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EC number: 247-979-2 | CAS number: 26761-45-5
- 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 cell study: DNA damage and/or repair
- Remarks:
- Type of genotoxicity: DNA damage and/or repair
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: The study was conducted according to established published methodology under the GLP regulations.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 981
- Report date:
- 1981
Materials and methods
- Principles of method if other than guideline:
- Petzold GL, Swenberg JA. Detection of DNA damage induced in vivo following exposure of rats to carcinogens. Cancer Res. 1978 Jun;38(6):1589-94.
- GLP compliance:
- yes
- Type of assay:
- other: Alkaline elution detection of DNA single breaks.
Test material
- Reference substance name:
- 2,3-epoxypropyl neodecanoate
- EC Number:
- 247-979-2
- EC Name:
- 2,3-epoxypropyl neodecanoate
- Cas Number:
- 26761-45-5
- Molecular formula:
- C13H24O3
- IUPAC Name:
- (oxiran-2-yl)methyl 2,2-dimethyloctanoate
- Test material form:
- other: Liquid at room temperature.
- Details on test material:
- As per IUCLID5 Sections 1.1, 1.2. and 1.4..
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Male and female albino Wistar strain rats (6—8 weeks of age) were obtained from the Rodent Breeding unit of the Shell Toxicology Laboratory (Tunstall). The animals were individually housed during the study.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- Test substance was dosed neat. DMSO was the vehicle for the positive control methyl methane sulphonate.
- Details on exposure:
- 2,3-Epoxypropyl neodecanoate was administered without solvent carrier, to pairs of rats of both sexes (body wt. ranges: female, 200—250gm; male, 350—470gm), by the oral gavage route.
- Duration of treatment / exposure:
- 6 hr
- Frequency of treatment:
- Once
- Post exposure period:
- None
Doses / concentrations
- Remarks:
- Doses / Concentrations:
Approximately 4850 mg/kg of body weight.
Basis:
nominal conc.
- No. of animals per sex per dose:
- 2
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Methyl Methanesulphonate at 300 mg/kg of body weight in DMSO.
Examinations
- Tissues and cell types examined:
- Liver cells
- Details of tissue and slide preparation:
- A 2gm sample of the liver from each animal was placed in a small beaker containing 2 ml of ice—cold homogenising medium (0.023M Na3 EDTA; 0.075M NaC1; pH 7.5). The tissue was gently squashed using the blunt end of a spatula (Cox et al., 1972) and the resultant cell suspension centrifuged (200 rpm, 1 mm) to sediment large pieces of liver.
- Evaluation criteria:
- No data
- Statistics:
- No data
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- not specified
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- Alkaline elution profiles of rat liver DNA, derived from solvent control animals, showed that the bulk of the DNA (greater than 90%) was retained on the membrane filter demonstrating little or no DNA damage. Treatment of the rats with a single oral dose of methyl methanesulphonate (300 mg/kg) gave single—strand damage which was manifested as a reduction in single strand molecular weight and observed as an increase in rate of elution of radioactivity upto seven-fold the solvent control value. 2,3-Epoxypropyl neodecanoate was administered to rats at a single oral dose level of approximately 4850 mg/kg and failed to produce any detectable DNA single—strand damage under these experimental conditions
Any other information on results incl. tables
Summary Data Tables of radioactivity and Alkaline Elution Profile figures are attached below.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
Treatment of rats by oral gavage with 2,3-epoxypropyl neodecanoate at a dose level of approximately 4850 mg/kg of body weight did not result in the detection of DNA single strand breaks in the rat liver cells. DNA single strand breaks are the manifestaion of premutagenic and preclastogenic DNA lesions (Petzold and Swenberg, 1978; Fornace AJ et. al. 1980a; Fornace AJ Jr. et. al. 1980b; Bootsma and Hoeijmakers, 1994). Therefore, 2,3-epoxypropyl neodecanoate did not induce DNA damage that could result in gene-mutation and/or chromosome damage in vivo under the conditions of this study. - Executive summary:
When 2,3 -epoxypropyl neodecanoate was assessed in a rat oral gavage liver alkaline elution DNA damage study at a dose level of approximately 4850 mg/kg of body weight, no evidence of DNA single strand break formation was observed. Therefore, 2,3 -epoxypropyl neodecanoate did not cause DNA damage in rat liver cells and is not genotoxic in vivo under the conditions of this study. .
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