Toxicity of chronic exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin in diethylnitrosamine-initiated ovariectomized rats implanted with subcutaneous 17 beta-estradiol pellets.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is a potent hepatocarcinogen in female but not in male rats. Several lines of evidence suggest a key role of ovarian hormones, presumably estrogen, in the mechanism of TCDD-induced hepatocarcinogenesis. The aim of this current study was to determine the toxicity of co-treatment with TCDD and 17 beta-estradiol and assess the efficacy of 90-day subcutaneous constant release 17 beta-estradiol pellets. Ovariectomized (OVX) female Sprague-Dawley rats were initiated with diethylnitrosamine (DEN) and treated with TCDD for 20 or 30 weeks in the presence and absence of 17 beta-estradiol. TCDD concentrations were equivalent in livers of TCDD-treated sham operated and OVX rats following 20 weeks of treatment. Following 30 weeks of TCDD treatment, liver TCDD concentrations were higher in OVX rats than in intact rats. TCDD concentrations in livers of TCDD-treated OVX rats receiving supplemental 17 beta-estradiol were similar to intact rats following either 20 or 30 weeks of treatment. Mean hepatic background TCDD concentrations in untreated rats were 2-fold higher in intact rats compared to OVX rats, regardless of 17-estradiol exposure following 20, but not 30 weeks of treatment. Serum indicators of hepatocellular and hepatobiliary toxicity indicated transient hepatotoxicity in TCDD-treated OVX rats receiving 17 beta-estradiol. Histopathological alterations indicated hepatotoxicity induced by exposure to TCDD following either 20 or 30 weeks of exposure. No excess hepatotoxicity was associated with 17 beta-estradiol-supplementation in TCDD-exposed OVX female Sprague-Dawley rats. Serum 17 beta-estradiol concentrations were not constant and resulted in supra-physiological levels that decreased over time, resulting in target physiological serum 17 beta-estradiol concentrations following several weeks of release. Treatment with 17 beta-estradiol resulted in uterine weights and total body weights comparable to sham-operated female rats. These data confirm the efficacy of supplemental subcutaneous 17 beta-estradiol pellets on the induction of estrogenic responses in TCDD-treated rats and indicate no increased hepatotoxicity associated with 17 beta-estradiol exposure in TCDD-treated rats.     

Physiological implications of estrogen receptor modulation by 2,3,7,8-tetrachlorodibenzo-p-dioxin

The interactions of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) with hormones and hormone receptors have important implications for TCDD toxicity. Evidence suggests that TCDD modulates receptors for glucocorticoids, prolactin, thyroxine, low density lipids, epidermal growth factor, and estrogens. Estrogen receptor modulation and the animal's physiological responses to this modulation appear to be particularly important effects and can explain much of the toxicity observed in TCDD-treated animals. Susceptibility of different species to TCDD correlates with their steroid glucuronidation capacity. Because of the close interactions and interdependent regulation of hormonal systems, other hormones may have a similar role in TCDD toxicity.     

Inhibition of the 17 beta-estradiol-induced and constitutive expression of the cellular protooncogene c-fos by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in the female rat uterus

Acute administration of 17 beta-estradiol (5 micrograms/rat) to 25-day-old female Sprague-Dawley rats resulted in an increase of uterine mRNA for the cellular oncogene c-fos. The c-fos mRNA levels were significantly elevated 12 and 24 h after exposure to the hormone (232 and 164% of control values) and the elevation was not observed after 48 h. In contrast, treatment of the animals with either 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) or 6-methyl-1,3,8-trichlorodibenzofuran (MCDF) resulted in a dose-dependent decrease in constitutive uterine c-fos mRNA levels. In rats co-treated with 17 beta-estradiol plus TCDD or MCDF, it was apparent from the results that the halogenated aromatic hydrocarbons significantly inhibited the estrogen-induced increases in uterine c-fos mRNA levels. These observations further extend the diverse spectrum of antiestrogenic effects caused by TCDD and related compounds and also show an interaction between TCDD and the constitutive expression of the c-fos proto-oncogene in the female rat uterus.     

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.     

Induction of hepatic 8-oxo-deoxyguanosine adducts by 2,3,7,8-tetrachlorodibenzo-p-dioxin in Sprague-Dawley rats is female-specific and estrogen-dependent.

2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) is a hepatocarcinogen that induces sex-specific hepatic neoplastic alterations in female, but not male, rats. It has been hypothesized that TCDD-induced alterations in estrogen metabolism lead to increased generation of reactive oxygen species. The resulting oxidative damage to DNA may contribute to TCDD-induced tumor promotion and hepatocarcinogenesis. This hypothesis is supported by previous observations of increased 8-oxo-deoxyguanosine (8-oxo-dG) adduct formation in the livers of intact, but not ovariectomized (OVX), rats following chronic exposure to TCDD. The aim of the current study was to more clearly define the roles of hormonal regulation, gender, dose-response, and exposure duration in TCDD induction of 8-oxo-dG adducts. Diethylnitrosamine (DEN)-initiated male and female (both intact and OVX) rats were exposed to TCDD in the presence or absence of 17 beta-estradiol. Following 30 weeks of exposure, hepatic 8-oxo-dG adduct levels were significantly higher in TCDD-treated intact female rats, and TCDD-treated OVX female rats receiving supplemental 17 beta-estradiol, when compared to respective corn oil vehicle controls. In DEN-initiated female rats exposed to a range of TCDD concentrations for 30 weeks, TCDD induced 8-oxo-dG adduct levels in a dose-dependent manner. However, 8-oxo-dG adduct levels were not altered in TCDD-treated male or OVX female rats following 30 weeks of exposure. In noninitiated female rats, the level of 8-oxo-dG adducts 4 days following a single dose of TCDD was not significantly different than in control rats. Additionally, 8-oxo-dG adduct formation was not affected by exposure to TCDD for 20 weeks in intact female rats. These data suggest that the induction of 8-oxo-dG adduct levels by TCDD is likely a response to chronic oxidative imbalance. These studies provide strong evidence that the induction of 8-oxo-dG by TCDD occurs via a chronic, sex-specific, estrogen-dependent mechanism.     

Alterations in splenocyte protein kinase C (PKC) activity by 2,3,7,8-tetrachlorodibenzo-p-dioxin in vivo

The effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on growth factor-coupled activation of nuclear protein kinase C (nPKC) and on the subcellular distribution of PKC activity in rat splenocytes were investigated. Seven days after a single injection of TCDD (50 μg/kg body weight), cytosolic and particulate PKC activity was significantly higher in splenocytes from TCDD-treated rats or pair-fed control rats compared to ad libitum-fed animals. In a separate experiment, purified splenocyte nuclei from TCDD-treated animals and controls were used to study activation of nPKC by growth factors and other trophic agents. Growth factor-stimulated nPKC activation was attenuated in splenic nuclei from TCDD-treated rats compared to vehicle-treated controls. Evidence presented here suggests that the cellular mechanism of TCDD toxicity leading to immunosuppression in rodents may be mediated in part by uncoupling of growth factor receptors linked to PKC activation at the level of the nucleus. However, changes in total splenocyte PKC activity appear to be correlated with hypophagia since cytosolic and particulate PKC levels were elevated in TCDD-treated rats and their pair-fed partners.     

Effect of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on tryptophan and glucose homeostasis in the most TCDD-susceptible and the most TCDD-resistant species,guinea pigs and hamsters

 We have previously reported that in rats 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) lethality is associated (although not necessarily causally) with changes in brain serotonin (5-HT) metabolism. In the present study, we have examined whether this holds for other species by comparing the effect of TCDD in the most TCDD-susceptible and the most TCDD-resistant species, guinea pigs and hamsters, respectively. Body weight gain of guinea pigs exposed to TCDD (0.3–2.7 μg/kg) diminished dose dependently, while the effect was marginal in hamsters (900–4600 μg/kg). Brain 5-hydroxyindoleacetic acid (the main metabolite of brain 5-HT), brain tryptophan (the precursor amino acid of 5-HT), and plasma free and total tryptophan were not affected at any dose in guinea pigs. In contrast, 4 days after exposure, the levels of plasma free and total tryptophan were consistently increased in hamsters. These, as well as brain tryptophan, were still elevated 10 days after exposure. TCDD did not affect plasma glucose level in either species. Liver glycogen was decreased in a dose-dependent manner in TCDD-treated guinea pigs as well as in their pair-fed controls on day 10. There was no change in liver glycogen in hamsters. The activity of the gluconeogenic enzyme, phosphoenolpyruvate carboxykinase was only depressed in hamsters by all doses of TCDD. We conclude that changes in tryptophan metabolism or in carbohydrate homeostasis cannot explain the wide interspecies differences in susceptibility to the acute lethality of TCDD, although they may correlate with some aspects of its toxicity in certain species. Received: 12 January 1995 / Accepted: 27 February 1995     

Effect of monooxygenase inducers and inhibitors on the hepatic metabolism of 2,3,7,8-tetrachlorodibenzo-p-dioxin in the rat and hamster

The rat and hamster exhibit about a 100-fold difference in sensitivity to the acute toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), with the hamster representing the most resistant species examined to date. The present study compared the induction and inhibition of hepatic TCDD metabolism in these species using suspensions of isolated hepatocytes. Purified 14C-TCDD or 3H-TCDD (2.2 microM) was incubated for 2-6 hr with hepatocytes isolated from untreated, TCDD-pretreated (5 micrograms/kg, ip), 3-methylcholanthrene-pretreated (3-MC, 50 mg/kg, ip, x 3 days), isosafrole-pretreated (ISO, 150 mg/kg, ip, x 3 days), or phenobarbital-pretreated (PB, 80 mg/kg, ip, x 3 days) rats and hamsters. Untreated rat and hamster hepatocytes metabolized TCDD at a similar rate (0.20 and 0.18 pmol/hr/mg, respectively). In both species, TCDD and 3-MC pretreatments elevated the rate of TCDD metabolism by 5-6-fold, while PB pretreatment had no effect. isosafrole modestly increased (1.8-2.5-fold) TCDD metabolism in each species. Analysis by high performance liquid chromatography indicated similarities in the TCDD-metabolite profiles formed by hepatocytes from both species, with two major metabolite peaks detected following induction by TCDD and 3-MC. The in vitro metabolism of TCDD in hepatocytes from TCDD-pretreated rats and hamsters was inhibited by 7,8-benzoflavone (100 microM), but not by metyrapone (100 microM). The effect of these cytochrome P-450 inducers and inhibitors on the metabolism of 3H-benzo(a)pyrene (BaP) in rat hepatocytes was similar to their effect on TCDD metabolism. However, marked differences were observed in their effects on the metabolism of BaP and TCDD in hamster hepatocytes.(ABSTRACT TRUNCATED AT 250 WORDS)     

Changes in thyroid hormones and thyroxine glucuronidation in hamsters compared with rats following treatment with 2,3,7,8-tetrachlorodibenzo-p-dioxin

In rats exposed to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and related compounds, serum thyroxine (T4) is depressed. Since hamsters are relatively insensitive to TCDD-induced lethality, the effects of TCDD on several parameters of thyroid status were measured in hamsters as a comparison with the more sensitive rat. At 7 days after ip injection of TCDD, there was a dose-dependent increase in serum 3,5,3'-triiodothyronine (T3) and T4 in hamsters to a maximum level 200% of control; the ED50 was approximately 10 micrograms/kg. Hamsters receiving 100 micrograms/kg lost up to 4% of their body weight but began to recover after about 3 weeks. Serum T4 in these animals was elevated compared to pair-fed and ad libitum controls throughout the 53-day experiment, although it also began to recover after Day 21. This was in direct contrast to the marked reduction of T4 in rats exposed to lower doses of TCDD. T3 was significantly higher in TCDD-treated hamsters than in pair-fed controls on Days 2-7, and TSH was also elevated on Days 2-21. Reverse T3, like T4, was increased by TCDD in hamsters whereas it was decreased in rats. Hepatic microsomal UDP-glucuronosyltransferase (GT) activity was measured using T4 as substrate (T4-GT). On a whole liver basis, T4-GT was induced by TCDD by the same proportion in both rats and hamsters (170-180% of controls) although absolute activities in rats were 3- to 4-fold higher than in hamsters. This similarity in T4-GT inducibility by TCDD suggests that there are likely mechanisms in addition to T4-GT induction which account for the species-specific alterations in T4. Thus, while the response of thyroid hormones to TCDD differed qualitatively, effective doses in hamsters were higher than in rats, suggesting that these changes, although secondary, may correlate more directly with toxicity than does enzyme induction (whose ED50s are similar in both species). An understanding of the mechanism of this species difference may be helpful in unravelling the primary mechanisms of TCDD toxicity.     

Regulation of 2,3,7,8-tetrachlorodibenzo-p-dioxin-induced tumor promotion by 17 beta-estradiol in female Sprague--Dawley rats

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is a potent hepatocarcinogen in female but not in male rats. In an initiation-promotion model, ovariectomy inhibits TCDD-induced cell replication and reduces both TCDD-induced tumor formation and the promotion of enzyme-altered hepatocellular foci (AHF). The aim of this study was to determine the involvement of the ovarian hormone 17 beta-estradiol in the induction of cell proliferation and development of putative preneoplastic AHF following chronic exposure to TCDD. Diethylnitrosamine (DEN)-initiated ovariectomized (OVX) female rats were treated with TCDD for 20 or 30 weeks in the presence and absence of 17 beta-estradiol administered continuously by implanted 90-day release pellets. Following 20 weeks of treatment, cell proliferation in TCDD-treated rats was decreased regardless of ovarian hormones. Following 30 weeks of exposureTCDD, only significantly induced cell proliferation in OVX rats receiving supplemental 17 beta-estradiol. These data demonstrate that the the transitory mitoinhibition of cell replication by TCDD is not hormonally responsive, but that induction of cell replication at later time points is. TCDD exposure resulted in elevated AHF expressing gamma-glutamyltranspeptidase (GGT) in intact, but not OVX rats at both time points. TCDD also induced GGT-positive AHF in 17 beta-estradiol-supplemented OVX rats. TCDD induced AHF expressing the placental form of glutathione-S-transferase (PGST) in both intact and OVX rats regardless of 17 beta-estradiol exposure, indicating that the modulating effect of 17 beta-estradiol on AHF was specific to the GGT-positive phenotype.     

2,3,7,8-Tetrachlorodibenzo-p-dioxin: Acute oral toxicity in hamsters

The acute oral toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was evaluated in hamsters. Male golden Syrian hamsters received 0 (corn oil only), 300, 600, 1000, 3000, or 6000 μg TCDD/kg body wt by single-dose gavage. To facilitate dosage, TCDD was fed as a suspension in acetone/corn oil (1:9). The 55-day single-dose oral LD50 was 5051 μg/kg (3876–18,487 μg/kg, 95% confidence interval). Deaths occurred from Day 9 through Day 43 following single-dose administration. Initially, no hamsters exhibited adverse effects related to dosage with TCDD, but 4–5 weeks following dosage, hamsters of the 1000, 3000, and 6000 μg/kg dose groups began to develop unkempt hair coats. A dose-related depression of mean body weight when compared to control weights was apparent in hamsters of the 1000, 3000, and 6000 μg/kg dose groups by 3 weeks posttreatment. Gross necropsy revealed the primary target organs affected in the hamster to be the same as in other laboratory species, namely, liver and thymus; this was accompanied by a slight decrease in adipose tissue reserves. No other significant effects were noted upon necropsy. Based on these results, the hamster appears to be much less sensitive than other laboratory species to the acute oral toxicity of TCDD.     

Qualitative and quantitative differences in the induction and inhibition of hepatic benzo[a]pyrene metabolism in the rat and hamster

The present study compared the induction and inhibition of the metabolism of the prototype polycyclic aromatic hydrocarbon, benzo[a]pyrene (BaP), in rat and hamster liver microsomes. The production of total polar metabolites was quantitated by separating 3H-metabolites from [3H]-BaP using reverse-phase thin-layer chromatography. The rate of hepatic microsomal BaP metabolism was similar in the rat and hamster (0.81 vs 0.72 nmol/min/nmol cytochrome P-450 respectively). In the rat, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD; 5 micrograms/kg, i.p.) and 3-methylcholanthrene (3-MC; 50 mg/kg, i.p., X 3 days) pretreatments doubled the rate of BaP metabolism, whereas phenobarbital pretreatment (PB; 80 mg/kg, i.p., X 3 days) had no effect. In contrast, hamster hepatic microsomal BaP metabolism was elevated 2.3-fold by PB pretreatment, whereas TCDD and 3-MC pretreatments had no effect. Isosafrole pretreatment (ISO; 150 mg/kg, i.p., X 3 days) elevated the rate by almost 2-fold in each species. Another cytochrome P-448-mediated activity, 7-ethoxyresorufin O-deethylase (EROD), was induced by the same compounds that induced BaP metabolism in the rat. In hamster liver microsomes, in contrast to BaP metabolism, EROD was induced by TCDD and 3-MC but not PB or ISO pretreatments. The results suggest differences in the substrate specificity of the cytochromes P-448-450 induced by TCDD, 3-MC and PB in these species. This was supported by the different selectivity of the in vitro inhibitors, metyrapone and 7,8-benzoflavone, towards BaP metabolism and EROD in hepatic microsomes from TCDD- or PB-pretreated rats and hamsters. Reverse-phase HPLC analysis indicated that, while 3-hydroxy-BaP was the major metabolite formed by the untreated rat, untreated hamster liver microsomes formed predominantly BaP-4,5-diol. Microsomes from TCDD-treated rats generated elevated levels of all BaP-diols, diones and 3-hydroxy-BaP, with the major metabolites being BaP-9,10- and BaP-7,8-diols. In contrast, the metabolite profile from TCDD-pretreated hamsters was unchanged from the control. PB-treated hamster microsomes produced elevated levels of BaP-diones and 3-hydroxy-BaP. However, the major hepatic metabolite formed by PB-pretreated hamsters was BaP-4,5-diol, while BaP-9,10- and BaP-7,8-diols were not detected. The results of the study indicate differences in the induced cytochrome P-450s and the generation of toxic BaP metabolites in the liver of the rat and hamster.     

Experimental acute intoxication with ripe fruit of Karwinskia humboldtiana (Tullidora) in rat, guinea-pig, hamster and dog.

Previous acute toxicity studies with 'Tullidora' in mice showed mainly hepatic and pulmonary complications. We tested samples in rat, guinea-pig, hamster and dog, searching for the mechanism of death. A single oral preparation of ripe fruit of Karwinskia humboldtiana was given to all animals. Clinical signs and histopathology were reproduced in all species except dogs. We propose a selective toxicity of the toxins of this fruit to the lungs and liver.     

Comparative effects of pair-feeding and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on various biochemical parameters in female rats

Hypophagia is a common characteristic of the toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and may be responsible for some of the toxic manifestations. Pair-feeding has been used in control animals to compensate for the hypophagia, but relatively few studies have assessed biochemical changes associated with pair-feeding versus weight loss induced by TCDD. Rats were treated with TCDD and killed 7 days post-treatment while pair-fed animals received an amount of diet equivalent to TCDD-treated partner animals. Ad libitum-fed rats were also used. No correlations were seen in altered calcium and iron homeostasis between pair-feeding and TCDD administration relative to ad libitum-fed animals. Pair-feeding resulted in greater alterations than TCDD administration in the subcellular distribution of iron in mitochondria, microsomes and cytosol. Pair-feeding also resulted in greater accumulation of calcium in mitochondria and microsomes in pair-fed as compared to TCDD-treated animals. Greater lipid peroxidation was observed in whole liver and nuclei of rats receiving TCDD relative to pair-fed animals. A significantly greater incidence of DNA single strand breaks occurred in hepatic nuclei of TCDD-treated animals as compared to pair-fed and ad libitum-fed animals. Significantly greater inhibition of hepatic glutathione peroxidase activity and thymic involution were observed in TCDD treated animals as compared to the pair-fed group. Although some similarities existed between TCDD-treated animals and pair-fed rats, the overall biochemical changes which were observed following TCDD administration cannot be attributed to weight loss associated with hypophagia.     

Intermediary metabolism of the mature rat following 2,3,7,8-tetrachlorodibenzo-p-dioxin treatment

Changes in body weight, feed intake, hepatic cellularity, and intermediary metabolism were assessed in the mature male (450 g) rat following 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) administration. All animals were schedule-fed (8-hr feeding period/24 hr) and treated with a single oral dose of either TCDD (75 micrograms/kg) or vehicle. Blood and tissues were sampled 16 to 18 hr following the end of the feeding period on 2, 4, 6, and 8 days post-treatment. Mature rats treated with TCDD exhibited a slight but progressive reduction in both body weight and feed intake throughout the 8-day experimental period. An increase in liver mass that was apparent at 2 days and plateaued by 4 days after TCDD treatment was associated with a decrease in the concentration of DNA per gram of wet liver. However, the total liver content of DNA in TCDD-treated rats remained similar to pair-fed animals. Thus, TCDD treatment produced liver enlargement in the mature rat that was the result of hepatocellular hypertrophy and not an increase in cell number. Hepatic glycogen content in TCDD-treated rats was threefold higher than their pair-fed counterparts at 2 to 6 days post-treatment, and this augmentation would account, in part, for the hypertrophy of the liver cell found after administration of TCDD. Plasma glucose and lactate concentrations were similar in TCDD-treated and pair-fed rats, suggesting that the Cori cycle remained unaltered following TCDD administration. Likewise, heart and gastrocnemius glycogen concentrations were similar in all experimental groups. Urinary excretion of urea, ammonia, and creatinine was comparable in TCDD-treated rats and their pair-fed counterparts, indicative of a nitrogen balance that was not disturbed by TCDD. Plasma glutamine concentrations in TCDD-treated rats tended to be reduced and were significantly lower at Day 6 post-treatment when compared to those of pair-fed counterparts, suggestive that amino acid release from muscle was not enhanced in TCDD-treated rats. Likewise, plasma concentrations of branched-chain amino acids, which are metabolized to a large extent in muscle, tended to be lower on Day 6 following TCDD treatment. Yet at Day 6 post-treatment, the circulating concentrations of amino acids that are metabolized by the liver were elevated in TCDD-treated animals. TCDD administration also resulted in an increase in total hepatic protein concentration which was evident at 4 days and increased progressively at 6 and 8 days post-treatment. Liver content of phospholipids also increased gradually following administration of TCDD.(ABSTRACT TRUNCATED AT 400 WORDS)     

Promotion of altered hepatic foci by 2,3,7,8-tetrachlorodibenzo-p-dioxin and 17beta-estradiol in male Sprague-Dawley rats.

The determination of differences in hormonal regulation of tumor promotion-related response to 2,3,7,8-tetrachlorodibenzop-dioxin (TCDD) between males and females may identify factors contributing to the female-specific hepatocarcinogenicity of TCDD in rats. In the current study, diethylnitrosamine-initiated male Sprague-Dawley rats were exposed to TCDD or corn oil vehicle in the presence and absence of 17beta-estradiol (E2), and cell proliferation and development of preneoplastic altered hepatic foci (AHF) were determined. After 30 weeks of exposure, gamma-glutamyltranspeptidase (GGT)-positive AHF and the number of placental glutathione-s-transferase (PGST)-positive AHF were significantly higher in TCDD-treated rats than in control rats. Both the number and volume fraction of GGT-positive AHF were significantly lower in rats cotreated with E2 regardless of TCDD exposure compared with corresponding non-E2-treated groups and were unaffected by TCDD. In contrast, the number of PGST-positive AHF was significantly higher in E2-treated rats in the absence of TCDD treatment. In addition, whereas E2 had no effect on the volume fraction of PGST-positive foci, the levels in rats cotreated with both E2 and TCDD were significantly higher than in controls. No differences were observed in cell proliferation between TCDD-treated and control rats, although cell proliferation was lower in rats exposed to E2 compared with placebo controls. The weaker potency of tumor promotion and lack of induction of cell replication and DNA damage in male rats likely explain the female-specific hepatocarcinogenicity of TCDD in chronic bioassays.     

2,3,7,8-Tetrachlorodibenzo-p-dioxin as an antiestrogen: effect on rat uterine peroxidase activity

Treatment of 25-day-old female Sprague-Dawley rats with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) significantly lowered constitutive uterine peroxidase activity and decreased uterine wet weights in a dose-response fashion. In cotreatment studies with 17 beta-estradiol, 2,3,7,8-TCDD antagonized the increase in uterine peroxidase activity and uterine wet weights, and these effects persisted for up to 156 hr. In the rat uterus, the antiestrogenic affects of two potent Ah receptor agonists, 2,3,7,8-TCDD and 2,3,4,7,8-pentachlorodibenzofuran, were comparable at a dose of 80 micrograms/kg, whereas the weaker Ah receptor agonist, 1,2,4,7,8-pentachlorodibenzo-p-dioxin, was relatively inactive at this dose. These results show that 2,3,7,8-TCDD antagonizes a well-characterized estrogen-induced response (uterine peroxidase activity), and the structure-activity data suggest that the Ah receptor is involved in mediating the antiestrogenic responses in target cells/organs.     

Gestational exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) severely alters reproductive function of female hamster offspring.

Low doses of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), administered as a single dose to the dam during gestation, alter development of the fetal rodent reproductive system. In male rat and hamster offspring, dosing with TCDD during gestation reduces epididymal and ejaculated sperm counts and delays puberty. In female rats, in utero TCDD-exposure results in reduced ovarian weight and fecundity, and induces cleft phallus and a persistent thread of tissue across the vaginal orifice. Here, we demonstrate that 2-microgram TCDD/kg, administered as a single oral dose prior to sexual differentiation, alters reproductive function in female hamster offspring, a species relatively resistant to the lethal effects of TCDD. In the current study, pregnant hamsters (P0 generation) were dosed orally with vehicle (corn oil) or 2 micrograms TCDD/kg on gestational day (GD) 11.5. P0 maternal viability, body weight, fertility, and F1 litter size did not differ between control and treated groups. In the F1 generation, body weights were permanently reduced by about 30%, vaginal opening was delayed (p < 0.0001), and vaginal estrous cycles were altered by TCDD treatment. In contrast, most treated female offspring displayed regular 4-day behavioral estrous cycles, indicating that in utero TCDD treatment did not markedly disrupt hypothalamic-pituitary-gonadal hormonal cyclicity. Although both control and TCDD-treated F1 females mated successfully with a control male (estrous cyclicity was abolished by mating), 20% of the F1 treated females did not become not pregnant (no implants). In addition, 38% of pregnant F1 females from the TCDD group died near-term, and the numbers of implants in pregnant animals (treated 5.1 versus 11.3) and pups born live (2.7 treated vs. 8.7 control) were reduced by TCDD-treatment. In the F2, survival through weaning was drastically reduced (15% treated vs. 78% for control) by TCDD treatment of P0 dams. F1 female hamster offspring exposed in utero to TCDD displayed external urogenital malformations, with most females having complete clefting of the phallus, an effect previously reported in the rat. Unlike rats exposed to TCDD (0.2-1.0 microgram/kg) on GD 15 or GD 8, hamster offspring did not display vaginal threads. These results demonstrate that in utero administration of TCDD adversely affects growth, reproductive function, and anatomy in female hamster offspring given a dosage level nearly four orders of magnitude below the dosage level toxic to the adult animal. Adverse effects of TCDD persisted through two generations (F1 and F2), even though the F1 was only indirectly exposed during gestation and lactation.     

The effect of total parenteral nutrition on the toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin in the rat

The effects of total parenteral nutrition (TPN) upon the toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in rats has been studied. At doses of 50 or 100 μg/kg, TPN-fed, TCDD-treated rats demonstrated a weight gain similar to that of TPN-fed controls, but died at Days 13–17 following treatment. Gross examination of moribund animals revealed icterus, thymic atrophy, increased adipose tissue depots, and enlarged livers. The liver weights ranged from two to three times those from TPN-fed control animals. Histologically the livers were severely necrotic. Most cells which were not necrotic were markedly swollen and disorganized. Extensive vacuolization of hepatocytes and cystic areas containing cell debris were also prominent features. Whereas glycogen stores were depleted, the total content of water, lipid, protein, RNA, and DNA in the livers was increased. Alterations in cytochrome P-450-associated monooxygenase activities were also observed. Statistically significant increases in serum iron, bilirubin, alkaline phosphatase, serum glutamic-oxaloacetic transaminase and cholesterol were found in the TPN-fed, TCDD-treated animals. Serum protein, glucose, and triglycerides were significantly decreased except in a few severely moribund animals in which hyperglycemia was observed. The results in the TPN-fed, TCDD-treated rats were compared with TCDD-treated rats fed a chow diet ad libitum. At the same dose of TCDD, the liver damage in the TPN-fed, TCDD-treated rats was histologically more severe.     

6-Alkyl-1,3,8-trichlorodibenzofurans as antiestrogens in female Sprague-Dawley rats

The comparative antiestrogenic effects of 6-methyl-1,3,8-trichlorodibenzofuran (MCDF), 6-t-butyl-1,3,8-trichlorodibenzofuran (triCDF) and 6-cyclohexyl-1,3,8-triCDF were determined in immature female Sprague-Dawley rats. Treatment of the animals with 17 beta-estradiol (0.33 mumol/kg X 2) caused an increase in uterine cytosolic and nuclear estrogen and progesterone receptor levels, uterine peroxidase activity, uterine wet weights and uterine epidermal growth factor (EGF) receptor binding activity and steady state EGF receptor mRNA levels. MCDF and 6-t-butyl-1,3,8-triCDF, two compounds which exhibit moderate aryl hydrocarbon (Ah) receptor binding affinity were also administered (100 mumol/kg) to the female rats in the presence or absence of 17 beta-estradiol. The results of these studies show that both compounds decrease the constitutive and 17 beta-estradiol-induced responses noted above. In contrast, 6-cyclohexyl-1,3,8-triCDF, a congener which exhibits low Ah receptor binding, was inactive as an antiestrogen. These studies clearly demonstrate that selected 6-alkyl-1,3,8-triCDFs elicit a broad spectrum of antiestrogenic activity in immature female rats. Moreover, in contrast to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) which also is a potent antiestrogen, the 6-alkyl-1,3,8-triCDFs are relatively non-toxic and can serve as prototypes for the future development of a new class of antiestrogens with potential for clinical applications.