Enrofloxacin (Ref: BAY VP 2674) |
![]() Last updated: 15/09/2025 |
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(Also known as: BRN 5307824) |
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A broad-spectrum bactericidal antibiotic used in veterinary medicine | |
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Used to treat domesticated animals for a variety of infections including E.coli., Enterobacter, Campylobacter, Shigella and Salmonella | |
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Domestic animals including: Dogs, Cats, Rabbits, Horses. May also be used on Reptiles, Poultry, Swine and Cattle. |
Approval status |
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Approved - usually available as a prescription only medicine to be authorised by a veterinarian (POM-V) | |
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Approved |
Chemical structure |
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Enrofloxacin primarily exhibits conformational isomerism, meaning its flexible molecular structure allows it to adopt different spatial arrangements due to rotation around single bonds. Though not optically active in solution, it can form racemic crystals containing equal amounts of left- and right-handed conformers. | |
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C₁₉H₂₂FN₃O₃ | |
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CCN1CCN(CC1)C2=C(C=C3C(=C2)N(C=C(C3=O)C(=O)O)C4CC4)F | |
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No data | |
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SPFYMRJSYKOXGV-UHFFFAOYSA-N | |
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InChI=1S/C19H22FN3O3/c1-2-21-5-7-22(8-6-21)17-10-16-13(9-15(17)20)18(24)14(19(25)26)11-23(16)12-3-4-12/h9-12H,2-8H2,1H3,(H,25,26) | |
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Yes |
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Common Name | Relationship | Link |
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enrofloxacin | - | ![]() |
General status |
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Antibiotic, Chemotherapeutic agent, Medicinal drug, Bactericide | |
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Fluoroquinolone | |
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Synthetic | |
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Not clear but believed to act by inhibiting bacterial DNA gyrase | |
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[DNA gyrase subunit A, Antagonist], [DNA topoisomerase 2-alpha, Antagonist] | |
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93106-60-6 | |
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Antiinfectants for systemic use: Antibacterials for systemic use | |
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QJ01MA90 | |
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No | |
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Allowed substance (Table 1: All food producing species) | |
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359.4 | |
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1,4-dihydro-1-cyclopropyl-7-(4-ethyl-1-piperazinyl)-6-fluoro-4-oxo-3-quinolinecarboxylic acid | |
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1-cyclopropyl-7-(4-ethyl-1-piperazinyl)-6-fluoro-1,4-dihydro-4-oxo-3-quinolinecarboxylic acid | |
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Pale yellow crystalline powder | |
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Commercial |
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Current | |||
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1980s, developed; 2005, restricted use EU | |||
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Available in a variety of formulations including solution for injection, powder, additives for feed and drinking water, and tablets | |||
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The production of enrofloxacin involves a multi-step chemical synthesis starting with 7-chloro-1-cyclopropyl-6-fluoro-4-oxo-1,4-dihydroquinoline-3-carboxylic acid, which is reacted with N-ethylpiperazine in the presence of a catalyst such as nano iron oxide on sulphonated zirconia. This reaction is typically carried out under reflux conditions in water, and monitored using thin-layer chromatography to track progress. Once complete, the catalyst is removed and the mixture is cooled to precipitate the product. The solid is then filtered, washed with ethanol, and recrystallised from methanol to yield high-purity enrofloxacin. | |||
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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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250 | 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 ) at 25 °C4 = Verified data |
Moderate | ||||||||
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220 | 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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5.01 X 1004 | Calculated | - | |||||||
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4.7 | R4 R = Peer reviewed scientific publications 4 = Verified data |
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6.21 | R4 R = Peer reviewed scientific publications 4 = Verified data |
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2.53 X 10-08 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
Low volatility | ||||||||
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3.2 X 10-08 | R4 R = Peer reviewed scientific publications 4 = Verified data |
Non-volatile | ||||||||
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Max @ 270+1nm and 314+2nm | R4 R = Peer reviewed scientific publications 4 = Verified data |
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Identified in pig and poultry manure at high concentrations implying manure implying a major release route |
Degradation |
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123 | 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 |
Persistent | |||||||
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297 | 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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DT₅₀ range 99-149 days, DT₉₀ range 330-495 days; Industry data DT₅₀ 359-696 days (R3) | ||||||||||
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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 |
Non-mobile | |||||||
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392600 | ||||||||||
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Koc range 16506-768740 mL g⁻¹ | ||||||||||
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Fate indices |
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-3.94 | Calculated | Low leachability | ||||||||||||||||||||||||||
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Known soil and groundwater metabolites |
None
Other known metabolites |
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ciprofloxacin (Ref: BRN 3568352) | - | Animal (Urine and faecal) | - | ||||
enrofloxacin amide | - | Animal (Urine and faecal) | - |
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Terrestrial ecotoxicology |
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> 5000 | Q3 Q = Miscellaneous data from online sources Rat3 = Unverified data of known source |
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Aquatic ecotoxicology |
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> 10 | E3 E = Manufacturers safety data sheets Lepomis macrochirus3 = Unverified data of known source |
Moderate | ||||||||
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~ 1 | 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 ) Pimephales promelas 7 day3 = Unverified data of known source |
Moderate | ||||||||
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> 100 | E3 E = Manufacturers safety data sheets Daphnia magna3 = Unverified data of known source |
Low | ||||||||
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~ 1.0 | 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 ) Daphnia magna 48 hr3 = Unverified data of known source |
Moderate | ||||||||
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> 3 | 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 ) Ceriodaphnia dubia LC₅₀4 = Verified data |
Moderate | ||||||||
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> 0.084 | 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 ) Lemna gibba4 = Verified data |
Moderate | ||||||||
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> 2.6 | 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 ) Raphidocelis subcapitata4 = Verified data |
Moderate | ||||||||
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General |
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High (class III) | - | - | ||||||||
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> 5000 | Q3 Q = Miscellaneous data from online sources Rat3 = Unverified data of known source |
Low | ||||||||
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2000 | Q3 Q = Miscellaneous data from online sources Rat3 = Unverified data of known source |
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> 35.47 | Q3 Q = Miscellaneous data from online sources Rat 4 hr3 = Unverified data of known source |
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Intravenous LD₅₀ = 200 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Mouse3 = Unverified data of known source |
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Eliminated by both renal and hepatic metabolism | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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Health issues |
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May cause gastrointestinal disturbances |
Handling issues |
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Light sensitive | |||
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Not listed (Not listed) | |||
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enrofloxacin | ||
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enrofloxacine | ||
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enrofloxacino | ||
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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 |