The dioxin TCDD protects against aflatoxin-induced mutation in female rats, but not in male rats

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is an environmental contaminant and a potent carcinogen in laboratory rodents. When combined with other environmental toxins, it has been shown to increase the (geno)toxicity of some compounds. In this study, the effect of TCDD on the mutagenicity of aflatoxin-B1 (AFB1) was examined in the rat liver using a lacI transgenic rodent mutation assay. AFB1 induces GC-->TA transversions. Since TCDD is known to have a differential effect in male and female rodents, both sexes were studied. The data showed that a 6-week pre-exposure to TCDD had no significant effect on the frequency of aflatoxin-induced mutation in the liver of male rats. However, the TCDD treatment completely prevented the aflatoxin-induced transversion mutations in female animals.     

Effect of 2,3,7,8-Tetrachlorodibenzo-p-dioxin on the Hepatic Distribution of Iron,Copper, Zinc,and Magnesium in Rats

The distribution of iron, copper, zinc, and magnesium in hepatic subcellular fractions of male and female rats treated with 2,3,7,8-tetrachloro-dibenzo-p-dioxin (TCDD) was determined. Animals received 40 μg TCDD per kilogram per day for three days by mouth (PO) or the vehicle and were killed seven or nine days posttreatment. Iron, copper, zinc, and magnesium were determined by atomic absorption spectroscopy. The iron content of liver from female animals was twofold higher than male animals. The administration of TCDD increased the iron content of mitochondria in female and male rats and decreased iron content of microsomes of both sexes. Significant increases occurred in the copper content of whole liver, mitochondria, and cytosol of male rats and in whole liver and cytosol of female rats. Decreases in the copper content of the microsomes of male rats were observed following TCDD treatment; however, TCDD produced no changes in the zinc content of hepatic subcellular fractions of either sex. The magnesium content of female TCDD-treated rats increased in whole liver, mitochondria, and cytosol, while the magnesium content of microsomes was not altered. With respect to the subcellular distribution of iron, copper, zinc, and magnesium, TCDD produces differential effects. The altered distribution of some cations may contribute to the broad range of effects of TCDD.     

Induction and suppression of hepatic and extrahepatic microsomal foreign-compound-metabolizing enzyme systems by 2,3,7,8-tetrachlorodibenzo-p-dioxin

The effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on a number of hepatic and extrahepatic foreign-compound-metabolizing enzyme systems in microsomes from rats, rabbits and guinea pigs were investigated.Following TCDD treatment, the N-demethylation of benzphetamine, aminopyrine and ethylmorphine was suppressed in hepatic microsomes from male but not from female rats. However, both cytochrome P-450 and benzpyrene hydroxylase were significantly stimulated in hepatic microsomes from both male and female rate at doses as small as 1 μg TCDD/kg body weight. The inductive effect on rat hepatic microsomal enzymes was considerably more persistent than the suppressive effect. Following a single oral dose of 25 μg TCDD/kg body weight, benzpyrene hydroxylase of male rat liver microsomes remained significantly elevated for 73 days but the suppression of benzphetamine N-demethylase had gone after 35 days.The induction of benzpyrene hydroxylase in male rat liver microsomes by TCDD was independent of the age of the rat and the levels to which this enzyme was increased was similar in male rats of all ages. However, the suppression of benzphetamine N-demethylase in male rat liver microsomes was age related: the suppression was seen only in adult animals and in the very young (10 days old) the enzyme was actually induced by TCDD. Inductive effects appeared in both smooth and rough-surfaced hepatic microsomes from male rats but the suppression of N-demethylidon occurred perhaps the derepression arises through the interaction of TCDD or metabolite of TCDD, with the operator gene itself.     

Perinatal exposure to low doses of 2,3,7,8-tetrachlorodibenzo-p-dioxin alters sex-dependent expression of hepatic CYP2C11

The cytochrome P450 (CYP) isoform CYP2C11 is specifically expressed in the liver of adult male rats, and 5alpha-reductase is specifically expressed in the liver of the adult female rats. The sexually dimorphic expressions of these hepatic enzymes are regulated by the sex-dependent profiles of the circulating growth hormone (GH). However, it is not well known whether hormonal imprinting or activation factors in the neonatal brain influence the sexually dimorphic expression patterns of hepatic enzymes. We therefore examined the effect of perinatal exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on sex-dependent expressions of hepatic enzymes. Pregnant rats were treated with TCDD at a dose of 0, 200, or 800 ng/kg on gestation day 15, exposing the pups to the chemical. Although the expression of CYP2C11 protein in the livers of male pups on postnatal day (PND) 49 was significantly higher than that of the controls, but the 5alpha-reductase activities in the livers of female pups were not altered by exposure to TCDD. Focusing on perinatal periods, testosterone and estrogen levels significantly increased in the brain of male pups on PND 2. The results suggest that the alteration of testosterone and estrogen levels affect hormonal imprinting in the neonatal brain of male pups, and thus induces a change in the level of male-specific hepatic CYP2C11. We conclude that perinatal exposure to TCDD at low doses may change the sexual differentiation of the neonatal brain in male rats.     

Tetrachlorodibenzo-p-dioxin exposure alters radial arm maze performance and hippocampal morphology in female AhR mice

Perinatal exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) has been reported to alter spatial learning in rats tested on a radial arm maze (RAM). TCDD is believed to exert most of its effects through binding to the aryl hydrocarbon receptor (AhR). To determine whether the AhR mediates TCDD-induced alterations in spatial learning, we tested male and female AhR-knockout (AhR-/-), heterozygous (AhR+/-) and wild-type (AhR+/+) mice on the RAM. AhR+/- male and female mice were time mated, and treated dams were dosed with 5 microg TCDD/kg body weight on day 13 of gestation. When offspring reached adulthood, male and female AhR+/+, AhR+/- and AhR-/- mice from TCDD-exposed and unexposed litters were tested on the eight-arm RAM. After testing, we examined hippocampal morphology as visualized by the Timm's silver sulfide stain. TCDD-exposed female AhR+/- mice made more errors than their respective controls on the RAM and exhibited a decrease in the size of the intra- and infrapyramidal mossy fiber (IIP-MF) field of the hippocampus. None of the other TCDD-exposed groups differed from their respective control groups with regard to maze performance or hippocampal morphology. The reduction of IIP-MF field indicates a possible morphological basis for the learning deficit that was observed in the female AhR+/- mice. It is hypothesized that the effect of TCDD exposure is AhR dependent and that TCDD may alter GABAergic activity in the hippocampus of female mice during development.     

In utero and lactational exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin and 2,3,4,7,8-pentachlorodibenzofuran reduces growth and disrupts reproductive parameters in female rats

2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and 2,3,4,7,8-pentachlorodibenzofuran (PCDF) are widespread environmental pollutants. TCDD is well known for its adverse effects on female reproduction when administered acutely to immature or adult rats. It is also known that fetal/neonatal exposure to this compound alters reproductive parameters. It is unknown whether exposure to PCDF causes similar adverse effects in offspring. The objectives of the study were to investigate the effects of in utero and lactational (IUL) exposure to TCDD and PCDF on subsequent growth, estrous cycles, and ovulation. Additionally a gonadotropin-primed immature rat model was used to investigate possible direct effects on the ovary after IUL exposure to TCDD (2.5 microg/kg) by evaluating 1) ovarian morphometrics and 2) serum estradiol concentrations. Body weights were reduced in animals with IUL exposure to TCDD and PCDF relative to those in controls at 10 days of age (P < 0.05 for each), and this difference was maintained until termination of the experiment at 125-165 days of age (P < 0.05). Exposure to TCDD or PCDF also disrupted regular estrous cycles and inhibited ovulation rate. On Day 23 (before eCG stimulation), ovaries from animals exposed to TCDD contained the same number of primordial, primary, secondary, preantral, and antral follicles as ovaries from control animals. On Day 25 (48 h after eCG stimulation), ovaries from TCDD-exposed rats had significantly fewer large preovulatory follicles when compared with ovaries from controls. The numbers of smaller follicles (both antral and small antral) were not different. Serum estradiol was significantly lower in TCDD-exposed animals 48 h after eCG stimulation.     

Lack of genetic and cytogenetic effects in mice fed on irradiated wheat.

Experiments were conducted to test the mutagenicity of wheat irradiated with 20 and 200 krad gamma-rays by feeding male and female mice for various periods starting from weaning time. The results obtained from dominant lethal tests, specific locus mutation test, studies on chromosome rearrangements in males and gonadal cell survival studies indicated no positive evidence for genetic and cytogenetic effects.     

The presence of genotoxic and bioactive components in indigo dyed fabrics--a possible health risk?

Extracts of pure cotton and jeans fabrics were tested for mutagenicity in Salmonella typhimurium strains TA98 and TA100. The vat dye indigo, technical grade as well as 98% and greater than 99.5% pure, was also tested for mutagenicity. Synthetic indigo, indirubin and isatin were tested for TCDD receptor affinity in competition experiments in vitro. The mutagenicity of the extracts was associated with the cotton denim and nondyed cotton gave only marginal effects. The mutagenicity of the indigo dyed fabrics was dependent on type and treatment of the fabrics. Extracts of both bleached and nonbleached jeans gave mutagenic effects on TA98 +/- S9 and TA100 +/- S9. The greatest effects were seen in the presence of S9. Bleaching gave an additional increase in the mutagenicity in the absence of S9. Normal washing of the fabrics after bleaching reduced the mutagenicity. Synthetic indigo of technical grade or 98% pure showed mutagenic effects, especially on TA98 + S9. Further purification to 99.5% reduced the mutagenicity to 24 revertants/mg (6.2 rev/mu mole). Considering the amount of indigo in the extracts and its low mutagenicity, the genotoxicity of jeans extracts must be caused by other unknown components. However, indigo showed a high (Kd = 1.9 nM) affinity for the Ah or TCDD receptor. Indigo can therefore still be a potential health risk either by eliciting toxic effects of other compounds or by being a nongenotoxic carcinogen. The worldwide use of jeans with a possible exposure of a large population to genotoxic and biologically active components emphasizes the need for a more thorough characterization of these effects.     

Role of hypergastrinemia in the antiatrophy effect of 2,3,7,8-tetrachlorodibenzo-p-dioxin on oxyntic gland mucosa of the rat stomach

Atrophy of the gastrointestinal mucosa that occurs in pair-fed control rats is not observed in 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-treated rats (1). Our objective was to determine if the gastrointestinal trophic hormone, gastrin, is involved in the antiatrophy effect of TCDD on the gut mucosa. Adult male Sprague-Dawley rats treated with 100 micrograms/kg of TCDD were slightly hypergastrinemic 7 days after dosing and markedly hypergastrinemic 14 days after treatment whereas pair-fed control rats were normogastrinemic. After 14 days of feed restriction, atrophy of the oxyntic gland and ileum mucosa occurred in pair-fed control rats but only atrophy of the ileum mucosa developed in TCDD-treated animals. The oxyntic gland mucosa of TCDD-treated rats was protected from mucosa atrophy as well as from mucosa erosions. The protection against feed restriction-induced atrophy was demonstrated by measurements of oxyntic gland mucosal height and DNA and protein content. Since hypergastrinemia stimulates growth of oxyntic gland mucosa, but not ileum mucosa, the antiatrophy effect of TCDD on mucosa of the oxyntic gland might in part be due to hypergastrinemia. In support of this interpretation, TCDD treatment exerted an antiatrophy effect on the oxyntic gland mucosa only when TCDD-treated animals were hypergastrinemic. For example, hypergastrinemia does not develop within the first 48 hr after TCDD administration, and TCDD treatment affords no protection against fasting-induced atrophy of the oxyntic gland mucosa during this time. On the other hand, the ability of TCDD treatment to protect against feed restriction-induced erosions of the oxyntic gland mucosa might be mediated by hypergastrinemia since these events occur at a later time.(ABSTRACT TRUNCATED AT 250 WORDS)     

4-chloro-o-phenylenediamine induces a dose-related increase in G:C > T:A transversions and one major DNA adduct in the liver of Big Blue mice after 26 weeks in feed treatment

The monocyclic aromatic amine 4-chloro-o-phenylenediamine (4-C-o-PDA), a known mutagen and mouse hepatocarcinogen, was tested for its in vivo mutagenic potential in the Big Blue transgenic mouse assay system. Genomic DNA was isolated from liver tissue of control and treated animals and lacI mutants were recovered. In an initial 2-week study 4-C-o-PDA was administered daily per os to groups of male and female C57BL/6 Big Blue mice at doses of 0 and 200 mg/kg for 2 weeks (on working days) followed by a treatment free expression time of 10 days. Only a weak increase in the mutant frequencies in females was observed. In a 26-week study, where 4-C-o-PDA was given to groups of male and female Big Blue mice in feed at dietary concentrations of 0, 5,000 and 10,000 ppm, 4-C-o-PDA was found to induce a pronounced dose-dependent increase in mutant frequencies in either sex. In the present work, we analyzed the mutation spectrum by automated DNA sequencing of lacI mutants from both studies. Following the 2-week administration of 4-C-oT:A transversions in both sexes. In addition, upon 26-week treatment with 4-C-o-PDA, one major DNA adduct was detected by 33P postlabelling and subsequent multidimensional thin layer chromatography. It is concluded that 4-C-oT:A transversions after 26 weeks in feed treatment. This result indicates that the sensitivity of the Big Blue transgenic assay system, in detecting a unique chemically induced mutation spectrum, is dependent on experimental parameters, such as treatment time. The data suggest that the formation of one major DNA adduct upon 4-C-o-PDA treatment may be critical for its mutagenicity.     

Mutagenicity of the peroxisome proliferators clofibrate, Wyeth 14,643 and di-2-ethylhexyl phthalate in the lacZ plasmid-based transgenic mouse mutation assay

BACKGROUND: Peroxisome proliferators are considered rodent carcinogens that are putative human non-carcinogens based on the presumed absence of direct genetic toxicity in rodent and human cells and the resistance of human cells to the induction of peroxisomes by peroxisome proliferators. The highly sensitive lacZ plasmid-based transgenic mouse mutation assay was employed to investigate the mutagenicity of several peroxisome proliferators based on several lines of evidence suggesting that these agents may in fact exert a genotoxic effect. METHODS: Male and female lacZ-plasmid based transgenic mice were treated at 4 months of age with 6 doses of 2,333 mg di-2-ethylhexyl phthalate (DHEP), 200 mg Wyeth-14,643, or 90 mg clofibrate per kg of bodyweight, respectively, over a two-week period. Control animals were treated with the respective vehicles only (35% propyl glycol for DEHP and Wyeth-14,643 treatment controls and sterile water for clofibrate treatment controls).The mutant frequency in liver, kidney and spleen DNA was determined as the proportion of retrieved mutant and wild-type lacZ plasmids expressed in Escherichia Coli C host cells employing a positive selection system for mutant plasmids. RESULTS: Exposure to DEHP or Wyeth-14,643 significantly increased the mutant frequency in liver, but not in kidney or spleen, of both female and male mice. Treatment with clofibrate did not lead to an increased mutant frequency in any of the organs studied. CONCLUSION: The results indicate that some peroxisome proliferators display an organ-specific mutagenicity in lacZ plasmid-based transgenic mice consistent with historical observations of organ- and compound-specific carcinogenicity.     

Persistent influence of neonatal 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) treatment on glucocorticoid receptors and on the microsomal enzyme system.

Neonatal treatment with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) accounted for a considerable decrease in the number of thymic glucocorticoid receptors in both male and female rats, as assessed at 6 weeks of age. TCDD also gave rise to a marked and prolonged increase in microsomal enzyme activity in the female rats but had practically no such effect on the males. These experimental observations attract attention on to the lasting microsomal inducer effect of the herbicide contaminant dioxin which damages foreign receptors and substantiate the chemical imprinting potential of aromatic hydrocarbons.     

Effect of SCID mutation on the occurrence of mouse Pc-1 (Ms6-hm) germline mutations

Mouse Pc-1 (Ms6-hm) is a hypervariable minisatellite locus that is unstable during intergenerational transmission. This hyper-instability of Pc-1 is useful for detecting germline mutation using a small number of experimental animals, although its molecular mechanism has not yet been elucidated. We examined the effect of severe combined immune deficiency (SCID) mutation on the spontaneous germline mutation at the Pc-1 locus using the CB17 mouse strain. Our results showed that the frequency of spontaneous germline mutation at Pc-1 in the offspring of wild-type parents was 9.7%. In F1 between SCID male and wild-type female, however, the frequency of germline mutation was drastically increased to 42.3%. When SCID female mice were mated with wild-type male, the frequency of germline mutation in F1 was slightly increased to 13.6%. These results suggest that DNA protein kinase catalytic subunit (DNA-PKcs), deficiency of which causes SCID mutation, plays an important role in the stable transmission of a genome containing hypervariable tandem repeats to progeny in male germ cells.     

Effects of TCDD upon IkappaB and IKK subunits localized in microsomes by proteomics

Biochemical studies have shown that microsomes represent an important subcellular fraction for determining 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) effects. Proteomic analysis by two-dimensional gel-mass spectrometry of liver microsomes was undertaken to gain new insight into the actions of TCDD in male and female rats. Proteomic analysis showed TCDD induced several xenobiotic metabolism enzymes as well as a protein at 90kDa identified by mass spectrometry as IkappaB kinase beta/IKK2. This observation led to the discovery of other NF-kappaB binding proteins and kinases in microsomes and effects by TCDD. Western blotting for IKK and IkappaB family members in microsomes showed a distinct pattern from cytosol. IKK1 and IKK2 were both present in microsomes and were catalytically active although, unlike cytosol, IKKgamma/NEMO was not detectable. TCDD exposure produced an elevation in cytosolic and microsomal IKK activity of both genders. The NF-kappaB binding proteins IkappaBbeta and IkappaBgamma were prevalent in microsomes, while IkappaBalpha and IkappaB epsilon proteins were absent. TCDD treatment produced hyperphosphorylation of microsomal IkappaBbeta in both sexes with females being most sensitive. In cytosol, IkappaBalpha, IkappaBbeta, and IkappaB epsilon, but not IkappaBgamma, were clearly observed but were not changed by TCDD. Overall, proteomic analysis indicated the presence of NF-kappaB pathway members in microsomes, selectively altered by dioxin, which may influence immune and inflammatory responses within the liver.     

The relationship of 2-acetamidofluorene mutagenicity in plate tests with its in vivo liver cell component distribution and its carcinogenic potential

1. Using a plating technique, the mutagenic potentials of 2-acetamidofluorence (AAF) and N-hydroxy-AAF were examined after metabolic activation by liver preparations from different animals. Animals used were: male and female rats; male rats treated with 3-methylcholanthrene (MC); male rats treated with AAF; hamsters; guinea pigs; cotton rats and baboons. Irrespective of the animal susceptibility to AAF carcinogenesis, mutation frequency was always increased in the Salmonella typhimurium TA 1538 tester strain. Indeed, the greater response was found in the presence of liver from cotton rats, a species which is resistant to AAF-induced carcinogenesis.

2. Carcinogen binding, with labelled molecules, was also studied in liver cell constituents of rats, guinea pigs and cotton rats. A much better correlation was found between carcinogenicity and carcinogen binding, at least in those species studied, than between carcogenicity and plate test mutagenicity. The difficulty which this new information poses for the interpretation of plate tests is discussed.

Effect of dipyridoimidazole pretreatment on mutagen activation in rats

Rats were pretreated with a single oral dose of different mutagenic fractions obtained from glutamic acid pyrolysate: Glu-P-2 (2-amino-dipyrido[1,2-a:3',2'-d]imidazole), Glu-P-3 (3-amino-4,6-dimethyldipyrido[1,2-a:3',2'-d]imidazole), the tar residue and a basic extract (B2). The liver S9 fractions of these animals were used to investigate the mutagenic activation of 3 promutagens (2-aminoanthracene, Glu-P-2 and Glu-P-3) in Salmonella typhimurium strain TA1538. Different factors were analyzed; influence of the structure of the compounds administered, doses, time interval between pretreatment and sacrifice and sex of the rats. Interpretation of the hepatic induction effects was complicated, however, by the fact that simple oral pretreatment with the solvents (DMSO or ethanol) enhances the activation of the substrates tested for mutagenicity. A dose-effect relationship was found between 2-AA mutagenic activation and Glu-P-2 pretreatment. Glu-P-3 induced the activation of 2-AA more than did Glu-P-2, in the male as in the female. The mutagenicity of 2-AA activated with S9 from male rats was found to be optimal after 24 h pretreatment with 20 mg Glu-P-2/kg b.w. The mutagenicity of Glu-P-2 was poorly influenced by the different pretreatments applied to either the males or the females, whereas some dose effect was found in the autoinduction of Glu-P-2 mutagenicity. Compared to Glu-P-2, the mutagenicity of Glu-P-3 was increased at higher levels when tested with S9 from males pretreated with the same compound, but no differences were observed between males and females.     

Biochemical and toxic effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin in immature male and female chickens

It has been reported that 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-induced body wasting in mammals is associated with decreased adipose tissue lipoprotein lipase (LPL) and glucose transporting (GT) activity with differential sensitivity between genders. This study extends those findings to chickens as an avian model. A significant decrease in body weight gain was demonstrated in immature male and female chickens 10 days after treatment with a single intraperitoneal (i.p.) dose of 10 and 100 microg TCDD/kg. Body weight gain decrease was associated with hepatomegaly and induction of hepatic CYP1A enzymes in both genders. The increase in liver/body weight ratio (48%) and the decreased LPL activity (28%) were significant only in females at 10 microg TCDD/kg. However, the increase in liver/body weight ratio (31%) and the decrease in LPL activity (26%) were significantly demonstrated in males at 100 microg TCDD/kg. Levels of GT were significantly decreased in females (46%) and in males (48%) following treatment with 10 microg TCDD/kg and 100 microg TCDD/kg, respectively. Therefore, in chickens, as in mammals, the TCDD-induced body wasting is accompanied with decreased LPL activity and decreased GT activity and the magnitude of these changes is gender dependent. In contrast to mammals, this study suggests that female chickens are equally, if not more responsive to TCDD toxicity than males.     

Mutagenicity testing with transgenic mice. Part I: Comparison with the mouse bone marrow micronucleus test

As part of a larger literature study on transgenic animals in mutagenicity testing, test results from the transgenic mutagenicity assays (lacI model; commercially available as the Big Blue(R) mouse, and the lacZ model; commercially available as the Mutatrade markMouse), were compared with the results on the same substances in the more traditional mouse bone marrow micronucleus test. 39 substances were found which had been tested in the micronucleus assay and in the above transgenic mouse systems. Although, the transgenic animal mutation assay is not directly comparable with the micronucleus test, because different genetic endpoints are examined: chromosome aberration versus gene mutation, the results for the majority of substances were in agreement. Both test systems, the transgenic mouse assay and the mouse bone marrow micronucleus test, have advantages and they complement each other. However, the transgenic animal assay has some distinct advantages over the micronucleus test: it is not restricted to one target organ and detects systemic as well as local mutagenic effects.     

The effect of TCDD on acyl CoA:retinol acyltransferase activity and vitamin A accumulation in the kidney of male Sprague-Dawley rats

Previous studies have shown that rats treated with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) show signs of toxicity that are similar to the responses of animals to a vitamin A-deficient diet. These include hypophagia, loss of body weight, loss of hepatic vitamin A, and accumulation of renal retinoids. Male Sprague-Dawley rats treated with 10, 30, or 100 nmol/kg of TCDD accumulated renal vitamin A, with retinyl palmitate concentrations reaching 8 times those of control animals, similar to that of male rats fed a vitamin A-free diet for 26 days. Acyl CoA:retinol acyltransferase (ACARAT) activities in both TCDD-treated rats and rats fed a vitamin A-free diet for 26 days were similarly elevated, and were strongly and positively correlated with the renal retinyl palmitate concentrations. Retinol concentrations in the kidneys of rats treated with TCDD or fed a vitamin A-free diet were only slightly elevated when compared to control rats. We suggest that accumulation of retinyl esters in the kidneys of rats treated with TCDD or fed a vitamin A-free diet occurs as a result of increased rates of retinol esterification.