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EC number: 237-572-8 | CAS number: 13845-18-6
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data

Endpoint summary
Administrative data
Description of key information
The oral administration of Sodium sulphamate to rats by gavage, at dose levels of 100, 300 and 1000 mg/kg bw/day, did not result in any toxicologically significant effects. The ‘No Observed Adverse Effect Level’ (NOAEL) for systemic toxicity was therefore considered to be 1000 mg/kg bw/day.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Endpoint conclusion
- Dose descriptor:
- NOAEL
- 1 000 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
Additional information
The study was designed to investigate the systemic toxicity and potential adverse effects of the test item on reproduction (including offspring development) and was designed to be compatible with the requirements of the OECD Guidelines for Testing of Chemicals No. 422 “Combined Repeated Dose Toxicity Study with the Reproduction/Developmental Toxicity Screening Test” (adopted 22 March 1996).
The oral administration of Sodium sulphamate to rats for a period of up to eight weeks (including two weeks pre-mating, gestation and early lactation period for females) at dose levels of up to 1000 mg/kg bw/day resulted in treatment related effects detected in animals of either sex treated with 1000 mg/kg bw/day.
No clinical signs of toxicity were detected in treated animals however the physical condition of males treated with 1000 mg/kg bw/day was affected slightly with reductions in body weight development during the first and last weeks of treatment. Subsequently a slight reduction in overall body weight gain, a slight reduction in overall food consumption and a slight reduction in food efficiency was evident in these males.
Haematological investigations revealed increases in haemoglobin, haematocrit and clotting time in females treated with 1000 mg/kg bw/day. This together with the slight decline in male health was probably associated with the bone marrow and spleen changes seen microscopically. Changes were identified as increased hematopoiesis in the spleen and an increased incidence and mean severity of erythroid hyperplasia in the bone marrow in animals of either sex treated with 1000 mg/kg bw/day. The findings detected in the spleen and bone marrow are considered to be related to treatment however are considered not to be an adverse effect of treatment. Therefore the slight decline in health detected in males and the changes detected in the haematological parameters measured are considered not to be of toxicological significance.
Absolute and relative kidney weights were elevated in females treated with 1000 mg/kg bw/day and microscopic examination of kidney sections revealed focal and multifocal occurring basophilic tubules in females treated with 1000 mg/kg bw/day. The majority of individual organ weight values were within the normal range for rats of the strain and age used. The basophilic tubules detected in female kidneys did not reveal a true dose-relationship and they were also present in a few control animals. The kidney changes were also only minimally increased in incidence therefore, this finding was considered to be still within the biological range known for rats of this age and strain used and as such was considered not to be of toxicological importance.
There were no toxicologically significant effects observed during the weekly open field arena observations, in the blood chemical parameters measured or at necropsy.
There were no treatment-related effects detected in the reproductive parameters observed.
Justification for classification or non-classification
The oral administration of Sodium sulphamate to rats by gavage, at dose levels of 100, 300 and 1000 mg/kg bw/day, did not result in any toxicologically significant effects (see discussion for details on effects observed). The ‘No Observed Adverse Effect Level’ (NOAEL) for systemic toxicity was therefore considered to be 1000 mg/kg bw/day.
Based on the determined NOAEL of 1000 mg/kg bw/day and assessment of effects seen in the study, it is considered that the test substance does not meet the criteria for classification for repeat dose toxicity.
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