Quintiofos (Ref: BAY 9037) |
![]() Last updated: 16/09/2025 |
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(Also known as: quintiophos) |
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A largely obsolete organophosphate insecticide | |
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Shown to control mites and other livestock pests | |
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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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Quintiofos exhibits stereoisomerism due to its chiral phosphorus centre and so exists in both R- and S-enantiomeric forms. The compound is typically referred to as a racemic mixture (RS), meaning it contains equal amounts of both enantiomers. | |
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C₁₇H₁₆NO₂PS | |
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CCOP(=S)(C1=CC=CC=C1)OC2=CC=CC3=C2N=CC=C3 | |
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No data | |
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OYFLKNAULOKYRI-UHFFFAOYSA-N | |
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InChI=1S/C17H16NO2PS/c1-2-19-21(22,15-10-4-3-5-11-15)20-16-12-6-8-14-9-7-13-18-17(14)16/h3-13H,2H2,1H3 | |
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Yes |
General status |
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Miticide | |
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Organophosphate insecticide; Organophosphate acaricide; Organothiophosphate insecticide; Organothiophosphate acaricide | |
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>98% | |
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Synthetic | |
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Acetylcholinesterase (AChE) inhibitor | |
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[Cholinesterase, Inhibitor] | |
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1776-83-6 | |
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217-208-4 | |
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72069 | |
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No data found | |
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None allocated | |
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No | |
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329.35 | |
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(E)-(O-ethyl O-quinolin-8-yl phenylphosphonothioate) | |
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(RS)-(O-ethyl O-8-quinolyl phenylphosphonothioate) | |
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O-ethyl O-8-quinolinyl P-phenylphosphonothioate | |
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Commercial |
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Considered obsolete but may be available in some countries | |||
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1970s, developed; 1979, first research published; 1980s, experimental use; Mid 1990s, usage declined; 2013, not approved UK | |||
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Usually formulated as an emulsifiable concentrate or solution for topical application in livestock settings | |||
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Quintiofos is produced through a multi-step chemical synthesis involving the formation of a phosphonothioate ester. The process typically begins with the preparation of phenylphosphonothioic acid derivatives, which are then reacted with ethanol to introduce the ethoxy group. In a subsequent step, the quinolin-8-ol moiety is attached via esterification, forming the O-quinolinyl linkage. | |||
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Data for the amount of life cycle GHGs produced by quintiofos 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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455 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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229 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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1.28 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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1.649 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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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 |
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Terrestrial ecotoxicology |
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150 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
Moderate | ||||||||
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Aquatic ecotoxicology |
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General |
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High (class III) | - | - | ||||||||
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150 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
Moderate | ||||||||
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50 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
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Type I | - | - | ||||||||
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Eliminated via hepatic metabolism followed by renal and biliary excretion | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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Health issues |
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Toxic if ingested or absorbed through the skin |
Handling issues |
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No data available | |||
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Not classified: Obsolete | |||
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Not listed (Not listed) | |||
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quintiofos | ||
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quintiofos | ||
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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 |