Effect of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on plasma and tissue beta-endorphin-like immunoreactivity in the most TCDD-susceptible and the most TCDD-resistant rat strain

Cell death induced by 2,3,7,8-tetrachlorodibenzo-p-dioxin (2,3,7,8-TCDD) in AtT-20 pituitary cells

The environmental man-made pollutant 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) has profound and deleterious effects on the endocrine system, and the pituitary gland is among TCDD endocrine target organs. In the present study, we have investigated the effects of TCDD (1 pM, 0.1 nM and 1 nM) on the AtT-20 pituitary cell line. TCDD induces cell death, with morphological and biochemical changes indicating the occurrence of both apoptotic and necrotic cell death. Exposed cells exhibited apoptotic features including DNA condensation, activation of caspase-3 and exposure of phosphatidylserine (PS) on the outer plasma membrane. Concomitantly, cells with necrotic morphology such as cell swelling and plasma membrane damage were also present. The relative level of Fas ligand mRNA was increased after TCDD exposure, as well as Fas and Fas ligand protein levels detected by Western blotting and immunocytochemistry. Taken together, the results suggest that TCDD induces both necrosis and apoptosis in the pituitary AtT-20 cells and that the Fas/FasL system plays a critical role in inducing necrotic cell death rather than apoptosis (supported by the Swedish Research Council).

Constitutive and TCDD-induced expression of Ah receptor-responsive genes in the pituitary

The 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and related substances cause a wide variety of pathological alterations, with the most severe being progressive anorexia and body weight loss. These features suggest a possible involvement of the nervous system and endocrine organs, including the pituitary gland. TCDD-related toxicity is considered mainly to be mediated by the aryl hydrocarbon receptor (AHR) protein, which binds TCDD, and heterodimerizes with its partner protein, the aryl hydrocarbon receptor nuclear translocator (ARNT), and binds to xenobiotica responsive elements (XREs) in the promoter regions of biotransformation genes as well as genes involved in growth, differentiation and cellular homeostasis. In the present study, we have investigated the expression of AHR responsive genes in the pituitary of untreated and TCDD treated 129/SV/C57BL/6 mice in vivo and in pituitary cells in vitro. After TCDD or beta-naphthoflavone (beta NF) treatment, the relative levels of cytochrome P4501A1 (CYP1A1) mRNA and protein were dramatically increased in pituitary cells. The AHR repressor (AHRR) mRNA level was induced 7-13-fold by TCDD and beta NF. Furthermore, the expression of the adrenocorticotrophic hormone (ACTH) precursor, the proopiomelanocortin (POMC) gene, was investigated. A three-fold increase in POMC mRNA was observed in the pituitary of TCDD treated mice. POMC mRNA level was also increased in the pituitary cell line AtT-20 after TCDD treatment. The proteins encoded by POMC translational products, ACTH and beta-endorphin, were found with immunocytochemistry staining to be increased in AtT-20 cells after TCDD exposure. The presence of several XRE sequences in the promoter region and in the first intron of the human POMC gene suggest that the up-regulation of POMC expression in the pituitary may play a role in the endocrine alterations induced by TCDD. All together, the results point to the pituitary gland being a direct target for TCDD.

A review of mechanisms controlling ovulation with implications for the anovulatory effects of polychlorinated dibenzo-p-dioxins in rodents

Polychlorinated dibenzo-p-dioxins (PCDDs) can impinge on female fertility by preventing ovulation. In this review, the aspects of normal ovulatory physiology most relevant to our current understanding of PCDD action on the ovary are briefly reviewed. This is followed by a comprehensive assessment of data relevant to the effects of PCDDs during ovulation in the rat. PCDDs interrupt ovulation through direct effects on the ovary in combination with dysfunction of the hypothalamo-hypophyseal axis.

2,3,7,8-tetrachlorodibenzo-p-dioxin decreases responsiveness of the hypothalamus to estradiol as a feedback inducer of preovulatory gonadotropin secretion in the immature gonadotropin-primed rat

Sprague-Dawley rats (23-day-old) were dosed with TCDD (32 microg/kg) in corn oil or vehicle alone. Equine chorionic gonadotropin (eCG) was injected (5 IU, sc) 24 h later to induce follicular development. Another 24 h later, half of TCDD- or corn oil-treated rats were injected (sc) with 17 beta-estradiol-cypionate (ECP, at 0.004 to 0.5 mg/kg). Blood and ovaries were collected on expected proestrous (preovulatory period) at 51, 54, and 58 h after eCG injection as well as in the morning after ovulation (72 h after eCG). Serum concentrations of 17 beta-estradiol (E), progesterone (P), luteinizing hormone (LH), and follicle-stimulating hormone (FSH) were determined by radioimmunoassay. The number of ova shed was measured at 72 h after injection of eCG by irrigating ova from oviducts. During the preovulatory period (approximately 58 h after eCG injection), a circulating level of 70-100 pg E/ml coincided with LH and FSH surges and later normal ovulation of 10 to 12 ova/rat was observed in controls. However, the same concentration of E was not associated with LH and FSH surges in rats treated with TCDD (32 microg/kg), resulting in reduced ovarian weight gain and reduction of ovulation by 70 to 80% (2-3 ova/rat). Blockage of the gonadotropin surge, reduced ovarian weight gain, and ovulation were all reversed completely by the lowest effective dose of ECP (0.1 mg/kg). At 72 h after eCG, serum P secretion was reduced and serum E levels were significantly increased compared to those of corn oil-treated controls. ECP alone had no effect on serum P levels at any time point, but in rats treated with TCDD and ECP, both the reduction of P (at 58 and 72 h) and the increase in E secretion (72 h) were completely reversed. Further studies confirmed that restoration by ECP of gonadotropin surges and associated ovulation could not be attained until circulating levels of E rose sufficiently high to trigger the LH and FSH surges. The new action threshold of E for inducing gonadotropin surges in rats treated with TCDD (32 microg/kg) was determined to be eight- to 10-fold higher than that in controls. Thus, it is apparent that TCDD decreased the responsiveness of the hypothalamus to E as a feedback inducer of preovulatory gonadotropin secretion.

In utero and lactational exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin: effects on development of the male and female reproductive system of the mouse

To evaluate effects of in utero and lactational 2,3,7,8-tetrachlorodibenzo-rho-dioxin (TCDD) exposure on male and female reproductive system development of the mouse, the offspring of pregnant ICR mice administered 0, 15, 30, or 60 microg TCDD/kg on Gestation Day (GD) 14 were examined at the postweanling, pubertal, young adult, and adult stages of development. Dam and offspring body weights and prenatal and postnatal mortality were unaffected by TCDD exposure. The most sensitive endpoints in male offspring were decreased ventral prostate, coagulating gland, and thymus weights, accelerated eye opening, and hydronephrosis. Decreases in pituitary gland weight and epididymal sperm numbers were also found in TCDD-exposed male offspring. Testis, epididymis, and dorsolateral prostate weights, anogenital distance, latencies to testis descent and to preputial separation, and serum testosterone concentrations were unaffected. At the highest maternal TCDD dose uterus weights were decreased in female offspring evaluated during estrus and diestrus. No morphologic changes in the external genitalia of female offspring were found, nor were there alterations in ovary or pituitary gland weights. Cross-species comparisons showed that the mouse was not as sensitive to TCDD-induced developmental reproductive toxicity as the rat and hamster. Many endpoints affected by TCDD in rat and hamster offspring were either not affected or were less sensitive in mouse offspring. Endpoints of androgenic status were not affected in the mouse, decreases in accessory sex organ weights were restricted to fewer organs in the mouse, and decreases in daily sperm production were not found in the mouse. The only developmental reproductive endpoint observed in all three species was a reduction in epididymal sperm numbers.

Toxic equivalency factors do not predict the acute toxicities of dioxins in rats

Risk evaluation of complex environmental mixtures of polychlorinated dibenzo-p-dioxins and related halogenated aromatic hydrocarbons (polychlorinated dibenzofurans, azo- and azoxybenzenes, naphthalenes and some of the biphenyls) is currently carried out by measuring the concentration of each congener in the mixture and then multiplying every figure by its specific constant, toxic equivalency factor (TEF). All congeners are thought to produce highly similar effects albeit at different doses, and the TEFs are believed to represent the potencies of the congeners relative to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), considered the most toxic derivative of this class of environmental contaminants. Here we compared the acute toxicities of TCDD, 1,2,3,7,8-penta-, 1,2,3,4,7,8-hexa- and 1,2,3,4,6,7,8-heptachloro-dibenzo-p-dioxin in the most TCDD-susceptible (Long-Evans Turku AB; L-E) and the most TCDD-resistant (Han/Wistar kuopio; H/W) rat strain. While L-E rats exhibited the expected rank order of sensitivities to the four dioxins, the higher chlorinated dioxins were more toxic than TCDD (in terms of acute lethality) to H/W rats, with the hexachlorodioxin showing the greatest potency. Even if the doses were adjusted according to the LD50 values, both biochemical and morphological effects elicited by the dioxins turned out to depend, often critically, on strain, congener or the interaction of these two determinants. These findings demonstrate that the dioxins have distinct profiles of acute toxicities and underscore the importance of response and test organism in defining the TEFs.

Strain as a determinant factor in the differential responsiveness of rats to chemicals

The beneficial effects derived from the use of chemicals in agriculture, energy production, transportation, pharmaceuticals, and other products that improve the quality of life are clearly established. However, continued exposure to these chemicals is only advantageous in conditions where the benefit far outweighs toxic manifestations. By law, determination of risk of toxicity necessitates the use of laboratory animals to establish whether chemical exposure is safe for humans. To simulate the human condition, it is incumbent upon investigators to choose a species in which pharmacokinetic and toxicokinetic principles are established and resemble those of humans. Some of the advantages to the use of rat in chemical toxicity testing include (a) similarities in metabolism, anatomy, and physiological parameters to humans; (b) the short life span, especially for carcinogenesis study; (c) the availability, ease of breeding, and maintenance at a relatively low cost; and (d) the existence of a large database to enable comparison of present to reported literature findings. However, the choice of rat can be complicated by several factors such as sex, age, and nutrition, but especially strain, where currently there are over 200 different strains of rat known to exist. The aim of this review is to demonstrate that there are differences in the responsiveness of rat strains to chemicals and that the susceptibility observed is dependent on the tissue examined. It is evident that the genotype differs among strains, and this may be responsible for differences in sensitivities to chemicals. Awareness of strain as a factor in susceptibility to toxicant action needs to be taken into account in interpretation of relevance of risk of toxicity for humans.

Biochemical effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and related compounds on the central nervous system

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) and related compounds are an important class of environmental contaminants which induce several types of biochemical alterations. Their effects have been most thoroughly characterized in the liver, especially regarding the Ah receptor-mediated induction of xenobiotic metabolizing enzymes. The behavioral signs exhibited by animals exposed to TCDD (progressive anorexia and body weight loss) suggest a role for the central nervous system (CNS) in TCDD toxicity. At lethal doses, TCDD affects the metabolism of serotonin, a neurotransmitter able to modulate food intake in the brain. This effect is associated with an elevated concentration of free tryptophan in the plasma. There does not appear to be any major changes in catecholaminergic neurotransmitter systems in TCDD-treated rats. Cytochrome P-450 related enzyme activities are induced by TCDD in the brain. As is the case in the liver, this induction does not correlate with susceptibility to TCDD lethality in rats. The involvement of the CNS in TCDD toxicity is still obscure. Elucidation of this role as well as the mechanism of TCDD-induced wasting may well advance our understanding of the regulation of food intake and body weight.

Subchronic (13-week) toxicity of heptachlorodibenzo-p-dioxin in male Sprague-Dawley rats

A 13-week oral toxicity study with 1,2,3,4,6,7,8-heptachlorodibenzo-p-dioxin (HpCDD) was performed in Sprague-Dawley rats. Rats received HpCDD at five different dose levels or 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) at one dose level. The doses were divided into 4 daily loading doses and 6 biweekly maintenance doses. At the end of the 13-week dosing period half of the rats were scheduled for necropsy and the other half after another 13-week off-dose period. This preliminary report contains only data from male rats during the 13-week main study period. At the two highest doses of HpCDD and in the TCDD dosage group the body weight or body weight gain was reduced. Mortality was 15, 50 and 5%, respectively. Wasting syndrome was the primary cause of death, but some rats died of hemorrhage without wasting, which may be related to the dose-dependent decrease in platelet counts. Phosphoenolpyruvate carboxykinase (PEPCK), the rate limiting enzyme of gluconeogenesis, was decreased only at the two highest dose levels of HpCDD and in the TCDD group, all of which also showed mortality. Ethoxyresorufin O-deetylase (EROD) was induced dose-dependently in all treated groups. Serum total thyroxine (T4) concentrations were decreased beginning at the middle dose of HpCDD. The study demonstrates that the toxicity observed after subchronic exposure to HpCDD is very similar to that of TCDD. Most importantly, most of the effects after subchronic and acute dose exposure are identical, confirming the validity of 0.007 as the toxic equivalency factor for HpCDD.