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EC number: 271-360-6 | CAS number: 68551-08-6
- 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 cytogenicity / micronucleus study
- Remarks:
- Type of genotoxicity: micronucleus
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Acceptable, well-documented stury report equivalent or similar to OECD guideline 487: GLP
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 016
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 487 (In vitro Mammalian Cell Micronucleus Test)
- Deviations:
- no
- GLP compliance:
- yes
- Type of assay:
- in vitro mammalian cell micronucleus test
Test material
- Reference substance name:
- Isotridecan-1-ol
- EC Number:
- 248-469-2
- EC Name:
- Isotridecan-1-ol
- Cas Number:
- 27458-92-0
- Molecular formula:
- C13H28O
- IUPAC Name:
- 3,5,7 trimethyl decanol
- Reference substance name:
- Isododecan-1-ol
- Molecular formula:
- C12H26O
- IUPAC Name:
- Isododecan-1-ol
- Reference substance name:
- Isotetradecan-1-ol
- Molecular formula:
- C14H30O
- IUPAC Name:
- Isotetradecan-1-ol
- Reference substance name:
- Isoundecan-1-ol
- EC Number:
- 257-376-6
- EC Name:
- Isoundecan-1-ol
- Cas Number:
- 51750-47-1
- Molecular formula:
- C11H24O
- IUPAC Name:
- 3,5 dimethyl nonanol-1
- Reference substance name:
- Water
- EC Number:
- 231-791-2
- EC Name:
- Water
- Cas Number:
- 7732-18-5
- Molecular formula:
- H20
- IUPAC Name:
- water
- Test material form:
- liquid
Constituent 1
Constituent 2
Constituent 3
Constituent 4
Constituent 5
Method
- Target gene:
- Not applicable
Species / strain
- Species / strain / cell type:
- Chinese hamster Ovary (CHO)
- Details on mammalian cell type (if applicable):
- - Type and identity of media: F-12K Medium supplemented with 10% fetal bovine serum
- Properly maintained: yes - Additional strain / cell type characteristics:
- not specified
- Metabolic activation:
- with and without
- Metabolic activation system:
- S9 fraction of Aroclor induced rat liver
- Test concentrations with justification for top dose:
- Rangefinder cytotoxicity:
(+S9): (0.006, 0.02, 0.06, 0.2, 0.6, 2 ul/mL)
(-S9): (0.006, 0.02, 0.06, 0.2, 0.6, 2 ul/mL)
Micronucleus Test:
Short term exposure (0.004, 0.006, 0.008, 0.02, and 0.04 uL/ml)
Long term exposure (0.004, 0.006, 0.008, 0.02, and 0.04 uL/ml) - Vehicle / solvent:
- DMSO
Controls
- Negative solvent / vehicle controls:
- yes
- Remarks:
- DMSO alone
- Positive controls:
- yes
- Positive control substance:
- cyclophosphamide
- mitomycin C
- other: cytosine B-D-arabinofuranoside and digitonin
- Details on test system and experimental conditions:
- METHOD OF APPLICATION:
- Cells were plated at a seeding density of 1.25x104 cells/well in 48-well plates for both cytotoxicity and test runs, allowed to grow for 24 hours post-seeding, and then exposed to the test article and controls. Test article was added to the wells with or without S9 fraction.
DURATION
Short Exposure:
- Exposure duration: 3 hours
- Expression time (cells in growth medium): 21 hours
Long Exposure (absence of S9):
- Exposure duration: 21 hours
- Expression time (cells in growth medium): 21 hours
NUMBER OF REPLICATIONS:
- 3 replicate wells
STAIN
- Microflow Kit, using EMA (nucleic acid dye A solution), PeakFlow Green Flow Cytometry Reference Beads
DETERMINATION OF CYTOTOXICITY
- Method: assessment of relative increase in cell counts (RICC) - Evaluation criteria:
- The data from the flow cytometer was collected and compared to the negative control. The sample in each well was analyzed for % of events that are EMA-positive total counts of nucleated events, total counts of hypodiploidy, total bead counts and total micronuclei counts. The data was assessed as follows:
-The percent hypodiploid counts in each well, percent micronuclei counts in each well, and the nuclei to bead ratio in each well was determined
-The fold change in hypodiploidy in each well, fold change in micronuclei in each well, and the fold change in %EMA positive cells in each well was determined
-The mean fold change in hypoploidy EMA positive cell and micronuclei was determined
-The cell viability was determined by dividing the mean nuclei-bead ratio of the test article by the mean nuclei-bead ratio of the negative control, and multiplying by 100
A test article is considered clearly positive if, in any of the experimental conditions examined: at least one of the test concentrations exhibits a statistically significant increase of 2-fold compared with the concurrent negative control, which is considered a biologically relevant induction in this system; if the increase is dose-related in at least one experimental condition when evaluated with an appropriate trend test; or if any of the results are outside the distribution of the historical negative control data.
A test article is considered clearly negative if, in all experimental conditions examined: none of the test concentrations exhibits a statistically significant increase compared with the concurrent negative control; or if there is no concentration-related increase when evaluated with an appropriate trend test. - Statistics:
- For cytotoxicity the mean % viability and standard deviation were calculated. The mean of fold change vs vehicle control (negative) control was determined. A Student’s paired T-test was performed to assess statistical significance (p≤0.01) between each tested concentration and the negative (vehicle) control.
Results and discussion
Test results
- Species / strain:
- Chinese hamster Ovary (CHO)
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- Short term exposure (0.04ul/mL)
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- Short term exposure - The test substance did not induce a statistically significant increase in micronuclei formation at any of the non-cytotoxic dose levels tested, with or without metabolic activation.
Long term exposure - The test substance did not induce a statistically significant increase in micronuclei formation at any of the dose levels tested without metabolic activation.
Any other information on results incl. tables
Table 1: Osmolality and pH of Exxal™ 13 at final concentrations in culture media (i.e. dosing solutions) were assessed in the presence and absence of S9.
-S9 | Osmolality | pH | ||
1% DMSO | 494 | 493 | 493 | 8.68 |
2µL/mL Exxal 13 | 445 | 448 | 451 | 8.64 |
+ S9 | Osmolality | pH | ||
1% DMSO | 470 | 467 | 465 | 8.59 |
2 µL/mL Exxal 13 | 437 | 435 | 435 | 8.56 |
Table 2: Cytotoxicity assessment of the test article in the rangefinder under a) short term exposure +S9 and b) long term exposure no S9.
a)
MEAN | SD | SEM | %CV | |
Vehicle | 100.0 | 12.1 | 7.0 | 12.1 |
1mM Digitonin | 14.3 | 1.6 | 0.9 | 10.9 |
0.006µL/mL Exxal 13 | 61.5 | 11.3 | 6.5 | 18.3 |
0.02 µL/mL Exxal 13 | 64.5 | 4.6 | 2.7 | 7.2 |
0.06 µL/mL Exxal 13 | 58.5 | 5.9 | 3.4 | 10.1 |
0.2 µL/mL Exxal 13 | 51.9 | 12.7 | 7.3 | 24.4 |
0.6 µL/mL Exxal 13 | 41.1 | 7.2 | 4.2 | 17.6 |
2 µL/mL Exxal 13 | 10.4 | 2.3 | 1.3 | 21.9 |
b)
MEAN | SD | SEM | %CV | |
Vehicle | 100.0 | 3.8 | 2.2 | 3.8 |
1mM Digitonin | 5.0 | 0.1 | 0.1 | 2.5 |
0.006µL/mL Exxal 13 | 87.9 | 20.2 | 11.7 | 23.0 |
0.02 µL/mL Exxal 13 | 75.1 | 24.2 | 14.0 | 32.2 |
0.06 µL/mL Exxal 13 | 5.0 | 0.3 | 0.1 | 5.1 |
0.2 µL/mL Exxal 13 | 5.2 | 0.5 | 0.3 | 9.9 |
0.6 µL/mL Exxal 13 | 5.5 | 0.2 | 0.1 | 4.0 |
2 µL/mL Exxal 13 | 4.8 | 0.7 | 0.4 | 14.8 |
Table 3: CHO-K1 cells were exposed to the a) positive control mytomycin C and b) the test article Exxal™ 13, for approximately 3 hours in the absence of S9, and then incubated for approximately 1.5 – 2.0 population doublings. Cells were assessed for micronuclei formation according to Section 12.j. Statistical significance if p ≤ 0.01.
a)
Exposure | Conc (µg/mL) |
Mean Fold Change EMA | Mean Fold Change MN | Mean Fold Change Hypoploid | Cell Viability (% of control) | T-Test p value | Statistically Significant MN Induction? |
Negative (Solvent) Control | 0 | 1.00 | 1.00 | 1.00 | 100.00 | N/A | N/A |
Mitomycin C | 0.2 | 0.78 | 1.87 | 1.29 | 94.2 | 0.0123 | NO |
2 | 3.03 | 11.01 | 2.03 | 56.41 | 0.0001 | YES |
b)
Exposure | Conc (µg/mL) |
Mean Fold Change EMA | Mean Fold Change MN | Mean Fold Change Hypoploid | Cell Viability (% of control) | T-Test p value | Statistically Significant MN Induction? |
Negative (Solvent) Control | 0 | 1.00 | 1.00 | 1.00 | 100.00 | N/A | N/A |
Exxal 13 | 0.004 | 1.05 | 1.19 | 1.38 | 96.05 | 0.1347 | NO |
0.006 | 5.11 | 1.19 | 1.11 | 94.20 | 0.1609 | NO | |
0.008 | 1.90 | 1.22 | 1.20 | 99.38 | 0.1296 | NO | |
0.02 | 1.37 | 1.23 | 1.17 | 103.45 | 0.0754 | NO | |
0.04 | 15.49 | 1.74 | 1.74 | 13.69 | 0.0084 | YES |
Table 4: CHO-K1 cells were exposed to the a) positive control cyclophosphamide and b) the test article Exxal™ 13, for approximately 3 hours in the presence of S9, and then incubated for approximately 1.5 – 2.0 population doublings. Cells were assessed for micronuclei formation according to Section 12.j. Statistical significance if p ≤ 0.01.
a)
Exposure | Conc (µg/mL) |
Mean Fold Change EMA | Mean Fold Change MN | Mean Fold Change Hypoploid | Cell Viability (% of control) | T-Test p value | Statistically Significant MN Induction? |
Negative (Solvent) Control | 0 | 1.00 | 1.00 | 1.00 | 100.00 | N/A | N/A |
Cyclo-phosphamide | 2 | 0.95 | 1.88 | 0.83 | 107.64 | <0.0001 | YES |
5 | 1.17 | 3.07 | 1.60 | 69.23 | <0.0001 | YES |
b)
Exposure | Conc (µg/mL) |
Mean Fold Change EMA | Mean Fold Change MN | Mean Fold Change Hypoploid | Cell Viability (% of control) | T-Test p value | Statistically Significant MN Induction? |
Negative (Solvent) Control | 0 | 1.00 | 1.00 | 1.00 | 100.00 | N/A | N/A |
Exxal 13 | 0.004 | 0.94 | 1.04 | 0.91 | 109.63 | 0.3828 | NO |
0.006 | 1.11 | 1.31 | 1.28 | 82.42 | 0.1101 | NO | |
0.008 | 1.15 | 1.03 | 1.14 | 90.76 | 0.7255 | NO | |
0.02 | 1.02 | 1.18 | 1.04 | 96.61 | 0.0129 | NO | |
0.04 | 0.57 | 1.04 | 0.92 | 175.40* | 0.382 | NO |
* data shows there was no increase in RICC suggesting this mean cell viability is false
Table 5: CHO-K1 cells were exposed to the a) positive control cytosine β-D-arabinofuranoside and b) the test article Exxal™ 13, for approximately 1.5 – 2.0 population doublings in the absence of S9. Cells were assessed for micronuclei formation according to Section 12.j. Statistical significance if p ≤ 0.01.
a)
Exposure | Conc (µg/mL) |
Mean Fold Change EMA | Mean Fold Change MN | Mean Fold Change Hypoploid | Cell Viability (% of control) | T-Test p value | Statistically Significant MN Induction? |
Negative (Solvent) Control | 0 | 1.00 | 1.00 | 1.00 | 100.00 | N/A | N/A |
Cytosineβ-D-arabino- furanoside |
0.04 | 0.74 | 2.32 | 1.76 | 70.19 | 0.0009 | YES |
0.4 | 1.42 | 5.52 | 2.63 | 39.50 | 0.0001 | YES |
b)
Exposure | Conc (µg/mL) |
Mean Fold Change EMA | Mean Fold Change MN | Mean Fold Change Hypoploid | Cell Viability (% of control) | T-Test p value | Statistically Significant MN Induction? |
Negative (Solvent) Control | 0 | 1.00 | 1.00 | 1.00 | 100.00 | N/A | N/A |
Exxal 13 | 0.004 | 0.84 | 1.19 | 1.21 | 97.38 | 0.161 | NO |
0.006 | 0.49 | 1.15 | 1.08 | 111.36 | 0.3034 | NO | |
0.008 | 0.51 | 1.13 | 1.20 | 98.76 | 0.2672 | NO | |
0.02 | 0.47 | 1.15 | 1.24 | 94.73 | 0.2479 | NO | |
0.04 | 1.83 | 1.10 | 0.85 | 41.68 | 0.5276 | NO |
Applicant's summary and conclusion
- Conclusions:
- The mammalian cell micronucleus test to assess the genotoxicity of Exxal 13 was negative.
- Executive summary:
Exxal 13 was examined for its potential to induce the formation of micronuclei in Chinese Hamster Ovary (CHO) cells, at both short (with and without S9 metabolic activation) and long (without S9 metabolic activation) exposures. The doses were: short term exposure (0.004, 0.006, 0.008, 0.02, and 0.04 uL/ml) and long term exposure (0.004, 0.006, 0.008, 0.02, and 0.04 uL/ml).
Exxal 13 did not induce a statistically significant increase in the number of cells with micronuclei at any of the non-cytotoxic doses chosen with or without metabolic activation; significant cytotoxicity was observed at 0.02 ul/mL and above in the absence of S9, and at concentrations at and above 0.006ul/mL in the presence of S9. Under the conditions in this study, Exxal 13 was cytotoxic but negative for micronuclei formation in all three tested conditions (short term exposure with and without metabolic activation; long exposure without metabolic activation) for CHO cells.
The mammalian cell micronucleus test to assess the genotoxicity of Exxal 13 was negative.
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