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EC number: 220-076-0 | CAS number: 2623-23-6
- 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 bacteria
- Remarks:
- Type of genotoxicity: gene mutation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The study was performed according to OECD 471 and GLP, but the plate incorporation method was used for both experiments
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 999
- Report date:
- 1999
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.13/14 (Mutagenicity - Reverse Mutation Test Using Bacteria)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- bacterial reverse mutation assay
Test material
- Reference substance name:
- Menthyl acetate
- EC Number:
- 201-911-8
- EC Name:
- Menthyl acetate
- Cas Number:
- 89-48-5
- Molecular formula:
- C12H22O2
- IUPAC Name:
- Menthyl acetate
Constituent 1
Method
- Target gene:
- Histidine
Species / strain
- Species / strain / cell type:
- other: TA1535, TA1537, TA102, TA98 and TA100
- Metabolic activation:
- with and without
- Metabolic activation system:
- 10% liver S9 in standard co-factors
- Test concentrations with justification for top dose:
- Preliminary toxicity test: 0.15, 0.5, 1.5, 5, 15, 50, 150, 500, 1500 and 5000 µg/plate
Experiment I: 5, 15, 50, 150, 500, 1500 and 5000 µg/plate
Experiment II: 15, 50, 150, 500, 1500 and 5000 µg/plate - Vehicle / solvent:
- - Vehicle(s)/solvent(s) used: dimethyl sulphoxide
- Justification for choice of solvent/vehicle: not reported
Controls
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: N-ethyl-N'-nitro-N-nitrosoguanidine (TA100, TA1535), 9-Aminoacridine (TA1537), Mitomycin C (TA102), 4-Nitroquinoline-l-oxide (TA98)
- Details on test system and experimental conditions:
- METHOD OF APPLICATION: in agar (plate incorporation)
DURATION
- Exposure duration: 48 hours
NUMBER OF REPLICATIONS: 3
NUMBER OF CELLS EVALUATED: not reported
DETERMINATION OF CYTOTOXICITY
- Method: visible reduction in the bacterial background lawn, reduction in colony frequency - Evaluation criteria:
- The test material may be considered to be positive in this test system if the following criteria are met:
The test material should have induced a reproducible, dose-related and statistically (Dunnett's method of linear regression) significant increase in the revertant count in at least one strain of bacteria. - Statistics:
- Dunnett's method of linear regression
Results and discussion
Test results
- Species / strain:
- other: TA1535, TA1537, TA102, TA98 and TA100
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- Visible reduction in the bacterial background lawn in tester strains TA100 and TA1535 with and without S9 (first evidence of a weakened bacterial background lawn at 1500 pg/plate). Tested up to the maximum recommended dose of 5000 µg/plate.
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- TEST-SPECIFIC CONFOUNDING FACTORS
- Precipitation: No test material precipitate was observed on the plates at any of the doses tested in either the presence or absence of S9-mix.
RANGE-FINDING/SCREENING STUDIES: The test material was non-toxic to the bacterial background lawn but did cause a reduction in colony frequency at 5000 µg/plate (particularly after the addition of S9-mix).
COMPARISON WITH HISTORICAL CONTROL DATA: Done.
ADDITIONAL INFORMATION ON CYTOTOXICITY: The test material caused a visible reduction in the bacterial background lawn in tester strains TA100 and TA1535 both with and without metabolic activation. The first evidence of a weakened bacterial background lawn was observed at 1500 µg/plate. The test material was tested up to the maximum recommended dose of 5000 µg/plate. No test material precipitate was observed on the plates at any of the doses tested in either the presence or absence of S9-mix. - Remarks on result:
- other: all strains/cell types tested
- Remarks:
- Migrated from field 'Test system'.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information):
negative
The test material was considered to be non-mutagenic under the conditions of this test. - Executive summary:
Salmonella typhimurium strains TA1535, TA1537, TA102, TA98 and TA100 were treated with the test material using the plate incorporation method at up to seven dose levels, in triplicate, both with and without the addition of a rat liver homogenate metabolising system (10% liver S9 in standard co-factors). The dose range for the first experiment was determined in a preliminary toxicity assay and ranged from 5 to 5000 µg/plate depending on bacterial strain type and presence or absence of S9-mix. The experiment was repeated on a separate day using a dose range based on results observed in Experiment 1, fresh cultures of the bacterial strainsand fresh test material formulations. The method used conforms with the OECD TG471 and the test was performed under GLP. Extra dose levels were included (where applicable) to allow for the toxicity of the test material and to ensure there were a minimum of four non-toxic doses plated out.
The vehicle (dimethyl sulphoxide) control plates gave counts of revertant colonieswithin the normal range. All of the positive control chemicals used in the test induced marked increases in the frequency of revertant colonies, both with and without metabolic activation. Thus, the sensitivity of the assay and the efficacy of the S9-mix were validated. The test material caused a visible reduction in the bacterial background lawn in testerstrains TA100 and TA1535 both with and without metabolic activation. The first evidence of a weakened bacterial background lawn was observed at 1500 µg/plate. The test material was tested up to the maximum recommended dose of 5000 µg/plate. No test material precipitate was observed an the plates at any of the doses tested in either the presence or absente of S9-mix. No significant increases in the frequency of revertant colonies were recorded for any of the bacterial strains, with any dose of the test material, either with or without metabolic activation. The test material was considered to be non-mutagenic under the conditions of this test.
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