G. Mason

Polychlorinated dibenzofurans (PCDFs): Effects of structure on binding to the 2,3,7,8-TCDD cytosolic receptor protein, AHH induction and toxicity

The effects of structure on the activity of 26 polychlorinated dibenzofurans (PCDFs) as competitive ligands for the 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) rat hepatic cytosolic receptor protein were determined in a dose-response fashion. The ED50 values for these compounds varied 100 000-fold and the most active PCDFs were substituted in the 2,3,7 and 8 lateral positions; the ED50 for the most active PCDF, 2,3,4,7,8-pentachlorodibenzofuran was 1.5 X 10(-8) M which was only slightly less active than 2,3,7,8-TCDD (1.0 X 10(-8) M). A comparison of the binding affinities of several isomer pairs also indicated the relative importance of chlorine substitution at C-4 (or C-6) compared to C-1 (or C-9). Moreover, for some isomers it is apparent that C-4 (or C-6) substituents are more active than lateral substituents for facilitating ligand binding to the receptor protein. This is illustrated by the relative binding potencies of the following isomer pairs: 1,2,4,6,7-/1,2,4,7,8 = 19.2; 2,6,7-/2,3,8- = 2.2; 1,3,6-/1,3,8- = 19. Most of the PCDF structure-activity effects noted above were also observed for the induction of aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) in rat hepatoma H-4-II-E cells in culture. The most active compounds were also substituted in the lateral 2,3,7 and 8 positions and a comparison of C-4 (or C-6) vs. C-1 (or C-9) substituted PCDFs confirmed the higher induction potencies for most of the former group of compounds. The in vitro quantitative structure-activity data were complemented by in vivo studies which determined the relative activities of selected PCDFs as inducers of hepatic microsomal cytochrome P-448 dependent monooxygenases and their effects on body weight gain and thymus weights in immature male Wistar rats. The results indicated that for 2 series of isomers, namely the 2,3,4,7,8-, 1,2,4,7,8- and 1,2,4,7,9-pentachlorodibenzofurans and the 2,3,7,8-, 2,3,4,8- and 1,2,4,8-tetrachlorodibenzofurans, their biologic and toxic potencies were dependent on one major structural factor, the number of lateral chloro substituents. These results support the proposed role of the cytosolic receptor protein in mediating the biologic and toxic effects of the PCDFs.

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

Fifteen polychlorinated dibenzofuran (PCDF) congeners were administered in a dose-response fashion to immature male Wistar rats and ED50 values for body weight loss, thymic atrophy and the induction of the hepatic microsomal cytochrome P-448-dependent monooxygenases, aryl hydrocarbon hydroxylase (AHH) and 4-chlorobiphenyl hydroxylase were determined. There was an excellent correlation between the in vivo quantitative structure-activity relationships for these PCDFs and their in vitro activities as AHH inducers in rat hepatoma H-4-II E cells and as ligands for the 2,3,7,8-TCDD receptor protein. A comparison of isomers which differ at all 4 positions in the dibenzofuran ring system indicated that chlorine substitution at each position contributed differentially to the overall molecular activity [C-3 (or C-7) greater than C-2 (or C-8) greater than C-4 (or C-6) greater than C-1 (or C-9)]. There was also an excellent linear correlation between a plot of the -log ED50 for body weight loss vs. -log EC50 for in vitro AHH induction (correlation coefficient, r = 0.96) and -log ED50 for thymic atrophy vs. -log EC50 for in vitro AHH induction (correlation coefficient, r = 0.88). Since body weight loss and thymic atrophy in the rat are representative toxic responses to PCDFs and related toxic halogenated aryl hydrocarbons, the correlations noted above support the use of the in vitro AHH induction assay as a short term quantitative test system for this class of toxic halogenated aryl hydrocarbons.

Polychlorinated dibenzo-p-dioxins: quantitative in vitro and in vivo structure-activity relationships.

There were marked effects of structure on the activities of 14 polychlorinated dibenzo-p-dioxins (PCDDs) as competitive ligands for the 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) receptor and as inducers of aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) in rat hepatoma H-4-II E cells in culture. 2,3,7,8-TCDD was the most active compound in both assays and several PCDD congeners which were fully substituted in the lateral 2, 3, 7 and 8 positions but also contained additional chlorosubstituents in non-lateral 1, 4, 6 and 9 positions were less active. It was also evident that there was a decrease in in vitro binding and induction activities with decreasing lateral chlorine substitution. Although comparable structure-activity relationships (SARs) for the PCDDs were observed for the induction and receptor binding assays, there was not a linear or rank order correlation between the 2 sets of data. Several in vivo biologic and toxic activities of 2,3,7-trichloro-, 2,3,7,8- and 1,3,7,8-tetrachloro-, 1,2,4,7,8- and 1,2,3,7,8-pentachloro- and 1,2,3,4,7,8-hexachlorodibenzo-p-dioxin were determined in a dose-response fashion in immature male Wistar rats. The ED50 values for hepatic microsomal AHH and EROD induction, body weight loss and thymic atrophy were obtained. There was an excellent linear correlation between the -log EC50 values for AHH or EROD induction in cell culture and the -log ED50 values for enzyme induction, body weight loss and thymic atrophy in the rat. The in vitro enzyme induction data could be used to quantitatively estimate the toxicity of the PCDD congeners in the rat: this latter correlation has previously been observed for a series of polychlorinated dibenzofurans.

Polybrominated dibenzo-p-dioxins and related compounds: Quantitative in vivo and in vitro structure-activity relationships

The effects of structure on the in vitro receptor binding affinities, aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) induction potencies in rat hepatoma cells were determined for the following compounds: 2-bromo-, 2,7/2,8-dibromo-, 2,3,7-tribromo-, 2,4,6,8/1,3,7,9-tetrabromo-, 2,3,7,8-tetrabromo-, 1,3,7,8-tetrabromo-, 1,2,3,7,8-pentabromo-, 1,2,4,7,8-pentabromo-, 2,3-dibromo-7,8-dichloro-, 2,8-dibromo-3,7-dichloro- and 2-bromo-3,7,8-trichlorodibenzo-p-dioxin. The structure-activity relationships (SARs) for the polybrominated dibenzo-p-dioxins (PBDDs) were comparable for both in vitro responses: the most active compounds were substituted only in the lateral 2,3,7 and 8 position and the addition of non-lateral or removal of lateral halogen substituents reduced the activity of the resultant compound. The biologic and toxic effects of 2,3,7,8-tetrabromo-, 1,3,7,8-tetrabromo-, 1,2,4,7,8-pentabromo-1,2,3,7,8-pentabromo-, 2-bromo-3,7,8-trichloro- and 2,3-dibromo-7,8-dichlorodibenzo-p-dioxin on several receptor-mediated responses (thymic atrophy, body weight loss, hepatic microsomal AHH and EROD induction) were determined in a dose-response fashion in immature male Wistar rats. A comparison of the ED50 values for the in vivo responses demonstrated that the SARs for the PBDDs and brominated polychlorinated dibenzo-p-dioxins were comparable to those observed for in vitro receptor binding and AHH induction. Moreover, there was an excellent linear correlation between the -log EC50 (in vitro AHH induction) vs. the in vivo -log ED50 (thymic atrophy) and -log ED50 (body wt loss) correlation coefficient, r = 0.97 for all 2 correlations).

Synthesis, biologic and toxic effects of the major 2,3,7,8-tetrachlorodibenzo-p-dioxin metabolites in the rat.

The two major mammalian metabolites of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), namely 2-hydroxy-3,7,8-trichlorodibenzo-p-dioxin and 2-hydroxy-1,3,7,8-tetrachlorodibenzo-p-dioxin, have been synthesized. The compounds were individually administered to immature male Wistar rats and their effects on body weight loss, thymic atrophy, liver and spleen weights and their activities as inducers of hepatic microsomal benzo[a]pyrene hydroxylase, 4-chlorobiphenyl hydroxylase and ethoxyresorufin O-deethylase were determined using dose levels of 100, 1000 and 5000 micrograms/kg. The 2 metabolites did not affect organ or body weights after 14 days of exposure and only 2-hydroxy-3,7,8-trichlorodibenzo-p-dioxin was active as an inducer of the microsomal monooxygenases at dose levels of 1000 and 5000 micrograms/kg. A comparison of the relative enzyme induction activities of 2,3,7,8-TCDD and 2-hydroxy-3,7,8-trichlorodibenzo-p-dioxin indicates that the former compound was greater than 3 orders of magnitude more active than the metabolite.

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 envi ronmental 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 develop ment 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, inhibi tion of body weight gain and thymic atrophy in the rat. It has also been shown for selected compounds that there was a good correla tion 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 uti lized to quantitate 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 brom inated flame retardants which contain a complex mixture of halo genated dibenzo-p-dioxins and dibenzofurans.

Comparative toxicities of the polychlorinated dibenzofuran (PCDF) and biphenyl (PCB) mixtures which persist in Yusho victims

Abstract The toxic Yusho oil contained a mixture of polychlorinated biphenyls (PCBs) which were contaminated by other halogenated aromatics including the highly toxic polychlorinated dibenzofurans (PCDFs). It has been reported that the PCBs and PCDFs which persist in the liver of victims still suffering from Yusho poisoning include the following compounds; 2,3′,4,4′,5-penta-,2,2′,4,4′,5,5′-,2,2′,3′,4,4′,5- and 2,3,3′,4,4′,5-hexa, 2,2′,3,4,4′,5,5′- and 2,2′,3,3′,4,4′,5-heptachlorobiphenyls and the 2,3,7,8-tetra-, 1,2,4,7,8-, 1,2,3,7,8- and 2,3,4,7,8-penta- and 1,2,3,4,7,8-hexachlorodibenzofurans. All of these PCBs and PCDFs have been synthesized and reconstituted to approximate their composition in human liver. A comparison of the dose-response effects of the reconstituted PCB and PCDF mixtures in causing weight loss, thymic atrophy and the induction of cytochrome P-448-dependent monooxygenases indicated that the PCDF mixture was at least 700 times more active than the PCBs. Since the ratio of PCBs/PCDFs persisting in Yusho patients blood and liver was less than 600:1 and 5:1 respectively, the results suggest that the PCDFs are the major etiologic agent in Yusho poisoning.

The biologic and toxic effect of 2,3,7,8-tetrachlorodibenzo-p-dioxin in chickens

The administration of 2,3,7,8-TCDD to 2-week-old White Leghorn cockerels produced a dose-dependent induction of hepatic microsomal ethoxyresorufin O-deethylase (EROD) and benzo[alpha]pyrene (B[alpha]P) hydroxylase activities with induction EC50 values of 778 and 302 ng/kg, respectively. In addition, 2,3,7,8-TCDD also induced 4-dimethylaminoantipyrine (DMAP) N-demethylase (EC50 = 561 ng/kg), this result contrasting with studies reported for other animal species in which 2,3,7,8-TCDD either does not induce or inhibits this cytochrome P-450 dependent monooxygenase enzyme activity. However, the reduced cytochrome P-450:CO binding difference spectral absorption maxima for the 2,3,7,8-TCDD induced microsomes was observed at 448 nm which was similar to that reported for most animals which have been investigated. Electrophoresis of control and 2,3,7,8-TCDD induced microsomal proteins using SDS polyacrylamide slab gels showed intensification of 3 protein staining bands at Mr 53 000, 56 000 and 58 000. Incubation of the 2,3,7,8-TCDD-induced microsomes with SKF-525A and alpha-naphthoflavone showed that both compounds inhibited DMAP N-demethylase, EROD and AHH and that alpha-naphthoflavone was the more potent inhibitor of all 3 microsomal monooxygenases. 2,3,7,8-TCDD treatment caused significant involution of the Bursa of Fabricius when administered at a dose level of 10 micrograms/kg for 3 days and this result confirmed the extreme sensitivity of the immature White Leghorn cockerel to the biologic and toxic effects elicited by 2,3,7,8-TCDD. However, in contrast to other sensitive species, no high affinity cytosolic receptor protein for [3H]2,3,7,8-TCDD could be detected in the liver of chick embryos or 2-week-old birds.

Validation of in vitro bioassays for 2,3,7,8-TCDD equivalents

Abstract The inducibility of aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) in rat hepatoma H-4-II E cells culture has been utilized as a quantitative bioassay for polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs). There was an excellent linear correlation between the -log EC50 (in vitro enzyme induction) for 16 PCDD and PCDF congeners and their -log ED50 values for in vivo toxicity (body weight loss and thymic atrophy) in the rat. There was also a comparable linear correlation between the in vitro and in vivo AHH/EROD induction activities. Extraction of a fly ash sample with methylene chloride followed by cleanup gave a PCDD/PCDF fraction which contained a complex mixture of isomers and congeners. The total PCDD and PCDF levels were 3.83 and 5.52 ug/g fly ash respectively and 2,3,7,8-TCDD constituted 2–3% of the total tetrachlorodibenzo-p-dioxins. Using the in vitro enzyme induction bioassay procedure, the estimated 2,3,7,8-TCDD (equivalents) in this extract were 105 ng/g fly ash. The doseresponse in vivo induction of AHH was also determined and the estimated 2,3,7,8-TCDD (equivalents) in this extract were 75 ng/kg fly ash and this confirms the excellent correlation between the in vivo and in vitro bioassays.

Monoclonal antibodies to chlorinated dibenzo-p-dioxins

A thyroglobulin conjugate of dioxin (thyroglobulin-2 adipamide, 3,7,8-trichlorodibenzo-p-dioxin) (TG-TCDD) was used to immunize BALB/c mice. Hybridomas were produced by cell fusion between immune spleen cells and mouse myelomas SP2/0, P3, or NS1. To screen the thousands of resultant cultures for production of monoclonal antibodies (MoAb), a rapid, solid-phase radioimmunoassay for antibody to dioxins was developed. This procedure involved attaching bovine serum albumin coupled with trichlorodibenzo-p-dioxin (BSA-TCDD) to polystyrene plates to be used as a solid-phase target antigen for reaction with MoAb. Fourteen hybridomas were identified that produced MoAb reacting with BSa-TCDD but not with BSA alone. Antibodies were tested for binding to BSA-aniline to eliminate those with limited binding specificity. Initial studies indicated that most MoAbs bound BSA-aniline as well as BSA-TCDD. More detailed analyses indicated that while most MoAbs showed some reaction with BSA-aniline, two showed preferential binding to BSA-TCDD of more than 200-fold whereas rabbit antisera demonstrated only a 5-fold discrimination. MoAb 391-1B was purified from mouse ascites fluid and after radioiodination, was tested for direct binding to BSA-TCDD or BSA-aniline. 125I-MoAb 391-1B showed no significant binding to BSA-aniline while demonstrating high binding to BSA-TCDD (Ka = 4.5 X 10(8) liters/mol).