-pentachlorodibenzo-p-dioxin (PeCDD), 1,2,3,7,8-pentachlorodibenzofuran (1-PeCDF), 2,3,4,7,8-pentachlorodibenzofuran (4-PeCDF), octachlorodibenzofuran (OCDF), 3,3',4,4'-tetrachlorobiphenyl (PCB 77), 3,3',4,4',5-pentachlorobiphenyl (PCB 126), and 3,3',4,4',5,5'-hexachlorobiphenyl (PCB 169) in ratios approximating that in food. Rats were euthanized on GD 16, GD 21, and postnatal day 4 (PND 4). The chemical concentrations in fetus, pup, placenta, and maternal liver, serum, and adipose tissue were determined using gas chromatography/high-resolution mass spectrometry. A dose-dependent increase in hepatic sequestration was seen with TCDD, PeCDD, 4-PeCDF, OCDF, PCB 126, and PCB 169, and the transfer to offspring was reduced at higher doses. 4-PeCDF, PeCDD and PCB 126 showed higher liver affinity than TCDD. TCDF, 1-PeCDF, and PCB 77 were metabolized rapidly. On GD 16, TCDD and the three PCBs reached equilibration between the fetus and placenta, but this did not occur with PeCDD and 4-PeCDF until GD 21, according to the lipid-based concentrations. Offspring compartments received more of the dosed compounds lactationally than transplacentally (7-28% versus 0.5-3%). The behavior of each congener was dose-dependent; therefore, extrapolation of high-dose experimental data should be used with caution.

Relative potency values derived from hepatic vitamin A reduction in male and female Sprague-Dawley rats following subchronic dietary exposure to individual polychlorinated dibenzo-p-dioxin and dibenzofuran congeners and a mixture thereof

This study investigated the potency of individual polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs) to reduce hepatic vitamin A in the rat. Dose-response relationships were determined following long-term dietary exposure to 2,3,7, 8-tetrachlorodibenzo-p-dioxin (TCDD), 2,3,4,7, 8-pentachlorodibenzofuran, 1,2,3,4,8-pentachlorodibenzofuran, 1,2,3, 7,8-pentachlorodibenzofuran, 1,2,3,6,7,8-hexachlorodibenzofuran, 1,2, 3,7,8-pentachlorodibenzo-p-dioxin, octachlorodibenzo-p-dioxin, octachlorodibenzofuran, or mixtures of some of these congeners. The aim was to estimate vitamin A-related relative potency (REP) values for each congener in relation to that of TCDD and to investigate if these values were in accordance with REP values estimated for the subchronic toxicity observed in the same study. An additional aim was to investigate if the effect on hepatic vitamin A levels was additive compared to the effect of the individual congeners. The obtained results demonstrate that hepatic vitamin A reduction occurs as a consequence of long-term low-level exposure to 2,3,7, 8-substituted but not to non-2,3,7,8-substituted congeners. Female rats were slightly more responsive to this effect as judged from the lower EC50 values for all the congeners in this sex. The vitamin A-related REP values were similar for female and male rats and were in good agreement with the estimated REP values for subchronic toxicity in the same animals. The vitamin A effect of the individual congeners in the mixture tended to be somewhat less than pure additive for male rats and very close to pure additive for female rats. In conclusion, the presented data show that reduction of hepatic vitamin A is a sensitive marker of an altered retinoid homeostasis following long-term low-dose exposure to dioxin-like compounds, which essentially conforms to their assumed additive mechanism of action.

Effects of polychlorinated dibenzofurans, biphenyls, and their mixture with dibenzo-p-dioxins on ovulation in the gonadotropin-primed immature rat: support for the toxic equivalency concept

Previous studies have shown that 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 1,2,3,7,8-pentachlorodibenzo-p-dioxin (PeCDD), and 1,2,3,4,7, 8-hexachlorodibenzo-p-dioxin (HxCDD), and their equipotent mixture block ovulation, reduce ovarian weight gain and alter preovulatory hormone levels in a similar manner. The objective of the current experiment was to investigate the effect of other structurally related compounds such as chlorinated furans and biphenyls on ovulation and related hormonal endpoints. The gonadotropin-primed immature female rat model was used to study the effect of 2,3,4,7, 8-pentachlorodibenzofuran (PeCDF), 3,3',4,4',5-pentachlorobiphenyl (PeCB), and 2,2',5,5' tetrachlorobiphenyl (TCB) and their mixture with polychlorinated dibenzo-p-dioxins (PCDDs) on ovulation. Rats were dosed on Day 23 of age at 0900 h with individual congeners (PeCDF, PeCB, TCB) or a mixture of five compounds, which included TCDD, PeCDD, HxCDD, in addition to PeCDF and PeCB. Equine choronic gonadotropin (eCG; 5 IU) was injected 24 h later to induce follicular development. Blood and ovaries were harvested, and ovarian weights determined at various times after eCG. Serum concentrations of 17beta-estradiol (E(2)), progesterone (P(4)), luteinizing hormone (LH), and follicle-stimulating hormone (FSH) were determined by radioimmunoassay. At 72 h after injection of eCG, the number of ova shed was measured by irrigating the ova from oviducts. The slopes of the dose-responses for inhibition of ovulation generated by the individual PeCDF, PeCB, and/or their mixture with PCDDs were similar. PeCDF, PeCB, and the mixture increased serum concentrations of E(2) at 72 h after eCG injection, the day of expected ovulation; in contrast, serum P(4) and FSH were decreased at that same time point. Only the high doses of TCDD, PeCDF, and PeCB blocked LH and FSH surges at 58 h after eCG. The ovarian histology revealed that the effects of PeCDF, PeCB, and the mixture were very similar to those of PCDDs, consisting of ova in large preovulatory follicles and a lack of or reduced number of corpora lutea. Parallel dose-responses of the individual congeners (PeCDF and PeCB) and their equipotent mixture with PCDDs support the toxic equivalency (TEQ) concept for the blockage of ovulation. Thus, PCDDs, PCDFs, and PeCBs appear to block ovulation by the same or a very similar mechanism of action.

Halogenated aromatic hydrocarbon-induced suppression of the plaque-forming cell response in B6C3F1 splenocytes cultured with allogenic mouse serum: Ah receptor structure activity relationships

The immunosuppressive effects of halogenated aromatic hydrocarbons (HAHs) were investigated in B6C3F1 female mice and in mouse splenocytes cultured with allogenic mouse serum using the Mishell-Dutton model for in vitro immunization to trinitrophenyl-lipopolysaccharide (TNP-LPS). Exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 2,3,4,7,8-pentachlorodibenzofuran (PeCDF), 1,2,3,7,8-PeCDF, 1,3,6,8-tetrachlorodibenzofuran (TCDF), 3,3',4,4',5-pentachlorobiphenyl (pentaCB), or 3,3',4,4',5,5'-hexaCB resulted in a dose-dependent suppression of the splenic plaque-forming cell (PFC) response both in vivo and in vitro. The effective dose required to decrease 50% (ED50) of the response to 2,3,7,8-TCDD, 2,3,4,7,8-PeCDF, 1,2,3,7,8-PeCDF, 1,3,6,8-TCDF, 3,3',4,4',5-pentaCB, or 3,3',4,4',5,5'-hexaCB in vivo was 14.1, 5.5, 1695, 34,800, 21, and 19 nmol/kg, respectively, and in vitro was 7.0, 10.6, 149, 2325, 9.1 and 9.1 nM, respectively. There was an excellent rank order and linear correlation between the in vivo versus in vitro activities for these HAHs (r < 0.99) and the relative immunosuppressive potencies of these compounds paralleled their binding affinities for the aryl hydrocarbon (Ah) receptor. These results show that splenocytes cultured with allogenic mouse serum is an Ah-responsive in vitro assay which can be used for quantitating the immunosuppressive effects of HAHs.

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.

The effect of 1,2,3,4-tetrachlorodibenzo-p-dioxin on drug-metabolizing enzymes in the rat liver

The effects of 1,2,3,4-tetrachlorodibenzo-p-dioxin (1,2,3,4-TCDD) on drug-metabolizing enzymes were studied in male and female rats. 1,2,3,4-TCDD (25, 50, 100 and 200 mumol/kg) was administered by i.p. injection once. Among the cytochrome P-450 (P450)-mediated monooxygenase activities tested, 7-ethoxyresorufin O-deethylase (EROD) activities in both male and female rats, which are associated with CYP1A1, were remarkably induced by all doses of 1,2,3,4-TCDD. The relative induction to each control activity were from 3.0- to 24.5-fold and from 2.2- to 16.5-fold, respectively. Also, 1,2,3,4-TCDD increased other CYP1A-mediated monooxygenase activities such as 7-ethoxycoumarin O-deethylase (ECOD) and 7-methoxyresorufin O-demethylase (MROD) in male and female rats dose-dependently (1.4- to 4.3-fold). Western immunoblotting showed that the levels of CYP1A1 and CYP1A2 proteins in liver microsomes were increased by 1,2,3,4-TCDD. Although the activities of other P450-mediated monooxygenases, namely 7-pentoxyresorufin O-depentylase (PROD), 7-benzyloxyresorufin O-debenzylase (BROD), aminopyrine N-demethylase (APND) and nitrosodimethylamine N-demethylase (NDAND) in both male and female rats were induced at high doses (> or = 50 mumol/kg) of 1,2,3,4-TCDD, the relative level was low compared with those of the CYP1A-mediated monooxygenase such as EROD, ECOD or MROD. In addition to P450-mediated monooxygenase, there was significant induction in the activities of the Phase II drug-metabolizing enzymes, UDP-glucuronyltransferase (UGT) activities towards 4-nitrophenol (4-NP) and 7-hydroxycoumarin (7-HC) and glutathione S-transferase (GST) towards 1-chloro-2,4-dinitrobenzene (CDNB), 1,2-dichloro-4-nitrobenzene (DCNB) and DT-diaphorase. These results indicate that 1,2,3,4-TCDD induces both Phase I (CYP1A-mediated monooxygenase) and Phase II drug-metabolizing enzymes (UGT, GST, DT-diaphorase) in the male and female rat liver, and that the alterations of drug-metabolizing enzyme are characteristic of PCDD toxicity.

Dioxin-receptor ligands in urban air and vehicle exhaust

The ability of extracts of urban air and vehicle exhaust particulates to bind to the dioxin receptor has been determined. It was shown that such extracts do contain significant amounts of dioxin-receptor binding activity. The level of dioxin-receptor binding found in ambient air reflects its pollution level as determined by mutagenic activity. Furthermore, it was shown that the extracts of both urban air and vehicle exhaust particulates could provoke the induction of cytochrome P450IA1 in cultured rat hepatoma cells. Chemical fractionation of the extracts revealed that the majority of the dioxin-receptor binding activity from urban air and gasoline vehicle samples fractionated with the polycyclic aromatic compounds. However, unknown polycyclic aromatic compounds were responsible for the majority of the binding activity measured. In the case of diesel vehicle exhausts, the majority of the dioxin-receptor binding activity was found to be associated with nitro-polycyclic aromatic compounds. Studies with a variety of diesel fuels showed that the amount of dioxin-receptor ligands present in exhaust emissions are fuel-dependent and that substantial amounts of dioxin-receptor ligands are present in the semivolatile phase of exhaust emissions.

Inhibition of estrogen-induced progesterone receptor in MCF-7 human breast cancer cells by aryl hydrocarbon (Ah) receptor agonists

17 beta-Estradiol (E2) induces progesterone receptor (PR) binding, immunoreactive protein, nuclear PR formation and PR mRNA levels in MCF-7 human breast cancer cells. Gel mobility shift analysis of nuclear extracts from E2-treated cells also exhibited a higher intensity retarded band associated with formation of a PR complex with a consensus [32P]progesterone/glucocorticoid responsive element. In contrast, 1 nM 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) alone did not alter or decrease these same responses in MCF-7 cells; however, in cells co-treated with 1 nM TCDD plus 1 nM E2, TCDD significantly inhibited all the E2-induced responses. Scatchard analysis of PR binding demonstrated that TCDD decreased the number of E2-induced PR cellular binding sites but not the binding affinity of the PR for a radiolabeled promegestrone. In parallel studies, 3-methylcholanthrene, a prototypical polynuclear aromatic hydrocarbon, also inhibited E2-induced PR binding and immunoreactive protein. For a series of halogenated aromatics including 2,3,7,8- and 1,2,7,8-tetrachlorodibenzofuran, 1,3,7,8-TCDD and 6-methyl-1,3,8-trichlorodibenzofuran, their rank order potency for inhibiting E2-induced PR binding paralleled their rank order binding to the aryl hydrocarbon (Ah) receptor. These results support a role for the Ah receptor in mediating the antiestrogenic activity of polynuclear and halogenated aromatic hydrocarbons and illustrate cross-talk between the Ah and estrogen receptor signal transduction pathways.

Mutagenicity of tryptophan photoproducts in the Ames Salmonella assay

During the photolysis of tryptophan a large number of products is formed. In this study, aqueous solutions of tryptophan were irradiated by ultraviolet light during 5, 20 or 40 h. Each of the irradiated batches was divided into two aliquots, which were freeze-dried or extracted with chloroform. For each batch the latter extract was subsequently divided into a purified chloroform extract and a methanol extract. Aliquots of the purified chloroform extracts were fractionated and pooled, peakwise, into seven fractions. A recombined sample was also constructed. All extracts and samples were tested for mutagenicity using the standard Ames Salmonella assay. The results indicate an exposure time dependent increase in mutagenicity of the extracts, as seen with tester strain TA100 both with and without metabolic activation. The mutagenicity of the freeze-dried extracts well approximated the mutagenicity of the chloroform extracts, indicating that most mutagenicity can be extracted with chloroform. With the fractions the highest mutagenic responses were seen in the late, i.e., less lipophilic fractions. This response pattern seen in TA98 and TA100, mainly with S9 activation, was in contrast to the response of TA102 without S9, which was highest to the more lipophilic fractions. On a fraction level, no general exposure dependent increase of mutagenicity was observed. The results also show that photooxidation of tryptophan gives rise to a different spectrum of products compared to pyrolysis. Both processes result in compounds with strong biological effects. Photooxidation results in compounds with low genotoxicity and high Ah receptor affinity while pyrolysis generates compounds with high genotoxicity and low or no Ah receptor affinity.

The toxicokinetics and metabolism of polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs) and their relevance for toxicity

This article reviews the present state of the art regarding the toxicokinetics and metabolism of polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs). The absorption, body distribution, and metabolism can vary greatly between species and also may depend on the congener and dose. In biota, the 2,3,7,8-substituted PCDDs and PCDFs are almost exclusively retained in all tissue types, preferably liver and fat. This selective tissue retention and bioaccumulation are caused by a reduced rate of biotransformation and subsequent elimination of congeners with chlorine substitution at the 2,3,7, and 8 positions. 2,3,7,8-Substituted PCDDs and PCDFs also have the greatest toxic and biological activity and affinity for the cytosolic arylhydrocarbon (Ah)-receptor protein. The parent compound is the causal agent for Ah-receptor-mediated toxic and biological effects, with metabolism and subsequent elimination of 2,3,7,8- substituted congeners representing a detoxification process. Congener-specific affinity of PCDDs and PCDFs for the Ah-receptor, the genetic events following receptor binding, and toxicokinetics are factors that contribute to the relative in vivo potency of an individual PCDD or PCDF in a given species. Limited human data indicate that marked species differences exist in the toxicokinetics of these compounds. Thus, human risk assessment for PCDDs and PCDFs needs to consider species-, congener-, and dose-specific toxicokinetic data. In addition, exposure to complex mixtures, including PCBs, has the potential to alter the toxicokinetics of individual compounds. These alterations in toxicokinetics may be involved in some of the nonadditive toxic or biological effects that are observed after exposure to mixtures of PCDDs or PCDFs with PCBs.

Relative tumour promoting activity of three polychlorinated biphenyls in rat liver

The relative tumour promoting activity of three structurally and toxicologically diverse polychlorinated biphenyls (3,4,5,3',4'-penta- 2,3,4,3',4'-penta- and 2,4,5,2',4',5'-hexachlorobiphenyl) was measured in an initiation/promotion assay in nitrosodiethylamine-initiated female Sprague-Dawley rats. The congeners under study were administered by once-weekly subcutaneous injections for 20 weeks. Evaluation of the development of gamma-glutamyl transpeptidase (GGT)- and glutation transferase P (GST-P)-positive hepatic foci showed that all congeners promoted altered hepatic foci, although 3,4,5,3',4'-pentachlorobiphenyl was far more potent. The volume fraction of the liver occupied by GGT-positive tissue in the 3,4,5,3',4'-pentachlorobiphenyl-treated animals (100 micrograms/kg per week) was 23%, while the volume fractions of altered liver tissue in the rats treated with 2,3,4,3',4'-pentachlorobiphenyl (5000 micrograms/kg per week) and 2,4,5,2',4',5'-hexaCB (20,000 micrograms/kg per week) were 1.2 and 2.3, respectively. The enhancement of GGT- and GST-P-positive foci was accompanied by an increased incidence of histological changes in the livers.

Dietary 2,3,7,8-tetrachlorodibenzofuran in rainbow trout: accumulation, disposition, and hepatic mixed-function oxidase enzyme induction

Juvenile rainbow trout (Oncorhynchus mykiss) were exposed to dietary 2,3,7,8-[3H]tetrachlorodibenzofuran (TCDF) (0.36 to 42.8 ng g-1) and accumulation, tissue distribution, biotransformation, and hepatic monooxygenase enzyme (MO) induction were studied. The assimilation efficiency of TCDF ranged from 49 to 62% in 30-day exposures and was independent of the TCDF level in the diet. Depuration half-lives (whole body) of TCDF following 30-day exposure ranged from 40 to 77 days and were significantly more rapid in fish exposed to 42.8 ng g-1. Liver somatic index (LSI) and rate of increase in liver weight were elevated in fish exposed to 42.8 ng g-1 TCDF compared to controls. Exposure to 9.2 ng g-1 TCDF in the diet for 140 days also resulted in higher LSI values, as well as increased mortality (16%), but had no significant effects on growth. [3H]TCDF was found mainly in the carcass (63-74%) and GI tract (18-31%), with lesser amounts in liver (0.6-2.3%) during the 140-day exposure, primarily (> 98%) in the form of the parent compound. Radioactivity in bile was found mainly as a single polar transformation product by reverse-phase HPLC. Glucuronidase hydrolysis yielded a product with the retention time expected of hydroxylated TCDF, suggesting the presence of a glucuronide conjugate. MO enzyme induction measured by ethoxyresorufin-O-deethylase (EROD) activity in liver (postmitochondrial supernatant) was 137.5 and 15 times higher than that in control fish after 30 days dietary exposure to 42.8 and 9.2 ng g-1, respectively. EROD activities were correlated with TCDF concentrations in liver (R2 = 0.59, N = 45).

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.

Polychlorinated biphenyls in the environment

This review surveys the problems arising from the release of PCBs into the environment from the point of view of the analytical chemist. These problems are very complex and interdependent and so it is essential to recognize their mutual links rather than to separate one problem from another (sources of contamination, fate in the environment, toxic properties and particular capabilities, limitations and purposes of analytical methods). Prominent attention should be paid in the future to congener-specific analyses of "toxic" congeners using high-resolution gas chromatography and to toxicity-assessing biological methods.

Effects of organochlorine chemicals on the reproductive outcome of humans who consumed contaminated Great Lakes fish: an epidemiologic consideration

Three sets of studies of the impacts of human exposure to PCB contaminated fish from the Great Lakes basin--the Michigan Sports Fisherman Cohort, the Michigan Maternal/Infant Cohort, and the Wisconsin Maternal/Infant Cohort-were evaluated using the epidemiologic criteria of Susser (1986). The studies were compared against each other, and against comparable data from other geographic locales. A total of seven major categories of exposure sequelae were evaluated. These ranged from the effects of primary exposure to contaminants upon maternal health status, to effects from secondary intrauterine fetal exposure, including alterations in birth size and gestational age, changes in neonatal health status, and effects persisting into early infancy. Results of the evaluations suggest that the causal hypothesis may be strongly affirmed for the relationship between PCB exposure and alterations in both neonatal health status and in health status in early infancy may be affirmed with reasonable certainty. While the evidence from the Michigan Maternal/Infant Cohort related to maternal exposure to PCB and infant size at birth and gestational age affirms the causal hypothesis, studies from other geographic locales tend only to be supportive. Analytic differences are likely responsible for this variation, but epidemiologically, the composite rating must be regarded as indeterminate. The relationship with observed alterations in maternal health status, composite activity ranking, and McCarthy Memory Scale deficits were also classified as indeterminate. No evidences of obvious negation were seen, although one portion of a study was disqualified because of incoherence.

The Ah receptor and the mechanism of dioxin toxicity

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In situ and in vitro photoaffinity labeling of the nuclear aryl hydrocarbon receptor from transformed rodent and human cell lines

The photoaffinity labeling of the nuclear aryl hydrocarbon (Ah) receptor from mouse Hepa 1c1c7, rat hepatoma H-4-II E, and human liver Hep G2 cells was investigated using two high affinity ligands, namely 2,3,7,8-[3H]tetrachlorodibenzo-p-dioxin (TCDD) and 7-[125I]iodo-2,3,-dibenzo-p-dioxin ([125I]DBDD). Irradiation of nuclear [3H]TCDD-Ah receptor complexes from the three cell lines for 5 min gave 47, 38, and 62% yields of trichloroacetic acid-precipitable photoadducts from the Hepa 1c1c7, H-4-II E, and Hep G2 cell lines, respectively; denaturing sodium dodecyl sulfate-polyacrylamide gel electrophoresis separation followed by autoradiography gave one major Ah receptor photoadduct for each cell line with apparent molecular masses at 97, 100, and 110 kDa, respectively. [125I]DBDD could also be used as a photoaffinity label for the nuclear Ah receptor from the three cell lines; although the maximum net yield of photoaffinity labeled nuclear Ah receptor from the rodent nuclear Ah receptor preparations was relatively low (0.5-2.5%), a greater than 15% yield of photoadduct was obtained from the human Hep G2 cells. Both [3H]TCDD and [125I]DBDD were utilized to photoaffinity label the nuclear Ah receptor in Hepa 1c1c7 cells in suspension and the net yield of photoadducts with these ligands was 94.6 and 3.0%, respectively. The cytosolic Ah receptor from the three cell lines was photolabeled with [125I]DBDD and the net yield of photoadducts varied from 3.3 to 14.7%. The functional activity of the photoaffinity-labeled nuclear TCDD-Ah receptor complexes from the cell lines was also determined by comparing relative binding affinities of the photolyzed and unphotolyzed complexes with a synthetic dioxin-responsive element (DRE) using a gel retardation assay. The photolyzed and unphotolyzed complexes from the three cell lines all bound with the DRE in the gel shift assay; however, the gel mobilities of the rodent and human nuclear receptor-DRE complexes were different. Quantitative analysis of the DRE binding showed that there were no significant differences between the photolyzed and unphotolyzed nuclear receptor complexes from the rodent cells, whereas there was a significant 27% decrease in the DRE binding of the photolyzed versus the unphotolyzed nuclear receptor complex from the human Hep G2 cells. These studies demonstrate the utility of [3H]TCDD and [125I]DBDD as photoaffinity labels for the Ah receptor and illustrate the structural and photochemical differences between the rodent and the human nuclear Ah receptor complexes.

2,3,7,8-Tetrachlorodibenzo-p-dioxin inhibition of 17 beta-estradiol-induced increases in rat uterine epidermal growth factor receptor binding activity and gene expression

Treatment of immature female Sprague-Dawley rats with 17 beta-estradiol (5 micrograms/animal) resulted in an increase in uterine epidermal growth factor (EGF) receptor binding activity. Moreover, in a separate study it was also shown that 17 beta-estradiol increased steady-state levels of rat uterine EGF receptor mRNA as determined by Northern analysis. In contrast, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) caused a dose-response decrease in constitutive rat uterine EGF receptor binding activity and this was paralleled by a decrease in steady-state levels of uterine EGF receptor mRNA. Cotreatment of the animals with both TCDD (16 nmol/kg) and 17 beta-estradiol (5 micrograms/rat) gave results which showed that TCDD significantly inhibited the estrogen-induced increases in rat uterine EGF receptor binding activity and EGF receptor mRNA levels. These results further extend the range of antiestrogenic properties of TCDD and suggest that the inhibition of growth factor expression may play a role in the growth-inhibiting properties of TCDD in estrogen-responsive tissues or cells.

Structure-dependent induction of aryl hydrocarbon hydroxylase activity in C57BL/6 mice by 2,3,7,8-tetrachlorodibenzo-p-dioxin and related congeners: mechanistic studies

The time- and dose-dependent induction of murine hepatic microsomal aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) activities by five polychlorinated dibenzo-p-dioxin and dibenzofuran congeners showed that the order of induction potency was 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) greater than 2,3,7,8-tetrachlorodibenzofuran (TCDF) greater than 1,2,3,7,8-pentachlorodibenzo-p-dioxin (PCDD) greater than 1,2,3,7,8-pentachlorodibenzofuran (PCDF) greater than 2,3,7-trichlorodibenzo-p-dioxin (TrCDD). These structure-induction relationships were comparable to the structure-toxicity and competitive structure-receptor binding relationships previously reported for these compounds. However, using the corresponding radiolabeled congeners, the direct binding Kd values for dissociation of the cytosolic receptor-ligand complexes were 9.52, 7.96, 1.27, 3.10, and 8.31 nM for the 2,3,7,8-TCDD, 2,3,7,8-TCDF, 2,3,7-TrCDD, 1,2,3,7,8-PCDD, and 1,2,3,7,8-PCDF congeners and these data were clearly not structure dependent (i.e., similar to the structure-activity relationships). Some of the molecular properties for several radioligand-receptor complexes were similar; for example, the sedimentation coefficients for the cytosolic and nuclear receptor complexes varied from 8.8-10.4 S and 5.98-7.0 S, respectively, and the nuclear receptor complexes for all the radioligands eluted from a DNA-Sepharose column at salt concentrations of 0.27-0.29 M. Treatment of the mice with a maximum inducing dose of 2,3,7,8-[3H]TCDD resulted in a time-dependent formation of the nuclear receptor complex which was maximized between 16-24 hr and subsequently decreased up to 72 hr after initial exposure. In parallel studies, the nuclear receptor complex levels were determined 16 hr after treatment of the mice with different doses (2.25, 4.5, and 45 micrograms/kg) of all five radioligands. The results showed that at submaximal induction of the monooxygenase enzyme activities there was a linear correlation between the induced AHH or EROD activities (after 32 hr) and the corresponding nuclear receptor complex levels. It was also apparent from the data that the relative levels of nuclear receptor complex were structure dependent and this suggests that the transformation or activation of cytosolic receptor complexes may be a ligand structure-dependent process which correlates with the observed structure-activity relationships for 2,3,7,8-TCDD and related compounds.

Immunosuppressive and monooxygenase induction activities of polychlorinated diphenyl ether congeners in C57BL/6N mice: quantitative structure-activity relationships

The dose-response effects of several polychlorinated diphenyl ether (polyCDE) congeners on the inhibition of the splenic plaque-forming cell (PFC) response to sheep red blood cell antigen and the induction of hepatic microsomal aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) activities were determined in male C57BL/6 mice. The immunotoxic potencies for the polyCDE congeners (ED50 values for the suppression of PFCs/spleen and PFCs/10(6) cells) followed the order 2,3,3',4,4',5-hexaCDE (0.5 and 2.2 mumols/kg) greater than 3,3',4,4',5-pentaCDE (8.8 and 5.1 mumols/kg) greater than 2,3',4,4',5-pentaCDE (21.8 and 14.2 mumols/kg) greater than 3,3',4,4'-tetraCDE (50.6 and 28.7 mumols/kg) greater than 2,2',4,4',5,5'-hexaCDE (81.2 and 56.5 mumols/kg) greater than 2,2',4,5,5'-pentaCDE (258 and 228 mumols/kg) greater than 2,2',4,4',5,6'-hexaCDE (greater than 400 mumols/kg for both responses). The potencies of the polyCDE congeners as inducers of hepatic microsomal AHH and EROD activities were similar to their immunotoxicities and only one compound, namely, 2,3',4,4',5,5'-hexaCDE, did not cause dose-response immunosuppressive effects in the mice. The structure-activity relationships for the polyCDEs exhibited both differences and similarities. For example, the coplanar 3,3',4,4'-tetraCDE and 3,3',4,4',5-pentaCDE congeners were less immunotoxic than their monoortho 2,3',4,4',5-pentaCDE and 2,3,3',4,4',5-hexaCDE analogs, respectively, and similar results were also observed for their enzyme induction potencies. For the corresponding polychlorinated biphenyls (PCB) congeners the coplanar compounds were significantly more active than their monoortho analogs. In addition, two diortho-substituted compounds, namely, 2,2',4,5,5'-pentaCDE and 2,2',4,4',5,5'-hexaCDE, were also immunotoxic at a dose of 400 mumols/kg whereas, their PCB analogs were inactive. These studies clearly demonstrate that for the polyCDE congeners, increasing ortho-chloro substitution is less effective in reducing the activity of these congeners compared to the well-recognized ortho effects reported for the PCBs. The differences in the structure-activity relationships between polyCDEs and PCBs are related to the ether bridge in the polyCDEs in which the resultant increased bond length between the two phenyl rings thereby diminishes the effects of ortho substituents on the biochemical and toxic potencies of these compounds.

Quantitative risk assessment of polychlorodibenzofurans (PCDFs) released in PCB fires: use of high-resolution gas chromatography

The toxicity of polychlorodibenzofurans (PCDFs), produced during incineration and in accidental fires involving polychlorinated biphenyls (PCBs), is generally assessed in terms of total concentration or more recently in terms of the group concentrations of the tetra-, penta- and hexachloro-isomers. This approach fails to account for the great differences in potency of the relatively few toxic congeners and isomers present in the sample. A quantitative risk assessment of PCDF mixtures must not only be based on the concentrations of the toxic components but also account for the relative potency of each congener in a form which permits summation of the toxicities of the individual contributors. This paper outlines a method by which the concentration of each of the toxic components, determined by high-resolution congener-specific gas chromatographic analysis, may be converted to equivalent toxic concentrations of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Summation of the resulting values permits the overall toxicity of the sample to be expressed in terms of an equivalent toxic weight of TCDD per unit weight of sample (ng TCDD/g) in the case of fly ash or an equivalent toxic weight of TCDD per unit area (ng TCDD/m2) for soot deposit.

Polychlorinated biphenyls (PCBs), dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), and related compounds: environmental and mechanistic considerations which support the development of toxic equivalency factors (TEFs)

Halogenated aromatic compounds, typified by the polychlorinated dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), biphenyls (PCBs), and diphenylethers (PCDEs), are industrial compounds or byproducts which have been widely identified in the environment and in chemical-waste dumpsites. Halogenated aromatics are invariably present in diverse analytes as highly complex mixtures of isomers and congeners and this complicates the hazard and risk assessment of these compounds. Several studies have confirmed the common receptor-mediated mechanism of action of toxic halogenated aromatics and this has resulted in the development of structure-activity relationships for this class of chemicals. The most toxic halogenated aromatic is 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and based on in vivo and in vitro studies the relative toxicities of individual halogenated aromatics have been determined relative to TCDD (i.e., toxic equivalents). The derived toxic equivalents can be used for hazard and risk assessment of halogenated aromatic mixtures; moreover, for more complex mixtures containing congeners for which no standards are available (e.g., bromo/chloro mixtures), several in vitro or in vivo assays can be utilized for hazard or risk assessment.

6-substituted-1,3,8-trichlorodibenzofurans as 2,3,7,8-tetrachlorodibenzo-p-dioxin antagonists in the rat: structure activity relationships

The activities of several 6-substituted-1,3,8-trichlorodibenzofurans (CDFs) as partial antagonists of the induction of hepatic microsomal aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) activities in the rat by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) were structure-dependent. Treatment of the rats with TCDD (16 nmol/kg), the 6-substituted-1,3,8-triCDFs (50 mumol/kg) and TCDD plus the 6-substituted-1,3,8-triCDFs showed that most of the substituted congeners were either inactive (6-methyl, ethyl, propyl, i-propyl, t-butyl) or weak (6-cyclohexyl, nitro) inducers of AHH and EROD activities, whereas TCDD caused an 8.1- and 58-fold induction of these enzyme activities respectively. In the co-administration studies, the 6-methyl, propyl, ethyl, isopropyl and t-butyl analogs partially antagonized the induction of the monooxygenase enzyme activities by TCDD, whereas, the 6-cyclohexyl and 6-nitro-1,3,8-triCDFs exhibited minimal activity as TCDD antagonists. The Ah receptor binding affinities of the 6-substituted compounds were determined in a series of in vitro competitive binding studies using [3H]TCDD as the radioligand. Analysis of the data by Scatchard and Dixon plots showed that the avidities for the Ah receptor by the 6-substituted-1,3,8-triCDFs followed the order 6-methyl greater than 6-t-butyl greater than 6-i-propyl greater than 6-propyl approximately 6-ethyl greater than 6-cyclohexyl greater than 6-nitro-1,3,8-triCDF. In addition there was a good correlation between the in vitro binding avidities and Ki values for these compounds and their in vivo activity as partial antagonists of the induction of AHH and EROD activities by TCDD. The results suggested that the 6-substituted-1,3,8-triCDFs competitively displayed TCDD from the Ah receptor and this interaction may play a role in the mechanism of action of this class of TCDD antagonists.

Biological activity of 2,4,8-trichlorodibenzofuran: promotion of rat liver foci and induction of cytochrome P-450-dependent monooxygenases

The biological activity of 2,4,8-trichlorodibenzofuran (2,4,8-TCDF) was tested using 2 endpoints: (a) the promotion of enzyme-altered, preneoplastic foci initiated by diethylnitrosamine (DEN) in livers of weanling female Sprague-Dawley rats; and (b) the induction of aryl hydrocarbon (benzo[a]pyrene) hydroxylase (AHH), a marker for cytochrome P-4501 activity, in livers of adult female Sprague-Dawley rats and in H4IIEC3 rat hepatoma cells. When animals were treated with 200 or 500 mg/kg 2,4,8-TCDF 5 X weekly over 10 weeks after a single application of 10 mg/kg DNA, the higher dose of 2,4,8-TCDF had a promoting effect on the appearance of preneoplastic foci. Thus number and total area of foci deficient in adenosine-5'-triphosphatase were significantly increased by a factor of 1.6. 2,4,8-TCDF induced AHH-activities in 9000 X g supernatants of liver 2-3-fold, when rats were treated with 100-1000 mg/kg/day for 5 days and monooxygenase activities determined after another 3 days. The amounts of 2,4,8-TCDF required for inducing AHH activity in H4IIEC3 cells were 7 orders of magnitude higher than those of 2,3,7,8-tetrachlorodibenzo-p-dioxin (2,3,7,8-TCDD). the results indicate that the 2,4,8-TCDF has a biological activity which is extremely low compared to that of 2,3,7,8-TCDD.

Development and validation of in vitro induction assays for toxic halogenated aromatic mixtures: a review

Halogenated aromatic industrial compounds, typified by the polychlorinated dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs) and biphenyls (PCBs) have been identified as residues in almost every component of the global ecosystem. Risk assessment of the complex mixtures of halogenated aromatics found in environmental samples is complicated by analytical problems and the lack of toxicological information on individual compounds and mixtures. Research in our laboratory has focused on the development and vadidation of the in vitro aryl hydrocarbon hydroxylase (AHH) induction assay in rat hepatoma H-4-II E cells in culture for quantitating individual toxic halogenated aryl hydrocarbons and their mixtures. For several PCB, PCDD, PCDF congeners, their mixed bromo/chloro analogs and reconstituted mixtures there was an excellent linear correlation between their -log ED50 values for AHH induction in rat hepatoma cells and their -log ED50 values for in vivo hepatic microsomal AHH induction, inhibition of body weight gain and thymic atrophy in the rat. It has also been shown for selected compounds that there was a good correlation between their in vitro AHH induction potencies and their effects in guinea pigs (AHH induction, inhibition of body weight gain) and mice (immunotoxicity). This assay system has been utilized to quantitative the "2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) equivalents" present in extracts from diverse sources including fly ash from a municipal incinerator and pyrolyzed brominated flame retardants which contain a complex mixture of halogenated dibenzo-p-dioxins and dibenzofurans.

Induction of cytochrome P450-dependent monooxygenase activities in rat hepatoma H-4-IIE cells in culture by 2,3,7,8-tetrachlorodibenzo-p-dioxin and related compounds: mechanistic studies using radiolabeled congeners

Treatment of rat hepatoma H-4-IIE cells in culture with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 2,3,7,8-tetrachlorodibenzofuran (TCDF), 1,2,3,7,8-pentachlorodibenzo-p-dioxin (PeCDD), 1,2,3,7,8-pentachlorodibenzofuran (PeCDF), 1,2,7,8-TCDF, and 2,3,7-trichlorodibenzo-p-dioxin (TrCDD) resulted in the structure-dependent induction of aryl hydrocarbon hydroxylase and ethoxyresorufin O-deethylase activities. The induction potencies followed the order 2,3,7,8-TCDD greater than 2,3,7,8-TCDF greater than 1,2,3,7,8-PeCDD approximately 1,2,3,7,8-PeCDF greater than 1,2,7,8-TCDF greater than 2,3,7-TrCDD and were comparable to structure-toxicity relationships which have previously been reported. In contrast, many of the properties of these compounds were structure-independent. For example, using tritiated congeners of high specific activity (greater than 30 Ci/mmol) the sedimentation coefficients (S) for the nuclear and cytosolic aryl hydrocarbon (Ah) receptor complexes were 5-6 and 9-10 S, respectively, for all the radioligands. Moreover, examination of the processing of nuclear Ah receptor complexes for the radiolabeled congeners showed that after 6 h, the rates of nuclear processing were very low and varied between 0.006 and 0.0385 fmol degraded/mg protein/mg total DNA. These results were consistent with the reported stability and persistence of the nuclear Ah receptor complexes and in addition, there were no apparent structure-dependent differences in the processing rates. Inspection of the nuclear receptor levels and the corresponding induced enzyme activities for the congeners showed that there was a linear correlation between average nuclear receptor complex levels (18-42 h) and induced enzyme activities (32-42 h) for all six radioligands; these data indicated that the rates of cytochrome P450-dependent gene expression correlated with the levels of nuclear Ah receptor complex. In contrast, the accumulation of occupied nuclear receptor complexes in rat hepatoma H-4-IIE cells was structure-dependent and appeared to be one of the factors which governed the observed structure-induction and the previously reported structure-toxicity relationships for 2,3,7,8-TCDD and related halogenated aryl hydrocarbons.

6-Methyl-1,3,8-trichlorodibenzofuran (MCDF) as a 2,3,7,8-tetrachlorodibenzo-p-dioxin antagonist in C57BL/6 mice

6-Methyl-1,3,8-trichlorodibenzofuran (MCDF), 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and TCDD plus MCDF were administered to C57BL/6 mice and their effects on several aryl hydrocarbon (Ah) receptor-mediated responses including hepatic microsomal aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) induction, immunotoxicity and teratogenicity were determined. MCDF did not induce hepatic microsomal AHH and EROD at doses up to 500 mumol/kg, however, co-administration of MCDF (50 mumol/kg) with a dose of TCDD which elicited a submaximal induction response (i.e. ED80-100, 15 nmol/kg) resulted in some small but significant inhibition of the induction of hepatic microsomal AHH and EROD (14 and 17%, respectively) compared to that observed with TCDD alone. Co-administration of TCDD and other doses of MCDF (10, 100, 200 or 500 mumol/kg) did not effect the induction response. These results were in contrast to the effectiveness of MCDF as an antagonist of the induction of AHH and EROD by TCDD in the rat (up to 50% inhibition of monooxygenase induction). Administration of MCDF (4, 20 and 40 mumol/kg) to C57BL/6 mice caused some inhibition of the splenic plaque-forming cell response to sheep erythrocytes only at the highest dose (26% decrease); the interaction of MCDF (4, 20 and 40 mumol/kg) and an immunotoxic dose of TCDD (3.7 nmol/kg) resulted in significant protection from the immunotoxic effects of TCDD at the 2 higher dose levels of MCDF. Similarly, MCDF (400 mumol/kg) did not cause cleft palate in mice but at this dose level MCDF afforded some protection from TCDD (20 micrograms/kg)-mediated cleft palate in mice. However, studies utilizing [3H]TCDD suggested that the protective effects may be due to modulation of TCDD reaching the palate in the co-treated animals (MCDF plus TCDD). Although both MCDF and Aroclor 1254 were both weak Ah receptor agonists in C57BL/6 mice, the former compound was much less effective as a TCDD antagonist. The observed species-specific effects for these 2 TCDD antagonists may be related species-dependent differences in receptor structure and receptor-ligand (i.e. agonist or antagonist) interactions.

Kinetic models for association of 2,3,7,8-tetrachlorodibenzo-p-dioxin with the Ah receptor

Saturation binding studies of the interaction between 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and the Ah receptor obtained from the hepatic cytosol of Wistar rats have been carried out. The conventional Scatchard analysis for determination of the equilibrium constant for ligand-receptor binding has been shown to be inappropriate due to thermal inactivation of the unoccupied receptor. Simulation models of the receptor-ligand binding kinetics which take into account receptor degradation have been developed and the results are consistent with two alternative kinetic models. In Model 1, reversible 2,3,7,8-TCDD-receptor binding occurs in parallel with inactivation of the unbound receptor; analysis of the observed data using this model suggests that the previously determined equilibrium constants (Kass) for association of the ligand with the receptor are orders of magnitude too low and the total initial receptor concentrations are somewhat underestimated. In Model 2, the unbound receptor is converted unimolecularly to an activated state which then undergoes competitive degradation or entrapment by ligand. Experiments have been carried out over the temperature range 4-37 degrees C, enabling activation parameters to be obtained. According to Scheme 1, the activation enthalpies for association of receptor with ligand and for thermal inactivation of the unoccupied receptor are high, and numerically almost identical (delta H++ ca 125 kJ mol-1). These reactions are strongly entropically driven and this is consistent with association being accompanied by a conformational change in the receptor protein, and the previously postulated binding of the ligand to a hydrophobic pocket. According to Scheme 2, there is only one enthalpy of activation because both inactivation and entrapment by 2,3,7,8-TCDD are fast processes which follow the same slow activation step. On the basis of this latter model, a 10(-9) M concentration of 2,3,7,8-TCDD is sufficient to trap roughly two-thirds of the activated receptors.

Applications of the in vitro aryl hydrocarbon hydroxylase induction assay for determining "2,3,7,8-tetrachlorodibenzo-p-dioxin equivalents": pyrolyzed brominated flame retardants

The pyrolysis of brominated flame retardants FR 300 BA (decabromobiphenyl) ether, FireMaster BP-6 (polybrominated biphenyls), Bromkal 70-5-DE (primarily pentabromodiphenylether), Bromkal 70-DE (primarily penta and tetrabromodiphenylether) and Bromkal G1 (pentabromodiphenylether) resulted in the formation of relatively high levels of polybrominated dibenzofurans (PBDFs) and dibenzo-p-dioxins (PBDDs as determined by gas chromatography-mass spectrometric analysis. The dose response EC50 values for the induction of aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) by the flame retardant pyrolysates was determined in rat hepatoma H-4-II E cells and compared to the relative induction activities of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and the concentrations of "2,3,7,8-TCDD equivalents" were calculated. The range of "2,3,7,8-TCDD equivalents" levels (micrograms/g or ppm) derived from values obtained from the AHH and EROD bioassays for each of the pyrolyzed flame retardant samples was: 174-194, 480-1400, 2140-4680, 6740-8780 and 3920-5260 ppm for FR 300 BA, FireMaster BP-6, Bromkal 70 DE, Bromkal 70-5 DE and Bromkal G1, respectively. The in vivo dose-response effects of 2 pyrolyzed flame retardants were determined in immature male Wistar rats and compared to the dose-response activities of 2,3,7,8-TCDD. The in vivo responses which were measured included hepatic microsomal AHH and EROD induction, body weight loss and thymic atrophy. For the pyrolyzed FireMaster BP-6 and Bromkal 70-5 DE samples, the range of calculated in vivo "2,3,7,8-TCDD equivalents" (ppm in sample) for the 4 in vivo bioassays was 520-1780 ppm and 3860-8960 ppm, respectively. The excellent overlap between the in vivo and in vitro 2,3,7,8-TCDD equivalents for the 2 flame retardant pyrolysate extracts supports the utility of the in vitro induction bioassay for quantitatively determining "2,3,7,8-TCDD equivalents" for mixtures containing toxic halogenated aryl hydrocarbons.

Immunosuppressive activities of polychlorinated dibenzofuran congeners: quantitative structure-activity relationships and interactive effects

The dose-response immunosuppressive effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 2,3,4,7,8- and 1,2,3,7,9-pentachlorodibenzofuran (PeCDF), 2,3,7,8- and 1,3,6,8-tetrachlorodibenzofuran (TCDF) on the splenic plaque-forming cell (PFC) response to sheep red blood cells were determined in C57BL/6 mice. The ED50 values for immunosuppression were 2.4, 3.0, 14.0, 710, and 35,700 nmol/kg for 2,3,7,8-TCDD, 2,3,4,7,8-PeCDF, 2,3,7,8-TCDF, 1,2,3,7,9-PeCDF, and 1,3,6,8-TCDF, respectively, and the results confirmed that lateral chlorine substitutions were important structural determinants for the toxicity of the polychlorinated dibenzofuran congeners. Interaction of both 2,3,7,8-TCDD and 2,3,4,7,8-PeCDF with subimmunotoxic doses of 1,3,6,8-TCDF resulted in significant antagonism of the immunotoxic effects of both 2,3,7,8-TCDD and 2,3,4,7,8-PeCDF. Previous studies have also demonstrated that 1,3,6,8-TCDF also antagonizes the induction of aryl hydrocarbon hydroxylase by 2,3,7,8-TCDD and analysis of competitive receptor binding studies suggests that 1,3,6,8-TCDF acts as a competitive partial antagonist of the action of 2,3,7,8-TCDD. The antagonism of 2,3,7,8-TCDD immunosuppression was found to be dependent on the timing of administration of 1,3,6,8-TCDF. Using a protocol in which 2,3,7,8-TCDD is administered 5 days prior to the antigen and 9 days prior to assessing the splenic PFC response, it was possible to partially antagonize the immunosuppressive effects of 2,3,7,8-TCDD by administering the antagonist up to 5 days after the initial dose of the toxin. Administration of 1,3,6,8-TCDF after the antigen does not afford any significant protection from the effects of 2,3,7,8-TCDD and these results are consistent with the hypothesis that 2,3,7,8-TCDD modulates some early event in B-cell differentiation. However, these results do not exclude a role for 2,3,7,8-TCDD in modulating other cellular processes associated with the PFC response.

Biologic and toxic effects of polychlorinated dibenzo-p-dioxin and dibenzofuran congeners in the guinea pig. Quantitative structure-activity relationships

The dose-response effects of 2,3,7,8-tetrachorodibenzo-p-dioxin, 1,3,7,8-tetrachlorodibenzo-p-dioxin, 1,2,4,7,8-pentachlorodibenzo-p-dioxin, 2,3,4,7,8-, 1,2,3,7,9-, and 2,3,4,7,9-pentachlorodibenzofuran on body weight loss and hepatic microsomal aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) induction were determined in the immature male guinea pig. The ED50 values for each compound were measured for the three in vivo responses. The quantitative structure-activity relationships clearly illustrated that the most toxic congeners were substituted in the lateral 2, 3, 7 and 8 positions, and removal of a lateral chlorine group substantially reduced the potency of the resulting compound. The most toxic congener in this series was 2,3,7,8-tetrachlorodibenzo-p-dioxin in which the in vivo ED50 values for AHH and EROD induction and body weight loss were 2.8 X 10(-10), 9.3 X 10(-11) and 5.6 X 10(-9) mol/kg. The structure-activity relationships observed in this study were comparable to those previously reported in rats and rat hepatoma H-4-II E cells in culture. Moreover, there was an excellent linear correlation between in vivo -log ED50 values for body weight loss, AHH and EROD induction and the corresponding in vitro -log EC50 data for AHH induction in rat hepatoma cells [S. Safe, Chemosphere 16, 791 (1987)].

Synthesis and aryl hydrocarbon receptor binding properties of radiolabeled polychlorinated dibenzofuran congeners

Microchlorination of 1,4,9[3H]dibenzofuran gave several polychlorinated dibenzofuran (PCDF) products and 2,3,7,8-[3H]tetrachlorodibenzofuran (TCDF), 1,2,3,7,8-[3H]pentachlorodibenzofuran (PeCDF), and 1,2,3,6,7,8-/1,2,3,4,7,8-hexachlorodibenzofuran (HCDF) of high specific activity (57, 34, and 32.5 Ci/mmol, respectively) were purified by preparative high-pressure liquid chromatography. These compounds were investigated as radioligands for the rat liver cytosolic aryl hydrocarbon (Ah) receptor protein. Like 2,3,7,8-[3H]tetrachlorodibenzo-p-dioxin (TCDD), the radiolabeled PCDF congeners exhibited saturable binding with the receptor protein and sucrose density gradient analysis of the radiolabeled ligand-receptor complexes gave specific binding peaks with comparable sedimentation profiles. The rank order of radioligand binding affinities (Kd values) was 2,3,7,8-TCDD greater than 2,3,7,8-TCDF greater than 1,2,3,6,7,8-HCDF greater than 1,2,3,7,8-PeCDF and the maximum difference in Kd values for the four radioligands was less than 13-fold (0.44-5.9 nM). The interactions of the PCDF radioligands with the cytosolic receptor all exhibited saturable binding curves and linear Scatchard plots and the slopes of their Hill plots were in the range 1.0-1.1, thus indicating that cooperativity was not a factor in these binding interactions. The relative stabilities and dissociation kinetics of the radioligand-receptor complexes were highly dependent on the structure of the radioligand. The dissociation curves of the 2,3,7,8-[3H]TCDD and PCDF receptor complexes were biphasic and this suggests that there may be a temporal shift in ligand binding affinities. However, the rates of dissociation did not correlate with the rank order of ligand binding affinities. The stabilities of the radioligand-receptor complexes were also dependent on the structures of the radioligands; for example, the 2,3,7,8-[3H]TCDD-receptor complex degraded more rapidly than the PCDF-receptor complex and these relative stabilities were clearly not related to the Kd values or the relative in vivo or in vitro biologic potencies of these halogenated aryl hydrocarbons.