Zilpaterol hydrochloride (Ref: RU 42173) |
![]() Last updated: 16/09/2025 |
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(Also known as: zilpaterol HCl; RU 41173) |
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A synthetic beta2-adrenoreceptor agonist | |
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Used to improve growth and feeding efficiency | |
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Cattle |
Approval status |
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Not approved | |
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Not approved |
Chemical structure |
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Zilpaterol has two chiral carbons and consequently four optical enantiomers. Commercial product is usually a racemic trans-zilpaterol HCl, a mixture of the (6R,7R) and (6S,7S) enantiomers. | |
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C₁₄H₂₀ClN₃O₂ | |
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CC(C)NC1CCN2C3=C(C1O)C=CC=C3NC2=O.Cl | |
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CC(C)N[C@@H]1CCN2C3=C([C@H]1O)C=CC=C3NC2=O.Cl | |
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GIEFXLLRTJNFGT-LOCPCMAASA-N | |
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InChI=1S/C14H19N3O2.ClH/c1-8(2)15-11-6-7-17-12-9(13(11)18)4-3-5-10(12)16-14(17)19;/h3-5,8,11,13,15,18H,6-7H2,1-2H3,(H,16,19);1H/t11-,13-;/m1./s1 | |
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Yes |
General status |
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Medicinal drug, Growth promotor | |
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Beta-Adrenergic agonist | |
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Synthetic | |
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A synthetic beta2-adrenoreceptor agonist that binds with the muscle beta-adrenoreceptors leading to the activation of protein kinase A, an enzyme responsible for changes in protein synthesis and degradation | |
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[Beta-2 adrenergic receptor, Agonist], [Beta-1 adrenergic receptor, Binder], [Muopiod receptor, Antagonist | |
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119520-06-8 | |
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601-619-4 | |
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11507658 | |
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Growth promotor | |
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None allocated | |
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No | |
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297.78 | |
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(9R,10R)-9-hydroxy-10-(propan-2-ylamino)-1,3-diazatricyclo[6.4.1.04,13]trideca-4,6,8(13)-trien-2-one;hydrochloride | |
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White to yellow coloured powder |
Commercial |
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Current; Banned in some countries | |||
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1980s, developed; 1990s, field trials; 2003, first approvals USA; 2013, voluntary market withdrawal | |||
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Usually formulated as a medicated feed additive or premix | |||
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The production of zilpaterol hydrochloride involves a multi-step chemical synthesis starting from a heterocyclic precursor such as 4,5,6,7-tetrahydroimidazo[4,5,1-jk][1]benzazepine-2,7-dione. The first step typically includes hydrogenation using a nickel-based or palladium catalyst to convert the oxime group at the 6-position into an amino group, forming a key intermediate. This is followed by alkylation, where the intermediate reacts with 2-bromopropane to introduce the isopropylamino side chain, yielding the active zilpaterol base. The compound is then subjected to reduction and purification, often under controlled temperature and pressure, to ensure high stereoselectivity and yield. Finally, the purified zilpaterol is reacted with hydrochloric acid to form the hydrochloride salt. | |||
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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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150000 | 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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200 | 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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1.00 X 1001 | Calculated | - | |||||||
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1 | F2 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 ) 2 = Unverified data of unknown source |
Low | ||||||||
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8.09 | 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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Substance may enter the environment via the urine and faeces of treated animals or by leaching from spilt medicated feed. |
Degradation |
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21.5 | 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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USEPA data: Soil DT₅₀ 17.3-24.8 days | ||||||||||
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Stable | 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 ) No degradation seen in 126 days3 = Unverified data of known source |
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60 | 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 |
Stable | |||||||
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pH sensitive: DT₅₀ 53 days at pH4, Dt50 28 days at pH9 | ||||||||||
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365 | 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 |
Very persistent | |||||||
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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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Soil adsorption and mobility |
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- | 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 |
Slightly mobile | |||||||
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566 | ||||||||||
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Fate indices |
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1.66 | Calculated | Low leachability | ||||||||||||||||||||||||||
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Known metabolites |
None
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Terrestrial ecotoxicology |
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> 500 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) Rat5 = Verified data used for regulatory purposes |
Moderate | ||||||||
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Aquatic ecotoxicology |
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General |
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> 500 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) Rat5 = Verified data used for regulatory purposes |
Moderate | ||||||||
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0.04 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) 5 = Verified data used for regulatory purposes |
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0.04 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) 5 = Verified data used for regulatory purposes |
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Eliminated almost completely via urine (50–55%) and faeces (40–42%) within 8 days | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) 5 = Verified data used for regulatory purposes |
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Health issues |
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May cause cardiovasuclar effects May cause tremors |
Handling issues |
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No information available | |||
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Health: H302, H332, H372 | |||
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Not listed (Not listed) | |||
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zilpaterol hydrochloride | ||
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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 |