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At least 19 recordsLinked to original sources
PubMed1990

Studies on the formation of methoxychlor-protein adduct in rat and human liver microsomes. Is demethylation of methoxychlor essential for cytochrome P450 catalyzed covalent binding?

Previous studies demonstrated that liver microsomal monooxygenases metabolize the pesticide methoxychlor into phenolic estrogenic derivatives. Additionally, methoxychlor is activated by the hepatic cytochrome P450 monooxygenase to bind covalently to microsomal proteins (Bulger WH, Temple JE and Kupfer D, Toxicol Appl Pharmacol 68: 367-374, 1983). The current study examines, in liver microsomes from control and phenobarbital-treated rats and humans, whether demethylation of methoxychlor is essential for covalent binding and whether demethylated methoxychlor metabolites are on the pathway of formation of the reactive intermediate and protein adduct. Using 3H-methoxyl-labeled and 14C-ring-labeled methoxychlor, it was demonstrated that demethylation is not essential for covalent binding. Namely, the major portion of the methoxychlor moiety in the protein adduct was found to contain intact methoxyls. Nevertheless, in the absence of methoxychlor, both the mono- and bis-demethylated methoxychlor metabolites could undergo monooxygenase-mediated covalent binding to proteins. This was demonstrated in incubations of purified 14C-labeled mono- and bis-demethylated methoxychlor metabolites with liver microsomes, in the presence of NADPH. Additionally, the dehydrochlorinated metabolite of methoxychlor, containing a double bond, underwent covalent binding, which exhibited characteristics similar to those of methoxychlor. These findings demonstrated that the protein adduct from relatively brief incubation periods contains a methoxychlor derivative with intact methoxyls. The possibility that the activation of methoxychlor involves modification of the side chain, which is the active site that binds to proteins, is discussed.

Animals↗
PubMedDate not supplied

Interactions of methoxychlor, methoxychlor base-soluble contaminant, and 2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane with rat uterine estrogen receptor.

Laboratory grade methoxychlor (99% pure), base-washed methoxychlor, and a metabolite of methoxychlor, 2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane (HPTE), were tested for their ability to compete with [3 H] estradiol-17 beta ([3 H]E2) for specific binding to the estrogen receptor from immature rat uterine cytosol. The binding was determined on 10--30% sucrose gradients and by a dextran-coated charcoal assay and subsequent Scatchard plot analysis. On gradients, laboratory grade methoxychlor, but not base-washed methoxychlor, suppressed [3 H]E2 binding to the 8S estrogen receptor. However, the base-soluble fraction from washing of laboratory grade methoxychlor caused suppression o[3 H]E2 binding on sucrose gradients at a concentration as low as 3.6 ppm. Scatchard plot analysis indicated that the inhibition of binding observed with laboratory grade methoxychlor was competitive in nature and not caused by receptor destruction. It was concluded that laboratory grade methoxychlor contained a contaminant that was potentially estrogenic. HPTE, an in vivo metabolite of methoxychlor, caused a marked suppression of [3 H]E2 binding in the 85 region of the gradients. Analysis by Scatchard plot indicated that the effect of HPTE was not to decrease the number of E2 binding sites but merely to alter the affinity of binding to the receptor, presumably in a competitive manner. The low K1 value for HPTE suggested an extremely high affinity for uterine cytosolic E2 receptors.

Animals↗
PubMed1975

Residues of methoxychlor and other chlorinated hydrocarbons in water, sand, and selected fauna following injections of methoxychlor black fly larvicide into the Saskatchewan River, 1972.

In May 1972, 0.309 ppm methoxychlor black fly larvicide was applied in a single test on the North Saskatchewan River. Eight to nine days later residues of 0.05-0.10 ppm methoxychlor occurred in sand 21-22 km downstream from the point of injection. Methoxychlor was not detected in water, insect larvae, shellfish, or muscle tissues of three fish species on the same sampling date. Perhaps because of relatively high oil content in goldeye fish, methoxychlor residues in muscle tissues were 1.0-1.5 ppm in 8 percent of those sampled, 0.21-0.99 in 21 percent, and 0.02-0.20 in 37 percent. In 34 percent of the goldeye fish no residues were detected. Goldeye and other fish collected before or 17 weeks after this injection did not contain detectable levels of methoxychlor. River water in two samples of the injected slug of water collected 6.5 km downstream from the point of injection contained 0.14 and 0.16 ppm methoxychlor. The suspended solids filtered from these sample contained 40 and 47 percent of this methoxychlor (437 and 892 ppm, respectively). Thus methoxychlor may act selectively against filter-feeding species, especially black fly larvae.

Animals↗
PubMed1985

Role of hepatic monooxygenases in generating estrogenic metabolites from methoxychlor and from its identified contaminants.

Previous investigations demonstrated that methoxychlor [1,1,1-trichloro-2,2-bis(4-methoxyphenyl)ethane] contains estrogenic contaminants and that methoxychlor per se is not an estrogen but is a proestrogen being metabolized in vivo into estrogenic products. The present study examined structurally identified methoxychlor contaminants as to their estrogenic or proestrogenic properties. Also, the estrogenic activity of demethylated metabolites of methoxychlor and of one contaminant was determined. To examine these properties, we utilized an assay developed by us that monitors whether a given compound, incubated with isolated rat uteri, can diminish the uterine cytosolic estrogen receptor and elevate the nuclear estrogen receptor and whether metabolic intervention by hepatic microsomal monooxygenase(s) is required by the respective compound for this cellular redistribution of the receptor. Of the 15 compounds examined which constitute with methoxychlor 99.5% of total technical grade methoxychlor, two compounds, 1,1-dichloro-2-(4-hydroxyphenyl)-2-(4-methoxyphenyl)ethene (mono-OH-MDDE) and 1,1,1-trichloro-2-(4-hydroxyphenyl)-2-(4-methoxyphenyl)ethane (mono-OH-methoxychlor), were active per se and two compounds, 1,1-dichloro-2,2-bis(4-methoxyphenyl)ethene (MDDE) and methoxychlor, required metabolic transformation for estrogenic activity to be manifested. Subsequently, it was shown that the mono- and bis-OH metabolites of MDDE and of methoxychlor were active estrogens and that the order of activity, either by the above procedure or in terms of relative binding affinity to rat uterine cytosolic receptor, was as follows: bis-OH-MDDE much greater than bis-OH-methoxychlor greater than mono-OH-MDDE greater than mono-OH-methoxychlor. Following the in vitro observations, the activity of MDDE and bis-OH-MDDE was determined in vivo in immature rats. It appears that both compounds are estrogenic, yielding marked elevation in ornithine decarboxylase (EC 4.1.1.17) levels and moderate increase in uterine weight. A comparison with methoxychlor and bis-OH-methoxychlor [1,1,1-trichloro-2,2-bis(p-hydroxyphenyl)ethane] demonstrates that the order of potencies is similar to that observed in the in vitro determinations. These studies demonstrate the usefulness of the in vitro assay for determining the estrogenic and proestrogenic properties of compounds of which limited quantities are available, often insufficient for in vivo determination. Also, whereas the in vitro assay is simple and rapid, a lengthy investigation might be required to determine in vivo whether a given compound is an estrogen or a proestrogen.(ABSTRACT TRUNCATED AT 400 WORDS)

Animals↗
PubMed1986

Characteristics of the active oxygen in covalent binding of the pesticide methoxychlor to hepatic microsomal proteins.

This study examined the characteristics of the active oxygen species involved in generation of the reactive intermediate of methoxychlor which covalently binds to liver microsomal proteins. The possibility that the active oxygen participating in the above reaction is the superoxide anion (O2-) or a species generated from O2- was examined with the help of superoxide dismutase (SOD) and with an SOD-mimetic agent, CuDIPS [Cu2+(3,5-diisopropylsalicylic acid)2]. It was observed that, whereas CuDIPS inhibited covalent binding of methoxychlor metabolite(s), SOD did not. However, ZnDIPS [Zn2+(3,5-diisopropylsalicylic acid)2], which exhibits no SOD-mimetic activity, did not inhibit covalent binding. Furthermore, both CuDIPS and ZnDIPS had little or no effect on the formation of demethylated (polar) metabolites of methoxychlor, demonstrating that the inhibition of covalent binding by CuDIPS was not merely due to a general inhibition of the hepatic monooxygenase system. These findings suggested that O2- was involved in covalent binding, but was not accessible to SOD. Additional support for O2- involvement stems from the observation that alpha-tocopheryl acid succinate markedly inhibited covalent binding of methoxychlor. The possibility that hydrogen peroxide (H2O2) was involved in covalent binding of methoxychlor appears unlikely. Catalase had no effect on covalent binding when NADPH was the cofactor, and the use of H2O2 in place of NADPH did not yield covalent binding. Certain scavengers of hydroxyl radical (ethanol, t-butanol and benzoate) inhibited, and other known scavengers (DMSO and mannitol) did not inhibit, covalent binding. EDTA stimulated binding, desferal (desferrioxamine) exhibited no effect on binding, and diethylenetriaminepentaacetic acid (DETAPAC) inhibited binding. A possible explanation for this observation is that the Fe2+ needed for generation of X OH is much more easily obtained from Fe3+-EDTA than from Fe3+-desferal, which resists reduction. The inhibitory effect by DETAPAC may be due to chelation of another metal which is needed for the reaction. Lastly, certain scavengers of singlet oxygen inhibited covalent binding with little effect on the formation of polar metabolites of methoxychlor. In conclusion, these studies support the involvement of X OH and singlet oxygen, possibly derived from O2-, in the formation of the reactive methoxychlor intermediate.(ABSTRACT TRUNCATED AT 400 WORDS)

Benzoates↗
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↗
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↗
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↗
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↗
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↗
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↗
PubMed1989

A dose-response analysis of methoxychlor-induced alterations of reproductive development and function in the rat.

In the present study rats were dosed from weaning, through puberty and gestation, to Day 15 of lactation with methoxychlor at 25, 50, 100, or 200 mg/kg/day. Morphological landmarks of puberty were measured, including the ages at vaginal opening, first estrus, and first estrous cycle in females and at preputial separation in males. In the female, estrous cyclicity, fertility, litter size, number of implantation sites, organ weights, and ovarian and uterine histology were also measured. The viability of the offspring (F1) and their fertility were evaluated using a continuous breeding protocol. Males were necropsied after breeding, the reproductive organs were weighed, and the cauda epididymal sperm counts were determined. One testis was used for histopathology, while the other was used to quantify interstitial fluid (IF) content, IF testosterone concentration, and testicular sperm production. Testosterone and androgen-binding protein were measured in the caput epididymis, and sperm motility and morphology were evaluated from a caudal sample. The serum and pituitary were saved for hormonal determinations. Methoxychlor accelerated the age at vaginal opening and first estrus, and the vaginal smears were cornified. Growth was retarded at 100 and 200 mg/kg/day and fertility was reduced when the females were bred with untreated or similarly treated males. In the highest-dose group, the mated females went from constant estrus into pseudopregnancy following mating, but they had no implants. In males, methoxychlor treatment markedly reduced growth, seminal vesicle weight, cauda epididymal weight, caudal sperm content, and pituitary weight. Puberty was delayed in the two highest-dosage groups. Testicular sperm measures were much less affected than caudal measures. Testis weight and histology were slightly affected, and testicular sperm production, sperm morphology, and motility were unaffected. Endocrine function of the testes and pituitary was altered by methoxychlor administration. Leydig cell testosterone production, in response to human chorionic gonadotropin challenge, was reduced and pituitary levels of prolactin, thyroid-stimulating hormone (TSH), and follicle-stimulating hormone (FSH) were altered. In contrast, serum levels of prolactin, FSH, and luteinizing hormone were unaffected. Serum TSH was reduced by 50% of control at 100 and 200 mg/kg/day, while pituitary levels were increased. Gonadotropin-releasing hormone concentration in the mediobasal hypothalamus was also elevated. In spite of the many reproductive alterations, the fertility of treated males was not reduced when they were mated with untreated females.(ABSTRACT TRUNCATED AT 400 WORDS)

Animals↗
PubMed1991

Protein secretions in mouse uterus after methoxychlor or estradiol exposure.

Four-month-old, ovariectomized mice were treated with 14 daily ip injections of either 10.0 micrograms of 17 beta-estradiol or 1.0 mg technical grade methoxychlor. Uterine luminal proteins were radiolabeled with 35S-methionine and run on 2-dimensional electrophoresis gels. The influence of methoxychlor or estradiol was compared to untreated controls by examining reproductive tract weights, uterine histology, and the patterns of uterine protein secretions. The data indicate that the stimulation of the uterus in ovariectomized, adult mice by methoxychlor is indistinguishable from that caused by estradiol. Both substances alter reproductive tract weights, promote cellular hypertrophy, stimulate uterine development, and induce the secretion of comparable levels of incorporation of methionine into a large number of proteins. The data further indicate that the alterations in gene expression promoted by estradiol in terms of secreted proteins appear to be qualitatively similar to those caused by the pesticide methoxychlor.

Animals↗
PubMed1973

Biomagnification of p, p'-DDT and methoxychlor by bacteria.

Aerobacter aerogenes and Bacillus subtilis accumulated p, p'-DDT and methoxychlor directly from water. Uptake of both (14)C-labeled organochlorine insecticides was rapid; 80 to 90% of the 24-h residues were reached within 30 min. Total cellular residues varied linearly with concentrations of DDT and methoxychlor in water ranging from 0.5 to 5.0 mug/liter. The residue magnification factors from water were between 1,400- to 4,300-fold, but were independent of insecticide concentrations in water. When the insecticide-exposed microbial cells were washed with pesticide-free water, DDT residues were 45% in A. aerogenes and 30% in B. subtilis, whereas the methoxychlor level decreased nearly 75% in both organisms. Subsequent washing did not further reduce the insecticide residue. Autoclave-killed bacteria also rapidly adsorbed DDT and methoxychlor from water and, in some instances, residues were higher than in the living cells. Molecular polarity and lipid solubility appear to influence the retention of the organochlorine insecticides by bacterial cells.

Autoradiography↗