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EC number: 231-640-0 | CAS number: 7665-72-7
- 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 / bone marrow chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Study period:
- 1976-09-19
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 979
- Report date:
- 1979
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- - Short description of test conditions:
Metaphase cells from bone marrow preparations of the animals were scored for structural chromosomal aberrations. A total of 100 metaphases from each animal were scored. - GLP compliance:
- not specified
- Type of assay:
- mammalian bone marrow chromosome aberration test
Test material
- Reference substance name:
- (tert-butoxymethyl)oxirane
- EC Number:
- 231-640-0
- EC Name:
- (tert-butoxymethyl)oxirane
- Cas Number:
- 7665-72-7
- Molecular formula:
- C7H14O2
- IUPAC Name:
- 2-[(tert-butoxy)methyl]oxirane
Constituent 1
- Specific details on test material used for the study:
- - Name: tertiary-butyl glycidyl ether
- CAS No. : 7665-72-7
- Lot No. : 21311-34GWS
- Supplier: Shell
Test animals
- Species:
- mouse
- Strain:
- other: B6D2F1
- Sex:
- female
- Details on test animals or test system and environmental conditions:
- - Weight: 20 - 25 g
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- Vehicle used: Corn oil
- Details on exposure:
- - Dilutions of t-BGE in corn oil were administered orally once a day for five days to separate groups of ten B6D2F1 female mice
- The positive control compounds were administered only twice.
- All animals were sacrificed 4 hours after the last treatment. - Duration of treatment / exposure:
- 5 days
- Frequency of treatment:
- once a day
Doses / concentrationsopen allclose all
- Dose / conc.:
- 100 mg/kg bw/day
- Dose / conc.:
- 200 mg/kg bw/day
- Dose / conc.:
- 400 mg/kg bw/day
- No. of animals per sex per dose:
- 10 females
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cytoxan and hycanthone were used as positive controls
Examinations
- Tissues and cell types examined:
- Metaphase cells from bone marrow preparations were used for scoring of structural DNA damage.
Results and discussion
Test results
- Key result
- Sex:
- female
- Genotoxicity:
- negative
- Toxicity:
- not specified
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- The frequency of gaps was essentially the same for both treated and control groups. The known positive controls Cytoxan and hycanthone demonstrated frequencies of damaged cells in the same range as prvious studies conducted in this laboratory. This test showed no differences between the control and the t-BGE dosage group oin the percentage of metaphases with chromosomal damage.
Applicant's summary and conclusion
- Conclusions:
- In an in-vivo cytogenicity toxicity test, t-BGE was orally exposed to ten female B6D2F1mice weighing 20 - 25 g at concentrations of 100 - 400 mg/kg once per day for five consecutive days. All animals were sacrificed 4 hours after the last treatment. Extraction of bone marrow, preparation of smears, staining and analysis was conducted and the metaphase cells from bone marrow preparations were scored for structural chromosomal aberrations. A total of 100 metaphases from each animal were scored. The frequency of gaps was essentially the same for both treated and control groups. The known positive controls Cytoxan and hycanthone demonstrated frequencies of damaged cells in the same range as prvious studies conducted in this laboratory. This test showed no differences between the control and the t-BGE dosage group oin the percentage of metaphases with chromosomal damage.
- Executive summary:
In an in-vivo cytogenicity toxicity test, t-BGE was orally exposed to ten female B6D2F1mice weighing 20 - 25 g at concentrations of 100 - 400 mg/kg once per day for five consecutive days. All animals were sacrificed 4 hours after the last treatment. Extraction of bone marrow, preparation of smears, staining and analysis was conducted and the metaphase cells from bone marrow preparations were scored for structural chromosomal aberrations. A total of 100 metaphases from each animal were scored. The frequency of gaps was essentially the same for both treated and control groups. The known positive controls Cytoxan and hycanthone demonstrated frequencies of damaged cells in the same range as prvious studies conducted in this laboratory. This test showed no differences between the control and the t-BGE dosage group oin the percentage of metaphases with chromosomal damage.
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