Thyroid hormones modulate the toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)

These experiments examine the role of thyroxine (T4) and triiodothyronine (T3) on the toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). The first experiment is continuation of a study reported previously (Rozman et al., 1984). In this experiment, 60 male Sprague-Dawley rats were divided into 6 equal groups. Four groups of rats were thyroidectomized by 3 mCi Na131 l/kg rat. Five weeks later 2 of the thyroidectomized and 1 of the nonthyroidectomized groups of rats received ip 100 micrograms TCDD/kg body weight in corn oil/acetone, whereas 3 corresponding groups of rats served as vehicle controls. Two days after dosing and every 7 d thereafter, 1 thyroidectomized control group and 1 thyroidectomized TCDD-dosed group were given ip 105 micrograms T4/kg body weight. Mortality and body weight were monitored. The course of TCDD toxicity was similar in nonthyroidectomized and thyroidectomized T4-treated rats but was different in thyroidectomized animals without T4 replacement therapy. At d 90 after TCDD dosage, mortality was still lower and the mean time to death was increased (p less than 0.01) in this group of rats compared to nonthyroidectomized or thyroidectomized T4-treated rats. However, administration of T4 starting at d 91 after dosing with TCDD resulted within 2 wk in the same final mortality in thyroidectomized rats as in nonthyroidectomized or thyroidectomized T4-treated animals, indicating that thyroid hormones modulate the time course of the wasting syndrome but do not affect the ultimate mortality figure. Body weight loss was much slower in thyroidectomized (approximately 1 g/d) than in nonthyroidectomized or thyroidectomized T4-treated rats (approximately 8 g/d). In the second experiment the three vehicle control groups of the first experiment were used. Nonthyroidectomized vehicle controls and thyroidectomized T4-treated controls were maintained as before, whereas thyroidectomized controls received T3 at 5 micrograms/kg daily. One month later each rat was dosed with TCDD at 100 micrograms/kg in corn oil/acetone. Toxicity of TCDD was similar in nonthyroidectomized, thyroidectomized T4-treated, and thyroidectomized T3-treated rats as judged by mortality, body weight, and food intake, indicating no difference between T3 and T4 in the modulation of TCDD toxicity.     

Comparative toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in four (sub)strains of adult male rats

Four (sub)strains of adult male rats were given single oral doses of various concentrations of TCDD to establish and compare the oral 30-day LD50 values. The strains of rats were Fischer (F/334N) supplied by Harlan Industries, Frederick Cancer Research Center, and Charles River Breeding Laboratories; and CD supplied by Charles River Breeding Laboratories. The Charles River/Fischer rats were most sensitive to TCDD (LD50 = 164, 95% confidence limits 104-217 micrograms/kg), the Frederick/Fischer and Charles River/CD rats were moderately sensitive to TCDD (LD50 = 303, 250-360; and 297, 240-360 micrograms/kg, respectively), and the Harlan/Fischer rats were most resistant to TCDD (LD50 = 340, 281-409 micrograms/kg). The mean times of death were from 24.5 +/- 1.0 to 28.3 +/- 0.5 days and the percentage body weight loss at death was 37.4 +/- 1.2 to 42.7 +/- 1.3%. One week after exposure of the Charles River/Fischer animal to 45 micrograms TCDD/kg (1/4 the established 30-day LD50 dose), the same serum profile was induced as previously observed in the Harlan/Fischer rat, which includes hypoglycemia, hypertriglyceridemia, and hypercholesterolemia. These results emphasize the importance of indicating the precise dose, strain of rat, and time after dosing before termination in reporting the effects of TCDD on a particular biological response.     

2,3,7,8-Tetrachlorodibenzo-p-dioxin toxicity in yellow perch (Perca flavescens)

Growth, mortality and morphologic lesions in juvenile, hatchery-reared yellow perch, Perca flavescens, were studied after treatment with graded single doses of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD, 1-125 micrograms/kg, intraperitoneally). TCDD doses of 25 and 125 micrograms/kg caused 95% mortality by 28 d after treatment, without decreasing body weight. A TCDD dose of 5 micrograms/kg resulted in progressive loss of body weight with cumulative mortality of 80% by 80 d posttreatment. Periodic handling stress did not affect the time course of mortality or cumulative percent lethality in TCDD-treated perch. Fin necrosis, petechial cutaneous hemorrhage, and ascites occurred in perch treated with 5 micrograms/kg or more of TCDD. Thymic atrophy, decreased hematopoiesis in the head kidney, fibrinous pericarditis, focal myocardial necrosis, submucosal gastric edema, and hyperplasia of the epithelium of gill filaments and lamellae occurred in perch dosed with 25 or 125 micrograms/kg. Dose-related splenic lymphoid depletion occurred in perch receiving 5 micrograms/kg or more TCDD, and hepatocyte lipidosis occurred in groups treated with doses of 1 microgram/kg or more TCDD. Thus yellow perch are as responsive to the acute toxic effects of TCDD as some of the more sensitive mammalian species, and neither loss of body weight nor histologic lesions in TCDD-treated perch are sufficient to explain mortality.     

Reduced activities of key enzymes of gluconeogenesis as possible cause of acute toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in rats.

Male Sprague--Dawley rats (350-375 g) were injected i.p. with TCDD (25 [sublethal dose] and 125 micrograms/kg [lethal dose], respectively, in corn oil/acetone), or vehicle only; vehicle-treated animals were pair-fed to their TCDD-treated counterparts. 1, 2, 4, 8, 16, and 32 days (28 days for lethal dose) thereafter, animals were sacrificed and activities of two key enzymes of gluconeogenesis determined in livers of rats. In livers of pair-fed rats both enzyme activities were little affected. In the livers of TCDD-treated animals the activity of phosphoenolpyruvate carboxykinase (PEPCK, EC 4.1.1.32) decreased rapidly, exhibiting significant losses by the 2nd day after treatment. Time course and extent of loss of PEPCK activity (about 50%) were similar after either dose. The activity of glucose-6-phosphatase (G-6-Pase, EC 3.1.3.9) decreased more slowly as a result of TCDD treatment; statistically significant losses were observed by 4 or 8 days after the lethal and sublethal dose, respectively. These results confirm the hypothesis that reduced in vivo rates of gluconeogenesis in TCDD-treated rats are due to decreased activities of gluconeogenic enzymes. In an additional set of experiments, rats were treated with 125 micrograms/kg TCDD, 25 micrograms/kg TCDD, or with vehicle alone. The 25 micrograms/kg or vehicle-treated rats were then pair-fed to rats dosed with 125 micrograms/kg of TCDD. Mean time to death and body weight loss at the time of death were essentially identical in all groups, lending additional support to the hypothesis that reduced feed intake is the major cause of TCDD-induced death in male Sprague--Dawley rats. Both appetite suppression and reduced total PEPCK activity in whole livers occurred in the same dose-ranges of TCDD, suggesting the possibility of a cause-effect relationship.     

Metabolism and distribution of [14C]glucose in rats treated with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)

Male Sprague-Dawley rats were given a single, usually lethal, dose of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD, 125 micrograms/kg ip in corn oil), or vehicle alone. Twenty-four hours after ip administration of TCDD the animals received an ip injection of 14C-labeled glucose, and the time course and amount of exhalation of 14CO2 were monitored for 8 h continuously and once daily for 20 min for the subsequent 5 d. TCDD treatment reduced the amount of 14CO2 exhaled within 8 h after the injection of [14C]glucose by 33%, as compared to pair-fed controls. Blood levels of radioactivity were affected by TCDD accordingly. No particular organ appeared to act as a sink for the radioactivity not exhaled during these 8 h by the treated animals. TCDD (125 micrograms/kg) induced significant changes in the disposition of radioactivity in heart and brown adipose tissue between 25 and 125 min after the iv injection of [14C]glucose. The areas under the curve of [14C]glucose-derived radioactivity were the same after either iv or ip injection in the blood of TCDD-treated rats, allowing a direct comparison of experiments with iv or ip injection of [14C]glucose. The half-lives of radioactivity in the exhaled air and in feces of treated animals were greatly elevated during the 5 d following administration of [14C]glucose. These results indicate that TCDD induces in rats, within 24 h after dosing, alterations in the metabolism of glucose that preceded changes in insulin homeostasis, because hypoglycemia and hypoinsulinemia in rats do not occur until about a week after TCDD treatment. Since overt signs of acute toxicity (reduced feed intake and body weight loss) are also not noticeable until several days after a lethal dose of TCDD, it is probable that this earlier disturbance of glucose metabolism is part of the biological changes that result in wasting away and eventually in death.     

Corticosterone Modulates Acute Toxicity of 2,3,7,8-Tetrachlorodibenzo-p-1 dioxin (TCDD) in Male Sprague--Dawley Rats

Corticosterone Modulates Acute Toxicity of 2,3,7,8-Tetrachlorodibenzo-p-dioxin(TCDD) in Male Sprague-Dawley Rats.GORSKI, J. R., ROZMAN, T.,GREIM, H., AND ROXMAN, K. (1988). Fundam Appl. Toxicol 11, 494-502.Bilateral adrenalectomy or adrenal demedullation was performedon male Sprague-Dawley rats by established surgical techniques.Subsequently, the dose-response (mortality and mean time todeath) to TCDD was determined in adrenalecto-mized (10, 20,40 µg/kg TCDD ip in 95:5 corn oil: acetone) or demedullated(15, 30, 60 µg/kg TCDD) rats. Adrenalectomy drasticallyincreased mortality and greatly shortened mean time to deathafter dosing with TCDD. More importantly, adrenalectomized TCDD-treatedrats died 3 of hypoglycemic shock without losing much body weightConversely, adrenal demedullation had no effect on mortalityor mean time to death caused by TCDD when compared to non-demedullatedTCDD-treated controls. Thus, it was concluded that the factors)modulating the acute toxicity of TCDD resides in the adrenalcortex and not in the medulla. Administration of corticosterone(25 ngjµl in drinking water) to adrenalectomized ratsreturned the toxicity of TCDD to levels seen in nonadrenalectomizedrats suggesting that this hormone is another key 3 factor (inaddition to the thyroid hormones) in the modulation of the acutetoxicity of TCDD. Corticosterone supplementation (25, 50, or100 µg/) to nonadrenalectomized rats, or to thy- roidectomized-adrenalectomizedrats (25 µg/ml), resulted in no additional beneficialeffect indicating that a factoids) other than thyroid hormonesand corticosterone is also involved in the 14 acute toxicityof TCDD     

Interaction of estradiol and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in an ovulation model: evidence for systemic potentiation and local ovarian effects

Immature rats were treated with estradiol cypionate, (ECP, 0, 0.1, 1, or 2 mg/kg s.c.) followed 24 h later by TCDD (0 or 10 microg/kg orally). Follicular development was induced with eCG [5 or 10 IU subcutaneously (s.c.)] followed by an ovulatory dose of hCG (10 IU s. c.). Inhibition of ovulation by TCDD was potentiated by ECP in hypophysectomized but not intact rats. Only hypophysectomized rats exposed systemically to TCDD and ECP exhibited weight loss. Pair feeding mimicked the combined effects of TCDD and ECP in hypophysectomized rats. In another experiment, intact rats received ECP s.c. (0 or 2 mg/kg) and TCDD into the ovarian bursa (0 or 250 ng). Another group of intact rats received TCDD orally (10 microg/kg) and ECP into the ovarian bursa (0 or 1.5 microg). Blockade of ovulation by systemic or local TCDD was alleviated by ECP pretreatment. Estrogen increased the systemic toxicity of TCDD in rats whereas antagonizing its direct ovarian effects.     

Increased permeability of the rat biliary tree by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) treatment and protection by hepatoactive agents

Male Sprague-Dawley rats were treated ip on Day 0 with 0, 20, 50, or 100 micrograms/kg of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and biliary tree permeability was evaluated on Days 2, 4, 7, 10, 14, or 20 by segmented retrograde intrabiliary injection of [3H]sucrose or [14C]mannitol. Seven days after 100 micrograms/kg TCDD, the percentage recovery in bile of both [3H]sucrose (73.9 +/- 4.2 vs 27.6 +/- 7.6, control vs TCDD, means +/- SE) and [14C]mannitol (22.7 +/- 2.2 vs 12.1 +/- 2.2) was decreased, demonstrating that the permeabilities of both the intracellular (canalicular) and paracellular pathways were increased. Seven days after 50 micrograms/kg TCDD, the recovery of [3H]sucrose was decreased (73.5 +/- 5.4 vs 39.0 +/- 2.8) but the recovery of [14C]mannitol was not (25.5 +/- 1.5 vs 22.9 +/- 1.9). Thus, an increase in paracellular permeability is obtained at a lower dose of TCDD. In rats treated with 100 micrograms/kg TCDD on Day 0, co-treatment with chlordecone (15 mg/kg/day on Days 2-6) or thyroxine (50 micrograms/kg on Day 2) had no effect. Pregnenolone-16 alpha-carbonitrile (75 mg/kg/day on Days 4-6) treatment increased [14C]mannitol recovery in both TCDD and control groups; its effect must not be specific. Methimazole given in drinking water (0.5%) on Days -7 through 7 reversed the increased permeability effects of TCDD (100 micrograms/kg) without affecting the biliary tree permeability ([14C]mannitol recovery) of control animals.     

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

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

Effects of adenine and its isomer 4-aminopyrazolo-[3,4-d]-pyrimidine on 2,3,7,8-tetrachlorodibenzo-p-dioxin-induced mortality in rats

Adult male Fischer rats were given a single po dose of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) equal to 2 times the LD50 to increase the serum and liver lipid concentrations and to induce mortality. In addition, animals were given 4-aminopyrazolo-[3,4-d]-pyrimidine (4APP), an agent that decreases serum lipids, or adenine (Ad), an agent that prevents the formation of fatty liver, to examine the relationship between changes in lipids and TCDD-induced mortality. The principal effect of 4APP on TCDD-induced mortality (325 micrograms TCDD/kg body wt) was that it shortened the mean time to death. In contrast, Ad stimulated feed consumption and decreased body weight loss, but the mean times to death were similar for TCDD and TCDD + Ad animals. Based on these mortality studies, 4APP, but not Ad, affects the TCDD-induced mortality in Fischer rats. The TCDD-induced sensitivity to 4APP, based on decreased mean time to death, implies that blocking the release and/or synthesis of triglyceride-rich lipoproteins by the liver, and the subsequent decrease in serum lipids, may play an important role in the TCDD-induced mortality. The increase in serum triglyceride associated with TCDD exposure appears to be essential in providing metabolic energy under circumstances where lipoprotein retrieval is reduced.     

Morphologic lesions and acute toxicity in rainbow trout (Salmo gairdneri) treated with 2,3,7,8-tetrachlorodibenzo-p-dioxin

To determine effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on growth, mortality, and morphologic lesions in rainbow trout, juvenile Shasta or Wytheville strain fish, obtained from 4 hatcheries, were administered graded single doses of TCDD, 0.1-125 micrograms/kg, ip. TCDD doses of 25 and 125 micrograms/kg caused 85% lethality 2-4 wk after treatment. At these high doses, death occurred before body weight loss could be detected. A lower dose of 5 micrograms/kg caused decreased growth and cumulative mortality of 20% after 11 wk. Stress associated with netting and weighing the fish at weekly intervals significantly shortened the delay period prior to TCDD-induced lethality. Gross and microscopic lesions were evident in rainbow trout treated with 10 micrograms TCDD/kg, but not in fish treated with 1 or 0.1 microgram/kg. Morphologic lesions occurred consistently in epithelial and lymphomyeloid tissues of TCDD-treated fish. Lymphomyeloid lesions included thymic involution, splenic lymphoid depletion, and hypocellularity of hematopoietic tissues in the head kidney and trunk kidney. In association with decreased hematopoiesis, peripheral leukopenia and thrombocytopenia occurred in Shasta strain yearling trout treated with 1 microgram/kg or more TCDD. Regarding epithelial lesions, all 4 hatchery strains treated with 10 micrograms/kg or more TCDD showed multifocal necrosis of gastric cardiac glandular mucosa, 3 of 4 hatchery strains showed vacuolar inclusions in exocrine pancreatic cells, and 2 of 4 hatchery strains showed fin necrosis. The severity and character of lesions in the liver and gastric mucosa varied markedly between hatchery strains of trout. One hatchery strain showed no hepatic lesions, two showed mild hepatocyte lesions, and one exhibited severe diffuse hepatopathy. In this severely affected hatchery strain, hyaline intracytoplasmic inclusions occurred in hepatocytes at 14 and 34 d after TCDD exposure, and bile-duct hyperplasia occurred at 34 d following TCDD exposure. One of 4 hatchery strains showed atrophy of serous gastric glands and 1 of 4 hatchery strains showed hyperplasia of these same glands at 25 and 34 d, respectively, following TCDD treatment. Thus, lymphomyeloid and epithelial tissues are the primary targets for TCDD-induced pathologic lesions in rainbow trout, and the incidence and severity of these lesions is influenced by the strain of trout used and the hatchery from which the trout were obtained.     

Effect of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on thermogenesis in brown adipose tissue of rats

Male Sprague-Dawley rats were treated with a usually lethal dose of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD; 125 micrograms/kg i.p. in corn oil) or with vehicle alone. Two, 4, and 8 days after treatment the temperature of interscapular brown adipose tissue (IBAT) was monitored during venous infusion of norepinephrine (480 ng/min) for 60 min. The temperature response was about 1.0-1.5 degrees C within 1 h in vehicle-treated, pair-fed and ad libitum-fed controls. In TCDD-treated animals, the response of IBAT decreased with time after TCDD dosage, amounting to only 0.3 +/- 0.1 degree C at 8 days after dosing (differences significant with respect to both controls, P less than 0.05). GDP binding to IBAT mitochondria (a measure of thermogenic capacity) was unchanged in all groups, indicating that the reduced thermogenic response was probably not caused by an impairment of the mitochondrial uncoupling process by TCDD.     

Differences in acute toxicity syndromes of 2,3,7,8-tetrachlorodibenzo-p-dioxin and 1,2,3,4,7,8-hexachlorodibenzo-p-dioxin in rats

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is the most potent congener of polychlorinated dibenzo-p-dioxins. The potency of 1,2,3,4,7,8-hexachlorodibenzo-p-dioxin (HxCDD) is only 10% of that of TCDD for typical aryl hydrocarbon receptor (AHR)-mediated effects. Acute lethality, macroscopic effects, and liver toxicity of TCDD and HxCDD were compared in male rats of the strain Han/Wistar (Kuopio; H/W), and of the lines A and B. The latter two rat lines originate from crossbreeding of H/W and Long-Evans (Turku/AB) rats. H/W and line A rats are highly resistant to acute toxicity of TCDD due to an altered AHR, while line B rats are moderately resistant due to H/W-type alleles of another, yet unidentified gene contributing to TCDD resistance ("gene B"). The rats received 200-10,000 microg/kg of either TCDD or HxCDD intragastrically and were monitored for 46 days. In all rats, the highest dose of HxCDD (10,000 microg/kg) reduced body weight more effectively than an identical dose of TCDD. Only HxCDD (10,000 microg/kg) caused gastrointestinal hemorrhage, pale (fatty) livers and death by day 15 in H/W and line A rats. In line B rats, HxCDD caused pronounced hepatic fatty degeneration, whereas TCDD induced hepatic accumulation of biliverdin and its derivatives. Both congeners induced sinusoidal distension in liver. In H/W and line A rats, the estimated LD(50) values were >10,000 microg/kg and 2000-10,000 microg/kg for TCDD and HxCDD, respectively; for line B rats they were 480 microg/kg and 1000-2000 microg/kg, respectively. Thus, HxCDD was more potent than TCDD in inducing acute mortality in H/W and line A rats, contrary to what is predicted by toxic equivalency factor (TEF) values. In line B, the expected rank order of potencies prevailed. These findings suggest that in addition to the canonical AHR-mediated toxic pathways, HxCDD possesses an AHR-independent mechanism of toxicity, whose main manifestations are rapid body weight loss, mortality, fatty liver and gastrointestinal hemorrhage.     

NAD(P)H: quinone oxidoreductase (DT-diaphorase) in chick embryo liver. Comparison to activity in rat and guinea pig liver and differences in co-induction with 7-ethoxyresorufin deethylase by 2,3,7,8-tetrachlorodibenzo-p-dioxin

NAD(P)H:quinone oxidoreductase (EC 1.6.99.2; DT-diaphorase) was present in the liver of 18- and 19-day-old chick embryos as assayed both by reduction of resorufin and by the more traditional assay, reduction of 2,6-dichlorophenolindophenol (DCPIP). Both reductions had the classic characteristics of DT-diaphorase: they were equally supported by NADPH and NADH and almost entirely inhibited by dicumarol. Chick embryo liver DT-diaphorase was entirely cytosolic. It was undetectable in the microsomal and mitochondrial fractions. Chick embryo liver cytosol and mitochondrial fractions contained an enzyme oxidizer of resorufin but not of DCPIP. The Km for NADPH for resorufin reductase was an order of magnitude higher in chick embryo than in rat or guinea pig cytosol (1 mM vs 0.1 mM). Resorufin reductase activity was higher for chick embryo than for rat or guinea pig cytosols: Vmax (nmol resorufin reduced per mg cytosolic protein per min +/- SEM) 355 +/- 28 for chick embryo, 159 +/- 10 for guinea pig and 68 +/- 28 for rat. The Vmax for DCPIP reduction was also twice as high in chick embryo as rat liver cytosol. In the chick embryo, 7 days after treatment with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) at 6.4 micrograms/kg egg (1 nmol/egg) mortality was increased 2.4-fold, hepatic DT-diaphorase 1.3-fold, and 7-ethoxyresorufin deethylase (7-EROD) 72-fold over control levels. At 32 micrograms/kg, mortality was increased 4.2-fold, DT-diaphorase 2.3-fold and 7-EROD 100-fold. In the guinea pig, 5 days after treatment with TCDD at 10 micrograms/kg, TCDD toxicity was also evident (loss of body weight and thymus weight); there was no change in DT-diaphorase as measured by resorufin reduction, confirming by a different assay the observation of Beatty and Neal (Biochem Pharmacol 27: 505-510, 1978) that TCDD does not induce DT-diaphorase in guinea pig liver, and 7-EROD was increased 8-fold. In contrast, in the rat, 7 days after exposure to TCDD at 10 micrograms/kg, there was no evidence of toxicity, DT-diaphorase was increased close to 7-fold and 7-EROD, 100-fold. The results demonstrate that avian liver contains DT-diaphorase and show that the extent to which DT-diaphorase is part of the pleiotypic response of the liver to an Ah (aryl hydrocarbon) receptor ligand is species dependent. They also suggest that DT-diaphorase induction and TCDD toxicity may be inversely related. The possibility that DT-diaphorase protects against TCDD toxicity and participates in species differences in sensitivity to TCDD toxicity warrants further investigation.     

Effect of thyroidectomy and thyroxine on 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) induced toxicity

Chemical thyroidectomy effectively protected athyroid rats from mortality during 45 days after dosing with 100 micrograms 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)/kg, whereas 70 to 80% of nonthyroidectomized-euthyroid and thyroidectomized-T4 (thyroxine)-maintained-euthyroid rats died within the same period of time. There was a significant decrease in body weight of all TCDD-treated groups compared to vehicle controls. However, body weight loss was much slower in thyroidectomized-athyroid (congruent to 1 g/day) than in nonthyroidectomized-euthyroid or in thyroidectomized-T4-euthyroid (congruent to 8 g/day) rats. TCDD significantly reduced feed intake in nonthyroidectomized-euthyroid and thyroidectomized-T4-euthyroid rats, but no altered feed consumption was observable in thyroidectomized-athyroid animals. These data indicate that thyroid hormone(s) play(s) an important role in mediating the toxicity of TCDD.     

Inhibition of the vascular actions of IgG aggregates by BN 52021, a highly specific antagonist of paf-acether

The effect of BN 52021, a selective antagonist of paf-acether (Braquet GB patent 8, 418, 424 July 19, 1984), was studied in normotensive rats challenged with different doses of paf-acether. Sudden death was observed in animals receiving an i.v. dose of 10 micrograms/kg of paf-acether and this was prevented by prior treatment with BN 52021 (5 mg/kg, i.v.). Animals receiving 2.5 micrograms/kg of paf-acether had a fall of mean arterial pressure of 92.5 +/- 4.7 mmHg which recovered to the prechallenge level 20.5 +/- 0.2 min thereafter. Previous treatment with BN 52021 (5 mg/kg, i.v.) reduced the mean arterial pressure fall to 47 +/- 0.9 mmHg and the time of recovery to 5.7 +/- 1.7 min. The extravasation of 125I-bovine serum albumin under the above conditions was reduced by BN 52021 from 36 +/- 3 to 18 +/- 3%. A lower dose of BN 52021 (1 mg/kg, i.v.) was also effective in reducing later extravasation, but was unable to prevent the extravasation which appears up to 10 min after the injection of paf-acether. To extend these findings to a model of endogenous production of paf-acether, other animals were challenged with soluble aggregates of human IgG (40 mg/kg, i.v.; I?arrea et al., Immunopharmacology 6:7, 1983).(ABSTRACT TRUNCATED AT 250 WORDS)     

Studies on the role of lipid peroxidation in the acute toxicity of TCDD in rats

Lipid peroxidation has been shown to be enhanced following exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), but its role in TCDD toxicity is unclear. The present study was undertaken to further elucidate the relations between lipid peroxidation and TCDD lethality. A time course and dose-response experiment in Long-Evans (L-E; LD50 ca. 10 micrograms/kg) and Han/Wistar (H/W; LD50 greater than 3000 micrograms/kg) rats showed that hepatic lipid peroxidation, measured as the amount of thiobarbituric acid-reactive substances (TBA-RS), was induced by TCDD dose-dependently in L-E, but not in H/W rats. Hepatic glutathione peroxidase activity was suppressed in much the same manner in both strains. Lipid peroxidation correlated with body weight loss in L-E rats alone. When 500 micrograms/kg of TCDD was given to L-E rats, lipid peroxidation increased about 3-fold on Day 11 in the liver, while no change was seen in cardiac or renal TBA-RS. The pair-fed controls did not survive the 11-day test period and exhibited gastrointestinal hemorrhages. At 6 days, liver atrophy and elevated (over 2-fold) TBA-RS values were recorded in pair-fed controls but not in their TCDD-treated counterparts. TCDD decreased hepatic glutathione peroxidase activity by almost 50% at 6 days, while pair-feeding was without effect. Liver morphology was different between TCDD-treated and pair-fed rats. Moreover, the livers of TCDD-treated L-E rats contained much higher concentrations of probably peripheral fat-derived fatty acids than did the livers of pair-fed or ad libitum control rats. Restricted feeding over 6 days induced hepatic lipid peroxidation more in H/W than in L-E rats. Endotoxin increased liver TBA levels similarly in both strains having an additive effect with high doses of TCDD in H/W rats. Added as a 0.5% concentration in chow, butylated hydroxyanisole (BHA), but not ethoxyquin, tended to increase survival rate and time in L-E rats exposed to 20 micrograms/kg of TCDD; at 50 micrograms/kg the only survivor was again in the BHA group. However, neither antioxidant had any effect on initial body weight loss. It is concluded that lipid peroxidation mainly arises as a secondary phenomenon in TCDD toxicity, is not the cause of the typical histopathological liver lesion, but may contribute to lethality.     

Toxicity and reproductive effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin in ring-necked pheasant hens.

Hen pheasants (Phasianus colchicus) injected with graded single doses of TCDD (6.25, 25, or 100 micrograms/kg) exhibited delayed-onset body weight loss and mortality--classic signs of the wasting syndrome. The lowest single dose of TCDD to produce this effect was 25 micrograms/kg. When hen pheasants were treated weekly with far lower doses of TCDD (0.01-1.0 microgram/kg/wk) for 10 wk, signs of the wasting syndrome and mortality were also produced. The lowest cumulative TCDD dose required to produce the response, using a weekly dosing regimen, was 10 micrograms/kg. Furthermore, using this dosing regimen, egg production by hens treated with a cumulative TCDD dose of 10 micrograms/kg was reduced, as was hatchability of their eggs. We conclude that hen pheasants are responsive to the overt toxic effects of TCDD and that the lowest cumulative dose of TCDD that produces overt signs of toxicity, 10 micrograms/kg, also reduces egg production and egg hatchability.     

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

In summary, the toxicity of TCDD has been comprehensively examined in multiple acute, subchronic, and chronic studies. Acute toxicity studies have shown marked species differences, with up to a 10,000-fold difference between the single oral LD50 dose for the guinea pig and hamster. TCDD is capable of causing an acnegenic response in man and a similar skin response in certain animals. It is also a potent inducer of microsomal enzymes in some but not all species. A dose-related suppression of cell-mediated immunity has been observed at higher dose levels in laboratory animals but not in humans manifesting TCDD-induced acnegenic response. TCDD causes a dose-related teratogenic response in mice, with the no-adverse-effect level of 0.1 micrograms TCDD/kg/day. In rats, TCDD causes embryo- and fetotoxicity above the no-adverse-effect level of 0.03-0.125 micrograms/kg/day. Dose-related reproductive effects have also been noted in monkeys at doses that elicit maternal toxicity, and additional long-term studies are presently underway. A multigeneration reproduction study as well as a lifetime chronic toxicity study have been completed with TCDD in rats; in both studies, the no-adverse-effect level was found to be 0.001 microgram TCDD/kg/day. Numerous mutagenic studies have been performed using in vitro plant and microbial test systems as well as in vivo tests in mammals and man. A mutagenic response was noted in a few of the vitro test systems, but there are no definitive in vivo correlates of TCDD mutagenicity in higher mammals or man. TCDD has been studied for carcinogenic potential in rats and mice. There is good correlation of the results, with a carcinogenic response noted in both species only after long-term ingestion of higher dose levels that induce toxicity. No carcinogenic response occurred at continuous dose levels of 0.001-0.0014 micrograms/kg/day in rats and 0.001-0.03 micrograms/kg/day in mice. Data presently available are more supportive of a nongenetic (?promotor) rather than a genetic mechanism of carcinogenesis. The most recent research, some of which is still underway, indicates that the biologic uptake and toxicity of TCDD may be significantly decreased if the TCDD is adsorbed onto carbon or soil particles. This information is helpful in hazard assessment of exposure to TCDD.     

Validation of Haber's Rule (dose x time = constant) in rats and mice for monochloroacetic acid and 2,3,7,8-tetrachlorodibenzo-p-dioxin under conditions of kinetic steady state

Haber's Rule and associated time to coma after monochloroacetic acid (MCA) exposure in male Sprague-Dawley (SD) rats and time to death after 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) exposure in female Sprague-Dawley rats and male A/J mice were investigated at isoeffective or nearly isoeffective doses. Animals exposed to MCA received either single bolus intravenous (iv) doses or a loading dose rate via the iv route followed by a maintenance dose rate through subcutaneously implanted osmotic mini pumps. For TCDD, rats received a loading dose rate via bolus oral gavage followed by maintenance dose rates through iv injection every fourth day until death. Mice received both loading and maintenance (once a week) dose rates via oral gavage. Different dosing regimens were employed to demonstrate that the key to Haber's Rule lies not in the route of administration but in conducting experiments under conditions of kinetic steady state. Single doses of MCA produced inconsistent time responses but a reasonably constant c x t product (7657+/-391 mg/kg x min) which was not anticipated although it should have been expected because MCA's elimination half-life (2 h) is twice as long as its time to coma ( approximately 1h). Generation of kinetic steady state by infusion of MCA after iv injection of a loading dose rate resulted in a consistently decreasing time response with increasing dose which diminished the variability in the c x t (dose x time)=k relationship (8032+/-136 mg/kg x min). Both acute and chronic toxicity of TCDD under conditions of kinetic steady state yielded consistent time responses with inverse proportionality between dose and time leading to robust c x t=k products in both rats (1060+/-82 microg/kg x day) and mice (80+/-2 mg/kg x day).