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PubMed1992

Passage of methoxychlor in milk and reproductive organs of nursing female mice; 1. Light and scanning electron microscopic observations.

To determine whether the pesticide methoxychlor can be excreted in milk, lactating mouse dams received 14 daily intraperitoneal injections of either sesame oil, or 10.0 micrograms of 17-beta estradiol, or 1.0, 2.0, or 5.0 mg of technical grade methoxychlor. At 15 days, suckling female pups were sacrificed and the effects of the chemicals in milk on the morphology of the immature reproductive tract were examined. The stimulatory changes in both the vagina and uterine horns indicate that the estradiol or methoxychlor doses were excreted in milk and remained biologically active in the suckling mice. Although the stimulatory changes from estradiol or methoxychlor were similar, the higher methoxychlor doses produced some cellular atypia in uterine horns. The possible consequences of early stimulatory influence of methoxychlor on adult reproductive organs are discussed in the text.

Animals↗

PubMed2003

The multidrug resistance-associated protein 1 transports methoxychlor and protects the seminiferous epithelium from injury.

We examined the ability of the multidrug resistance-associated protein 1 (MRP1/ABCC1) to transport pesticides, as this transporter mediates the cellular efflux of a variety of xenobiotics, typically as glucuronide, sulfate, or glutathione conjugates. NIH3T3 cells stably expressing MRP1 were 3.37-fold more resistant to the toxicity of fenitrothion, 3.12-fold more resistant to chlorpropham, and 2.5-fold more resistant to methoxychlor, a pesticide with estrogenic and anti-androgenic metabolites. The cells expressing MRP1 also eliminated methoxychlor two times more rapidly than their mock-transfected counterparts. We then examined whether mrp1 expression could alter the toxicity of methoxychlor in vivo using male FVB/mrp1 knockout mice (FVB/mrp1-/-). Both control and knockout mice were fed 25 mg/kg methoxychlor in honey for 39 days, and its effects on testicular morphology were examined. Methoxychlor treatment did not significantly affect testicular morphology in the FVB mice, but markedly reduced the number of developing spermatocytes in the FVB/mrp1-/- mice. These results suggest that MRPI may play a role in protecting the seminiferous tubules from methoxychlor-induced damage.

3T3 Cells↗

PubMed2002

Modulation of mammary gland development in prepubertal male rats exposed to genistein and methoxychlor.

The estrogenic isoflavone genistein is a common dietary component that has been shown to affect reproductive development in experimental animals at high doses. The objective of the present study was to examine interactions of genistein and the hormonally active pesticide methoxychlor on mammary gland development in juvenile rats. Timed-pregnant Sprague-Dawley rats were fed a soy- and alfalfa-free diet containing different combinations of genistein (300 and 800 ppm) and methoxychlor (800 ppm). Rats were fed these diets starting on gestation day (GD)1 and continuing through pregnancy and lactation until postnatal day (PND) 22, when the pups were killed. Inguinal mammary glands from both female and male pups were processed as whole-mount preparations for morphometric analysis. The total glandular area and the numbers of branch points, lateral buds, and terminal end buds in the male rats were found to be significantly greater in the groups exposed to methoxychlor than those exposed to genistein only. These effects were not observed in the female rats. In the male rats, methoxychlor had the most prominent effect on elongating the glandular ducts, while genistein enhanced the ductile branching. The 2 compounds in combination promoted the development of alveolar-lobular structure, an effect not observed with either compound alone. Immunostaining for proliferating cell nuclear antigen revealed a high percentage of immunopositive cells in the mammary epithelia of the males exposed to methoxychlor and genistein (800 ppm) compared to the controls. While no significant changes in serum levels of mammotrophic hormones were detected, increased immunostaining for insulin-like growth factor-1 receptor, estrogen receptor alpha, and progesterone receptor in the genistein + methoxychlor group suggested that local factors involved in regulating mammary growth may have played a role in propagating the endocrine effects of these two compounds. These results indicated that the mammary glands of juvenile male rather than juvenile female rats may be more sensitive to certain endocrine-active compounds and that high levels of phytoestrogens have the potential to alter the toxicological behaviors of other hormone mimics.

Animals↗

PubMed1998

Mechanism of induction of rat hepatic CYP2B and 3A by the pesticide methoxychlor.

Our earlier investigation demonstrated that methoxychlor treatment induced hepatic cytochrome P450 2B1/2B2 and 3A proteins in rats and enhanced their respective enzymatic activities. To determine the mechanism of the methoxychlor-mediated induction and whether methoxychlor acts as a frank inducer and not merely by causing stabilization of the cytochrome P450 proteins or of their mRNAs, we assessed the effect of methoxychlor treatment on the transcriptional rate and mRNA levels of these hemeproteins by nuclear run-on and northern blot analyses. Methoxychlor treatment markedly elevated the transcriptional rates of cytochrome P4502B1/2B2 and 3A. Also, higher levels of mRNA of these CYPs were observed. By contrast, mRNA levels of CYP1A1/1A2 were not affected. Using a nuclear run-on method that apparently measures specifically the transcription initiation rate of CYP2B1 and 2B2, we observed that the transcriptional rate of 2B2 was increased substantially more than that of CYP2B1. This differential induction of CYP2B2 versus 2B1 may account for the discrepancy between the levels of induced CYP2B protein and the much lower-than-expected CYP2B-mediated enzymatic activity observed in our earlier study.

Animals↗

PubMed2001

A repeated 28-day oral dose toxicity study of methoxychlor in rats, based on the 'enhanced OECD test guideline 407' for screening endocrine-disrupting chemicals.

In association with the international validation project to establish an OECD Enhanced Test Guideline 407, we performed a 28-day repeated-dose toxicity study of methoxychlor, a chlorinated hydrocarbon pesticide with pro-estrogenic and anti-androgenic activities. Attention was paid to the sensitivity of certain additional parameters for detecting endocrine related effects of endocrine disrupting chemicals based on the existing TG 407. Seven-week-old Crj:CD(SD)IGS rats were allocated to one of four groups, each consisting often males and ten females, and methoxychlor was administered once daily by gavage at doses of 0 (control), 20, 100 or 500 mg/kg body weight per day. Male rats were killed on the day after the 28th administration. Female rats were killed on the day of the diestrus stage during 4 days after the 28th administration. Male rats receiving methoxychlor showed mainly atrophy of mammary acinus in the 20 mg/ kg and higher groups, together with decreases in prostate and seminal vesicle weights, and atrophy of epididymis, prostate, seminal vesicle and coagulating gland in the 100 and 500 mg/kg groups. In addition, decrease in serum testosterone level, increase in follicle-stimulating hormone level, decrease in testis and epididymis weights, atrophy of semiferous tubules and Leydig cells, decrease in the number of sperm in the caudal epididymis and their motility were observed in the 500 mg/kg group. Female rats receiving methoxychlor showed mainly abnormal estrous cycles, decrease in serum luteinizing hormone level, decrease in ovary weight, proliferation of mammary acinus, atrophy of ovary due to decrease in follicles and corpus luteum in histopathology, hypertrophy of endometrial epithelium of uterus and vagina epithelium in the 100 and 500 mg/kg groups. Among the parameters tested in the present experimental system, effects of methoxychlor on endocrine-related organs were detected with regard to serum hormone, organ weights, histopathological examination in both sexes, estrus cycle in females and sperm examination in males. Based on these results, a no-observed-adverse-effect level (NOAEL) in the present study was estimated to be below 20 mg/kg per day. In particular, the adverse effects were effectively detected in organ weights of accessory sex organs and histopathological examination.

Administration, Oral↗

PubMed1985

Alteration of behavioral sex differentiation by exposure to estrogenic compounds during a critical neonatal period: effects of zearalenone, methoxychlor, and estradiol in hamsters.

The present study was designed to determine if neonatal exposure to the estrogenic mycotoxin zearalenone or the weakly estrogenic pesticide methoxychlor could masculinize and/or defeminize the behavior of female hamsters. Neonatal hamsters were given a single sc injection of either zearalenone (1 mg/pup), methoxychlor (1 mg/pup), 17 beta-estradiol (E2) (40 micrograms/pup), or the vehicle 2 days after birth. After puberty, behavioral estrous cyclicity was measured. The females were then ovariectomized, treated with the male hormone testosterone, and tested for their ability to mount a receptive female (a behavior not normally displayed by female hamsters). Females treated neonatally with estradiol or zearalenone were masculinized but not defeminized, an effect consistent with perinatal exposure to low doses of sex hormones. Females in these two treatment groups displayed normal 4-day behavioral estrous cycles, but following ovariectomy and testosterone treatment they mounted a sexually receptive female at a frequency comparable to the males. Methoxychlor-treated females did not differ from controls. The mounting behavior of similarly treated males was unaffected by any of the chemicals. However, males receiving estradiol treatment had smaller testes, seminal vesicles, and cauda epididymides and 57% had epididymal cysts. These results demonstrate that a single exposure to a weakly estrogenic chemical like zearalenone during a critical developmental period can cause the brain to differentiate in a manner inconsistent with the female's genetic sex. This enables the female to respond to the activational influence of testosterone as an adult and readily mount a sexually receptive female. The failure of methoxychlor to alter reproductive development in the current study may be due to an inability of the neonatal hamster to convert methoxychlor to estrogenic metabolites.

Animals↗

PubMed1991

Ultrastructure of vagina and uterus in young mice after methoxychlor exposure.

Ultrastructural effects of 17 beta-estradiol were compared with technical pesticide methoxychlor in uterus and vagina of young mice. Neonates received 14 daily ip injections of either sesame oil, 10.0 micrograms 17 beta-estradiol, or 0.05, 0.1, 0.5, or 1.0 mg methoxychlor. Estradiol accelerated vaginal opening to 11 days, increased reproductive tract weight gain, and induced vaginal cornification, the cells of which exhibited complex surface microridge patterns. The hypertrophied uterine cells were covered with dense, enlarged microvilli with bulbous expansions or clumps. The highest three methoxychlor doses were stimulatory. Exposure to 0.5 or 1.0 mg methoxychlor increased reproductive tract weights threefold due to excessive fluid accumulation, and induced vaginal cornification and opening by 10 days. The cornified cells lacked complex surface microridges, while uterine cells exhibited dense microvilli growth, atypical morphology, and separation. Although 0.5 and 1.0 mg methoxychlor were highly stimulatory, the surface alterations in uterus and vagina appeared different from estradiol.

Animals↗

PubMed2000

The effect of raloxifene on the uterine weight response in immature mice exposed to 17beta-estradiol, 1,1,1-trichloro-2, 2-bis(p-chlorophenyl)ethane, and methoxychlor.

OBJECTIVE: The purpose of this study was to determine the effects of raloxifene on the uterine responses to both estradiol and the environmental estrogens 1,1,1-trichloro-2, 2-bis(p-chlorophenyl)ethane and methoxychlor in immature mice. STUDY DESIGN: Immature female mice received the following compounds alone or in combination: sesame oil (control), 17beta-estradiol 1 mg/kg body weight, tamoxifen 1 mg/kg body weight, raloxifene 5 mg/kg body weight, 1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane 10 mg/kg body weight, and methoxychlor 10 mg/kg body weight. The animals were treated subcutaneously once a day for 5 consecutive days with the compound or compounds of interest in 0.1 mL sesame oil. Approximately 24 hours after the final treatment the animals were killed and the uteri were excised, stripped of remaining fat and mesentery, and weighed. Groups were analyzed with analysis of variance. RESULTS: Estradiol increased the mean (+/-SE) weight from 20 +/- 6.4 mg (as measured in the control group) to 77 +/- 6.2 mg. Tamoxifen increased uterine weight to 60 +/- 6.2 mg; however, raloxifene had no effect on uterine weight. Both 1,1,1-trichloro-2, 2-bis(p-chlorophenyl)ethane and methoxychlor increased uterine weight significantly, to 82 +/- 2.4 mg and 35 +/- 6.0 mg respectively. When raloxifene was coadministered with 17beta-estradiol it did not block the increase in uterine weight; however, when raloxifene was coadministered with 1,1,1-trichloro-2, 2-bis(p-chlorophenyl)ethane or methoxychlor, it completely blocked the uterine weight gain induced by either xenoestrogen. CONCLUSION: Raloxifene blocked the xenoestrogens 1,1,1-trichloro-2, 2-bis(p-chlorophenyl)ethane and methoxychlor but did not block 17beta-estradiol in the mouse model described. These results suggest that the xenoestrogens exert their estrogenic activities through a different site on the estrogen receptor or through a different mechanism than 17beta-estradiol.

Animals↗

PubMed1984

The fate of methoxychlor in soils and transformation by soil microorganisms.

Methoxychlor was found to be sufficiently persistent in soil and its residues were present even 18 months after the soil treatment. Saprophytes, fungi and actinomyces were unaffected by varying concentrations of methoxychlor, azotobacter however was susceptable. Soil strains isolated did not utilize methoxychlor as a sole carbon source except for 9 cultures belonging to the genera Bacillus, Acinetobacter and Rhodococcus which carried out the complete dechlorination, demethylation and splitting of one of methoxychlor aromatic rings. Anaerobic conditions were more favorable for methoxychlor biodegradation by soil and pure microbial cultures.

Acinetobacter↗

PubMed2000

Estrogenic activity of octylphenol, nonylphenol, bisphenol A and methoxychlor in rats.

Considerable attention has recently been focused on environmental chemicals that disrupt the reproductive system by altering steroid receptor function. Although numerous in vitro and in vivo methods have been shown to be useful approaches for identifying chemicals that can disrupt reproduction through a direct interaction with the estrogen receptor, it is imperative that the protocols selected be capable of detecting chemicals with a broad range of estrogenic activity. Here we evaluate the reliability of the 3-day uterotrophic assay for detecting chemicals with strong or weak estrogenic activity in both prepubertal and ovariectomized adult Long Evans rats. These data were compared to additional measures of estrogenic activity, which included the age of vaginal opening, the induction of cornified vaginal epithelial cells in ovariectomized adult rats, and estrous cyclicity in intact adult rats. Test chemicals selected for these studies included 17-beta-estradiol, ethynyl estradiol, methoxychlor, 4-tert-octylphenol, 4-nonylphenol and bisphenol A. Data from in vitro receptor binding assays compared the ability of the test chemicals to compete with [3H]-estradiol or [3H]-promegestone for binding to estrogen or progesterone receptors. As expected, the binding affinities for the estrogen receptor ranged from high to low, as reflected by Ki concentrations of 0.4 nM for 17-beta-estradiol and ethynyl estradiol, and 0.05-65 microM for 4-tert-octyphenol, 4-nonylphenol, and methoxychlor. Although none of the test chemicals demonstrated a high affinity for binding to the progesterone receptor, 4-tert-octylphenol and 4-nonylphenol exhibited a weak affinity, with Ki concentrations ranging from 1.2 to 3.8 microM. In vivo studies indicated that the 3-day uterotrophic assay in prepubertal rats was the best method for detecting estrogenic activity when compared with all other end points, based upon the dose-response data for ethynyl estradiol (0.01-0.1 mg/kg), 4-tert-octylphenol (50-200 mg/kg, oral), and 4-nonylphenol (25-100 mg/kg, oral). Although oral doses of ethynyl estradiol (0.01 mg/kg) and 4-nonylphenol (50 mg/kg) induced a significant increase in uterine weight in the prepubertal rats, these doses were ineffective for stimulating a similar response in ovariectomized adult rats. The age of vaginal opening was advanced following oral exposure from postnatal days 21-35 to ethynyl estradiol (0.01 mg/kg), methoxychlor (50 mg/kg), 4-tert-octylphenol (200 mg/kg), and 4-nonylphenol (50 mg/kg). Although bisphenol A (200 mg/kg, oral) induced a significant uterotrophic response within 3 days in prepubertal rats, doses up to 400 mg/kg failed to advance the age of vaginal opening. Monitoring changes in the vaginal epithelium of ovariectomized adult rats was the least effective method for detecting estrogenic activity for 4-tert-octylphenol and bisphenol A. The number of 4-5 day estrous cycles was reduced during a 25-day exposure to ethynyl estradiol (0.01 mg/kg), methoxychlor (50 mg/ kg), 4-tert-octylphenol (200 mg/kg), 4-nonylphenol (100 mg/kg), and bisphenol A (100 mg/kg) by oral gavage. Although long periods of extended diestrus (7-14 days) were generally correlated with exposure to ethynyl estradiol and 4-tert-octylphenol, the cycling patterns following exposure to methoxychlor, 4-nonylphenol and bisphenol A were not as clearly defined, with shorter periods of extended diestrus (4-7 days) and/or estrus (3-5 days) intermittently observed throughout the exposure period. Together these data provide a comparison of the 3-day uterotrophic assay with alternative measures of estrogenic activity for a group of test chemicals with a broad range of affinities for the estrogen receptor. These data can be useful during the assessment and validation of methods for screening environmental chemicals for endocrine disrupting activity.

Animals↗

PubMed1990

Morphological and biochemical alterations in reproductive tracts of neonatal female mice treated with the pesticide methoxychlor.

Effects of estradiol-17 beta and the estrogenicity of different doses of the technical grade pesticide methoxychlor were compared in the vagina, uterus, and oviducts of neonatal mice. Beginning within 24 h of birth, neonates received 10 daily i.p. injections of sesame oil vehicle, 10.0 micrograms estradiol, or 0.05, 0.1, 0.5, or 1.0 mg methoxychlor. Estradiol injections induced precocious vaginal opening, complete vaginal cornification, and increased total reproductive tract weight and its DNA content. In comparison to the controls, the three highest methoxychlor doses also significantly increased the weights of the reproductive tracts and stimulated their development. The two highest doses (0.5 and 1.0 mg) also induced precocious vaginal opening and complete vaginal cornification. In addition, the same two doses produced atypical cells in the uterus and oviducts that may be indicative of early dysplasia; similar atypia were not recorded following estradiol treatments. Total DNA content in various reproductive organs increased with increased methoxychlor dosages. Dose-response changes were observed in the oviduct and uterus but not vagina. In summary, methoxychlor stimulated the development of neonatal female reproductive tracts, even at concentrations not previously reported to be biologically active. Furthermore, the higher doses induced abnormalities that were not seen following estradiol treatment; these abnormalities may represent precursors of pathological changes.

Animals↗

PubMed2002

Metabolism of the endocrine disruptor pesticide-methoxychlor by human P450s: pathways involving a novel catechol metabolite.

The metabolism of methoxychlor, a proestrogenic pesticide (endocrine disruptor), was investigated with cDNA expressed human cytochrome P450s and liver microsomes (HLM). In addition to 1,1,1-trichloro-2-(4-hydroxyphenyl)-2-(4-methoxyphenyl)ethane (mono-OH-M), 1,1,1-trichloro-2, 2-bis(4-hydroxyphenyl)ethane (bis-OH-M), and 1,1,1-trichloro-2-(4-hydroxyphenyl)-2-(3, 4-dihydroxyphenyl)ethane (tris-OH-M), a new metabolite was identified as 1,1,1-trichloro-2-(4-methoxyphenyl)-2-(3, 4-dihydroxyphenyl)ethane (catechol-M; previously assumed to be ring-OH-M) and as a key metabolic intermediate. A novel metabolic route was proposed involving methoxychlor O-demethylation to mono-OH-M, followed by bifurcation of the pathway, both leading to the same final product tris-OH-M: pathway a, mono-OH-M is demethylated to bis-OH-M, followed by ortho-hydroxylation forming tris-OH-M and pathway b, mono-OH-M is ortho-hydroxylated forming catechol-M that is O-demethylated forming tris-OH-M. Among the human cDNA-expressed P450s examined, CYP1A2, 2A6, 2C8, 2C9, 2C19, and 2D6 exhibited mainly O-demethylation, with CYP2C19 being the most catalytically competent. CYP3A4, 3A5, and rat 2B1 catalyzed primarily ortho-hydroxylation of mono-OH-M (CYP3A4 being catalytically the most active) but were weak in O-demethylation. CYP1A1, 1B1, 2E1, and 4A11 demonstrated little or no catalytic activity. CYP2B6 appeared unique, catalyzing effectively both O-demethylation and ortho-hydroxylation. Thus, CYP2B6 demethylated methoxychlor to mono-OH-M and ortho-hydroxylated the mono-OH-M forming catechol-M; however, 2B6 did not appreciably demethylate mono-OH-M or ortho-hydroxylate bis-OH-M, suggesting a narrow substrate specificity. CYP2C19-catalyzed demethylation of methoxychlor, mono-OH-M and catechol-M, demonstrating relatively good substrate affinity (K(m) = 0.23 - 0.41 microM). However, the 3A4 ortho-hydroxylation of mono-OH-M and bis-OH-M exhibited lower affinity, K(m) = 12 and 25 microM, respectively. Thus, a phenolic group seems essential for efficient ortho-hydroxylation, forming catechol-M and tris-OH-M. Inhibition studies with HLM and P450s indicate that CYP2C9 and likely 2C19 are catalysts of methoxychlor-mono-demethylation.

Catechols↗

PubMed1997

Methoxychlor as a model for environmental estrogens.

Estrogens can have a variety of physiological effects, especially on the reproductive system. Chemicals with estrogenic activity that are present in the environment may thus be considered potentially hazardous to development and/or reproduction. Methoxychlor is one such chemical, a chlorinated hydrocarbon pesticide with proestrogenic activity. Metabolism of the chemical either in vivo or using liver microsomes produces 2,2-bis(p-hydroxyphenyl)- 1,1,1-trichloroethane (HPTE), the active estrogenic form, and the delineation of this mechanism is reviewed herein. When administered in vivo, methoxychlor has adverse effects on fertility, early pregnancy, and in utero development in females as well as adverse effects on adult males such as altered social behavior following prenatal exposure to methoxychlor. Effects of methoxychlor on the female have been studied extensively, whereas reports on the chemical's effects on males are less common. From the studies reviewed here, the reproductive toxicity of methoxychlor is evident, but the significance of this toxicity with respect to human health remains to be determined.

Animals↗

PubMedDate not supplied

Metabolism of the proestrogenic pesticide methoxychlor by hepatic P450 monooxygenases in rats and humans. Dual pathways involving novel ortho ring-hydroxylation by CYP2B.

Previous studies demonstrated that methoxychlor [1,1,1-trichloro-2,2-bis-(4-methoxyphenyl)ethane] is a proestrogen and is toxic to mammalian reproductive processes. Mammalian liver microsomes sequentially demethylate methoxychlor (I), yielding two estrogenic metabolites, mono-OH-M (II) and bis-OH-M (III). Liver microsomes from phenobarbital (PB)-treated rats (PB microsomes) additionally formed a catechol product, tris-OH-M (VII) (Kupfer et al., Chem. Res. Toxicol. 3, 8-16, 1990). This study shows that, in addition to compounds II, III and VII, male and female rat PB microsomes catalyze the formation of a novel ring-hydroxylated methoxychlor metabolite, ring-OH-M (IV). Liver microsomes from male rats treated with pregnenolone-16 alpha-carbonitrile formed the same metabolites as PB microsomes, but the ring-OH-M was formed only in minute amounts, and there was no tris-OH-M. Liver microsomes from methylchlolanthrene-treated and control male rats demethylated methoxychlor, but did not form ring-hydroxylated products. Similarly, human liver microsomes exhibited demethylation but not ring-hydroxylation. Incubation of mono-OH-M (II) with control rat liver microsomes yielded only bis-OH-M (III), whereas incubation of ring-OH-M (IV) resulted in monodemethylated (dihydroxy) compounds V/VI and didemethylated ring-hydroxylated compound, tris-OH-M (VII). Incubation of (IV) with PB microsomes led to compounds V and/or VI and tris-OH-M (VII), whereas incubation of mono-OH-M (II) yielded bis-OH-M (III) and tris-OH-M (VII). The evidence indicates that ring-hydroxylation is catalyzed by CYP2B: a) induction of CYP2B was required for ring-hydroxylation; b) antibodies against CYP2B1/2 strongly inhibited the formation of the ring-hydroxylated products by PB microsomes; c) incubation of methoxychlor with reconstituted CYP2B1 yielded both the hydroxylated (IV and VII) and the demethylated (II and III) metabolites; and d) reconstituted CYP2B1 converted mono-OH-M into bis-OH-M and tris-OH-M, whereas bis-OH-M was converted into tris-OH-M. Human CYP2B6 exhibits ring-hydroxylation, indicating that this reaction is catalyzed by several CYP2B isozymes. In addition, this study demonstrates that the formation of the catechol tris-OH-M involves two metabolic pathways: via O-demethylation followed by ring-hydroxylation and via ring-hydroxylation and subsequent O-demethylation.

Animals↗

PubMed1979

Interstitial cell carcinomas of the testis in Balb/C male mice ingesting methoxychlor.

Balb/c and C3H strains male and female mice ingested 750 ppm methoxychlor or 100 ppm DDT in the diet for 2 years. Balb/c strain male mice ingesting methoxychlor developed a highly significant incidence of interstitial cell carcinomas of the testis. Balb/c strain male mice ingesting DDT and C3H strain male mice receiving methoxychlor or DDT did not have testicular tumors. The carcinomas of the testis varied from well-differentiated to poorly differentiated and undifferentiated and were capable of metastasis. Carcinomas of the testis have been described in Balb/c strain male mice, but not C3H, given estrogens. The carcinogenicity for testis of Balb/c strain male mice is most likely related to the estrogenic activity of methoxychlor.

Animals↗

PubMed1976

Methoxychlor effects on hepatic storage of vitamin A in rats.

Sixty Sprague-Dawley rats were fed diets containing 0, 10, 100, 1,000, and 10,000 ppm of methoxychlor for 16 weeks under ad libitum- and restricted-feeding regimens. Methoxychlor at 10,000 ppm was lethal to some rats, reduced food consumption and growth, and increased liver weight relative to body weight. Methoxychlor at 1,000 ppm reduced food consumption and growth of rats fed ad libitum but did not reduce growth of restricted-fed rats. Reduced hepatic storage of vitamin A was detectable when methoxychlor was fed at levels of 100 ppm or higher.

Animals↗

PubMed2004

Embryonic co-exposure to methoxychlor and Clophen A50 alters sexual behavior in adult male quail.

Embryonic exposure to estrogens and estrogenic pollutants is known to demasculinize sexual behavior in adult male Japanese quail. In the present study, we administered the insecticide methoxychlor to quail eggs at a dose of 150 microg/g egg and then studied sexual behavior and other reproductive variables in adult males. In a second experiment we administered the same dose of methoxychlor together with 10 microg/g egg of the commercial polychlorinated biphenyl (PCB) mixture Clophen A50 (CA50) and also CA50 alone. Neither methoxychlor nor CA50 had any significant effects by themselves, but when they were administered together a significant reduction in male sexual behavior was observed. It seems likely that induction of biotransformation enzymes in the embryos by CA50 resulted in increased conversion of methoxychlor to the more estrogenic metabolite 2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane (HPTE).

Animals↗

PubMed1988

Methoxychlor induces estrogen-like alterations of behavior and the reproductive tract in the female rat and hamster: effects on sex behavior, running wheel activity, and uterine morphology.

The current investigation was designed to determine if the pesticide methoxychlor (M) mimicked the effects of estrogen in the brain and on behavior. Running wheel activity (RWA) and sex behaviors were evaluated in this study because the role of estrogen in the regulation of these behaviors has been thoroughly established. M exposure at 400 mg/kg/day (90% pure) induced high levels of acyclic RWA and persistent vaginal estrus in the female rats. Following ovariectomy (ovx), RWA declined precipitously in controls but remained at high levels in M-treated-ovx females. M also produced estrogen-like alterations of the uterine endometrial epithelium, the ovary, and growth after ovx. In another study, ovx female rats were dosed with M at 200 mg/kg/day and then with progesterone (P). P acts as an antiestrogen and specifically suppresses estrogen-induced RWA. P blocks the synthesis of estrogen receptors in the CNS and reproductive tract but does not lower RWA induced by nonestrogenic mechanisms. After 14 days of M administration RWA was increased fourfold over the ovx-oil-treated females. Subsequently, P injections reduced RWA levels far below those seen when the ovx-M-treated rats were injected with oil. The P-induced decline represents a 95% inhibition of the M-induced increase in RWA. Subsequently, M-treated-ovx rats and hamsters were injected with P and tested for their ability to display reproductive behaviors when paired with a stud male. Female sexual behaviors are induced by the administration of estrogen followed by progesterone. In this study the M-treated females displayed reproductive behaviors, in contrast to the oil-treated rats and hamsters. The observation that the high levels of RWA induced by methoxychlor treatment in ovx rats can be suppressed by concurrent progesterone injections demonstrates that the increase in RWA is due to the estrogenic effects of methoxychlor on the CNS. The fact that methoxychlor, followed by P injections, induces behavioral estrus in the rat and hamster extends this estrogenicity to other areas in the CNS.

Animals↗