An insecticide. Methoxychlor has estrogenic effects in mammals, among other effects.
Pesticides designed to control insects that are harmful to man. The insects may be directly harmful, as those acting as disease vectors, or indirectly harmful, as destroyers of crops, food products, or textile fabrics.
A highly chlorinated polycyclic hydrocarbon insecticide whose large number of chlorine atoms makes it resistant to degradation. It has been shown to be toxic to mammals and causes abnormal cellular changes in laboratory animals.
Non-steroidal compounds with estrogenic activity.
The removing of alkyl groups from a compound. (From McGraw-Hill Dictionary of Scientific and Technical Terms, 5th ed)
Benzene derivatives that include one or more hydroxyl groups attached to the ring structure.
Steroidal compounds related to ESTRADIOL, the major mammalian female sex hormone. Estradiol congeners include important estradiol precursors in the biosynthetic pathways, metabolites, derivatives, and synthetic steroids with estrogenic activities.
Ductless glands that secrete HORMONES directly into the BLOOD CIRCULATION. These hormones influence the METABOLISM and other functions of cells in the body.
Exogenous agents, synthetic and naturally occurring, which are capable of disrupting the functions of the ENDOCRINE SYSTEM including the maintenance of HOMEOSTASIS and the regulation of developmental processes. Endocrine disruptors are compounds that can mimic HORMONES, or enhance or block the binding of hormones to their receptors, or otherwise lead to activating or inhibiting the endocrine signaling pathways and hormone metabolism.
The family of steroids from which the androgens are derived.
Hydrocarbon compounds with one or more of the hydrogens replaced by CHLORINE.
A family of North American freshwater CATFISHES. It consists of four genera (Ameiurus, Ictalurus, Noturus, Pylodictis,) comprising several species, two of which are eyeless.
Material prepared from plants.
The degeneration and resorption of an OVARIAN FOLLICLE before it reaches maturity and ruptures.
Drug metabolizing enzymes which oxidize methyl ethers. Usually found in liver microsomes.
PLANT EXTRACTS and compounds, primarily ISOFLAVONES, that mimic or modulate endogenous estrogens, usually by binding to ESTROGEN RECEPTORS.
A polychlorinated pesticide that is resistant to destruction by light and oxidation. Its unusual stability has resulted in difficulties in residue removal from water, soil, and foodstuffs. This substance may reasonably be anticipated to be a carcinogen: Fourth Annual Report on Carcinogens (NTP-85-002, 1985). (From Merck Index, 11th ed)
Works containing information articles on subjects in every field of knowledge, usually arranged in alphabetical order, or a similar work limited to a special field or subject. (From The ALA Glossary of Library and Information Science, 1983)
Chlorinated ethanes which are used extensively as industrial solvents. They have been utilized in numerous home-use products including spot remover preparations and inhalant decongestant sprays. These compounds cause central nervous system and cardiovascular depression and are hepatotoxic. Include 1,1,1- and 1,1,2-isomers.
A potent androgenic steroid and major product secreted by the LEYDIG CELLS of the TESTIS. Its production is stimulated by LUTEINIZING HORMONE from the PITUITARY GLAND. In turn, testosterone exerts feedback control of the pituitary LH and FSH secretion. Depending on the tissues, testosterone can be further converted to DIHYDROTESTOSTERONE or ESTRADIOL.
The female reproductive organs. The external organs include the VULVA; BARTHOLIN'S GLANDS; and CLITORIS. The internal organs include the VAGINA; UTERUS; OVARY; and FALLOPIAN TUBES.
Steroid-producing cells in the interstitial tissue of the TESTIS. They are under the regulation of PITUITARY HORMONES; LUTEINIZING HORMONE; or interstitial cell-stimulating hormone. TESTOSTERONE is the major androgen (ANDROGENS) produced.

Effects of endocrine-disrupting contaminants on amphibian oogenesis: methoxychlor inhibits progesterone-induced maturation of Xenopus laevis oocytes in vitro. (1/84)

There is currently little evidence of pollution-induced endocrine dysfunction in amphibia, in spite of widespread concern over global declines in this ecologically diverse group. Data regarding the potential effects of endocrine-disrupting contaminants (EDCs) on reproductive function in amphibia are particularly lacking. We hypothesized that estrogenic EDCs may disrupt progesterone-induced oocyte maturation in the adult amphibian ovary, and tested this with an in vitro germinal vesicle breakdown assay using defolliculated oocytes from the African clawed frog, Xenopus laevis. While a variety of natural and synthetic estrogens and xenoestrogens were inactive in this system, the proestrogenic pesticide methoxychlor was a surprisingly potent inhibitor of progesterone-induced oocyte maturation (median inhibitive concentration, 72 nM). This inhibitory activity was specific to methoxychlor, rather than to its estrogenic contaminants or metabolites, and was not antagonized by the estrogen receptor antagonist ICI 182,780, suggesting that this activity is not estrogenic per se. The inhibitory activity of methoxychlor was dose dependent, reversible, and early acting. However, washout was unable to reverse the effect of short methoxychlor exposure, and methoxychlor did not competitively displace [3H]progesterone from a specific binding site in the oocyte plasma membrane. Therefore, methoxychlor may exert its action not directly at the site of progesterone action, but downstream on early events in maturational signaling, although the precise mechanism of action is unclear. The activity of methoxychlor in this system indicates that xenobiotics may exert endocrine-disrupting effects through interference with progestin-regulated processes and through mechanisms other than receptor antagonism.  (+info)

Monospecific antipeptide antibody to cytochrome P-450 2B6. (2/84)

To study cytochrome P-450 (CYP) 2B6 contribution to methoxychlor metabolism within human liver microsomes and to initiate an investigation of CYP2B6 protein expression, we developed a polyclonal antibody targeted to a 20-residue peptide within that protein. The antibody was found to be highly sensitive and monospecific for CYP2B6 on immunoblots. Although many immunological studies have described the absence or low expression of CYP2B6 in human livers, in the present investigation, we have found this not to be the case. We immunoquantified CYP2B6 apoprotein expression in a panel of 28 livers and found concentrations ranging from 2 to 82 pmol/mg protein, with a mean value of 25 pmol/mg protein. Five livers ( approximately 18%) displayed relatively high levels of CYP2B6 (>40 pmol/mg protein). There were no sex-related differences, although the highest level was observed in a 1-week postpartum donor given several medications. A marked diminution in variability was found in individuals aged 56 or older (n = 12), but there were no age-related trends in mean CYP2B6 content. We suggest that CYP2B6 represents a significant portion of total CYP in human liver. The exquisite sensitivity of this antibody (fmol quantities are detected easily on immunoblots) may explain our detection of CYP2B6 in 100% of livers versus its detection in a limited number of livers by certain other investigators. The antibody also was found to immunoinhibit CYP2B6-catalyzed N-demethylation of (S)-mephenytoin in human liver microsomes by 68 to 79%. The utility of this antibody for determining human liver microsomal CYP2B6 contribution to the ortho-hydroxylation of methoxychlor was demonstrated.  (+info)

Growth stimulation of a rat pituitary cell line MtT/E-2 by environmental estrogens in vitro and in vivo. (3/84)

Endocrine disruptors are a diverse group of chemicals that alter the functions of the endocrine system. A large proportion of endocrine disruptors have estrogenic effects, thus are called environmental estrogens. In the present study, an estrogen (E2) responsive rat pituitary cell line, MtT/E-2, was employed to examine 1) the potency of several endocrine disruptors including bisphenol A (BPA), o,p'-DDD, methoxychlor, 1,2,3,4,5,6-hexachlorocyclohexane (HCH) and dibromoacetic acid (DBAA) in terms of E2 responsive pituitary cell growth; 2) whether BPA has estrogenic action in vivo causing the growth of MtT/E-2 cells grafted in rats. Binding assays showed the test chemicals were able to compete with 3H-E2 binding to the estrogen receptor (ER). The compounds also stimulated growth of MtT/E-2 cells at rates corresponding to their ER binding affinity. Their transcription activation of an (ERE)3-SV40-luciferase reporter in MtT/E-2 cells was comparable to their stimulation of cell growth, with the exception of HCH which showed little induction of cell growth but strong stimulation in ERE dependent transcription activation. MtT/E-2 cells were inoculated into ovariectomized female F344 rats treated with E2 or BPA. The first tumors were noted at day 22 in the E2 treated group, at day 25 in the highest dose of BPA group and at day 41 in the control group. These results suggest 1) that the growth assay with MtT/E-2 cells provides simple and sensitive test for detection of estrogenic activity of environmental chemicals; 2) that BPA has estrogenic potency to stimulate E2 responsive cell growth in vivo as well as in vitro.  (+info)

A metabolite of methoxychlor, 2,2-bis(p-hydroxyphenyl)-1,1, 1-trichloroethane, reduces testosterone biosynthesis in rat leydig cells through suppression of steady-state messenger ribonucleic acid levels of the cholesterol side-chain cleavage enzyme. (4/84)

Postnatal development of Leydig cells involves transformation through three stages: progenitor, immature, and adult Leydig cells. The process of differentiation is accompanied by a progressive increase in the capacity of Leydig cells to produce testosterone (T). T promotes the male phenotype in the prepubertal period and maintains sexual function in adulthood; therefore, disruption of T biosynthesis in Leydig cells can adversely affect male fertility. The present study was designed to evaluate the ability of a xenoestrogen, methoxychlor (the methoxylated isomer of DDT [1,1, 1-trichloro-2,2-bis(p-chlorophenyl)ethane]), to alter Leydig cell steroidogenic function. Purified progenitor, immature, and adult Leydig cells were obtained from, respectively, 21-, 35-, and 90-day-old Sprague-Dawley rats treated with graded concentrations of the biologically active metabolite of methoxychlor, 2, 2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane (HPTE), and assessed for T production. HPTE caused a dose-dependent inhibition of basal and LH-stimulated T production by Leydig cells. Compared to the control value, reduced T production by progenitor and immature Leydig cells was apparent after 10 h of HPTE treatment in culture; the equivalent time for adult Leydig cells was 18 h. The reversibility of HPTE-induced inhibition was evaluated by incubating Leydig cells for 3, 6, 10, 14, or 18 h and measuring T production after allowing time for recovery. After treatment with HPTE for 3 h, T production by immature and adult Leydig cells for the 18-h posttreatment period was similar to the control value, but that of progenitor Leydig cells was significantly lower. The onset of HPTE action and the reversibility of its effect showed that Leydig cells are more sensitive to this compound during pubertal differentiation than in adulthood. T production was comparable when control and HPTE-treated immature Leydig cells were incubated with pregnenolone, progesterone, and androstenedione, but HPTE-treated Leydig cells produced significantly reduced amounts of T when incubations were conducted with 22R-hydroxycholesterol (P < 0.01). This finding suggested that HPTE-induced inhibition of T production is related to a decrease in the activity of cytochrome P450 cholesterol side-chain cleavage enzyme (P450(scc)) and cholesterol utilization. The reduced steady-state mRNA level for P450(scc) in HPTE-treated Leydig cells was demonstrated by reverse transcription-polymerase chain reaction and densitometry. In conclusion, this study showed that HPTE causes a direct inhibition of T biosynthesis by Leydig cells at all stages of development. This effect suggests that reduced T production could be a contributory factor in male infertility associated with methoxychlor and, possibly, other DDT-related compounds.  (+info)

Estrogenic activity of octylphenol, nonylphenol, bisphenol A and methoxychlor in rats. (5/84)

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.  (+info)

Effect of methoxychlor administration to male rats on hepatic, microsomal iodothyronine 5'-deiodinase, form I. (6/84)

We previously reported that methoxychlor administration inhibits the activity of the hepatic, microsomal iodothyronine 5'-deiodinase, form I (ID-I; ). Our data further suggested that the inhibition was due to the covalent binding of a methoxychlor metabolite to a 56-kDa protein identified as ID-I (; ). This protein is 98% homologous to the thiol:protein disulfide oxidoreductase, form Q5 (ERp55;; ). Although at the time there was some controversy, most studies now suggest that ID-I is actually catalyzed by a 27-kDa selenoprotein that does not form adducts with methoxychlor (;; ). Because the 27-kDa protein is considered to be ID-I instead of ERp55, we have further examined the basis for the decreased ID-I activity observed after methoxychlor administration. Male, 150- to 200-g Sprague-Dawley rats were given methoxychlor (0-100 mg/kg/day) in corn oil by gavage for 14 days. ID-I was determined by a thyronine-specific immunoassay. Treated rats showed a significant 15% decline in total hepatic, microsomal protein at all doses. The ID-I-specific activity showed a linear decrease with increasing log doses of methoxychlor. The maximum decrease was 42% at 100 mg/kg/day. The 27-kDa protein specific content declined 37%. In rats given methoxychlor the ratios of the 27-kDa protein mRNA to the 18S ribosomal RNA declined from 2.2 +/- 0.27 x 10(-3) (controls) to 0.99 +/- 0.09 x 10(-3) (100 mg/kg/day). These data suggest that the decreased ID-I observed with chronic methoxychlor administration was due to decreased transcription or stability of the mRNA encoding the 27-kDa protein.  (+info)

Attempted suicide by ingestion of methoxychlor. (7/84)

A rare case involving an attempt to commit suicide by ingestion of a commercially available product containing methoxychlor as the active ingredient is presented. Clinical symptoms exhibited by the patient included no response to stimuli, pale skin, and profuse sweating. A serum sample collected at the time of admission to the hospital was found to contain 0.67 microg/mL of methoxychlor. The determination of methoxychlor was performed using gas chromatography-mass spectrometry.  (+info)

Interaction of methoxychlor and related compounds with estrogen receptor alpha and beta, and androgen receptor: structure-activity studies. (8/84)

We previously demonstrated differential interactions of the methoxychlor metabolite 2,2-bis(p-hydroxyphenyl)-1,1, 1-trichloroethane (HPTE) with estrogen receptor alpha (ERalpha), ERbeta, and the androgen receptor (AR). In this study, we characterize the ERalpha, ERbeta, and AR activity of structurally related methoxychlor metabolites. Human hepatoma cells (HepG2) were transiently transfected with human ERalpha, ERbeta, and AR plus an appropriate steroid-responsive luciferase reporter vector. After transfection, cells were treated with various concentrations of HPTE or structurally related compounds in the presence (for detecting antagonism) and absence (for detecting agonism) of 17beta-estradiol and dihydrotestosterone. The monohydroxy analog of methoxychlor, as well as monohydroxy and dihydroxy analogs of 2, 2-bis(p-hydroxyphenyl)-1,1-dichloroethylene, had ERalpha agonist activity and ERbeta and AR antagonist activity similar to HPTE. The trihydroxy metabolite of methoxychlor displayed only weak ERalpha agonist activity and did not alter ERbeta or AR activities. Replacement of the trichloroethane or dichloroethylene group with a methyl group resulted in a compound with ERalpha and ERbeta agonist activity that retained antiandrogenic activities. This study identifies some of the structural requirements for ERalpha and ERbeta activity and demonstrates the complexity involved in determining the mechanism of action of endocrine-active chemicals that simultaneously act as agonists or antagonists through one or more hormone receptors.  (+info)

Methoxychlor is not typically considered a medical term, but rather a chemical compound. However, I can provide you with a general definition:

Methoxychlor is an organochlorine pesticide that was widely used in the past for agricultural and residential applications due to its relatively low toxicity compared to other organochlorines like DDT. It acts as a contact and stomach insecticide, disrupting the nervous system of insects. Methoxychlor has been banned or restricted in many countries because of environmental concerns and potential health risks.

In a medical context, exposure to methoxychlor might be discussed in relation to possible human health effects, such as endocrine disruption, reproductive issues, or developmental problems. However, it is not a term commonly used by medical professionals in the same way that they would use terms related to specific diseases, symptoms, or treatments.

Insecticides are substances or mixtures of substances intended for preventing, destroying, or mitigating any pest, including insects, arachnids, or other related pests. They can be chemical or biological agents that disrupt the growth, development, or behavior of these organisms, leading to their death or incapacitation. Insecticides are widely used in agriculture, public health, and residential settings for pest control. However, they must be used with caution due to potential risks to non-target organisms and the environment.

Chlordecone is a synthetic chlorinated hydrocarbon insecticide that was widely used in the past for agricultural purposes, particularly in banana plantations. It has been banned in many countries due to its persistence in the environment and its potential negative effects on human health.

Chlordecone is classified as a possible human carcinogen by the International Agency for Research on Cancer (IARC). Exposure to this chemical can occur through contaminated food, water, or air, and it has been linked to various health problems, including neurological effects, endocrine disruption, and an increased risk of certain cancers.

In the medical field, chlordecone exposure is often evaluated in patients who have been exposed to this chemical through environmental contamination or occupational exposure. Medical professionals may use various tests, such as blood or urine tests, to measure the levels of chlordecone in a patient's body and assess any potential health risks.

Non-steroidal estrogens are a class of compounds that exhibit estrogenic activity but do not have a steroid chemical structure. They are often used in hormone replacement therapy and to treat symptoms associated with menopause. Examples of non-steroidal estrogens include:

1. Phytoestrogens: These are plant-derived compounds that have estrogenic activity. They can be found in various foods such as soy, nuts, seeds, and some fruits and vegetables.
2. Selective Estrogen Receptor Modulators (SERMs): These are synthetic compounds that act as estrogen receptor agonists or antagonists, depending on the target tissue. Examples include tamoxifen, raloxifene, and toremifene. They are used in the treatment of breast cancer and osteoporosis.
3. Designer Estrogens: These are synthetic compounds that have been specifically designed to mimic the effects of estrogen. They are often used in research but have not been approved for clinical use.

It is important to note that non-steroidal estrogens can also have side effects and risks, including an increased risk of certain types of cancer, cardiovascular disease, and thromboembolic events. Therefore, their use should be carefully monitored and managed by a healthcare professional.

Dealkylation is a chemical process that involves the removal of an alkyl group from a molecule. In the context of medical and biological sciences, dealkylation often refers to the breakdown of drugs or other xenobiotics (foreign substances) in the body by enzymes.

Dealkylation is one of the major metabolic pathways for the biotransformation of many drugs, including chemotherapeutic agents, opioids, and benzodiazepines. This process can result in the formation of more polar and water-soluble metabolites, which can then be excreted from the body through the urine or bile.

Dealkylation can occur via several mechanisms, including oxidative dealkylation catalyzed by cytochrome P450 enzymes, as well as non-oxidative dealkylation mediated by other enzymes. The specific dealkylation pathway depends on the structure of the substrate and the type of enzyme involved.

Phenols, also known as phenolic acids or phenol derivatives, are a class of chemical compounds consisting of a hydroxyl group (-OH) attached to an aromatic hydrocarbon ring. In the context of medicine and biology, phenols are often referred to as a type of antioxidant that can be found in various foods and plants.

Phenols have the ability to neutralize free radicals, which are unstable molecules that can cause damage to cells and contribute to the development of chronic diseases such as cancer, heart disease, and neurodegenerative disorders. Some common examples of phenolic compounds include gallic acid, caffeic acid, ferulic acid, and ellagic acid, among many others.

Phenols can also have various pharmacological activities, including anti-inflammatory, antimicrobial, and analgesic effects. However, some phenolic compounds can also be toxic or irritating to the body in high concentrations, so their use as therapeutic agents must be carefully monitored and controlled.

Estradiol congeners refer to chemical compounds that are structurally similar to estradiol, which is the most potent and prevalent form of estrogen in humans. Estradiol congeners can be naturally occurring or synthetic and may have similar or different biological activities compared to estradiol.

These compounds can be found in various sources, including plants, animals, and industrial products. Some estradiol congeners are used in pharmaceuticals as hormone replacement therapies, while others are considered environmental pollutants and may have endocrine-disrupting effects on wildlife and humans.

Examples of estradiol congeners include:

1. Estrone (E1): a weak estrogen that is produced in the body from estradiol and is also found in some plants.
2. Estriol (E3): a weaker estrogen that is produced in large quantities during pregnancy.
3. Diethylstilbestrol (DES): a synthetic estrogen that was prescribed to pregnant women from the 1940s to the 1970s to prevent miscarriage, but was later found to have serious health effects on their offspring.
4. Zeranol: a synthetic non-steroidal estrogen used as a growth promoter in livestock.
5. Bisphenol A (BPA): a chemical used in the production of plastics and epoxy resins, which has been shown to have weak estrogenic activity and may disrupt the endocrine system.

Endocrine glands are ductless glands in the human body that release hormones directly into the bloodstream, which then carry the hormones to various tissues and organs in the body. These glands play a crucial role in regulating many of the body's functions, including metabolism, growth and development, tissue function, sexual function, reproduction, sleep, and mood.

Examples of endocrine glands include the pituitary gland, thyroid gland, parathyroid glands, adrenal glands, pineal gland, pancreas, ovaries, and testes. Each of these glands produces specific hormones that have unique effects on various target tissues in the body.

The endocrine system works closely with the nervous system to regulate many bodily functions through a complex network of feedback mechanisms. Disorders of the endocrine system can result in a wide range of symptoms and health problems, including diabetes, thyroid disease, growth disorders, and sexual dysfunction.

Endocrine disruptors are defined as exogenous (external) substances or mixtures that interfere with the way hormones work in the body, leading to negative health effects. They can mimic, block, or alter the normal synthesis, secretion, transport, binding, action, or elimination of natural hormones in the body responsible for maintaining homeostasis, reproduction, development, and/or behavior.

Endocrine disruptors can be found in various sources, including industrial chemicals, pesticides, pharmaceuticals, and personal care products. They have been linked to a range of health problems, such as cancer, reproductive issues, developmental disorders, neurological impairments, and immune system dysfunction.

Examples of endocrine disruptors include bisphenol A (BPA), phthalates, dioxins, polychlorinated biphenyls (PCBs), perfluoroalkyl substances (PFAS), and certain pesticides like dichlorodiphenyltrichloroethane (DDT) and vinclozolin.

It is important to note that endocrine disruptors can have effects at very low doses, and their impact may depend on the timing of exposure, particularly during critical windows of development such as fetal growth and early childhood.

Androstanes are a class of steroidal compounds that have a basic structure consisting of a four-ring core derived from cholesterol. Specifically, androstanes contain a 19-carbon skeleton with a chemical formula of C19H28O or C19H28O2, depending on whether they are alcohols (androgens) or ketones (androstanes), respectively.

The term "androstane" is often used to refer to the parent compound, which has a hydroxyl group (-OH) attached at the C3 position of the steroid nucleus. When this hydroxyl group is replaced by a keto group (-C=O), the resulting compound is called androstane-3,17-dione or simply "androstane."

Androstanes are important precursors in the biosynthesis of various steroid hormones, including testosterone, estrogen, and cortisol. They are also used as intermediates in the synthesis of certain drugs and pharmaceuticals.

Chlorinated hydrocarbons are a group of organic compounds that contain carbon (C), hydrogen (H), and chlorine (Cl) atoms. These chemicals are formed by replacing one or more hydrogen atoms in a hydrocarbon molecule with chlorine atoms. The properties of chlorinated hydrocarbons can vary widely, depending on the number and arrangement of chlorine and hydrogen atoms in the molecule.

Chlorinated hydrocarbons have been widely used in various industrial applications, including as solvents, refrigerants, pesticides, and chemical intermediates. Some well-known examples of chlorinated hydrocarbons are:

1. Methylene chloride (dichloromethane) - a colorless liquid with a mild sweet odor, used as a solvent in various industrial applications, including the production of pharmaceuticals and photographic films.
2. Chloroform - a heavy, volatile, and sweet-smelling liquid, used as an anesthetic in the past but now mainly used in chemical synthesis.
3. Carbon tetrachloride - a colorless, heavy, and nonflammable liquid with a mildly sweet odor, once widely used as a solvent and fire extinguishing agent but now largely phased out due to its ozone-depleting properties.
4. Vinyl chloride - a flammable, colorless gas, used primarily in the production of polyvinyl chloride (PVC) plastic and other synthetic materials.
5. Polychlorinated biphenyls (PCBs) - a group of highly stable and persistent organic compounds that were widely used as coolants and insulating fluids in electrical equipment but are now banned due to their toxicity and environmental persistence.

Exposure to chlorinated hydrocarbons can occur through inhalation, skin contact, or ingestion, depending on the specific compound and its physical state. Some chlorinated hydrocarbons have been linked to various health effects, including liver and kidney damage, neurological disorders, reproductive issues, and cancer. Therefore, proper handling, use, and disposal of these chemicals are essential to minimize potential health risks.

Ictaluridae is not a term that has a medical definition, as it pertains to the field of biology and zoology rather than medicine. Ictaluridae is the family of freshwater fishes commonly known as "North American catfishes." These fishes are characterized by their barbels, which resemble cats' whiskers, and their armored bodies.

However, in a medical context, certain types of Ictaluridae may be mentioned in relation to food safety or allergies. For example, if a patient has an allergy to fish, they may need to avoid consuming Ictaluridae species such as channel catfish or blue catfish. Similarly, if there is a concern about foodborne illness, certain types of Ictaluridae may be implicated in outbreaks of diseases such as scombrotoxin poisoning.

Therefore, while "Ictaluridae" itself does not have a medical definition, it is a term that may be used in medicine in relation to food safety or allergies.

"Plant preparations" is not a term with a specific medical definition in the field of medicine or pharmacology. However, it is commonly used to refer to various forms of plant material that have been prepared for medicinal use. This can include dried and powdered plant parts, such as leaves, roots, or flowers, as well as extracts or concentrates made from plants. These preparations may be used in traditional medicine or as the basis for modern pharmaceuticals. It is important to note that the safety, effectiveness, and quality of plant preparations can vary widely, and they should only be used under the guidance of a qualified healthcare provider.

Follicular atresia is a physiological process that occurs in the ovary, where follicles (fluid-filled sacs containing immature eggs or oocytes) undergo degeneration and disappearance. This process begins after the primordial follicle stage and continues throughout a woman's reproductive years. At birth, a female has approximately 1 to 2 million primordial follicles, but only about 400 of these will mature and release an egg during her lifetime. The rest undergo atresia, which is a natural process that helps regulate the number of available eggs and maintain hormonal balance within the body.

The exact mechanisms that trigger follicular atresia are not fully understood, but it is believed to be influenced by various factors such as hormonal imbalances, oxidative stress, and apoptosis (programmed cell death). In some cases, accelerated or excessive follicular atresia can lead to infertility or early menopause.

Oxidoreductases, O-demethylating are enzymes that belong to the larger family of oxidoreductases. Specifically, they are involved in catalyzing the removal of methyl groups (-CH3) from various substrates through oxidation reactions. This process is known as O-demethylation.

These enzymes play a crucial role in the metabolism of xenobiotics (foreign substances) such as drugs, toxins, and carcinogens. They help convert these substances into more water-soluble forms, which can then be easily excreted from the body. O-demethylating oxidoreductases are often found in the liver, where they contribute to the detoxification of xenobiotics.

The reaction catalyzed by these enzymes involves the transfer of a hydrogen atom and the addition of an oxygen atom to the methyl group, resulting in the formation of formaldehyde (-CH2O) and a demethylated product. The cytochrome P450 family of enzymes is one example of O-demethylating oxidoreductases.

Phytoestrogens are compounds found in plants that have estrogen-like properties. They can bind to and activate or inhibit the action of estrogen receptors in the body, depending on their structure and concentration. Phytoestrogens are present in a variety of foods, including soy products, nuts, seeds, fruits, and vegetables.

Phytoestrogens have been studied for their potential health benefits, such as reducing the risk of hormone-dependent cancers (e.g., breast cancer), improving menopausal symptoms, and promoting bone health. However, their effects on human health are complex and not fully understood, and some studies suggest that high intake of phytoestrogens may have adverse effects in certain populations or under specific conditions.

It is important to note that while phytoestrogens can mimic the effects of estrogen in the body, they are generally weaker than endogenous estrogens produced by the human body. Therefore, their impact on hormonal balance and health outcomes may vary depending on individual factors such as age, sex, hormonal status, and overall diet.

DDT (dichlorodiphenyltrichloroethane) is a synthetic insecticide that was widely used in the mid-20th century to control agricultural pests and vector-borne diseases such as malaria. It belongs to a class of chemicals called organochlorines, which are known for their persistence in the environment and potential for bioaccumulation in the food chain.

DDT was first synthesized in 1874, but its insecticidal properties were not discovered until 1939. Its use as an insecticide became widespread during World War II, when it was used to control typhus and malaria-carrying lice and mosquitoes among troops. After the war, DDT was widely adopted for agricultural and public health purposes.

However, concerns about the environmental and human health effects of DDT led to its ban or severe restriction in many countries starting in the 1970s. The United States banned the use of DDT for most purposes in 1972, and the Stockholm Convention on Persistent Organic Pollutants (POPs) prohibited its production and use globally in 2004, except in cases where there is a risk of vector-borne diseases.

DDT has been linked to several health problems, including reproductive effects, developmental toxicity, neurotoxicity, and endocrine disruption. It is also highly persistent in the environment, with a half-life of up to 15 years in soil and up to 30 years in water. This means that DDT can accumulate in the food chain, posing risks to wildlife and humans who consume contaminated food or water.

In summary, DDT is a synthetic insecticide that was widely used in the mid-20th century but has been banned or restricted in many countries due to its environmental and health effects. It belongs to a class of chemicals called organochlorines, which are known for their persistence in the environment and potential for bioaccumulation in the food chain. DDT has been linked to several health problems, including reproductive effects, developmental toxicity, neurotoxicity, and endocrine disruption.

An encyclopedia is a comprehensive reference work containing articles on various topics, usually arranged in alphabetical order. In the context of medicine, a medical encyclopedia is a collection of articles that provide information about a wide range of medical topics, including diseases and conditions, treatments, tests, procedures, and anatomy and physiology. Medical encyclopedias may be published in print or electronic formats and are often used as a starting point for researching medical topics. They can provide reliable and accurate information on medical subjects, making them useful resources for healthcare professionals, students, and patients alike. Some well-known examples of medical encyclopedias include the Merck Manual and the Stedman's Medical Dictionary.

Trichloroethanes are not a medical term, but rather a group of chemical compounds that include 1,1,1-trichloroethane and 1,1,2-trichloroethane. These chemicals have been used as solvents, degreasing agents, and refrigerants.

1,1,1-Trichloroethane, also known as methyl chloroform, is a colorless liquid with a sweet, mild odor. It has been used as a solvent for cleaning electronic components, removing adhesives, and degreasing metals. It can also be found in some consumer products such as spray paints, aerosol cleaners, and spot removers.

1,1,2-Trichloroethane, also known as aerothane, is a colorless liquid with a mild sweet odor. It has been used as a solvent for cleaning and degreasing metals, plastics, and other surfaces. It can also be found in some consumer products such as typewriter correction fluids and spot removers.

Exposure to trichloroethanes can occur through inhalation, skin contact, or ingestion. Short-term exposure to high levels of these chemicals can cause irritation of the eyes, nose, throat, and lungs, dizziness, headache, and nausea. Long-term exposure to lower levels can lead to liver and kidney damage, neurological effects, and an increased risk of cancer.

It is important to handle trichloroethanes with care and follow proper safety precautions, including using appropriate personal protective equipment (PPE) such as gloves, goggles, and respirators, and ensuring adequate ventilation in the work area.

Testosterone is a steroid hormone that belongs to androsten class of hormones. It is primarily secreted by the Leydig cells in the testes of males and, to a lesser extent, by the ovaries and adrenal glands in females. Testosterone is the main male sex hormone and anabolic steroid. It plays a key role in the development of masculine characteristics, such as body hair and muscle mass, and contributes to bone density, fat distribution, red cell production, and sex drive. In females, testosterone contributes to sexual desire and bone health. Testosterone is synthesized from cholesterol and its production is regulated by luteinizing hormone (LH) and follicle-stimulating hormone (FSH).

Female genitalia refer to the reproductive and sexual organs located in the female pelvic region. They are primarily involved in reproduction, menstruation, and sexual activity. The external female genitalia, also known as the vulva, include the mons pubis, labia majora, labia minora, clitoris, and the external openings of the urethra and vagina. The internal female genitalia consist of the vagina, cervix, uterus, fallopian tubes, and ovaries. These structures work together to facilitate menstruation, fertilization, pregnancy, and childbirth.

Leydig cells, also known as interstitial cells of Leydig or interstitial cell-stroma, are cells in the testes that produce and release testosterone and other androgens into the bloodstream. They are located in the seminiferous tubules of the testis, near the blood vessels, and are named after Franz Leydig, the German physiologist who discovered them in 1850.

Leydig cells contain cholesterol esters, which serve as precursors for the synthesis of testosterone. They respond to luteinizing hormone (LH) released by the anterior pituitary gland, which stimulates the production and release of testosterone. Testosterone is essential for the development and maintenance of male secondary sexual characteristics, such as facial hair, deep voice, and muscle mass. It also plays a role in sperm production and bone density.

In addition to their endocrine function, Leydig cells have been shown to have non-hormonal functions, including phagocytosis, antigen presentation, and immune regulation. However, these functions are not as well understood as their hormonal roles.

No FAQ available that match "methoxychlor"

No images available that match "methoxychlor"