| Estradiol |
![]() Last updated: 20/10/2025 |
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(Also known as: oestradiol; 17beta oestradiol; beta-estradiol) |
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A semisynthetic estrogenic hormone with veterinary applications | |
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Mainly used as a hormone replacement therapy in conditions of inadequate estrogen production | |
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Horses; Cattle; Cats; Dogs |
| Approval status |
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Not approved | |
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Not approved |
| Chemical structure |
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Estradiol exhibits stereoisomerism, primarily due to the configuration of its hydroxyl groups and the orientation of its steroid backbone. The most biologically active form is 17beta-estradiol, where the hydroxyl group at carbon 17 is in the beta position. Its stereoisomer, 17alpha-estradiol, has the hydroxyl group in the alpha position and is significantly less potent in estrogenic activity. Additionally, estradiol can undergo glucuronidation at either the 3-hydroxyl or 17-hydroxyl positions, forming estradiol-3-glucuronide and estradiol-17-glucuronide, which are regioisomers with distinct metabolic pathways and biological roles. | |
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C₁₈H₂₄O₂ | |
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CC12CCC3C(C1CCC2O)CCC4=C3C=CC(=C4)O | |
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C[C@]12CC[C@H]3[C@H]([C@@H]1CC[C@@H]2O)CCC4=C3C=CC(=C4)O | |
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VOXZDWNPVJITMN-ZBRFXRBCSA-N | |
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InChI=1S/C18H24O2/c1-18-9-8-14-13-5-3-12(19)10-11(13)2-4-15(14)16(18)6-7-17(18)20/h3,5,10,14-17,19-20H,2,4,6-9H2,1H3/t14-,15-,16+,17+,18+/m1/s1 | |
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Yes |
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| Common Name | Relationship | Link |
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| estradiol hemihydrate | Hydrate | ![]() |
| estradiol | - | ![]() |
| ethinyl estradiol | Variant | ![]() |
| General status |
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Medicinal drug; Hormone | ||||||||||||||
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Steroid hormone | ||||||||||||||
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Semi-synthetic | ||||||||||||||
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Substance binds to its specific intracellular receptor and regulates DNA transcription for protein formation | ||||||||||||||
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[Estrogen receptor alpha, Agonist], [Estrogen receptor beta, Agonist], [Beclin-1, Binder], [ATP synthase subunit a, Inhibitor], [Nuclear receptor subfamily 1 group I member 2, Binder], [Neuronal acetylcholine receptor subunit alpha-4, Binder], [G-protein coupled estrogen receptor 1, Binder] | ||||||||||||||
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17916-67-5 | ||||||||||||||
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200-023-8 | ||||||||||||||
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5757 | ||||||||||||||
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Estrogens: Natural and semisynthetic estrogens, plain | ||||||||||||||
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QG03CA03 | ||||||||||||||
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No | ||||||||||||||
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272.4 | ||||||||||||||
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(8R,9S,13S,14S,17S)-13-methyl-6,7,8,9,11,12,14,15,16,17-decahydrocyclopenta[a]phenanthrene-3,17-diol | ||||||||||||||
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3,17β-dihydroxy-1,3,5(10)-estratriene | ||||||||||||||
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White crystalline solid | ||||||||||||||
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| Commercial |
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Current | |||
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1929, first isolated; 1930s, clinical use began; 1950s, veterinary adoption | |||
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Typically supplied as a sterile oil-based solution for intramuscular injection | |||
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The commercial production of estradiol typically begins with a steroidal precursor, such as estrone or testosterone, which undergoes a series of chemical transformations to yield the active estrogen compound. These steps include oxidation, reduction, and selective hydroxylation, often facilitated by catalysts and solvents that ensure high purity and yield. Advanced methods may incorporate continuous flow chemistry, allowing for more efficient and scalable synthesis. Historically, some estrogen products were derived from pregnant mare urine, but modern estradiol is almost exclusively synthesised chemically to avoid variability and ethical concerns. | |||
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Published GHG data is not available for most pharmaceuticals. However, according to industry, global averages suggest producing 1 kg of a typical active pharmaceutical ingredient can range from 10 to 100 kg CO₂e for small molecule drugs and potentially up to 1000 kg CO₂e for complex biologicals such as vaccines, depending on the drug type, its formulation, complexity of synthesis, solvent recovery, and energy sources used |
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3.6 | F3 F = U.S. EPA ECOTOX database / U.S. EPA pesticide fate database / Miscellaneous WHO documents / FAO data, IPCS INCHEM data (US EPA Databases Related to Pesticide Risk Assessment ) 3 = Unverified data of known source |
Low | ||||||||
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173 | F3 F = U.S. EPA ECOTOX database / U.S. EPA pesticide fate database / Miscellaneous WHO documents / FAO data, IPCS INCHEM data (US EPA Databases Related to Pesticide Risk Assessment ) 3 = Unverified data of known source |
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445.9 | F3 F = U.S. EPA ECOTOX database / U.S. EPA pesticide fate database / Miscellaneous WHO documents / FAO data, IPCS INCHEM data (US EPA Databases Related to Pesticide Risk Assessment ) 3 = Unverified data of known source |
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1.02 X 1004 | Calculated | - | |||||||
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4.01 | F3 F = U.S. EPA ECOTOX database / U.S. EPA pesticide fate database / Miscellaneous WHO documents / FAO data, IPCS INCHEM data (US EPA Databases Related to Pesticide Risk Assessment ) 3 = Unverified data of known source |
High | ||||||||
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1.2 | E3 E = Manufacturers safety data sheets 3 = Unverified data of known source |
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10.46 | F3 F = U.S. EPA ECOTOX database / U.S. EPA pesticide fate database / Miscellaneous WHO documents / FAO data, IPCS INCHEM data (US EPA Databases Related to Pesticide Risk Assessment ) 3 = Unverified data of known source |
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| Degradation |
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As this parameter is not normally measured directly, a surrogate measure is used: ‘Photochemical oxidative DT₅₀’. Where data is available, this can be found in the Fate Indices section below. | ||||||||||
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| Fate indices |
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| Known metabolites |
None
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| Terrestrial ecotoxicology |
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960 | F4 F = U.S. EPA ECOTOX database / U.S. EPA pesticide fate database / Miscellaneous WHO documents / FAO data, IPCS INCHEM data (US EPA Databases Related to Pesticide Risk Assessment ) Rat4 = Verified data |
Moderate | ||||||||
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| Aquatic ecotoxicology |
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> 0.139 | E3 E = Manufacturers safety data sheets Daphnia magna3 = Unverified data of known source |
Moderate | ||||||||
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> 2.48 | E3 E = Manufacturers safety data sheets Desmodesmus subspicatus3 = Unverified data of known source |
Moderate | ||||||||
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| General |
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960 | F4 F = U.S. EPA ECOTOX database / U.S. EPA pesticide fate database / Miscellaneous WHO documents / FAO data, IPCS INCHEM data (US EPA Databases Related to Pesticide Risk Assessment ) Rat4 = Verified data |
Moderate | ||||||||
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Primarily eliminated from the body through hepatic metabolism followed by renal and fecal excretion | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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| Health issues |
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CPL data: suspected of causing cancer | ||||||||||||||||||||||||||||
| Handling issues |
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May emit acrid smoke and irritating fumes if heated to decomposition IMDG Transport Hazard Class 9 |
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Health: H351, H360fd, H362 Environment: H410 |
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Not listed (Not listed) | |||
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UN3077 | |||
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Packaging group III (minor danger) | |||
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Chemically stable under standard ambient conditions |
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estradiol | ||
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| Record last updated: | 20/10/2025 |
| Contact: | aeru@herts.ac.uk |
| Please cite as: | Lewis, K.A., Tzilivakis, J., Warner, D. and Green, A. (2016) An international database for pesticide risk assessments and management. Human and Ecological Risk Assessment: An International Journal, 22(4), 1050-1064. DOI: 10.1080/10807039.2015.1133242 |
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