| Flubendazole |
![]() Last updated: 16/09/2025 |
![]() |
(Not known by any other names) |
|
|
|
A broad spectrum anthelmintic used in veterinary medicine | |
|---|---|---|
|
Used to treat worm infestations | |
|
Poultry; Pigs; Dogs |
| Approval status |
|
Approved - usually supplied as a prescription only medicine to be authorised by a veterinarian (POM-V) | |
|---|---|---|
|
Approved |
| Chemical structure |
|
None | |
|---|---|---|
|
C₁₆H₁₂FN₃O₃ | |
|
COC(=O)NC1=NC2=C(N1)C=C(C=C2)C(=O)C3=CC=C(C=C3)F | |
|
- | |
|
CPEUVMUXAHMANV-UHFFFAOYSA-N | |
|
InChI=1S/C16H12FN3O3/c1-23-16(22)20-15-18-12-7-4-10(8-13(12)19-15)14(21)9-2-5-11(17)6-3-9/h2-8H,1H3,(H2,18,19,20,22) | |
|
Yes |
|
|
| Common Name | Relationship | Link |
|---|---|---|
| flubendazole | - | ![]() |
| General status |
|
Anthelmintic | ||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
Benzimidazole drug | ||||||||||||||
|
- | ||||||||||||||
|
- | ||||||||||||||
|
- | ||||||||||||||
|
Binds to tubulin, a protein required for functions including nutrient uptake, thus disrupting parasite energy metabolism | ||||||||||||||
|
[Tubulin alpha-3 chain, Antagonist] | ||||||||||||||
|
31430-15-6 | ||||||||||||||
|
250-624-4 | ||||||||||||||
|
- | ||||||||||||||
|
- | ||||||||||||||
|
35802 | ||||||||||||||
|
Anthelmintics: Benzimidazoles and related substances | ||||||||||||||
|
QP52AC12 | ||||||||||||||
|
No | ||||||||||||||
|
- | ||||||||||||||
|
313.288 | ||||||||||||||
|
methyl N-[6-(4-fluorobenzoyl)-1H-benzimidazol-2-yl]carbamate | ||||||||||||||
|
methyl N-[6-(4-fluorobenzoyl)-1H-benzimidazol-2-yl]carbamate | ||||||||||||||
|
- | ||||||||||||||
|
|
||||||||||||||
|
- | ||||||||||||||
|
- | ||||||||||||||
|
Current | ||||||||||||||
|
White powdery solid | ||||||||||||||
| Commercial |
|
|
|||
|---|---|---|---|---|
|
Not applicable | |||
|
1980s, first approvals; 1990s, vet use expanded | |||
|
|
|||
|
|
|||
|
Usually formulated as a solution for drinking water or as a medicated feed. | |||
|
The production of flubendazole begins with the synthesis of the core benzimidazole ring, typically via condensation of o-phenylenediamine with a carboxylic acid derivative such as formic acid or its esters. To create flubendazole specifically, the benzimidazole nucleus is first functionalized with a benzyl group at the 5-position. This intermediate is then reacted with ethyl 2-(2,4-dichlorophenyl)acetate, introducing the essential side chain through a nucleophilic substitution or acylation reaction. The resulting compound undergoes cyclisation to form the final flubendazole structure, followed by purification steps such as recrystallisation or chromatography to ensure pharmaceutical-grade purity. | |||
|
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. |
|
|
|
|
|
|
||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
243 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
- | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
| - | |||||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
Flubendazole may enter the environment via the faeces of treated animals or by leaching from spilt medicated feed | ||||||||||
| Degradation |
|
|
|
|
||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | ||||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
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. | ||||||||||
|
- | ||||||||||
| Soil adsorption and mobility |
|
|
|
|
||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | ||||||||||
|
- | ||||||||||
|
- | ||||||||||
| Fate indices |
|
|
|
|
||||||||||||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
- | - | - | ||||||||||||||||||||||||||
|
|
- | - | - | |||||||||||||||||||||||||
|
- | - | |||||||||||||||||||||||||||
| Known metabolites |
None
|
|
| Terrestrial ecotoxicology |
|
|
|
|
||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
|
> 5000 | F5 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 ) Rat5 = Verified data used for regulatory purposes |
Low | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
| - | |||||||||||
|
- | - | - | ||||||||
| - | |||||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- |
|
- | - | - | ||||||
|
- | ||||||||||
| Aquatic ecotoxicology |
|
|
|
|
||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
0.204 | 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 ) Danio rerio as EC₅₀ Larvae4 = Verified data |
Moderate | ||||||||
|
> 0.055 | 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 |
High | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - |
|
- | - | - | |||
|
- | - | - | ||||||||
|
|
| General |
|
|
|
|
||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
|
- | - | - | ||||||||
|
> 5000 | F5 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 ) Rat5 = Verified data used for regulatory purposes |
Low | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | |||||||||
|
- | ||||||||||
|
Most of the applied drug is eliminated unchanged in the faeces | Q4 Q = Miscellaneous data from online sources 4 = Verified data |
- | ||||||||
| Health issues |
|
|
||||||||||||||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
No further information available | ||||||||||||||||||||||||||||
| Handling issues |
|
|
|||
|---|---|---|---|---|
|
Incompatible with oxidising agents | |||
|
- | |||
|
Not listed (Not listed) | |||
|
Not regulated | |||
|
- | |||
|
- |
|
|
|
|
||
|---|---|---|---|
|
flubendazole | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- |
| Record last updated: | 16/09/2025 |
| 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 |
© Copyright University of Hertfordshire, 2006-2026. All Rights Reserved
Your use of this website and its various databases is subject to the terms detailed in the University of Hertfordshire’s copyright and IPR statement that can be found at https://www.herts.ac.uk/about-us/legal. In addition, your use of this website and its various databases is subject to the terms of this additional Copyright Statement and the database Conditions of use document. Unless explicitly stated otherwise, the content of this website and databases are owned and controlled by the University of Hertfordshire. Site content, including its selection and arrangement, is owned by the University of Hertfordshire and is protected by copyright and other laws. Except as otherwise expressly permitted under copyright law or within the database Conditions of Use document, the content of this site may not be copied, reproduced, republished, downloaded, posted, broadcast or transmitted in any way without first obtaining the University of Hertfordshire’s written permission. By using our databases the user is deemed to have agreed to comply with all of the terms and conditions as described above and within all relevant documentation.





