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EC number: 308-783-3 | CAS number: 98510-75-9
- 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 vitro
Administrative data
- Endpoint:
- in vitro gene mutation study in mammalian cells
- Remarks:
- Type of genotoxicity: gene mutation
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 2009-10-21 to 2009-12-14
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 476 (In Vitro Mammalian Cell Gene Mutation Test)
- Version / remarks:
- 1997
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.17 (Mutagenicity - In Vitro Mammalian Cell Gene Mutation Test)
- Version / remarks:
- 2008
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- mammalian cell gene mutation assay
Test material
- Reference substance name:
- C8-18 AAPB
- IUPAC Name:
- C8-18 AAPB
Constituent 1
Method
- Target gene:
- Thymidine Kinase Locus
Species / strain
- Species / strain / cell type:
- mouse lymphoma L5178Y cells
- Details on mammalian cell type (if applicable):
- - Type and identity of media: RPMI
- Periodically checked for Mycoplasma contamination: yes
- Periodically checked for karyotype stability: yes
- Periodically "cleansed" against high spontaneous background: yes - Additional strain / cell type characteristics:
- other: Clone 3.7.2C
- Metabolic activation:
- with and without
- Metabolic activation system:
- Rat liver S9
- Test concentrations with justification for top dose:
- Pre-Experiment: 39.1; 78.1; 156.3; 312.5; 625; 1250; 2500; 5000 µg/mL
Experiment I:
without S9 mix (4 hours treatment): 2.4; 4.9; 9.8; 19.5; 39.0; 58.5; 78.0 µg/mL; evaluated: 2.4; 4.9; 9.8; 39 µg/mL
with S9 mix (4 hours treatment): 4.9; 9.8; 19.5; 39.0; 78.0; 117.0; 156.0 µg/mL; evaluated: 4.9; 9.8; 19.5; 39.0; 78.0 µg/mL
Experiment II:
without metabolic activation (24 hours treatment): 2.5; 5.0; 10.0; 20.0; 40.0; 50.0; 60.0 µg/mL; evaluated: 10; 20; 40; 50; 60 µg/mL
with metabolic activation (4 hours treatment): 10.0; 20.0; 40.0; 80.0; 100.0; 110.0; 120.0 µg/mL; evaluated: 40, 80, 100, 110, 120 µg/mL - Vehicle / solvent:
- - Vehicle(s)/solvent(s) used: deionised water (10 %)
- Justification for choice of solvent/vehicle: solubility properties
Controlsopen allclose all
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- Remarks:
- deionised water
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- methylmethanesulfonate
- other: without metabolic activation
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- Remarks:
- deionised water
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- cyclophosphamide
- other: with metabolic activation
- Details on test system and experimental conditions:
- METHOD OF APPLICATION:
DURATION
- Exposure duration: Experiment I: 4 hours with and without metabolic activation
Experiment II: 24 hours without metabolic activation, 4 hours with metabolic activation
- Expression time (cells in growth medium): 48 hours
- Selection time (if incubation with a selection agent): 10 to 15 days
SELECTION AGENT (mutation assays): RPMI 1640 medium by addition of 5 µg/mL TFT (Trifluorothymidine)
NUMBER OF REPLICATIONS: 2
NUMBER OF CELLS EVALUATED: approx. 4000 cells per well
DETERMINATION OF CYTOTOXICITY
- Method: relative total growth
- Evaluation criteria:
- A test item is classified as mutagenic if the induced mutation frequency reproducibly exceeds a threshold of 126 colonies per 106 cells above the corresponding solvent control.
A relevant increase of the mutation frequency should be dose-dependent.
A mutagenic response is considered to be reproducible if it occurs in both parallel cultures.
However, in the evaluation of the test results the historical variability of the mutation rates in the solvent controls of this study are taken into consideration.
Results of test groups are generally rejected if the relative total growth is less than 10 % of the vehicle control unless the exception criteria specified by the IWGT recommendations are fulfilled.
Whenever a test item is considered mutagenic according to the above mentioned criteria, the ratio of small versus large colonies is used to differentiate point mutations from clastogenic effects. If the increase of the mutation frequency is accompanied by a reproducible and dose dependent shift in the ratio of small versus large colonies clastogenic effects are indicated. - Statistics:
- Linear regression analysis (least squares) using SYSTAT11 (SYSTAT Software, Inc., 501, Canal Boulevard, Suite C, Richmond, CA 94804, USA)
Results and discussion
Test results
- Species / strain:
- mouse lymphoma L5178Y cells
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- TEST-SPECIFIC CONFOUNDING FACTORS
- Effects of pH: not effected
- Effects of osmolality: not increased
- Precipitation: No
- Other confounding effects: None
RANGE-FINDING/SCREENING STUDIES:
The highest concentration used in the pre-test was chosen with regard to the solubility of the test item in deionised water. Test item concentrations between 39.1 and 5000 µg/mL were used to evaluate toxicity in the presence (4 h treatment) and absence (4 h and 24 h treatment) of metabolic activation.
Strong toxic effects were observed at 78.1 µg/mL and above in the absence of metabolic activation (4 h treatment) and at 312.5 µg/mL and above in the presence of metabolic activation. Following continuous treatment (24 hours) toxic effects as described above occurred already at the lowest concentration of 39.1 µg/mL and above.
The test medium was checked for precipitation at the end of each treatment period (4 or 24 hours) before the test item was removed. No precipitation occurred up to the maximum concentration with and without metabolic activation at both treatment intervals.
The dose range of the main experiments was limited by toxicity of the test item. The individual concentrations were generally spaced by a factor of 2.0. A closer spacing was used in the upper concentration range to cover toxic effects more closely. A very narrow dose spacing was used in the second experiment with and without metabolic activation to cover the recommended cytotoxic range of approximately 10-20% relative total growth.
COMPARISON WITH HISTORICAL CONTROL DATA:
In experiment II the mutant frequency exceeded the range of the historical solvent control data at several test points without metabolic activation (both cultures) and at one test point with metabolic activation (culture I). However, the threshold described above was not reached at any test point of the second experiment and no dose dependent increase was indicated by statistical analysis.
ADDITIONAL INFORMATION ON CYTOTOXICITY:
Relevant cytotoxic effects indicated by a relative total growth of less than 50 % in both parallel cultures were observed in the absence of metabolic activation at 39 µg/mL in experiment I following 4 hour treatment and at 40 µg/mL and above in experiment II following 24 hours treatment. In the presence of metabolic activation toxic effects as described above occurred at 100 µg/mL and above in experiment II. No reproducible cytotoxic effects were noted in the first experiment with metabolic activation. The recommended toxic range of approximately 10-20 % RTG was covered in the second experiment with and without metabolic activation.
The isolated minor reduction of the relative total growth to 43.5 % in the first culture of experiment I with metabolic activation was not considered a real toxic effect since no comparable reduction was observed in the parallel culture under identical conditions. - Remarks on result:
- other: all strains/cell types tested
- Remarks:
- Migrated from field 'Test system'.
Any other information on results incl. tables
Summary Table
relative | mutant | relative | mutant | |||||
conc. µg | S9 | total | colonies/ | total | colonies/ | |||
per mL | mix | growth | 106cells | threshold | growth | 106cells | threshold | |
Column | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 |
Experiment I / 4 h treatment | culture I | culture II | ||||||
Solv. control with water | - | 100.0 | 147 | 273 | 100.0 | 141 | 267 | |
Pos. control with MMS | 19.5 | - | 32.4 | 424 | 273 | 23.7 | 403 | 267 |
Test item | 2.4 | - | 131.7 | 122 | 273 | 67.5 | 209 | 267 |
Test item | 4.9 | - | 122.7 | 134 | 273 | 129.3 | 139 | 267 |
Test item | 9.8 | - | 103.9 | 137 | 273 | 126.0 | 104 | 267 |
Test item | 19.5 | - | 43.7 | 275 | 273 | 96.9 | 96 | 267 |
Test item | 39.0 | - | 31.1 | 187 | 273 | 39.3 | 181 | 267 |
Test item | 58.5 | - | culture was not continued# | culture was not continued# | ||||
Test item | 78.0 | - | culture was not continued# | culture was not continued# | ||||
Solv. control with water | + | 100.0 | 130 | 256 | 100.0 | 141 | 267 | |
Pos. control with CPA | 3.0 | + | 61.5 | 232 | 256 | 90.0 | 250 | 267 |
Pos. control with CPA | 4.5 | + | 44.8 | 320 | 256 | 54.6 | 348 | 267 |
Test item | 4.9 | + | 66.2 | 164 | 256 | 137.6 | 99 | 267 |
Test item | 9.8 | + | 104.3 | 140 | 256 | 134.1 | 146 | 267 |
Test item | 19.5 | + | 57.7 | 202 | 256 | 125.6 | 134 | 267 |
Test item | 39.0 | + | 111.4 | 105 | 256 | 147.5 | 83 | 267 |
Test item | 78.0 | + | 43.5 | 149 | 256 | 108.2 | 154 | 267 |
Test item | 117.0 | + | culture was not continued# | culture was not continued# | ||||
Test item | 156.0 | + | culture was not continued# | culture was not continued# | ||||
Experiment II / 24 h treatment | culture I | culture II | ||||||
Solv. control with water | - | 100.0 | 158 | 284 | 100.0 | 153 | 279 | |
Pos. control with MMS | 13.0 | - | 19.2 | 569 | 284 | 25.0 | 573 | 279 |
Test item | 2.5 | - | culture was not continued## | culture was not continued## | ||||
Test item | 5.0 |
- | culture was not continued## | culture was not continued## | ||||
Test item | 10.0 | - | 65.9 | 217 | 284 | 78.7 | 264 | 279 |
Test item | 20.0 | - | 44.3 | 208 | 284 | 71.1 | 230 | 279 |
Test item | 40.0 | - | 33.1 | 173 | 284 | 45.8 | 208 | 279 |
Test item | 50.0 | - | 38.5 | 182 | 284 | 29.8 | 214 | 279 |
Test item | 60.0 | - | 20.7 | 209 | 284 | 16.2 | 241 | 279 |
Experiment II / 4 h treatment | culture I | culture II | ||||||
Solv. control with water | + | 100.0 | 164 | 290 | 100.0 | 145 | 271 | |
Pos. control with CPA | 3.0 | + | 52.2 | 355 | 290 | 25.0 | 312 | 271 |
Pos. control with CPA | 4.5 | + | 23.6 | 385 | 290 | 23.3 | 407 | 271 |
Test item | 10.0 | + | culture was not continued## | culture was not continued## | ||||
Test item | 20.0 | + | culture was not continued## | culture was not continued## | ||||
Test item | 40.0 | + | 75.5 | 171 | 290 | 102.9 | 189 | 271 |
Test item | 80.0 | + | 40.2 | 210 | 290 | 61.6 | 159 | 271 |
Test item | 100.0 | + | 47.1 | 133 | 290 | 49.0 | 149 | 271 |
Test item | 110.0 | + | 32.6 | 183 | 290 | 42.0 | 167 | 271 |
Test item | 120.0 | + | 22.0 | 203 | 290 | 29.0 | 201 | 271 |
Threshold = number of mutant colonies per 106cells of each solvent control plus 126
# culture
was not continued due to exceedingly severe cytotoxic effects
## culture
was not continued since a minimum of only four analysable concentrations
is required
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information):
negative
The test item did not induce mutations in the mouse lymphoma thymidine kinase locus assay using the cell line L5178Y in the absence and presence of metabolic activation. - Executive summary:
The study was performed to investigate the potential of C8 -18 AAPB to induce mutations at the mouse lymphoma thymidine kinase locus using the cell line L5178Y.
The assay was performed in two independent experiments, using two parallel cultures each. The first main experiment was performed with and without liver microsomal activation and a treatment period of 4 h. The second experiment was performed with a treatment period of 24 hours in the absence and 4 hours in the presence of metabolic activation.
The main experiments were evaluated at the following concentrations:
Experiment I:
without S9 mix: 2.4; 4.9; 9.8; 19.5; and 39.0 µg/mL
with S9 mix: 4.9; 9.8; 19.5; 39.0; and 78.0 µg/mLExperiment II:
without S9 mix: 10; 20; 40; 50; and 60 µg/mL
with S9 mix: 40; 80; 100; 110; and 120 µg/mL
Relevant cytotoxic effects indicated by a relative total growth of less than 50 % in both parallel cultures were observed in the absence of metabolic activation at 39 µg/mL in experiment I following 4 hour treatment and at 40 µg/mL and above in experiment II following 24 hours treatment. In the presence of metabolic activation toxic effects as described above occurred at 100 µg/mL and above in experiment II. No reproducible cytotoxic effects were noted in the first experiment with metabolic activation. The recommended toxic range of approximately 10-20 % RTG was covered in the second experiment with and without metabolic activation.
The isolated minor reduction of the relative total growth to 43.5 % in the first culture of experiment I with metabolic activation was not considered a real toxic effect since no comparable reduction was observed in the parallel culture under identical conditions.
No substantial and reproducible dose dependent increase of the mutation frequency was observed with and without metabolic activation. The mutation frequency did not reproducibly reach or exceed the threshold of 126 above the mutation frequency of the corresponding solvent control in any of the experimental parts. An isolated increase exceeding the threshold was noted in the first culture of experiment I without metabolic activation at 19.5 µg/mL. However, this increase was judged as irrelevant fluctuation since it was not reproduced in the parallel culture under identical experimental conditions. Furthermore, the increase was not dose dependent as indicated by the lacking statistical significance. In experiment II the mutant frequency exceeded the range of the historical solvent control data at several test points without metabolic activation (both cultures) and at one test point with metabolic activation (culture I). However, the threshold described above was not reached at any test point of the second experiment and no dose dependent increase was indicated by statistical analysis.
A linear regression analysis (least squares) was performed to assess a possible dose dependent increase of mutant frequencies using SYSTATâ11statistics software. No significant dose dependent trend of the mutation frequency indicated by a probability value of <0.05 was determined in all experimental groups.
In this study the range of the solvent controls was from 130 up to 164 mutant colonies per 106cells; the range of the groups treated with the test item was from 83 up to 275 mutant colonies per 106cells. The solvent controls remained within the range of the historical data.
Methylmethanesulfonate (19.5 µg/mL in experiment I and 13.0 µg/mL in experiment II) and cyclophosphamide (3.0 µg/mL and 4.5 µg/mL in both main experiments) were used as positive controls and showed a distinct increase in induced total mutant colonies at acceptable levels of toxicity with at at least one of the concentrations of the controls.
There was no concentration related positive response of induced mutant colonies over background.
This study is classified as acceptable. This study satisfies the requirement for Test Guidelines Ninth Addendum to the OECD Guidelines for the Testing of Chemicals, February 1998, adopted July 21, 1997, Guideline No. 476 "In vitro Mammalian Cell Gene Mutation Test“ and Commission Regulation (EC) No. 440/2008 B.17: ”Mutagenicity –In vitro Mammalian Cell Gene Mutation Test“, dated May 30, 2008 for in vitro mutagenicity (mammalian forward gene mutation) data.
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