Separation of wasting syndrome and lethality caused by 2,3,7,8-tetrachlorodibenzo-p-dioxin

Disruption of paired-associate learning in rat offspring perinatally exposed to dioxins

The prevalence of cognitive abnormalities in children has partly been ascribed to environmental chemical exposure. Appropriate animal models and tools for evaluating higher brain function are required to examine this problem. A recently developed behavioral test in which rats learn six unique flavor-location pairs in a test arena was used to evaluate paired-associate learning, a hallmark of the higher cognitive function that is essential to language learning in humans. Pregnant Long-Evans rats were dosed by gavage with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) or 2,3,7,8-tetrabromodibenzo-p-dioxin (TBDD) at a dose of  0, 200, or 800 ng/kg (referred as Control, TCDD-200, TCDD-800, TBDD-200, or TBDD-800, hereafter) on gestational day 15, and the offspring was tested during adulthood. Paired-associate learning was found to be impaired in the TCDD-200 and TBDD-200 groups, but not in either group exposed to 800 ng/kg, the observations of which were ensured by non-cued trials. As for the emotional aspect, during habituation, the TCDD-200 and TBDD-200 groups showed significantly longer latencies to enter the test arena from a start box than the Control, TCDD-800, and TBDD-800 groups, suggesting that the TCDD-200 and TBDD-200 groups manifested anxiety-like behavior. Thus, both the chlorinated dioxin and its brominated congener affected higher brain function to a similar extent in a nearly identical manner. Use of the behavioral test that can evaluate paired-associate learning in rats demonstrated that in utero and lactational exposure to not only TCDD but also TBDD perturbed higher brain function in rat offspring in a nonmonotonic manner.

Decreased survival in pancreatic cancer patients with high concentrations of organochlorines in adipose tissue

We analysed adipose tissue concentrations of persistent organic pollutants (POPs) in 21 cases with exocrine pancreatic cancer. The comparison group consisted of 59 subjects. Significantly increased concentrations of polychlorinated biphenyls (PCBs), hexachlorobenzene (HCB), sum of chlordanes and polybrominated diphenylethers (PBDEs) were found in the cases. For 1,1,-dichloro-2,2-bis(p-chlorophenyl)-ethylene (p,p'-DDE) no significant difference was seen. For PCBs no odds ratio (OR) could be calculated since all cases had concentration>median in controls used as a cut-off. HCB yielded OR=53.0, 95% confidence interval (CI)=4.64-605 and sum of chlordanes OR=18.4, 95% CI=2.71-124 whereas OR was not significantly increased for p,p'-DDE or PBDEs. Body mass index (BMI) at the time of tissue sampling was significantly lower for the cases. This might have influenced the results. Using BMI one year previously or decreasing the concentrations of POPs with the same percentage as weight loss among the cases did not change the results. Survival of the cases was shorter in the group with the concentration of POPs>median among cases, significantly so for the sum of PCBs (147 vs. 294 days), p,p'-DDE (134 vs. 302 days), and sum of chlordanes (142 vs. 294 days) in the high and low group, respectively. The results were based on a low number of cases and should be interpreted with caution.

2,3,7,8-Tetrachlorodibenzo-p-dioxin increases reliance on fats as a fuel source independently of diet: evidence that diminished carbohydrate supply contributes to dioxin lethality

The environmental toxin, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) causes a wasting syndrome marked by hypophagia, loss of body fat, changes in intermediary metabolism and death. Use of conventional laboratory animals has not resolved whether or not TCDD affects intermediary metabolism independently of hypophagia. We used the chick embryo, which does not require an exogenous food supply for energy, to answer this question. Our results show that TCDD treatment increases dependence on fats as a fuel source independently of changes in food intake and therefore can affect intermediary metabolism independently of hypophagia. Results of experiments using aminocarnitine to inhibit fatty acid oxidation suggest that TCDD treatment impairs carbohydrate production rather than its utilization and that the former effect contributes to TCDD lethality.

Is a serotonergic mechanism involved in 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-induced appetite suppression in the Sprague-Dawley rat?

The major cause of TCDD-induced death in rats is a progressive voluntary feed refusal which has been correlated with reduced gluconeogenesis. Since centrally administered TCDD does not cause death or decreased feed intake in rats, the ability of TCDD to suppress appetite via peripheral mechanisms acting on the central nervous system was examined in two experimental models. First, it was found that the feed intake of rats on scheduled feeding cycles was not decreased by blood transfused from rats with TCDD-induced appetite suppression (8 days after a lethal dose of TCDD, i.p.). In contrast, a similar transfusion from normal, satiated rats did reduce feed intake of recipient rats by approximately 40%, suggesting that TCDD-treated rats are not satiated but rather that they are not hungry. In the second study tryptophan (the amino acid precursor of the neurotransmitter serotonin) was measured in the plasma and tryptophan, serotonin, norepinephrine and dopamine in the hypothalamus as well as dopamine and its metabolites in the striatum 4, 8, and 16 days after TCDD dosage (125 micrograms/kg, i.p.). Progressive time-dependent increases in tryptophan levels in plasma and brain were paralleled by increases in brain serotonin and 5-hydroxyindoleacetic acid (the primary metabolite of serotonin) in TCDD-treated rats. No changes were observed regarding the other biogenic amines. It is suggested based on these data and on substantial evidence from the published literature that a serotonergic mechanism may be involved in TCDD-induced feed intake reduction.

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.

The central nervous system may be involved in TCDD toxicity

In the present study, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was administered to both the most TCDD-susceptible (Long-Evans) and the most TCDD-resistant rat strain (Han/Wistar) as a constant 1-week infusion either centrally (intracerebroventricularly; i.c.v.) or peripherally (s.c.). Lethality, feed and water consumption as well as weight gain were observed. For both strains of rat, feed intake was most severely affected in the groups given TCDD i.c.v., while the s.c. infusion of TCDD did not markedly depress eating. The same pattern of responsiveness was discernible in the reduction of water consumption and of weight gain. Two out of 7 i.c.v.-treated rats of the TCDD-susceptible strain died after TCDD exposure, whereas all s.c.-dosed animals survived. A statistically significant strain difference was manifest in the magnitude of response between the i.c.v.-TCDD groups in feed intake and body weight change. Moreover, no deaths occurred among the TCDD-resistant Han/Wistar rats. An additional experiment did not disclose any difference in TCDD toxicity between 2 peripheral routes (s.c. and i.p.). Further, lethality tended to have a shorter latent period with the readily absorbable dimethyl sulphoxide (DMSO) as the solvent than with the potentially slowly absorbed corn oil. These findings suggest an important role for the central nervous system in TCDD toxicity.

Skeletal muscle glucocorticoid receptor and glutamine synthetase activity in the wasting syndrome in rats treated with 2,3,7,8-tetrachlorodibenzo-p-dioxin

This study demonstrated specific changes in rat skeletal muscles after a single oral dose (100 micrograms/kg) of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). The development of the wasting syndrome was characterized by marked body weight loss, as well as atrophy of plantaris and gastrocnemius muscles. Fourteen days after administration of TCDD, gastrocnemius muscle cytosolic glucocorticoid receptor binding, measured at a single saturating concentration of [3H]triamcinolone acetonide, was significantly diminished, while plantaris muscle glutamine synthetase activity was strikingly elevated, indicating that specific biochemical alterations occur in skeletal muscle in the wasting syndrome.

Han/Wistar rats are exceptionally resistant to TCDD. I

Adult male Han/Wistar rats were administered 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) intraperitoneally at doses ranging from 125 to 1400 micrograms/kg and monitored for 39 to 48 days. Two rats succumbed in the course of the experiment: one in the group receiving 625 and one dosed 1000 micrograms/kg. Body weights of the animals decreased by 20 to 30% during the first 10 to 14 days and became stable thereafter. Feed consumption decreased to 1/3-1/2 of control levels by Day 4 (calculated per metabolic body mass) and returned gradually to starting values by about 4 weeks after dosing. Water intake displayed a triphasic pattern: at first it was slightly increased (Days 1 to 3), then reduced (on Days 4 to 12) and finally increased again throughout the remainder of the test period. The absolute and/or relative weights of thymus, testicles, ventral prostate and interscapular brown fat were significantly decreased at termination. These results indicate that the LD50-value for TCDD in the male, adult Han/Wistar rat is substantially above 1400 micrograms/kg, and that suppression of appetite is the principal phenomenon responsible for TCDD-induced body weight reduction.

Toxicity and evidence for metabolic alterations in 2,3,7,8-tetrachlorodibenzo-p-dioxin-treated guinea pigs fed by total parenteral nutrition

The effect of total parenteral nutrition (TPN) on the toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in male, Hartley-strain guinea pigs was determined. At a single dose of 2 micrograms TCDD/kg, TPN-fed guinea pigs maintained body weight at a level which was slightly, but consistently, below that of the TPN-fed control animals. However, despite the sustenance of body weight, TCDD-treated animals died or were sacrificed due to morbidity between Days 8 and 24 following treatment. Approximately 50% of this group demonstrated a profound loss of body weight within a few days prior to death or sacrifice. With the exception of the pattern of weight loss, the signs of toxicity in the TPN-fed, TCDD-treated animals were strikingly similar to those observed in TCDD-treated guinea pigs fed ad libitum. Although livers from TCDD-treated, TPN-fed animals demonstrated increased content of lipid and cytochrome P-450, this tissue appeared to be morphologically and functionally comparable to that from TPN-fed controls. Of the blood chemistry examined, only the serum concentrations of 3,5,3'-triiodothyronine were significantly decreased in the treated animals fed by TPN. Results were also compared to TCDD-treated guinea pigs fed ad libitum and respective pair-fed controls. Many of the physiological and biochemical responses observed in animals fed ad libitum following TCDD treatment could be explained by a decrease in food consumption. This study demonstrated that although food consumption clearly accounts for the major effect of TCDD on body weight loss in guinea pigs fed ad libitum, additional physiological and/or biochemical alterations occurred which also contribute to body weight loss, other signs of toxicity, and subsequent lethality.

Relationship of the wasting syndrome to lethality in rats treated with 2,3,7,8-tetrachlorodibenzo-p-dioxin

Young adult male Sprague-Dawley rats treated with a LD95 dose of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) exhibited a progressive reduction in feed intake and body weight until death occurred 15 to 32 days post-treatment. The time course and magnitude of weight loss and lethality of pair-fed control rats were essentially identical to that of TCDD-treated rats with each pair-fed control animal dying within 3 days of its TCDD-treated partner. Body composition analysis of the dead animals revealed that the total amounts of protein, fat, water, and ash in the carcasses of TCDD-treated and pair-fed control rats were each reduced to a similar extent. The temporal pattern of daily feed intake in TCDD-treated and pair-fed control rats (3 meals/day) or (1 meal/day) did not influence the results. Studies conducted at LD25-62 doses of TCDD in male Sprague-Dawley rats of different ages--weanling (90 g), young adult (275 g), and mature (450 g)--showed that the severity of the wasting syndrome in all age groups was greatest for animals that died. Also, young adult rats treated with a LD25 dose of TCDD that died displayed the same degree of hypophagia and weight loss prior to death as rats administered a LD95 dose. Histopathology of the liver and gastrointestinal tract was compared in TCDD-treated (LD95 dose) and pair-fed control rats killed 1 day before they otherwise would have died. Hepatocytes of TCDD-treated rats were enlarged relative to those of pair-fed control rats and contained nuclei that varied in size and number. Pair-fed control rats exhibited atrophy of the liver cords due to a decrease in the cytoplasmic volume of their hepatocytes. The stomach and small intestine of TCDD-treated rats were histologically similar to those of ad libitum-fed controls. In contrast, the glandular mucosa of the stomach of pair-fed control rats was ulcerated and the intestinal mucosa was atrophied. Stomach ulcers were the source of clotted blood found throughout the gastrointestinal tract of pair-fed control rats but not that of TCDD-treated animals. These findings demonstrate that hypophagia-induced weight loss is one of perhaps several responses that contribute to the death of TCDD-treated rats. That other responses are also involved is suggested by differences between pair-fed control and TCDD-treated rats in the weight and histopathology of certain organs. In addition, gastrointestinal blood loss contributes to the death of pair-fed control rats but not TCDD-treated animals.

Hexadecane increases the toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD): is brown adipose tissue the primary target in TCDD-induced wasting syndrome?

Addition of 5% hexadecane to the diet of rats increased fecal excretion of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) from 14 to 39% of an LD50 dose (60 micrograms/kg) during 10 days after dosing. This enhanced elimination did not result in reduced toxicity. On the contrary, the treatment has increased mortality from 60% in controls to 100% in hexadecane treated animals. Body weight changes were good indicators for predicting survival or nonsurvival after the LD50 dose but thymus weights were depressed without regard to survival status. The mechanism by which hexadecane potentiates the toxicity of TCDD is unknown but it is likely to be due to effects altering the disposition of TCDD. Based on similarities in the disposition of TCDD and hexachlorobenzene (HCB), it is suggested that the lethality causing target of TCDD is part of the peripheral compartment. The only site in the peripheral compartment that is compatible with the many thousand-fold species differences observed in TCDD toxicity is brown adipose tissue. The hypothesis is advanced that interaction between thyroid hormones and brown adipose tissue are responsible for the species differences in TCDD toxicity.