Halofuginone hydrobromide |
Last updated: 23/02/2024 |
(Also known as: halofuginone HBr) |
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A quinazoline anti-coccidial drug with veterinary applications. The active substance was originally obtained by modification of a substance isolated from Dichroa febrifuqa | |
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Current | |
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early 1980s, introduced; 1986, registered USA | |
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Used for the prevention of diarrhoea due to diagnosed Cryptosporidium parvum | |
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Poultry; Cattle (calves) |
Approval status |
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Approved | |
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Approved |
Chemical structure |
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Isomeric | |
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C₁₆H₁₈Br₂ClN₃O₃ | |
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C1CC(C(NC1)CC(=O)CN2C=NC3=CC(=C(C=C3C2=O)Cl)Br)O.Br | |
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C1C[C@@H]([C@H](NC1)CC(=O)CN2C=NC3=CC(=C(C=C3C2=O)Cl)Br)O.Br | |
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SJUWEPZBTXEUMU-LIOBNPLQSA-N | |
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InChI=1S/C16H17BrClN3O3.BrH/c17-11-6-13-10(5-12(11)18)16(24)21(8-20-13)7-9(22)4-14-15(23)2-1-3-19-14;/h5-6,8,14-15,19,23H,1-4,7H2;1H/t14-,15+;/m1./s1 | |
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Yes |
General status |
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Coccidiostat, Antiprotozoal, Feed additive | |
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Quinazolinone | |
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Semi-synthetic | |
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Inhibits the development of T helper 17 cells that influence immune function | |
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[Growth factor - Beta (TGF-Beta), Inhibitor] | |
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64924-67-0 | |
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57426-42-3 | |
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694-602-6 | |
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11591339 | |
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Antiparasitic products, insecticides & repellents: Antiprotozoals | |
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QP51AX08 | |
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No | |
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Allowed substance (Table 1: Bovine) | |
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495.6 | |
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7-bromo-6-chloro-3-[3-[(2R,3S)-3-hydroxypiperidin-2-yl]-2-oxopropyl]quinazolin-4-one; hydrobromide | |
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Yellow liquid | |
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Formulations |
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Usually formulated as a medicated pre-mix |
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3.0 | 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 |
Low | ||||||||
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294 | 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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294 | 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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Maxima at 243nm, 275nm, 300nm, 313nm & 326nm | - | - | ||||||||
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Degradation |
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43 | 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 |
Moderately persistent | ||||||||
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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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34.7 | 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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3855 | ||||||||||
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USEPA data: Kd range 22-51.8 mL g⁻¹, Koc range 1515-3855 mL g⁻¹, Soils=3 | ||||||||||
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Fate indices |
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0.68 | Calculated | Low leachability | ||||||||||||||||||||||||||
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Known metabolites |
None
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Terrestrial ecotoxicology |
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F4 Mouse, as halofuginone 4.4 | - | High | ||||||||
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17.6 | 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 ) Gallus gallus domesticus as halofuginone3 = Unverified data of known source |
High | ||||||||
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> 21.0 | A3 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 ) Lumbricus terrestris NOEL lactate salt3 = Unverified data of known source |
Moderate | ||||||||
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Aquatic ecotoxicology |
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0.12 | 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 ) Lepomis macrochirus as halofuginone3 = Unverified data of known source |
Moderate | ||||||||
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0.02 | 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 ) Daphnia magna as halofuginone3 = Unverified data of known source |
High | ||||||||
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General |
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High (class III) | - | - | ||||||||
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F4 Mouse, as halofuginone 4.4 | - | High | ||||||||
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Around 80% of dose is eliminated in faeces within a week. Some residues also identified in bile. | 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 ) 4 = Verified data |
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Health issues |
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Possible liver and kideny toxicant |
Handling issues |
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No information available | |||
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Not listed (Not listed) | |||
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halofuginone hydrobromide | ||
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Record last updated: | 23/02/2024 |
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 |