Triclabendazole (Ref: CGA 89317) |
![]() Last updated: 12/09/2025 |
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(Also known as: CGA 89317) |
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A benzimidazole anthelmintic used in veterinary medicine | |
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Used for the control of liver flukes, scabies causing mites, bloodsuck lice and fly larvae | |
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Cattle; Sheep; Goats |
Approval status |
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Approved - usually available as a prescription only medicine to be authorised by suitably qualified person (POM-VPS) | |
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Approved |
Chemical structure |
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None | |
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C₁₄H₉Cl₃N₂OS | |
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CSC1=NC2=CC(=C(C=C2N1)Cl)OC3=C(C(=CC=C3)Cl)Cl | |
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No data | |
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NQPDXQQQCQDHHW-UHFFFAOYSA-N | |
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InChI=1S/C14H9Cl3N2OS/c1-21-14-18-9-5-8(16)12(6-10(9)19-14)20-11-4-2-3-7(15)13(11)17/h2-6H,1H3,(H,18,19) | |
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Yes |
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Common Name | Relationship | Link |
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triclabendazole | - | ![]() |
General status |
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Anthelmintic, Antiparasitic Medicinal drug | |
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Benzimidazole | |
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>97% | |
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Synthetic | |
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It binds to tubulin impairing intracellular transport mechanisms and interferes with protein synthesis. | |
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[Microtubule formation, Inhibitor] | |
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68786-66-3 | |
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Antiparasitic products, insecticides & repellents: Anthelmintics | |
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QP52AC01 | |
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No | |
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Allowed substance (Table 1: Ruminants) | |
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359.66 | |
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5-chloro-6-(2,3-dichlorophenoxy)-2-(methylthio)-1H-benzimidazole | |
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6-chloro-5-(2,3-dichlorophenoxy)-2-methylthio-benzimidazole | |
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White to brown crystalline powder | |
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Commercial |
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Current | |||
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1980s, first introduced | |||
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Usually available, often in combination with levamisole hydrochloride, as oral suspensions or as pour-on formulations | |||
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The production of triclabendazole typically begins with the synthesis of 2,3-dichlorophenol, which is then reacted with 4-chloro-5-nitroaniline to form a key intermediate via etherification. This intermediate undergoes reduction of the nitro group to yield the corresponding amine, followed by cyclisation with methyl isothiocyanate to construct the benzimidazole ring. The final step involves methylation of the thiol group to produce triclabendazole: 5-chloro-6-(2,3-dichlorophenoxy)-2-methylthio-1H-benzimidazole. Modern methods often use catalytic hydrogen transfer to avoid iron waste and improve environmental safety, making the process more suitable for industrial-scale production. | |||
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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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1.0 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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175 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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496 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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253.7 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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1.59 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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1.724 | 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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Soil adsorption and mobility |
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Fate indices |
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Known soil and groundwater metabolites |
None
Other known metabolites |
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triclabendazole sulfone | - | Animal (Faeces) | - | ||||
4-hydroxy triclabendazole | - | Animal (Faeces) | - | ||||
2-benzimidazolone | - | Animal (Urine and Faeces) | - | ||||
triclabendazole sulfoxide | - | Animal (Faeces) | - |
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Terrestrial ecotoxicology |
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> 5000 | 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 |
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Aquatic ecotoxicology |
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0.14 | E3 E = Manufacturers safety data sheets Oncorhynchus mykiss3 = Unverified data of known source |
Moderate | ||||||||
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General |
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High (class III) | - | - | ||||||||
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> 5000 | 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 |
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4000 | Q3 Q = Miscellaneous data from online sources Rat3 = Unverified data of known source |
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> 0.5 | E3 E = Manufacturers safety data sheets Rat 4 hr3 = Unverified data of known source |
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Mostly metabolised and excreted via urine and faeces. Also identified unchanged in breast milk. | 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 ) 4 = Verified data |
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Health issues |
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Possible liver and kidney toxicant |
Handling issues |
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No information available | |||
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Not listed (Not listed) | |||
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triclabendazole | ||
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triclabendazol | ||
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Record last updated: | 12/09/2025 |
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 |