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EC number: 245-844-2 | CAS number: 23726-93-4
- 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 vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- From March 28 to November 20, 2003
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- GLP study conducted according to OECD Guideline No. 474 (1997 version). The study was fully reliable, however the reliability score was lowered to 2 which is the maximum score for read-across. The supporting substance is considered adequate for read-across purpose (see Iuclid section 13 for additional justification).
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 003
- Report date:
- 2003
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- Principles of method if other than guideline:
- Not applicable
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- GLP principles of the German "Chemikaliengesetz" (inspected on May 15 and June 26, 2001/signed on September 24, 2001)
- Type of assay:
- micronucleus assay
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
- IUPAC Name:
- 4-(2,6,6-trimethylcyclohex-1-en-1-yl)but-3-en-2-one
- Test material form:
- other: liquid
- Details on test material:
- - Physical state: Clear liquid
- Storage condition of test material: Stored in refrigerator, protected from light.
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Deutschland GmbH
- Age at study initiation: 5-8 weeks
- Weight at study initiation: 29 g (mean weight)
- Assigned to test groups randomly: yes, using an appropriate computer program.
- Housing: Animals were housed individually in Makrolon cages, type Ml.
- Diet: Standardized pelleted feed (Maus/Ratte Haltung "GLP", Provimi Kliba SA, Kaiseraugst, Switzerland), ad libitum
- Water: Drinking water, ad libitum
- Acclimation period: At least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature: 20-24 °C
- Humidity: 30-70 %
- Photoperiod: 12 h dark/ 12 light
IN-LIFE DATES: From: March 28, 2003 To: November 20, 2003
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- - Vehicle(s)/solvent(s) used: olive oil
- Justification for choice of solvent/vehicle: Due to the insolubility of the test substance in water, olive oil was selected as the vehicle, which had been demonstrated to be suitable in the in vivo micronucleus test and for which historical data are available.
- Concentration of test material in vehicle: 25, 50 and 75 mg/mL (main study). - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: Test material was dissolved in olive oil. All test substance formulations were prepared immediately before administration. The stability of the test substance at 4°C in the vehicle over a period of 4 days was verified analytically.
ANALYSIS OF FORMULATION: For the determination of the test substance concentrations in the vehicle, 3 samples of each dose were taken from the test substance preparations, kept at room temperature until the treatment of the last animal (approximately 1 h) and then deep-frozen until they were determined analytically . The determination of the concentrations in the vehicle was carried out by HPLC.
DOSE VOLUME: 10 mL/kg bw - Duration of treatment / exposure:
- Single intraperitoneal administration
- Frequency of treatment:
- Single intraperitoneal administration
- Post exposure period:
- 250 and 500 mg/kg bw: 24 h
750 mg/kg bw: 24 and 48 h
Doses / concentrations
- Remarks:
- Doses / Concentrations:
250, 500 and 750 mg/kg bw
Basis:
other: actual administered by intraperitoneal injection
- No. of animals per sex per dose:
- Main study: 5 males/dose
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide and vincristine sulphate.
- Justification for choice of positive control(s): Cyclophosphamide and vincristine sulphate are well established reference clastogens and aneugens, respectively.
- Route of administration: Intraperitoneal
- Doses / concentrations: Cyclophosphamide: 20 mg/kg bw; vincristine sulphate: 0.15 mg/kg bw.
Examinations
- Tissues and cell types examined:
- - 2000 polychromatic erythrocytes (PCEs) were evaluated per animal and investigated for micronuclei (MN).
- The normochromatic erythrocytes (NCEs) with and without micronuclei occurring per 2000 polychromatic erythrocytes were also recorded.
- Ratio of PCEs/NCEs.
- Number of small MN (diameter of MN < cell diameter/4) and of large MN (diameter of MN ≥ cell diameter/4). - Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
- Dose selection was based on the range-finding test conducted in male and female animals at 500, 750, 1000 and 2000 mg/kg bw. Mortality was observed at 2000 mg/kg bw; evident signs of toxicity observed and some animals were sacrificed moribund at 750 and 1000 mg/kg bw; all animals survived but evident signs of toxicity were observed at 500 mg/kg bw. Therefore, a dose of 750 mg/kg bw was selected as the highest dose and 500 and 250 mg/kg bw were administered as further doses in the main study.
TREATMENT AND SAMPLING TIMES:
- The animals were sacrificed and the bone marrow of the femurs was prepared at 24 and 48 h after administration in the highest dose group of 750 mg/kg bw and in the vehicle controls.
- In the test groups of 500 and 250 mg/kg bw and in the positive control groups, only 24 h sacrifice interval was investigated.
DETAILS OF SLIDE PREPARATION:
- The bone marrow was prepared according to the method described by Schmid (1976, 1977) and Salamone et al (1980). Animals were sacrificed by cervical dislocation and femurs were prepared by dissection and removing all soft tissues. Femurs of the mice were removed and the bone marrow cells were extracted with fetal calf serum. After centrifugation, the supernatant was removed and a drop of the cell suspension was placed and spread on a slide.
- Slides were air-dried and stained in eosin and methylene blue (modified May-Grunwald solution or Wrights solution) for about 5 minutes, then followed by rinsing in purified water, stained in Giemsa solution for about 15 minutes and rinsed twice in purified water. Slides were clarified in xylene and then mounted in Corbit-Balsam.
METHOD OF ANALYSIS:
- Slides were examined under microscope to determine the frequency of micronuclei in 2000 polychromatic erythrocytes (PCEs) per animal. In addition, normochromatic erythrocytes (NCEs) with and without micronuclei occurring per 2000 polychromatic erythrocytes were also recorded. Ratio of PCEs to NCEs calculated. Number of small MN (diameter of MN < cell diameter/4) and of large MN (diameter of MN ≥ cell diameter/4) recorded. - Evaluation criteria:
- - A test substance is considered positive if the following criteria are met:
Significant and dose-related increase in the number of PCEs containing micronuclei observed; the number of PCEs containing micronuclei has to exceed both the concurrent negative control and the highest value of the historical control range.
- A test substance is considered negative if the number of cells containing micronuclei in the dose groups is not significantly above the negative control and is within the historical control data. - Statistics:
- - Statistical evaluation of the data was carried out using the program system MUKERN (BASF Aktiengesellschaft).
- The asymptotic U test according to MANN-WHITNEY (modified rank test according to WILCOXON) was carried out to clarify the question whether there were significant differences between the control group and dose groups with regard to the micronucleus rate in polychromatic erythrocytes.
- The relative frequencies of cells containing micronuclei of each animal were used as a criterion for the rank determination for the U test.
- Significances were identified as follows:
* p ≤ 0.05
** p ≤ 0.01
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- squatting posture, irregular respiration and poor general state
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range: 500, 750, 1000 and 2000 mg/kg bw
- Rationale for exposure: Determination of the acute intraperitoneal toxicity of test material.
- Clinical signs of toxicity in test animals: Mortality was observed at 2000 mg/kg bw; evident signs of toxicity observed and some animals were sacrificed moribund at 750 and 1000 mg/kg bw; all animals survived but evident signs of toxicity were observed at 500 mg/kg bw.
RESULTS OF DEFINITIVE STUDY
- Induction of micronuclei (for Micronucleus assay): Test material did not lead to any increase in the rate of micronuclei. The number of normochromatic or polychromatic erythrocytes containing small micronuclei (d < D/4) or large micronuclei (d ≥ D/4) did not deviate from the vehicle control value at any of the sacrifice intervals and was within the historical control range.
- Ratio of PCE/NCE (for Micronucleus assay): No dose-dependent inhibition of erythropoiesis induced by the treatment of mice with test material was detected; the ratio of polychromatic to normochromatic erythrocytes was always in the same range as that of the control values in all dose groups.
Any other information on results incl. tables
Table 7.6.2/1: Micronucleus data
|
Vehicle Control (0 mg/kg bw) |
250 mg/kg bw |
500 mg/kg bw |
750 mg/kg bw |
CCP 20 mg/kg bw |
VCR 0.15 mg/kg bw |
||
Interval |
24 h |
48 h |
24 h |
24 h |
24 h |
48 h |
24 h |
24 h |
Total No. of PCEs |
10000 |
10000 |
10000 |
10000 |
10000 |
10000 |
10000 |
10000 |
Total No. of NCEs |
4594 |
3439 |
3755 |
4646 |
2476 |
2804 |
3920 |
5374 |
MN in PCEs (%) |
1.4 |
0.7 |
1.6 |
1.8 |
1.2 |
1 |
11.1** |
47.2** |
MN in NCEs (%) |
0.7 |
1.5 |
0.5 |
1.1 |
0.8 |
0.4 |
2 |
0.9 |
PCEs: Polychromatic erythrocytes
NCEs: Normochromatic erythrocytes
MN: Micronuclei
CCP: Cyclophosphamide
VCR: Vincristine
* : Statistically significant (Wilcoxon test, one-sided) vs. Vehicle control group, p<= 0.05
**: Statistically significant (Wilcoxon test, one-sided) vs. Vehicle control group, p<= 0.01
- The administration of the test substance at 250, 500 and 750 mg/kg bw led to squatting posture, poor general state and irregular respiration.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
Under the test conditions, test material is not classified as clastogenic or aneugenic according to the criteria of the Annex VI of the of the Regulation (EC) No.1272/2008 (CLP). - Executive summary:
In an in vivo bone marrow micronucleus test, performed according to OECD guideline 474 (1997 version) and in compliance with GLP, Crl:NMRI mice (5 males/dose) were administered once intraperitoneally with test material, dissolved in olive oil, at the dose levels of 250, 500 and 750 mg/kg bw in a volume of 10 mL/kg bw. Vehicle control group was administered with olive oil and positive control groups were given cyclophosphamide (20 mg/kg bw) and vincristine (0.15 mg/kg bw) by the same route. Animals were sacrificed and the bone marrow of the femurs was prepared 24 and 48 h after administration in the 750 mg/kg bw dose group and in the vehicle controls. In the test groups of 250 and 500 mg/kg bw and in the positive control groups, only 24 h sacrifice interval was investigated. After staining of the preparations, 2000 polychromatic erythrocytes (PCEs) were evaluated per animal and investigated for micronuclei. The normocytes (NCEs) with and without micronuclei occurring per 2000 polychromatic erythrocytes were also recorded. Range-finding test was conducted to determine the dose levels for main study.
Test material did not lead to any increase in the number of PCEs containing either small or large micronuclei. The rate of micronuclei was always close to the range as that of the concurrent vehicle controls in all dose groups and at all sacrifice intervals and within the range of the historical control data. No inhibition of erythropoiesis determined from the ratio of PCE/NCE was detected. Both of the positive control chemicals, i.e. cyclophosphamide for clastogenicity and vincristine for spindle poison effects, led to the expected increase in the rate of polychromatic erythrocytes containing small or large micronuclei indicating the validity of the study.
Under the test conditions, test material is not classified as clastogenic or aneugenic according to the criteria of the Annex VI of the of the Regulation (EC) No.1272/2008 (CLP).
This study is considered as acceptable and satisfies the requirement for mammalian erythrocyte micronucleus test. The supporting substance is considered adequate for read-across purpose (see Iuclid section 13 for additional justification).
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