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EC number: 204-127-4 | CAS number: 116-15-4
- 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 bacteria
- Remarks:
- Type of genotoxicity: gene mutation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- GLP compliance:
- yes
- Type of assay:
- bacterial reverse mutation assay
Test material
- Reference substance name:
- Hexafluoropropene
- EC Number:
- 204-127-4
- EC Name:
- Hexafluoropropene
- Cas Number:
- 116-15-4
- Molecular formula:
- C3F6
- IUPAC Name:
- 1,1,2,3,3,3-hexafluoroprop-1-ene
- Details on test material:
- - Purity: 99.998%
Constituent 1
Method
Species / strainopen allclose all
- Species / strain / cell type:
- S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
- Species / strain / cell type:
- E. coli WP2 uvr A
- Metabolic activation:
- with and without
- Metabolic activation system:
- Aroclor-induced rat liver S9
- Test concentrations with justification for top dose:
- 0, 0.026, 0.078, 0.23, 0.69, 2.8, 8.3 and 25 mmoles/L
Controlsopen allclose all
- Untreated negative controls:
- yes
- Remarks:
- ambient air
- Negative solvent / vehicle controls:
- no
- Positive control substance:
- other: 2-aminoanthracene with activation
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: 2-nitrofluorene, sodium azide, 9-aminoacridine, and methyl methanesulfonate without activation
- Details on test system and experimental conditions:
- METHOD OF APPLICATION: The test system was exposed to the test substance via the desiccator methodology, a modification of the plate incorporation methodology.
DURATION: 48-72 hours
NUMBER OF REPLICATIONS: 3 - Evaluation criteria:
- For each replicate plating, the mean and standard deviation of the number of revertants per plate were calculated and are reported.
For the test substance to be evaluated positive, it must have caused a dose-related increase in the mean revertants per plate of at least one tester strain over a minimum of two increasing concentrations of test substance. Data sets for tester strains TA1535 and TA1537 were judged positive if the increase in mean revertants at the peak of the dose response was greater than or equal to 3.0-times the mean vehicle control value. Data sets for tester strains TA98, TA100 and WP2 uvrA were judged positive if the increase in mean revertants at the peak of the dose response was greater than or equal to 2.0-times the mean vehicle control value.
An equivocal response is a biologically relevant increase in a revertant count that partially meets the criteria for evaluation as positive. This could be a dose-responsive increase that does not achieve the respective threshold cited above or a non-dose responsive increase that is equal to or greater than the respective threshold cited. A response was evaluated as negative, if it is neither positive nor equivocal.
Results and discussion
Test resultsopen allclose all
- Species / strain:
- S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Species / strain:
- E. coli WP2 uvr A
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
Any other information on results incl. tables
(Without Activation)
|
Mean Revertants Per Plate |
||||
Strain TA98 |
Strain TA100 |
Strain TA1535 |
Strain 1537 |
Strain WP2uvrA
|
|
HFP |
|
|
|
|
|
0 mmole/ |
12 |
91 |
10 |
4 |
33 |
25 mmole/L |
0 |
0 |
0 |
0 |
0 |
8.3 mmole/L |
2 |
5 |
0 |
0 |
19 |
2.8 mmole/L |
10 |
59 |
18 |
5 |
20 |
0.69 mmole/L |
8 |
82 |
9 |
6 |
22 |
0.23 mmole/L |
11 |
72 |
12 |
4 |
26 |
0.078 mmole/L |
10 |
98 |
9 |
4 |
23 |
0.026mmole/L |
10 |
97 |
10 |
6 |
28 |
Positive control name |
|
|
|
|
|
2-nitrofluorene (1 µg) |
183 |
|
|
|
|
sodium azide(1 µg)
|
|
901 |
691 |
|
|
9-Aminoacridine(75 µg)
|
|
|
|
462 |
|
methyl methanesulfonate(1000 µg)
|
|
|
|
|
510 |
(With Activation)
|
Mean Revertants Per Plate |
||||
Strain TA98 |
Strain TA100 |
Strain TA1535 |
Strain 1537 |
Strain WP2uvrA
|
|
HFP |
|
|
|
|
|
0 mmole/ |
15 |
105 |
14 |
6 |
38 |
25 mmole/L |
0 |
0 |
0 |
0 |
0 |
8.3 mmole/L |
1 |
1 |
0 |
0 |
18 |
2.8 mmole/L |
12 |
71 |
11 |
5 |
25 |
0.69 mmole/L |
16 |
89 |
11 |
3 |
30 |
0.23 mmole/L |
20 |
78 |
11 |
4 |
31 |
0.078 mmole/L |
15 |
93 |
14 |
5 |
31 |
0.026mmole/L |
13 |
96 |
11 |
7 |
30 |
Positive control name |
|
|
|
|
|
2-aminoanthracene (1 µg) |
523 |
|
208 |
59 |
|
2-aminoanthracene (2 µg) |
|
1762 |
|
|
|
2-aminoanthracene (10 µg) |
|
|
|
|
241 |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information):
negative
HFP was not mutagenic in the Ames test.
The study and the conclusions which are drawn from it fulfil the quality criteria (validity, reliability, repeatability). - Executive summary:
The test substance was tested in the Bacterial Reverse Mutation Assay Using Gas-Phase Exposure using Salmonella typhimurium tester strains TA98, TA100, TA1535 and TA1537 and Escherichia coli tester strain WP2uvrA in the presence and absence of Aroclor-induced rat liver S9. The assay was performed in two phases, using the desiccator method, a modification of the plate incorporation method. The first phase, the preliminary toxicity assay, was used to establish the dose-range for the mutagenicity assay. The second phase, the mutagenicity assay was used to evaluate the mutagenic potential of the test substance.
Dosing chamber analysis for concentration and stability was not conducted. The interpretation of the study data was based on the nominal dose levels and not on the actual test substance concentration in the exposure chambers as confirmed by analytical analysis. Nevertheless, toxicity in the assay demonstrated that the test system was dosed up to the regulatory-required level. Ambient air was used as the negative control.
In the preliminary toxicity assay (Experiment A1), the dose levels tested were 1.4, 4.2, 6.9, 14, 21, 28 and 37 mmoles/L. No precipitate was observed. Toxicity was observed beginning at 1.4, 4.2, 6.9, 14 or 21 mmoles/L. Based on the findings of the preliminary toxicity assay, the maximum dose plated in the mutagenicity assay was 25 mmoles/L.
In the mutagenicity assay (Experiment B1), no positive mutagenic response was observed. The dose levels tested were 0.026, 0.078, 0.23, 0.69, 2.8, 8.3 and 25 mmoles/L. No precipitate was observed. Toxicity was observed beginning at 8.3 or at 25 mmoles/L.
The results of the Bacterial Reverse Mutation Assay Using Gas-Phase Exposure indicate that, under the conditions of this study, the test substance did not exhibit any mutagenic responses in either the presence or absence of Aroclor-induced rat liver S9. Therefore, the test substance was concluded to be negative in this assay.
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