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 g/kg; a PCB mixture was given in a dose of 50 mg/kg. The order of AHH inducing ability was TCDD > PCDFs 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.A part of this work was presented at the 51st annual meeting of the Japanese Society for Hygiene, May 1–3, 1981, Sapporo, Japan and the 52nd annual meeting of the Japanese Society for Hygiene, March 29–31, 1982, Tokyo, Japan     

Augmented atherogenesis in ApoE-null mice co-exposed to polychlorinated biphenyls and 2,3,7,8-tetrachlorodibenzo-p-dioxin

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) and polychlorinated biphenyls (PCBs) are persistent organic pollutants found as complex mixtures in the environment throughout the world. Therefore, humans are ubiquitously and simultaneously exposed to TCDD and PCBs. TCDD and PCBs alone have been linked to atherosclerosis. However, the effects of interactions or synergism between TCDD and PCBs on atherogenesis are unknown. We investigated the possible enhanced atherogenesis by co-exposure to TCDD and PCBs and the potential mechanism(s) involved in this enhancement. Male ApoE^−/− mice were exposed to TCDD (15 μg/kg) and Aroclor1254 (55 mg/kg, a representative mixture of PCBs) alone or in combination by intraperitoneal injection four times over six weeks of duration. Our results showed that mice exposed to TCDD alone, but not Aroclor1254 alone, developed atherosclerotic lesions. Moreover, we found that atherosclerotic disease was exacerbated to the greatest extent in mice co-exposed to TCDD and Aroclor1254. The enhanced lesions correlated with several pro-atherogenic changes, including a marked increase in the accumulation of the platelet-derived chemokine PF4, and the expression of the proinflammatory cytokine MCP-1 and the critical immunity gene-RIG-I. Our data demonstrated that co-exposure to TCDD and Aroclor1254 markedly enhanced atherogenesis in ApoE^−/− mice. Significantly, our observations suggest that combined exposure to TCDD and PCBs may be a greater cardiovascular health risk than previously anticipated from individual studies.     

Elevation of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) polychlorinated biphenyls. Structure-activity relationships

Administration of the commercial polychlorinated biphenyl (PCB) Aroclor 1254 to immature male Wistar rats resulted in increased levels (80-110%) of the 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) hepatic cytosolic receptor protein which remained elevated for 14 days. The effects of structure on the activity of individual PCB congeners to modulate hepatic cytosolic receptor levels were compared to the structure-activity relationships (SARs) which have been developed previously for PCBs as inducers of hepatic microsomal monooxygenases. 3,3',4,4'-Tetra- and 3,3',4,4',5-pentachlorobiphenyl induced the cytochrome P-448-dependent monooxygenase, ethoxyresorufin O-deethylase (EROD), and resembled 3-methylcholanthrene in their mode of monooxygenase enzyme induction. These congeners also bound to the receptor protein; however, neither compound increased hepatic cytosolic receptor protein levels. Several PCB congeners which exhibit low binding affinities for the cytosolic receptor protein resembled phenobarbitone (PB) in their mode of monooxygenase enzyme induction and, like PB, elevated cytosolic receptor protein levels. Nevertheless, a comparison of the time course of monooxygenase enzyme induction and receptor protein elevation by 2,2',4,4',5,5'-hexachlorobiphenyl and PB illustrated significant differences in their activities. PB-mediated elevation of receptor levels was maximized 24 hr after the last dose, and 48 hr later the receptor levels decreased to control values. In contrast, 5 days after administration of a single dose of 2,2',4,4',5,5'-hexachlorobiphenyl (300 mumoles/kg) the receptor levels were elevated significantly, and these increased levels (205-127% increases over control) persisted for 14 days. There was no correlation between increased levels of hepatic receptor protein and the induction of the cytochrome P-450-dependent monooxygenases, aldrin epoxidase or 4-dimethylaminoantipyrine N-demethylase. Two PCBs, 2,3,3',4,4',5- and 2,2',3,4,4',5-hexachlorobiphenyl, which resembled Aroclor 1254 in their mode of monooxygenase enzyme induction, also elevated hepatic receptor protein levels but were less active than the PB-type inducers. Thus, the SARs developed for PCBs which elevate cytosolic receptor levels demonstrate that the most active compounds exhibit the lowest affinity for the receptor protein and do not induce EROD. In contrast, the more toxic PCB congeners which are approximate isostereomers of 2,3,7,8-TCDD both induced EROD and bound with high affinity to the receptor protein but did not increase hepatic cytosolic receptor protein levels.     

Absorption of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) after low dose dermal exposure

Human dermal exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) occurs through contact with soil and paper products. In a previous study, relative percutaneous absorption of TCDD increased as the dose decreased (Brewster et al., 1989). To determine the rate of absorption of a low dose of TCDD, absorption, distribution, and elimination were examined at 1, 4, 8, 12, 24, 48, 72, and 120 hr after dermal application of 200 pmol (111 pmol/cm2) [3H]TCDD to 10-week-old male Fischer 344 rats. The compound was applied over a 1.8 cm2 area of the interscapular region of the back in 60 microliters acetone and covered with a perforated cap; animals were held in individual metabolism cages. Within 120 hr after dosing, 82 pmol (26 ng) of TCDD was absorbed. Absorption kinetics appeared to be first-order; the absorption rate constant was 0.005 hr-1. At each time point, greater than 70% of the radioactivity detected in the application site could be removed by swabbing with acetone. The time-related increase in the amount of TCDD in liver and fat closely paralleled the amount absorbed, while the percentage of the administered dose detected in the blood was never greater than 0.3%. Thus, absorption of a low dose of TCDD through the skin is extremely slow and appears to be a first-order process.     

Percutaneous absorption of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) from soil

Eight dermal absorption experiments (two in vivo; six in vitro) and one intravenous experiment were conducted using 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) either neat (high dose at approximately 250 microg/cm(2) and low dose at 10 ng/cm(2)) or sorbed on a low organic soil (LOS) or high organic soil (HOS) at 1 ppm (10 ng TCDD/10 mg soil/cm(2)). After 96 h the percent of applied dose absorbed (PADA) for the neat low dose was 78% in vivo (rat) and 76% in vitro (rat). PADA for the equivalent TCDD dose sorbed on LOS were 16.3% (rat in vivo), 7.7% (rat in vitro) and 2.4% (human in vitro). The PADA for TCDD sorbed on HOS (1 ppm) was 1.0% (rat in vitro). Generally, rat skin was observed to be three to four times more permeable to TCDD than human skin. At steady state, the dermal flux of TCDD in neat form, sorbed on LOS at 1 ppm, and sorbed on HOS at 1 ppm (all in vitro, rat) was 120, 0.007, and 0.0007 ng/cm(2)/h, respectively (ratio = 1.7 x 10(5):10:1). Making adjustments to account for differences between in vitro and in vivo results and adjusting for application to monolayer loads, the 24-h TCDD absorption for human skin is estimated as 1.9% from LOS (1 ppm) and 0.24% from HOS (1 ppm).     

Dose-response immunotoxicities of commercial polychlorinated biphenyls (PCBs) and their interaction with 2,3,7,8-tetrachlorodibenzo-p-dioxin

The relative potencies of the commercial polychlorinated biphenyl (PCB) mixtures Aroclors 1260, 1254, 1248, 1242, 1016 and 1232 to inhibit the murine splenic plaque-forming cell response to sheep red blood cells was determined by dose-response treatment of C57BL/6 mice followed by logit plot analysis of the data. The ED50 values obtained for Aroclors 1260, 1254, 1248, 1242, 1016 and 1232 were 104, 118, 190, 391, 408 and 464 mg/kg or 0.28, 0.35, 0.66, 1.5, 1.5 and 2.0 mmol/kg, respectively. It was apparent that the higher chlorinated PCB preparations (Aroclors 1260, 1254 and 1248) were more potent than the lower chlorinated preparations (Aroclors 1242, 1016 and 1232). Previous studies have shown that the interaction of a subeffective dose of Aroclor 1254 (25 mg/kg) with an immunotoxic dose (3.7 nmol/kg) of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) resulted in significant antagonism of the toxicity of the latter compound. Co-treatment of mice with a 25 mg/kg dose of all the commercial Aroclors and with a 50 mg/kg dose of a reconstituted PCB mixture (resembling a PCB extract from human milk) with TCDD (3.7 nmol/kg) showed that, with the exception of Aroclor 1232, all of the commercial PCBs and the reconstituted PCB mixture significantly antagonized the TCDD-mediated inhibition of the splenic plaque-forming cell response in C57BL/6 mice. The identities of the PCB congeners responsible for this antagonism and the mechanism of this process are unknown and are currently being investigated.     

Inhibition of intestinal glucose absorption in rats treated with 2,3,7,8-tetrachlorodibenzo-p-dioxin.

Male Sprague-Dawley rats were injected with either 125 micrograms 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)/kg or vehicle (pair-fed and ad libitum-fed controls). Transfer of water, electrolytes and D-glucose as well as fats of a tracer dose of the non-metabolizable radioactive marker 3-O-methyl-D-[U-14C]glucose was studied in isolated perfused jejunal segments 1, 2, 7, and 21 d after treatment (TCDD-treated and pair-fed control rats) and after 26 d in ad libitum-fed controls. TCDD-treated rats demonstrated reduced feed consumption and loss of body weight. Active intestinal absorption of glucose was significantly inhibited 30 and 22% compared to pair-fed controls, respectively 2 and 7 d after TCDD treatment. After 21 d the inhibition (14%) was less significant. There were no differences in glucose transfer between severely starved pair-fed controls (body weights 370 +/- 26 g) and ad libitum-fed rats (body weights 512 +/- 15 g). Water absorption and transfer of sodium and calcium was not influenced by TCDD treatment. However, a significant increase of potassium transfer was observed in parallel with impaired glucose absorption. The uptake of 3-O-methylglucose into mucosal tissue was not impaired, whereas the transfer to the serosal side was significantly inhibited by 30-60% compared to pair-fed as well as ad libitum-fed animals from day 2 until the end of the experiment. These results suggest that TCDD is involved in an inhibition of glucose transport at the basolateral membrane.     

Effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin on the distribution and biliary excretion of polychlorinated biphenyls in rats.

Plasma disappearance, biliary excretion, and tissue distribution of two polychlorinated biphenyls (PCBs), 2,5,2′,5′-[³H]tetrachlorobiphenyl (4-CB) and 2,4,5,2′,4′,5′-[³H]hexachlorobiphenyl (6-CB), was determined in rats 10 days after oral administration of a single 10 or 25 μg/kg dose of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Plasma disappearance of both PCBs was not altered by TCDD treatment, but biliary excretion was depressed. Associated with the depressed excretion was a reduction in bile flow and concentration of 4-CB- and 6-CB-derived ³H in bile. Treatment with TCDD resulted in less PCB being distributed to the skin and a greater percentage of the dose being accumulated in the liver. The content of PCB-derived ³H in skeletal muscle, adipose tissue, and urine was similar in control and TCDD-treated rats. Extraction of bile with hexane showed that the majority of biliary radioactivity was in the form of polar metabolites and that the proportion of parent PCB (hexane-extractable radioactivity) to polar metabolites was not altered by TCDD treatment. In rats given 4-CB and sacrificed 1 hr later, the majority of radioactivity in the liver was hexane extractable, and the smaller amount of hepatic radioactivity due to polar 4-CB metabolites was greater in the TCDD treatment group than in the control group. When biliary metabolites of 4-CB were administered, biliary excretion of the metabolites was depressed in TCDD-treated animals. Thus, TCDD treatment impairs the initial and main excretory pathway for PCB elimination in the rat—biliary excretion—and alters the distribution of PCBs to the skin and liver.     

Genetically mediated induction of aryl hydrocarbon hydroxylase activity in mice by polychlorinated dibenzofuran isomers and 2,3,7,8-tetrachlorodibenzo-p-dioxin

Hepatic aryl hydrocarbon hydroxylase (AHH)-inducing potency of toxic polychlorinated aromatic hydrocarbons such as polychlorinated dibenzofurans (PCDFs), 3,4,5,3,4,5-hexachlorobiphenyl (HCB) and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was studied in four inbred strains of mice with different phenotypes of Ah locus, i.e., AHH-responsive strains: C57BL/6N and AKR/Ms Qdj, and AHH-nonresponsive strains: DBA/2Cr Slc and Qdj; DDD. Eight individual PCDF isomers or TCDD were administered IP in doses of 30 g/kg; HCB was given in a dose of 120 g/kg. In AHH-nonresponsive strains of mice, only TCDD significantly induced hepatic AHH activity, while in AHH-responsive strains, 2,3,7,8-tetrachlorodibenzofuran(2,3,7,8-TCDF), 1,2,3,7,8-pentachlorodibenzofuran(1,2,3,7,8-PCDF) 2, 3, 4, 7, 8-pentachlorodibenzofuran (2, 3,4, 7, 8-PCDF), and TCDD significantly enhanced the enzyme activity, and the induced AHH activities with the three PCDF isomers were about 30–65% of those of TCDD. These results indicate that AHH responsiveness in mice segregates with the induction of AHH activity by PCDF isomers and may also segregate with the toxic potency of the isomers; i.e., toxic potencies of 2,3,7,8-TCDF, 1,2,3,7,8-PCDF, and 2,3,4,7,8-PCDF in AHH-responsive strains of mice may be much greater than those in AHH-nonresponsive strains of mice. Taking into account both the potent AHH inducibility and the high bioaccumulation of 2,3,7,8-TCDF, 1,2,3,7,8-PCDF, and 2,3,4,7,8-PCDF, these three PCDF isomers should be given greater attention with regard to environmental contamination.A part of this work was presented at the 41st annual meeting of the Japanese Society of Public Health, October 27–29, 1982, Fukuoka, Japan.     

Pharmacokinetics and biological activity of 2,3,7,8-tetrachlorodibenzo-p-dioxin

Concentrations of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in rat liver and adipose tissue, and hepatic ethoxyresorufin O-deethylase (EROD) activity were studied subsequent to a single subcutaneous injection of TCDD. Two types of experiments were performed to study: (a) time-dependent changes following a single injection of 300 ng TCDD/kg body wt (points 1-4), and (b) dose-dependent changes measurable after 7 days following a single injection (points 5-7). 1. Absorption of TCDD following a single subcutaneous injection was about 90% after 3 days and 98% after 5 days. 2. Following a single dose of 300 ng TCDD/kg body wt peak concentrations were: liver (after 3 days): 4.7 +/- 0.9 ng/g wet wt, and adipose tissue (after 7 days): 0.82 +/- 0.07 ng/g wet wt. 3. T1/2 of TCDD in liver was 13.6 days over the total experimental period (from day 10 to 91 of the study), apparently with an initial faster phase: 11.5 days (from day 10 to 49), and a slower period at the end of the experiment: 16.9 days (from day 49 to 91); in adipose tissue the t1/2 was 24.5 days (from day 14 to 91 of the study). 4. Maximum induction of EROD in the liver was observed (14-fold at 300 ng TCDD/kg body wt) 3-7 days following the injection; the activity was decreased to about one third of the maximum 3 weeks after the injection; increase in total cytochrome P-450 at this dose was only about 1.4-fold at the induction maximum. 5. The ratio of the TCDD concentrations in liver and adipose tissue increased considerably between doses of 3 ng TCDD/kg body wt (ratio: about 0.74) and 3000 ng TCDD/kg body wt (ratio: about 7.7). 6. The extent of EROD induction in the liver increased dose dependently. A significant effect was first observed with a dose of 3 ng TCDD/kg body wt (activity about +32% above control activity). The corresponding tissue concentration was about 10 pg TCDD/g liver wet wt. 7. An almost perfect linear relationship exists (when using a double-log plot) between the hepatic TCDD concentration and the EROD activity for tissue concentrations ranging from 40 to 30,000 pg TCDD/g wet wt.     

Pharmacokinetics and biological activity of 2,3,7,8-tetrachlorodibenzo-p-dioxin

Wistar rats were treated initially with very high single doses of ¹⁴C-2,3,7,8-TCDD (either 75 or 25 g/kg body wt) followed by weekly maintenance doses of 15 and 5 g/kg body wt, respectively. ¹⁴C-radioactivity was measured in various organs over a period of 22 weeks. 1) 75 g TCDD/kg body wt (followed by the maintenance doses) was lethal for all the rats within a period of 9 weeks. While the concentration of ¹⁴C-TCDD equivalents in liver and thymus stayed reasonably constant during this period in the surviving rats, the concentration in adipose tissue and kidneys clearly increased in the same animals. 2) The dose of 25 g TCDD/kg body wt (followed by weekly doses of 5 g/kg body wt) proved to be a just tolerable dose over a period of 22 weeks for our strain of rats. 3) Within the individual variabilities the TCDD concentrations in the investigated organs showed no clear-cut decline, indicating that the animals were exposed to fairly constant levels of TCDD throughout the study. Thus, this dosing regime is suitable for maintaining constant TCDD exposure during long-term studies.Abbreviations TCDD 2,3,7,8-tetrachlorodibenzo-p-dioxin     

Reproductive toxicity and pharmacokinetics of 2,3,7,8-tetrachlorodibenzo-p-dioxin

A study on the reproductive toxicity of ¹⁴C-TCDD in male rats was performed. Two dose regimes were applied subcutaneously: TCDD-25 (initial dose: 25 g/kg body wt; maintenance dose: 5 g/kg body wt) and TCDD-75 (initial dose: 75 g/kg body wt; maintenance dose: 15 g/kg body wt); the maintenance dose was administered once weekly. The rats were treated for 10 weeks before they were mated and throughout the entire mating period. The dose regime TCDD-75 led to a mortality rate of 93% within a period of 16 weeks. The first animals died during 4 weeks, and an LD₅₀ was reached after 8 weeks. The dose regime TCDD-25 did not cause any mortality over a period of 12 weeks; but an LD₁₀ was reached within 13–20 weeks. The body weight was significantly decreased in both groups treated with TCDD after 1 week of treatment. It stabilized in the TCDD-25-group 4 weeks after treatment and stayed at this level until the end of the treatment period. The most significant finding is the delayed fertilization by the treated males; 15% of the males were found to be sterile. The mating index (84%) and fertility index (14 ± 11 days) of the TCDD-25-group were lower when compared with controls (95%, 8 ± 5), but the pregnancy index was not reduced. Application of the chosen TCDD doses led to clear-cut morphological changes of the testes. The Sertoli cells were changed (increased occurrence of vacuoles, swelling of endoplasmatic cavities), and the contact between the Sertoli cells and spermatogonia was disturbed, which might indicate an inhibited maturation of spermatozoa percursors.Abbreviations TCDD 2,3,7,8-tetrachlorodibenzo-p-dioxin     

Reproductive toxicity and toxicokinetics of 2,3,7,8-tetrachlorodibenzo-p-dioxin

Possible effects on the next generation after long-term exposure (subcutaneous administration) of male rats to very high doses of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) were studied. Two dose regimes were applied: TCDD-25 (initial dose: 25 g/kg body wt; maintenance dose: 5 g/kg body wt, once weekly) and TCDD-75 (initial dose: 75 g/kg body wt; maintenance dose: 15 g/kg body wt). Male rats were treated for 10 weeks before mating and then throughout the entire 12 week mating period. They were mated to unexposed virgin females. One group of pregnant females was used for teratological evaluations, and another group was allowed to deliver. No significant differences were observed in the number of implantations or fetuses per litter, and resorption rate, and fetal weight between the controls and TCDD-treated groups. No gross-structural anomalies occurred in any of the fetuses sired by TCDD-treated males. In the TCDD-25 group an increased frequency of two types of variations was observed which also occur in controls: incompletely ossified fingers (TCDD-25=5.1%, controls=2.6%), and incompletely ossified ossa zygomatica (TCDD-25=1.8%, controls=0.5%). In the TCDD-25 group a slight but statistically significant increase was observed in the rate of stillbirths (TCDD-25=1.3%, controls=0.1%), apparently due to an unusually low frequency occurring in the controls (overall historical controls=0.6%). There was no difference in postnatal mortality (TCDD-25=1.3%, controls=1.3%). Taken together, despite the very high doses of TCDD used, the data do not provide evidence for biologically significant paternally-mediated developmental toxicity in the fetuses and newborn.     

Reproductive toxicity and toxicokinetics of 2,3,7,8-tetrachlorodibenzo-p-dioxin

The effects of a single dose of TCDD on the testis were studied in rats. The animals were treated (subcutaneously) once with TCDD doses of 0, 0.5, 1.0, 3.0, 5.0 g/kg body weight. Doses of 3.0 or 5.0 g TCDD/kg reduced the number of spermatids/testis significantly (60% of the controls). Electron microscopic inspection revealed that both doses led to a dissolution on the germinal epithelium. Altered germ cells at all developmental stages occurred in all testes evaluated. Doses of 0.5 or 1.0 g TCDD/kg did not induce any effects in the testis; therefore, under these experimental conditions of single exposure to rats the dose of 1.0 g TCDD/kg can be considered as NOAEL.     

Comparative activities of 2,3,7,8-tetrachlorodibenzo-p-dioxin and progesterone as antiestrogens in the female rat uterus

The comparative antiestrogenic effects of progesterone and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on cytosolic and nuclear estrogen (ERc and ERn, respectively) and progesterone (PRc and PRn, respectively) receptor levels were determined in female Long Evans rats. Estradiol treatment typically increases ER and PR levels in target cells or tissues and these proteins have been proposed as markers of estrogen action. 2,3,7,8-TCDD causes a dose-dependent decrease in uterine ERc, ERn, PRc, and PRn levels which persist up to 7 days. Progesterone treatment caused significant decreases in uterine ERc, ERn, and PRn levels; however, after 7 days, the effects of the hormone on receptor levels were diminished. The effects of 2,3,7,8-TCDD and progesterone on hepatic ER and PR levels were comparable to those observed in the uterus. Treatment of the rats with estradiol (5 micrograms/kg), estradiol (5 micrograms/kg) plus progesterone (1 mg/animal), or 2,3,7,8-TCDD (80 micrograms/kg) showed that both progesterone and 2,3,7,8-TCDD significantly antagonized the estradiol-mediated increases in uterine (and hepatic) ERc, ERn, PRc, and PRn levels and for 2,3,7,8-TCDD the decreased receptor levels persisted for up to 7 days. In vitro studies with freshly isolated uterine strips demonstrated that both 2,3,7,8-TCDD and progesterone antagonized the estradiol-mediated increases in ER and PR levels. Previous studies suggest that the antiestrogenic activity of progesterone is due, in part, to the induction of proteins which are involved in decreasing ERn levels in target cells. Moreover in the uterine strip assay procedure, it was previously shown and reproduced in this study that the decrease in uterine ERn by progesterone was inhibited by both protein and RNA synthesis inhibitors over a 4-hr incubation period. In contrast, the 2,3,7,8-TCDD-mediated decrease in uterine ERn was inhibited only by actinomycin D and not by cycloheximide or puromycin. These in vitro studies thus confirm that both progesterone and 2,3,7,8-TCDD exhibit comparable antiestrogenic effects in vivo and in vitro; however, the results suggest that these effects are expressed through different mechanisms.     

Comparative developmental toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin in the hamster, rat and guinea pig

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is a persistent environmental contaminant capable of causing a wide variety of adverse health effects including teratogenesis and altered development. The objective of this study was to compare the developmental toxicity of TCDD in the hamster, rat and guinea pig, which in mature animals exhibit a relatively low, medium and high sensitivity to TCDD, respectively. A single oral dose of TCDD was administered to pregnant rats (0, 1.5, 3.0, 6.0 or 18.0microg/kg) on gestation day 10, pregnant hamsters (0, 1.5, 3.0, 6.0 or 18.0microg/kg) on gestation day 9 and pregnant guinea pigs (0, 0.15 or 1.5microg/kg) on gestation day 14 with fetal analysis on gestation day 20, 15 and 56, respectively. The developmental toxicity of TCDD in the three species included increased fetal mortality, alterations to fetal body weight, body length, organ weight and significant changes to the fetal white blood cell differential counts. Additionally, teratogenic responses were observed in the hamster and rat consisting of cleft palate, kidney congestion, hydronephrosis and intestinal hemorrhaging. Furthermore, the results from this study demonstrate that despite the up to 5000-fold interspecies variability to the acute lethal potency of TCDD observed in mature guinea pigs, rats and hamsters, the developing fetus is uniquely vulnerable to gestational TCDD exposure and displays approximately a 10-fold variability in fetal lethal potency in these species. Together, these results will assist efforts to reduce the uncertainty in the risk assessment for TCDD in sensitive populations, such as the developing embryo and fetus.     

Dose-response analysis of short-term effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin in three differentially susceptible rat lines

Line A, B, and C rats were selectively bred from TCDD-resistant Han/Wistar (Kuopio; H/W) and TCDD-sensitive Long-Evans (Turku/AB; L-E) rats. Line A rats are the most resistant to TCDD acute lethality followed by line B and line C rats. The resistance in line A rats is associated with a mutated H/W-type aryl hydrocarbon receptor (Ahr) allele (Ahr(hw)) and in line B rats the resistance is associated with an allele of an unknown gene B (B(hw)), while line C rats are almost as sensitive to TCDD as L-E rats. The dose-responses of characteristic short-term effects (day 8 postexposure) of TCDD were used to evaluate the efficacy (magnitude of effect) and potency relationships between these lines. Line A rats showed similar efficacies as line C (line A:line C efficacy ratio more than 0.7) for thymus weight, EROD activity, and incisor tooth defects. In contrast, efficacies in line A were decreased (efficacy ratios 0.19-0.37) for body weight change, serum bilirubin, and FFA levels, and serum ASAT activity. For most endpoints the efficacies in line B rats seem to be lower than in line C rats. The potencies were close to each other in line A and B rats, but somewhat lower than in line C rats. The results support our previous concept of two different AHR-mediated signaling pathways leading to dioxin type I and type II endpoints. Rats with the Ahr(hw/hw) genotype show a markedly decreased efficacy for type II endpoints, but B(hw) allele had only a minor effect on efficacies for most endpoints. Both H/W-type resistance alleles also decreased the potency of TCDD. However, the potency differences in short-term toxicity seem not to explain, at least alone, the differences seen in acute lethality among the rat lines.     

Genetically mediated induction of aryl hydrocarbon hydroxylase activity in human lymphoblastoid cells by polychlorinated dibenzofuran isomers and 2,3,7,8-tetrachlorodibenzo-p-dioxin

Aryl hydrocarbon hydroxylase(AHH)-inducing potency of toxic polychlorinated aromatic hydrocarbons such as polychlorinated dibenzofuran (PCDF) isomers, 3,4,5,3,4,5-hexachlorobiphenyl (HCB) and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was investigated in human lymphoblastoid cell lines with different AHH inducibility for 3-methylcholanthrene (3-MC) obtained from healthy subjects. Each of the cell lines was treated with eitht individual PCDF isomers, TCDD, and HCB at doses of 1.9–15 ng/ml of culture medium, 1.9–7.5 ng/ml and 95 ng/ml, respectively. Lymphoblastoid cell lines were arbitrarily classified into three groups based on their AHH inducibilities with 3-MC (2.5 M); low (3-MC/ control=I<3), middle (3<=I<6) and high (I>=6). Degrees of the enzyme inducibilities of the organochlorine compounds proportionally increased with those for 3-MC. AHH inducibilities with 2,3,4,7,8-pentachlorodibenzofuran(2,3,4,7,8-PCDF), 1,2,3,4,6,7-hexachlorodibenzofuran(1,2,3.4,6,7-HCDF) and 1,2,3,4,7,8-hexachlorodibenzofuran(1,2,3,4,7,8-HCDF) were comparable to those of TCDD at doses of 7.5 ng/ ml, and about twice as high as those of 2,3,7,8-tetrachlorodibenzofuran (TCDF), at the same dose, HCB, at a dose of 95 ng/ ml, did not induce enzyme activity. The experimental evidence indicated that AHH inducibility by the organochlorine compounds reflected the genetic susceptibility of the cells to the phenomenon of induction, and PCDF isomers found at relatively high concentrations in tissues of mammals exerted the highest values of AHH induction.Part of this work was presented at the 53rd annual meeting of the Japanese Society for Hygiene, April 5–7, 1983, Osaka, Japan     

Teratogenicity of three polychlorinated dibenzofurans in C57BL/6N mice

Polychlorinated dibenzofurans (PCDFs) are widespread environmental contaminants which have been detected in human tissues and implicated in several poisoning incidents. Their toxic effects are similar to those observed with other related halogenated aromatic hydrocarbons such as TCDD. The teratogenic effects of three PCDFs, 1,2,3,7,8-pentachlorodibenzofuran (1-PeCDF), 2,3,4,7,8-pentachlorodibenzofuran (4-PeCDF), and 1,2,3,4,7,8-hexachlorodibenzofuran (HCDF), were assessed in C57BL/6N mice. Pregnant mice were exposed on Gestation Days 10-13 to 10 ml corn oil/kg containing PCDFs. The dams were killed on Gestation Day 18 and maternal and fetal toxicity were assessed. All three compounds were highly teratogenic, with very steep and parallel dose-response curves for the two diagnostic indicators of dioxin-like teratogenicity, hydronephrosis, and cleft palate. 4-PeCDF was the most teratogenic with an ED50 of 36 micrograms/kg for cleft palate and 7 micrograms/kg for hydronephrosis. 4-PeCDF was approximately 4 times as potent as 1-PeCDF and 10 times as potent as HCDF. The teratogenic responses occurred at a dose below that where any obvious maternal or fetal toxicity was detected. Thus, these three compounds cause teratogenic responses similar to those seen with TCDD but are only 1/10 to 1/100 as potent.