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EC number: 203-233-8 | CAS number: 104-75-6
- 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 007
- Report date:
- 2007
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- GLP compliance:
- yes
- Type of assay:
- other: mammalian erythrocyte micronucleus test
Test material
- Reference substance name:
- Octylammonium chloride
- EC Number:
- 205-574-8
- EC Name:
- Octylammonium chloride
Constituent 1
- Specific details on test material used for the study:
- Lot/batch No.: A0108056
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories, Germany
- Age at study initiation: 5 - 8 weeks
- Weight at study initiation: about 30 g
- Housing: Makrolon cages, type MI
- Diet (e.g. ad libitum): Standardized pelleted feed (Maus/Ratte Haltung "GLP", Provimi Kliba SA, Kaiseraugst, Switzerland)
- Water (e.g. ad libitum): ad libitum
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20 - 24
- Humidity (%): 30 - 70
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- purified water
- Vehicle/solvent used: purified water
- Justification for choice of solvent/vehicle: Due to the good solubility of the test substance in water, purified water was selected as the vehicle. - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
The substance to be administered per kg body weight was dissolved in purified water. The pH values of all test substance preparations were between 4.0 - 6.0 prior to dosing without thoroghly.
To achieve a solution of the test substance in the vehicle, the test substance preparation was shaken thoroughly.
All test substance formulations wereprepared immediately before administration. - Duration of treatment / exposure:
- The animals were treated once and samples of bone marrow were taken 24 hours and 48 hours after the treatment.
- Frequency of treatment:
- The animals were treated once.
Doses / concentrationsopen allclose all
- Dose / conc.:
- 75 mg/kg bw/day
- Dose / conc.:
- 150 mg/kg bw/day
- Dose / conc.:
- 300 mg/kg bw/day
- No. of animals per sex per dose:
- 5 male animals per dose
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide (CPP) / Vincristine Sulphate (VCR)
- Route of administration: oral / i.p.
- Doses / concentrations: 20 mg / 0.15 mg
Examinations
- Tissues and cell types examined:
- In general 2000 polychromatic erythrocytes (PCEs) from each of the male animals of every test group are evaluated and investigated for micronuclei.
The normochromatic erythrocytes (NCEs) which occur are also scored. - Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: Pretest were performed
DETAILS OF SLIDE PREPARATION:
The bone marrow was prepared according to the method described by SCHMID, W. (7, 8) and SALAMONE, M. et al. (6).
• The two femora of the animals sacrificed by cervical dislocation were prepared by dissection and removing all soft tissues.
• After cutting off the epiphyses, the bone marrow was flushed out of the diaphysis into a centrifuge tube using a cannula filled with fetal calf serum (FCS) which was at 37°C (about 2 mL/femur).
• The suspension was mixed thoroughly with a pipette, centrifuged at 300 x g for 5 minutes, the supernatant was removed and the precipitate was resuspended in about 50 µL fresh FCS.
• 1 drop of this suspension was dropped onto clean microscopic slides, using a Pasteur pipette. Smears were prepared using slides with ground edges, the preparations were dried in the air and subsequently stained.
• The slides were stained in eosin and methylene blue (modified May-Grünwald solution or Wrights solution) for about 5 minutes.
• After having briefly been rinsed in purified water, the preparations were soaked in purified water for about 2 - 3 minutes.
• Subsequently, the slides were stained in Giemsa solution (15 mL Giemsa, 185 mL purified water) for about 15 minutes.
• After having been rinsed twice in purified water and clarified in xylene, the preparations were mounted in Corbit-Balsam.
- Evaluation criteria:
- A finding is considered positive if the following criteria are met:
• Significant and dose-related increase in the number of PCEs containing micronuclei.
• The number of PCEs containing micronuclei has to exceed both the concurrent negative control and the highest value of the historical control range.
A test substance is considered negative if the following criteria are met:
• The number of cells containing micronuclei in the dose groups is not significantly above the negative control and is within the historical control data. - Statistics:
- The statistical evaluation of the data was carried out using the program system MUKERN (BASF Aktiengesellschaft).
The asymptotic U test according to MANN-WHITNEY (modified rank test according to WILCOXON) was carried out to clarify the question whether there were significant differences between the control group and dose groups with regard to the micronucleus rate in polychromatic erythrocytes. The relative frequencies of cells containing micronuclei of each animal were used as a criterion for the rank determination for the U test. Significances were identified as follows:
* p ≤ 0.05
** p ≤ 0.01
Results and discussion
Test results
- Key result
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- not examined
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Clinical signs of toxicity in test animals: no adverse signs or symptoms
- Motality: none
The number of normochromatic erythrocytes containing micronuclei did not differ to any appreciable extent in the negative control or in the various dose groups at any of the sacrifice intervals.
No inhibition of erythropoiesis induced by the treatment of mice with Octylamine hydrochloride was detected; the ratio of polychromatic to normochromatic erythrocytes was always in the same range as that of the control values in all dose groups.
Any other information on results incl. tables
Percent micronucleated PCE/200 PCE
dose | 24 hours sacrifice interval | 48 hours sacrifice interval |
vehicle control | 1.4 % mPCE | 0.8 % mPCE |
300 mg/kg b.w. | 1.4 % mPCE | 1.5 % mPCE |
150 mg/kg b.w. | 1.1 % mPCE | |
75 mg/kg b.w. | 1.3 % mPCE | |
positive control (CCP) | 15 % mPCE, mainly small micronuclei | |
positive control (VCR) | 30.6 % mPCE, 8 % was lange micronuclei |
Thus, under the experimental conditions chosen here, the test substance Octylamine hydrochloride has no chromosome-damaging (clastogenic) effect nor does it lead to any impairment of chromosome distribution in the course of mitosis (aneugenic activity) in bone marrow cells in vivo.
Applicant's summary and conclusion
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