Chloramine-T |
![]() Last updated: 15/09/2025 |
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(Also known as: chloramine-T anhydrous; N-chlorotosylamide, sodium salt; tosylchloramide) |
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A chlorinated and deprotonated sulfonamide that is an effective broad spectrum antibacterial substance with veterinary applications | |
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Used to control Gill Flukes, Body Flukes, White Spot, Costia and Bacterial Gill Disease, as a disinfectnt and for the reduction of pathogenic bacterial levels. | |
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Salmonid fish |
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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C₇H₇ClNNaO₂S | |
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CC1=CC=C(C=C1)S(=O)(=O)[N-]Cl.[Na+] | |
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VDQQXEISLMTGAB-UHFFFAOYSA-N | |
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InChI=1S/C7H7ClNO2S.Na/c1-6-2-4-7(5-3-6)12(10,11)9-8;/h2-5H,1H3;/q-1;+1 | |
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Yes |
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Common Name | Relationship | Link |
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chloramine-T trihydrate | Hydrate | ![]() |
General status |
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Antibacterial | |
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Antifouling agent; Biocide; Disinfectant; Preservative | |
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Sulphonamide | |
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Synthetic | |
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[Cytochrome P450 2E1, Activator], [Cytochrome P450 1A1, Activator], [Cytochrome P450 2B1, Activator], [DNA, Inhibitor] | |
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127-65-1 | |
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204-854-7 | |
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76502 | |
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3641960 | |
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Dermatologicals; Other antiseptics and disinfectants | |
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QD08AX04 | |
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No | |
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227.64 | |
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sodium; chloro-(4-methylphenyl)sulfonylazanide | |
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One used as a herbicide in the USA but was withdrawn mid-1980s | |
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White powder |
Commercial |
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Current | |||
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Early- to mid-1990's, first registered USA | |||
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Usually supplied as a powder | |||
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Chloramine-T is synthesised through an oxidation process involving p-toluenesulfonamide and sodium hypochlorite. The reaction begins by dissolving p-toluenesulfonamide in an aqueous alkaline medium, typically using sodium hydroxide, which helps maintain a basic pH and stabilise the hypochlorite. Sodium hypochlorite is then added gradually, acting as the oxidising agent that introduces the electrophilic chlorine atom to the nitrogen of the sulfonamide group. This forms the active compound, sodium N-chloro-p-toluenesulfonamide, known as chloramine-T. | |||
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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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150000 | 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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Decomposes before melting | 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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Decomposes before boiling | 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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167 | 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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5.01 X 10-02 | Calculated | - | |||||||
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-1.3 | 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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1.43 | 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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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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0.91 | - | Mobile | |||||||
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US EPA data: Kd range 0.58-1.04 mL g⁻¹, Koc range 31-52 mL g⁻¹, Soils=3 | ||||||||||
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Fate indices |
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Known soil and groundwater metabolites |
None
Other known metabolites |
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p-toluenesulfonamide Note: LC50 Poecilia reticulata = 31 mg/L; NOEC Daphnia magna = 4.5 mg/L |
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Terrestrial ecotoxicology |
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Q3 Mouse 1100 | - | Moderate | ||||||||
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Aquatic ecotoxicology |
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> 2.8 | 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 ) Oncorhynchus mykiss4 = Verified data |
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> 2.12 | 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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1.3 | 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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0.31 | 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 ) Desmodesmus subspicatus4 = Verified data |
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General |
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Q3 Mouse 1100 | - | Moderate | ||||||||
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Intraperitoneal LD₅₀ = 300 mmol/kg | Q3 Q = Miscellaneous data from online sources Rat3 = Unverified data of known source |
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Elimination primarily through the urine | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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Health issues |
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Exposure may cause burning sensation, coughing, shortness of breath, sore throat and various adverse respiratory conditions |
Handling issues |
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Corrosive May explode on heating above 130°C Combustable IMDG Transport Hazard Clsss 8 |
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Health: H302, H3334 Handling: H334 |
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Not listed (Not listed) | |||
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Packaging group III (minor danger) | |||
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chloramine-T | ||
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Record last updated: | 15/09/2025 |
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 |