Identification and toxicological evaluation of chlorinated dibenzofuran and chlorinated naphthalene in two commercial polychlorinated biphenyls

Linking field and laboratory studies: Reproductive effects of perfluorinated substances on avian populations

Although both laboratory and field studies are needed to effectively assess effects and risk of contaminants to free-living organisms, the limitations of each must be understood. The objectives of this paper are to examine information on field studies of reproductive effects of perfluorinated substances (PFASs) on bird populations, discuss the differences among field studies, and then place those results in context with laboratory studies. Hypotheses to explain the divergences between field studies and between laboratory and field studies will be discussed. Those differences include mixture issues, misattribution of the mechanism or the specific PFAS causing impairments, as well as other possible reasons. Finally, suggestions to better link laboratory and field studies will be presented. Integr Environ Assess Manag 2021;17:690-696. Published 2021. This article is a US Government work and is in the public domain in the USA.

[A memoir of my researches on xenobiotic metabolism for 48 years--researches on Kanemi Yusho and endocrine disrupting chemicals]

The author started a research on xenobiotic metabolism at Graduate School of Pharmaceutical Sciences, Kyushu University in 1965. In 1968, an epidemic of a "strange disease", called Yusho, occurred in western Japan. The epidemic was soon identified to be a food poisoning caused by the ingestion of commercial Kanemi rice bran oil which had been accidentally contaminated with large amounts of polychlorinated biphenyls (PCBs) and their related compounds such as polychlorinated dibenzofurans (PCDFs.) At first, in this review, our toxicological studies on Yusho during the early thirty years were briefly described. Next, the studies on aldehyde oxidase, a molybdenum hydroxylase, which is involved in the lactam formation reaction such as 1-phenyl-2-(2-oxopyrrolidine)pentane(oxoprolintane) from 1-phenyl-2-pyrrolidinopentane(prolintane) and 1-methyl-4-phenyl-1,2,3,6-tetrahydropyridine(MPTP) lactam from 1-methyl-4-phenyl-2,3-dihydropyridinium ion (MPDP⁺) were also presented. Finally, we investigated how the xenobiotic metabolism of endocrine disrupting chemicals such as bisphenol A (BPA) and some isoflavones affects their estrogenic activities. In this study, we demonstrated that BPA is converted to 4-methyl-2,4-bis(4-hydroxyphenyl)pent-1-ene (MBP), an active metabolite as estrogen, by rat liver S9. In the cases of isoflavones, although genistein was inactivated, biochanin A, 4'-methoxy analogue of genistein, was activated to genistein by O-demethylation with rat liver S9.

Discovery of hydroxylated polychlorinated biphenyls (OH-PCBs) in sediment from a lake Michigan waterway and original commercial aroclors

Hydroxylated polychlorinated biphenyls (OH-PCBs) were measured in surficial sediment from Indiana Harbor and Ship Canal (IHSC), East Chicago, IN and five original Monsanto Aroclors. These compounds were measured using gas chromatography with tandem mass spectrometry (GC-MS/MS) and certified standards that allowed us to identify 65 individual or coeluting congeners. Concentrations in the sediment ranged from 0.20 to 26 ng/g dry weight. Profiles of most samples were similar and were dominated by mono- to penta-chlorinated OH-PCBs. Interestingly, most of the samples strongly resembled the OH-PCB profiles of Aroclors 1221, 1242, 1248, and 1254, yet 25% of OH-PCBs measured in the sediment were not detected in Aroclors. A strong positive correlation was found between ΣOH-PCB and ΣPCB (p < 0.0001) and also between many individual OH-PCB:PCB pairs (p < 0.05). Analysis of OH-PCB:PCB pairs suggest PCB degradation is unlikely as a source of OH-PCBs in IHSC sediment. We are the first to report levels of OH-PCBs in sediment and Aroclors, and our discovery is significant because it is likely that OH-PCB contamination exists in sediment anywhere that PCB contamination from Aroclors is present.

Acute non-cancer mortality excess after polychlorinated biphenyls and polychlorinated dibenzofurans mixed exposure from contaminated rice oil: Yusho

In Japan in 1968, rice-oil contaminated by polychlorinated biphenyls and polychlorinated dibenzofurans caused severe food poisoning, termed "Yusho" (oil disease). Several previous studies attempted to evaluate the effects targeting officially-certified Yusho patients. However, these studies have several limitations such as the left-truncated nature of the registry or residual confounding arising from the referent population selection. We thus conducted an area-based standardized mortality ratios (SMRs) study using vital statistics. A severely affected area (Tamanoura area) was adopted as the exposure group, with a reference population from Nagasaki prefecture in Kyushu, which included the Tamanoura. A large number of residents in Tamanoura were exposed to the rice-oil (28% of all the certified cases as of 2009). We estimated SMRs of non-cancer and cancer diseases for the years 1968-2002. Shortly after the exposure, SMRs of all causes, diabetes mellitus, cardiovascular disease, pneumonia/bronchitis, and bronchus/lung cancer were elevated. In particular, SMRs of heart disease were 1.97 [95% confidence intervals (CI): 1.09-3.56] in 1968, 2.05 (95% CI: 1.16-3.60) in 1969, and 1.89 (95% CI: 1.05-3.41) in 1975. However, we did not observe clear increase in SMRs more than 10 years after the exposure. This study provides further evidence in Yusho, especially on acute effects on non-cancer mortality.

Polychlorinated naphthalenes in animal aquatic species and human exposure through the diet: a review

Polychlorinated naphthalenes (PCNs) are a group of environmental pollutants, which contain one to eight chlorine atoms per naphthalene molecule, forming a total of 75 possible congeners. Several of the PCN congeners display toxicity similar to that of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) through AhR-mediated mechanisms. There are toxicological similarities between PCNs and other well known environmental contaminants such as polychlorinated dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs) and biphenyls (PCBs). However, in contrast to these compounds, information on exposure to PCNs for non-occupationally exposed populations is rather scarce. In this article, information on human exposure to PCNs through dietary intake is reviewed. Because this information is very limited and taking into account that most data on PCN levels in potential foods concern to aquatic species, these data are also reviewed. It is concluded that further investigations on dietary intake and potential human health effects of PCNs are clearly necessary.

Bioanalytical screening methods for dioxins and dioxin-like compounds a review of bioassay/biomarker technology

Determination of environmental pollutants utilizing biodetectors such as bioassays, biomarkers, enzyme immunoassays (EIAs), or other bioanalytical tools is a continuously growing area. The present literature review describes the principles and advantages/limitations of several bioanalytical detection methods (BDMs) for the screening and diagnosis of dioxin and dioxin-like compounds. This study characterizes briefly the family of dioxin and dioxin-like compounds, discusses potential Ah receptor (AhR) ligands and cytochrome P-450 (CYP) 1A1-enzyme-inducing compounds. 'Milestones' in the development of BDMs are summarized and explained in detail for a number of bioanalytical tools that can be used to detect these classes of dioxin-like persistent bioaccumulative toxicants (PBTs). The design of a screening profile with a battery of bioassays/biomarkers coupled with the chemical analysis is evaluated. The relative potencies (REPs) to 2,3,7,8-TCDD for dioxin-like compounds are reviewed for various BDMs and the differences are noted.

Polychlorinated naphthalenes in groundwater samples from the Llobregat aquifer (Spain)

Polychlorinated naphthalenes (PCNs) have characteristics fairly similar to those of polychlorinated biphenyls and terphenyls (PCBs and PCTs) and although they have been used in numerous applications, very few reports on the occurrence of PCNs in water have been published. Both automated solid-phase extraction (SPE) and liquid-liquid extraction (LLE) procedures were evaluated to concentrate PCNs. High-resolution gas chromatography with electron-capture detection (HRGC-ECD) and mass spectrometric detection in the selected ion monitoring mode (SIM) were used to analyze PCNs in groundwater samples from the aquifer of the Llobregat river near Barcelona (NE Spain). The homologue distribution profiles of PCNs found in groundwater samples and the standard mixtures of Halowax (1099, 1013 and 1014) were compared. Quantification was achieved by HRGC-ECD. Total PCN concentrations expressed as Halowax 1099 equivalents ranged from < 0.5 ng/l to 79.1 micrograms/l in the water samples, with tetrachloronaphthalenes (TetraPCN) as the major group of congeners.

Polychlorinated diphenyl ethers, dibenzo-p-dioxins, dibenzofurans and biphenyls in seals and sediment from the Gulf of Finland

Polychlorinated diphenyl ethers (PCDEs), 2,3,7,8-substituted polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs), and polychlorinated biphenyls (PCBs) were analyzed in seals from the Gulf of Finland and in sediments from the Gulf of Finland and near Gotland. The sediments included one surface core from both sampling sites. The seal material consisted of 14 ringed seals and 6 grey seals that all were found dead and examined for pathology. The main aims were to scrutinize levels and patterns of PCDEs for the first time in seals from the Baltic Sea and to estimate whether chlorinated compounds mentioned have an influence on an exceptional high mortality that occurred among ringed seals in the Gulf of Finland in late 1991. The concentrations of 50 congeners of tetra- through deca-CDEs analyzed ranged from < 0.3 to 62 ng/g lipid weight (lw) in seal blubber, but in the sediments PCDEs were non-detectable (tetra- through hepta-CDEs < 0.1 ng/g dry weight (dw)). In ringed seals with good nutritional status, the concentrations of almost all PCDE congeners were greater in two adult females than in specimens of younger age groups. The concentrations of PCDDs and PCDFs as TCDD-equivalents exceeded those of the coplanar (non-ortho) PCBs in sediments, whereas non- and monoortho PCBs constituted greater toxic loads as those calculated for PCDDs and PCDFs in seals. However, the levels revealed do not explain the high mortality of ringed seals.

Histopathology of postpartum placental sites in mink (Mustela vison) exposed to polychlorinated biphenyls or fractions thereof

Polychlorinated biphenyls (PCB) cause reproductive failure in mink. Ovulation and nidation occur, but the fetuses die during gestation. The toxicity of different chlorinated biphenyl (CB) congeners differs markedly. Dioxin-like congeners with no (0-ortho CBs) chlorine in the ortho position to the biphenyl bond are considered to be highly toxic. Altogether, 13 groups of 10 female mink (Mustela vison) were exposed to PCB or CB fractions thereof during the reproductive season of 1988 and 1989. In 1988, one group of mink received 2 mg/day of Clophen A50 and five groups received single fractions thereof or synthetic 0-ortho CB in their diet. In 1989, one group received 1.64 mg/day of Aroclor 1254 and six groups received combinations of fractions thereof. The daily amounts of the fractions administered per animal were equivalent to those present in 2 mg of Clophen A50 or 1.64 mg of Aroclor 1254. After administration for 3 months in both experiments, the animals were killed 5 days after parturition. Histological examination focused on the placental sites. The most involuted placental sites were those of early fetal death in primiparous, non-whelping animals in the 1989 experiment. The least involuted placental sites, displaying a hyperplastic and pleomorphic uterine luminal epithelium, in which proliferating cell nuclear antigen (PCNA) was present, were those of late fetal death in biparous, non-whelping animals in the 1988 experiment. The survival of the fetoplacental unit was related to PCB exposure. The histology of the placental sites seemed only to be related to the survival time of the fetuses and to the number of former reproductive seasons.

Polychlorinated diphenyl ethers, dibenzo-P-dioxins and dibenzofurans in Finnish human tissues compared to environmental samples

Finnish human samples from the Helsinki area and Arctic cod samples from Vestertana Fjord (Norway) were analyzed for polychlorinated diphenyl ethers (PCDE) and 2,3,7,8-chloro substituted dibenzo-p-dioxins (PCDD) and dibenzofurans (PCDF). The PCDE, PCDD and PCDF contents in human and animal samples from Finland and elsewhere were briefly reviewed. PCDEs were non-detectable in human liver and testis, but some PCDE congeners were identified in human adipose tissue and fat of boiled Arctic cod liver composite. The contents of PCDEs in Finnish human samples were similar to those reported in the literature for human tissues from North America. The estimated concentrations of PCDEs 99, 147 + 153 (coeluting) and 206 ranged between 2 and 8 ng/g lipid weight (lw) in one Finnish human adipose tissue. The concentrations of PCDE congeners identified in the cod liver fat were between 0.4 and 5 ng/g lw. Of toxic PCDDs and PCDFs, hepta- and octa-CDDs dominated in human. The concentrations of PCDD and PCDF congeners varied from < 2 to 7700 pg/g lw in human. In Arctic cod samples analyzed (muscle tissues of an air dried cod and cod liver fat), 2,3,7,8-tetra-CDF was nearly the only congener of PCDD/PCDFs detected.

Great Lakes embryo mortality, edema, and deformities syndrome (GLEMEDS) in colonial fish-eating birds: similarity to chick-edema disease

Several species of colonial fish-eating birds nesting in the Great Lakes basin, including herring gulls, common terns and double-crested cormorants, have exhibited chronic impairment of reproduction. In addition to eggshell thinning caused by high levels of DDT and metabolites, the reproductive impairment is characterized by high embryonic and chick mortality, edema, growth retardation, and deformities, hence the name Great Lakes embryo mortality, edema, and deformities syndrome (GLEMEDS). The hypothesis has been advanced that GLEMEDS in colonial fish-eating birds resembles chick-edema disease of poultry and has been caused by exposure to chick-edema active compounds that have a common mode of action through the cytochrome P-448 system. Detailed evidence has been collected from the following three groups of studies on herring gulls in the lower Great Lakes during the early 1970s; Forster's terns in Green Bay, Wisconsin in 1983; and double-crested cormorants and Caspian terns in various locations in the upper Great Lakes from 1986 onwards. It has proved difficult to establish not only the onset of the disease in the various species at various locations but also the period in which chick-edema active compounds were released. Anecdotal evidence suggested that serious egg mortality in Lake Ontario herring gulls first occurred in 1966, through the signs of chick-edema disease were not looked for until 1974. Only indirect evidence is available on the date of the release of one of the presumed causal agents, 2,3,7,8-tetrachlorodibenzo-p-dioxin, but highest levels may have occurred in the early to mid 1960s. More reliable data show that the onset of the improvement of reproduction of Lake Ontario herring gulls coincided with the declines in organochlorine compounds and particularly 2,3,7,8-TCDD and PCB. Similarly, information on the onset of the disease and exposures in the Forster's tern and double-crested cormorants in Green Bay is uncertain but bird banders did not observe deformities until the 1970s, which corresponds with the onset of high levels of PCB. If the disappearance of the Caspian tern from Saginaw Bay in the mid 1960s corresponds with the onset of GLEMEDS at that location, then there is a close temporal relationship to the onset of high PCB levels. Chick-edema disease is difficult to diagnose because there is no specific lesion, but rather there is a suite of lesions.(ABSTRACT TRUNCATED AT 400 WORDS)

Carcinogenicity of polyhalogenated biphenyls: PCBs and PBBs

Polychlorinated biphenyls (PCBs) and polybrominated biphenyls (PBBs) are compounds whose physical/chemical properties led to their widespread commercial use. Although their production has been banned or severely limited in most countries since the 1970s, the persistence and stability of these compounds have resulted in a worldwide distribution, especially of PCBs. PBB contamination is limited principally to the state of Michigan, where a series of tragic errors eventually resulted in the accumulation of residues in livestock and the general human population. Long-term exposure to PCBs and PBBs in animals has been associated with the induction of neoplastic nodules in the liver and in some cases hepatocellular carcinoma. This review discusses the role of PCBs and PBBs in the process of carcinogenesis. The mutagenicity/genotoxicity of these compounds, as well as their initiation/promotion potential is discussed. The epidemiology of PCB and PBB exposure is reported along with an estimation of the risk of cancer to humans. Finally, possible molecular mechanisms of action are suggested for polyhalogenated biphenyls in cancer development.

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.

Decreased ligand binding to the hepatic glucocorticoid and epidermal growth factor receptors after 2,3,4,7,8-pentachlorodibenzofuran and 1,2,3,4,7,8-hexachlorodibenzofuran treatment of pregnant mice

2,3,4,7,8-Pentachlorodibenzofuran (PeCDF) and 1,2,3,4,7,8-hexachlorodibenzofuran (HCDF) are environmental contaminants which mimic many of the toxic effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Like TCDD, these polychlorinated dibenzofurans (PCDFs) induce hepatic benzo[a]pyrene hydroxylase activity (BPH) and possess high affinity for the Ah receptor. Another similarity of these PCDFs to TCDD is their ability to induce teratogenic effects such as cleft palate and hydronephrosis in mice. Recent studies have shown that TCDD modifies the equilibrium binding kinetics of the rat liver cytosolic glucocorticoid receptor (GRc) and the hepatic plasma membrane epidermal growth factor (EGF) receptor. To gain a better understanding of the action of halogenated hydrocarbons on these cytosolic and membrane-bound receptor systems during pregnancy, we investigated the biochemical effects of PeCDF and HCDF on the binding kinetics of maternal mouse liver GRc and EGF receptors and the induction of BPH activities. Pregnant C57BL/6N mice were treated once daily on gestation Days 10 through 13 with PeCDF (0-30 micrograms/kg) or HCDF (0-300 micrograms/kg). Hepatic [3H]dexamethasone and [125I]EGF equilibrium binding studies indicated that all doses of PeCDF tested (10, 20, and 30 micrograms/kg) significantly reduced the GRc and EGF receptor maximum binding capacities but did not affect the binding affinities of these receptors when compared to corn oil-treated control pregnant mice. Similar effects were observed for doses of HCDF greater than or equal to 100 micrograms/kg. These data suggest that the dibenzofuran-mediated decreases in GRc and EGF receptor binding capacities are similar to those caused by TCDD. Although the mechanism of action is not yet clear, our results indicate that halogenated aromatic compounds in addition to TCDD have profound effects on both steroid and growth factor receptor systems.

Comparative dermal absorption of 2,3,7,8-tetrachlorodibenzo-p-dioxin and three polychlorinated dibenzofurans

Polychlorinated dibenzodioxins (PCDDs) and dibenzofurans (PCDFs) are toxic environmental contaminants which have the potential to accumulate in human tissues. In order to examine the potential for systemic exposure following dermal exposure, the absorption, distribution, and elimination of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 2,3,7,8-tetrachlorodibenzofuran (TCDF), 1,2,3,7,8-pentachlorodibenzofuran (1PeCDF), and 2,3,4,7,8-pentachlorodibenzofuran (4PeCDF) were evaluated in male F344 rats. TCDD (0.00015, 0.001, 0.01, 0.1, 0.5, and 1.0 mumol/kg) and the three PCDFs (0.1, 0.5, and 1.0 mumol/kg) were applied to a preclipped region on the back of the rat and covered with a perforated cap. The rats were held in individual metabolism cages for 3 days. In animals administered 0.1 mumol/kg, the absorption of TCDF was greater than that of 4PeCDF, 1PeCDF, and TCDD. Relative absorption (percentage of administered dose) declined with increasing dose while the absolute absorption (microgram/kg) increased nonlinearly with dose. Absorption of TCDF at 0.1 mumol/kg was 48% of the administered dose which was significantly greater than that of the other compounds. At this dose, absorption of 4PeCDF was greater than that of TCDD. Absorption at the higher doses was similar for all four compounds. Maximum relative absorption of TCDD (approximately 40% of the administered dose) was obtained at 0.001 and 0.00015 mumol/kg. Major tissue depots for these four chemicals included liver, adipose, skin, and muscle tissue; however, the liver:fat ratio for 4PeCDF was approximately fourfold higher than that for the other three compounds. When normalized to 100% of dose absorbed, the distribution of 4PeCDF-derived radioactivity in liver and adipose tissue was similar to that previously observed after oral and iv administration. In animals administered 0.1 mumol TCDF or 1PeCDF/kg, 56 and 32% of the respective absorbed dose was excreted as polar metabolites within 3 days. Very little of the absorbed dose of either TCDD (approximately 10%) or 4PeCDF (approximately 2%) was eliminated. Results indicate that the dermal absorption of these compounds is incomplete and that systemic toxicity following acute dermal exposure to levels found in the environment is unlikely.

Disposition of 1,2,3,7,8-pentachlorodibenzofuran in the rat

1,2,3,7,8-Pentachlorodibenzofuran (1PeCDF) is one of several toxic polychlorinated dibenzofurans (PCDFs) which are ubiquitous environmental contaminants. Related in structure and toxicity to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), PCDFs have been detected in municipal and industrial effluents, PCB mixtures, and in a variety of antiseptics and preservative solutions. The objective of this study was to evaluate the distribution and elimination of 1PeCDF in the rat and to compare these parameters with that of 2,3,4,7,8-pentachlorodibenzofuran (4PeCDF) and 2,3,7,8-tetrachlorodibenzofuran (TCDF). After iv administration of 0.1 mumol [3H]1PeCDF/kg, 1PeCDF was rapidly cleared from the blood and distributed to the liver, muscle, skin, and adipose tissue in a manner similar to that for other dibenzofurans. The initial pool sizes of 1PeCDF-derived radioactivity in the liver, muscle, skin, and adipose tissue were 43,35,10, and 7% of the administered dose, respectively. In all cases, loss of radioactivity from these tissues could be described by exponential decay and the initial half-lives for these tissues were 1.36, 0.03, 13, and 1 day, respectively. After redistribution from the muscle, skin, and adipose tissues to the liver, 1PeCDF was metabolized to a polar metabolite(s) and excreted from the body via the bile into the feces. No parent compound was detected in the bile and fecal excretion was the major route of elimination. Most of the radioactivity in the urine was excreted within the first day, after which less than 0.5% of the dose/day was detected. More than half of the administered dose was excreted in the urine and feces within 2 days. The whole-body half-life of related compounds is 4PeCDF much greater than 1PeCDF greater than or equal to TCDF. Therefore, persistence appears to be inversely related to the metabolism of these compounds and metabolism is inhibited by chlorine-substituted carbon atoms adjacent to the oxygen atom in the dibenzofuran ring.

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.

Teratogenic potency of TCDD, TCDF and TCDD-TCDF combinations in C57BL/6N mice

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) and 2,3,7,8-tetrachlorodibenzofuran (TCDF) cause the same spectrum of fetal anomalies in C57BL/6N mice. Pregnant dams were treated with TCDD, TCDF and combinations of the 2 compounds on gestation day 10, and examined for maternal and fetal effects on day 18. The fetal kidneys were the most sensitive target for teratogenicity. The dose response for cleft palate induction fit the probit model for both compounds, suggesting that TCDD was approximately 30 times more potent than TCDF. The interaction between these 2 compounds was consistent with a model for additive toxicity.

Teratogenicity of 2.3.7.8-tetrachlorodibenzofuran (TCDF) in mice

Treatment of pregnant C57BL/6N mice with 2,3,7,8-tetrachlorodibenzofuran (TCDF) (0, 250, 500, and 1000 micrograms/kg on gestation day 10 or 0, 10, 30, 50, and 100 micrograms/kg on gestation days 10-13) results in dose-related increases in isolated cleft palates and hydronephrotic kidneys in the offspring. TCDF is teratogenic in 100% of the fetuses at dose levels that are not maternally toxic. The fetal kidney is the most sensitive target organ but the kidney lesions may be reversible.

Teratogenicity of 2,3,7,8-tetrachlorodibenzofuran in the mouse

2,3,7,8-Tetrachlorodibenzofuran (TCDBF) was administered in single doses (0.1-0.8 mg/kg body weight) intraperitoneally to pregnant C57BL mice on d 10, 11, 12, or 13 of gestation. A dose-dependent increase was observed in the frequency of fetal resorptions and fetal death, especially in the earlier stages (d 10-11). Cleft palate and hydronephrosis as well appeared in a dose-dependent manner, with a peak in sensitivity after administration on d 11-12. TCDBF given at a dose level of 0.1 mg/kg body weight on d 12 of gestation (only dose- and stage-tested) produced a marked thymic hypoplasia as well. A few cases of general hydrops occurred. The pattern of malformations and time of sensitivity corresponded well to that observed earlier after administration of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD; ED50 approximately equal to 25 micrograms/kg) and 3,3',4,4'-tetrachloroazoxybenzene (TCAOB; ED50 approximately equal to 6 mg/kg), two congeners of TCDBF, indicating common mechanisms of action of this family of compounds. Ornithine decarboxylase (ODC) is an important enzyme in cell proliferation and growth with a high activity in embryonic tissues. Liver ODC activity has previously been found to be stimulated by TCDD in weaning mice. However, this enzyme was not found to be stimulated in fetal and placental tissues, but slightly in maternal kidney after treatment with TCDBF in teratogenic doses. It is possible that the ODC activity increases under certain conditions only, on administration of TCDD and its congeners.

Toxicity and distribution of 2,3,7,8-tetrachlorodibenzofuran in male guinea pigs

The toxicity of 2,3,7,8-tetrachlorodibenzofuran (TCDF) was studied in male Hartley guinea pigs after single or multiple oral treatment. In each animal studied, adipose tissue, liver, and skin were the major depots of TCDF and accounted for 50-74% of the total dose. The whole-body half-life of TCDF in guinea pigs was estimated to be approximately 40 d. This slow clearance of TCDF by guinea pigs may explain the high toxicity of TCDF for this species even when very low repeated doses were administered. Intervals of 1, 2, or 4 wk between doses had little effect on TCDF lethality, but did have an effect on the pattern of toxicity. Treatment of mature animals with high single doses of TCDF (10 or 15 micrograms/kg body weight) resulted in the immediate loss of weight and the eventual death of all treated animals within 2-4 wk after the loss of approximately 35% of their initial body weight. Treatment of immature animals with low multiple doses totaling cumulative doses of between 4 and 12 micrograms/kg resulted in the death of 75% of these animals, with the deaths occurring between 7 and 19 d after the initial appearance of quantitative toxic symptoms (loss of weight); however, weight loss was less dramatic following repeated low doses than after acute high doses. Concentration of TCDF in adipose tissue was generally proportional to dose of TCDF. With increasing time after dosage, there was a shift in distribution from adipose tissue to liver.

A comparative study of polychlorinated dibenzofurans, polychlorinated biphenyls and 2,3,7,8-tetrachlorodibenzo-p-dioxin on aryl hydrocarbon hydroxylase inducing potency in rats

The aryl hydrocarbon hydroxylase (AHH) inducing potency of toxic chlorinated aromatic hydrocarbons such as polychlorinated dibenzofurans (PCDFs), polychlorinated biphenyls (PCBs) and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was studied in the young male Wistar rats. Alternatively, a technical PCDF mixture, 15 individual PCDF isomers or TCDD were administered i.p. in doses of 5 micrograms/kg; a PCB mixture was given in a dose of 50 mg/kg. The order of AHH inducing ability was TCDD greater than PCDFs much greater than PCBs in kidney, lung, and liver. In the prostate, thymus, and spleen, only TCDD enhanced the AHH activity. The AHH inducibility in the lung and liver, induced by 15 pure PCDF isomers with varying chlorine substitutions was also examined. Only 2,3,7,8-tetrachlorodibenzofuran (2,3,7,8-tetra-CDF) and 2,3,4,7,8-pentachlorodibenzofurans (2,3,4,7,8-penta-CDF) significantly induced the hepatic AHH activity (4- and 2-fold, respectively), while eight PCDF isomers, including these two, significantly enhanced the pulmonary AHH activity (6- to 30-fold). Taking into account both the potent AHH inducibility and the high bioaccumulation of these compounds, 2,3,7,8-tetra- and 2,3,4,7,8-penta-CDF should be given due attention with regard to environmental-related factors and the possibility of involvement in the etiology of "yusho" disease.

Physiological model for the pharmacokinetics of 2,3,7,8-tetrachlorodibenzofuran in several species

A flow-limited physiological model was developed to describe the time course of 2,3,7,8-tetrachlorodibenzofuran (TCDF) in the blood and tissues of rats, mice, and monkeys. The liver showed the greatest tendency to concentrate the material with tissue-to-blood distribution coefficients ranging from 30 in the monkey to 130 in the mouse. TCDF was also concentrated in the fat with tissue-to-blood distribution coefficients between 25 and 40 in all species. TCDF was eliminated by metabolism followed by excretion primarily to the feces. Urinary excretion was a minor route of elimination in all species. Metabolism was modeled as a linear process occurring in the liver. Intrinsic metabolic clearances ranged from 0.45 ml/min/kg in the monkey to 2.8 ml/min/kg in one species of mice. Fecal excretion of TCDF-derived radioactivity can be simulated with a series of well-mixed compartments which receive input of metabolites in the bile.

Liver morphology in guinea pigs administered either pyrolysis products of a polychlorinated biphenyl transformer fluid or 2,3,7,8-tetrachlorodibenzo-p-dioxin

A transformer cooled and insulated with a mixture of 65% Aroclor 1254 and 35% chlorinated benzenes located in the Binghamton State Office Building in Binghamton, New York, was involved in a fire, which produced soot containing polychlorinated biphenyls, biphenylenes, dioxins, and dibenzofurans. A single dose of either soot or 2,3,7,8-tetrachlorodibenzo-p-dioxin in aqueous methyl cellulose was administered by gavage to Hartley guinea pigs of both sexes. The liver tissue was examined 42 days after administration. By light microscopy hypertrophy of hepatocytes, steatosis, focal necrosis, and cytoplasmic hyalin-like bodies were observed as a result of both treatments. Bile duct proliferation (adenofibrosis) was observed only in the guinea pig groups administered soot. These animals also showed proliferation of the smooth endoplasmic reticulum, concentric membrane arrays (CMA), mitochondrial alterations, decreased rough endoplasmic reticulum, and autophagolysosomes by electron microscopy. The CMAs, which corresponded to the hyalin-like bodies, surrounded lipid droplets and cytoplasmic matrix containing mitochondria and degenerating organelles.

Induction of porphyria in the rat by chronic versus acute exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin

Chronic oral administration of 1 microgram . kg-1 . week-1 of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) to female rats for 16 weeks resulted in hepatic porphyria. In contrast, administration of single oral doses as high as 30 micrograms/kg did not produce porphyria, either acutely or 16 weeks later. Activities of hepatic drug-metabolizing enzymes [aryl hydrocarbon hydroxylase (AHH) and glucuronyl transferase] were increased by chronic oral doses of TCDD as low as 0.01 microgram . kg-1 . week-1. When animals were dosed with TCDD chronically and then allowed to recover for 6 months, AHH and glucuronyl transferase activities returned toward normal (98 and 86% recovery). However, animals showed only partial recovery from TCDD-induced porphyria. Hepatic porphyrin levels did decrease during this period, but urinary porphyrins and the rate-limiting enzyme in porphyrin synthesis, delta-aminolevulinic acid synthetase, remained maximally elevated during the 6-month recovery period. It is concluded that single doses of TCDD do not produce porphyria in the rat, but that TCDD is porphyrogenic when given chronically. Moreover, when TCDD administration is stopped, recovery from the porphyrogenic effects of TCDD is very slow and does not correlate with the biological half-life of TCDD in the rat.

Mutagenicity testing of chlorinated biphenyls and chlorinated dibenzofurans

4 chlorinated biphenyl and 5 chlorinated dibenzofuran compounds have been evaluated in the reversion assay developed by B.N Ames using Salmonella typhimurium histidine auxotrophs. All these compounds (2,4,2'-4'-tetrachlorobiphenyl, 3,4,3',4'-tetrachlorobiphenyl, 4-chlorobiphenyl, 2,4,,6,2',4',6'-hexachlorobiphenyl, dibenzofuran, 2,9-dichlorodibenzofuran, 3,6-dichlorodibenzofuran, 2,3,7,8-tetrachlorodibenzofuran and octachlorodibenzofuran) were nonmutagenic for strains TA98 and TA100 when tested over a 3-log dose range. They were also not mutagenic whether or not varying concentrations of microsomal extracts (S9) from uninduced rats or from rats induced by several methods were included in the experimental protocol.

Dermatological findings in capacitor manufacturing workers exposed to dielectric fluids containing polychlorinated biphenyls (PCBs)

Significant occupational exposure to polychlorinated biphenyls (PCBs) may occur in the manufacturing of capacitors and transformers, in which PCBs are used as electrical insulators. Reports of adverse health effects resulting from PCB exposure have come primarily from an incident resulting from the accidental ingestion of contaminated rice oil in Japan in 1968 ("yusho"). Dermatological findings were prominent features and included pigmentation disturbances and chloracne. To evaluate the dermatological effects of long-term occupational exposure to PCBs, a cross-sectional clinical survey was conducted of 326 capacitor manufacturing workers. A high prevalence (37%) of dermatological abnormalities was found, but typical PCB-associated signs, such as chloracne, were less frequent than among patients with "yusho," despite high concentrations of plasma PCB. As association between dermatological signs and plasma levels of higher homologues of PCBs was suggested, but contaminants which have been reported to be present in commercial PCB mixtures (polychlorinated dibenzofurans) should be considered an etiologic factor or co-factor in the development of "PCB-associated" dermatological findings.

Effects of polychlorinated biphenyls on liver regeneration in the rat: influence of position and degree of chlorination

The effects of PCBs, administered intragastrically, were studied on partially hepatectomized (70%) rats. Seven days after hepatectomy, a relationship was noted between the increase in the degree of chlorination of the biphenyl molecule and the hypertrophy and lipid accumulation in the liver. When the 3' and 4' positions are chlorinated, the relationship still holds but, for a constant number of chlorine atoms, the intensity of the effects are decreased. Fourteen days after hepatectomy, there was only a significant difference in the case of decachlorobiphenyl and Phenoclor DP5, for which the hypertrophy is accompanied by hyperplasia. The relationships are discussed between the chemical structure of the PCBs, their metabolization, their toxicity, and the reversibility of their effects.

Role of polychlorinated dibenzofuran in yusho (PCB poisoning)

In the blood of 15 patients with yusho or "polychlorinated biphenyl poisoning" that occurred in 1979 in Taiwan, was found polychlorinated dibenzofurans (14 of 15) and polychlorinated quaterphenyls (15 of 15), as well as polychlorinated biphenyls (15 of 15). The mean concentration ratio of these substances was approximately 1 : 160 : 500. Based on the following evidence, we propose that polychlorinated quaterphenyls were major pathogenic substances in the development of yusho: (1) Clinical manifestations and course of yusho patients are disproportionately severe and persistent for the observed blood levels of polychlorinated biphenyls, while patients who were occupationally exposed to pure polychlorinated biphenyls take characteristically mild and benign clinical course despite polychlorinated biphenyl levels often much higher than those noted in yusho patients; (2) Polychlorinated debenzofurans show a marked tendency to accumulate in the liver, which might explain frequent presence of jaundice and other abdominal symptoms in yusho, which are, again, not observed in those with occupational polychlorinated biphenyl poisoning; (3) Toxicity of polychlorinated dibenzofurans is a hundred to ten thousand times greater than that of polychlorinated biphenyls and polychlorinated quaterphenyls in animal experiments.