Chloromethiuron (Ref: CGA 13444) |
![]() Last updated: 15/09/2025 |
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(Also known as: C-9140) |
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A thiourea insecticide which is now considered to be obsolete | |
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Once used to treat Ixodidae ticks, mites and lice | |
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Cattle; Sheep; Horses; Dogs |
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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C₁₀H₁₃ClN₂S | |
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CC1=C(C=CC(=C1)Cl)NC(=S)N(C)C | |
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IBZZDPVVVSNQOY-UHFFFAOYSA-N | |
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InChI=1S/C10H13ClN2S/c1-7-6-8(11)4-5-9(7)12-10(14)13(2)3/h4-6H,1-3H3,(H,12,14) | |
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Yes |
General status |
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Acaricide, Insecticide, Ixodicide | |
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Thiourea substance | |
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Synthetic | |
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Unknown mode of action however compounds of this class typically act by inhibiting photosynthesis, particularly targeting photosystem II in plant chloroplasts | |
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[Probable - photosystem II, Inhibitor] | |
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28217-97-2 | |
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3034465 | |
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3034465 | |
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None allocated | |
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No | |
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228.75 | |
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N'-(4-chloro-2-methylphenyl)-N,N-dimethylcarbonothioic diamide | |
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3-(4-chloro-2-methylphenyl)-1,1-dimethylthiourea | |
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N'-(4-chloro-2-methylphenyl)-N,N-dimethylthiourea | |
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Colourless crystalline solid |
Commercial |
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Considered obsolete but may be available in some countries | |||
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1975, first reported | |||
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Chloromethiuron was typically sold as a solid formulation i.e.powders and granules | |||
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Chloromethiuron is synthesised through a multi-step chemical process starting with p-chloro-toluidine hydrochloride. This compound is first prepared by chlorinating o-toluidine in nitrobenzene with acetic anhydride, followed by acid treatment and crystallisation. The resulting p-chloro-toluidine salt is then reacted with carbon disulphide and dimethylamine in the presence of sodium hydroxide, under controlled temperature conditions. This reaction forms the thiourea linkage characteristic of chloromethiuron. After refluxing and cooling, the product is isolated and purified. | |||
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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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50 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
Moderate | ||||||||
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37000 | L3 L = Pesticide manuals and hard copy reference books / other sources Acetone3 = Unverified data of known source |
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40000 | L3 L = Pesticide manuals and hard copy reference books / other sources Dichloromethane3 = Unverified data of known source |
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50 | L3 L = Pesticide manuals and hard copy reference books / other sources Isopropanol3 = Unverified data of known source |
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175 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
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6.61 X 1002 | Calculated | - | |||||||
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2.82 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
Moderate | ||||||||
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1.34 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
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0.0011 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
Low volatility | ||||||||
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5.03 X 10-06 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
Non-volatile | ||||||||
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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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Fate indices |
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Low risk | Q3 Q = Miscellaneous data from online sources Based on LogP < 33 = Unverified data of known source |
Low risk | |||||||||||||||||||||||||
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Known metabolites |
None
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Terrestrial ecotoxicology |
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> 2500 | 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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General |
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High (class III) | - | - | ||||||||
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> 2500 | L3 L = Pesticide manuals and hard copy reference books / other sources Rat3 = Unverified data of known source |
Low | ||||||||
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2150 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
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Elimination route is unclear but based on its chemical structure it is likely to undergo hepatic metabolism and excreted via the renal route (urine). | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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Health issues |
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No further information available |
Handling issues |
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No information available | |||
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U (Unlikely to present an acute hazard) | |||
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chloromethiuron | ||
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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 |