| Nifursol |
![]() Last updated: 15/09/2025 |
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(Also known as: Histomon; Nifursolo) |
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A potent and orally active nitrofuran veterinary antibiotic | |
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Used for the management of blackhead (histomoniasis) | |
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Turkeys and other poultry |
| Approval status |
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Not approved | |
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Not approved |
| Chemical structure |
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Nifursol exhibits geometrical (E/Z) isomerism due to the presence of a C=N double bond in its hydrazone linkage. Specifically, the molecule contains a methylene bridge between the 5-nitrofuran ring and the benzohydrazide moiety, forming a (E)-configuration where the bulky groups are positioned opposite each other across the double bond. | |
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C₁₂H₇N₅O₉ | |
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C1=C(OC(=C1)[N+](=O)[O-])C=NNC(=O)C2=CC(=CC(=C2O)[N+](=O)[O-])[N+](=O)[O-] | |
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C1=C(OC(=C1)[N+](=O)[O-])/C=N/NC(=O)C2=CC(=CC(=C2O)[N+](=O)[O-])[N+](=O)[O-] | |
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XXUXXCZCUGIGPP-WLRTZDKTSA-N | |
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InChI=1S/C12H7N5O9/c18-11-8(3-6(15(20)21)4-9(11)16(22)23)12(19)14-13-5-7-1-2-10(26-7)17(24)25/h1-5,18H,(H,14,19)/b13-5+ | |
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Yes |
| General status |
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Antibiotic, Feed additive, Prophylactic drug, Coccidiostat | ||||||||||||||
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Nitrofuran drug | ||||||||||||||
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>98% | ||||||||||||||
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Synthetic | ||||||||||||||
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Inhibits the growth of Histomonas meleagridis, Nifursol targets DNA within anaerobic protozoa and bacteria. Its mechanism involves enzymatic reduction of the nitrofuran moiety by microbial enzymes, especially nitroreductases, which generates reactive intermediates. These intermediates form covalent bonds with DNA, leading to strand breaks, inhibition of replication, and cell death. | ||||||||||||||
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[Nitroreductases, Reduction] | ||||||||||||||
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16915-70-1 | ||||||||||||||
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240-963-6 | ||||||||||||||
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Antiparasitic products, insecticides & repellents: Other antiprotozoal agents | ||||||||||||||
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QP51AX05 | ||||||||||||||
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No | ||||||||||||||
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365.21 | ||||||||||||||
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2-hydroxy-3,5-dinitro-N'-[(5-nitrofuran-2-yl)methylidene]benzohydrazide | ||||||||||||||
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3,5-dinitro-n'-(5-nitrofurfurylidene)salicylohydrazide | ||||||||||||||
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Yellow solid | ||||||||||||||
| Commercial |
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1960s, introduced | |||
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Typically formulated as a widely as a feed additive or a prophylactic drug | |||
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The synthesis of nifursol begins with the preparation of its two key components: a 5-nitrofuran derivative and a dinitrosalicylic acid hydrazide. First, the nitrofuran ring is functionalized at the 2-position to introduce a reactive aldehyde or methylene group. Separately, dinitrosalicylic acid is converted into its hydrazide form through reaction with hydrazine. These two intermediates are then condensed via a hydrazone formation reaction, where the hydrazide reacts with the aldehyde group to form a C=N double bond, yielding the final nifursol molecule. | |||
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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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215 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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1.87 | Q3 Q = Miscellaneous data from online sources 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. | ||||||||||
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8.4 | 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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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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| Fate indices |
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| Known metabolites |
None
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| Terrestrial ecotoxicology |
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> 10000 | Q3 Q = Miscellaneous data from online sources Rat3 = Unverified data of known source |
Low | ||||||||
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> 10 | 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 |
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| General |
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High (class III) | - | - | ||||||||
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> 10000 | Q3 Q = Miscellaneous data from online sources Rat3 = Unverified data of known source |
Low | ||||||||
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Rapidly metabolized. In rats 80-85% appears in the faeces and 11% in the urine within 24 hours. Residues detected in foodstuffs | 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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Light sensitive | |||
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Not listed (Not listed) | |||
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nifursol | ||
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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 |
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