Melatonin preserves ovarian tissues of rats exposed to chronic TCDD: An electron microscopic approach to effects of TCDD on ovarian cells

2,3,7,8-Tetrachlorodibenzo- p-dioxin (TCDD) is a toxic agent and has disruptive effects on reproductive tissues in females. TCDD disrupts the hormonal regulation of the body and decreases the production of melatonin. In this study, we investigated the protective effects of melatonin supplements against the toxic effects of TCDD on ovaries of female rats. TCDD caused a significant decrease in the average number of corpora lutea and follicles per tissue section (2.1 ± 0.7; 2.3 ± 0.8, respectively), whereas these numbers were maintained in the melatonin supplemented group (5.0 ± 0.8; 5.1 ± 0.8, respectively) and were similar to the control group (5.3 ± 1.0; 5.9 ± 0.9, respectively). Electron microscopic analysis showed that the disruption of ultrastructure components such as cell membrane and organelles due to TCDD exposure was inhibited by melatonin supplements. This study suggested that melatonin has a protective and a possible ameliorative effect over histopathological damage of rat ovaries exposed to TCDD.

Molecular perspectives and recent advances in microbial remediation of persistent organic pollutants

Nutrition and pollution stress stimulate genetic adaptation in microorganisms and assist in evolution of diverse metabolic pathways for their survival on several complex organic compounds. Persistent organic pollutants (POPs) are highly lipophilic in nature and cause adverse effects to the environment and human health by biomagnification through the food chain. Diverse microorganisms, harboring numerous plasmids and catabolic genes, acclimatize to these environmentally unfavorable conditions by gene duplication, mutational drift, hypermutation, and recombination. Genetic aspects of some major POP catabolic genes such as biphenyl dioxygenase (bph), DDT 2,3-dioxygenase, and angular dioxygenase assist in degradation of biphenyl, organochlorine pesticides, and dioxins/furans, respectively. Microbial metagenome constitutes the largest genetic reservoir with miscellaneous enzymatic activities implicated in degradation. To tap the metabolic potential of microorganisms, recent techniques like sequence and function-based screening and substrate-induced gene expression are proficient in tracing out novel catabolic genes from the entire metagenome for utilization in enhanced biodegradation. The major endeavor of today's scientific world is to characterize the exact genetic mechanisms of microbes for bioremediation of these toxic compounds by excavating into the uncultured plethora. This review entails the effect of POPs on the environment and involvement of microbial catabolic genes for their removal with the advanced techniques of bioremediation.

Very low-dose (femtomolar) 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) disrupts steroidogenic enzyme mRNAs and steroid secretion by human luteinizing granulosa cells

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is the most toxic congener of the polyhalogenated aromatic hydrocarbons (PAH), which causes anatomical abnormalities and developmental defects, impairs ovulation and reduces fertility. TCDD's endocrine-disrupting effects are, in part, caused by a direct action at the ovary. Herein we investigated the in-vitro effects of environmentally relevant doses of TCDD on estradiol-17β (E2) production by human luteinizing granulosa cells (hLGC) obtained from women stimulated for in-vitro fertilization (IVF). TCDD at all concentrations tested (3.1fM, 3.1pM and 3.1nM) significantly decreased E2 secretion when assayed for by radioimmunoassay (RIA). Herein we confirm that TCDD alters E2 secretion by hLGC in a time-, not dose-dependent fashion and are the first to show decreases in E2 secretion with fM concentrations of TCDD. Using real-time quantitative PCR (RT-qPCR), the decreased E2 secretion correlates with a decrease in the mRNA expression levels two enzymes in the estrogen biosynthesis pathway: CYP11A1 and CYP19A1.

Decreased vitellogenin inducibility and 17β-estradiol levels correlated with reduced egg production in killifish (Fundulus heteroclitus) from Newark Bay, NJ

Aquatic species inhabiting polluted estuaries are exposed to complex mixtures of xenobiotics which can alter normal reproduction. We previously reported that female Atlantic killifish (Fundulus heteroclitus) from the highly contaminated Newark Bay, NJ (USA) exhibited an inhibition of oocyte development due to reduced vitellogenin (egg-yolk precursor) levels. Our hypothesis was that the inhibition of oocyte development in Newark Bay killifish is due to (1) deficient levels of circulating 17β-estradiol, and (2) a decreased sensitivity of the vitellogenin pathway to physiological doses of 17β-estradiol. In the first study, adult naïve killifish from Tuckerton, NJ (reference) were caged at Tuckerton and Newark Bay. After 1 month, males caged at Newark Bay exhibited inductions of hepatic vitellogenin and estrogen receptor α, which were transient and returned to basal levels after 2 months (p≤0.05). In the second study, fecundity and 17β-estradiol levels were measured in reproductively active adult females from Tuckerton and Newark Bay. Tuckerton females produced 140 eggs per female and Newark Bay females produced 11 eggs per female. Embryos from Newark Bay had 34% greater mortality and 28% less hatch, relative to Tuckerton. In addition, embryo mass and yolk-volume of Newark Bay embryos compared to Tuckerton embryos was 16% and 25% lower, respectively. Circulating 17β-estradiol levels in Newark Bay females (0.26 ng/mL) were measured to be 8-fold lower than Tuckerton females (2.25 ng/mL). In the third study, adult killifish from both sites were dosed with 17β-estradiol to assess the sensitivity of the vitellogenin pathway. At doses of 0.01, 0.1, 1 and 10 ng/g body weight, induction levels of circulating vitellogenin in Newark Bay males were significantly inhibited by 97, 99, 98 and 44%, respectively, compared to Tuckerton males. At doses of 0.01, 0.1, 1, 10 and 100 ng/g body weight, induction levels of circulating vitellogenin in Newark Bay females were inhibited by 89, 79, 61, 40 and 30%, respectively, compared to Tuckerton females. These differences in inducibility could not be explained by altered hepatic expression of estrogen receptors α, βa or βb. Based on the caged and dose-response studies, contaminants that down-regulate vitellogenin would interfere with its ability to be used as a biomarker for xeno-estrogen exposures. These studies demonstrate that contaminants within Newark Bay exert both estrogenic and anti-estrogenic responses which results in an overtly anti-estrogenic phenotype (reduced egg production due to inhibition of vitellogenesis).

Theoretical targets for TCDD: a bioinformatics approach

Dioxins are a group of highly toxic molecules that exert their toxicity through the activation of the aryl hydrocarbon receptor (AhR). The most important agonist of the AhR, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) is a highly toxic compound. Although most of the effects related to TCDD exposure have been linked to the activation of AhR, the objective of this work was to use a bioinformatics approach to identify possible new targets for TCDD. The Target Fishing Docking (TarFisDock) Server was used to find target proteins for TCDD. This virtual screening allowed the identification of binding sites with high affinity for TCDD in diverse proteins, such as metallopeptidases 8 and 3, oxidosqualene cyclase, and myeloperoxidase. Some of these proteins are well known for their biochemical role in some pathological effects of dioxin exposure, including endometriosis, diabetes, inflammation and liver damage. These results suggest that TCDD could also be interacting with cellular targets though AhR-independent pathways.

Autoradiographic localization of aromatic hydrocarbon receptor (AHR) in rhesus monkey ovary

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is the most toxic congener of a large class of manmade pollutants that persist in the environment. TCDD exerts its toxic effects, in part, by binding to its receptor known as the aromatic hydrocarbon receptor (AHR). TCDD is estrogen modulatory and in some systems its receptor associates directly with estrogen receptors via co-activator molecules. TCDD inhibits steroid synthesis in human ovarian granulosa cells and AHR is found in these cells. We have previously shown that AHR is found in whole rhesus monkey ovary, but have yet to establish its location. In the present study, we set out to show that radiolabeled TCDD binds to monkey ovarian follicles and that this binding is receptor mediated. Ovaries from Macaca mulatta were sectioned on a cryostat at 10 micro m; and sections were incubated with either control vehicle, (3)H-TCDD, or (3)H-TCDD plus alpha-naphthoflavone (ANF), a known receptor-blocking agent. Here, we show for the first time specific binding of TCDD to the granulosa cells of antral follicles and other regions of the rhesus monkey ovary. Our data indicate a 60-fold increase in binding with (3)H-TCDD over that of control, and that this binding is reduced to the levels seen in controls with the addition of the competitive antagonist ANF. These findings support the hypothesis that TCDD directly affects primate ovarian function via the AHR.

Molecular targets of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) within the zebrafish ovary: insights into TCDD-induced endocrine disruption and reproductive toxicity

TCDD is a reproductive toxicant and endocrine disruptor, yet the mechanisms by which it causes these reproductive alterations are not fully understood. In order to provide additional insight into the molecular mechanisms that underlie TCDD's reproductive toxicity, we assessed TCDD-induced transcriptional changes in the ovary as they relate to previously described impacts on serum estradiol concentrations and altered follicular development in zebrafish. In silico computational approaches were used to correlate candidate regulatory motifs with observed changes in gene expression. Our data suggest that TCDD inhibits follicle maturation via attenuated gonadotropin responsiveness and/or depressed estradiol biosynthesis, and that interference of estrogen-regulated signal transduction may also contribute to TCDD's impacts on follicular development. TCDD may also alter ovarian function by disrupting various signaling pathways such as glucose and lipid metabolism, and regulation of transcription. Furthermore, events downstream from initial TCDD molecular-targets likely contribute to ovarian toxicity following chronic exposure to TCDD. Data presented here provide further insight into the mechanisms by which TCDD disrupts follicular development and reproduction in fish, and can be used to formulate new hypotheses regarding previously documented ovarian toxicity.

Effects of Vertically Transferred 3,3',4,4',5-Pentachlorobiphenyl on Gene Expression in the Ovaries of Immature Sprague-Dawley Rats

We have previously shown that 3,3',4,4',5-pentachlorobiphenyl (PCB-126) vertically transferred from dams potentially exerts a direct effect on the ovaries of offspring and adversely affects female puberty. To investigate its toxicological targets in ovarian tissues, mRNAs encoding representative peptides that regulate follicular development in granulosa cells, theca cells, and oocytes were quantified using ovaries collected on postnatal days (PND) 5, 15, and 24 from the offspring of dams administered oral doses of 0, 1 or 3 microg/kg PCB-126 starting 2 weeks prior to mating and continuing until 20 days after delivery. Quantification using the real-time RT-PCR method revealed that PCB-126 lowered the amounts of mRNAs that encoded the inhibin alpha- and inhibin/activin beta A-subunits from PND 15 onwards; the amounts of mRNAs for inhibin/activin beta B-subunit, follicle-stimulating hormone (FSH) receptor, and aromatase on PND 15; and the amounts of luteinizing hormone receptor mRNA on PND 24 compared with those of the age-matched controls. In contrast, no differences were noted for mRNAs encoding c-kit, growth differentiation factor-9, bone morphogenetic protein-15, or kit ligand for any of the age groups examined. The serum FSH level on PND 24 was higher than that in the control. Since the earliest effects on the mRNAs in the rat ovaries were observed in those expressed in the granulosa cells of the growing follicles after the antral follicles had developed, molecules in granulosa cells but not in oocytes during the early stages of the antral follicles might be the primary targets of vertically transferred PCB-126.

Internal dose-effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in gonadotropin-primed weanling rat model

Single sc injection of 5 IU equine chorionic gonadotropin (eCG) induces ovulation in weanling female rats 3 days later. It has been shown that treatment with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) 24 h before eCG injection reduces eCG-stimulated ovarian hypertrophy and inhibits ovulation. The present study intended to compare internal dose-effects of TCDD between these endpoints and representative endpoints for TCDD toxicity, such as weights of the liver and thymus, in weanling female rats given orally 0, 1, 4 or 16 microg/kg TCDD 24 h before eCG injection on postnatal day 25. Measurement of plasma TCDD concentrations by ELISA at 6, 72 and 96 h after TCDD revealed that significant levels of TCDD were maintained in systemic circulation until 96 h (on the day of induced ovulation) with the highest level at 6 h after TCDD treatment. Ovarian TCDD concentrations varied similarly and tended to be higher than those in the thymus at all time points, whereas hepatic concentrations of TCDD were the highest among the tissues. Although > or = 4 microg/kg TCDD affected the weights of the thymus and liver, no differences were observed in ovarian weights at any time point or in ovulation between corn oil-treated and TCDD-treated groups. Furthermore, ovarian levels of representative mRNAs in follicles were not affected by TCDD treatment. Since TCDD increased the amount of cytochrome P450 1A1 mRNA in the ovary, the administered TCDD stimulated the aryl hydrocarbon receptor-signaling pathway. From these results, we concluded that thymus weights of weanling female rats responded to TCDD at a lower internal dose as compared with that ovarian hypertrophy and follicular growth from early antral stage to ovulation would respond to.

H. TCDD increases inhibin A production by human luteinized granulosa cells in vitro

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is the most toxic of the halogenated dioxins and one of the most poisonous substances known to man. The major toxic effects of TCDD on reproduction are decreased fertility and diminished ability to maintain a pregnancy. Granulosa cells obtained from hormonally stimulated women participating in an in-vitro fertilization program were cultured with 3.1 femtomolar, 3.1 picomolar and 3.1 nanomolar TCDD. While inhibin B production was not altered, inhibin A production increased significantly after 4 hours of exposure to both nanomolar and micromolar TCDD concentrations. By 8 hours of exposure to these concentrations of dioxin, human luteinizing granulosa cells exhibited a pronounced increase in inhibin A, nearly quadrupling secretion from unexposed control cells. TCDD continued to increase inhibin A secretion at the picomolar concentration at 24 and 36 hours. It is conceivable that TCDD may act at the ovary to augment inhibin A secretion, thereby reducing FSH-stimulable estrogen secretion by granulosa cells.

Effects of Acute and Chronic Exposure to the Aryl Hydrocarbon Receptor Agonist 2,3,7,8-Tetrachlorodibenzo-p-Dioxin on the Transition to Reproductive Senescence in Female Sprague-Dawley Rats1

Activation of the aryl hydrocarbon receptor (AHR) can occur in polluted environments, either from smoking-related toxicants or from endogenous ligands. We tested whether acute or chronic exposure to the AHR agonist 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) alters the transition to reproductive senescence in female Sprague-Dawley rats. In experiment 1, rats (n = 6 per experimental group) received a single dose of 0 or 10 mug/kg of TCDD orally (p.o.) on Postnatal Day 29. Vaginal cytology was monitored for 1 wk each month until rats were killed at 1 yr of age. The single prepubertal exposure to TCDD hastened the transition to reproductive senescence in female rats and was associated with delayed puberty, abnormal cyclicity, and premature reproductive senescence. In a second experiment, rats were exposed to TCDD chronically through weekly dosing (0, 50, or 200 ng kg(-1) wk(-1) p.o., n = 7 each dose) beginning in utero. Lifelong exposure to these lower doses of TCDD induced a dose- and time-dependent loss of normal cyclicity and significantly hastened the onset of the transition to reproductive senescence (P < 0.05). This premature transition to reproductive senescence was associated with prolonged estrous cycles and, at the highest dose of TCDD, persistent estrus or diestrus. The number and size of ovarian follicles were not altered by TCDD. Diestrous concentrations of LH in rats exposed chronically to TCDD were similar to those in controls, whereas progesterone tended to be elevated at both doses of the dioxin (P < 0.08). Serum FSH was elevated in the group exposed to 50 ng/kg of TCDD (P < 0.02), whereas estradiol was decreased at both doses of dioxin (P < 0.01). Data thus far support endocrine disruption rather than depletion of follicular reserves as a primary mechanism of the premature transition to reproductive senescence following activation of the AHR pathway by TCDD in female rats.

Effects of Vertically Transferred 3,3',4,4',5-Pentachlorobiphenyl (PCB-126) on the Reproductive Development of Female Rats

In order to study the effects of vertically transferred coplanar polychlorinated biphenyls on female reproductive development, female rat offspring from dams of Sprague-Dawley strain, which received daily oral administration of vehicle (corn oil) or 1 or 3 microg/kg of 3,3',4,4',5-pentachlorobiphenyl (PCB-126) from 2 weeks prior to mating with intact males until 20 days after delivery were examined from birth until puberty. Hepatic expression of the aryl hydrocarbon receptor (AhR)-inducible enzyme cytochrome P450 1A1 (CYP1A1) was detected in all offspring from PCB-126-exposed dams, indicating vertical transfer of PCB-126. Furthermore, quantification of ovarian mRNAs encoding CYP1A1, AhR and ARNT demonstrated that the ovary equipped the AhR-signaling system through which transcription of the CYP1A1 gene was enhanced in a dose-dependent manner. Exposure to PCB-126 retarded the growth of offspring in both exposed groups, while the viability of the neonates of the exposed groups was comparable to that of the oil-exposed controls. The exposure to 3 mug/kg/day reduced the ovarian weight on postnatal day (PND) 24, with atresia of most of the antral follicles and delayed vaginal opening. Exposure to 1 microg/kg/day did not produce such effects; however, both doses of PCB-126 induced external urogenital anomalies, such as vaginal thread and hypospadias, in all of the PCB-126-exposed female offspring. These results indicate that vertically transferred PCB-126 is potent enough to exert a direct effect on the ovary and adversely affect female puberty by altering the morphological and functional development of the female reproductive system.

Inhibition of follicular development, vitellogenesis, and serum 17beta-estradiol concentrations in zebrafish following chronic, sublethal dietary exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin

The environmental toxicant 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) is a potent endocrine disruptor with the ability to affect several biologic processes, including reproduction. In fish, sublethal exposure to TCDD is known to modulate overall reproductive capacity, but impacts on follicular development and vitellogenesis are unknown. Here we show that chronic, dietary exposure to 0.08, 0.32, or 0.80 ng TCDD female(-1) day(-1) decreased egg production by more than 50% and that spawning success was reduced by as much as 96%. Serum estradiol concentrations were decreased more than twofold, accounting, in part, for observed decreases in serum vitellogenin concentrations by as much as 29%. Our data suggest that decreased egg production is likely the result of TCDD-mediated inhibition of the transition from pre-vitellogenic stage follicles to vitellogenic stage follicles, as well as the induction of follicular atresia. The majority of reproductive toxicity of TCDD is likely due to direct impacts on the ovary, yet histopathologic observations suggest liver toxicity could also contribute to observed impacts on vitellogenesis. Importantly, even when overall egg production is not significantly affected, our data show that subtle physiologic changes induced by TCDD can lead to altered gonadogenesis. This suggests that long-term exposure to very low concentrations of TCDD could greatly affect fecundity and reproductive success in fishes.

Effects of zearalenone on mRNA expression and activity of cytochrome P450 1A1 and 1B1 in MCF-7 cells

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is a ubiquitous pollutant and promoter of carcinogenesis with both estrogenic and antiestrogenic effects in mammal epithelium. Zearalenone (ZEA) is a naturally occurring estrogenic contaminant of moldy feeds and is present in high concentrations in dairy products and cereals. Numerous studies describe a possible correlation between xenoestrogens and breast cancer risk. A potential mechanism for the etiology of breast cancer involves altered cytochrome P450 (CYP) enzymes. Since cocontamination of multiple compounds in our environmental and occupational circumstances likely happens and since few studies have addressed the molecular consequences of combinations of contaminants, we decided to investigate the effects of ZEA on basal and TCDD-induced mRNA expression and enzymic activity of CYP1A1 and CYP1B1 in human breast cancer MCF-7 cells. CYP1A1 enzyme activity was measured by the CYP1A1-referential activity assay, ethoxyresorufin O-deethylase (EROD), in MCF-7 cells. To investigate CYP1B1 activity, we employed the microsomal EROD assay prepared from baculovirus-infected insect cells expressing human cDNA CYP1B1. Reverse transcription-polymerase chain reaction was used to detect mRNA expression of CYP1A1 and CYP1B1 in MCF-7 cells. The results demonstrated that 10nM TCDD could readily induce a significant increase in the enzyme activity and mRNA expression of CYP1A1 in MCF-7 cells and 5 nM estradiol (E2) significantly reduced both basal and TCDD-induced activity and mRNA expression in MCF-7 cells. The same pattern was observed with 50nM ZEA. The estrogen receptor antagonist 4-hydroxytamoxifen could attenuate these inhibitive effects of both E2 and ZEA. Interestingly, Both E2 and ZEA could promote basal and TCDD-induced CYP1B1 activity but with no effect on CYP1B1 mRNA expression. These results suggest that the effect of ZEA on the TCDD-induced CYP1A1 activity and gene expression involved the estrogen receptor pathway and that the increase in the CYP1B1/CYP1A1 ratio underlying the basal or TCDD-treated condition might constitute one of the mechanisms underlying the synergic carcinogenic action of these compounds.

Alteration of pregnancy related hormones and fetal survival in F-344 rats exposed by inhalation to benzo(a)pyrene

The objective of this study was to evaluate the effect of subacute exposure to inhaled benzo(a)pyrene (BaP) on fetal survival and luteal maintenance using timed-pregnant Fisher 344 rats. Prior to assignment of pregnant rats to treatment and control groups, numbers of implantation sites were determined on gestation day (GD) 8 via midventral laparotomy. Subsequently, animals were assigned randomly to three treatment groups and two control groups. Treatment consisted of subacute exposure of rats via inhalation to BaP 25, 75, and 100 micro g/m(3), 4h daily for 10 days (GD-11-20). Control animals were either sham exposed to carbon black (CB) to control for inert BaP carrier or remained unexposed (UNC). Blood samples were collected on days 15 and 17 of gestation via sinus orbital veini-puncture for plasma. Number of pups per litter was determined postpartum and fetal survival rate was expressed as a percentage of the corresponding implantation sites. Radioimmunoassays were used to determine plasma progesterone, estrogen, and prolactin (indirect measurement of decidual luteotropin) concentrations. Fetal survival among BaP-treated rats declined in a dose-dependent manner (25 micro g/m(3), 78.3% per litter; 75 micro g/m(3), 38.0% per litter; 100 micro g/m(3), 33.8% per litter; P<0.05) compared with CB (96.7% per litter) and UNC (98.9% per litter). Plasma progesterone, estrogen, and prolactin concentrations also declined as a result of subacute exposure of rats to BaP compared to controls. These data suggest that inhaled BaP compromised fetal survival and consequently luteotropic activity in the exposed animals.

Estrous cycle-regulated expression of CYP1B1 mRNA in the rat ovary

CYP1B1, a member of the cytochrome p450 superfamily, is expressed constitutively in the steroidogenic tissues of mammals and is inducible by peptide hormones, cAMP and aromatic hydrocarbon receptor (AHR) ligands. The mechanism of induction of this cytochrome p450 is similar to that for CYP1A1, i.e. through the aromatic hydrocarbon receptor (AHR) signaling pathway. We have recently reported that CYP1B1, but not CYP1A1, is expressed in rat granulosa cells (GC) in the absence of any external stimulus. The induction of CYP1B1 mRNA in rat GC by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in vitro was followed by an increase in AHR and estrogen receptor (ER-beta) RNA levels. Estrous cycle-dependent expression of AHR, AHR-nuclear translocator (ARNT) and ER-mRNAs in the rat ovary was reported. We suggest that CYP1B1 may play a major role in the regulation of rat ovarian function/cycle but until now this has been unexplored experimentally. The present study was therefore aimed at examining the expression of CYP1A1, CYP1B1 and ER-mRNA in rat ovarian tissues throughout the estrous cycle to establish any correlation in the expressions of these mRNAs in rat ovary. Total RNA was extracted from the ovary and liver of cycling adult rats and the mRNAs were analyzed using relative RT-PCR with gene-specific primers for the target mRNA and for RPL 19 or S16 primers as an internal control. The results indicated that in the ovary, CYP1B1 mRNA increased significantly on the evening of proestrus and dramatically decreased on the morning of estrus, while ER-mRNA remained unaltered throughout the estrous cycle. CYP1A1 mRNA in the ovary and both CYP1A1 and CYP1B1 mRNAs in the liver were undetectable. That the sudden decrease of ovarian CYP1B1 mRNA on the morning of estrus was not an effect of the LH surge was verified in vitro using our short-term GC culture model. GC prepared from rats super-stimulated with equine chorionic gonadotropin (eCG) were cultured for 6 h with or without LH and TCDD. It was observed that both CYP1A1 and CYP1B1 mRNAs were induced by TCDD with no apparent effect of LH. It is suggested that the high level of CYP1B1 mRNA expression on the evening of proestrus in rat ovary might be involved in metabolism of estrogens to catecholestrogen (a known effect of CYP1B1), and that expression is unaffected in GC by LH.

Incorporation of endocrine disruption into chemical hazard scoring for pollution prevention and current list of endocrine disrupting chemicals

Research continues to support the theory of endocrine disruption. Endocrine disruption is defined as the ability of a chemical contaminating the workplace or the environment to interfere with homeostasis, development, reproduction, and/or behavior in a living organism or it's offspring. Certain classes of environmentally persistent chemicals such as polychlorinated biphenyls (PCBs), dioxins, furans, and some pesticides can adversely effect the endocrine systems of aquatic life and terrestrial wildlife. The University of Tennessee, Knoxville (UTN), developed a method for hazard scoring chemicals for the aquatic ecosystem. The Indiana Clean Manufacturing Technology and Safe Materials Institute at Purdue University (CMTI) later expanded the scoring system to include terms for worker hazard as well as terms for contamination of soil and air quality, and for stratospheric ozone depletion. We call the CMTI chemical hazard score the Purdue score. At West Virginia University, two improvements of the Purdue chemical hazard score are developed, a normalizing of the term for soil contamination, and addition of hazard score terms for ecosystem endocrine disruption. The results of incorporating endocrine disruption terms into the hazard scoring equations resulted in increased hazard rankings, often substantially increased, for 26 endocrine disrupting chemicals (EDCs) among 200 Superfund chemicals. Because data suggesting human endocrine disruption from such chemicals is still controversial, no endocrine disruptor term has been added to the human toxicity portions of the chemical hazard scoring system at this time. The third product of this work is assembly of a current consolidated list of (1) established or probable, mostly synthetic, industrial chemical and medication EDCs and (2) suspect (less certain) synthetic and natural (phytoestrogen) possible endocrine disrupting chemicals, with the goal of contributing to future development of quantitative structure activity relationship software for predicting whether an untested chemical is likely to be an endocrine disruptor. We conclude that enough endocrine disrupting chemicals are now identified to make an attempt at developing structure activity estimates of disrupting potential worthwhile. Further, we conclude that within a group of 200 chemicals of concern to the US EPA, the addition of endocrine disrupting terms to the Purdue score substantially increases its representativeness in reflecting ecological exposure hazard. We have developed this enhanced Purdue score risk management tool to be of assistance to industry.

2,3,7,8-Tetrachlorodibenzo-p-dioxin increases steady-state estrogen receptor-beta mRNA levels after CYP1A1 and CYP1B1 induction in rat granulosa cells in vitro

Previous in-vitro investigations of rat granulosa cells (GC) have shown that 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) inhibits estrogen secretion and FSH-induced aromatase activity. Although TCDD exerted no effect on basal aromatase enzyme activity, TCDD did reduce steady-state aromatase mRNA levels in GC using competitive RT-PCR. TCDD is hypothesized to induce these changes through aromatic hydrocarbon receptor(AHR)-mediated gene transcription and the modulation of the estrogen receptor (ER)-signaling pathway. In this study we show that rat GC express mRNA for AHR and the AHR nuclear translocator (ARNT) as well as biomarkers of TCDD action, CYP1A1 and CYP1B1 mRNA. Basal CYP1A1 and ER-alpha mRNAs were present only in trace amounts. By relative RT-PCR analysis we showed that CYP1A1 and CYP1B1 mRNA were induced significantly by TCDD at 6 h and that induction of CYP1A1 was maintained throughout the experiment. Using competitive RT-PCR, we observed no significant change in the mRNA levels of ARNT between control and TCDD-treated GC. Both AHR and ER-beta mRNA levels increased significantly at 48 h with TCDD compared with controls. Since ER-beta mRNA was not increased significantly until 48 h in culture, we suggest that in rat GC, the observed ER-beta mRNA increase by TCDD might be a result of CYP1A1/CYP1B1 catalyzed estrogen metabolism and aromatase mRNA inhibition via AHR.

Disruption of pituitary-ovarian axis by carbofuran in catfish, Heteropneustes fossilis (Bloch)

We investigated whether carbofuran (CF), a carbamate pesticide, at sub-lethal concentration had any adverse effects on reproductive function of the Indian catfish, Heteropneustes fossilis. 17beta-Estradiol content of serum and ovary of pre-spawning (P) and spawning (S) fish was reduced after sub-lethal concentration of carbofuran treatment (0.5-2 mg/ml, 30 days). After 30 days of CF treatment, the serum and ovarian vitellogenin levels of fish at the P stage were also reduced but remained unaltered in the S stage. The staining intensity of the pituitary gonadotrophs of the pre-spawning fish was significantly higher in CF-treated fish compared to controls suggesting the inability of the pituitary gonadotrophs to release gonadotropin following CF treatment. CF thus acts as an antiestrogenic, endocrine-disrupting agent in fish, possibly targeting the pituitary-gonad axis.

The effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on weight gain and hepatic ethoxyresorufin-o-deethylase (EROD) induction vary with ovarian hormonal status in the immature gonadotropin-primed rat model

Immature female rats received 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) during an induced proestrus or diestrus. The inhibitory effect of TCDD on acute weight gain and the induction of hepatic ethoxyresorufin-o-deethylase (EROD) activity by TCDD were greatest during proestrus. In a second experiment, ovariectomized rats received estradiol cypionate (ECP) or progesterone followed by TCDD. TCDD and estradiol each alone significantly inhibited weight gain. Progesterone potentiated the effects of TCDD on weight gain. The highest dose of ECP was associated with greater induction of hepatic EROD activity by TCDD than seen with TCDD alone. Estradiol modulates the induction of hepatic EROD activity by TCDD. Differential effects of TCDD on acute weight gain during proestrus vs. diestrus in this model do not mimic changes induced by estrogen alone. Hepatic responses to TCDD may vary according to phase of the female reproductive cycle.

Demonstration of 2,3,7,8-tetrachlorodibenzo-p-dioxin attenuation of P450 steroidogenic enzyme mRNAs in rat granulosa cell in vitro by competitive reverse transcriptase-polymerase chain reaction assay

We investigated the effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), in prepubertal (PP) and adult (A) rat granulosa cells (GC) in vitro by examining the changes in estrogen secretion, aromatase enzyme activity and mRNAs for steroidogenic enzymes P450scc, 3beta-HSDI, P450arom; and for components of the AHR signaling pathway-CYP1A1, aromatic hydrocarbon receptor (AHR), and the AHR nuclear translocator protein (ARNT). In PP and A rat GC, TCDD (3.1 nM) reduced estrogen secretion at 48 h without altering aromatase enzyme activity. Addition of FSH (50 ng/ml) increased aromatase activity in GC with or without TCDD. FSH-induced aromatase activity was significantly reduced by TCDD (3.1 nM) at 48 h. Semi-quantitative RT-PCR showed a significant increase in CYP1A1 mRNA both at 24 and 48 h with TCAP, while a significant reduction in P450scc and P450arom mRNA was observed with competitive RT-PCR. All steroidogenic enzyme mRNAs were significantly lower in adults than in PP GC. We conclude that in rat GC, TCDD modulates the level of cytochrome P450 enzymes involved in the steroid biosynthetic cascade. This effect may be attributable to AHR interaction with dioxin-responsive elements present in the genes encoding these enzymes.

Estrous cycle-dependent changes in the expression of aromatic hydrocarbon receptor (AHR) and AHR-nuclear translocator (ARNT) mRNAs in the rat ovary and liver

The aromatic hydrocarbon receptor (AHR) and AHR nuclear translocator protein (ARNT) mediate the toxic effects of a wide variety of halogenated and polycyclic aromatic hydrocarbons. While it can be assumed that AHR has an endogenous function, its role in reproduction is currently undefined. The present study seeks to examine the regulation of AHR and ARNT mRNAs in liver and ovarian tissues across the rat estrous cycle. Message for hepatic AHR was increased significantly on the morning of proestrus, and decreased dramatically by the evening of proestrus; while hepatic ARNT mRNA was significantly decreased between diestrus and the morning of proestrus, and between the evening of proestrus and the morning of estrus. Ovarian AHR mRNA was unchanged from diestrus to proestrus, and was decreased on the evening of proestrus. Changes in the expression of ARNT mRNA mirrored changes in the liver. To assess interaction between the AHR- and estrogen-receptor (ER)-signaling pathways and to test the hypothesis that estrogen regulates AHR mRNA, 25-day-old female rats were injected with either 17beta-estradiol, the ER antagonist ICI 182 780, or with vehicle, and hepatic AHR mRNA was measured. Treatment with estrogen or the estrogen antagonist did not alter the abundance of AHR mRNA in the liver. These data suggest that while estrogen may not be the key regulator of AHR mRNA expression, a factor associated with the rat reproductive cycle may be important in regulating the expression of both the AHR and ARNT genes in the ovary and liver.