Thiamphenicol |
![]() Last updated: 16/09/2025 |
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(Also known as: thiophenicol; dextrosulphenidol; Win 5063-2; thiocymetin) |
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A broad spectrum antimicrobial and immunosuppressive substance intended for the treatment of cutaneous infections | |
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Used to treat superficial wound infections such as infectious conjunctivitis, claw and hoof rot, dermatitis | |
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Cattle; Pigs; Poultry; Horses; Goats; Sheep; Mink; Rabbits |
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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Thiamphenicol exhibits stereoisomerism, specifically diastereomerism, due to the presence of two chiral centres in its molecular structure. These chiral centres are located on the propanediol side chain, which connects to the dichloroacetamide and the methylsulfonylphenyl groups. The clinically active form of thiamphenicol is the D-threo isomer, where the two hydroxyl groups on the propanediol moiety are in a specific spatial arrangement that enhances its antibacterial activity. Other stereoisomers, such as the L-threo or erythro forms, may exist but are either inactive or significantly less potent. | |
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C₁₂H₁₅Cl₂NO₅S | |
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CS(=O)(=O)C1=CC=C(C=C1)C(C(CO)NC(=O)C(Cl)Cl)O | |
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CS(=O)(=O)C1=CC=C(C=C1)[C@H]([C@@H](CO)NC(=O)C(Cl)Cl)O | |
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OTVAEFIXJLOWRX-NXEZZACHSA-N | |
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InChI=1S/C12H15Cl2NO5S/c1-21(19,20)8-4-2-7(3-5-8)10(17)9(6-16)15-12(18)11(13)14/h2-5,9-11,16-17H,6H2,1H3,(H,15,18)/t9-,10-/m1/s1 | |
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Yes |
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Common Name | Relationship | Link |
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thiamphenicol | - | ![]() |
General status |
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Antibiotic, Antimicrobial | |
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Unclassified substance | |
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Synthetic | |
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Peptidyl transferase - inhibits protein synthesis in bacteria. | |
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[Dr hemagglutinin structural subunit, Inhibitor] | |
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15318-45-3 | |
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239-355-3 | |
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Antiinfectants for systemic use: Amphenicols | |
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QJ01BA52 | |
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No | |
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Allowed substance (Table 1: All food producing species) | |
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356.22 | |
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2,2-dichloro-N-{(1R,2R)-2-hydroxy-1-(hydroxymethyl)-2-[4-(methylsulfonyl)phenyl]ethyl}acetamide | |
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2-dichloroacetamido-1-(4-methylsulfonylphenyl)-1,3-propanediol | |
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White crystalline powder | |
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Commercial |
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Current | |||
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1955, first synthesis & introduction; 2000s, wide approval globally | |||
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Formulated for topical appliaction such as sprays and gels | |||
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The production of thiamphenicol involves a multi-step chemical synthesis starting from a suitable precursor such as p-methylsulfonylphenylacetic acid. The process typically includes reduction, acylation, and recrystallisation steps. In modern industrial methods, a tubular reactor is often used to carry out the reduction and acylation reactions efficiently, minimizing impurity formation and improving yield. The dichloroacetyl group is introduced via acylation, and the final product is purified through distillation, dissolving, filtering, and recrystallisation to ensure high purity and stereochemical integrity. | |||
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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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5.00 | 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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50 | Q3 Q = Miscellaneous data from online sources Methanol3 = Unverified data of known source |
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20 | Q3 Q = Miscellaneous data from online sources Ethanol3 = Unverified data of known source |
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1.0 | Q3 Q = Miscellaneous data from online sources Ethyl acetate3 = Unverified data of known source |
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1.0 | Q3 Q = Miscellaneous data from online sources Chloroform3 = Unverified data of known source |
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164 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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4.68 X 10-01 | Calculated | - | |||||||
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-0.33 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 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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Low risk | Q3 Q = Miscellaneous data from online sources Based on LogP < 33 = Unverified data of known source |
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Known metabolites |
None
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Terrestrial ecotoxicology |
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> 3000 | 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 ) Rat4 = Verified data |
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Aquatic ecotoxicology |
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8.86 | R4 R = Peer reviewed scientific publications Raphidocelis subcapitata4 = Verified data |
Moderate | ||||||||
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4.06 | 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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> 3000 | 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 ) Rat4 = Verified data |
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Intravenous LD₅₀ = 339 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
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Intraperitoneal LD₅₀ > 5000 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
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Thiamphenicol is excreted in the urine largely in unchanged | 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 testes, bone marrow, liver & kidney toxicant Harmful if swallowed May cause gastrointestinal problems |
Handling issues |
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No information available | |||
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Not listed (Not listed) | |||
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thiamphenicol | ||
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tiamfenicol | ||
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Record last updated: | 16/09/2025 |
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 |