Mechanism of action of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)

mRNA levels in control rat liver display strain-specific, hereditary, and AHR-dependent components

Rat is a major model organism in toxicogenomics and pharmacogenomics. Hepatic mRNA profiles after treatment with xenobiotic chemicals are used to predict and understand drug toxicity and mechanisms. Surprisingly, neither inter- and intra-strain variability of mRNA abundances in control rats nor the heritability of rat mRNA abundances yet been established. We address these issues by studying five populations: the popular Sprague-Dawley strain, sub-strains of Long-Evans and Wistar rats, and two lines derived from crosses between the Long-Evans and Wistar sub-strains. Using three independent techniques--variance analysis, linear modelling, and unsupervised pattern recognition--we characterize extensive intra- and inter-strain variability in mRNA levels. We find that both sources of variability are non-random and are enriched for specific functional groups. Specific transcription-factor binding-sites are enriched in their promoter regions and these genes occur in "islands" scattered throughout the rat genome. Using the two lines generated by crossbreeding we tested heritability of hepatic mRNA levels: the majority of rat genes appear to exhibit directional genetics, with only a few interacting loci. Finally, a comparison of inter-strain heterogeneity between mouse and rat orthologs shows more heterogeneity in rats than mice; thus rat and mouse heterogeneity are uncorrelated. Our results establish that control hepatic mRNA levels are relatively homogeneous within rat strains but highly variable between strains. This variability may be related to increased activity of specific transcription-factors and has clear functional consequences. Future studies may take advantage of this phenomenon by surveying panels of rat strains.

LTR: Linear Cross-Platform Integration of Microarray Data

The size and scope of microarray experiments continue to increase. However, datasets generated on different platforms or at different centres contain biases. Improved techniques are needed to remove platform- and batch-specific biases. One experimental control is the replicate hybridization of a subset of samples at each site or on each platform to learn the relationship between the two platforms. To date, no algorithm exists to specifically use this type of control. LTR is a linear-modelling-based algorithm that learns the relationship between different microarray batches from replicate hybridizations. LTR was tested on a new benchmark dataset of 20 samples hybridized to different Affymetrix microarray platforms. Before LTR, the two platforms were significantly different; application of LTR removed this bias. LTR was tested with six separate data pre-processing algorithms, and its effectiveness was independent of the pre-processing algorithm. Sample-size experiments indicate that just three replicate hybridizations can significantly reduce bias. An R library implementing LTR is available.

Toxicity of 2,3,7,8-Tetrachlorodibenzo-p-dioxin in the Developing Male Wistar(Han) Rat. I: No Decrease in Epididymal Sperm Count after a Single Acute Dose

It has been reported that fetal exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) causes defects in the male reproductive system of the rat. We set out to replicate and extend these effects using a robust experimental design. Groups of 75 (control vehicle) or 55 (50, 200, or 1000 ng of TCDD/kg bodyweight) female Wistar(Han) rats were exposed to TCDD on gestational day (GD)15, then allowed to litter. The high-dose group dams showed no sustained weight loss compared to control, but four animals had total litter loss. Pups in the high-dose group showed reduced body weight up till day 21, and pups in the medium dose group showed reduced body weight in the first week postpartum. Balano-preputial separation was significantly delayed in the high-dose group male offspring. There were no significant effects of treatment when the offspring were subjected to a functional observational battery or mated with females to assess reproductive capability. Twenty-five males per group were killed on postnatal day (PND) 70, and approximately 60 animals per group (approximately 30 for the high-dose group) on PND120 to assess seminology and other end points. At PND120, the two highest dose groups showed a statistically significant elevation of sperm counts, compared to control; however, this effect was small (approximately 30%), within the normal range of sperm counts for this strain of rat, was not reflected in testicular spermatid counts nor PND70 data, and is therefore postulated to have no biological significance. Although there was an increase in the proportion of abnormal sperm at PND70, seminology parameters were otherwise unremarkable. Testis weights in the high-dose group were slightly decreased at PND70 and 120, and at PND120, brain weights were decreased in the high-dose group, liver to body weight ratios were increased for all three dose groups, with an increase in inflammatory cell foci in the epididymis in the high-dose group. These data show that TCDD is a potent developmental toxin after exposure of the developing fetus but that acute developmental exposure to TCDD on GD15 caused no decrease in sperm counts.

Toxicity of 2,3,7,8-Tetrachlorodibenzo-p-dioxin in the Developing Male Wistar(Han) Rat. II: Chronic Dosing Causes Developmental Delay

We have investigated whether fetal exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) causes defects in the male reproductive system of the rat using chronically exposed rats to ensure continuous exposure of the fetus. Five- to six-week-old rats were exposed to control diet, or diet containing TCDD, to attain an average dose of 2.4, 8, and 46 ng TCDD/kg/day for 12 weeks, whereupon the rats were mated and allowed to litter; rats were switched to control diet after parturition. Male offsprings were allowed to develop until kills on PND70 (25 per group) or PND120 (all remaining animals). Offspring from the high-dose group showed an increase in total litter loss, and the number of animals alive on postnatal day (PND)4 in the high-dose group was approximately 26% less than control. The high and medium dose offsprings showed decreased weights at various ages. Balano-preputial separation (BPS) was significantly delayed in all three dose groups compared to control. There were no significant effects of maternal treatment when the offsprings were subjected to a functional observational battery or learning tests, with the exception that the high-dose group showed a deficit in motor activity. Twenty rats per group were mated to females, and there were no significant effects of maternal treatment on the fertility of these rats or on the F1 or F2 sex ratio. Sperm parameters at PND70 and 120 showed no significant effect of maternal treatment, with the exception that there was an increase in the proportion of abnormal sperm in the high-dose group at PND70; this is associated with the developmental delay in puberty in this dose group. There were no remarkable findings of maternal treatment on organ weights, with the exception that testis weights were reduced by approximately 10% at PND70 (but not PND120), and although the experiment was sufficiently powered to detect small changes, ventral prostate weight was not reduced. There were no significant effects of maternal treatment upon histopathological comparison of high-dose and control group organs. These data confirm that developmental exposure to TCDD shows no potent effect on adult sperm parameters or accessory sexual organs, but show that delay in BPS occurs after exposure to low doses of TCDD, and this is dependent upon whether TCDD is administered acutely or chronically.

Changes in food intake and food selection in rats after 2,3,7, 8-tetrachlorodibenzo-p-dioxin (TCDD) exposure

Effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on food selection were studied in TCDD-resistant Han/Wistar and TCDD-sensitive Long-Evans rats and their crosses. The rats were offered a selection diet consisting of chocolate, cheese, and chow, and TCDD was given at the same time or 4 or 16 days later. TCDD persistently reduced the chocolate intake. When the selection diet was started at the time of or less than 11 h after TCDD exposure, TCDD almost completely prevented the intake of chocolate and also cheese in all strains already on the first day, while controls started to consume large amounts of both foods. This may be due to conditioned taste aversion. The effect on food selection with familiar foods seemed to reduce fat intake, while protein and carbohydrate intakes were more variable. There were no major strain differences in the chocolate intake inhibition despite a 1000-fold sensitivity difference in TCDD lethality.

TCDD-induced anorexia and wasting syndrome in rats: effects of diet-induced obesity and nutrition

Interactions of diet and diet-induced obesity, and the characteristic wasting syndrome caused by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) were studied in TCDD-resistant Han/Wistar and TCDD-sensitive Long-Evans rats. The rats were made obese by feeding them either a high-energy diet (consisting of chocolate, cheese, and chow) or force feeding. TCDD reduced body weight in a parallel manner in lean and obese rats. The high-energy diet diminished the body weight loss and increased the survival time in L-E rats after a lethal dose of TCDD, while energy supplement with high-fat/low-protein food had an opposite effect. In conclusion, diet-induced obesity and TCDD had additive effects on body weight. Dietary manipulations were able to modify the weight loss and survival time after TCDD. Fat seems to have a negative impact, while carbohydrate or protein may have a positive impact in this respect. The results are in agreement with a view that TCDD-exposed rats have a negative fat balance favoring fat loss.

Physicochemical differences in the AH receptors of the most TCDD-susceptible and the most TCDD-resistant rat strains

Long-Evans rats (strain Turku AB; L-E) are at least 1000-fold more sensitive (LD50 about 10 microg/kg) to the acute lethal effects of 2, 3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) than are Han/Wistar (Kuopio; H/W) rats (LD50 > 9600 microg/kg). The AH receptor (AHR) is believed to mediate the toxic effects of TCDD and related halogenated aromatic hydrocarbons. We compared the AHRs of L-E and H/W rats to determine if there were any structural or functional receptor differences that might be related to the dramatic difference in the sensitivity of these two strains to the lethal effects of TCDD. Cytosols from liver and lung of the sensitive L-E rats contained about twofold higher levels of specific binding sites for [3H]TCDD than occurred in H/W rats; the Kd for binding of [3H]TCDD to AHR in hepatic cytosols was similar between the two strains. Addition of the oxyanions, molybdate or tungstate (20 mM), had little effect upon ligand binding to AHR in hepatic cytosols from L-E rats whereas in cytosols from H/W rats these agents substantially diminished or totally abolished TCDD binding. The AHR in H/W cytosols also lost ligand-binding function when NaCl (20 to 400 mM) was added to the buffer whereas, in cytosols from L-E rats, the addition of 400 mM NaCl caused the receptor complex to shift from 9S to 6S during velocity sedimentation but did not destroy ligand binding function. AHR from hepatic cytosol of both the L-E and H/W rats could be transformed to the DNA-binding state in the presence of TCDD or other dioxin congeners as assessed by gel mobility shift assays. The most dramatic difference in AHR properties between L-E and H/W rats is molecular mass. Immunoblotting of cytosolic proteins revealed that the AHR in L-E rats has an apparent mass of approximately 106 kDa, similar to the mass of the receptor previously reported in several other common laboratory rat strains. In contrast, the mass of the AHR in H/W rats is approximately 98 kDa, significantly smaller than the mass of receptor reported in any other rat strains. F1 offspring of a cross between L-E and H/W rats expressed both the 106- and the 98-kDa protein. There was no apparent difference in the mass of the AHR nuclear translocator protein (ARNT) between the two strains, but the hepatic concentration of ARNT was about three times as high in L-E as in H/W rats. It will be interesting to find out how the altered structure of the AHR in H/W rats is related to their remarkable resistance to the lethal effects of TCDD.

The AH receptor and a novel gene determine acute toxic responses to TCDD: segregation of the resistant alleles to different rat lines

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD),12 the most toxic congener of dioxins, exhibits wide sensitivity differences between a sensitive Long-Evans (L-E) rat and a resistant Han/Wistar (H/W) rat. The sensitivity is determined probably by two autosomal genes and it is highly end point dependent. The difference is more than 1000-fold for acute toxicity and negligible for CYP1A1 induction. The rat strains were recently shown to have differences in the size of AH receptor (AHR), which mediates most effects of TCDD. In the present study, the rat strains were crossed and the resistant alleles of genes determining TCDD sensitivity were segregated to new rat lines. Selection was based on AHR phenotype determined by Western blot and resistance to TCDD lethality. Two genes determining resistance were found: the Ahr and a novel gene designated "B." In homozygous rats, the H/W type Ahrhw allele prevented TCDD lethality up to 2000 microg/kg or more, and the H/W type "Bhw" allele also increased resistance to TCDD lethality but to a lesser extent. Heterozygous rats were only slightly more resistant to acute lethality than the respective sensitive homozygous rats. CYP1A1 induction was similar irrespective of the Ahr and "B" genotypes, but a substantial increase in serum bilirubin seen after low doses in sensitive rats occurred only after large doses in "Bhw/hw" and not at all in Ahrhw/hw rats. In conclusion, the Ahrhw allele is a major determinant of the exceptional resistance of H/W rats to TCDD lethality. There is also an additional gene, whose function remains to be characterized, conferring limited resistance to TCDD toxicity. These two H/W rat-derived alleles are separately expressed in the new rat lines created.

2,3,7,8-Tetrachlorodibenzo-p-dioxin-induced anorexia and wasting syndrome in rats: aggravation after ventromedial hypothalamic lesion

Long-term regulation of body weight and food intake were studied after rats were subjected to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), which causes hypophagia and body weight loss, and to ventromedial hypothalamic lesion, which causes hyperphagia, metabolic changes and obesity. These two factors appeared to have an interaction, as ventromedial hypothalamic lesion initially aggravated the effects of TCDD on body weight and food intake. This was seen in both TCDD-resistant and TCDD-susceptible rat strains. In contrast, if TCDD was given several weeks before the lesion and body weight had stabilized to a low level, no aggravation was seen, but TCDD completely blocked the effects of ventromedial hypothalamic lesion. Thus, TCDD seems to affect the same regulation chain that is involved in the lesioning of the ventromedial hypothalamus. TCDD might serve as a tool in studying different mechanisms of long-term food intake and body weight regulation.

Characterization of 2,3,7,8-tetrachlorodibenzo-p-dioxin-induced brain serotonin metabolism in the rat

It has previously been shown that a lethal dose of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) increases the brain concentrations of serotonin precursor, tryptophan, and its metabolite 5-hydroxyindoleacetic acid (5-HIAA) in TCDD-susceptible Long-Evans but not in TCDD-resistant Han/Wistar rats. In the present study, TCDD (50 micrograms/kg; LD100 for Long-Evans and nonlethal for Han/Wistar rats) enhanced de novo biosynthesis of serotonin in the brain of Long-Evans but not Han/Wistar or food-restricted Long-Evans rats 10 days after exposure. Furthermore, TCDD increased the plasma level of free tryptophan in Long-Evans rats alone, which may be causally related to the observed effects of TCDD on brain tryptophan levels. Administration of hemin modified the time course of TCDD-induced anorexia although 10 day cumulative food consumption was not altered. Hemin tended to attenuate TCDD-elicited increases in brain serotonin turnover, whereas a beta-adrenergic blocker, propranolol, did not. In the majority of Long-Evans rats, TCDD inhibited the main tryptophan degrading enzyme in the liver, tryptophan pyrrolase, but the rest exhibited augmented activities; these effects were not altered by hemin. TCDD increased the plasma levels of nonesterified fatty acids in Long-Evans (five-fold) but not in Han/Wistar rats. A slight elevation (two-fold) was also seen in food-restricted Long-Evans rats. It is concluded that TCDD selectively promotes brain serotonin turnover in Long-Evans rats and this acceleration is related to increased plasma levels of free tryptophan. The inhibition of tryptophan catabolism in the liver and elevation of plasma nonesterified fatty acids may contribute to these changes.

TCDD-induced hypophagia is not explained by nausea

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is one of the most potent known anorexigens with an unestablished mechanism of action. In the present study, the role of nausea in TCDD-induced hypophagia was assessed by a battery of behavioral (conditioned taste aversion [CTA], kaolin consumption, protein selection), biochemical (plasma oxytocin), and antiemetic drug intervention (trimethobenzamine, metoclopramide) approaches. Moreover, both the most TCDD-susceptible (Long-Evans [L-E]; IP LD50 approximately 10 micrograms/kg) and the most TCDD-resistant (Han/Wistar [H/W]; IP LD50 > 3000 micrograms/kg) rat strains were employed in the experiments. L-E rats were exposed to a lethal dose of TCDD (50 micrograms/kg), whereas H/W rats were treated with high but nonlethal doses (50 or 1000 micrograms/kg). TCDD produced a positive CTA response in H/W rats alone. These animals also increased their kaolin consumption more than L-E rats of either gender after TCDD exposure. TCDD decreased the proportional intake of energy from high-protein diet in female L-E rats, but tended to increase it in male L-E and H/W rats. TCDD did not affect plasma oxytocin concentration by itself, but potentiated the elevation caused by the positive control compound, LiCl, in L-E rats on day 8. Neither antiemetic tested had any detectable influence on TCDD-induced wasting. These findings imply that the degree of nausea elicited by TCDD in the rat depends on strain and gender. However, nausea has only a minor, if at all, causal role in the lethal wasting syndrome characteristic of this compound.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) induced ethoxyresorufin-O-deethylase (EROD) and aldehyde dehydrogenase (ALDH3) activities in the brain and liver. A comparison between the most TCDD-susceptible and the most TCDD-resistant rat strain

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is a potent inducer of ethoxyresorufin O-deethylase (EROD) and aldehyde dehydrogenase (EC 1.2.1.3., ALDH3) enzyme activities in the liver. Little is known about their inducibility by TCDD in the brain, although it may be a target organ for TCDD toxicity. Two strains of rat, Long-Evans (L-E) and Han/Wistar (H/W) exhibit an over 1000-fold difference in their LD50-values for TCDD. The induction of EROD and ALDH3 in discrete brain regions and in the liver of L-E and H/W rats were now compared at 10 days after TCDD exposure to assess the role of these responses in the strain difference. Liver EROD and ALDH3 were maximally induced at 5 micrograms/kg and 50 micrograms/kg, respectively, in both strains. In the brain 50 micrograms/kg TCDD was mostly needed to enhance EROD activity in both strains. The induction occurred especially in olfactory bulbs, but was also seen in the midbrain plus thalamus of both rat strains. The induced EROD activity in the olfactory bulb was almost totally abolished by a monoclonal antibody (Mab) 1-7-1 raised against CYP1A1. ALDH3 activities were increased more dose dependently in olfactory bulbs of H/W than L-E rats. In other brain areas measured, ALDH3 activities were induced more in L-E rats. Kinetic factors did not explain the differential induction of EROD and ALDH3 among discrete brain regions. We conclude that both EROD and ALDH3 are induced in the brain by TCDD although the activities are much lower than in the liver. The induction in the brain is region specific with olfactory bulbs being the most responsive area. As in the liver, the TCDD-induced activity of EROD in the brain is primarily associated with CYP1A1. According to the present findings, enzyme induction in the brain does not seem to have a crucial role in determining the strain susceptibility to the acute lethality of TCDD.

Effect of a single lethal dose of TCDD on the levels of monoamines, their metabolites and tryptophan in discrete brain nuclei and peripheral tissues of Long-Evans rats

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is one of the most potent anorexigens in rats with a yet unidentified mechanism of action. Since biogenic amines are known to essentially participate in the control of body weight and food intake, their levels were determined in various hypothalamic and other brain sites together with selected peripheral tissues after TCDD administration to adult male Long-Evans rats. Rats were given a single lethal dose of TCDD (1000 micrograms/kg intraperitoneally, in dimethylsulphoxide) or vehicle alone and they were decapitated at 1, 5, 25 hr or 8 days after TCDD administration. The samples were analyzed for concentrations of biogenic amines and their metabolites by HPLC-EC. Administration of TCDD increased the concentration of tryptophan at 8 days after exposure by about 20% in almost all nuclei examined, with the change reaching statistical significance in the lateral hypothalamic area and in lateral and medial accumbens nuclei. Importantly, this elevation was not seen in pair-fed control animals. Although not statistically significant, there was a tendency to 5-10% diminished dopamine, serotonin and/or 5-hydroxyindoleacetic acid levels in most brain sites during the first day postexposure. The present results argue against a crucial role for catecholamines as mediators of TCDD toxicity. However, the delayed changes in brain tryptophan do not appear to be secondary to TCDD hypophagia.

Comparative toxicity of four chlorinated dibenzo-p-dioxins (CDDs) and their mixture. Part III: Structure-activity relationship with increased plasma tryptophan levels, but no relationship to hepatic ethoxyresorufin o-deethylase activity

Male Sprague-Dawley rats were treated with an LD20, an LD50, and an LD80 of 2,3,7,8-tetrachlorodibenzo-p-dioxin (tetra-CDD), 1,2,3,7,8-pentachlorodibenzo-p-dioxin (penta-CDD), 1,2,3,4,7,8-hexachlorodibenzo-p-dioxin (hexa-CDD), 1,2,3,4,6,7,8-heptachlorodibenzo-p-dioxin (hepta-CDD), respectively, and a mixture of the four homologues where each CDD was represented at one-fourth its previously established LD20, LD50, and LD80, respectively. Plasma tryptophan levels, liver ethoxyresorufin O-deethylase (EROD) activities, and liver weights were determined at 2 and 8 days after treatment. Plasma tryptophan levels were dose-dependently elevated, particularly at 8 days after treatment, by as much as 75% over control levels. EROD activity in CDD-treated animals was induced 27- to 28-fold, as compared with vehicle-treated controls, but did not show any dose-response. Liver weights were also significantly increased by the CDD treatments, but the increase was not dose related. There was no correlation between plasma tryptophan levels, a biomarker of acute toxicity of CDDs, and EROD activity, a biomarker of arylhydrocarbon (Ah) receptor-mediated enzyme induction. It is concluded that the acute toxicity of CDDs, which correlates and shows perfect structure-activity relationship with reduced activities of key enzymes of intermediary metabolism, and the induction of enzymes by much lower doses of CDDs in the liver, have different mechanisms of action.

Characterization of the enhanced responsiveness to postingestive satiety signals in 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-treated Han/Wistar rats

Previous studies have shown that under free-feeding conditions, TCDD-treated Han/Wistar (H/W) rats consume less sucrose solution but ingest more saccharin solution than their controls thus implying hyperresponsiveness to postingestive satiety signals. In this study, nutrient preloads were employed to further elucidate this phenomenon. Male H/W rats were given a single high but usually non-lethal intraperitoneal dose (1000 micrograms/kg) of TCDD. Feed intake was stimulated by 24 hr feed deprivation at various time points after TCDD exposure. When TCDD-dosed rats were allowed to drink either a 20% sucrose or a 0.25% saccharin solution and then given access to feed, those that had had sucrose ate only about 50% of the amount consumed by the saccharin group. Although the preloads were similar in control rats, no such difference in subsequent feeding occurred. The sucrose solution also produced a longer-lasting suppression of feed intake in TCDD-treated compared with control rats when infused directly into the stomach. By contrast, TCDD-treated H/W rats failed to exhibit an augmented satiety response to parenterally applied glucose independent of testing time. Oral corn oil reduced feed intake in both control and TCDD-exposed rats, but the inhibition was slightly larger in TCDD-treated animals. TCDD did not markedly affect the responsiveness of H/W rats to the suppression of feeding by CCK-8 or bombesin. It is concluded that gastrointestinal factors appear critical to the exaggerated response of TCDD-treated H/W rats to nutrient energy.