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EC number: 202-849-4 | CAS number: 100-41-4
- 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 vitro
Administrative data
- Endpoint:
- in vitro gene mutation study in mammalian cells
- Remarks:
- Type of genotoxicity: gene mutation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2006
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP/Guideline study
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 006
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.5300 - In vitro Mammalian Cell Gene Mutation Test
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 476 (In Vitro Mammalian Cell Gene Mutation Test)
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.17 (Mutagenicity - In Vitro Mammalian Cell Gene Mutation Test)
- Principles of method if other than guideline:
- not applicable
- GLP compliance:
- yes
- Type of assay:
- mammalian cell gene mutation assay
Test material
- Reference substance name:
- Ethylbenzene
- EC Number:
- 202-849-4
- EC Name:
- Ethylbenzene
- Cas Number:
- 100-41-4
- Molecular formula:
- C8H10
- IUPAC Name:
- ethylbenzene
- Details on test material:
- - Name of test material (as cited in study report): Ethylbenzene
- Physical state: colorless liquid
- Analytical purity: 99.85%
- Lot/batch No.: 01353MC
Constituent 1
Method
- Target gene:
- not applicable
Species / strain
- Species / strain / cell type:
- mouse lymphoma L5178Y cells
- Details on mammalian cell type (if applicable):
- no data
- Additional strain / cell type characteristics:
- not applicable
- Metabolic activation:
- with and without
- Metabolic activation system:
- Aroclor 1254 induced S9 liver homogenates
- Test concentrations with justification for top dose:
- Assay A1: 0, 4.2, 8.3, 16.6, 33.1, 66.25, 132.5, 265, 530 and 1060 µg/ml.
Assay B1: 0, 10, 20, 30, 40, 50, 60, 70, 80, 100, 120 µg/ml.
Assay C1: 0, 10, 30, 38, 42, 46, 50, 54, 60, 70 µg/ml. - Vehicle / solvent:
- - Vehicle(s)/solvent(s) used: DMSO
Controls
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: Methyl methanesulfonate and 20-methylcholanthrene
- Details on test system and experimental conditions:
- no data
- Evaluation criteria:
- The activation and non-activation assays were considered independent assays with their own negative and positive controls. For an assay to be considered acceptable, (1) the mutation frequency of positive controls should have been significantly higher, 95 x 10-6 above the average of the concurrent solvent controls, and (2) the mutant frequency of the negative controls should have been within 35-140 x 10-6. The negative controls must have had an average absolute cloning efficiency between 65- 120% and a cumulative suspension growth greater than eight.
Mutant frequencies were evaluated based upon biological significance criteria (Moore et al., 2003). The test chemical was considered positive when the conditions listed below were met:
a) the average mutant frequency in at least one dose level of the treated cultures (resulting in ≥ 10% relative total growth) was 95 x 10-6 above the average of the concurrent solvent controls (assuming these to be in the range of 35-140 x 10-6).
b) There was a positive dose related linear trend. This was tested using a linear trend test at alpha = 0.05, provided the above criterion was met.
The test material was considered negative in this assay if the following condition was met:
a) There was no evidence of increase in mutant frequency at RTG values ≥ 10%.
The test material was considered equivocal in this assay if the following conditions were met:
a.) there was a significant increase in mutant frequency that met the criteria for a positive response only at RTG values > 10% and < 20%.
b.) there was no evidence of increase in mutant frequency at RTG values ≥ 20%. - Statistics:
- no data
Results and discussion
Test results
- Species / strain:
- mouse lymphoma L5178Y cells
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- other: In absence of S9, the test material was excessively toxic at the five highest concentrations (66.25, 132.5, 265, 530 and 1060 µg/ml.
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- TEST-SPECIFIC CONFOUNDING FACTORS
- Effects of pH and osmolality:
There was no appreciable change in either the pH or the osmolality of the culture medium following the addition of the test material as compared to the culture medium with solvent alone (culture medium with the test material, pH = 7.56; osmolality = 432 mOsm/kgH2O; culture medium with 1% DMSO, pH = 7.43, osmolality 447 mOsm/kgH2O).
COMPARISON WITH HISTORICAL CONTROL DATA:
Cultures treated with the positive control chemical induced a positive response as compared to the solvent control. The solvent control values were within the range.
ADDITIONAL INFORMATION ON CYTOTOXICITY:
In a preliminary toxicity assay (Assay A1), the test material was evaluated at concentrations ranging from 4.2 to 1060 mg/ml in the absence and presence of an externally supplied metabolic activation system (S9). The highest concentration represented the limit dose of 10 mM and exceeded the solubility of the test material in the treatment medium. In the absence of S9, the test material was excessively toxic at the five highest concentration levels (i.e.,66.25, 132.5, 265, 530 and 1060 mg/ml) as measured by Day 2 relative suspension growth (RSG). The remaining cultures had day 2 RSG values ranging from 52 to 107% (Table 1A). In the presence of S9, excessive toxicity was observed at the 132.5 mg/ml concentration level and above as measured by Day 2 RSG. The remaining concentration levels had RSG values ranging from 15 to 95% (Table 1B). Based upon the results of this assay, concentrations in the range of 10 to 120 mg/ml were selected for the initial mutagenicity assay both in the absence and presence of S9. - Remarks on result:
- other: other: The cell line, TK +/- -3.7.2C clonal line of L5178Y mouse lymphoma cells were used in the study
- Remarks:
- Migrated from field 'Test system'.
Any other information on results incl. tables
None
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information):
negative
Based upon the frequency of TK-/- mutants in the treated cultures, it was concluded that ethylbenzene was non-mutagenic in the absence and presence of S9 in the assay system employed. - Executive summary:
Ethylbenzene was evaluated in anin vitromouse lymphoma (L5178Y TK+/-) forward mutation assay. The genotoxic potential of the test material was assessed in two independent assays at concentrations ranging from 10 to 120 mg/ml in the absence and presence of an externally supplied metabolic activation (S9) system. The highest concentration tested in an initial toxicity assay (i.e., 1060 mg/ml) was the limit dose of 10 mM and exceeded the solubility of the test material. There were no significant increases in mutant frequency in the test material treated cultures as compared to the solvent controls in the absence or the presence of S9. The adequacy of the experimental conditions for detection of induced mutation was confirmed by employing positive control chemicals, methyl methanesulfonate for assays without S9 and 20-methylcholanthrene for assays with S9. Negative control cultures were treated with the solvent used to dissolve the test material (i.e., dimethyl sulfoxide). Based upon the frequency of TK -/- mutants in the treated cultures, it was concluded that ethylbenzene was non-mutagenic in the mouse lymphoma assay.
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