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EC number: 805-722-7 | CAS number: 1064082-81-0
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
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- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
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- 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
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- Endpoint summary
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- 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 vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2020-11-24 to 2021-07-26
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 021
- Report date:
- 2021
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Version / remarks:
- adopted 29th July 2016
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- mammalian erythrocyte micronucleus test
Test material
- Reference substance name:
- (3E)-3-[(3-{[(E)-[2,2-dimethyl-3-(prop-1-en-2-yloxy)propylidene]amino]methyl}-3,5,5-trimethylcyclohexyl)imino]-2,2-dimethylpropyl acetate
- EC Number:
- 805-722-7
- Cas Number:
- 1064082-81-0
- Molecular formula:
- C24H42N2O4
- IUPAC Name:
- (3E)-3-[(3-{[(E)-[2,2-dimethyl-3-(prop-1-en-2-yloxy)propylidene]amino]methyl}-3,5,5-trimethylcyclohexyl)imino]-2,2-dimethylpropyl acetate
- Test material form:
- liquid
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Details on species / strain selection:
- The NMRI mouse is a recommended test system for the Mammalian Erythrocyte Micronucleus Test
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Envigo RMS B.V., Inc.
- Age at study initiation: 6 – 10 weeks
- Weight at study initiation: 30.4 - 36.7 g
- Assigned to test groups randomly: Yes
- Housing: Singly in Makrolon Type II / III cages with wire mesh top and granulated soft wood bedding
- Diet: Ad libitum (certified 2018C Teklad Global 18% protein rodent diet)
- Water: Ad libitum (tap water)
- Acclimation period: 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 + 2
- Humidity (%): 45-65
- Air changes (per hr): At least 8
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: From day 1 to day 2 (positive control animals) or from day 1 to day 3 (negative control and treated animals)
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle used: Corn oil
- Justification for choice of solvent/vehicle: The vehicle was chosen due to its relative non-toxicity for the animals and its ability to formulate a suitable dosing preparation since the test item is not stable in water.
- Amount of vehicle: 10 mL/kg bw - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
The preparations were made freshly before each dosing occasion. - Duration of treatment / exposure:
- Animals used for micronuclei evaluation: 48 hours (2 applications at an interval of 24 hours + 24 hours post treatment period)
Animals used for plasma sampling: 25 hours and 28 hours (2 applications at an interval of 24 hours + 1 hour or 4 hours post treatment period) - Frequency of treatment:
- Animals were treated twice (test item treatment + negative control) at an interval of 24 hours or once (positive control)
- Post exposure period:
- 24 hours
Doses / concentrationsopen allclose all
- Dose / conc.:
- 2 000 mg/kg bw/day (nominal)
- Dose / conc.:
- 1 000 mg/kg bw/day (nominal)
- Dose / conc.:
- 500 mg/kg bw/day (nominal)
- Dose / conc.:
- 0 mg/kg bw/day (nominal)
- Remarks:
- vehicle
- No. of animals per sex per dose:
- 6 animals per sex per dose for micronucleus evaluation and 6 high dose animals (3 animals 1 hour after last application and 3 animals 4 hours after last substance application) and 3 vehicle animals for plasma sampling
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide
- Route of administration: Oral (gavage)
- Doses / concentrations: 40 mg/kg bw
Examinations
- Tissues and cell types examined:
- Bone marrow erythrocytes
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
The maximum tolerated dose was selected on the basis of a pre-experiment with two animals per sex at a dose level of 2000 mg/kg bw under identical conditions as in the mutagenicity study concerning animal strain, vehicle, route, frequency, and volume of administration. As no deaths or severe suffering occured, 2000 mg/kg bw was selected as the highest concentration recommended in the guideline.
DETAILS OF SLIDE PREPARATION:
The animals were sacrificed using CO2 followed by cervical dislocation. The femora were removed, the epiphyses were cut off and the marrow was flushed out with foetal calf serum using a syringe. The cell suspension was centrifuged at 1500 rpm (390 x g) for 10 minutes and the supernatant was discarded. A small drop of the re-suspended cell pellet was spread on a slide. The smear was air-dried and then stained with May-Grünwald/Giemsa. Cover slips were mounted with EUKITT. At least one slide was made from each bone marrow sample.
METHOD OF ANALYSIS:
Evaluation of the slides was performed using NIKON microscopes with 100x oil immersion objectives. 4000 polychromatic erythrocytes (PCE) per animal were analysed for micronuclei. To describe a cytotoxic effect, the ratio between polychromatic and normochromatic erythrocytes was determined in the same sample and expressed in polychromatic erythrocytes per total erythrocytes. The analysis was performed with coded slides. All animals per test group were evaluated as described. - Evaluation criteria:
- Providing that all acceptability criteria are fulfilled, a test substance is classified as positive in the assay if
a) at least one of the treatment groups exhibits a statistically significant increase in the frequency of micronucleated immature erythrocytes compared with the concurrent negative control;
b) this increase is dose-related at least at one sampling time when evaluated with an appropriate trend test and
c) any of these results are outside the distribution of the historical negative control data (e.g., Poisson-based 95 % control limits).
Providing that all acceptability criteria are fulfilled, a test substance is considered clearly negative in the assay if:
a) none of the treatment groups exhibits a statistically significant increase in the frequency of micronucleated immature erythrocytes compared with the concurrent negative control;
b) there is no dose-related increase at any sampling time when evaluated by an appropriate trend test;
c) all results are inside the distribution of the historical negative control data (e.g., Poisson-based 95 % control limits), and
d) bone marrow exposure to the test substance(s) occurred.
There is no requirement for verification of a clearly positive or negative response. In case the response is neither clearly negative nor clearly positive as described above or in order to assist in establishing the biological relevance of a result, the data should be evaluated by expert judgment and/or further investigations. - Statistics:
- Statistical methods (as appropriate, Mann-Whitney Test, linear regression analysis) were used as an aid in evaluating the results.
Results and discussion
Test results
- Key result
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range: 500 - 2000 mg/kg bw per application
- Solubility: Soluble in corn oil at all tested concentrations
- Clinical signs of toxicity in test animals: One animal showed partially closed eyes 2-4 hours after the first treatment. Two animals showed piloerection 2-4 hours after the first treatment. The animals did not express any clinical symptoms after the second treatment.
- Evidence of cytotoxicity in tissue analysed: The mean number of polychromatic erythrocytes was not substantially decreased after treatment with the test item as compared to the mean value of PCEs of the vehicle control indicating that the test item did not have any cytotoxic properties in the bone marrow.
- Rationale for exposure: The maximum recommended dose outlined in OECD guideline 474 was used in the pre-experiment as no severe toxicity was expected based on information from the acute oral toxicity and the repeated dose toxicity studies.
RESULTS OF DEFINITIVE STUDY
- Induction of micronuclei: See "Any other information on results incl. tables"
- Ratio of PCE/NCE: See "Any other information on results incl. tables"
- Appropriateness of dose levels and route: The dose levels were chosen according to the maximum recommended dose outlined in OECD guideline 474. This dose induced no severe suffering or deaths in the pre-experiment and was thus considered well tolerated in the main experiment. The substance was considered to have the highest bioavailability via the oral route as the substance rapidly hydrolyses in contact with aqueous solutions (e.g. stomach fluid) and its hydrolysis products are thus considered to become bioavailable via the oral route.
- Statistical evaluation: See "Any other information on results incl. tables"
Any other information on results incl. tables
Table 1: Summary of micronucleus test results
Test | Dose | Sampling | Mean MN/4000 PCE | SD MN/4000 PCE | Range | Ratio | % ratio | |
min | max | |||||||
Vehicle | 0 | 24 | 7.0 | 3.1 | 2 | 11 | 0.732 | 100.00 |
Dose 1 | 500 | 24 | 4.5 | 2.3 | 1 | 8 | 0.750 | 102.46 |
Dose 2 | 1000 | 24 | 5.7 | 1.8 | 3 | 8 | 0.714 | 97.54 |
Dose 3 | 2000 | 24 | 5.7 | 2.4 | 3 | 10 | 0.716 | 97.81 |
Positive | 40 | 24 | 115.7 | 32.9 | 61 | 144 | 0.729 | 99.59 |
Table 2: Biometry. Statistical significance at the five per cent level (p < 0.05) was evaluated by means of the non-parametric Mann-Whitney test using the validated statistical program RScript Wilcoxon_2.Rnw. The Holm-Bonferroni Adjustment method was used to correct for the Familiywise error rate of multiple comparisons.
Negative control versus test group | Significance | p | p adjusted |
500 mg test item/kg b.w.; 24 h | - | 0.139 | 0.417 |
1000 mg test item/kg b.w.; 24 h | - | 0.325 | 0.650 |
2000 mg test item/kg b.w.; 24 h | - | 0.418 | 0.650 |
Positive Control - 40 mg CPA/kg b.w.; 24 h | + | 0.005 | 0.020 |
- = not significant
+ = significant
Furthermore, a linear regression analysis was performed (least squares, calculated using the validated statistical program RScript LM_v02.Rnw) in order to assess a possible dose dependent increase of mean micronuclei values. The mean number of micronuclei obtained for the groups treated with the test item was compared to the vehicle control group.
A trend was judged as significant whenever the p-value (probability value) is below 0.05. A p-value of 0.7372 was obtained, demonstrating that there was no dose dependent increase of mean micronuclei values.
Table 3: Content of the test item in dose formulation samples (corn oil)
Sample ID
| Nominal test concentration [mg/mL] | Timing | Test item analysed | % of nominal test concentration [%] |
1 a | Control | After the | n.d. | n.a. |
2 a | 50 | 45.2 | 90 | |
3 a | 100 | 94.8 | 95 | |
4 a | 200 | 185 | 93 | |
5 a | Control | After the second application | n.d. | n.a. |
6 a | 50 | 45.8 | 92 | |
7 a | 100 | 94.2 | 94 | |
8 a | 200 | 188 | 94 |
n.d.: not detectable (< 7.5 mg/mL); n.a.: not applicable
Table 4: Contents of the hydrolysis products 2,2-dimethyl-3-oxopropyl acetate and 3-aminomethyl-3,5,5-trimethylcyclohexylamine in blood plasma
Sample ID *
| Timing | Treatment | 2,2-dimethyl-3-oxopropyl acetate analysed | 3-aminomethyl-3,5,5-trimethylcyclohexylamine analysed |
P-1 a/b | 1 h after second treatment | Control (Vehicle) | n.d. | n.d. |
P-2 a/b | n.d. | n.d. | ||
P-3 a/b | n.d. | n.d. | ||
P-4 a/b | 2000 mg/kg | n.d. | < LOQ | |
P-5 a/b | n.d. | < LOQ | ||
P-6 a/b | n.d. | < LOQ | ||
P-7 a/b | 4 h after second treatment | 2000 mg/kg | n.d. | 14.5 |
P-8 a/b | n.d. | 9.02 | ||
P-9 a/b | n.d. | < LOQ |
* two aliquots of each sample were provided by the test facility: aliquot a was used for analysis of 2,2-dimethyl-3-oxopropyl acetate analysed, aliquot b was used for analysis of 3-aminomethyl-3,5,5-trimethylcyclohexylamine; n.d.: not detectable (< 2.4 mg/L); < LOQ: below limit of quantification (i.e. < 8 mg/L)
Applicant's summary and conclusion
- Conclusions:
- In conclusion, in can be stated that under the experimental conditions reported, the test item did not induce micronuclei as determined by the micronucleus test with bone marrow cells of the mouse. Therefore, the test item is considered to be non-genotoxic in this in vivo micronucleus assay.
- Executive summary:
A study according to OECD guideline 474 and GLP was peformed to investigate the potential of the test item to induce micronuclei in polychromatic erythrocytes (PCE) in the bone marrow of the mouse. The test item was dissolved in corn oil, which was also used as vehicle control. The dose volume administered orally (twice) was 10 mL/kg b.w. The administered volume of the positive control was 10 mL/kg. 24 h after the second administration of the test item, the bone marrow cells were collected for micronuclei analysis. Six males per test group were evaluated for the occurrence of micronuclei. Per animal, 4000 polychromatic erythrocytes were scored for micronuclei. To investigate a cytotoxic effect due to the treatment with the test item, the ratio between polychromatic and normochromatic erythrocytes was determined in the same sample and reported as the number of PCEs per total erythrocytes. The following dose levels of the test item were investigated: 500, 1000, and 2000 mg/kg bw.
The highest dose (maximum guideline-recommended dose) was estimated by a pre-experiment to be suitable. The animals treated with the test item and the vehicle control as well as with the test item did not exhibit any clinical symptoms. Accuracy of dose formulations was confirmed within phase number 20I13137-01-RATX. Recoveries were between 90 and 95% of nominal concentrations. Furthermore, within the same phase, bioavailability was confirmed by analytical detection of the test item in plasma (namely, the analytes 2,2-dimethyl-3-oxopropyl acetate (CAS 16184-79-5) and 3-aminomethyl-3,5,5-trimethylcyclohexylamine (CAS 2855-13-2)). 2,2-dimethyl-3-oxopropyl acetate could not be detected in plasma at any time point, whereas 3-aminomethyl-3,5,5-trimethylcyclohexylamine was present in plasma in test item treated animals and could be quantified in two of three animals at the 4 h after the second application time point (9.02 and 14.5 mg/L, respectively). In the third animal with blood withdrawal 4 h after the second application, 3-aminomethyl-3,5,5-trimethylcyclohexylamine could also be detected, but at a level which was below the Limit of Quantification (LOQ, <8 mg/L) but above the Limit of Detection (LOD, >2.4 mg/L). In conclusion, exposure of the blood and consequently also the bone marrow could be demonstrated. At 1 h after the second application, 3-aminomethyl-3,5,5-trimethylcyclohexylamine concentration in plasma was below LOQ in the three animals sacrificed at that time point.
After treatment with the test item, the number of PCEs was not substantially decreased as compared to the mean value of PCEs of the vehicle control thus indicating that the test item not exert any cytotoxic effects in the bone marrow (see table below).
Table 1: Summary of micronucleus test results
Test
GroupDose
mg/kg
b.w.Sampling
time
(after 2nd application)Mean MN/4000 PCE
SD MN/4000 PCE
Range
Ratio
PCE /total Ery% ratio
Vehiclemin
max
Vehicle
0
24
7.0
3.1
2
11
0.732
100.00
Dose 1
500
24
4.5
2.3
1
8
0.750
102.46
Dose 2
1000
24
5.7
1.8
3
8
0.714
97.54
Dose 3
2000
24
5.7
2.4
3
10
0.716
97.81
Positive
40
24
115.7
32.9
61
144
0.729
99.59
In comparison to the corresponding vehicle controls, there was no biologically relevant or statistically significant enhancement in the frequency of the detected micronulclei after administration of the test item with any dose level used. The concurrent vehicle control range (2-11 MN per 4000 PCE) was well within the range of the historical control data (0-18 MN per 4000 PCE). 40 mg/kg b.w. orally administered cyclosphosphamide was used as positive control which induced a substantial and statistically significant increase in cells with micronuclei (range: 61-144 MN per 4000 PCE), which was well within the range of the historical control data (range: 36-249 MN per 4000 PCE).
In conclusion, in can be stated that under the experimental conditions reported, the test item did not induce micronuclei as determined by the micronucleus test with bone marrow cells of the mouse. Therefore, the test item is considered to be non-clastogenic in this in vivo micronucleus assay.
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