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EC number: 217-752-2 | CAS number: 1948-33-0
- 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: gene mutation
- Remarks:
- Micronucleus study
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Justification for type of information:
- Data is from NTP report
Data source
Reference
- Reference Type:
- publication
- Title:
- Gene mutation in vivo toxcity study of the test chemical
- Author:
- DHHS
- Year:
- 1 997
- Bibliographic source:
- NTP
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: Refer below principle
- Principles of method if other than guideline:
- Mouse bone marrow micronucleus test was performed to determine the mutagenic nature of the test chemical
- GLP compliance:
- not specified
- Type of assay:
- other: Micronucleus assay
Test material
- Reference substance name:
- 2-tert-butylhydroquinone
- EC Number:
- 217-752-2
- EC Name:
- 2-tert-butylhydroquinone
- Cas Number:
- 1948-33-0
- Molecular formula:
- C10-H14-O2
- IUPAC Name:
- 2-tert-butylbenzene-1,4-diol
- Details on test material:
- - Name of test material: tert-Butyl hydroquinone (TBHQ)
- IUPAC name: 2-tert-Butylhydroquinone
- Molecular formula: C10H14O2
- Molecular weight: 166.219 g/mol
- Substance type: Organic
- Physical state: No data
- Purity: No data
- Impurities (identity and concentrations): No data
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- B6C3F1
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- No data
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- - Vehicle(s)/solvent(s) used: Corn oil
- Justification for choice of solvent/vehicle: The test chemical was soluble in corn oil
- Concentration of test material in vehicle: 0, 9.38, 18.75, 37.50, 75.00, 150.00, 300.00 mg/Kg
- Amount of vehicle (if gavage or dermal): 10 mL/Kg
- Type and concentration of dispersant aid (if powder): No data
- Lot/batch no. (if required): No data
- Purity: No data - Details on exposure:
- No data
- Duration of treatment / exposure:
- 72 hrs
- Frequency of treatment:
- Thrice at 24 hrs interval
- Post exposure period:
- No data
Doses / concentrations
- Remarks:
- 0, 9.38, 18.75, 37.50, 75.00, 150.00, or 300.00 mg/Kg
- No. of animals per sex per dose:
- 5 mice/ dose
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide
- Justification for choice of positive control(s): No data
- Route of administration: Intraperitoneally
- Doses / concentrations: 25 mg/Kg
Examinations
- Tissues and cell types examined:
- Bone marrow smears obtained from femurs
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: No data
TREATMENT AND SAMPLING TIMES ( in addition to information in specific fields): Male B6C3F1 mice received three intraperitoneal injections of the test chemical dissolved in com oil at 24-hour intervals. Up to five mice were treated per exposure group and the highest dose administered was 400 mg/kg. Solvent control animals received com oil only, and the positive control mice received injections of 25 mg/kg cyclophosphamide. The mice were killed 24 hours after the final injection and slides were prepared from bone marrow smears obtained from the femurs.
DETAILS OF SLIDE PREPARATION: Slides were air-dried, fixed, and stained.
METHOD OF ANALYSIS: Two thousand polychromatic erythrocytes (PCEs) were scored per animal for frequency of micronucleated cells.
OTHER: Selection of doses was based upon published LD50 information; no preliminary range-finding studies were required. - Evaluation criteria:
- No data
- Statistics:
- The mean of the pooled results from all animals within an exposure group, plus or minus the standard error of the mean. The frequency of micronucleated cells among PCEs was analyzed by a statistical software package that tested for increasing trend over exposure groups using a one-tailed Cochran-Armitage trend test, followed by pairwise comparisons between each exposure group and the control group. In the presence of excess binomial variation, as detected by a
lbinomial dispersion test, the binomial variance of the Cochran-Armitage test was adjusted upward in lproportion to the excess variation. In the micronucleus test, an individual trial is considered positive if the trend test P value is ≤0.025 or the P valuefor any single exposure group is ~0.025/n where n = the number of exposure groups. A final call of positive for micronucleus induction is preferably based on reproducibly positive trials.
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- not specified
- Vehicle controls validity:
- valid
- Negative controls validity:
- not specified
- Positive controls validity:
- valid
- Additional information on results:
- No data
Any other information on results incl. tables
Table: Mutagenic potential of the test chemical
Dose |
No. of mice |
Micronucleated PCEs/ 1000 cells |
CPA 25.00 |
5 |
17.6±1.46 |
Test chemical |
|
|
0 |
5 |
0.8±0.44 |
9.38 |
4 |
0.9±0.43 |
18.75 |
5 |
1.7±0.46 |
37.50 |
5 |
1.3±0.41 |
75.00 |
5 |
1.0±0.45 |
150.00 |
5 |
1.4±0.19 |
300.00 |
1 |
1.0 |
Applicant's summary and conclusion
- Conclusions:
- The test chemical did not induce micronuclei formation in bone marrow smears of B6C3F1 mice.
- Executive summary:
In vivo micronucleus assay was performed to determine the mutagenic nature of the test chemical. The study was performed using male B6C3F1 mice. Male B6C3F1 mice received three intraperitoneal injections of the test chemical dissolved in com oil at 24-hour intervals. Up to five mice were treated per exposure group and the highest dose administered was 400 mg/kg. Solvent control animals received com oil only, and the positive control mice received injections of 25 mg/kg cyclophosphamide. The mice were killed 24 hours after the final injection and slides were prepared from bone marrow smears obtained from the femurs. Slides were air-dried, fixed, and stained. Two thousand polychromatic erythrocytes (PCEs) were scored per animal for frequency of micronucleated cells. No animals survived in the 400 mg/kg group and only one mouse survived in the 300 mg/kg dose group. Based on the observations made, the test chemical did not induce micronuclei formation in bone marrow smears of B6C3F1 mice.
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