| Transpermethrin (Ref: NRDC 146) |
![]() Last updated: 15/09/2025 |
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(Also known as: RU 22090; trans-permethrin) |
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An obsolete pyrethroid insecticide | |
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Used to control animal parasites | |
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Domestic and farm animals |
| Approval status |
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Not approved | |
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Not approved |
| Chemical structure |
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Trans-permethrin is one of the two main geometric isomers of permethrin, the other being cis-permethrin. Trans-permethrin exhibits geometric isomerism due to the rigid structure of its cyclopropane ring, where the spatial arrangement of substituents defines its stereochemistry. In the trans-isomer, the bulky groups on the cyclopropane ring are positioned on opposite sides, distinguishing it from the cis-isomer, where they lie on the same side. This difference in configuration affects the compound’s physical and biological properties, trans-permethrin tends to be more photostable but generally less potent as an insecticide compared to its cis counterpart. | |
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C₂₁H₂₀Cl₂O₃ | |
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CC1(C(C1C(=O)OCC2=CC(=CC=C2)OC3=CC=CC=C3)C=C(Cl)Cl)C.CC1(C(C1C(=O)OCC2=CC(=CC=C2)OC3=CC=CC=C3)C=C(Cl)Cl)C | |
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CC1([C@@H]([C@H]1C(=O)OCC2=CC(=CC=C2)OC3=CC=CC=C3)C=C(Cl)Cl)C.CC1([C@H]([C@@H]1C(=O)OCC2=CC(=CC=C2)OC3=CC=CC=C3)C=C(Cl)Cl)C | |
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SULTWYFHTOOZFD-UYEAFXNLSA-N | |
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InChI=1S/C21H20Cl2O3/c1-21(2)17(12-18(22)23)19(21)20(24)25-13-14-7-6-10-16(11-14)26-15-8-4-3-5-9-15/h3-12,17,19H,13H2,1-2H3 | |
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Yes |
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| Common Name | Relationship | Link |
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| transpermethrin | Isomer | ![]() |
| transpermethrin | - | ![]() |
| General status |
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Insecticide | ||||||||||||||
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Pyrethroid insecticide; Pyrethroid ester insecticide | ||||||||||||||
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Synthetic | ||||||||||||||
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Neurotoxin, acts on the nervous system of insects, and disturbs the function of neurons by interaction with the sodium channel. | ||||||||||||||
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[Sodium channel, Modulator] | ||||||||||||||
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61949-77-7 | ||||||||||||||
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52341-32-9; 51877-74-8; 52341-32-9 | ||||||||||||||
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263-347-9 | ||||||||||||||
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43859 | ||||||||||||||
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No data found | ||||||||||||||
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Antiparasitic products, insecticides & repellents: Pyrethrins & pyrethroids | ||||||||||||||
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QP53AC04 | ||||||||||||||
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No | ||||||||||||||
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391.29 | ||||||||||||||
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rac-(3-phenoxyphenyl)methyl (1R,3S)-3-(2,2-dichloroethenyl)-2,2-dimethylcyclopropane-1-carboxylate | ||||||||||||||
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3-phenoxybenzyl (1RS,3SR)-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropanecarboxylate | ||||||||||||||
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(3-phenoxyphenyl)methyl (1R,3S)-rel-3-(2,2-dichloroethenyl)-2,2-dimethylcyclopropanecarboxylate | ||||||||||||||
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| Commercial |
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Considered obsolete but may be available in some countries | |||
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1970s, first sythesised; 2000, start of withdrawal | |||
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Trans-permethrin is produced through an esterification reaction between 3-phenoxybenzyl alcohol and (1R, trans)-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropanecarboxylic acid, which is the trans-configured acid component. The synthesis begins with the preparation of the cyclopropane acid via cyclopropanation and chlorination, ensuring the correct trans stereochemistry. Separately, the alcohol is synthesised from 3-phenoxybenzaldehyde through reduction. These two components are then combined under controlled conditions to form the ester bond. Since permethrin consists of a mixture of cis and trans isomers, purification techniques such as recrystallisation or chromatographic separation are employed to isolate the trans isomer. This | |||
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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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| 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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> 5000 | L3 L = Pesticide manuals and hard copy reference books / other sources Rat3 = Unverified data of known source |
Low | ||||||||
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| Aquatic ecotoxicology |
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0.000052 | 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 ) Ceriodaphnia dubia LC₅₀4 = Verified data |
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| General |
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High (class III) | - | - | ||||||||
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> 5000 | L3 L = Pesticide manuals and hard copy reference books / other sources Rat3 = Unverified data of known source |
Low | ||||||||
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Primarily excreted through urinary and faecal routes following hepatic metabolism | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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| Health issues |
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CNS toxicant | ||||||||||||||||||||||||||||
| Handling issues |
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No information available | |||
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Health: H302, H317, H332 Environment: H400, H410 |
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Not listed (Not listed) | |||
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transpermethrin | ||
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transpermethrine | ||
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| Record last updated: | 15/09/2025 |
| 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 |
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