Abnormal Levels of Serum Dehydroepiandrosterone, Estrone
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Antiestrogenic Action of Dihydrotestosterone in Mouse Breast
Antiestrogenic action of dihydrotestosterone in mouse breast. Competition with estradiol for binding to the estrogen receptor. R W Casey, J D Wilson J Clin Invest. 1984;74(6):2272-2278. https://doi.org/10.1172/JCI111654. Research Article Feminization in men occurs when the effective ratio of androgen to estrogen is lowered. Since sufficient estrogen is produced in normal men to induce breast enlargement in the absence of adequate amounts of circulating androgens, it has been generally assumed that androgens exert an antiestrogenic action to prevent feminization in normal men. We examined the mechanisms of this effect of androgens in the mouse breast. Administration of estradiol via silastic implants to castrated virgin CBA/J female mice results in a doubling in dry weight and DNA content of the breast. The effect of estradiol can be inhibited by implantation of 17 beta-hydroxy-5 alpha-androstan-3-one (dihydrotestosterone), whereas dihydrotestosterone alone had no effect on breast growth. Estradiol administration also enhances the level of progesterone receptor in mouse breast. Within 4 d of castration, the progesterone receptor virtually disappears and estradiol treatment causes a twofold increase above the level in intact animals. Dihydrotestosterone does not compete for binding to the progesterone receptor, but it does inhibit estrogen-mediated increases of progesterone receptor content of breast tissue cytosol from both control mice and mice with X-linked testicular feminization (tfm)/Y. Since tfm/Y mice lack a functional androgen receptor, we conclude that this antiestrogenic action of androgen is not mediated by the androgen receptor. Dihydrotestosterone competes with estradiol for binding to the cytosolic estrogen receptor of mouse breast, […] Find the latest version: https://jci.me/111654/pdf Antiestrogenic Action of Dihydrotestosterone in Mouse Breast Competition with Estradiol for Binding to the Estrogen Receptor Richard W. -
Degradation and Metabolite Formation of Estrogen Conjugates in an Agricultural Soil
Journal of Pharmaceutical and Biomedical Analysis 145 (2017) 634–640 Contents lists available at ScienceDirect Journal of Pharmaceutical and Biomedical Analysis j ournal homepage: www.elsevier.com/locate/jpba Degradation and metabolite formation of estrogen conjugates in an agricultural soil a,b b,∗ Li Ma , Scott R. Yates a Department of Environmental Sciences, University of California, Riverside, CA 92521, United States b Contaminant Fate and Transport Unit, U.S. Salinity Laboratory, Agricultural Research Service, United States Department of Agriculture, Riverside, CA 92507, United States a r t i c l e i n f o a b s t r a c t Article history: Estrogen conjugates are precursors of free estrogens such as 17ß-estradiol (E2) and estrone (E1), which Received 10 April 2017 cause potent endocrine disrupting effects on aquatic organisms. In this study, microcosm laboratory Received in revised form 11 July 2017 ◦ experiments were conducted at 25 C in an agricultural soil to investigate the aerobic degradation and Accepted 31 July 2017 metabolite formation kinetics of 17ß-estradiol-3-glucuronide (E2-3G) and 17ß-estradiol-3-sulfate (E2- Available online 1 August 2017 3S). The aerobic degradation of E2-3G and E2-3S followed first-order kinetics and the degradation rates were inversely related to their initial concentrations. The degradation of E2-3G and E2-3S was extraordi- Keywords: narily rapid with half of mass lost within hours. Considerable quantities of E2-3G (7.68 ng/g) and E2-3S Aerobic degradation 17ß-estradiol-3-glucuronide (4.84 ng/g) were detected at the end of the 20-d experiment, particularly for high initial concentrations. -
Total Estradiol and Total Testosterone
Laboratory Procedure Manual Analyte: Total Estradiol and Total Testosterone Matrix: Serum Method: Simultaneous Measurement of Estradiol and Testosterone in Human Serum by ID LC-MS/MS Method No: 1033 Revised: as performed by: Clinical Chemistry Branch Division of Laboratory Sciences National Center for Environmental Health contact: Dr. Hubert W. Vesper Phone: 770-488-4191 Fax: 404-638-5393 Email: [email protected] James Pirkle, M.D., Ph.D. Division of Laboratory Sciences Important Information for Users CDC periodically refines these laboratory methods. It is the responsibility of the user to contact the person listed on the title page of each write-up before using the analytical method to find out whether any changes have been made and what revisions, if any, have been incorporated. Total Estradiol and Total Testosterone NHANES 2015-16 Public Release Data Set Information This document details the Lab Protocol for testing the items listed in the following table for SAS file TST_I: VARIABLE NAME SAS LABEL (and SI units) LBXTST Testosterone, total (nmol/L) LBXEST Estradiol (pg/mL) 1 of 49 Total Estradiol and Total Testosterone NHANES 2015-16 Contents 1 Summary of Test Principle and Clinical Relevance 7 1.1 Intended Use 7 1.2 Clinical and Public Health Relevance 7 1.3 Test Principle 8 2 Safety Precautions 10 2.1 General Safety 10 2.2 Chemical Hazards 10 2.3 Radioactive Hazards 11 2.4 Mechanical Hazards 11 2.5 Waste Disposal 11 2.6 Training 11 3 Computerization and Data-System Management 13 3.1 Software and Knowledge Requirements 13 3.2 Sample Information 13 3.3 Data Maintenance 13 3.4 Information Security 13 4 Preparation for Reagents, Calibration Materials, Control Materials, and All Other Materials; Equipment and Instrumentation. -
Feminizing Gender-Affirming Hormone Care the Michigan Medicine Approach
Feminizing Gender-Affirming Hormone Care The Michigan Medicine Approach Our goal is to partner with you to provide the medical care you need in affirming your gender. Our focus is on your lifelong health, safety, and individual medical and transition-related needs. The Michigan Medicine approach is based on the limited but growing medical evidence surrounding gender-affirming hormone care. Based on the available science, we believe mimicking normal physiology will provide you with the best balance of physical and emotional changes and long-term health. This philosophy aligns with current national and international medical guidelines in the care of gender diverse people. We are committed to staying up-to-date with the latest research and medical evidence to ensure you are getting the highest quality care. We know that there are competing approaches to gender-affirming care that are not based on validated scientific evidence. These approaches make scientifically unsubstantiated claims and have unknown short and long-term risks. We are happy to discuss these with you. Below are some answers to questions our patients have asked us about gender- affirming hormone care. We hope the Q&A will help you understand the medical evidence behind our approach to your gender-affirming hormone care, and how it may differ from other approaches, including the approach other well-known clinics in Southeast Michigan. Is there a benefit for monitoring both estrone (E1) and estradiol (E2) levels and aiming for a particular ratio? There are 3 naturally occurring human estrogens: estrone (E1), estradiol (E2), and estriol (E3). Your body naturally balances your estradiol and estrone ratio. -
Hormonal and Immunological Aspects of the Phylogeny of Sex Steroid
Proc. Nati. Acad. Sci. USA Vol. 77, No. 8, pp. 4578-4582, August 1980 Biochemistry Hormonal and immunological aspects of the phylogeny of sex steroid binding plasma protein (estradiol/dihydrotestosterone/a-fetoprotein) JACK-MICHEL RENOIR, CHRISTINE MERCIER-BODARD, AND ETIENNE-EMILE BAULIEU Unite de Recherches sur le Metabolisme Mol6culaire et la Physiopathologie des St6roides de l'Institut National de la Sante et de la Recherche MWdicale, (U 33), Universite Paris-Sud, DMpartement de Chimie Biologique, 78 rue du GUn6ral Leclerc, 94270 Bicetre, France Communicated by Seymour Lieberman, May 5,1980 ABSTRACT Sex steroid binding plasma protein (Sbp) in man acetate, 1:1 (vol/vol) for estradiol. Nonradioactive steroids were and in monkeys binds the androgens dihydrotestosterone and a gift of Roussel-Uclaf (Romainville) (guaranteed 99% testosterone and the estrogen estradiol with high affinity (Kd tO.5, 1, and 2 nM, respectively). Detailed studies of steroid pure). binding specificity give the same results in all primates, except Chemicals and Animals. Tubing [Visking-Nojax, 8/32 in. that in humans and chimpanzees estrone does not compete for (6.4 mm); from Union Carbide Corporation, New York] was dihydrotestosterone binding. In other mammals, Sbps of Arti- used in equilibrium dialyses. Agarose (Indubiose A 37) was odactyla and Lagomorpha have the same range of affinities for purchased from l'Industrie Biologique Francgaise (Paris), Ul- androgens but they do not bind estradiol to any significant ex- trogel AcA 34 was from LKB (Uppsala, Sweden), and Freund's tent (Kd >280 nM). The dog has an unusual Sbp (Kd for dihy- drotestosterone, 7.1 nM; for estiadiol, 125 nM), and rodents do complete and incomplete adjuvants were from Difco. -
Different Levels of Estradiol Are Correlated with Sexual Dysfunction in Adult
www.nature.com/scientificreports OPEN Diferent levels of estradiol are correlated with sexual dysfunction in adult men Tong Chen1,2,3,5, Fei Wu1,4,5, Xianlong Wang2, Gang Ma2, Xujun Xuan2, Rong Tang2, Sentai Ding1 & Jiaju Lu1,2* Ejaculatory dysfunction, including premature ejaculation (PE) and delayed ejaculation (DE), as well as erectile dysfunction (ED), constitute the majority of male sexual dysfunction. Despite a fair amount of data on the role of hormones and erection and ejaculation, it is inconclusive due to controversy in the current literature. To explore the correlation of male sexual dysfunction with hormonal profle, 1,076 men between the ages of 19–60 years (mean: 32.12 years) were included in this retrospective case–control study; 507 were categorized as ED, PE and DE groups. Five hundred and sixty-nine men without sexual dysfunction were enrolled in the control group. The background characteristics and clinical features of the four groups were collected and analyzed. The estradiol value was signifcantly elevated in the ED group than the control group (109.44 ± 47.14 pmol/L vs. 91.88 ± 27.68 pmol/L; P < 0.001). Conversely, the DE group had signifcantly lower level of estradiol than control did (70.76 ± 27.20 pmol/L vs. 91.88 ± 27.68 pmol/L; P < 0.001). The PE group had similar level of estradiol (91.73 ± 31.57 pmol/L vs. 91.88 ± 27.68 pmol/L; P = 0.960) but signifcantly higher level of testosterone (17.23 ± 5.72 nmol/L vs. 15.31 ± 4.31 nmol/L; P < 0.001) compared with the control group. -
Label Extension of HERS, HERS II
Depo®-Estradiol Estradiol cypionate injection, USP WARNINGS: ESTROGENS INCREASE THE RISK OF ENDOMETRIAL CANCER. Close clinical surveillance of all women taking estrogens is important. Adequate diagnostic measures including endometrial sampling when indicated, should be undertaken to rule out malignancy in all cases of undiagnosed persistent or recurring abnormal vaginal bleeding. There is currently no evidence that the use of “natural” estrogens result in a different endometrial risk profile than “synthetic” estrogens at equivalent estrogen doses. (See WARNINGS, malignant neoplasms, Endometrial cancer.) CARDIOVASCULAR AND OTHER RISKS Estrogens with and without progestins should not be used for the prevention of cardiovascular disease. (See WARNINGS, Cardiovascular disorders.) The Women’s Health Initiative (WHI) study reported increased risks of myocardial infarction, stroke, invasive breast cancer, pulmonary emboli, and deep vein thrombosis in postmenopausal women (50 to 79 years of age) during 5 years of treatment with oral conjugated estrogens (CE 0.625 mg) combined with medroxyprogesterone acetate (MPA 2.5 mg) relative to placebo. (see CLINICAL PHARMACOLOGY, Clinical Studies.) The Women’s Health Initiative Memory Study (WHIMS), a substudy of WHI, reported increased risk of developing probable dementia in postmenopausal women 65 years of age or older during 4 years of treatment with oral conjugated estrogens plus medroxyprogesterone acetate relative to placebo. It is unknown whether this finding applies to younger postmenopausal women or to women taking estrogen alone therapy. (See CLINICAL PHARMACOLOGY, Clinical Studies.) Other doses of conjugated estrogens with medroxyprogesterone acetate, and other combinations and dosage forms of estrogens and progestins were not studied in the WHI clinical trials and, in the absence of comparable data, these risks should be assumed to be similar. -
Other Data Relevant to an Evaluation of Carcinogenicity and Its Mechanisms
COMBINED ESTROGEN−PROTESTOGEN MENOPAUSAL THERAPY 263 4. Other Data Relevant to an Evaluation of Carcinogenicity and its Mechanisms 4.1 Absorption, distribution, metabolism and excretion The distribution of progestogens is described in the monograph on Combined estro- gen–progestogen contraceptives. That of estrogens is described below. 4.1.1 Humans Little more has been discovered about the absorption and distribution of estrone, estradiol and estriol products and conjugated equine estrogens in humans since the previous evaluation (IARC, 1999). Greater progress has been made in the identification and characterization of the enzymes that are involved in estrogen metabolism and excre- tion. The various metabolites and the responsible enzymes, including genotypic varia- tions, are described below (see Figures 3 and 4). Sulfation and glucuronidation are the main metabolic reactions of estrogens in humans. (a) Metabolites (i) Estrogen sulfates Several members of the sulfotransferase (SULT) gene family can sulfate hydroxy- steroids, including estrogens. The importance of SULTs in estrogen conjugation is demons- trated by the observation that a major component of circulating estrogen is sulfated, i.e. estrone sulfate (reviewed by Pasqualini, 2004). In addition to the parent hormones, estrone and estradiol, SULTs can also conjugate their respective catechols and also methoxyestro- gens (Spink et al., 2000; Adjei & Weinshilboum, 2002). The resulting sulfated metabolites are more hydrophilic and can be excreted. In postmenopausal breast cancers, levels of estrone sulfate can reach 3.3 ± 1.9 pmol/g tissue, which is five to nine times higher than the corresponding plasma concentration (equating gram of tissue with millilitre of plasma) (Pasqualini et al., 1996). In contrast, levels of estrone sulfate in premenopausal breast tumours are two to four times lower than those in plasma. -
Estrone Screening Profile Estrone Is a Contaminant That Has Been Detected in Minnesota Waters
CONTAMINANTS OF EMERGING CONCERN PROGRAM Estrone Screening Profile Estrone is a contaminant that has been detected in Minnesota waters. The information in this profile was collected for the screening process of the Minnesota Department of Health’s Contaminants of Emerging Concern (CEC) program in November 2011. The chemicals nominated to the CEC program are screened and ranked based on their toxicity and presence in Minnesota waters. Based on these rankings, some chemicals are selected for a full review. CEC program staff have not selected estrone for a full review. Estrone Uses Potential Health Effects Estrone is a hormone produced naturally in humans Adverse health effects from prescribed doses of and animals. Estrone is a component of some estrone can include cancer, cardiovascular effects, medications used for the treatment of menopausal stroke, dementia, and others.5 Drinking water and premenopausal symptoms. Estrone is produced contaminated with low levels of estrone is not likely to naturally by men and women, but women produce pose a health risk. much higher levels than men. It is the most abundant Based on the screening assessment, a full review of natural estrogen produced by postmenopausal estrone may be possible; however, it is ranked lower women. The placenta also produces estrogens, than other nominated CEC chemicals at this time. including estrone, during pregnancy. References Estrone in the Environment 1. Ying G, Kookana RS, Ru YJ.2002. Occurrence and fate of Estrone enters the environment when it is excreted hormone steroids in the environment. Env Intl; 28:545. from humans and animals. The spreading of poultry http://www.lu.lv/ecotox/publikacijas-3-kursa- and cattle waste on agricultural land increases the risk studentiem/Steroid_hormones_EI.pdf 2. -
The Truth About Bioidentical Hormone Therapy
MENOPAUSE MATTERS from The Truth About Bioidentical www.menopause.org Hormone Therapy JoAnn V. Pinkerton, MD, NCMP Confusion and unsubstantiated claims surround the custom- compounded bioidentical hormone therapy products used to treat menopausal symptoms, such as hot fl ashes. This review attempts to dispel some of the confusion. What Is Bioidentical implants, suppositories). Some of the Hormone Therapy? hormones used are not government ap- Bioidentical hormone therapy (BHT) proved (estriol) or monitored, and some- refers to exogenous hormones that are times the compounded therapies con- biochemically similar to those pro- tain nonhormonal ingredients (eg, dyes, duced endogenously by the ovaries or preservatives) that some women cannot elsewhere in the body.1 They are gener- tolerate.4 In addition, compounders do ally derived from soy and yams, but the not have to: plant product needs to be chemically al- ◾ Test for effi cacy or safety. tered to become a therapeutic agent for ◾ Provide product information about humans (eg, estrone, estradiol, estriol, proven benefi ts and risks. progesterone, and testosterone).2 Claims ◾ Give proof of batch and dose standard- by compounding pharmacies that BHT ization or purity. is “natural” and “identical” to the hor- By way of comparison, there are mones made in the body are not true.3 17β-estradiol and progesterone products Custom-made HT formulations that are that have been well tested and are regu- compounded for an individual woman larly inspected. Estradiol is available in according to a health care provider’s oral, patch, gel, ring, lotion, and mist prescription are not subject to govern- formulations. Micronized progesterone ment regulations or tested for safety. -
Reproductive Estrone Sulfate
Reproductive Estrone sulfate Analyte Information - 1 - Estrone sulfate Introduction Estrone sulfate (E1-S) is a sulfate derivative of estrone, and is the most abundant form of circulating estrogens in both men and non-pregnant women1,2. It is the aromatized C18-steroid with a 3-sulfate group and a 17-ketone. Its chemical name is 1,3,5 (10)-estradien-3-ol-17-one-3-sulfate, its summary formula is C18H22O5S, and its molecular weight is 350.4 Da. Fig.1: Structural formula of estrone sulfate Biosynthesis Estrone sulfate is the major metabolite of both estradiol and estrone 2,3. Formation of estrone sulfate occurs in various tissues in the body, but primarily in the liver. The reaction requires hydroxysteroid sulfotransferase activity and sulfate ions in the form of an active sulfate, namely phosphoadenosine phosphosulfate (PAPS) (4). Metabolism Estrone sulfate is hydrolyzed to estrone and then converted to various conjugates via sulfonation, glucuronidation and O-methylation. The main site of degradation is the liver, but these reactions may also take place in estrogen target tissues such as the breast, ovary and uterus. The conjugated forms are finally excreted in urine. Estrone sulfate may also be excreted in urine directly. The direct excretion rate is slow compared to that of the conjugated forms. - 2 - Thus, serum concentrations of estrone sulfate are three to five times higher than that of the corresponding glucuronide, but the opposite is true in urine. This is partly due to albumin’s greater affinity for estrone sulfate compared to estrone glucuronide, but also because of estrone glucuronide’s higher glomerular filtration rate. -
Workshop on Normal Reference Ranges for Estradiol in Postmenopausal Women, September 2019, Chicago, Illinois
Menopause: The Journal of The North American Menopause Society Vol. 27, No. 6, pp. 614-624 DOI: 10.1097/GME.0000000000001556 ß 2020 by The North American Menopause Society SYMPOSIUM REPORT Workshop on normal reference ranges for estradiol in postmenopausal women, September 2019, Chicago, Illinois Richard J. Santen, MD,1 JoAnn V. Pinkerton, MD, FACOG, NCMP,2 JamesH.Liu,MD,NCMP,3 Alvin M. Matsumoto, MD, FACP,4 Roger A. Lobo, MD, FACOG,5 Susan R. Davis, MBBS, FRACP, PhD, FAHMS,6 and James A. Simon, MD, CCD, NCMP, IF, FACOG7 Abstract The North American Menopause Society (NAMS) organized the Workshop on Normal Ranges for Estradiol in Postmenopausal Women from September 23 to 24, 2019, in Chicago, Illinois. The aim of the workshop was to review existing analytical methodologies for measuring estradiol in postmenopausal women and to assess existing data and study cohorts of postmenopausal women for their suitability to establish normal postmenopausal ranges. The anticipated outcome of the workshop was to develop recommendations for establishing normal ranges generated with a standardized and certified assay that could be adopted by clinical and research communities. The attendees determined that the term reference range was a better descriptor than normal range for estradiol measurements in postmenopausal women. Twenty-eight speakers presented during the workshop. Key Words: Estradiol – Estradiol assays – Estradiol workshop – Estrogen – Menopause. rs. Matsumoto, Pinkerton, Liu, and Santen opened purification steps (ie, those on automated platforms) lack the workshop by discussing the rationale and goals sensitivity, specificity, accuracy, and standardization. In for the workshop. They noted that this workshop addition, differences exist in the characteristics of patient pop- D 1,2 resulted because estradiol levels reported for postmenopausal ulations used to determine reference ranges.