Fenbendazole (Ref: Hoe 881v) |
![]() Last updated: 15/09/2025 |
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(Also known as: phenbendasol) |
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A broad spectrum benzimidazole anthelmintic used widely in veterinary medicine | |
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Used against gastrointestinal parasites in livestock, exotic animals and domestic pets | |
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Cattle; Sheep; Horses; Domestic pets; Hedgehogs; Bears; Elephants; Pigeons; Exotic birds; Ferrets; Fish |
Approval status |
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Approved - legal class and so availability is variable and depends on application and product type | |
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Approved |
Chemical structure |
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None | |
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C₁₅H₁₃N₃O₂S | |
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COC(=O)NC1=NC2=C(N1)C=C(C=C2)SC3=CC=CC=C3 | |
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No data | |
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HDDSHPAODJUKPD-UHFFFAOYSA-N | |
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InChI=1S/C15H13N3O2S/c1-20-15(19)18-14-16-12-8-7-11(9-13(12)17-14)21-10-5-3-2-4-6-10/h2-9H,1H3,(H2,16,17,18,19) | |
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Yes |
General status |
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Anthelmintic, Antiparasitic, Nematicide | |
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Benzimidazole | |
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Synthetic | |
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Binds to tubulin, a protein required for functions including nutrient uptake, thus disrupting parasite energy metabolism | |
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[Tubulin alpha-3 chain, Antagonist] | |
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43210-67-9 | |
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256-145-7 | |
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Antiparasitic products, insecticides & repellents: Anthelmintics | |
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QP52AC13 | |
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No | |
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Allowed substance (Table 1: Ruminants, Porcine, Equidae) | |
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299.35 | |
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methyl N-(6-phenylsulfanyl-1H-benzoimidazol-2-yl)carbamate | |
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2-(methoxycarbonylamino)-5-(phenylthio)benzimidazole | |
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White to dirty white coloured crystalline powder |
Commercial |
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Current | |||
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1970s, developed | |||
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Available in a variety of orally administered formulations including oral powders, medicated feeds and products for adding to drinking water | |||
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Fenbendazole is synthesised through a multi-step chemical process that begins with inexpensive raw materials like m-dichlorobenzene. This compound undergoes nitration, amination, condensation, reduction, and cyclization reactions to form the final product. Modern production methods have evolved to improve efficiency and reduce environmental impact, replacing older reduction techniques (such as those using sodium sulphide) with cleaner alternatives. | |||
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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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0.01 | 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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233 | 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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Decomposes on melting | 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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7.08 X 1003 | Calculated | - | |||||||
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3.85 | 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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1.40 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
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Max absorption at 296nm | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
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Substance may enter the environment via the faeces of treated animals or by leaching from spilt medicated feed. |
Degradation |
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0.53 | V4 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 4 = Verified data |
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Slight variation with pH: 0.71 days at pH5 & 0.47 days at pH9 | ||||||||||
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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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- | R4 R = Peer reviewed scientific publications 4 = Verified data |
Mobile | |||||||
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General literature states Koc range 35-57 mL g⁻¹ | ||||||||||
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Fate indices |
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Known soil and groundwater metabolites |
None
Other known metabolites |
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oxfendazole (Ref: HOE 8105) | - | - | - |
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Terrestrial ecotoxicology |
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> 10000 | V4 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat4 = Verified data |
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1068 | 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 ) Eisenia foetida4 = Verified data |
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Aquatic ecotoxicology |
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0.04 | F3 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 mykiss3 = Unverified data of known source |
High | ||||||||
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> 0.021 | F3 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 ) Danio rerio EC₅₀ Embryo3 = Unverified data of known source |
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0.0165 | R4 R = Peer reviewed scientific publications Daphnia magna4 = Verified data |
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General |
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High (class III) | - | - | ||||||||
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> 10000 | V4 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat4 = Verified data |
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Intraperitoneal LD₅₀ > 1250 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
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Subcutaneous LD₅₀ > 2000 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
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Slow adsorption, excreted mainly unchanged in the faeces | Q4 Q = Miscellaneous data from online sources 4 = Verified data |
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Health issues |
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No further information available |
Handling issues |
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Light sensitive | |||
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Not listed (Not listed) | |||
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fenbendazole | ||
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fenbendazole | ||
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fenbendazol | ||
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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 |