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EC number: 907-706-6 | CAS number: -
- 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 vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Type of information:
- experimental study
- Remarks:
- Read across data
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Justification for type of information:
- The study contains experimental data of a read-across analogue. This data was used as a basis for the SIDS dossier. All data were checked and validated by BUA. A final evaluation of the human health part has been performed by the Federal Institute for Risk Assessment (BfR).
Qualified BUA personnel performed quality control on the full SIDS dossier submitted by the industry. This quality control process followed internal BUA guidelines/instructions for the OECD/ICCA peer-review process. This included: i) A full (or update) literature search to verify completeness of data provided by industry in the IUCLID/HEDSET, ii) Review of data and assessment of the quality of data, iii) Review of data evaluation. iv) Check the adequacy of the selection process for key studies for OECD endpoints and, where relevant, for non-OECD endpoints by checking original reports/publications. v) Review of key study description according to robust summaries requirements; completeness and correctness are checked against original reports/publications (if original reports are missing: reliability (4), i.e. reliability not assignable). vi) Review of validity of structure-activity relationships, vii) Review of full SIDS dossier (including SIAR, SIAP and proposal for the conclusion and recommendation for further work), viii) In case of data gaps, review of testing plan or rationale for not testing.
Data source
Reference
- Reference Type:
- review article or handbook
- Title:
- In vivo micronucleus assay of a read-across analogue.
- Author:
- UNEP Publications
- Year:
- 2 003
- Bibliographic source:
- OECD SIDS Initial Assessment Report
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Version / remarks:
- July 21, 1997
- GLP compliance:
- no
- Type of assay:
- mammalian erythrocyte micronucleus test
Test material
- Reference substance name:
- (E)-4-(2,6,6-trimethyl-1-cyclohexen-1-yl)-3-buten-2-one
- EC Number:
- 201-224-3
- EC Name:
- (E)-4-(2,6,6-trimethyl-1-cyclohexen-1-yl)-3-buten-2-one
- Cas Number:
- 79-77-6
- Molecular formula:
- C13H20O
- IUPAC Name:
- (E)-4-(2,6,6-trimethyl-1-cyclohexen-1-yl)-3-buten-2-one
- Details on test material:
- - Name of the test chemical: β-Ionone
- Molecular formula: C13H20O
- Molecular weight: 192.3 g/mol
- SUbstance type: Organic
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Details on species / strain selection:
- No data
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- Healthy male Crl: NMRI mice (breeder: Charles River, Deutschland GmbH, GER) with a mean weight of about 29g (with an age range of about 5-8 weeks) were used in the test.
5 males/dose were received a single ip injection.
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- Olive oil was used as a vehicle of the test substance.
- Details on exposure:
- Frequency of dosing: single injection (ip)
Dosing volume: 10 ml/kg bw
Control groups:
negative: 1 x vehicle control (10 ml/kg bw olive oil)
positive: 1 x 20 mg/kg bw cyclophosphamide (CPP) for
clastogenic effects (10 ml/kg bw), 1 x 0.15 mg/kg bw
vincristine (VCR) for aneugenic effcts (10 ml/kg bw)
5 males/dose were received a single ip injection. - Duration of treatment / exposure:
- 24 hours for treatment groups.
48 hours for satelite groups. - Frequency of treatment:
- A single ip injection was applied in all control and treatment groups.
- Post exposure period:
- 24 hours for treatment groups
48 hours for satelite groups
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 mg/kg bw/day
- Remarks:
- Vehicle control
- Dose / conc.:
- 250 mg/kg bw/day
- Dose / conc.:
- 500 mg/kg bw/day
- Dose / conc.:
- 750 mg/kg bw/day
- Dose / conc.:
- 0 mg/kg bw/day
- Remarks:
- Satelite control
- Dose / conc.:
- 750 mg/kg bw/day
- Remarks:
- Satelite top dose
- No. of animals per sex per dose:
- Treatment groups: 5 males/dose
Satelite groups: 5 males/ groups - Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide (CPP) for clastogenic effects (10 ml/kg bw)
Vincristine (VCR) for aneugenic effcts (10 ml/kg bw)
Examinations
- Tissues and cell types examined:
- Bone marrow PCEs and NMEs.
- Details of tissue and slide preparation:
- Samples of bone marrow of the 2 femurs were collected. Preparation of the bone marrow was performed according to the method of Schmidt (1976 and 1977) and Salamone et al. (1980).
- Evaluation criteria:
- Microscopic evaluation: 2000 polychromatic erythrocytes (PCEs) from each animal of every test group were investigated for micronuclei (MN). The normochromatic erythrocytes (NCEs) were also scored. The ratio of polychromatic to normochromatic erythrocytes was determined.
- Statistics:
- U-test according to Mann-Whitney (modified rank test according to Wilcoxon) test was used to demonstrate differences between control and dose groups.
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Remarks:
- No statistically significant increase in the number of polychromatic erythrocytes containing either small or large micronuclei was noted at any doses tested.
- Toxicity:
- yes
- Remarks:
- Clinical signs of toxicity was observed at 500 and 750 mg/kg bw.
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
Any other information on results incl. tables
Table 1. Effect on PCE/NCE ratio - Mean numbers of PCEs and NCEs
Interval |
|
24 hrs |
48 hrs |
|
PCEs |
NCEs |
NCEs |
Vehicle |
10000 |
4594 |
3439 |
250 mg/kg bw |
10000 |
3755 |
|
500 mg/kg bw |
10000 |
4646 |
|
750 mg/kg bw |
10000 |
2476 |
2804 |
CPP (20 mg/kg bw) |
10000 |
3920 |
|
VCR (0.15 mg/kg bw) |
10000 |
5374 |
|
Table 2. Mean number of PCEs containing MN per 1,000 PCE at 24 hrs (differentiation between small and large micronuclei)
|
Small |
Large |
Total |
Vehicle |
1.3 |
0.1 |
1.4 |
250 mg/kg bw |
1.6 |
0.0 |
1.6 |
500 mg/kg bw |
1.7 |
0.1 |
1.8 |
750 mg/kg bw |
1.2 |
0.0 |
1.2 |
CPP (20 mg/kg bw) |
10.9 |
0.2 |
11.1 (p≤0.01) |
VCR (0.15 mg/kg bw) |
35.7 |
11.5 |
47.2 (p≤0.01) |
Table 3. Mean number of PCEs containing MN per 1,000 PCE at 48 hrs (differentiation between small and large micronuclei)
|
Small |
Large |
Total |
Vehicle |
0.7 |
0.0 |
0.7 |
750 mg/kg bw |
1.0 |
0.0 |
1.0 |
Applicant's summary and conclusion
- Conclusions:
- The substance (E)-4-(2,6,6-trimethyl-1-cyclohexen-1-yl)-3-buten-2-one (CAS 79-77-6), was tested negative (non-clastogenic) in a bone marrow micronucleus assay using male NMRI mice. The study was performed according to OECD TG 474 (1997).
- Executive summary:
The read across substance, i.e., (E)-4-(2,6,6-trimethyl-1-cyclohexen-1-yl)-3-buten-2-one (CAS 79-77-6), was tested for chromosomal damage (clastogenicity) and for the ability to induce spindle poison effects (aneugenic activity) in NMRI mice using the micronucleus test method. The test was performed according to OECD TG 474 (1997). Test doses were selected based on an initial experiment. In this pretest for determination of the acute i.p. toxicity, deaths were observed at 2000 mg/kg bw. Mice treated with 750 and 1000 mg/kg bw showed evident signs of toxicity, and some animals were sacrificed moribund. At 500 mg/kg bw, all animals survived, but l signs of clinical toxicity were noted. There were no distinct differences in the symptoms between males and female mice. Thus, only males were used for the cytogenetic investigations. Doses of 750, 500 and 250 mg/kg bw were selected for the main test. The test substance was dissolved in olive oil and was administered once intraperitoneally to male NMRI mice (5 mice/dose) at 0 (VC), 250, 500 and 750 mg/kg bw. Additional 5 mice were injected with the vehicle or 750 mg/kg of test substance served as a satellite group. Samples of the bone marrow of the 2 femurs were taken 24 (treatment groups) and 48 hrs (satelite groups) after the last treatment. 2000 polychromatic erythrocytes (PCEs) from each animal of every test group were investigated for micronuclei (MN). The normochromatic erythrocytes (NCEs) were also scored. The ratio of polychromatic to normochromatic erythrocytes was determined. After administration of the vehicle, test substance and positive controls, the animals were examined for clinical signs of toxicity. U-test according to Mann-Whitney (modified rank test according to Wilcoxon) was performed to confirm differences between control and dose groups. Results: No mortality was observed at any dose level. Clinical signs of toxicity were observed at 500 and 750 mg/kg bw, which included poor general state, irregular respiration, squatting posture. These clinical signs were reversible after 2 days. At 250 mg/kg bw only minor signs of clinical toxicity were observed after 2 and 4 hours of administration of the test substance (squatting posture). No inhibition of erythropoiesis, determined from the PCE/NCE ratio, was detected. The vehicle and the positive control substances, Cyclophosphamide (CPP, 20 mg/kg bw) and vincristine (VCR, 0.15 mg/kg bw), caused no evident signs of toxicity. The following mean number of PCEs and NCEs were observed: vehicle (PCEs: 10000, NCEs: 4594 (24 hrs), 3439 (48 hrs)), at 250 mg/kg bw (PCEs: 10000, NCEs:3755), at 500 mg/kg bw (PCEs: 10000, NCEs: 4646), at 750 mg/kg bw (PCEs: 10000, NCEs: 2476 (24 hrs), 2804 (48 hrs), CPP (PCEs: 10000, NCEs: 3920), VCR (PCEs: 10000, NCEs: 5374). The administration of the test substance did not lead to any statistically significant increase in the number of polychromatic erythrocytes containing either small or large micronuclei. The rate of micronuclei was nearly the range of the concurrent negative control in all dose groups and within the range of the historical control data (mean 1.6, min. 0.3, max. 3.3, SD 0.6; n=393). The positive controls led to the expected increases in micronuclei (either small or large). The mean number of PCEs containing MN per 1,000 PCE at 24 hrs (differentiation between small and large micronuclei) were the follows: vehicle (small: 1.3, large:0.1, total: 1.4), at 250 mg/kg bw (small: 1.6, large: 0.0, total: 1.6), at 500 mg/kg bw (small: 1.7, large: 0.1, total: 1.8), at 750 mg/kg bw (small: 1.2, large: 0.0, total: 1.2), CPP (small: 10.9, large: 0.2, total: 11.1; p ≤0.01), VCR (small: 35.7, large: 11.5 total: 47.2; p≤0.01). The mean number of PCEs containing MN per 1,000 PCE at 48 hrs (small and large and total number of micronuclei) were the follows: vehicle (small: 0.7, large: 0.0, total: 0.7) at 750 mg/kg bw (small: 1.0, large: 0.0, total: 1.0). Conclusion: The source substance, i.e., (CAS 79-77-6), did not have a chromosome-damaging (clastogenic) effect, and there were no indications of any impairment of chromosome distribution in the course of mitosis (aneugenic activity) in bone marrow cells in vivo.
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