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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

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

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

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

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

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

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

Rapid preparation of micro sample and gas-liquid chromatographic determination of methoxychlor residues in animal tissues and water.

Methods are described for analyses of methoxychlor (2,2-bis(p-methoxyphenyl)-1,1,1-trichloroethane) in tissues of fish and invertebrate animals and in water samples. These micro methods offer economy in solvents and materials, and reduce health and fire hazards. Furthermore, the methods sufficiently reduce sample weights to allow analyses of small animals (mayflies) or animal organs. Samples are extracted in a ball-mill with n-hexane, and lipids are removed from fatty samples by freezeout. Small Florisil columns give final lipid cleanup and partial separation of methoxychlor from interfering materials. Methoxychlor is determined on a short gas-liquid chromatographic column (retention time 2.2 min). Animal tissue samples as small as 0.1 g and water samples of 5 ml can be analyzed at sensitivities of 10 and 1 ppb, respectively. Methoxychlor recoveries were 84-101% (fish and crab tissue), 92-100% (cod liver oil), and 98-107% (water) over a concentration range of 0.-10 ppm. Results obtained for fish tissue by using micro procedures agreed to within 20% of results reported by an independent laboratory using an established method.

Animals

Collaborative study of a method for the analysis of dry methoxychlor formulations.

A collaborative study has been completed on a method for determining methoxychlor content in dry formulations. The method is based on a total halogen determination plus a selective, qualitative thin lay chromatographic (TLC) measurement to establish the p,p'-methoxychlor is the primary halogen-containing organic species present in the formulation. After extraction of the sample with toluene, the toluene solution of methoxychlor is treated with sodium biphenyl to convert all halogen to the halide. The halide is then extracted with a solution of nitric acid and titrated with silver nitrate according to the Volhard procedure or potentiometrically, using a pH meter assembly. Based on the results obtained from 7 collaborators, the standard deviation of the method is about 0.48% at the 50% level. The qualitative TLC measurement is made on an aliquot of the initial toluene extract, using a selective halogen detection system. The method has been adopted as official first action.

Chromatography, Thin Layer

Photochemical transformation of the DDT and methoxychlor degradation products, DDE and DMDE, by sunlight.

DDE and DMDE, degradation products of the pesticides DDT and methoxychlor, rapidly undergo an unusual photoisomerization in solution when exposed to sunlight. The isomerization involves the exchange of a vinyl chlorine and an ortho aromatic hydrogen. Other photoproducts identified were corresponding benzophenones and 1,1-diaryl-2-chloroethylenes. Quantum yields for the reactions were measured and then used to compute sunlight photolysis half-lives for DMDE and DDE. Although both compounds absorb only the short-wavelength ultraviolet component of sunlight, their photolysis was found to be surprisingly rapid. During summer at latitude 40 degrees N, the photolysis half-lives near the surface of a water body are one hour and one day for dissolved DMDE and DDE, respectively. Photolysis of the DDE photoisomers is about an order of magnitude slower than that of DDE, suggesting that they may accumulate under environmental conditions. The DDE photoisomers photocyclize to form chlorinated dibenzofulvene and dichlorofluorenone. Neither DDE nor its photoisomers photoreact in solution to form PCB's. The environmental significance of these results is discussed, and its is suggested that the persistence of DDE in inland surface waters may be related to its tendency to sorb onto sediments and biota where not light is present.

Dichlorodiphenyl Dichloroethylene

Mutagenicity and purative carcinogenicity tests of several polycyclic aromatic compounds associated with impurities of the insecticide methoxychlor.

Several polycyclic hydrocarbons, 3,6-dimethoxy-9,10-bis(p-methoxyphenyl)-phenathrene, tetrakis(p-methoxyphenylyethylene and 3,6,11,14-tetramethoxydibenzo(g,p)chrysene, which are associated as impurities in commerical samples of the insecticide methoxychlor, have been tested in the Ames mutagenicity test with strains of Salmonella thyphimurium, TA 1535, TA 1537, TA 1538, and TA 98. Activation by liver microsomes induced with either phenobarbitol or Aroclor was examined. The only active compound was 3,6,11,14-tetramethoxydibenzo(g,p)chrysene, mutagenic (0.39 revertants/nmol) tostrain TA 98.

Chrysenes

Effects of methoxychlor on the reproductive system of the adult female mouse. 1. Gross and histologic observations.

The purpose of this study is to examine the effects of the pesticide methoxychlor (MXC) on the reproductive system of the adult female mouse. Sexually mature (7- to 8-week) virgin female CD-1 mice were exposed to 1.25, 2.5, or 5.0 mg MXC (50% technical grade) via oral gavage for 5 consecutive days each week for either 2 or 4 weeks. Control groups received either 0.025 mg estradiol-17 beta (E-17 beta) or the sesame oil vehicle for the same time period. Vaginal smears were taken daily, and weights were recorded weekly. Twenty-four hours following the final exposure, animals were sacrificed. Ovaries and reproductive tracts were removed and weighed. One ovary from each animal was prepared for light microscopic evaluation. Results revealed a dose dependency of MXC in inducing persistent vaginal estrus (PVE). Ovaries of MXC-exposed and E-17 beta-exposed animals weighed significantly less than the sesame oil controls. In addition, there was an increase in the number of atretic large follicles in the E-17 beta group and in those mice treated with the two highest doses of MXC, indicating a potential reduction in the immediate fertility of the animal. Thus, this commonly employed pesticide appears to mimic closely those effects on the female reproductive system induced by estrogens.

Animals

Effects of methoxychlor treatment of pregnant mice on female offspring of the treated and subsequent pregnancies.

This study was designed to assess whether exposure to the estrogenic pesticide methoxychlor (MXC) during pregnancy would affect reproductive parameters not only in female offspring exposed prenatally, but also in those of a subsequent litter. Mice were exposed via oral gavage to 7.5, 5.0, or 2.5 mg technical grade MXC (50%) or 0.025 mg estradiol-17 beta (E-17 beta) from days 6 to 15 of pregnancy. Following delivery, female offspring (F1a) were cross-fostered and sacrificed at 8 weeks of age. Mothers exposed during their first pregnancy were allowed to mate again and their second set of offspring (F1b) were similarly evaluated to detect any latent effects from the initial exposure. Mice exposed to 7.5 mg MXC were unable to carry their litters to term. Results revealed a significant increase in the length of gestation of mice exposed to both E-17 beta and 5.0 mg MXC. A larger percentage of atretic follicles appeared in the ovaries of F1a females exposed prenatally to 5.0 mg MXC when compared to controls. Females from the F1b litter displayed a significant advance in time of vaginal opening, an apparent residual effect of MXC from a mother exposed during a previous pregnancy.

Abnormalities, Drug-Induced

Effects of methoxychlor on the reproductive system of the adult female mouse: 2. Ultrastructural observations.

The purpose of this study is to examine the effects of the pesticide methoxychlor (MXC) on the ultrastructural appearance of the different cellular components of the mouse ovary. Sexually mature (7- to 8-week) virgin female CD-1 mice were exposed to 5.0 mg MXC (50% technical grade) via oral gavage for 5 consecutive days each week for 4 weeks. Control groups received either 0.025 mg estradiol-17 beta (E-17 beta) or the sesame oil vehicle for the same time period. Twenty-four hours following the final exposure, animals were sacrificed. Ultrastructural observations revealed increased lipid accumulation in interstitial cells and theca cells of both estradiol-treated and 5.0 mg MXC-treated mice. This would suggest that these cells are unable to synthesize and secrete steroids. Thus, this commonly employed pesticide appears to closely mimic those effects on the female ovary induced by estrogen.

Animals