Methoxychlor Metabolite Research Articles

HPTE-Induced Embryonic Thymocyte Death and Alteration of Differentiation Is Not Rescued by ERα or GPER Inhibition but Is Exacerbated by Concurrent TCR Signaling.

Organochlorine pesticides, such as DDT, methoxychlor, and their metabolites, have been characterized as endocrine disrupting chemicals (EDCs); suggesting that their modes of action involve interaction with or abrogation of endogenous endocrine function. This study examined whether embryonic thymocyte death and alteration of differentiation induced by the primary metabolite of methoxychlor, HPTE, rely upon estrogen receptor binding and concurrent T cell receptor signaling. Estrogen receptor inhibition of ERα or GPER did not rescue embryonic thymocyte death induced by HPTE or the model estrogen diethylstilbestrol (DES). Moreover, adverse effects induced by HPTE or DES were worsened by concurrent TCR and CD2 differentiation signaling, compared with EDC exposure post-signaling. Together, these data suggest that HPTE- and DES-induced adverse effects on embryonic thymocytes do not rely solely on ER alpha or GPER but may require both. These results also provide evidence of a potential collaborative signaling mechanism between TCR and estrogen receptors to mediate adverse effects on embryonic thymocytes, as well as highlight a window of sensitivity that modulates EDC exposure severity.

Methoxychlor metabolite HPTE alters viability and differentiation of embryonic thymocytes from C57BL/6 mice

Endocrine-disrupting chemicals (EDC) are widespread in the built and natural environments. Heightened public awareness of their potential danger has led to concern about whether EDC and their metabolites have significant negative biological effects. Studies have shown that EDC like DDT and other organochlorine pesticides, such as methoxychlor (MXC), have adverse effects on immune cells, but no studies have addressed the impact of HPTE, the primary metabolite of MXC. To elucidate the presence and significance of HPTE adverse effects, this study explored the impact of HPTE on a critical window and component of immune system development, embryonic T-cell development. Lesions at this phase of development can lead to lifelong immune dysfunction and increased incidence of immune disease, such as autoimmunity. Embry-onic thymocytes (GD 16-18) from C57BL/6 mice were subjected to an in vitro differentiation culture that mimicked early steps in thymocyte development in the presence of 0.005, 0.05, 0.5, 5, or 50 μM HPTE, or a model endocrine disruptor, DES. The results indicated that compared to the vehicle control, HPTE- and DES-induced death of thymocytes. Annexin-V staining and Caspase 8, markers of programed cell death, revealed that the loss of cells was due at least in part to induction of apoptosis. Moreover, HPTE-induced cell death not only resulted in selective loss of double positive thymocytes, but also loss of developing CD4 intermediate cells (post-double positive partially differentiated thymocyte population). Phenotypic analysis of thymocyte maturation (T-cell receptor, TCR) and TCR ligation (CD5) surface markers revealed that surviving embryonic thymocytes expressed low levels of both. Taken together these data demonstrate that immature embryonic thymocytes are sensitive to HPTE exposure and that HPTE exposure targets thymocyte populations undergoing critical differentiation steps. These findings suggest HPTE may play a pivotal role in MXC exposure-induced immune dysfunction.

Hepatocytes as in vitro test system to investigate metabolite patterns of pesticides in farmed rainbow trout and common carp: Comparison between in vivo and in vitro and across species

In vitro tools using isolated primary fish hepatocytes have been proposed as a useful model to study the hepatic metabolism of xenobiotics in fish. In order to evaluate the potential of in vitro fish hepatocyte assays to provide information on in vivo metabolite patterns of pesticides in farmed fish, the present study addressed the following questions: Are in vitro and in vivo metabolite patterns comparable? Are species specific differences of metabolite patterns in vivo reflected in vitro? Are metabolite patterns obtained from cryopreserved hepatocytes comparable to those from freshly isolated cells? Rainbow trout and common carp were dosed orally with feed containing the pesticide methoxychlor (MXC) for 14days. In parallel, in vitro incubations using suspensions of freshly isolated or cryopreserved primary hepatocytes obtained from both species were performed. In vivo and in vitro samples were analyzed by thin-layer chromatography with authentic standards supported by HPLC-MS. Comparable metabolite patterns from a qualitative perspective were observed in liver in vivo and in hepatocyte suspensions in vitro. Species specific differences of MXC metabolite patterns observed between rainbow trout and common carp in vivo were well reflected by experiments with hepatocytes in vitro. Finally, cryopreserved hepatocytes produced comparable metabolite patterns to freshly isolated cells. The results of this study indicate that the in vitro hepatocyte assay could be used to identify metabolite patterns of pesticides in farmed fish and could thus serve as a valuable tool to support in vivo studies as required for pesticides approval according to the EU regulation 1107.

A computational model to predict rat ovarian steroid secretion from in vitro experiments with endocrine disruptors.

A finely tuned balance between estrogens and androgens controls reproductive functions, and the last step of steroidogenesis plays a key role in maintaining that balance. Environmental toxicants are a serious health concern, and numerous studies have been devoted to studying the effects of endocrine disrupting chemicals (EDCs). The effects of EDCs on steroidogenic enzymes may influence steroid secretion and thus lead to reproductive toxicity. To predict hormonal balance disruption on the basis of data on aromatase activity and mRNA level modulation obtained in vitro on granulosa cells, we developed a mathematical model for the last gonadal steps of the sex steroid synthesis pathway. The model can simulate the ovarian synthesis and secretion of estrone, estradiol, androstenedione, and testosterone, and their response to endocrine disruption. The model is able to predict ovarian sex steroid concentrations under normal estrous cycle in female rat, and ovarian estradiol concentrations in adult female rats exposed to atrazine, bisphenol A, metabolites of methoxychlor or vinclozolin, and letrozole.

Follicular Stage-Specific Gene Expression Analysis in Rat Ovary.

It is well established that endocrine-disrupting chemical (EDC) exposures during early development can cause ovarian dysfunction by adulthood. Studies with the organochlorine pesticide methoxychlor (MXC), a model EDC with estrogenic and anti-estrogenic activities, have demonstrated that neonatal and fetal exposure [embryonic day 18 to postnatal day (PND) 7] lead to accelerated puberty, irregular estrus cycles, reduced litter sizes, reduced superovulatory response to gonadotropins, and premature reproductive aging. In PND 50-60 ovaries, there was a disruption of follicular progression with a large number of follicles found in the early antral follicle stage with a concomitant reduction in corpora lutea. Furthermore, immunohistochemical studies showed that MXC-treated ovaries had decreased levels of CYP11A1 and LHR proteins in mid-late antral follicle stages and reduced ESR2 expression in the preantral and early antral follicles. Interestingly, there was no significant effect on ESR2 expression at earlier follicular stages such as primary and secondary follicles. Other studies with granulosa cell (GC) cultures demonstrated an enhanced effect of HPTE (a major metabolite of MXC) only in cells stimulated with FSH suggesting that gonadotropin responsive stages of follicles/GCs were more likely to exhibit the MXC mediated detrimental effects. Therefore, to identify the specific stages and the molecular/epigenetic mechanisms involved in EDC-associated effects, follicular isolations were performed. The objectives were (1) to establish a robust follicle separation method by enzymatic digestion and (2) to compare the gene expression patterns at the various follicular stages. Enzymatic digestions were performed with Collagenase Type I and various size beads (Polysciences, Inc.) were utilized to categorize the follicles into three groups: (1) “small” (50-180 μm, up to and including early pre-antral), (2) “medium” (180-300 μm, late pre-antral and early antral), and (3) “large” (300-700, mid- and late-antral follicles. Granulosa cells were collected from the large follicles by puncturing them prior to the enzymatic digestion. In this manner, approximately 25-30 small, 10-20 medium follicles and ~6 x 10-5 GCs from large follicles, per rat (n = 3), were obtained and RNA was isolated. Gene expression analyses were conducted after whole transcriptome amplification and QPCR with Taqman assays. Small follicles had a 100- to 200-fold enrichment ( p < 0.001) of Gdf9 and Bmp15 transcripts while GC from the large follicles had an enrichment of 100- to 500-fold ( p < 0.001) in steroidogenic enzyme transcripts such as Cyp11a1, Cyp19a1, and Hsd17b1 . These data validated our isolation techniques. Currently these data are being compared to those obtained from laser capture microdissection technique. Together they provide a useful tool for future studies of EDC exposed ovaries wherein gonadotropin responsive follicular stage-dependent gene expression and epigenetic analyses can be performed. Supported by R56 ES017059 from NIEHS (MU) and TUBITAK– BIDEB 2219 International Postdoctoral Fellowship Program (KA).

Quantification of steroids and endocrine disrupting chemicals in rat ovaries by LC-MS/MS for reproductive toxicology assessment

Reproductive function is controlled by a finely tuned balance of androgens and estrogens. Environmental toxicants, notably endocrine disrupting chemicals (EDCs), appear to be involved in the disruption of hormonal balance in several studies. To further describe the effects of selected EDCs on steroid secretion in female rats, we aim to simultaneously investigate the EDC concentration and the sex hormone balance in the ovaries. Therefore, an effective method has been developed for the quantification of the sex steroid hormones (testosterone, androstenedione, estradiol, and estrone) and four endocrine disrupting chemicals (bisphenol A, atrazine, and the active metabolites of methoxychlor and vinclozolin) in rat ovaries. The sample preparation procedure is based on the so-called "quick, easy, cheap, effective, rugged, and safe" approach, and an analytical method was developed to quantify these compounds with low detection limits by liquid chromatography coupled with a tandem mass spectrometer. This analytical method, applied to rat ovary samples following subacute EDC exposure, revealed some new findings for toxicological evaluation. In particular, we showed that EDCs with the same described in vitro mechanisms of action have different effects on the gonadal steroid balance. These results highlight the need to develop an integrative evaluation with the simultaneous measurement of EDCs and numerous steroids for good risk assessment.

Multi-residue analysis of free and conjugated hormones and endocrine disruptors in rat testis by QuEChERS-based extraction and LC-MS/MS

Endocrine disrupting compounds (EDCs) are suspected to be responsible for many disorders of the human reproductive system. To establish a causality relationship between exposure to endocrine disruptors and disease, experiments on animals must be performed with improved or new analytical tools. Therefore, a simple, rapid, and effective multi-residue method was developed for the determination of four steroid hormones (i.e., testosterone, androstenedione, estrone, and estradiol), glucuronide and sulfate conjugates of estrone and estradiol and four endocrine disruptors in rat testis (i.e., bisphenol A, atrazine, and active metabolites of methoxychlor and vinclozolin). The sample preparation procedure was based on the Quick, Easy, Cheap, Effective, Rugged, and Safe (QuEChERS) approach. An analytical method was then developed to quantify these compounds at ultra-trace levels by liquid chromatography coupled to tandem mass spectrometry. The QuEChERS extraction was optimized with regard to the acetonitrile/water ratio used in the extraction step, the choice of the cleanup method and the acetonitrile/hexane ratio used in the cleanup step. The optimized extraction method exhibited recoveries between 89% and 108% for all tested compounds except the conjugates (31% to 58%). The detection limits of all compounds were below 20 ng g(-1) of wet weight of testis. The method was subsequently applied to determine the levels of hormones and EDCs in seven rat testis samples.

A comparison of two human cell lines and two rat gonadal cell primary cultures as in vitro screening tools for aromatase modulation

Environmental toxicants are a serious health concern, and numerous studies have been devoted to studying the effects of environmental Endocrine Disrupting Chemicals (EDCs). The balance between androgens and estrogens controls the function of many EDC-sensitive organs, and the aromatase enzyme plays a key role in maintaining this balance. In vitro studies have suggested that aromatase expression and activity is a promising biomarker for initial screenings of putative hormonal disrupting compounds. To further validate the aromatase biomarker, we tested several EDCs (atrazine, bisphenol A, methoxychlor, methoxychlor metabolite HPTE, vinclozolin, vinclozolin metabolite M2) in four different models (human cell lines H295R and JEG-3, rat primary cultures of granulosa and leydig cells). We evaluated the similarities/differences in the chemical impact on aromatase mRNA levels and enzymatic activity for the different species and cell types. Aromatase gene expression was assessed by q-RT-PCR, and enzymatic activity was assessed via a tritiated water method with either intact cells or isolated microsomes. The aromatase gene mRNA levels and cellular enzymatic activity varied between the four different models tested, which suggests that the EDC effect varies among different cell types. However, regulation of microsomal aromatase activity appeared to be conserved across all the species and cell types tested. These results suggest that several well characterized complementary cellular models are required to fully characterize the effects of putative EDCs and predict the in vivo effects.

The methoxychlor metabolite, HPTE, inhibits rat luteal cell progesterone production

The methoxychlor metabolite, HPTE, was shown to inhibit P450-cholesterol side-chain cleavage (P450scc) activity resulting in decreased progesterone production by cultured ovarian follicular cells in previous studies. It is not known whether HPTE has any effect on progesterone formation by the corpus luteum. Results Exposure to 100 nM HPTE reduced progesterone production by luteal cells with progressive declines to <22% of control at 500 nM HPTE. Similarly, HPTE progressively inhibited progesterone formation and P450scc catalytic activity of hCG- or 8 Br-cAMP-stimulated luteal cells. However, HPTE did not alter mRNA and protein levels of P450scc. Compounds acting as estrogen (17β-estradiol, bisphenol-A or octylphenol), antiestrogen (ICI) or antiandrogen (monobutyl phthalate, flutamide or M-2) added alone to luteal cells did not mimic the action of HPTE on progesterone and P450scc activity. These results suggest that HPTE directly inhibits P450scc catalytic activity resulting in reduced progesterone formation, and this action was not mediated through estrogen or androgen receptors.

Diethylstilbestrol and the methoxychlor metabolite, HPTE, alter viability and differentiation of embryonic C57BL/6 thymocytes (64.9)

Abstract Endocrine disrupting chemicals (EDCs) with estrogenic activity are ubiquitous in the environment. Studies of select EDCs have suggested that human exposure alters the immune system leading to increases in infection and autoimmune disease frequency. How these alterations occur is unclear. Exogenous and pregnancy-related increases in estrogen have been shown to induce atrophy and alterations in thymocyte development, suggesting a potential mechanism for EDC alteration of the immune system. Diethylstilbestrol (DES), a synthetic estrogen once prescribed to pregnant women, and HPTE, the metabolite of the once widely applied pesticide Methoxychlor (a replacement for DDT) are EDCs of interest. Using an in vitro assay, our research probed whether HPTE and DES alter thymocyte development in embryonic C57Bl/6 mice and at what concentrations. We also examined the mechanism by which DES and HPTE affect thymocyte differentiation. Our preliminary data show a dose-dependent decrease in thymocyte viability and alterations in thymocyte population distribution. Over the range of doses tested, increasing DES and HPTE concentration led to significant decreases in CD4+ intermediate and DP T-cells. Furthermore, we designed a time course experiment to probe the cell death mechanism induced by DES and HPTE using Annexin V and PI staining. Our work suggests that one mechanism of action of DES and HPTE on embryonic thymocytes is induction of cell death through apoptosis.

Effects of methoxychlor and 2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane on 3β-hydroxysteroid dehydrogenase and 17β-hydroxysteroid dehydrogenase-3 activities in human and rat testes

Human and rat testis microsomes were used to investigate direct inhibitory activities of methoxychlor (MXC) and its metabolite 2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane (HPTE) on 3β-hydroxysteroid dehydrogenase (3β-HSD) and 17β-hydroxysteroid dehydrogenase type 3 (17β-HSD3). The 3β-HSD and 17β-HSD3 enzymes are involved in the reactions that culminate in androgen biosynthesis in Leydig cells. The results demonstrated that MXC and HPTE inhibited human 3β-HSD activity at a concentration of 10 nm. The half maximal inhibitory concentration (IC(50) ) for MXC inhibition of 3β-HSD was 53.21 ± 15.52 μm (human) and 46.15 ± 17.94 μm (rat), and for HPTE, it was 8.29 ± 2.49 μm (human) and 13.82 ± 2.26 μm (rat). At the higher concentration of 100 μm, MXC did not affect human and rat 17β-HSD3 activity. However, the IC(50) for HPTE inhibition of 17β-HSD3 was 12.1 ± 1.9 μm (human) and 32 .0 ± 8.6 μm (rat). The mode of action of MXC and HPTE on 3β-HSD activity was non-competitive with the substrate pregnenolone, but was competitive with the cofactor NAD(+) . The mode of HPTE inhibition of 17β-HSD3 was non-competitive with the substrate androstenedione, but was competitive with the cofactor NADPH. In summary, our results showed that HPTE, which is the biologically active metabolite of MXC, has the capacity for direct inhibition of 3β-HSD and 17β-HSD3 enzyme activity. Inhibition of enzyme activity is presumably associated with suppression of steroidogenesis in gonadal tissues and has implications for testis function.

Effects of endocrine disruptors on steroidogenic enzymes gene expression and on aromatase activity in two human cell lines

Endocrine disruptors are chemicals that can alter functions of the endocrine system by several ways. In the present study, we have evaluated the effects of several endocrine disruptors and of some of their metabolites on the last step of steroidogenesis in two cell line models. Two enzymes are implicated in this step: aromatase (CYP19A1), which plays a central role by catalyzing the irreversible conversion of androgens to estrogens, and 17beta-hydroxysteroid dehydrogenase (HSD17B), which catalyses the conversion of inactive sexual hormones to active ones in different steroidogenic organs. We have screened the selected chemicals for their ability to modulate the expression of steroidogenic enzymes and aromatase activity in the human choriocarcinoma JEG-3 cell line and in the human adrenocortical H295R cell line after both short (4 h) and long exposure (24 h). All chemicals were tested at concentrations that did not cause cytotoxicity after 24h of exposure, as tested by the MTT viability assay. Gene expression profile was assessed by real-time RT-PCR and aromatase activity was assessed by the method of tritiated water. Treatments of JEG-3 cells by atrazine, methoxychlor and the vinclozolin metabolite M2 resulted in an increase of CYP19A1 mRNA levels. In contrast, Bisphenol-A and the methoxychlor metabolite HPTE down-regulated the expression of CYP19A1 mRNA. Methoxychlor and HPTE decreased the amount of HSD17B1 mRNAs. In H295R cells, atrazine up-regulated CYP19A1 mRNA expression, HPTE increased HSD17B1 mRNA levels and methoxychlor increased HSD17B1 and HSD17B5 mRNA levels. Concerning the aromatase activity, treatment of H295R cells by atrazine induced aromatase activity. Furthermore, exposure of these cells to either bisphenol A or HPTE inhibited aromatase activity. In JEG-3 cells, which display higher basal aromatase expression than H295R cells, the pattern of aromatase activity regulation was similar but less pronounced. Taken together, these initial results contribute to a better characterization of the action of endocrine disrupting chemicals and their metabolites on the steroidogenic pathways, which needs to be considered when assessing their effects on human health.

Influence of Dietary Coexposure to Benzo(a)pyrene on the Biotransformation and Distribution of 14C-Methoxychlor in the Channel Catfish (Ictalurus punctatus)

Methoxychlor (MXC) is an organochlorine pesticide whose mono- and bis-demethylated metabolites, 2-(4-hydroxyphenyl)-2-(4-methoxyphenyl)-1,1,1-trichloroethane (OH-MXC) and 2,2-bis(4-hydroxyphenyl)-1,1,1-trichloroethane (HPTE), respectively, are estrogenic and antiandrogenic. Studies in vitro showed that treatment of channel catfish with a polycyclic aromatic hydrocarbon increased phase I and phase II metabolism of MXC. To determine the in vivo significance, groups of four channel catfish were treated by gavage for 6 days with 2 mg/kg (14)C-MXC alone or 2 mg/kg (14)C-MXC and 2 mg/kg benzo(a)pyrene (BaP). On day 7, blood and tissue samples were taken for analysis. Hepatic ethoxyresorufin O-deethylase activity was 10-fold higher in the BaP-treated catfish, indicating CYP1A induction. More MXC-derived radioactivity remained in control (42.8 +/- 4.1%) than BaP-induced catfish (28.5 +/- 3.2%), mean percent total dose +/- SE. Bile, muscle and fat contained approximately 90% of the radioactivity remaining in control and induced catfish. Extraction and chromatographic analysis showed that liver contained MXC, OH-MXC, HPTE, and glucuronide but not sulfate conjugates of OH-MXC and HPTE. Liver mitochondria contained more MXC, OH-MXC, and HPTE than other subcellular fractions. Bile contained glucuronides of OH-MXC and HPTE, and hydrolysis of bile gave HPTE and both enantiomers of OH-MXC. The muscle, visceral fat, brain and gonads contained MXC, OH-MXC, and HPTE in varying proportions, but no conjugates. This study showed that catfish coexposed to BaP and MXC retained less MXC and metabolites in tissues than those exposed to MXC alone, suggesting that induction enhanced the elimination of MXC, and further showed that potentially toxic metabolites of MXC were present in the edible tissues.

Glucuronidation and sulfonation, in vitro, of the major endocrine-active metabolites of methoxychlor in the channel catfish, Ictalurus punctatus, and induction following treatment with 3-methylcholanthrene

The organochlorine pesticide, methoxychlor (MXC), is metabolized in animals to phenolic mono- and bis-demethylated metabolites (OH-MXC and HPTE, respectively) that interact with estrogen receptors and may be endocrine disruptors. The phase II detoxication of these compounds will influence the duration of action of the estrogenic metabolites, but has not been investigated extensively. In this study, the glucuronidation and sulfonation of OH-MXC and HPTE were investigated in subcellular fractions of liver and intestine from untreated, MXC-treated and 3-methylcholanthrene (3-MC)-treated channel catfish, Ictalurus punctatus. MXC-treated fish were given i.p. injections of 2 mg MXC/kg daily for 6 days and sacrificed 24 h after the last dose. The 3-MC treatment was a single 10 mg/kg i.p. dose 5 days prior to sacrifice. In hepatic microsomes from control fish, the V max value (mean ± S.D., n = 4) for glucuronidation of OH-MXC was 270 ± 50 pmol/min/mg protein, higher than found for HPTE (110 ± 20 pmol/min/mg protein). For each substrate, the V max values observed in intestinal microsomes were approximately twice those found in the liver. The K m values for OH-MXC and HPTE glucuronidation in control liver were not significantly different and were 0.32 ± 0.04 mM for OH-MXC and 0.26 ± 0.06 mM for HPTE. The K m for the co-substrate, UDPGA, was higher in liver (0.28 ± 0.09 mM) than intestine (0.04 ± 0.02 mM). Treatment with 3-MC but not MXC increased the V max for glucuronidation in liver and intestine. Glucuronidation was a more efficient pathway than sulfonation for both substrates, in both tissues. The V max values for sulfonation of OH-MXC and HPTE, respectively, in liver cytosol were 7 ± 3 and 17 ± 4 pmol/min/mg protein and in intestinal cytosol were 13 ± 3 and 30 ± 5 pmol/min/mg protein. Treatment with 3-MC but not MXC increased rates of sulfonation of OH-MXC and HPTE and the model substrate, 3-hydroxy-benzo( a)pyrene in both intestine and liver. Comparison of the kinetics of the conjugation pathways with those published for the demethylation of MXC showed that formation of the endocrine-active metabolites was more efficient than either conjugation pathway. Residues of OH-MXC and HPTE were detected in extracts of liver microsomes from MXC-treated fish. This work showed that although OH-MXC and HPTE could be eliminated by glucuronidation and sulfonation, the phase II pathways were less efficient than the phase I pathway leading to formation of these endocrine-active metabolites.

The methoxychlor metabolite, HPTE, directly inhibits the catalytic activity of cholesterol side-chain cleavage (P450scc) in cultured rat ovarian cells

Exposure to the pesticide methoxychlor in rodents is linked to impaired steroid production, ovarian atrophy and reduced fertility. Following in vivo administration, it is rapidly converted by the liver to 2,2-bis-( p-hydroxyphenyl)-1,1,1-trichloroethane (HPTE), the reported active metabolite. Both methoxychlor and HPTE have weak estrogenic and antiandrogenic activities, and these effects are thought to be mediated through the estrogen and androgen receptors, respectively. Previous in vivo studies on methoxychlor exposure to female animals have demonstrated decreased progesterone production but no change in serum estrogen levels. We recently showed that HPTE specifically inhibits the P450 cholesterol side-chain cleavage (P450scc, CYP11A1) step resulting in decreased androgen production by cultured rat testicular Leydig cells. The current studies examined the mechanism of action of HPTE on progesterone production by cultured ovarian cells (granulosa and theca-interstitial) from pregnant mare serum gonadotropin-primed immature rats. In addition, we evaluated whether the effects of HPTE on rat ovarian cell progesterone biosynthesis were mediated through the estrogen or androgen receptors. Exposure to HPTE (0, 10, 50 or 100 nM) alone progressively inhibited progesterone formation in cultured theca-interstitial and granulosa cells and the P450scc catalytic activity in theca-interstitial cells in a dose-dependent manner with significant declines starting at 50 nM. However, HPTE did not change mRNA levels of the P450scc system (P450scc, adrenodoxin reductase and adrenodoxin) as well as P450scc protein levels. Of interest, estradiol, xenoestrogens (bisphenol-A or 4- tert-octylphenol), a pure antiestrogen (ICI 182,780), or antiandrogens (4-hydroxyflutamide or the vinclozolin metabolite M-2), had no effect on progesterone production even at 1000 nM. Co-treatment of HPTE with ICI 182,780 did not block the effect of HPTE on progesterone formation. These studies suggest that the decline in progesterone formation following exposure to HPTE in cultured ovarian cells is associated with the inhibition of catalytic activity of P450scc at least in theca-interstitial cells. This action does not appear to be mediated through the estrogen or androgen receptor signaling pathways, and other chemicals exhibiting estrogenic, antiestrogenic or antiandrogenic properties do not mimic its effect on ovarian steroid production.

Methoxychlor and Its Metabolites Inhibit Growth and Induce Atresia of Baboon Antral Follicles

Methoxychlor (MXC), an organochlorine pesticide, inhibits growth and induces atresia of antral follicles in rodents. MXC metabolites, mono-OH MXC (mono-OH) and bis-OH MXC (HPTE), are thought to be more toxic than the parent compound. Although studies have examined effects of MXC in rodents, few studies have evaluated the effects of MXC in primates. Therefore, the present study tested the hypothesis that MXC, mono-OH, and HPTE inhibit growth and induce atresia of baboon antral follicles. To test this hypothesis, antral follicles were isolated from adult baboon ovaries and cultured with vehicle (dimethylsulfoxide; DMSO), MXC (1-100 micro g/ml), mono-OH (0.1-10 micro g/ml), or HPTE (0.1-10 micro g/ml) for 96 hr. Growth was monitored at 24 hr intervals. After culture, follicles were processed for histological evaluation of atresia. MXC, mono-OH, and HPTE significantly inhibited follicular growth and increased atresia compared to DMSO. Moreover, the adverse effects of MXC and its metabolites on growth and atresia in baboon antral follicles were observed at lower (100-fold) doses than those causing similar effects in rodents. These data suggest that MXC and its metabolites inhibit growth and induce atresia of baboon antral follicles, and that primate follicles are more sensitive to MXC than rodent follicles.

Methoxychlor Metabolites May Cause Ovarian Toxicity Through Estrogen-Regulated Pathways

The pesticide methoxychlor (MXC) is a reproductive toxicant that targets antral follicles of the mammalian ovary. Cytochrome P450 enzymes metabolize MXC to mono-OH MXC (1,1,1-trichloro-2-(4-hydroxyphenyl)-2-(4-methoxyphenyl)ethane [mono-OH]) and bis-OH MXC (1,1,1-trichloro-2,2-bis(4-hydroxyphenyl)ethane [HPTE]), two compounds that are proposed to be more toxic than the parent compound, can interact with the estrogen receptor (ER), and are proposed to be responsible for ovarian toxicity. Thus, this work tested the hypothesis that MXC metabolites may be responsible for inducing antral follicle-specific toxicities in the ovary and that this toxicity may be mediated through ER-regulated pathways. Mouse antral follicles were isolated and exposed to mono-OH (0.01-10 microg/ml), HPTE (0.01-10 microg/ml), or MXC (100 microg/ml) alone or in combination with ICI 182,780 (ICI; 1 microM) or 17beta-estradiol (E2; 10 and 50 nM) for 96 h. Follicle diameters were measured at 24-h intervals. After culture, follicles were morphologically evaluated for atresia. Both mono-OH and HPTE (10 microg/ml) inhibited follicle growth and increased follicle atresia. The antiestrogen, ICI, did not protect antral follicles from MXC or metabolite toxicity in regard to follicle growth or atresia, but E2 decreased MXC- and mono-OH-induced atresia in small antral follicles. These data suggest that MXC metabolites inhibit follicle growth and induce atresia and that ER-regulated pathways may mediate the ovarian toxicity of MXC and its metabolites.

Comparative in vitro metabolism of methoxychlor in male and female rats: Metabolism of demethylated methoxychlor metabolites by precision-cut rat liver slices

The in vitro metabolism of demethylated methoxychlor (MXC) metabolites, mono-OH-MXC (including (R)- and (S)-isomers) and bis-OH-MXC (mono- and bis-demethylated MXC, respectively), was conducted using precision-cut liver slices to understand the sex-dependent metabolism of MXC in rats. In the study with bis-OH-MXC, the substrate underwent extensive conjugation producing its glucuronide and glucuronide/sulphate diconjugate, and no significant sex differences were found. On the contrary, the metabolism of mono-OH-MXC appeared to exhibit the sex differences in the metabolic profiles. The bis-OH-MXC glucuronide and glucuronide/sulphate diconjugate were major metabolites in male rat, whereas the mono- and bis-OH-MXC glucuronides predominated in the female. The per cent distribution of the demethylated products (sum of bis-OH-MXC derivatives) was approximately 90% for the male (for both isomers) and 81 (R-) to 56% (S-) for the female. The metabolic profiles in (S)-mono-OH-MXC, which is the predominant enantiomer preferentially produced in MXC metabolism in rats, showed a similar pattern to that of MXC compared with the (R)-isomer. The results indicate that the sex differences in oxidative demethylation of the intermediate, (S)-mono-OH-MXC, could be one of the probable reasons for the sex-dependent metabolism of MXC in rats, and the stereo-structural preference of the contributing demethylase enzymes appear to be involved.

SULFONATION OF ENVIRONMENTAL CHEMICALS AND THEIR METABOLITES IN THE POLAR BEAR (Ursus maritimus)

Although its habitat comprises mostly remote regions of the Arctic, the polar bear is subject to bioaccumulation of persistent environmental pollutants. Along with their phase I metabolites, they are potential substrates for detoxification via sulfonation and glucuronidation. The capability of polar bear liver to sulfonate a structurally diverse group of environmental chemicals, that is, 3-hydroxybenzo[a]pyrene (3-OH-B[a]P), triclosan, 4'-hydroxy-3,3',4,5'-tetrachlorobiphenyl (4'OH-PCB79), 4'-hydroxy-2,3,3',4,5,5'-hexachlorobiphenyl (4'-OH-PCB159), 4'-hydroxy-2,3,3',5,5',6-hexachlorobiphenyl (4'-OH-PCB165), the methoxychlor metabolite 2-(4-methoxyphenyl)-2-(4-hydroxyphenyl)-1,1,1-trichloroethane (OHMXC), tris(4-chlorophenyl)-methanol (TCPM), and pentachlorophenol (PCP) was investigated. The glucuronidation of 3-OH-B[a]P was also studied. Enzyme activity was assayed by incubation of liver cytosol or microsomes derived from three adult male polar bears with 3'-phosphoadenosine-5'-phosphosulfate or uridine 5'-diphosphoglucuronic acid and substrate, followed by fluorometric or radiochemical thin-layer chromatographic analysis. The efficiency of sulfonation decreased in the order 3-OH-B[a]P >>> triclosan >> 4'-OH-PCB79 > OHMXC > 4'-OH-PCB165 > TCPM > 4'-OH-PCB159 > PCP, all of which produced detectable sulfate conjugates. The 3-OH-B[a]P substrate was readily sulfonated and glucuronidated (apparent K(m) 0.41, 1.4 microM, and apparent V(max) 0.50, 3.00 nmol/min/mg, respectively). UDP-glucuronic acid kinetics suggested the presence of multiple enzymes glucuronidating 3-OH-B[a]P. Substrate inhibition was observed for the sulfonation of 3-OH-B[a]P and 4'OH-PCB79 (K(i) 1.0 and 217 microM, respectively). Triclosan was the most rapidly sulfated (apparent V(max) 1008 pmol/min/mg) of the substrates tested. Since sulfonation of an acyclic tertiary alcoholic group, as in TCPM, has not previously been reported, we also examined TCPM conjugation in humans and catfish, both of which formed TCPM-sulfate. The hexachlorinated polychlorinated biphenylols, TCPM, and PCP were poor substrates for sulfonation, suggesting that this may be one reason why these substances and structurally similar xenobiotics persist in polar bears.

The reported active metabolite of methoxychlor, 2,2-bis( p-hydroxyphenyl)-1,1,1-trichloroethane, inhibits testosterone formation by cultured Leydig cells from neonatal rats

Methoxychlor (MC) is an insecticide that is presently used on agricultural crops, especially after the ban on the use of 2,2-bis( p-chlorophenyl)-1,1,1-trichloroethane (DDT) in the United States. Following administration in vivo, MC is converted to 2,2-bis( p-hydroxyphenyl)-1,1,1-trichloroethane (HPTE), which is thought to be the active agent. However, both MC and HPTE have been reported to have weak estrogenic and antiandrogenic activities, and they are thought to exert their potential adverse (endocrine disruptive) effects through the estrogen and androgen receptors, respectively. In a recent study, HPTE was shown to inhibit both basal and hCG-stimulated testosterone production by cultured Leydig cells from immature and adult rats, and these effects were reported to be mediated through the estrogen receptor. Because fetal Leydig cells represent a separate population from adult Leydig cells and many of the reported adverse actions of endocrine disruptors are thought to have their effects during gestational exposure, the present studies examined the effects of HPTE on testosterone formation by cultured fetal Leydig cells from neonatal rats to determine whether these cells are sensitive to HPTE. Our studies demonstrated that HPTE inhibited both basal and hCG-stimulated testosterone formation in a dose-dependent manner. Significant declines in testosterone were observed at about 100 nM HPTE, and this effect was detected as early as 1 h after exposure. The main effects of HPTE appeared to be localized to the cholesterol side-chain cleavage step which converts cholesterol to pregnenolone. In addition, this effect did not appear to be mediated through the estrogen receptor as a weak estrogen or the androgen receptor as an antiandrogen, which are the currently proposed modes of action of MC and HPTE.