Coumaphos (Ref: OMS 485) |
![]() Last updated: 15/09/2025 |
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(Also known as: counafosum; coumafos; cumafos; ENT 17957) |
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An organophosphate insecticide used for control of a wide variety of livestock insects | |
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Used to control cattle grubs, screw-worms, lice, scabies, flies, and ticks | |
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Sheep; Goats; Cattle; Horses; Pigs; Poultry |
Approval status |
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Not approved | |
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Not approved |
Chemical structure |
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An organophosphate insecticide used for control of a wide variety of livestock insects | |
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C₁₄H₁₆ClO₅PS | |
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CCOP(=S)(OCC)OC1=CC2=C(C=C1)C(=C(C(=O)O2)Cl)C | |
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No data | |
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BXNANOICGRISHX-UHFFFAOYSA-N | |
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InChI=1S/C14H16ClO5PS/c1-4-17-21(22,18-5-2)20-10-6-7-11-9(3)13(15)14(16)19-12(11)8-10/h6-8H,4-5H2,1-3H3 | |
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Yes |
General status |
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Antiparasitic, Insecticide, Acaricide, Anthelmintic, Ectoparasiticide | |
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Organophosphate veterinary substance; Organothiophosphate veterinary substance | |
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- | |
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Synthetic | |
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Non-systemic, Acetylcholinesterase (AChE) inhibitor. | |
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[Cholinesterase, Inhibitor] | |
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56-72-4 | |
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200-285-3 | |
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121 | |
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036501 | |
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- | |
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Antiparasitic products, insecticides & repellents: Ecoparasiticides, insecticides & repellents | |
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QP53AF08 | |
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No | |
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Allowed substance (Table 1: Bees] | |
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362.77 | |
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- | |
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O-3-chloro-4-methyl-2-oxo-2H-chromen-7-yl O,O-diethyl phosphorothioate | |
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O-(3-chloro-4-methyl-2-oxo-2H-1-benzopyran-7-yl) O,O-diethyl phosphorothioate | |
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- | |
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- | |
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UK Environment Agency non-statutory standard for the protection of freshwater and saltwater aquatic life: 0.03 µg l⁻¹ as annual average; 0.1 µg l⁻¹ as max acceptable conc. | |
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Tan crystalline solid |
Commercial |
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Current | |||
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Circa 1953, introduced | |||
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Usually supplied as pour-ons, sprays and dips for topical use | |||
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The production of coumaphos typically involves the esterification of 3-chloro-4-methyl-7-hydroxycoumarin with diethyl chlorothiophosphate. One efficient method uses an aqueous-phase reaction, where the coumarin derivative is combined with an acid-binding agent and a phase-transfer catalyst, then reacted with diethyl chlorothiophosphate under controlled temperatures, usually between 50–80 DegC for 20 to 150 minutes. After the reaction, the mixture is filtered, washed to neutrality, and dried to yield coumaphos as a crystalline product. | |||
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Data for the amount of life cycle GHGs produced by coumaphos 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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1.5 | G3 G = Extension Toxicology network database EXTOXNET. Available online but no longer updated. (click here ) 3 = Unverified data of known source |
Low | ||||||||
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238200 | 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 ) Acetone3 = Unverified data of known source |
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900 | 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 ) Xylene3 = Unverified data of known source |
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130 | 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 ) Octanol3 = Unverified data of known source |
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63900 | 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 ) Methylene chloride3 = Unverified data of known source |
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95 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
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7.24 X 1003 | Calculated | - | |||||||
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3.86 | K3 K = Research datasets (e.g. Pandora, Demetra; these datasets no longer available). Norman Ecotoxicology database. (click here ) 3 = Unverified data of known source |
High | ||||||||
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1.38 | 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 |
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0.000013 | G3 G = Extension Toxicology network database EXTOXNET. Available online but no longer updated. (click here ) 3 = Unverified data of known source |
Low volatility | ||||||||
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0.011 | V1 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Estimated1 = Estimated data with little or no verification |
Non-volatile | ||||||||
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Degradation |
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152 | 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 |
Persistent | |||||||
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General literature gives DT₅₀ between 100-300 days (R4) | ||||||||||
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Stable | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
Stable | |||||||
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Not sensitive to pH | ||||||||||
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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 |
Non-mobile | |||||||
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18000 | ||||||||||
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Other literature values range 5778-21120 mL g⁻¹ (R3) | ||||||||||
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Fate indices |
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-0.56 | Calculated | Low leachability | ||||||||||||||||||||||||||
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Known soil metabolites |
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Known groundwater metabolites |
None
Other known metabolites |
None
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Terrestrial ecotoxicology |
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7.1 | 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 ) Rat4 = Verified data |
High | ||||||||
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29.4 | G4 G = Extension Toxicology network database EXTOXNET. Available online but no longer updated. (click here ) Anas platyrhynchos4 = Verified data |
High | ||||||||
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20 | 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 ) Apis mellifera3 = Unverified data of known source |
Moderate | |||||||
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4.6 | 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 ) Apis mellifera3 = Unverified data of known source |
Moderate | ||||||||
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> 25 | Q2 Q = Miscellaneous data from online sources 2 = Unverified data of unknown source |
Moderate | ||||||||
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Aquatic ecotoxicology |
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0.55 | F5 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 ) Oncorhynchus mykiss5 = Verified data used for regulatory purposes |
Moderate | ||||||||
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0.0001 | F5 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 magna5 = Verified data used for regulatory purposes |
High | ||||||||
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General |
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High (class III) | - | - | ||||||||
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7.1 | 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 ) Rat4 = Verified data |
High | ||||||||
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860 | L3 L = Pesticide manuals and hard copy reference books / other sources Rat3 = Unverified data of known source |
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0.341 | L3 L = Pesticide manuals and hard copy reference books / other sources Rat3 = Unverified data of known source |
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Intraperitoneal LD₅₀ = 7.5 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
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None allocated | 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 ) JMPR 19904 = Verified data |
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List I | - | - | ||||||||
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Occupational exposure may occur through inhalation of spray mists and dermal contact | ||||||||||
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In rats excretion is rapid largely unmetabolised | Q4 Q = Miscellaneous data from online sources 4 = Verified data |
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Health issues |
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May cause seizures, incontinence, respiratory depression, loss of consciousness Harmful if swallowed, inhaled or absorbed through the skin |
Handling issues |
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Prevent generation of dust IMDG Transport Hazard Class 6.1 |
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Health: H300, H312 Environment: H400, H410 |
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Ib (Highly hazardous) | |||
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UN2783 | |||
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coumaphos | ||
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coumaphos | ||
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Coumaphos | ||
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coumaphos | ||
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cumafos | ||
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cumafos | ||
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coumaphos | ||
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kumafos | ||
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cumafos | ||
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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 |