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EC number: 200-311-3 | CAS number: 57-09-0
- 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
Toxicity to reproduction
Administrative data
- Endpoint:
- screening for reproductive / developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Study initiated October 2019, Dose Range Finding (DRF) Study October 2019, Necropsy November 2019.
- Reliability:
- 1 (reliable without restriction)
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 021
- Report date:
- 2021
Materials and methods
- Principles of method if other than guideline:
- DRF study for “Combined 28-day repeated dose toxicity study with the reproduction/developmental toxicity screening of FeF cetyl trimethyl ammonium bromide (CTAB) USP/NF by oral gavage in rats” to follow OECD Guideline 422. Combined Repeated Dose Toxicity Study with the Reproduction/Developmental Toxicity Screening Test, July 2016 and EPA Health Effects Test Guideline OPPTS 870.3650: Combined Repeated Dose Toxicity Study with the Reproduction/Developmental Toxicity Screening Test, July 2000
- GLP compliance:
- yes
- Remarks:
- DRF study perfomed according to GLP,. Reported in Appendix 6, Appendix 7 and Appendix 8 of the report on main study 20212915
Test material
- Reference substance name:
- Cetrimonium bromide
- EC Number:
- 200-311-3
- EC Name:
- Cetrimonium bromide
- Cas Number:
- 57-09-0
- Molecular formula:
- C19H42N.Br
- IUPAC Name:
- cetrimonium bromide
- Test material form:
- solid
Constituent 1
- Specific details on test material used for the study:
- White powder
Batch (Lot) Number: GX0B433
Expiry date: 31 December 2022
Purity: 100% according to certificate of analysis
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- female
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on exposure:
- Dose levels: 0, 50, 100, 200, 300 mg/kg bw/day
- Duration of treatment / exposure:
- 14 days
- Frequency of treatment:
- daily
- No. of animals per sex per dose:
- 3 female rats/ group
Results and discussion
Results: P0 (first parental generation)
General toxicity (P0)
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- All rats treated at 100, 200 and 300 mg/kg/day were sacrificed moribund at Day 5, 4 and 3 respectively. Cause of moribundity were considered test item-related forestomach lesions in all rats in the form of the macroscopic finding irregular surface with the microscopic correlate ulceration/erosion of the forestomach up to marked degree. This was accompanied by (sub) mucosal edema (up to moderate) and lymphogranulocytic inflammation (up to marked) and/or squamous cell hyperplasia (minimal).
Furthermore, findings in the glandular stomach were noted which consisted of a focal ulcer at 300 mg/kg/day (minimal) and from 200 mg/kg/day onward a slightly increased incidence of granulocytic infiltrate (minimal). Although these findings can be seen as spontaneous background findings, a relationship with treatment with the test item for these latter two findings cannot be excluded.
Minor findings were noted for the intestines which included a minor increase in incidence and/or severity of inflammatory cell infiltrate (up to slight) at 200 and/or 300 mg/kg/day and epithelial necrosis in the duodenum of one rat treated at 300 mg/kg/day (minimal). A test item-relationship cannot be excluded.
There was no microscopic correlate for the macroscopic finding gelatinous contents (considered test item-related) noted in the stomach of all 300 mg/kg/day treated rats and in the intestinal tract of all rats treated at 100, 200 and 300 mg/kg/day.
There were no test item-related morphologic alterations in rats treated at 50 mg/kg/day for 14 consecutive days. - Dermal irritation (if dermal study):
- not specified
- Mortality:
- mortality observed, treatment-related
- Body weight and weight changes:
- not specified
- Food consumption and compound intake (if feeding study):
- not specified
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- not specified
- Haematological findings:
- not specified
- Clinical biochemistry findings:
- not specified
- Urinalysis findings:
- not specified
- Behaviour (functional findings):
- not specified
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- not specified
- Histopathological findings: non-neoplastic:
- not specified
- Histopathological findings: neoplastic:
- not specified
- Other effects:
- not specified
Effect levels (P0)
open allclose all
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- ca. 50 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- female
- Basis for effect level:
- gross pathology
- Key result
- Dose descriptor:
- LOAEL
- Effect level:
- ca. 100 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- female
- Basis for effect level:
- gross pathology
Results: F1 generation
Effect levels (F1)
- Remarks on result:
- not determinable because of methodological limitations
Overall reproductive toxicity
- Reproductive effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- Adverse test item-related morphologic alterations following the administration of FeF Cetyl Trimethyl Ammonium Bromide (CTAB) USP/NF were noted at 100, 200 and 300 mg/kg/day in the form of an early onset of moribundity related with marked forestomach ulceration/erosion and concomitant findings, as edema, inflammation and squamous cell hyperplasia.
Treatment for 14 days at 50 mg/kg/day was well tolerated.
Due to the observed steep dose-reponse relationship for forestomach ulceration/erosion and because of longer exposure period in the main study, the maximum dose in the main study should be no higher than 50 mg/kg bw/day.
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