| Fenchlorphos (Ref: Dow ET-14) |
![]() Last updated: 03/02/2026 |
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(Also known as: ronnel; fenclofos; dermaphos; dermafos; Dow ET-57) |
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An organophosphate insecticide once used in veterinary medicine for parasite management but now mainly obsolete | |
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Used for scabies management | |
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Cattle; Sheep |
| 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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C₈H₈Cl₃O₃PS | |
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COP(=S)(OC)OC1=CC(=C(C=C1Cl)Cl)Cl | |
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- | |
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JHJOOSLFWRRSGU-UHFFFAOYSA-N | |
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InChI=1S/C8H8Cl3O3PS/c1-12-15(16,13-2)14-8-4-6(10)5(9)3-7(8)11/h3-4H,1-2H3 | |
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Yes |
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| Common Name | Relationship | Link |
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| fenchlorphos | - | ![]() |
| General status |
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Insecticide | ||||||||||||||
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Organophosphate insecticide; Organothiophosphate insecticide; Phenyl organothiophosphate insecticide | ||||||||||||||
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Synthetic | ||||||||||||||
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Systemic. Acetylcholinesterase (AchE) inhibitor. | ||||||||||||||
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[Cholinesterase, Inhibitor] | ||||||||||||||
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299-84-3 | ||||||||||||||
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206-082-6 | ||||||||||||||
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112 | ||||||||||||||
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9298 | ||||||||||||||
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015-052-00-X | ||||||||||||||
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None allocated | ||||||||||||||
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No | ||||||||||||||
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321.55 | ||||||||||||||
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O,O-dimethyl O-(2,4,5-trichlorophenyl) phosphorothioate | ||||||||||||||
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O,O-dimethyl O-2,4,5-trichlorophenyl phosphorothioate | ||||||||||||||
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O,O-dimethyl O-(2,4,5-trichlorophenyl) phosphorothioate | ||||||||||||||
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UK Environment Agency non-statutory standard for the protection of aquatic life in freshwater and saltwater: 0.03 µg l⁻¹ as annual average, 0.1 µg l⁻¹ as max acceptable conc. | ||||||||||||||
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Colourless to light tan coloured crystalline powder | ||||||||||||||
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Considered obsolete but may be available in some countries | |||
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1984, first registered USA | |||
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Supplied in a wide variety of different formulations incuding emulsifiable concentrates and granules | |||
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The production of fenchlorphos involves a two-step synthetic process starting with 2,4,5-trichlorophenol as the key aromatic precursor. In the first step, this compound reacts with phosphorus oxychloride or dimethyl phosphorochloridothioate in the presence of a base such as pyridine or triethylamine, facilitating the formation of the O,O-dimethyl O-(2,4,5-trichlorophenyl) phosphorothioate structure. This reaction is carried out under controlled temperature and anhydrous conditions to prevent hydrolysis. | |||
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Data for the amount of life cycle GHGs produced by fenchlorphos are not available in the public domain. However, whilst estimates vary, more general data suggests that between 14 and 19 kilograms of CO₂e is emitted per kilogram of insecticide produced. |
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40.0 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
Moderate | ||||||||
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9080000 | L3 L = Pesticide manuals and hard copy reference books / other sources Acetone3 = Unverified data of known source |
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| 3470000 | L3 L = Pesticide manuals and hard copy reference books / other sources Chloroform3 = Unverified data of known source |
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| 5950000 | L3 L = Pesticide manuals and hard copy reference books / other sources Toluene3 = Unverified data of known source |
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| 5030000 | L3 L = Pesticide manuals and hard copy reference books / other sources Xylene3 = Unverified data of known source |
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41 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
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97 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
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7.59 X 1004 | Calculated | - | |||||||
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4.88 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
High | ||||||||
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1.58 | Q2 Q = Miscellaneous data from online sources 2 = Unverified data of unknown source |
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110 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
Highly volatile. If applied directly to plants or soil, drift is a concern & mitigation is advisable | ||||||||
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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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| Soil adsorption and mobility |
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- | Q2 Q = Miscellaneous data from online sources 2 = Unverified data of unknown source |
Non-mobile | |||||||
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10232 | ||||||||||
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Estimated | ||||||||||
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| Fate indices |
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| Known metabolites |
None
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| Terrestrial ecotoxicology |
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> 500 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
Moderate | ||||||||
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> 3500 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Anas platyrhynchos3 = Unverified data of known source |
Low | ||||||||
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| Aquatic ecotoxicology |
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0.74 | R3 R = Peer reviewed scientific publications Oncorhynchus mykiss juvenile 48 hr3 = Unverified data of known source |
Moderate | ||||||||
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| General |
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High (class III) | - | - | ||||||||
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> 500 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
Moderate | ||||||||
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> 2000 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
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List II | - | - | ||||||||
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May be absorbed through the skin | ||||||||||
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Mainly excreted in urine | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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| Health issues |
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Harmful in contact skin or if swallowed | ||||||||||||||||||||||||||||
| Handling issues |
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Prevent generation of dust Incompatible with alkaline pesticides IMDG Transport Hazard Class 6.1 |
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Health: H302, H312 Environment: H400, H410 |
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II (Moderately hazardous) | |||
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UN2811 | |||
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Packaging Group III (minor danger) | |||
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fenchlorphos | ||
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fenchlorphos | ||
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Fenchlorphos | ||
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fenclorfos | ||
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fenchlorfos | ||
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fenchloorfos | ||
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| Record last updated: | 03/02/2026 |
| 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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