Sulphanilamide |

Last updated: 23/02/2024
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(Also known as: 4-aminobenzenesulphonamide; bacteramid; 4-sulfamoylaniline; PABS; sulphonamide; sulfanilamide) |
The following alerts are based on the data in the tables below. An absence of an alert does not imply the substance has no implications for human health, biodiversity or the environment but just that we do not have the data to form a judgement.
Environmental fate |
Ecotoxicity |
Human health |
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A Sulphonamide antibiotic drug once used in veterinary medicine. Also a pesticide metbolite. |
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Current |
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1935, active parent introduced |
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Not applicable |
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Not applicable |
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Not applicable |
EC Regulation 1107/2009 (repealing 91/414) |
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Not applicable |
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Not applicable |
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Not applicable |
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Not applicable |
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No |
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ATAustria |
BEBelgium |
BGBulgaria |
CYCyprus |
CZCzech Republic |
DEGermany |
DKDenmark |
EEEstonia |
ELGreece |
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ESSpain |
FIFinland |
FRFrance |
HRCroatia |
HUHungary |
IEIreland |
ITItaly |
LTLithuania |
LULuxembourg |
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LVLatvia |
MTMalta |
NLNetherlands |
PLPoland |
PTPortugal |
RORomania |
SESweden |
SISlovenia |
SKSlovakia |
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- |
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C₆H₈N₂O₂S |
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C1=CC(=CC=C1N)S(=O)(=O)N |
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- |
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FDDDEECHVMSUSB-UHFFFAOYSA-N |
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InChI=1S/C6H8N2O2S/c7-5-1-3-6(4-2-5)11(8,9)10/h1-4H,7H2,(H2,8,9,10) |
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Yes |
Cambridge Crystallographic Data Centre diagrams |
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Common Name |
Relationship |
Link |
sulphanilamide |
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 |
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Veterinary substance, Metabolite |
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Soil, Animal, Surface water, Sediment |
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Sulphonamide substance |
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- |
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- |
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Natural |
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A competitive inhibitor of bacterial enzyme dihydropteroate synthetase |
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63-74-1 |
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200-563-4 |
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- |
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077902 |
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- |
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172.20 |
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- |
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4-aminobenzene-1-sulfonamide |
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4-aminobenzenesulfonamide |
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Possible groundwater pollutant |
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- |
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Not applicable |
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Not applicable |
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Not applicable |
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Not applicable |
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- |
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Yellow-white coloured solid |
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7500 |
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High |
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- |
- |
- |
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165.5 |
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- |
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Decomposes before boiling |
E3 E = Manufacturers safety data sheets 3 = Unverified data of known source |
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2.40 X 10-01 |
Calculated |
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-0.62 |
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Low |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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10.58 |
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- |
- |
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0.973 |
at 25 °C |
Low volatility. If applied directly to plants, drift is a concern & mitigation is advisable |
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1.52 X 10-05 |
at 25 °C |
Non-volatile |
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- |
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- |
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- |
- |
- |
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- |
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13.4 |
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Non-persistent |
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13.4 |
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Non-persistent |
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- |
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- |
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- |
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- |
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EU dossier Aerobic lab studies DT₅₀ range 3.1-76.3 days, Soils=6 |
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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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- |
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- |
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- |
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2.90 |
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Moderately mobile |
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166 |
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0.708 |
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EU dossier Kf range 1.45-4.07 mL g⁻¹, Kfoc range 96-278 mL g⁻¹, 1/n range 0.673-0.748, Soils=8 |
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No |
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2.01 |
Calculated |
Transition state |
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5.08 X 10-02 |
Calculated |
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Low |
Calculated |
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Moderately mobile |
Calculated |
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Low risk |
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source Based on LogP < 3 |
Low risk |
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None
Terrestrial ecotoxicology |
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3700 |
Rat |
Low |
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- |
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- |
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- |
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> 1000 |
Eisenia foetida |
Low |
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3.75 |
Eisenia foetida |
Moderate |
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Nitrogen mineralisation: No significant adverse eff |
Dose: 3.3 mg kg⁻¹ soil 28 Day |
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2.3 |
Lemna minor |
Moderate |
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- |
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> 21.15 |
Pseudokirchneriella subcapitata 120 hr |
Low |
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HUMAN HEALTH AND PROTECTION |
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High (class III) |
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3700 |
Rat |
Low |
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255 |
E3 E = Manufacturers safety data sheets 3 = Unverified data of known source Rat 4 hr |
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Intravenous LD₅₀ = 1400 mg kg⁻¹ |
Rat |
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Subcutaneous LD₅₀ = 2900 mg kg⁻¹ |
Mouse |
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EU MRL pesticide database |
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Excreted mainly in the urine but can also be found in most dody fluids including breast milk |
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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Carcinogen |
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Endocrine disruptor |
?Possibly, status not identified |
A0 A = Chromosome aberration (EFSA database) 0 = No data ; B0 B = DNA damage/repair (EFSA database) 0 = No data ; C0 C = Gene mutation (EFSA database) 0 = No data ; D0 D = Genome mutation (EFSA database) 0 = No data ; E1 E = Unspecified genotoxicity type (miscellaneous data source) 1 = Positive |
No data found |
Reproduction / development effects |
Acetyl cholinesterase inhibitor |
Neurotoxicant |
✓Yes, known to cause a problem |
No data found |
No data found |
Respiratory tract irritant |
Skin irritant |
Skin sensitiser |
?Possibly, status not identified |
?Possibly, status not identified |
No data found |
Eye irritant |
Phototoxicant |
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?Possibly, status not identified |
No data found |
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Ingestion may cause allergic reactions Long-term use may cause cancer of the thyroid gland Published studies suggest substance is carcinogenic |
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IMDG Transport Hazard Class 8 Corrosive solid |
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Not listed (Not listed) |
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UN1759 |
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sulphanilamide |
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Record last updated: |
23/02/2024 |
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 |