Triclocarban Disrupts the Epigenetic Status of Neuronal Cells and Induces AHR/CAR-Mediated Apoptosis.

Triclocarban is a phenyl ether that has recently been classified as a contaminant of emerging concern. Evidence shows that triclocarban is present in human tissues, but little is known about the impact of triclocarban on the nervous system, particularly at early developmental stages. This study demonstrated that triclocarban that was used at environmentally relevant concentrations induced apoptosis in mouse embryonic neurons, inhibited sumoylation, and changed the epigenetic status, as evidenced by impaired activities of HDAC, sirtuins, and DNMT, global DNA hypomethylation, and alterations of methylation levels of bax, bcl2, Ahr, and Car genes. The use of selective antagonists and specific siRNAs, which was followed by the co-localization of aryl hydrocarbon receptor (AHR) and constitutive androstane receptor (CAR) in mouse neurons, points to the involvement of AHR and CAR in triclocarban-induced neurotoxicity. A 24-h treatment with triclocarban enhanced protein levels of the receptors which was paralleled by Car hypomethylation and Ahr hypermethylation. Car hypomethylation is in line with global DNA hypomethylation and explains the increased mRNA and protein levels of CAR in response to triclocarban. Ahr hypermethylation could reflect reduced Ahr mRNA expression and corresponds to lowered protein levels after 3- and 6-h exposures to triclocarban that is likely related to proteasomal degradation of activated AHR. We hypothesize that the triclocarban-induced apoptosis in mouse neurons and the disruption of epigenetic status involve both AHR- and CAR-mediated effects, which may substantiate a fetal basis of the adult onset of neurological diseases; however, the expression of the receptors is regulated in different ways.

The Crucial Involvement of Retinoid X Receptors in DDE Neurotoxicity.

Dichlorodiphenyldichloroethylene (DDE) is a primary environmental and metabolic degradation product of the pesticide dichlorodiphenyltrichloroethane (DDT). It is one of the most toxic compounds belonging to organochlorines. DDE has never been commercially produced; however, the parent pesticide DDT is still used in some developing countries for disease-vector control of malaria. DDT and DDE remain in the environment because these chemicals are resistant to degradation and bioaccumulate in the food chain. Little is known, however, about DDE toxicity during the early stages of neural development. The results of the present study demonstrate that DDE induced a caspase-3-dependent apoptosis and caused the global DNA hypomethylation in mouse embryonic neuronal cells. This study also provided evidence for DDE-isomer-non-specific alterations of retinoid X receptor α (RXRα)- and retinoid X receptor ß (RXRß)-mediated intracellular signaling, including changes in the levels of the receptor mRNAs and changes in the protein levels of the receptors. DDE-induced stimulation of RXRα and RXRß was verified using selective antagonist and specific siRNAs. Co-localization of RXRα and RXRß was demonstrated using confocal microscopy. The apoptotic action of DDE was supported at the cellular level through Hoechst 33342 and calcein AM staining experiments. In conclusion, the results of the present study demonstrated that the stimulation of RXRα- and RXRß-mediated intracellular signaling plays an important role in the propagation of DDE-induced apoptosis during early stages of neural development.

Triclosan induces Fas receptor-dependent apoptosis in mouse neocortical neurons in vitro.

Triclosan (TCS) is a commonly used antimicrobial agent in personal care and sanitizing products, as well as in household items. Numerous studies have demonstrated the presence of TCS in various human tissues. Several studies have reported the accumulation of TCS in fish and human brain tissue. The aim of the present study was to investigate the effect of TCS on apoptosis in mouse neocortical neurons after 7 days of culture in vitro following 3, 6 and 24 h of exposure. To explore the mechanism underlying the effects of TCS in neurons, we studied the activation and protein expression of the Fas receptor (FasR) and caspase-8, caspase-9 and caspase-3, as well as DNA fragmentation in TCS-treated cells. Cultures of neocortical neurons were prepared from Swiss mouse embryos on day 15/16 of gestation. The cells were cultured in phenol red-free Neurobasal medium with B27 and glutamine. The cultures were treated with concentrations of TCS ranging from 1 nM to 100 µM for 3, 6 and 24 h. The level of lactate dehydrogenase (LDH) was measured in the culture medium to exclude the cytotoxic concentrations. The cytotoxic effects were only observed when the highest concentrations of TCS were used (50 and 100 µM). To study apoptosis, the activities of caspase-8, caspase-9 and caspase-3 were measured, and DNA fragmentation was evaluated. Our results are the first time to demonstrate that TCS can induce an apoptotic process in neocortical neurons in vitro. The data demonstrated that TCS caused caspase-3 activation, DNA fragmentation and apoptotic body formation. Non-cytotoxic concentrations of TCS activated the extrinsic apoptotic signaling pathway, which is dependent on FasR and caspase-8 activation. However, it is also possible that TCS may activate the intrinsic apoptotic pathway after long-term exposure. Therefore, further studies on the mechanism underlying the effects of TCS on the nervous system are needed.

Isomer-nonspecific action of dichlorodiphenyltrichloroethane on aryl hydrocarbon receptor and G-protein-coupled receptor 30 intracellular signaling in apoptotic neuronal cells.

Extended residual persistence of the pesticide dichlorodiphenyltrichloroethane (DDT) raises concerns about its long-term neurotoxic effects. Little is known, however, about DDT toxicity during the early stages of neural development. This study demonstrated that DDT-induced apoptosis of mouse embryonic neuronal cells is a caspase-9-, caspase-3-, and GSK-3ß-dependent process, which involves p,p'-DDT-specific impairment of classical ERs. It also provided evidence for DDT-isomer-nonspecific alterations of AhR- and GPR30-mediated intracellular signaling, including changes in the levels of the receptor and receptor-regulated mRNAs, and also changes in the protein levels of the receptors. DDT-induced stimulation of AhR-signaling and reduction of GPR30-signaling were verified using selective ligands and specific siRNAs. Co-localization of the receptors was demonstrated with confocal microscopy, and the presence of functional GPR30 was detected by electrophysiology. This study demonstrates that stimulation of AhR-signaling and impairment of GPR30-signaling play important roles in the propagation of DDT-induced apoptosis during the early stages of neural development.

The key involvement of estrogen receptor ß and G-protein-coupled receptor 30 in the neuroprotective action of daidzein.

Phytoestrogens have received considerable attention because they provide an array of beneficial effects, such as neuroprotection. To better understand the molecular and functional link between phytoestrogens and classical as well as membrane estrogen receptors (ERs), we investigated the effect of daidzein on the glutamate-mediated apoptotic pathway. Our study demonstrated that daidzein (0.1-10µM) inhibited the pro-apoptotic and neurotoxic effects caused by glutamate treatment. Hippocampal, neocortical and cerebellar tissues responded to the inhibitory action of daidzein on glutamate-activated caspase-3 and lactate dehydrogenase (LDH) release in a similar manner. Biochemical data were supported at the cellular level by Hoechst 33342 and calcein AM staining. The sensitivity of neuronal cells to daidzein-mediated protection was most prominent in hippocampal cultures at an early stage of development 7th day in vitro. A selective estrogen receptor ß (ERß) antagonist, 4-[2-phenyl-5,7-bis(trifluoromethyl)pyrazolo[1,5,-a]pyrimidin-3-yl]phenol (PHTPP), and a selective G-protein-coupled receptor 30 (GPR30) antagonist, 3aS(∗),4R(∗),9bR(∗))-4-(6-Bromo-1,3-benzodioxol-5-yl)-3a,4,5,9b-3H-cyclopenta[c]quinoline (G15), reversed the daidzein-mediated inhibition of glutamate-induced loss of membrane mitochondrial potential, caspase-3 activity, and LDH release. A selective ERα antagonist, methyl-piperidino-pyrazole (MPP), did not influence any anti-apoptotic effect of daidzein. However, a high-affinity estrogen receptor antagonist, 7α,17ß-[9-[(4,4,5,5,5-pentafluoropentyl)sulfinyl]nonyl]estra-1,3,5(10)-triene-3,17-diol (ICI) 182,780, and a selective GPR30 agonist, (±)-1-[(3aR(∗),4S(∗),9bS(∗))-4-(6-bromo-1,3-benzodioxol-5-yl)-3a,4,5,9b-tetrahydro-3H-cyclopenta[c]quinolin-8-yl]-ethanone (G1), intensified the protective action of daidzein against glutamate-induced loss of membrane mitochondrial potential and LDH release. In siRNA ERß- and siRNA GPR30-transfected cells, daidzein did not inhibit the glutamate-induced effects. Twenty-four hour exposure to glutamate did not affect the cellular distribution of ERß and GPR30, but caused greater than 100% increase in the levels of the receptors. Co-treatment with daidzein decreased the level of ERß without significant changing of the GPR30 protein level. Here, we elucidated neuroprotective effects of daidzein at low micromolar concentrations and demonstrated that the phytoestrogens may exert their effects through novel extranuclear GPR30 and the classical transcriptionally acting ERß. These studies uncover key roles of the ERß and GPR30 intracellular signaling pathways in mediating the anti-apoptotic action of daidzein and may provide insight into new strategies to treat or prevent neural degeneration.

Seasonal changes in the interactions among leptin, ghrelin, and orexin in sheep.

The adaptation of the physiology of an animal to changing conditions of light and food availability is evident at the behavioral and hormonal levels. Melatonin, leptin, ghrelin, and orexin, which exhibit rhythmic secretion profiles under ad libitum feeding conditions, are sensitive to changes in daylength, forming a tight web of interrelationships in the regulation of energy balance. The aim of this study was to determine the effects of central injections of leptin, ghrelin, and orexin on the reciprocal interactions among these hormones and the influence of photoperiod on these responses. Twenty-four ovariectomized and estradiol-implanted ewes were used in a replicated switchback design. The ewes were assigned randomly to 1 of 6 treatment groups, and the treatments were infused into their third ventricles 3 times at 0, 1, and 2 h, with 0 h being at dusk. The treatments were as follows: 1) control, Ringer-Locke buffer; 2) leptin, 0.5 µg/kg BW; 3) ghrelin, 2.5 µg/kg BW; 4) orexin B, 0.3 µg/kg BW; 5) leptin antagonist, 50 µg/kg BW, then ghrelin, 2.5 µg/kg BW; and 6) leptin antagonist, 50 µg/kg BW, then orexin B, 0.3 µg/kg BW. Blood samples (5 mL) were collected at 15-min intervals for 6 h. The administration of leptin increased (P < 0.05) plasma concentrations of melatonin during short-day (ShD) photoperiods and decreased (P < 0.05) them during long-day (LD) photoperiods, whereas ghrelin decreased (P < 0.05) melatonin concentrations during ShD photoperiod, and orexin had no effect (P > 0.1). Leptin attenuated (P < 0.05) ghrelin concentrations relative to the concentration in controls during ShD. The plasma concentrations of orexin were reduced (P < 0.05) after leptin infusions during LD and ShD photoperiods; however, ghrelin had the opposite effect (P < 0.05) on orexin concentration. Orexin increased (P < 0.05) ghrelin concentrations during LD. Ghrelin and orexin concentrations were increased (P < 0.05) after leptin antagonist infusions. Our data provide evidence that the secretion of leptin, ghrelin, and orexin are seasonally dependent, with relationships that are subject to photoperiodic regulation, and that leptin is an important factor that regulates ghrelin and orexin releases in sheep.

Endocrine disrupters: a review of some sources, effects, and mechanisms of actions on behaviour and neuroendocrine systems.

Some environmental contaminants interact with hormones and may exert adverse consequences as a result of their actions as endocrine disrupting chemicals (EDCs). Exposure in people is typically a result of contamination of the food chain, inhalation of contaminated house dust or occupational exposure. EDCs include pesticides and herbicides (such as dichlorodiphenyl trichloroethane or its metabolites), methoxychlor, biocides, heat stabilisers and chemical catalysts (such as tributyltin), plastic contaminants (e.g. bisphenol A), pharmaceuticals (i.e. diethylstilbestrol; 17α-ethinylestradiol) or dietary components (such as phytoestrogens). The goal of this review is to address the sources, effects and actions of EDCs, with an emphasis on topics discussed at the International Congress on Steroids and the Nervous System. EDCs may alter reproductively-relevant or nonreproductive, sexually-dimorphic behaviours. In addition, EDCs may have significant effects on neurodevelopmental processes, influencing the morphology of sexually-dimorphic cerebral circuits. Exposure to EDCs is more dangerous if it occurs during specific 'critical periods' of life, such as intrauterine, perinatal, juvenile or puberty periods, when organisms are more sensitive to hormonal disruption, compared to other periods. However, exposure to EDCs in adulthood can also alter physiology. Several EDCs are xenoestrogens, which can alter serum lipid concentrations or metabolism enzymes that are necessary for converting cholesterol to steroid hormones. This can ultimately alter the production of oestradiol and/or other steroids. Finally, many EDCs may have actions via (or independent of) classic actions at cognate steroid receptors. EDCs may have effects through numerous other substrates, such as the aryl hydrocarbon receptor, the peroxisome proliferator-activated receptor and the retinoid X receptor, signal transduction pathways, calcium influx and/or neurotransmitter receptors. Thus, EDCs, from varied sources, may have organisational effects during development and/or activational effects in adulthood that influence sexually-dimorphic, reproductively-relevant processes or other functions, by mimicking, antagonising or altering steroidal actions.

Effects of orexigenic peptides and leptin on melatonin secretion during different photoperiods in seasonal breeding ewes: an in vitro study.

The pineal gland (PG) acts as a neuroendocrine transducer of daily and seasonal time through the nocturnal release of melatonin. Here, we examined the interaction of season, orexin, ghrelin, and leptin on melatonin secretion by pineal explants in short-term culture. Glands were collected after sunset from 12 ewes during long days (LD; April and May) and from an additional 12 ewes during short days (SD; October and November). Glands were transected sagittally into strips, with each equilibrated in 2.5 mL of Dulbecco's modified Eagle's medium for 60 min, followed by a 2-h incubation in control medium or medium containing orexin B (10 and 100 ng/mL), ghrelin (10 and 100 ng/mL), or 50 ng/mL of leptin. After a 3-h incubation, some PG explants treated previously with lower doses of orexin or ghrelin were challenged with 50 ng/mL of leptin and those treated with both doses of orexin were challenged with 300 nM of the ß-agonist isoproterenol. One milliliter of medium was harvested and replaced from each well every 30 min. Treatment with the low dose of orexin during LD increased melatonin secretion about 110% (P<0.01); treatment with a high dose increased melatonin secretion about 47% (P<0.001). During the SD period, leptin stimulated (P < 0.05) melatonin secretion slightly compared with mean melatonin concentration in controls. However, together, orexin and leptin depressed (P<0.01) melatonin secretion. Both doses of ghrelin reduced (P < 0.01) melatonin concentration during the SD season compared with control culture. Addition of ghrelin and leptin to culture medium increased (P<0.01) melatonin concentration compared with ghrelin-treated culture and decreased melatonin concentration (P<0.01) compared with leptin-treated culture during SD. Isoproterenol stimulated (P<0.01) melatonin secretion compared with values observed during the pretreatment period. We conclude that orexigenic peptides (orexin B and ghrelin) and an anorectic peptide (leptin) affect PG directly. The responses of PG to those hormones depend on day length. Moreover, secretion of melatonin from the ovine PG is under an adrenergic regulation.

Aryl hydrocarbon receptor-mediated apoptosis of neuronal cells: a possible interaction with estrogen receptor signaling.

Activation of aryl hydrocarbon receptors (AhRs) induces neuronal damage, but the mechanism by which this occurs is largely unknown. This study evaluated the effects of an AhR agonist, beta-naphthoflavone, on apoptotic pathways in mouse primary neuronal cell cultures. beta-Naphthoflavone (0.1-100 micronhanced caspase-3 activity and lactate dehydrogenase (LDH) release in neocortical and hippocampal cells. These data were supported at the cellular level with Hoechst 33342 and calcein AM staining. alpha-Naphthoflavone inhibited the action of beta-naphthoflavone, thus confirming specific activation of AhRs. A high-affinity estrogen receptor (ER) antagonist, ICI 182,780, and a selective estrogen receptor modulator (SERM), tamoxifen, enhanced beta-naphthoflavone-mediated apoptosis. Another SERM, raloxifene, and an ERalpha antagonist, methyl-piperidino-pyrazole, did not affect beta-naphthoflavone-induced caspase-3 activity. However, they inhibited beta-naphthoflavone-induced LDH release at a late hour of treatment, thus suggesting delayed control of AhR-mediated neuronal cell death. The apoptotic effects of beta-naphthoflavone were accompanied by increased levels of AhRs, and these receptors colocalized with ERbeta as demonstrated by confocal microscopy. These data strongly support apoptotic effects of AhR activation in neocortical and hippocampal tissues. Moreover, this study provides evidence for direct interaction of the AhR-mediated apoptotic pathway with estrogen receptor signaling, which provides insight into new strategies to treat or prevent AhR-mediated neurotoxicity.

DDT- and DDE-induced disruption of ovarian steroidogenesis in prepubertal porcine ovarian follicles: a possible interaction with the main steroidogenic enzymes and estrogen receptor beta.

We evaluated impact of DDT isomers, o, p'- DDT [1, 1-dichloro-2, 2-bis (p, p'-chlorophenyl) ethylene] and p, p'-DDT [1, 1, 1-trichloro-2, 2-bis (p-chlorophenyl) ethane], and their metabolites, o, p'-DDE and p, p'-DDE, on ovarian steroidogenesis. All these compounds, except for p, p'-DDT, demonstrated estrogenic effects on steroid secretion in co-cultures of porcine prepubertal granulosa and theca cells. p,p'-DDT decreased progesterone and estradiol release, which was reversed by the addition of testosterone. In contrast, o, p'-DDT inhibited progesterone secretion with parallel stimulation of basal and testosterone-stimulated estradiol release. DDEs stimulated progesterone and estradiol secretion. The fluorometric assay confirmed that p,p'-DDE, o,p'-DDT, and o,p'-DDE stimulated aromatase activity. Western blots indicated that o,p-DDT and o,p'-DDE diminished the expression of estrogen receptor beta (ERbeta). This study demonstrated the isomer-dependent action of DDT in pig ovarian cells. We propose that DDT could disrupt ovarian steroidogenesis either by interfering with main steroidogenic enzymes or affecting ERbeta.

Polychlorinated biphenyls (PCB 153 and PCB 126) action on conversion of 20-hydroxylated cholesterol to progesterone, androstenedione to testosterone, and testosterone to estradiol 17beta.

To look for one of the possible mechanisms of action we investigated the effect of two congeners of polychlorinated biphenyls (PCB153 as one of the most prominent environmental contaminants and PCB 126 as one of the most toxic contaminants similar to dioxin) on the cellular conversion of steroid precursors as an indicator for enzyme activity (20-hydroxylated cholesterol to progesterone for P450 (scc,) androstendione to testosterone for 17-beta-HSD, and testosterone to estradiol for P450 (arom)). The net synthesis and secretion of particular steroids was used as the indicator of enzyme activity. Co-culture of pig granulosa and theca cells isolated from small (SF) and large (LF) follicles, was carried out in medium M199 supplemented with 100 ng/ml of PCB 153 or 100 pg/ml of PCB 126. The inhibitory action of both PCB 126 and PCB 153 on progesterone secretion by cells isolated from SF and LF follicles was reversed in the presence of 20-hydroxylated cholesterol. The addition of PCB 126 into the culture medium caused a decrease in testosterone secretion by cells isolated from both SF and LF and this effect was reversed in the presence of androstendione. The inhibitory action of PCB 153 on testosterone secretion was reversed by the addition of androstendione to the culture medium in SF, while it caused even additional stimulatory action on cells collected from LF. No effect of PCB 126 and statistically significant decrease in estradiol secretion by cells collected from SF under the influence of PCB153 was observed. The inhibitory effect of PCB 153 was reversed when the culture was supplemented with testosterone. The opposite effect of both tested congeners on estradiol secretion in both basal and testosterone supplemented culture was seen in LF. PCB 126 increased it while PCB 153 decreased both, the basal and testosterone-stimulated estradiol secretion. In conclusion, the presented results suggest that the effect of both PCBs on steroid secretion observed in an early stage of the follicular phase of the estrus cycle is due to the inhibition of cholesterol mobilisation and thus insufficient substrate availability for hormone synthesis. On the contrary, in large preovulatory follicles inhibition of testosterone secretion is due to their action on 17-beta-HSD while stimulatory or inhibitory action on estradiol secretion is the result of their action on P450 aromatase activity.

Valproate-induced alterations in testosterone, estradiol and progesterone secretion from porcine follicular cells isolated from small- and medium-sized ovarian follicles.

The aim of the present study was to investigate whether long-term exposure to valproate (VPA) alters follicular steroidogenesis and whether or not this effect is dependent on the degree of follicular development. Small- and medium-sized follicles were obtained from pig ovaries collected, respectively, at days 8-10 and 14-16 of oestrus cycle. Theca interna and granulosa cells were isolated from follicles and placed in the same well in the ratio 1 : 3 with or without the VPA in doses of 100, 300 and 500 micro g ml(-1). The culture medium was changed after 2, 4, 6 and 8 days. In both types of follicles, VPA caused a significant and dose-dependent reduction in both testosterone and estradiol secretion from follicular cells. In small-sized follicles, the testosterone to oestrogen ratio increased at all doses used and after all lengths of time in culture. In medium-sized follicles, a significant increase in the testosterone to oestrogen ratio was only observed at the highest dose level. All doses of VPA caused a marked inhibition of progesterone secretion after 48 hours while during long-term VPA exposure progesterone gradually increased demonstrating luteinization of cells. In conclusion, the present study demonstrates a direct effect of VPA on steroidogenesis. The effect seems to differ to some extent depending on the follicular stage of development. The elevated ratio of testosterone to estradiol suggests that VPA inhibits the conversion of testosterone to estradiol.

Time dependent and cell-specific action of polychlorinated biphenyls (PCB 153 and PCB 126) on steroid secretion by porcine theca and granulosa cells in mono- and co-culture.

To characterize PCB action on follicular cell steroidogenesis two PCB congeners were selected as model substances. PCB 126 because of its dioxin-like configuration and high toxicity and PCB 153 because it is one of the most commonly detected PCB congeners in breast milk. The direct effect of PCBs was investigated using a culture system of porcine theca and granulosa cells collected from porcine preovulatory follicles. Granulosa and theca cells were cultured in M199 medium supplemented with 1, 10 or 100 pg/ml of PCB 126 or 1, 10 and 100 ng/ml of PCB 153. The media were changed after 48, 96 and 144 h and frozen until further estradiol (E2) analysis. Additionally, progesterone (P4) was measured in the granulosa cells culture medium and testosterone (T) in theca cells culture medium. Decrease of testosterone concentration in the theca cells culture medium was found after 96 and 144 hours in culture by both investigated PCB congeners. A decrease in E2 concentration was found after exposure to PCB 153. These findings suggest different actions of two congeners on the steroid synthesis in theca cells. The lack of an increase in E2 secretion after the exposure to PCB 126 could be due to depletion of androgen precursor. In granulosa cell culture PCB153 decreased E2 secretion and increased P4 secretion suggesting luteinization and disruption of aromatization process. PCB 126 in a doses from 1 to 10 pg had no effect on granulosa cells steroidogenesis. However, the highest dose (100 pg) increased concentration of both E2 and P4. This observation suggest that PCB 126 in a pharmacological doses may affect cell membrane permeability, thereby increasing steroid outflow into the medium. These results suggest time dependent and cell-specific differences in PCB 153 and 126 action on follicular cells steroidogenesis. Further studies are required to elucidate the mechanism of PCBs action on ovarian steroidogenesis.

Dose-and-time dependent effect of 2,3,7,8-tetrachlorodibenzo-P-dioxin (TCDD) on progesterone secretion by porcine luteal cells cultured in vitro.

In the current study, to characterize TCDD action during luteal phase of the ovarian cycle, the direct effect of TCDD was investigated in vitro using a system of monolayer cell culture. Luteal cells isolated from mid-developing corpora lutea were cultured with four different doses of TCDD (0.1, 1.0, 10.0 and 100 nM). The dose of 0.1nM TCDD had no effect on progesterone (P4) secretion by luteal cells while the doses of 10nM and 100nM in the same, statistically significant manner decreased P4 secretion (p <0.05). The inhibitory effect of TCDD was dependent not only on doses by also on experimental conditions. In cells treated every day for 72 hrs of culture with 0.1nM TCDD, P4 secretion was 71% of basal secretion. 100nM TCDD added only at the beginning of the culture and nor repeated when medium was changed every 24 hrs decreased P4 secretion to 81.8% of basal secretion. The most inhibitory effect was observed in experiments in which 100nM TCDD was added at the beginning of the culture and medium was not changed for 72 hrs. Secretion of P4 was only 33.9% of that by control cultures. In order to show the time-dependent response to TCDD in terms of P4 secretion, luteal cells were cultured for 24,48, 72 hrs with 0.1 and 100nM TCDD. 85%, 75% and 72% of basal progesterone secretion was noted after 24, 48 and 72h respectively in 0.1nM TCDD-treated cells. In 100nM TCDD treated cells the decrease of progesterone secretion was 57%, 67% and 82% of basal secretion after 24, 48 and 72 hrs of culture. These experiments suggest that TCDD by suppressing progesterone secretion by corpora lutea can cause adverse reproductive effects such as early pregnancy failure. Endocrine disrupters that interfere with progesterone production can act as abortifacients.