Sulphaquinoxaline |
![]() Last updated: 11/09/2025 |
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(Also known as: sulfaquinoxaline) |
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An antiprotozoal veterinary drug | |
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Used for the prevention and treatment of coccidiosis. Also used in controlling fowl typhoid and fowl cholera as well asf infectious enteritis | |
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Poultry especially turkeys, chickens; Rabbits; Cattle |
Approval status |
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Not approved | |
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Not approved |
Chemical structure |
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None | |
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C₁₄H₁₂N₄O₂S | |
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C1=CC=C2C(=C1)N=CC(=N2)NS(=O)(=O)C3=CC=C(C=C3)N | |
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- | |
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NHZLNPMOSADWGC-UHFFFAOYSA-N | |
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InChI=1S/C14H12N4O2S/c15-10-5-7-11(8-6-10)21(19,20)18-14-9-16-12-3-1-2-4-13(12)17-14/h1-9H,15H2,(H,17,18) | |
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Yes |
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Common Name | Relationship | Link |
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sulphaquinoxaline | - | ![]() |
General status |
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Antiprotozoal agent | |
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Synergist | |
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Unclassified rodenticide; Synergist | |
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Synthetic | |
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Bactericide action, kills vitamin K-producing bacteria in the rat intestine | |
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[Dihydropteroate synthase, Inhibitor] | |
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59-40-5 | |
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200-423-2 | |
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077901 | |
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5338 | |
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No data found | |
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Antiprotozoals: Ectoparasiticides, including scabicides, insecticides and repellents | |
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QP51AG03 | |
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No | |
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300.34 | |
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4-amino-N-2-quinoxalinylbenzenesulfonamide | |
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4-amino-N-2-quinoxalinylbenzenesulfonamide | |
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4-amino-N-2-quinoxalinybenzenesulfonamide | |
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Commercial |
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Considered obsolete but may be available in some countries | |||
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2007, withdrawn UK | |||
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Usually formulated as bait when used as a rodenticide. For animal health it is usually formulated as wettable powders or solutions. | |||
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Sulphaquinoxaline is synthesised through a multi-step chemical process that begins with the preparation of 2-chloroquinoxaline, which is reacted with sulfanilamide in the presence of a base such as potassium carbonate and an appropriate solvent like ethanol or dimethylformamide. This nucleophilic substitution reaction forms the sulphaquinoxaline molecule by linking the sulfonamide group to the quinoxaline ring. The reaction mixture is typically heated under reflux to ensure complete conversion, then cooled and filtered to isolate the crude product. | |||
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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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7.5 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
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4300 | L3 L = Pesticide manuals and hard copy reference books / other sources Acetone3 = Unverified data of known source |
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700 | L3 L = Pesticide manuals and hard copy reference books / other sources Ethanol3 = Unverified data of known source |
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247 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
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4.79 X 1001 | Calculated | - | |||||||
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1.68 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
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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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Fate indices |
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Known metabolites |
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Terrestrial ecotoxicology |
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> 1.0 | L3 L = Pesticide manuals and hard copy reference books / other sources Mouse3 = Unverified data of known source |
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Aquatic ecotoxicology |
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> 119 | 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 ) Daphnia magna4 = Verified data |
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General |
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High (class III) | - | - | ||||||||
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> 1.0 | L3 L = Pesticide manuals and hard copy reference books / other sources Mouse3 = Unverified data of known source |
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Mainly eliminated in urine | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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Health issues |
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No information available |
Handling issues |
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No information available | |||
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Not listed (Not listed) | |||
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sulphaquinoxaline | ||
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sulfaquinoxalina | ||
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Record last updated: | 11/09/2025 |
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 |