| Cymiazol hydrochloride |
![]() Last updated: 25/10/2025 |
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(Not known by any other names) |
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A veterinary drug used as an ectoparasiticide | |
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Used for the control of mites and ticks especially those resistant to organochlorines, organophosphates and carbamates | |
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Cattle; Sheep; Honeybees |
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Not approved | |
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Not approved |
| Chemical structure |
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None | |
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C₁₂H₁₅ClN₂S | |
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CC1=CC(=C(C=C1)N=C2N(C=CS2)C)C.Cl | |
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- | |
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WDSSGOOJORKJEC-UHFFFAOYSA-N | |
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InChI=1S/C12H14N2S.ClH/c1-9-4-5-11(10(2)8-9)13-12-14(3)6-7-15-12;/h4-8H,1-3H3;1H | |
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Yes |
| General status |
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Acaricide, Ecoparasiticide | ||||||||||||||
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Benzenamine insecticide; Benzenamine acaricide; Amidine compound | ||||||||||||||
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Synthetic | ||||||||||||||
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Contact action. Acts on nervous system. Octopamine receptor agonist. | ||||||||||||||
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[Octopamine receptor, Agonist] | ||||||||||||||
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121034-85-3 | ||||||||||||||
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No data found | ||||||||||||||
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None allocated | ||||||||||||||
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18772390 | ||||||||||||||
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No data found | ||||||||||||||
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Antiparasitic products, insecticides & repellents: Sulphur-containing products | ||||||||||||||
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QP53AA02 | ||||||||||||||
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No | ||||||||||||||
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254.78 | ||||||||||||||
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N-[(2EZ)-3-methylthiazol-2(3H)-ylidene]-2,4-xylidine hydrochloride | ||||||||||||||
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N-[(2EZ)-3-methylthiazol-2(3H)-ylidene]-2,4-xylidine hydrochloride | ||||||||||||||
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2,4-dimethyl-N-(3-methyl-2(3H)-thiazolylidene)benzenamine hydrochloride (1:1) | ||||||||||||||
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| Commercial |
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Circa 1978, introduced | |||
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Typically formulated as a granulate for dissolving in water and using topically. For control Varroa mites it is often dripped directly on to bee pathways. | |||
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The production of cymiazol hydrochloride begins with the synthesis of its core structure, an iminophenyl thiazolidine derivative. This typically starts with a 2,4-dimethylphenyl precursor, which undergoes a condensation reaction with a thiazole ring system to form the key imine linkage that defines cymiazol’s activity. The resulting base compound, cymiazole, is then reacted with hydrochloric acid to form the hydrochloride salt, enhancing its solubility and stability for veterinary use. | |||
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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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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 soil metabolites |
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Major fraction | - | - |
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None
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None
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| Aquatic ecotoxicology |
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| General |
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High (class III) | - | - | ||||||||
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Unclear but probably eliminated via hepatic metabolism and renal excretion | 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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Not classified | |||
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Not listed (Not listed) | |||
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cymiazol hydrochloride | ||
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| Record last updated: | 25/10/2025 |
| 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 |
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