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EC number: 222-321-7 | CAS number: 3425-61-4
- 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 cytogenicity / micronucleus study
- Remarks:
- Type of genotoxicity: other: chromosome aberration and aneuploidy
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 03 January 2012 - 06 April 2012
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: 1a: Compliant to GLP and testing guidelines; adequate consistence between data, comments and conclusions.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 012
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: OECD Guideline 487 (In vitro micronucleus)
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- in vitro mammalian cell micronucleus test
Test material
- Reference substance name:
- tert-pentyl hydroperoxide
- EC Number:
- 222-321-7
- EC Name:
- tert-pentyl hydroperoxide
- Cas Number:
- 3425-61-4
- Molecular formula:
- C5H12O2
- IUPAC Name:
- 2-methylbutane-2-peroxol
- Test material form:
- other: liquid
- Details on test material:
- - Name of test material: Tert-amyl hydroperoxide
- Physical state: colorless liquid
- Lot/batch No.: 11011D1280
- Analytical purity: 83.1%
- Water content: 12 %
- Expiry date: 01 February 2013
- Storage condition: at room temperature.
Constituent 1
Method
- Target gene:
- Not applicable (not a gene mutation assay).
Species / strain
- Species / strain / cell type:
- mouse lymphoma L5178Y cells
- Details on mammalian cell type (if applicable):
- - Type and identity of media: cryoprotective medium
- Properly maintained: yes
- Periodically checked for Mycoplasma contamination: yes - Additional strain / cell type characteristics:
- not applicable
- Metabolic activation:
- with and without
- Metabolic activation system:
- rat liver S9 mix
- Test concentrations with justification for top dose:
- Experiments without S9 mix
. 2.3, 4.7, 9.4, 18.8, 37.5 and 75 µg/mL in the first experiment,
. 2.5, 5, 10, 15, 20, 25, 30 and 40 µg/mL in the second experiment.
Experiments with S9 mix :
. 2.3, 4.7, 9.4, 18.8, 37.5 and 75 µg/mL for the first experiment,
. 4.7, 9.4, 18.8, 28.2, 37.5 and 75 µg/mL for the second experiment,
. 5, 10, 20, 30, 35, 40, 45 and 50 µg/mL for the third experiment. - Vehicle / solvent:
- - Vehicle used: dimethylsulfoxide
- Justification for choice: using a test item concentration of 500 mg/mL in DMSO and a treatment volume of 20 µL/2 mL culture medium, the highest recommended dose-level of 5000 µg/mL was achievable.
Controls
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: mitomycin C, colchicine (-S9 mix); cyclophosphamide (+S9 mix)
- Details on test system and experimental conditions:
- METHOD OF APPLICATION: in medium
DURATION
see Executive summary
NUMBER OF CELLS EVALUATED: 2000/dose
DETERMINATION OF CYTOTOXICITY
- Method: population doubling - Evaluation criteria:
- The biological relevance of the results should be considered first. Statistical methods are used as an aid in evaluating the test results but should not be the only determinant of a positive response. A result is considered as positive if at least a 2.5-fold increase in the number of micronucleated cells in comparison to the concurrent control is observed, with a statistically significant difference, at one or more concentrations. Concentration-related increases in the frequency of micronucleated cells and comparison to the vehicle control historical data will also be taken into account.
When inconclusive results are observed, or in case of toxic items when the highest analyzable dose-level does not exhibit about 50% toxicity, additional confirmatory experiments may be needed.
Results and discussion
Test resultsopen allclose all
- Species / strain:
- mouse lymphoma L5178Y cells
- Metabolic activation:
- without
- Genotoxicity:
- ambiguous
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Species / strain:
- mouse lymphoma L5178Y cells
- Metabolic activation:
- with
- Genotoxicity:
- positive
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information):
ambiguous without metabolic activation
positive with metabolic activation
The test item induced chromosome damage, or damage to the cell division apparatus, in cultured L5178Y TK+/- mouse lymphoma cells, in the presence of a rat metabolizing system. In the absence of a rat metabolising system, its potential to induced chromosome damage, or damage to the cell division apparatus, remained equivocal. - Executive summary:
The objective of this study was to evaluate the potential of the test item to induce an increase in the frequency of micronucleated cells,in L5178Y TK+/-mouse lymphoma cells. The test was performed in accordance with OECD 487 guideline, and was GLP compliance.
Methods
After a preliminary toxicity test, the test item was tested in three independent experiments, with and/or without a metabolic activation system, the S9 mix, prepared from a liver microsomal fraction (S9 fraction) of rats induced with Aroclor 1254, as follows:
First experiment
Second experiment
Third experiment
Without S9 mix
3 h treatment +
24 h recovery24 h treatment +
20 h recoveryWith S9 mix
3 h treatment +
24 h recovery3 h treatment +
24 h recovery3 h treatment +
24 h recoveryEach treatment was coupled to an assessment of cytotoxicity at the same dose-levels. Cytotoxicity was evaluated by determining the PD (Population Doubling) of cells and quality of the cells on the slides has also been taken into account.
The test item was dissolved in dimethylsulfoxide (DMSO).
Results
The mean frequencies of micronucleated cells for the vehicle controls were as specified in the acceptance criteria, and positive controls showed clear unequivocal increases in the frequency of micronucleated cells. The study was therefore considered to be valid.
Since the test item was found severely cytotoxic in the preliminary test, the selection of the highest dose-level to be used in the main experiments was based on the level of toxicity, according to the criteria specified in the international guidelines.
Experiments without S9 mix
The dose-levels used for treatment were as follows:
. 2.3, 4.7, 9.4, 18.8, 37.5 and 75 µg/mL in the first experiment,
. 2.5, 5, 10, 15, 20, 25, 30 and 40 µg/mL in the second experiment.
Cytotoxicity
Following the 3-hour treatment, a marked to severe toxicity was observed at dose-levels = 37.5 µg/mL as shown by a 62 to 100% decrease in the PD.
Following the 24-hour treatment, a slight to marked toxicity was observed at 30 and 40 µg/mL as shown by a 32% and 72% decrease in the PD, respectively.
Micronucleus analysis
The dose-levels selected for micronucleus analysis were:
. 4.7, 9.4 and 18.8 µg/mL for the 3-hour treatment, higher dose-levels being too cytotoxic,
. 10, 20 and 30 µg/mL for the 24-hour treatment, higher dose-levels being too cytotoxic.
No significant increase in the frequency of micronucleated cells was noted after the 3-hour treatment.
Following the 24-hour treatment, an increase in the frequency of micronucleated cells (exceeding the threshold of 2.5-fold the vehicle control value) was observed at 30 µg/mL. This increase was statistically significant (p < 0.05). However, the corresponding micronucleated cells remained within the historical data range of the vehicle control (5 micronucleated cells in 1000 cells versus 0-5 for the historical data). Consequently, this increase is considered as equivocal.
Experiments with S9 mix
The dose-levels used for treatment were as follows:
. 2.3, 4.7, 9.4, 18.8, 37.5 and 75 µg/mL for the first experiment,
. 4.7, 9.4, 18.8, 28.2, 37.5 and 75 µg/mL for the second experiment,
. 5, 10, 20, 30, 35, 40, 45 and 50 µg/mL for the third experiment.
Cytotoxicity
Following the first experiment, a moderate to severe toxicity was observed at dose-levels = 37.5 µg/mL as shown by a 45 to 100% decrease in the PD.
Following the second experiment, a slight to severe toxicity was noted at dose-levels = 9.4 µg/mL as shown by a 32% to 100% decrease in the PD.
Following the third experiment, a slight to severe toxicity was observed at dose-levels = 20 µg/mL as shown by a 25% to 100% decrease in the PD.
Micronucleus analysis
The dose-levels selected for micronucleus analysis were as follows:
. 9.4, 18.8 and 37.5 µg/mL for the first experiment, the latter inducing a 45% decrease in the PD,
. 4.7, 9.4 and 18.8 µg/mL for the second experiment, the latter inducing a 55% decrease in the PD,
. 10, 20 and 30 µg/mL for the third experiment, the latter inducing a 57% decrease in the PD.
In all experiments, slight increases in the frequency of micronucleated cells (exceeding the threshold of 2.5-fold the vehicle control value) were observed. These increases reached statistical significance in the first and third experiments and were dose-related. Therefore, these increases being reproducible in independent experiments, they were considered to be biologically significant.
Conclusion
The test item induced chromosome damage, or damage to the cell division apparatus, in cultured L5178Y TK+/-mouse lymphoma cells, in the presence of a rat metabolizing system. In the absence of a rat metabolising system, its potential to induced chromosome damage, or damage to the cell division apparatus, remained equivocal.
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