Cyproterone acetate |
![]() Last updated: 16/09/2025 |
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(Also known as: CPA; cyproterone 17-O-acetate) |
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A 17-hydroxyprogesterone acetate derivative with strong progestagenic properties and which has veterinary applications | |
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Used for the treatment of benign prostatic hyperplasia and reducing aggressive or antisocial behaviour | |
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Dogs; Cats |
Approval status |
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Not approved | |
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Not approved |
Chemical structure |
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None | |
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C₂₄H₂₉ClO₄ | |
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[H][C@@]12C[C@]1([H])[C@@]1(C)C(=CC2=O)C(Cl)=C[C@@]2([H])[C@]3([H])CC[C@](OC(C)=O)(C(C)=O)[C@@]3(C)CC[C@]12[H] | |
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UWFYSQMTEOIJJG-FDTZYFLXSA-N | |
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InChI=1S/C24H29ClO4/c1-12(26)24(29-13(2)27)8-6-16-14-10-20(25)19-11-21(28)15-9-18(15)23(19,4)17(14)5-7-22(16,24)3/h10-11,14-18H,5-9H2,1-4H3/t14-,15+,16-,17-,18-,22-,23-,24-/m0/s1 | |
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Yes |
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Common Name | Relationship | Link |
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cyproterone acetate | - | ![]() |
cyproterone | Parent | ![]() |
General status |
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Medininal drug | |
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Pregnane steroid | |
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Synthetic | |
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It suppresses the actions of testosterone (and its metabolite dihydrotestosterone) on tissues | |
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[Androgen receptor, Antagonist], [Prostate-specific antigens] | |
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427-51-0 | |
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207-048-3 | |
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9880 | |
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Genito urinary system and sex hormones | |
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G03HA01 | |
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No | |
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416.94 | |
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(1S,2S,3S,5R,11R,12S,15R,16S)-15-acetyl-9-chloro-2,16-dimethyl-6-oxopentacyclo[9.7.0.0^{2,8}.0^{3,5}.0^{12,16}]octadeca-7,9-dien-15-yl acetate | |
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Solid |
Commercial |
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Current | |||
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1962, clinical effects discovered; 1980s, vet applications explored | |||
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In veterinary research contexts, it has been administered orally in capsule form | |||
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The synthesis of cyproterone acetate involves a multi-step chemical and biocatalytic process starting from steroidal precursors such as 4-androstene-3,17-dione. One advanced method uses continuous flow chemistry to streamline the production into a 10-step sequence. Key transformations include enzymatic 1-dehydrogenation to introduce a double bond in the A-ring, stereoselective Mukaiyama hydration to form the crucial C17alpha-hydroxyl group, and Corey–Chaykovsky cyclopropanation to construct the cyclopropyl moiety on the A-ring. These steps are integrated into a telescoped flow system that enhances stereocontrol, reduces reaction time, and improves overall yield and sustainability compared to traditional batch synthesis. The final step involves acetylation at the C17 position to yield cyproterone acetate. | |||
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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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50000 | E3 E = Manufacturers safety data sheets Methanol3 = Unverified data of known source |
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10000 | E3 E = Manufacturers safety data sheets Ethanol3 = Unverified data of known source |
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83000 | E3 E = Manufacturers safety data sheets DMSO3 = Unverified data of known source |
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200 | 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 ) 4 = Verified data |
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1.26 X 1003 | Calculated | - | |||||||
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3.1 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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Degradation |
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7 | 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 |
Non-persistent | |||||||
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Literature gives soil DT₅₀ as 135-217 hours depending on soil type | ||||||||||
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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 soil and groundwater metabolites |
None
Other known metabolites |
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15beta-hydroxycyproterone acetate | - | Humans (Liver) | - |
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Terrestrial ecotoxicology |
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> 5000 | E3 E = Manufacturers safety data sheets Rat3 = Unverified data of known source |
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Aquatic ecotoxicology |
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0.16 | 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 ) Pimephales promelas4 = Verified data |
Moderate | ||||||||
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2.1 | 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 ) Daphnia magna4 = Verified data |
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General |
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High (class III) | - | - | ||||||||
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> 5000 | E3 E = Manufacturers safety data sheets Rat3 = Unverified data of known source |
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Excreted around 60% in the bile and 33% through the kidneys. | 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 ) 4 = Verified data |
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Health issues |
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CLP data: suspected carcinogen |
Handling issues |
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Incompatible with trong oxidising agents Avoid generation of dusts |
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Health: H312, H332, H351, H360, H373 | |||
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Not listed (Not listed) | |||
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Not regulated | |||
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cyproterone acetate | ||
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Record last updated: | 16/09/2025 |
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 |