| Carbadox |
![]() Last updated: 10/10/2025 |
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(Not known by any other names) |
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A drug used to treat gram-negative bacterial infections | |
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Used for improved productivity - increased rate of weight gain and improved feed efficiency. Also has therapeutic applications, for example, to control swine dysentery and bacterial swine enteritis. | |
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Pigs; Cattle |
| Approval status |
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Not approved | |
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Not approved |
| Chemical structure |
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Carbadox exhibits tautomeric isomerism, a form of isomerism where the molecule can exist in multiple structural forms due to the migration of a proton and a shift in bonding electrons. Specifically, the molecule contains functional groups, such as hydrazone and quinoxaline 1,4-dioxide, that allow for tautomeric shifts, potentially resulting in more than one tautomer coexisting within its crystalline structure. Recent crystallographic studies have revealed that carbadox can adopt two distinct molecular configurations in the solid state: five molecules in a lower-energy configuration and three in a slightly higher-energy (~10%) form. | |
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C₁₁H₁₀N₄O₄ | |
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COC(=O)NN=CC1=[N+](C2=CC=CC=C2[N+](=C1)[O-])[O-] | |
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COC(=O)N/N=C/C1=[N+](C2=CC=CC=C2[N+](=C1)[O-])[O-] | |
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OVGGLBAWFMIPPY-WUXMJOGZSA-N | |
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InChI=1S/C11H10N4O4/c1-19-11(16)13-12-6-8-7-14(17)9-4-2-3-5-10(9)15(8)18/h2-7H,1H3,(H,13,16)/b12-6+ | |
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Yes |
| General status |
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Antibacterial, Antimicrobial, Medicinal drug, Growth promotor, Feed additive | ||||||||||||||
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Quinoxaline | ||||||||||||||
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Synthetic | ||||||||||||||
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It is believed to act as a bacterial DNA-damaging agent, likely through the generation of reactive intermediates that interact with nucleic acids. | ||||||||||||||
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[Unclear but interferes with DNA replication and transcription] | ||||||||||||||
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6804-07-5 | ||||||||||||||
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229-879-0 | ||||||||||||||
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135511839 | ||||||||||||||
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613-050-00-9 | ||||||||||||||
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Antiinfectants for systemic use: Antibacterials for system use | ||||||||||||||
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QJ01MQ | ||||||||||||||
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No | ||||||||||||||
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262.22 | ||||||||||||||
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methyl N-[(E)-(1,4-dioxidoquinoxaline-1,4-diium-2-yl)methylideneamino]carbamate | ||||||||||||||
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2-(methoxycarbonylhydrazonomethyl)quinoxaline 1,4-dioxide | ||||||||||||||
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Banned in many countries as a growth promotor; Not approved as feed additive in EU; Evidence of use in third world countries; | ||||||||||||||
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Yellow crystalline solid | ||||||||||||||
| Commercial |
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Considered obsolete but may be available in some countries | |||
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1970s, introduced | |||
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As a growth promotor it was formulated as a premix or feed additive | |||
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The production of carbadox involves a multi-step chemical synthesis based around the construction of its quinoxaline 1,4-dioxide core, a structure known for its antimicrobial properties. The process typically begins with the condensation of o-phenylenediamine with a suitable dicarbonyl compound to form the quinoxaline ring. This intermediate is then subjected to oxidation, often using hydrogen peroxide or peracids, to introduce the 1,4-dioxide functionality. Additional steps include the attachment of side chains, such as the methylcarbamoyl and hydrazone groups, which are critical for its biological activity. | |||
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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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15000 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
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239 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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4.27 X 10-02 | Calculated | - | |||||||
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-1.37 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
Low | ||||||||
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1.44 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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8.6 X 10-05 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
Low volatility | ||||||||
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Substance may enter the environment via the faeces of treated animals or by leaching from spilt medicated feed. | ||||||||||
| 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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| Fate indices |
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Low risk | Q3 Q = Miscellaneous data from online sources Based on LogP < 33 = Unverified data of known source |
Low risk | |||||||||||||||||||||||||
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| Known soil and groundwater metabolites |
None
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| carbadoxaldehyde | - | Swine (plasma) | 0.130 | ||||
| quinoxaline-2-carboxylic acid | - | Swine (plasma) | 0.190 | ||||
| hydrazine | - | Swine (plasma, urine) | - | ||||
| desoxycarbadox | - | Swine (plasma) | 0.190 |
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| Terrestrial ecotoxicology |
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> 50 | 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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| General |
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High (class III) | - | - | ||||||||
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> 50 | 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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Rapidly absorbed through the skin | ||||||||||
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Metabolises and then eliminated in the urine | 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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| Health issues |
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Possile adrenal & liver toxicant May cause photosensitisation Publish studies suggest substance is carcinogenic; CLP data - known carcinogen |
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| Handling issues |
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Flammable | |||
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Handling: H228 Health: H392, H350 |
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Not listed (Not listed) | |||
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carbadox | ||
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| Record last updated: | 10/10/2025 |
| 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 |
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