Dioxathion (Ref: Hercules AC25) |
![]() Last updated: 04/09/2025 |
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(Also known as: dioxation; delnav; dioxane phosphate; dioxationum) |
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An organophosphate compound once used as an insecticide on livestock | |
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Once used to control ticks, fleas and mites | |
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Cattle; Goats; Sheep; Pigs |
Approval status |
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Not approved | |
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Not approved |
Chemical structure |
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Dioxathion exhibits cis–trans isomerism, which arises from the spatial arrangement of its two sulphur-containing substituents on the dioxane ring. The molecule contains a central 1,4-dioxane ring substituted with two diethyl phosphorodithioate groups at the 2 and 3 positions. Depending on whether these bulky groups are on the same side of the ring (cis) or opposite sides (trans), the molecule exists in two distinct geometric forms. The cis-isomer is approximately four times more acutely toxic than the trans-isomer. Technical-grade dioxathion is typically a mixture of both isomers. | |
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C₁₂H₂₆O₆P₂S₄ | |
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CCOP(=S)(OCC)SC1C(OCCO1)SP(=S)(OCC)OCC | |
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No data | |
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VBKKVDGJXVOLNE-UHFFFAOYSA-N | |
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InChI=1S/C12H26O6P2S4/c1-5-15-19(21,16-6-2)23-11-12(14-10-9-13-11)24-20(22,17-7-3)18-8-4/h11-12H,5-10H2,1-4H3 | |
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Yes |
General status |
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Insecticide | |
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Organophosphate insecticide; Organophosphate acaricide; Organothiophosphate insecticide; Organothiophosphate acaricide | |
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>68% | |
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- | |
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Synthetic | |
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Acetylcholinesterase (AChE) inhibitor. | |
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[Cholinesterase, Inhibitor] | |
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78-34-2 | |
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201-107-7 | |
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124 | |
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037801 | |
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6531 | |
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015-063-00-X | |
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- | |
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None allocated | |
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No | |
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- | |
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456.54 | |
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O,O,O',O'-tetraethyl S,S'-1,4-dioxane-2,3-diyl bis(phosphorodithioate) | |
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S,S'-(1,4-dioxane-2,3-diyl) O,O,O',O'-tetraethyl bis(phosphorodithioate) | |
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S,S'-1,4-dioxane-2,3-diyl bis(O,O-diethyl phosphorodithioate) | |
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Marine Pollutant; Subject to the provisions of the UK Poisons Act 1972 | |
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Reddish-brown liquid |
Commercial |
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Considered obsolete but may be available in some countries | |||||||||
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1959, first reported; 1988, withdrawn USA | |||||||||
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The production of dioxathion involves synthesising a central 1,4-dioxane ring substituted with two diethyl phosphorodithioate groups at the 2 and 3 positions. The process begins with the formation of the dioxane backbone, typically through condensation of ethylene glycol derivatives under acidic conditions. Once the ring is established, the key step involves introducing the phosphorodithioate moieties via esterification or nucleophilic substitution using diethyl phosphorodithioic chloride or similar reagents. This results in the formation of the symmetrical bis-substituted compound. | |||||||||
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Data for the amount of life cycle GHGs produced by dioxathion 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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1.55 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) at 25 °C3 = Unverified data of known source |
Low | ||||||||
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20000 | L3 L = Pesticide manuals and hard copy reference books / other sources Kerosene3 = Unverified data of known source |
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10000 | L3 L = Pesticide manuals and hard copy reference books / other sources n-hexane3 = Unverified data of known source |
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-2 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
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2.82 X 1003 | Calculated | - | |||||||
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3.45 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
High | ||||||||
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Soluble | 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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Regulatory data - observed in metabolism and farm animal feeding studies | 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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1.26 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
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Degradation |
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35 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
Moderately persistent | |||||||
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Literature values give DT₅₀ range 15 (silty clay loam) - 55 days (clay) | ||||||||||
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Stable | Q2 Q = Miscellaneous data from online sources 2 = Unverified data of unknown source |
Stable | |||||||
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Stable | Q2 Q = Miscellaneous data from online sources 2 = Unverified data of unknown source |
Stable | |||||||
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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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11845 | ||||||||||
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Estimated | ||||||||||
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Fate indices |
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-0.11 | Calculated | Low leachability | ||||||||||||||||||||||||||
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Known metabolites |
None
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Terrestrial ecotoxicology |
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23 | L3 L = Pesticide manuals and hard copy reference books / other sources Rat3 = Unverified data of known source |
High | ||||||||
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> 3600 | 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 ) Anas platyrhynchos4 = Verified data |
Low | ||||||||
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> 50 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
Moderate | ||||||||
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Aquatic ecotoxicology |
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0.118 | 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 ) Oncorhynchus mykiss4 = Verified data |
Moderate | ||||||||
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0.00035 | 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 |
High | ||||||||
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General |
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High (class III) | - | - | ||||||||
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23 | L3 L = Pesticide manuals and hard copy reference books / other sources Rat3 = Unverified data of known source |
High | ||||||||
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235 | Q3 Q = Miscellaneous data from online sources Rat3 = Unverified data of known source |
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0.0015 | 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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List I; List II | - | - | ||||||||
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May be absorded through the skin - PPE/PPC required | ||||||||||
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Eliminated in faeces and urine | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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Health issues |
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May cause mild transient conjunctivitis Very toxic |
Handling issues |
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Prevent generation of mists | |||
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Health: H300, H311, H330 Environment: H400, H410 |
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Ib (Highly hazardous) | |||
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dioxathion | ||
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dioxathion | ||
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Dioxathion | ||
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dioxation | ||
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dioksation | ||
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Record last updated: | 04/09/2025 |
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 |