Norfloxacin |
![]() Last updated: 06/09/2025 |
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(Not known by any other names) |
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Broad spectrum antiobiotic drug active against both gram-positive and gram-negative bacteria | |
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Mainly used to treat urinary tract, respiratory and other infectious diseases | |
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Sheep; Pigs; Dogs; Cats |
Approval status |
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Not approved | |
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Not approved |
Chemical structure |
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Norfloxacin primarily exhibits polymorphism, a type of isomerism where the same chemical compound can crystallise into different solid forms. These polymorphs, known as Form A, Form B, and Form C, have distinct molecular packing arrangements and physical properties such as solubility, melting point, and stability. Notably, Form B is the most stable at room temperature, while Form A is metastable and can transform into Form B under certain conditions, demonstrating an enantiotropic relationship. | |
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C₁₆H₁₈FN₃O₃ | |
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CCN1C=C(C(=O)C2=CC(=C(C=C21)N3CCNCC3)F)C(=O)O | |
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No data | |
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OGJPXUAPXNRGGI-UHFFFAOYSA-N | |
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InChI=1S/C16H18FN3O3/c1-2-19-9-11(16(22)23)15(21)10-7-12(17)14(8-13(10)19)20-5-3-18-4-6-20/h7-9,18H,2-6H2,1H3,(H,22,23) | |
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Yes |
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Common Name | Relationship | Link |
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norfloxacin | - | ![]() |
General status |
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Antibiotic, Antibacterial, Chemotherapy drug, Medicinal drug | |
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Fluoroquinolone | |
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Synthetic | |
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Inhibits bacterial DNA gyrase | |
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[DNA topoisomerase 4 subunit A, Antagonist], [DNA gyrase subunit A, Antagonist], [DNA topoisomerase 2-alpha, Antagonist] | |
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70458-96-7 | |
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274-614-4 | |
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Antiinfectants for systemic use: Antibacterials for systemic use | |
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QJ01MA06 | |
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No | |
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319.33 | |
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1-ethyl-6-fluoro-4-oxo-7-piperazin-1-yl-1H-quinoline-3-carboxylic acid | |
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1,4-dihydro-1-ethyl-6-fluoro-4-oxo-7-(1-piperazinyl)-3-quinolinecarboxylic acid | |
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Evidence of use in third world countries | |
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White to pale yellow crystalline powder |
Commercial |
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1979, first patent | |||||||||
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The production of norfloxacin involves a multi-step synthetic process based around constructing its fluoroquinolone core. It begins with the preparation of key intermediates such as 3,4-difluoroaniline, which is reacted to form 6-fluoro-3,4-dihydro-4-oxoquinoline, a crucial building block. This intermediate undergoes cyclisation to establish the quinolone ring system, followed by the introduction of the piperazine moiety through nucleophilic substitution using piperazine under controlled temperature and pH conditions. | |||||||||
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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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178000 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
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980 | L3 L = Pesticide manuals and hard copy reference books / other sources Methanol3 = Unverified data of known source |
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1900 | L3 L = Pesticide manuals and hard copy reference books / other sources Ethanol3 = Unverified data of known source |
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5100 | L3 L = Pesticide manuals and hard copy reference books / other sources Acetone3 = Unverified data of known source |
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5500 | L3 L = Pesticide manuals and hard copy reference books / other sources Chloroform3 = Unverified data of known source |
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227 | 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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8.51 X 1000 | Calculated | - | |||||||
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0.93 | R4 R = Peer reviewed scientific publications 4 = Verified data |
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6.26 | R4 R = Peer reviewed scientific publications 4 = Verified data |
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pKa(2) = 8.75 | |||||||||||
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9.00 X 10-08 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
Low volatility | ||||||||
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In NaOH: 274nm, 325nm, 336nm | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
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Degradation |
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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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Fate indices |
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Known metabolites |
None
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Terrestrial ecotoxicology |
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> 4000 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
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Aquatic ecotoxicology |
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> 2 | 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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16.6 | R4 R = Peer reviewed scientific publications Raphidocelis subcapitata4 = Verified data |
Low | ||||||||
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4.01 | R4 R = Peer reviewed scientific publications Raphidocelis subcapitata4 = Verified data |
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General |
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High (class III) | - | - | ||||||||
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> 4000 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
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Subcutaneous LD₅₀ > 1500 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
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Intravenous LD₅₀ = 245 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
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Eliminated through metabolism, biliary excretion, and renal excretion. | 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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Health issues |
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Possible kidney, liver and renal toxicant |
Handling issues |
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Hygroscopic in air | |||
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Not listed (Not listed) | |||
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norfloxacin | ||
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norfloxacine | ||
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norfloxacino | ||
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Record last updated: | 06/09/2025 |
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 |