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EC number: 204-337-6 | CAS number: 119-61-9
- 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
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1993/2000
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 2 000
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- Principles of method if other than guideline:
- Preliminary range-finding studies were performed. Factors affecting dose selection included chemical solubility and toxicity and the extent of cell cycle delay induced by benzophenone exposure; the limiting factor was toxicity.
- GLP compliance:
- not specified
- Type of assay:
- other: micronucleus assay
Test material
- Reference substance name:
- Benzophenone
- EC Number:
- 204-337-6
- EC Name:
- Benzophenone
- Cas Number:
- 119-61-9
- Molecular formula:
- C13H10O
- IUPAC Name:
- diphenylmethanone
- Details on test material:
- Molecular weight 182.22
Boiling point 305.4° C
Flash point greater than 110° C
Vapor pressure 1 mm Hg at 108.2° C
Refractive index 1.60
Log octanol/water partition coefficient 3.18
Solubility Insoluble in water; soluble in organic solvents including alcohol, acetone, ether, acetic acid, chloroform, and benzene
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:
- corn oil
- Details on exposure:
- Mice were injected intraperitoneally
- Duration of treatment / exposure:
- 3 days
- Frequency of treatment:
- 3 times with intervals of 24 hours
- Post exposure period:
- 24 hours after last injection
Doses / concentrations
- Remarks:
- 200, 300, 400 or 500 mg/kg bw
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- 25 mg/kg bw cyclophosphamide i.p.
Examinations
- Tissues and cell types examined:
- The mice were killed 24 hours after the last injection, and blood smears were prepared from bone marrow cells obtained from the femurs.
- Details of tissue and slide preparation:
- Airdried smears were fixed and stained; 2,000 polychromatic erythrocytes (PCEs) were scored for the frequency of micronucleated cells in each of five animals per dose group.
- Evaluation criteria:
- In the micronucleus test, an individual trial was considered positive if the trend test P value was less than or equal to 0.025 or if the P value for any single dose group was less than or equal to 0.025 divided by the number of dose groups. A final call of positive for micronucleus induction is preferably based on reproducibly positive trials (as noted above). Ultimately, the final call is determined by the scientific staff after considering the results of statistical analyses, the reproducibility of any effects observed, and the magnitudes of those effects.
- Statistics:
- The results were tabulated as the mean of the pooled results from all animals within a treatment group, plus or minus the standard error of the mean. The frequency of micronucleated cells among PCEs was analysed by a statistical software package that tested for increasing trend over dose groups using a one-tailed Cochran-Armitage trend test, followed by pairwise comparisons between each dosed group and the control group. In the presence of excess binomial variation, as detected by a binomial dispersion test, the binomial variance of the Cochran-Armitage test was adjusted upward in proportion to the excess variation.
Results and discussion
Test results
- Key result
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- not specified
- Positive controls validity:
- valid
Applicant's summary and conclusion
- Conclusions:
- Benzophenone did not induce micronuclei in any of the doses tested and is therefore considered nonmutagenic in this test system.
- Executive summary:
Benzophenone was tested in an in vivo micronucleus test according to a standard three-exposure protocol. Male B6C3F1 mice were injected intraperitoneally three times at 24-hour intervals with benzophenone dissolved in corn oil; the total dosing volume was 0.4 mL, the doses were 200, 300, 400 and 500 mg/kg bw per injection. Solvent control mice were injected with 0.4 mL of corn oil only. The positive control mice received injections of 25 mg cyclophosphamide/kg. The mice were killed 24 hours after the last injection, and blood smears were prepared from bone marrow cells obtained from the femurs. Air-dried smears were fixed and stained and 2000 polychromatic erythrocytes (PCEs) were scored for the frequency of micronucleated cells in each of five animals per dose group. In contrast to the positive control, benzophenone did not increase the number of micronucleated polychromatic erythrocytes and did therefore not induce chromosomal damage.
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