Oxfendazole (Ref: HOE 8105) |
![]() Last updated: 15/09/2025 |
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(Also known as: OFDZ; RS-8858) |
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A benzimidazole anthelmintic active against both adults and laval stages of parasitic worms | |
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Used for the management roundworms, strongyles and pinworms | |
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Sheep; Cattle; Goats; Pigs; Horses |
Approval status |
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Approved - usually avilable 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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Oxfendazole exhibits enantiomeric isomerism, meaning it exists as (+)-oxfendazole and (–)-oxfendazole enantiomers. These isomers differ in the spatial arrangement around the chiral centre in the benzimidazole ring system, which can influence their pharmacokinetics and biological activity. Commercially available oxfendazole is typically a racemic mixture. | |
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C₁₅H₁₃N₃O₃S | |
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COC(=O)NC1=NC2=C(N1)C=C(C=C2)S(=O)C3=CC=CC=C3 | |
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No data | |
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BEZZFPOZAYTVHN-UHFFFAOYSA-N | |
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InChI=1s/C15H13N3O3S/c1-21-15(19)18-14-16-12-8-7-11(9-13(12)17-14)22(20)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 | |
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Benzimidazole | |
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Synthetic | |
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Inhibits tubulin synthesis in the parasite and leading to death by starvation. | |
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[Tubulin beta chain, Antagonist] | |
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53716-50-0 | |
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258-714-5 | |
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Antiparasitic products, insecticides & repellents: Anthelmintics | |
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QP52AC02 | |
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No | |
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Allowed substance (Table 1: Ruminants, Porcine, Equidae) | |
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315.35 | |
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(5-(phenylsulfinyl)-1H-benzimidazol-2-yl)carbamic acid methyl ester | |
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methyl-5-(phenylsulfinyl) benzimidazole-2-carbamate | |
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White to off-white powder |
Commercial |
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Current | |||
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Circa 1980, registered for veterinary use USA | |||
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Available in a variety of formulations including pour-ons, drenches, oral suspensions and pulsatile-release intraruminal devices | |||
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The production of oxfendazole involves the oxidation of fenbendazole, a structurally related benzimidazole compound. The process begins with fenbendazole, which contains a phenylthio group, undergoing a controlled oxidation using hydrogen peroxide in the presence of a strong, non-oxidising mineral acid and a C₁–C₆ aliphatic alcohol as a solvent or co-solvent. This reaction selectively converts the phenylthio group into a phenylsulfinyl moiety, yielding oxfendazole. | |||
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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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3.11 | 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 ) 3 = Unverified data of known source |
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245 | 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 ) 3 = Unverified data of known source |
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8.91 X 1001 | Calculated | - | |||||||
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1.95 | 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 ) 3 = Unverified data of known source |
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Main environmental release is via the slurry and manure from treated livestock |
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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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8.87 | 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 ) 3 = Unverified data of known source |
Slightly mobile | |||||||
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885 | ||||||||||
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USEPA data: Kd range 3.87-16.73 mL g⁻¹, Koc range 470-1673 mL g⁻¹, Soils=3 | ||||||||||
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8.87 | 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 ) 3 = Unverified data of known source |
Slightly mobile | |||||||
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0.9 | ||||||||||
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USEPA data: Kf range 4.5-15.7 mL g⁻¹, Kfoc range 544-1570 mL g⁻¹, 1/n range 0.87-0.93, Soils=3 | ||||||||||
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Fate indices |
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Known soil and groundwater metabolites |
None
Other known metabolites |
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2-amino-5(6)-phenylsulfinyl benzimidazole | oxfendazole amine | Hydrolysis | - |
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Terrestrial ecotoxicology |
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> 6400 | A4 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) Rat4 = Verified data |
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> 971 | R4 R = Peer reviewed scientific publications Eisenia foetida4 = Verified data |
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Aquatic ecotoxicology |
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> 2.7 | R4 R = Peer reviewed scientific publications Lepomis macrochirus4 = Verified data |
Moderate | ||||||||
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> 5.6 | 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 |
Moderate | ||||||||
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1.17 | 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 ) Daphnia magna4 = Verified data |
Moderate | ||||||||
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General |
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High (class III) | - | - | ||||||||
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> 6400 | A4 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) Rat4 = Verified data |
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Metabolised to active oxfendazole sulfoxide and sulfone. Excreted mainly in faeces. | 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 listed (Not listed) | |||
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oxfendazole | ||
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oxfendazole | ||
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oxfendazol | ||
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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 |