Sulphadimidine |
![]() Last updated: 06/09/2025 |
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(Also known as: sulfadimidine; sulfamethazine) |
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A Ssulfonamide drug used in veterinary medicine often in combination with chlortetracycline and penicillin | |
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Multiple uses including for the treatment of bovine respiratory disease, calf diphtheria, bacterial pneumonia and procine colibacillosis as wel as coccidiosis, fowl cholera and pullorum disease. | |
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Pigs; Fowl; Cattle; Sheep |
Approval status |
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Not approved | |
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Not approved |
Chemical structure |
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Sulphadimidine exhibits tautomeric isomerism, a form of structural isomerism where the molecule can exist in equilibrium between two or more isomeric forms due to the migration of a proton and a shift in bonding. Specifically, the sulfonamide group (-SO₂NH-) and the pyrimidine ring allow for tautomeric shifts between amino and imino forms, particularly under varying pH conditions. | |
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C₁₂H₁₄N₄O₂S | |
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CC1=CC(=NC(=N1)NS(=O)(=O)C2=CC=C(C=C2)N)C | |
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No data | |
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ASWVTGNCAZCNNR-UHFFFAOYSA-N | |
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InChI=1S/C12H14N4O2S/c1-8-7-9(2)15-12(14-8)16-19(17,18)11-5-3-10(13)4-6-11/h3-7H,13H2,1-2H3,(H,14,15,16) | |
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Yes |
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Common Name | Relationship | Link |
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sulphadimidine | - | ![]() |
General status |
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Antibacterial, Anti-infective, Antibiotic, Antimicrobial, Medicinal drug | |
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Sulfonamide | |
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Synthetic | |
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A competitive inhibitor of dihydropteroate synthase | |
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[Dihydropteroate synthetase, Antagonist] | |
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57-68-1 | |
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200-346-4 | |
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Antiparasitic products, insecticides & repellents: Antiprotozoals; Antiinfectants for systemic use: Antibacterials for systemic use | |
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QP51AG01; QJ01EQ | |
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No | |
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Allowed substance (Table 1: All food producing species) | |
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278.33 | |
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- | |
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4-amino-N-(4,6-dimethylpyrimidin-2-yl)benzenesulfonamide | |
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4,6-dimethyl-2-sulfanilamidopyrimidine | |
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Possible groundwater contaminant | |
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White crystalline powder |
Commercial |
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Current | |||||||||
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1941, first reported | |||||||||
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Intradine 30.89% w/v Solution for Injection | Norbrook Laboratories Ltd | Not licensed | Not licensed | ||||||
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Often supplied as a solution for injection or a solution for oral administration | |||||||||
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The synthesis of sulphadimidine typically begins with the formation of the p-aminobenzenesulfonamide core, which is then coupled with a 2-amino-4,6-dimethylpyrimidine derivative. The process involves a nucleophilic substitution reaction, where the sulfonamide nitrogen attacks the electrophilic carbon on the pyrimidine ring, forming the key N–C bond that links the two moieties. This reaction is usually carried out under controlled temperature and pH conditions to ensure selectivity and yield. The crude product is then purified through recrystallisation or chromatographic techniques. | |||||||||
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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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1500 | A5 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 ) at 29 °C5 = Verified data used for regulatory purposes |
High | ||||||||
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198.5 | A5 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 ) 5 = Verified data used for regulatory purposes |
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452 | A3 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 ) 3 = Unverified data of known source |
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1.55 X 1000 | Calculated | - | |||||||
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0.19 | A5 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 ) 5 = Verified data used for regulatory purposes |
Low | ||||||||
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7.59 | R4 R = Peer reviewed scientific publications 4 = Verified data |
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9.09 X 10-04 | A5 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 ) 5 = Verified data used for regulatory purposes |
Low volatility | ||||||||
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3.09 X 10-11 | R4 R = Peer reviewed scientific publications 4 = Verified data |
Non-volatile | ||||||||
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Acidic: max at 241nm and 297nm Neutral: max at 241nm Basic: max at 243nm and 257nm |
V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
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15044 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
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Degradation |
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18.6 | R4 R = Peer reviewed scientific publications 4 = Verified data |
Non-persistent | |||||||
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General literature suggests biodegradation may be slow in some soils. | ||||||||||
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- | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
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Hydolysis not expected | ||||||||||
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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 |
Moderately mobile | |||||||
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115.3 | ||||||||||
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General literature Kd range 0.9-3.5 mL g⁻¹, Koc values range 61-170 mL g⁻¹ | ||||||||||
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Fate indices |
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2.46 | Calculated | Transition state | ||||||||||||||||||||||||||
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Known soil and groundwater metabolites |
None
Other known metabolites |
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N4-acetylated sulfonamide | - | Human (Liver) | - |
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Terrestrial ecotoxicology |
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> 2000 | Q3 Q = Miscellaneous data from online sources Mouse3 = Unverified data of known source |
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Aquatic ecotoxicology |
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> 100 | A5 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 ) Oryzias latipes5 = Verified data used for regulatory purposes |
Low | ||||||||
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31.4 | A5 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 ) Daphnia magna5 = Verified data used for regulatory purposes |
Moderate | ||||||||
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8.7 | 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 ) Raphidocelis subcapitata4 = Verified data |
Moderate | ||||||||
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1.0 | 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 ) Raphidocelis subcapitata4 = Verified data |
Moderate | ||||||||
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General |
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High (class III) | - | - | ||||||||
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> 2000 | Q3 Q = Miscellaneous data from online sources Mouse3 = Unverified data of known source |
Low | ||||||||
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Subcutaneous LD₅₀ > 2000 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
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Intravenous LD₅₀ = 2450 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rabbit3 = Unverified data of known source |
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Partly metabolibised and eliminated predominately in urine with lesser amounts in faeces, bile and milk. | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
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Health issues |
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Harmful if inhaled may cause gastric irritation and vomiting Possible liver and kidney toxicant Some published studies suggest substance is carcinogenic |
Handling issues |
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Light sensitive Not explosive or oxidising |
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Health: H315, H319 | |||
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Not listed (Not listed) | |||
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sulphadimidine | ||
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sulfametazina | ||
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sulfadimidina | ||
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sulfametazina | ||
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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 |