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

Sex-specific Effects of Endocrine-disrupting Chemicals on Brain Monoamines and Cognitive Behavior

The period of brain sexual differentiation is characterized by the development of hormone-sensitive neural circuits that govern the subsequent presentation of sexually dimorphic behavior in adulthood. Perturbations of hormones by endocrine-disrupting chemicals (EDCs) during this developmental period interfere with an organism's endocrine function and can disrupt the normative organization of male- or female-typical neural circuitry. This is well characterized for reproductive and social behaviors and their underlying circuitry in the hypothalamus and other limbic regions of the brain; however, cognitive behaviors are also sexually dimorphic, with their underlying neural circuitry potentially vulnerable to EDC exposure during critical periods of brain development. This review provides recent evidence for sex-specific changes to the brain's monoaminergic systems (dopamine, serotonin, norepinephrine) after developmental EDC exposure and relates these outcomes to sex differences in cognition such as affective, attentional, and learning/memory behaviors.

GH3 and RC-4BC cell lines are not suitable as in vitro models to study prolactin modulation and AHR responsiveness in rat pituitary

Some environmental contaminants and pharmaceuticals increase the incidence of uterine tumors in toxicological studies with rats. These tumors can result from a hormonal imbalance due to rat-specific disrupted pituitary prolactin regulation, and are therefore of questionable relevance for humans. In this study we compared in vitro prolactin regulation in rat primary pituitary cells to that in pituitary cell lines, GH3 and RC-4BC. Moreover, we assessed the potential effects of aryl hydrocarbon receptor (AHR) activation on prolactin regulation by using two different AHR agonists, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and DELAQ, the N-deethylated minor metabolite of the pharmaceutical laquinimod. In rat primary pituitary cells, known prolactin stimulant thyrotropin-releasing hormone (TRH) marginally increased prolactin secretion (1.2-fold) and gene expression (1.3-fold). In contrast, synthetic dopamine receptor agonist quinpirole, a known inhibitor of prolactin release, significantly inhibited prolactin secretion (2.6-fold) and gene expression (3.6-fold). In GH3 cells, TRH strongly increased prolactin secretion (6.8-fold) and gene expression (30.8-fold), whereas quinpirole did not affect prolactin secretion nor gene expression. In RC-4BC cells, both TRH and quinpirole did not modulate prolactin secretion nor gene expression. Prolactin secretion and gene expression did not significantly change upon exposure to TCDD or DELAQ. However, DELAQ, but not TCDD, attenuated quinpirole-inhibited prolactin gene expression by 51% in primary pituitary cells. This study shows that pituitary prolactin regulation in rat primary pituitary cells in vitro is distinctly different from rat pituitary cell lines GH3 and RC-4BC. Therefore, effects on pituitary prolactin regulation in vitro should best be performed using rat primary pituitary cells. Additionally, AHR ligands may interact with rat pituitary prolactin regulation, but this appears to depend on the ligand and constitutive prolactin secretion. However, interpretation of the in vitro results with respect to occurrence of uterine tumors in rats should take the complex regulation of prolactin release in the pituitary into account as well as the in vivo hypothalamus-pituitary-gonadal (HPG) axis and its feedback loops.

The Aryl Hydrocarbon Receptor and the Nervous System

The aryl hydrocarbon receptor (or AhR) is a cytoplasmic receptor of pollutants. It translocates into the nucleus upon binding to its ligands, and forms a heterodimer with ARNT (AhR nuclear translocator). The heterodimer is a transcription factor, which regulates the transcription of xenobiotic metabolizing enzymes. Expressed in many cells in vertebrates, it is mostly present in neuronal cell types in invertebrates, where it regulates dendritic morphology or feeding behavior. Surprisingly, few investigations have been conducted to unravel the function of the AhR in the central or peripheral nervous systems of vertebrates. In this review, we will present how the AhR regulates neural functions in both invertebrates and vertebrates as deduced mainly from the effects of xenobiotics. We will introduce some of the molecular mechanisms triggered by the well-known AhR ligand, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), which impact on neuronal proliferation, differentiation, and survival. Finally, we will point out the common features found in mice that are exposed to pollutants, and in AhR knockout mice.

Aryl hydrocarbon receptor activation in lactotropes and gonadotropes interferes with estradiol-dependent and -independent preprolactin, glycoprotein alpha and luteinizing hormone beta gene expression

Arylhydrocarbon receptor (Ahr) activation by 2,3,7,8-tetrachlordibenzo-p-dioxin (TCDD) interferes with female reproductive functions, but there is little information on the specific targets of TCDD in the hypothalamic-pituitary-gonadal (HPG) axis. In these studies, we found that TCDD upregulated known AhR target genes, cytochrome p450 1a1 (Cyp1a1), Cyp1a2 and Cyp1b1 in the rat pituitary gland. Moreover, 75% of pituitary lactotropes and 45% of gonadotropes contained Ahr mRNA, and most Ahr-containing cells were estrogen receptor 1 (Esr1)-positive. TCDD abrogated estradiol (E(2))-induced prolactin (Prl) expression in vivo and in vitro; conversely, E(2) blocked TCDD upregulation of luteinizing hormone beta (Lhb) and glycoprotein hormone alpha polypeptide (Cga) expression. TCDD had no effect on levels of Ahr mRNA, but upregulated Esr1 mRNA. E(2) independently repressed Ahr and Esr1 expression and blocked TCDD upregulation of Esr1. Thus, complex interactions between Ahr and Esr alter Prl and luteinizing hormone (LH) synthesis by direct actions in lactotropes and gonadotropes. These findings provide important insights into how TCDD disrupts female reproductive functions.

Neurological and neurophysiological examinations on workers with chronic poisoning by 2,3,7,8-TCDD: follow-up 35 years after exposure

Between 1965 and 1968, about 350 workers were accidentally exposed to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in a chemical plant, which was producing herbicides based on the trichlorophenoxyacetic acid. About 80 workers developed signs of poisoning. The estimated mean concentration of TCDD at the time of exposure was about 5000 pg/g of plasma fat. Only 15 subjects from the original cohort remained available for the recent follow-up in 2004. All were men, mean age 60 years. The mean current TCDD plasma concentration was 128 pg/g. Neurological examination revealed some CNS impairment in eight subjects. Signs of polyneuropathy were found in nine subjects, confirmed by NCV studies in three cases. Electroencephalography was abnormal in three cases; Visual-evoked potential in five cases. Acquired dyschromatopsia was detected in six patients. SPECT showed focal reduction of perfusion in various brain locations in all but one patient. Two neuropsychological variables and the frequency of abnormal neurophysiological tests in individual patients correlated with TCDD plasma level. The findings support the hypothesis that TCDD can damage the nervous system. In addition to a direct neurotoxic effect of TCDD, changes secondary to vasculopathy should be considered, in the pathophysiology of the damage, because of the high frequency of lipid metabolism disorders and their complications.

Adverse health effects in humans exposed to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)

The environmental contaminant 2,3,7,8-tetrachlordibenzo-p-dioxin (TCDD) belongs to the category of highly toxic, persistent organic pollutants that accumulate in animal fat and plant tissues. Today, background TCDD levels in human fat are showing a decreasing trend. The food chain is the main source of exposure in the human population. TCDD regulates the expression of a wide range of drug-metabolizing enzymes and has an impact on a large number of biological systems. The most pronounced effects have occurred in occupational settings following the uncontrolled formation of TCDD after industrial accidents, as well as in rare intentional intoxications. Although the acute effects of TCDD exposure are well described in the literature, the long-term consequences have been underevaluated. The most well-known symptoms of severe acute intoxication are chloracne, porphyria, transient hepatotoxicity, and peripheral and central neurotoxicity. Because of the long-term persistence of TCDD in the human body, atherosclerosis, hypertension, diabetes, vascular ocular changes, and signs of neural system damage, including neuropsychological impairment, can be present several decades after massive exposure. Such chronic effects are nonspecific, multifactorial, and may be causally linked to TCDD only in heavily intoxicated subjects. This opinion is supported by the dose-dependent effect of TCDD found in exposed workers and by experimental animal studies.

Expression of hypothalamic neuropeptides after acute TCDD treatment and distribution of Ah receptor repressor

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is an environmental contaminant originating from industrial waste. At sublethal concentrations it induces anorexia and weight loss as part of the so-called wasting syndrome. To gain insight into its possible underlying mechanisms, mRNA expression of some key hypothalamic neuropeptides involved in the regulation of body weight was studied using in situ hybridization histochemistry in adult male Sprague-Dawley rats 6 days after single oral administration of TCDD (15 microg/kg) and in age-paired control rats. In TCDD-treated rats which displayed a decrease in body weight gain vs. controls, arcuate nucleus expression of neuropeptide Y (NPY), proopiomelanocortin (POMC) and cocaine- and amphetamine-regulated transcript (CART) mRNA was increased. In the lateral hypothalamic area, melanin-concentrating hormone (MCH) mRNA expression was also increased, while levels of CART and orexin/hypocretin mRNA were not significantly changed. Since TCDD is known to bind to the aryl hydrocarbon receptor (AhR), the distribution of the AhR repressor (AhRR), which is co-expressed with AhR in the same cells, was studied by immunohistochemistry in the mouse hypothalamus using mouse AhRR specific antiserum. AhRR immunoreactivity was present in the nuclei of neurons found in all main hypothalamic groups including NPY, CART, MCH and orexin/hypocretin neurons. Xenobiotic response elements were found in these neuropeptide genes with the exception of MCH. Thus changes in expression of orexigenic and anorexigenic neuropeptides after TCDD treatment may help to explain the occurrence of the TCDD-induced weight loss, which may be either directly or indirectly related to the effects of TCDD on neuropeptide expression.

Expression, cellular distribution and induction of cytochrome p4501A (CYP1A) in gilthead seabream, Sparus aurata, brain

The presence and induction of cytochrome p4501A (CYP1A) in the brain of a teleost fish, the seabream, Sparus aurata, was studied. Cerebral CYP1A expression of control fish or fish exposed to various concentrations of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was assessed at the enzyme activity level-measured as 7-ethoxyresorufin-O-deethylase; at the protein level-measured by means of Western blot and ELISA; and at the mRNA level-estimated by means of RT-PCR. Cellular localization of CYP1A in the brain tissue was studied using immunohistochemistry. In non-exposed control fish, expression of CYP1A could be demonstrated only in the olfactory bulbs. After TCDD exposure, the olfactory bulbs still showed the highest expression levels of CYP1A, however, other brain regions were now CYP1A-positive as well. Immunohistochemical examination of brain tissue sections from control fish demonstrated CYP1A immunoreactive fibers in the ventral telencephalon, in the glomerular layer of the olfactory bulbs, and in the endothelia of the cerebral vascular system. The same structures reacted positive in TCDD-exposed fish, but cell bodies and fibers from additional brain areas including telencephalon, diencephalon, mesencephalon and cerebellum showed CYP1A immunostaining. In the pituitary of TCDD-treated fish, putative GTH cells were positive for CYP1A, whereas in control fish no staining of the adenohypophysis was observed. The present findings provide evidence for basal expression of CYP1A in the telencephalon of Sparus aurata, and for the presence of inducible CYP1A in all other major brain regions, including the pituitary.

Induction of oxidative stress in the tissues of rats after chronic exposure to TCDD, 2,3,4,7,8-pentachlorodibenzofuran, and 3,3',4,4',5-pentachlorobiphenyl

The abilities of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 2,3,4,7,8-pentachlorodibenzofuran (PeCDF), 3,3',4,4',5-pentachlorobiphenyl (PCB126), and mixtures of these xenobiotics (toxic equivalents, TEQs) to induce oxidative stress in hepatic and brain tissues of rats have been investigated after chronic (30 wk) exposure to these congeners. TCDD, PeCDF, PCB126, and TEQs were administered daily to groups of rats at doses that corresponded to their toxic equivalency factors (TEFs), and the biomarkers of oxidative stress, including the production of superoxide anion, lipid peroxidation, and DNA single-strand breaks (SSBs), were determined in hepatic and brain tissues at the end of the exposure period. The three chemicals caused similar dose-dependent increases in the production of superoxide anion, lipid peroxidation, and DNA SSBs, which plateaued at certain dose ranges, followed by secondary increases at the higher dose levels. Similar effects were also produced by the TEQs; however, the dose-dependent increases in the biomarkers of oxidative stress were continuous and never achieved plateau levels. Except for PCB126, where statistical analyses revealed greater productions of superoxide anion and lipid peroxidation in brain tissues as compared with hepatic tissues, no significant differences were revealed between the two tissues in response to the other xenobiotics or the TEQs. Nonsignificant differences were also revealed when comparing the effects induced by the TEQs with those induced by the individual chemicals.

Persistent abnormalities in the rat mammary gland following gestational and lactational exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) exposure during gestation has revealed reproductive anomalies in rat offspring, including inconclusive reports of stunted mammary development in females (Brown et al., 1998, Carcinogenesis 19, 1623-1629; Lewis et al., 2001, TOXICOL: Sci. 62, 46-53). The current studies were designed to examine mammary-gland development in female offspring exposed in utero and lactationally to TCDD, and to determine a critical exposure period and cellular source of these effects. Long-Evans rats were exposed to 1 microg TCDD/kg body weight (bw) or vehicle on gestation day (GD) 15. TCDD-exposed females sacrificed on postnatal days (PND) 4, 25, 33, 37, 45, and 68 weighed significantly less than control litter mates, and peripubertal animals exhibited delayed vaginal opening and persistent vaginal threads, yet did not display altered estrous cyclicity. Mammary glands taken from TCDD-exposed animals on PND 4 demonstrated reduced primary branches, decreased epithelial elongation, and significantly fewer alveolar buds and lateral branches. This phenomenon persisted through PND 68 when, unlike fully developed glands of controls, TCDD-exposed rats retained undifferentiated terminal structures. Glands of offspring exposed to TCDD or oil on gestation days 15 and 20 or lactation days 1, 3, 5, and 10 were examined on PND 4 or 25 to discern that GD 15 was a critical period for consistent inhibition of epithelial development. Experiments using mammary epithelial transplantation between control and TCDD-exposed females suggested that the stroma plays a major role in the retarded development of the mammary gland following TCDD exposure. Our data suggest that exposure to TCDD prior to migration of the mammary bud into the fat pad permanently alters mammary epithelial development in female rat offspring.

Altered ethylbenzene-mediated hepatic CYP2E1 expression in growth hormone-deficient dwarf rats

Ethylbenzene (EB) effectively induces several hepatic P450 enzymes including CYP2E1 and CYP2B. Hypophysectomy diminishes the magnitude of EB-mediated induction of CYP2B. Although growth hormone (GH) plays a key role in sexual dimorphism of CYP2C11, its impact on EB-mediated P450 expression is still unknown. Because hypophysectomy leads to a depletion of multiple pituitary hormones besides GH, a study was designed to investigate the possible involvement of GH in EB-mediated hepatic P450 expression using GH-deficient dwarf rats as a more specific animal model. In these rats, pituitary GH was selectively reduced to about 10% of normal levels and other pituitary trophic hormones including thyroid-stimulating hormone, adrenocorticotropic hormone, luteinizing hormone, follicle-stimulating hormone, and prolactin are largely unchanged. Male control and HsdOla:DWARF-dw-4 (Harlan, UK) rats were subjected to a single ip injection of EB (10 mmol/kg). CYP2E1- and CYP2B-dependent activities, protein, and RNA levels were measured 10 and 24 h afterward. The results indicated that dwarf rats without EB exposure expressed higher CYP2E1. Although EB treatment induced CYP2E1 activity, protein, and mRNA both in controls and dwarf rats, the magnitude of the response to EB exposure was greater 10 h after the treatment in dwarf rats. Hypophysectomy also increased CYP2E1 protein induction by EB compared to intact rats. This effect was reversed by GH supplementation to hypophysectomized rats. Overall, responses of CYP2B to EB exposure in dwarf rats did not display basic differences from controls. In conclusion, the results demonstrate that (1) the suppression of CYP2B induction found in the multi-hormone-deficient HX rats is not found in the more specific GH-deficient rat model, confirming that GH does not have a major influence on CYP2B expression and (2) both hypophysectomized and GH-deficient rats show an altered inducibility of CYP2E1 after EB treatment.

Production of superoxide anion, lipid peroxidation and DNA damage in the hepatic and brain tissues of rats after subchronic exposure to mixtures of TCDD and its congeners

In this study the induction of oxidative stress in the hepatic and brain tissues of rats after subchronic exposure to various mixtures of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and two of its congeners, namely 2,3,4,7,8-pentachlorodibenzofuran (PeCDF) and 3,3',4,4',5-pentachlorobiphenyl (PCB 126) was investigated. Four mixtures of TCDD and its congeners, corresponding to 10, 22, 46 and 100 ng of toxic equivalence (TEQ) kg(-1) day(-1), were administered to groups of rats for 13 weeks. The animals were sacrificed at the end of the exposure period and the biomarkers of oxidative stress, including the production of superoxide anion, lipid peroxidation and DNA single-strand breaks (SSBs), were determined in the hepatic and brain tissues. All mixtures caused dose-dependent increases in the production of superoxide anion, lipid peroxidation and DNA SSBs in both tissues, with significantly higher damage in the hepatic compared with the brain tissues. The 22 ng TEQ dose level (TEQ = 22) contains TCDD, PeCDF and PCB 126 at levels that correspond to 7.3, 14.5 and 73.3 ng kg(-1) day(-1), respectively, and it produced effects that correspond to ca. 50% of the maximal production of superoxide anion, lipid peroxidation and DNA SSBs in the hepatic and brain tissues of those animals. Relative to the doses that are required to produce 50% of the maximal production of the biomarkers of oxidative stress by the individual congeners in hepatic and brain tissues of rats, the concentrations of the congeners in TEQ = 22 did result in significant interactivity, probably in the form of additive effects in the hepatic but not in brain tissues.

Effect of 2,3,7,8-tetrachlorodibenzo-p-dioxin on the expression of cytochrome P450 1A1, the aryl hydrocarbon receptor, and the aryl hydrocarbon receptor nuclear translocator in rat brain and pituitary

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) and related substances are ubiquitous environmental pollutants causing 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 neuroendocrine-related organs including the pituitary gland. However, so far there is little evidence for direct effects of TCDD on these areas. In the present study, male Sprague-Dawley rats were treated with a single oral dose of TCDD (10 microg/kg) and euthanized 1, 3, or 28 days after treatment. The expression of cytochrome P450 1A1 (CYP1A1), the aryl hydrocarbon receptor (AHR), and the aryl hydrocarbon receptor nuclear translocator (ARNT) were analyzed in different brain regions and pituitaries using semiquantitative RT-PCR and Western blotting. Relative levels of CYP1A1 mRNA and protein were dramatically increased in the pituitary. A significant increase in CYP1A1 mRNA was also detected in all the brain regions examined including olfactory bulb, striatum-caudate, hypothalamus, hippocampus, cortex, cerebellum, and substantia nigra. The increase in the expression was time-dependent with the highest level observed 1 day after TCDD treatment. The AHR and ARNT mRNAs were detected in the same areas but in contrast to CYP1A1 the changes in AHR and ARNT mRNA expression were limited to the 28-day time point. The present results provide evidence for the presence of CYP1A1, AHR, and ARNT in the central nervous system and in the pituitary, suggesting that TCDD may exert a direct effect on these regions.

Distribution of mRNAs encoding the arylhydrocarbon receptor, arylhydrocarbon receptor nuclear translocator, and arylhydrocarbon receptor nuclear translocator-2 in the rat brain and brainstem

Dioxin exposure alters a variety of neural functions, most likely through activation of the arylhydrocarbon receptor (AhR) pathway. Many of the adverse effects, including disruption of circadian changes in hormone release and depressed appetite, seem to be mediated by hypothalamic and/or brainstem neurons. However, it is unclear whether these effects are direct or indirect, because there have been no comprehensive studies mapping the expression of components of the AhR pathway in the brain. Therefore, we used a sensitive in situ hybridization histochemical (ISHH) method to map the neural expression of AhR mRNA, as well as those of the mRNAs encoding the AhR dimerization partners, arylhydrocarbon receptor nuclear translocator (ARNT) and ARNT2. We found that AhR, ARNT, and ARNT2 mRNAs were widely distributed throughout the brain and brainstem. There was no neuroanatomic evidence that AhR is preferentially colocalized with ARNT or ARNT2. However, ARNT2, unlike ARNT expression, was relatively high in most regions. The most noteworthy regions in which we found AhR, ARNT, and ARNT2 mRNA were several hypothalamic and brainstem regions involved in the regulation of appetite and circadian rhythms, functions that are disrupted by dioxin exposure. These regions included the arcuate nucleus (Arc), ventromedial hypothalamus (VMH), paraventricular nucleus (PVN), suprachiasmatic nucleus (SCN), nucleus of the solitary tract (NTS), and the dorsal and median raphe nuclei. This neuroanatomic information provides important clues as to the sites and mechanisms underlying the previously unexplained effects of dioxins in the central nervous system.

The relative abilities of TCDD and its congeners to induce oxidative stress in the hepatic and brain tissues of rats after subchronic exposure

The abilities of single doses of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) to induce oxidative stress in hepatic and some extra-hepatic tissues of animals, are well documented. In this study we have investigated the induction of oxidative stress in hepatic and brain tissues of rats after subchronic (13 weeks) exposure to TCDD and two of its congeners, namely 2,3,4,7,8-pentachlorodibenzofuran (PeCDF) and 3,3',4,4',5-pentachlorobiphenyl (PCB126). TCDD, PeCDF and PCB126 were administered daily to groups of rats at various doses, for 13 weeks, and biomarkers of oxidative stress, including the production of superoxide anion, lipid peroxidation and DNA-single strand breaks (SSBs), were determined in the hepatic and brain tissues at the end of the exposure period. The three congeners caused dose-dependent increases in the production of superoxide anion, lipid proxidation and DNA-SSBs, with maximal effects achieved at doses ranging between 10-100, 20-92, and 300-550 ng/kg per day for TCDD, PeCDF and PCB126, respectively. The doses that produce 50% of maximal responses by each of the xenobiotics in the hepatic and brain tissues were found to be within the ranges of 7-34, 13-32, and 137-400 ng/kg per day for TCDD, PeCDF and PCB126, respectively. The results of the study suggest that subchronic exposures to TCDD, PeCDF and PCB126 induce significant oxidative damage in the hepatic and brain tissues of rats, with more damage observed in the brain as compared to the hepatic tissues. Also, as inducers of oxidative stress in the hepatic and brain tissues, TCDD is the most potent among the three congeners and PCB126 being the least potent.

Interference with growth hormone stimulation of hepatic cytochrome P4502C11 expression in hypophysectomized male rats by 3-methylcholanthrene

Cytochrome P450 2C11 (CYP2C11) is a sexually dimorphic liver enzyme whose expression is regulated by the male pulsatile pattern of growth hormone (GH) secretion. Hepatic CYP2C11 expression is down-regulated by polycyclic aromatic hydrocarbons such as 3-methylcholanthrene (MC). An attractive hypothesis as to the mechanism of CYP2C11 down-regulation by aromatic hydrocarbons is the disruption of normal GH signaling by exposure to these compounds. To evaluate the effects of MC on the ability of GH to stimulate hepatic CYP2C11 expression, our approach was to employ GH replacement in male Fischer 344 rats made GH-deficient by hypophysectomy (hypx). Groups of hypx rats received the following treatments: vehicle; GH alone (twice daily, 125 microg/kg sc, days 1-6); MC alone (20 mg/kg gavage, days 1, 3, and 5); and both GH and MC. Rats were euthanized on day 7. As a positive control response, pronounced induction of hepatic CYP1A1 apoprotein was observed in all MC-treated rats. CYP2C11 expression in hypx rats receiving GH alone was increased at the mRNA, apoprotein, and catalytic activity (testosterone 16alpha-hydroxylation) levels, with mRNA and apoprotein levels approaching that of intact male rats. The inability of GH to fully restore CYP2C11 catalytic activity was attributed to the lowered NADPH-cytochrome P450 reductase apoprotein and catalytic activity observed in all hypx rats. CYP2C11 expression in hypx rats receiving both GH and MC was significantly lower at the mRNA, apoprotein, and catalytic activity levels than that observed in hypx rats treated with GH alone, but significantly higher at the mRNA, apoprotein, and catalytic activity levels than that observed in vehicle-treated hypx rats and in hypx rats treated with MC alone. These data suggest that MC interferes with the ability of GH to stimulate CYP2C11 expression. Thus, disruption of GH signaling by aromatic hydrocarbons may represent a mechanism contributing to the suppression of CYP2C11 gene expression.

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.

Peri- and postnatal exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin: effects on physiological development, reflexes, locomotor activity and learning behaviour in Wistar rats

Effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on the development of rat offspring were studied after administration of a loading dose of 300 or 1000 ng TCDD/kg body wt on day 19 of pregnancy, followed by weekly maintenance doses of 120 or 400 ng TCDD/kg body wt. The dose regimens led to a fluctuation of average TCDD concentrations in the liver of the offspring of 4.9-14.9 ng/g (TCDD1000/400 group) or 1.4-6.3 ng/g (TCDD300/120 group) during the course of the experiment. In both TCDD-exposed groups the body weight of the offspring was significantly lower on postnatal day 7 (PND 7); in the high dose group from PND 7 to PND 31. Some landmarks of postnatal development were retarded in the exposed groups; in particular, the vaginal opening was delayed for several days in both TCDD-exposed groups. The TCDD-exposed animals revealed a reduced ability to remain on a rotating rod. During reflex testing, the rate of successfully responding animals was higher in the exposed groups. No statistically significant differences in the locomotor activity between controls and TCDD-exposed offspring were detectable under our experimental conditions. In a discrimination learning test no effects on the learning ability were found. However, TCDD-exposed offspring showed an increase in unanswered trials during critical phases of the task. They also exhibited increased locomotor activity in a novel environment; prior to an amphetamine challenge dose of 1 mg/kg body weight. Amphetamine-induced activity was decreased in a dose-dependent manner.

Suppression of prolactin and cytotoxic T-lymphocyte activity in PCB-treated mice

Halogenated aromatic hydrocarbons (HAH) are ubiquitous environmental contaminants. Studies in rats have shown that HAH treatment can lead to dysregulation of circulating hormone levels, including prolactin. Reduction of prolactin levels in both rats and mice is inhibitory to immune function. Previous studies have reported suppression of alloantigen-specific cytotoxic T-lymphocyte (CTL) activity in mice treated with 3,3', 4,4', 5,5'-hexachlorobiphenyl (HxCB). Here we report that treatment of mice with HxCB (10 mg/kg body weight) leads to a significant reduction of serum prolactin levels (by 89% to 3.7 ng/ml) on day 10 post alloantigen injection (P815 mastocytoma), the day of peak alloantigen-specific CTL activity. Prolactin levels were not altered on day 3 post alloantigen injection. Treatment with bromocriptine (5 mg/kg/day) reduced serum prolactin levels slightly on day 3 and significantly (94% to 2.1 ng/ml) on day 10 post alloantigen injection. Splenic CTL activity was not altered by treatment with bromocriptine. The data presented here suggest that reduction of prolactin levels alone, to the extent observed in HxCB-treated mice, is not causative for CTL suppression.

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.

Acute neurobehavioural effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in Han/Wistar rats

The neurobehavioural effects of a single non-lethal dose (1000 micrograms/kg intraperitoneally) of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) were assessed in young male Han/Wistar rats, highly resistant to acute lethality of TCDD. TCDD decreased body weight significantly compared with ad libitum fed controls. TCDD did not change the behaviour or the motility of rats in the open field test 8 days after the treatment nor did it affect the spontaneous motor activity up to 27 days after the exposure. In the elevated plus-maze test for anxiety, TCDD-treated rats did not differ from either ad libitum fed controls or pair-fed controls. In the 24-hr passive avoidance test, the learning of TCDD-treated rats did not differ significantly from that of ad libitum fed controls or pair-fed controls from 8 hr to 16 days after the treatment. TCDD did not affect the motor coordination or the maintenance of balance on the rotating rod but it impaired them slightly in the elevated horizontal bridge test 16 hr after exposure. It did not affect nociception in the hot plate test 16 hr or 8 days after the injection. The results suggest that a single sublethal dose of TCDD does not alter markedly the general behaviour of Han/Wistar rats, in contrast to its striking effect on feeding behaviour which results in a marked decrease in body weight gain.

Effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on humoral immunity: I. Similarities to Staphylococcus aureus Cowan Strain I (SAC) in the in vitro T-dependent antibody response

We have determined that suppression of the in vitro T-dependent humoral immune response by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) is dependent on the type and concentration of serum used in the culture media. Only five out of 23 commercial lots of serum (screened at both 5 and 10%) could support a suppression in the presence of 30 nM TCDD, with the remaining lots demonstrating an apparent 'protective-like' effect against the TCDD exposure. When log dose response curves were established with TCDD (0.3, 3.0, and 30 nM) in media containing each of the serum lots supporting a suppression (at both 5 and 10%), we determined that only three lots could support a full dose-responsive suppression. Subsequently, in a comparison study between the effects of TCDD and the polyclonal B-cell activator Staphylococcus aureus Cowan Strain I (SAC) on the in vitro T-dependent humoral immune response, we have found that SAC suppresses the antibody response to SRBC and demonstrates the same serum dependency for this effect as was previously noted for TCDD. Under serum-free culturing conditions, TCDD (30 nM) caused a 15-fold increase in the AFC response to SRBCs over controls, suggesting that direct addition of TCDD to whole splenocyte cultures in the absence of serum-derived growth factors results in an increase in B-cell activation. Likewise, under serum-free conditions, SAC dose-dependently increased the AFC response over media controls, and at doses which achieved the same degree of suppression of the humoral response aa TCDD. Taken together, these studies suggest that TCDD has actions that are similar to a T cell independent polyclonal B cell activator such as SAC, and selectively acts on the B cell to suppress the T-dependent humoral immune response by a mechanism which is unique to this series of compounds. This effect however, is only detectable under appropriate serum-supported (or serum-deficient) culture conditions as described.

Changes in rat brain monoamines, monoamine metabolites and histamine after a single administration of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)

Male Long-Evans rats were given 50 micrograms/kg 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) intraperitoneally and after 1, 4, 28 or 76 hr, noradrenaline, dopamine, dihydroxyphenylacetic acid (DOPAC), homovanillic acid (HVA), 5-hydroxytryptamine (5-HT), 5-hydroxyindoleacetic acid (5-HIAA), tryptophan and histamine were measured in the brain (dissected into ten parts) as well as in the pituitary gland. Several slight but significant changes were observed, e.g. in the hypothalamus where HVA and 5-HIAA were decreased after 4 hr, noradrenaline was decreased after 76 hr and histamine increased after 28 hr. Several late changes were also found, conspicuously tryptophan was increased in most brain areas after 76 hr and in some cases earlier; these changes may be due to starvation after hypophagia rather than TCDD directly. The results demonstrate that TCDD causes changes in brain neurotransmitter systems, but the changes are minor and it is not likely that aminergic systems are the key mediators in TCDD-induced 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.

Suppression of male-specific cytochrome P450 2c and its mRNA by 3,4,5,3',4',5'-hexachlorobiphenyl in rat liver is not causally related to changes in serum testosterone

Rat cytochrome P450 2c (P450 gene IIC11) is a constitutive, male-specific hepatic enzyme which is suppressed greater than 90% by treatment with 3,4,5,3',4',5'-hexachlorobiphenyl (HCB) [H. N. Yeowell et al. (1987) Mol. Pharmacol. 32, 340-347]. HCB also decreases serum testosterone levels in adult male rats (greater than 98% loss). The present study assesses whether the suppression of P450 2c by HCB is a direct result of its effects on serum testosterone levels. Further, the site along the hypothalamic-pituitary-testicular axis at which HCB acts to depress testosterone secretion was examined. Administration of the synthetic androgen methyltrienolone to HCB-treated rats failed to prevent the suppression of P450 2c mRNA and its associated microsomal steroid 16 alpha-hydroxylase activity under conditions where it effectively reversed the large decrease in P450 2c mRNA and steroid 16 alpha-hydroxylase activity produced by castration. Hepatic steroid 6 beta-hydroxylase activity, which is catalyzed primarily by P450 2a (P450 gene IIIA2), was also suppressed by HCB and was not protected by methyltrienolone. Administration of either human chorionic gonadotropin, an analog of pituitary-derived luteinizing hormone, or the hypothalamic luteinizing hormone releasing hormone elevated serum testosterone levels to a much smaller extent in HCB-treated rats than in control rats. These results indicate that the effects of HCB on serum testosterone levels reflect its effects on testicular function rather than the pituitary or hypothalamus. However, the present study demonstrates that the consequential reduction in serum testosterone levels in HCB-treated rats is not causally related to the reduction in hepatic P450 2c levels. Thus, HCB must also act on some other regulatory mechanism involved in the expression of this protein.

Plasma concentrations of pituitary hormones in 2,3,7,8-tetrachlorodibenzo-p-dioxin-treated male rats

Experiments were conducted to test the hypothesis that acute TCDD toxicity is associated with pituitary hypofunction. Sexually mature male Sprague-Dawley rats were given graded doses of TCDD (0-100 micrograms/kg) and evaluated 7 days later. Despite pronounced hypophagia and body weight loss, plasma concentrations of growth hormone (GH), follicle-stimulating hormone (FSH), and luteinizing hormone (LH) were not significantly affected by any dose of TCDD. Only prolactin (PRL) concentrations were reduced, while, as previously reported, thyroid-stimulating hormone concentrations were elevated. Also, plasma LH, PRL, and adrenocorticotropic hormone (ACTH) concentrations were not significantly affected 1, 2, 3, 4, 5, or 7 days after a single dose of TCDD (50 micrograms/kg). We conclude that (1) pituitary hypofunction is not a major cause of the initial stages of acute TCDD toxicity, (2) growth retardation in TCDD-treated rats is not the result of a deficiency of GH, (3) alterations in plasma corticosterone concentrations are due to altered responsiveness of the adrenal to ACTH stimulation rather than to changes in plasma ACTH concentrations, and (4) that impaired spermatogenesis is not associated with a decrease in plasma FSH concentrations. In addition, the lack of a consistent effect on plasma PRL concentrations suggests that alterations in plasma PRL concentrations do not play a critical role in the toxicity of TCDD. Finally, because TCDD treatment causes a serious androgenic deficiency without increasing the rates at which androgens are catabolized or excreted, the fact that plasma LH concentrations were unaffected indicates that TCDD treatment must reduce the responsiveness of the testis to LH stimulation.(ABSTRACT TRUNCATED AT 250 WORDS)