Ofloxacin |
![]() Last updated: 08/09/2025 |
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(Also known as: floxin; HOE 280) |
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A broad-spectrum antibiotic active against both gram-positive and gram-negative bacterial infections | |
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Used to treat external eye infections such as some types of conjunctivitis | |
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Dogs; Cats |
Approval status |
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Not approved | |
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Not approved |
Chemical structure |
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Ofloxacin exhibits optical isomerism, specifically chirality, due to the presence of an asymmetric carbon atom at the C-3 position of its oxazine ring. This chiral centre gives rise to two enantiomers: the (R)-isomer and the (S)-isomer. The racemic mixture of these two is what’s known as ofloxacin, while the pure (S)-enantiomer is marketed separately as levofloxacin, which has significantly higher antibacterial potency. | |
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C₁₈H₂₀FN₃O₄ | |
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CC1COC2=C3N1C=C(C(=O)C3=CC(=C2N4CCN(CC4)C)F)C(=O)O | |
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No data | |
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GSDSWSVVBLHKDQ-UHFFFAOYSA-N | |
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InChI=1S/C18H20FN3O4/c1-10-9-26-17-14-11(16(23)12(18(24)25)8-22(10)14)7-13(19)15(17)21-5-3-20(2)4-6-21/h7-8,10H,3-6,9H2,1-2H3,(H,24,25) | |
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Yes |
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Common Name | Relationship | Link |
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ofloxacin | - | ![]() |
General status |
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Antibiotic, Bactericide, Medicinal drug | |
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Fluoroquinolone | |
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Synthetic | |
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Inhibits 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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82419-36-1 | |
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Sensory organs: Ophthalmologicals, Otologicals | |
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QS01AX11; QS02AA16 | |
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No | |
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361.37 | |
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(RS)-7-fluoro-2-methyl-6-(4-methylpiperazin-1-yl)-10-oxo-4-oxa-1-azatricyclo[7.3.1.05,13]trideca-5(13),6,8,11-tetraene-11-carboxylic acid | |
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9-fluoro-2,3-dihydro-3-methyl-10-(4-methyl-1-piperazinyl)-7-oxo-7H-pyrido(1,2,3-de)-1,4-benzoxazine-6-carboxylic acid | |
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Evidence of use in third world countries | |
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Solid | |
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Commercial |
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1982, first patented | |||
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Available in a range of formulations for oral, intravenous and topical use | |||
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The production of ofloxacin involves a multi-step chemical synthesis starting from key organic precursors. Initially, compounds like N,N-dimethylamino ethyl acrylate react with aminopropanols in a solvent such as methylbenzene. Protective groups are added using agents like trimethylchlorosilane to shield hydroxyl and amido functionalities, enhancing yield and reducing impurities. The intermediate is then acylated with tetrafluorobenzoyl chloride, followed by acid washing and deprotection. The organic layer is concentrated, and further reactions, often involving dimethylformamide and potassium fluoride, lead to the formation of a difluorocarboxylic acid intermediate. This is finally reacted with N-methylpiperazine in dimethylsulfoxide under controlled heat using triethylamine as a base, yielding Ofloxacin. | |||
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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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28300 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
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254 | 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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1.02 X 1001 | Calculated | - | |||||||
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1.01 | R4 R = Peer reviewed scientific publications 4 = Verified data |
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5.97 | R4 R = Peer reviewed scientific publications 4 = Verified data |
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2.06 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
Low volatility. If applied directly to plants or soil, drift is a concern & mitigation is advisable | ||||||||
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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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Non-mobile | |||||||
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Fate indices |
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Known metabolites |
None
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Terrestrial ecotoxicology |
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3590 | E3 E = Manufacturers safety data sheets Rat3 = Unverified data of known source |
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Aquatic ecotoxicology |
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> 16 | R4 R = Peer reviewed scientific publications Danio rerio 10 day4 = Verified data |
Low | ||||||||
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26.7 | R4 R = Peer reviewed scientific publications Ceriodaphnia dubia4 = Verified data |
Moderate | ||||||||
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10 | R3 R = Peer reviewed scientific publications Ceriodaphnia dubia 7 day3 = Unverified data of known source |
Moderate | ||||||||
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> 1.05 | 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 dubia4 = Verified data |
Moderate | ||||||||
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0.532 | R4 R = Peer reviewed scientific publications Lemna gibba4 = Verified data |
Moderate | ||||||||
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4.74 | R4 R = Peer reviewed scientific publications Raphidocelis subcapitata4 = Verified data |
Moderate | ||||||||
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General |
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High (class III) | - | - | ||||||||
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3590 | E3 E = Manufacturers safety data sheets Rat3 = Unverified data of known source |
Low | ||||||||
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Subcutaneous LD₅₀ = 7070 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
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Intravenous LD₅₀ = 273 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
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65 - 80% of administered oral dose is excreted unchanged via the kidneys within 48 hours of dosing, <8% is excreted in the faeces. These is also a small amount of bilary excretion. | 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 tendon deterioration May cause serious psychiatric side effects May cause sunlight sensitivity |
Handling issues |
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No information available | |||
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Not listed (Not listed) | |||
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ofloxacin | ||
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ofloxacine | ||
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ofloxacino | ||
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Record last updated: | 08/09/2025 |
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 |