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EC number: 206-007-7 | CAS number: 286-20-4
- 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 / bone marrow chromosome aberration
- Remarks:
- Type of genotoxicity: gene mutation
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 08/23/1994 (start date)
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: A non-GLP study performed to sound scientific principles with a sufficient level of detail to assess the quality of the submitted data.
Data source
Reference
- Reference Type:
- other company data
- Title:
- Unnamed
- Year:
- 1 994
- Report date:
- 1994
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 475 (Mammalian Bone Marrow Chromosome Aberration Test)
- Deviations:
- yes
- Remarks:
- Deviations from guideline - separation of split dose treatment.
- Principles of method if other than guideline:
- Deviations from guideline - separation of split dose treatment.
Not mentioned - details on animals and environmental conditions. - GLP compliance:
- not specified
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 1,2-epoxycyclohexane
- EC Number:
- 206-007-7
- EC Name:
- 1,2-epoxycyclohexane
- Cas Number:
- 286-20-4
- Molecular formula:
- C6H10O
- IUPAC Name:
- 7-oxabicyclo[4.1.0]heptane
- Test material form:
- not specified
- Details on test material:
- - Name of test material (as cited in study report): cyclohexene oxide
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- No further information on test animals and environmental conditions.
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- Corn oil
- Details on exposure:
- no data
- Duration of treatment / exposure:
- Injections at 3 and 72 hours.
- Frequency of treatment:
- Injections at 3 and 72 hours.
Doses / concentrations
- Remarks:
- Doses / Concentrations:
19.5, 39.06, 78.13, 156.25, 312.5, 625 and 1250 mg/kg
Basis:
nominal conc.
- No. of animals per sex per dose:
- 5 males per dose.
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide
Dose: 10 mg/kg
No. test animals: 5
Examinations
- Tissues and cell types examined:
- Erythrocytes in the bone marrow of the femurs.
- Details of tissue and slide preparation:
- - Animals were euthanized by CO2 inhalation and the femurs were removed.
- The bone marrow was flushed from the femurs and spread onto slides.
- The slides were air-dried, fixed, and stained with a fluorescent DNA-specific stain that easily illuminated any micronuclei that may be present. - Evaluation criteria:
- - Typically, 2000 polychromatic erythrocytes (PCEs, reticulocytes; immature erythrocytes) were scored per animal for frequency of micronucleated cells in each of test animals.
- In addition, the percentage of PCEs among the total erythrocyte population in the bone marrow was scored for each dose group as an indicator of chemically-induced toxicity.
- In non-treated healthy rats, the %PCE in bone marrow is usually around 50-60%.
- If a chemical interferes with the production of erythrocytes in the bone marrow, then the %PCE in the bone marrow may decline from the typical normal level.
- Conversely, if erythrocyte production is stimulated by chemical exposure, then a higher percentage of immature erythrocytes may be observed. - Statistics:
- A formal statistical analysis of the data was performed that includes a trend test, to determine if there was an overall increase across all doses in the frequency of cells containing micronuclei, and a pairwise comparison of each dose group to the corresponding control, to see if any one dose group was statistically different from the control group in frequency of micronucleated cells.
- A positive trend test is one in which the P value is equal to or less than 0.025.
- For the slide-based micronucleus data, the micronucleus frequency in any dose group is considered significantly elevated over the control group if the P value is equal to or less than 0.025 divided by the number of chemical-treatment groups.
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- not examined
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- All test animals died after receiving 625 and 1250 mg/kg of the test material and one animal died after receiving a dose of 312.5 mg/kg.
Any other information on results incl. tables
Dose | Animal | Polychromatic Erythrocytes | |||||||||
(mg/kg) | Number | Trend P = 0.638 | |||||||||
No. Examined | Total MN Cells | Percent PCE | MN Cells | ||||||||
per 1000 | |||||||||||
Vehicle Control | CRO | 0 | 1219 | 2000 | 2 | 40 | 1 | ||||
0 | 1250 | 2000 | 0 | 45 | 0 | ||||||
0 | 1261 | 2000 | 3 | 32 | 1.5 | ||||||
0 | 1620 | 2000 | 1 | 48.5 | 0.5 | ||||||
0 | 1689 | 2000 | 2 | 40 | 1 | ||||||
Average ± SEM | 41.10 ± 2.79 | 0.80 ± 0.25 | |||||||||
Test Material | 19.5 | 1150 | 2000 | 3 | 36 | 1.5 | |||||
19.5 | 1161 | 2000 | 3 | 40 | 1.5 | ||||||
19.5 | 1220 | 2000 | 3 | 36 | 1.5 | ||||||
19.5 | 1289 | 2000 | 5 | 41 | 2.5 | ||||||
19.5 | 1419 | 2000 | 3 | 38.5 | 1.5 | ||||||
Average ± SEM | 38.30 ± 1.02 | 1.70 ± 0.20 | |||||||||
Pairwise P | 0.0358 | ||||||||||
Test Material | 39.06 | 1121 | 2000 | 2 | 42 | 1 | |||||
39.06 | 1185 | 2000 | 1 | 51.5 | 0.5 | ||||||
39.06 | 1210 | 2000 | 1 | 39 | 0.5 | ||||||
39.06 | 1235 | 2000 | 6 | 57.5 | 3 | ||||||
39.06 | 1284 | 2000 | 7 | 45.5 | 3.5 | ||||||
Average ± SEM | 47.10 ± 3.33 | 1.70 ± 0.64 | |||||||||
Pairwise P | 0.0358 | ||||||||||
Test Material | 78.13 | 1327 | 2000 | 1 | 42.5 | 0.5 | |||||
78.13 | 1340 | 2000 | 5 | 40 | 2.5 | ||||||
78.13 | 1382 | 2000 | 1 | 35 | 0.5 | ||||||
78.13 | 1385 | 2000 | 4 | 41 | 2 | ||||||
78.13 | 1390 | 2000 | 4 | 36 | 2 | ||||||
Average ± SEM | 38.90 ± 1.45 | 1.50 ± 0.42 | |||||||||
Pairwise P | 0.0721 | ||||||||||
Test Material | 156.25 | 1205 | 2000 | 2 | 35.5 | 1 | |||||
156.25 | 1207 | 2000 | 4 | 45 | 2 | ||||||
156.25 | 1226 | 2000 | 4 | 49 | 2 | ||||||
156.25 | 1277 | 2000 | 2 | 42.5 | 1 | ||||||
156.25 | 1279 | 2000 | 2 | 47.5 | 1 | ||||||
Average ± SEM | 43.90 ± 2.37 | 1.40 ± 0.24 | |||||||||
Pairwise P | 0.1003 | ||||||||||
Test Chemical | 312.5 | 1181 | 2000 | 3 | 37 | 1.5 | |||||
312.5 | 1306 | 2000 | 1 | 35.5 | 0.5 | ||||||
312.5 | 1323 | 2000 | 2 | 30 | 1 | ||||||
312.5 | 1426 | 2000 | 3 | 36 | 1.5 | ||||||
312.5 | 1448d | 0 | 0 | 0 | 0 | ||||||
Average ± SEM | 34.63 ± 1.57 | 1.13 ± 0.24 | |||||||||
Pairwise P | 0.2403 | ||||||||||
Test Material | 625 | 1320d | 0 | 0 | N/A | 0 | |||||
625 | 1362d | 0 | 0 | N/A | 0 | ||||||
625 | 1364d | 0 | 0 | N/A | 0 | ||||||
625 | 1371d | 0 | 0 | N/A | 0 | ||||||
625 | 1383d | 0 | 0 | N/A | 0 | ||||||
Average ± SEM | N/A ± N/A | 0.00 ± 0.00 | |||||||||
Pairwise P | * | ||||||||||
Test Chemical | 1250 | 1105d | 0 | 0 | N/A | 0 | |||||
1250 | 1307d | 0 | 0 | N/A | 0 | ||||||
1250 | 1326d | 0 | 0 | N/A | 0 | ||||||
1250 | 1377d | 0 | 0 | N/A | 0 | ||||||
1250 | 1379d | 0 | 0 | N/A | 0 | ||||||
Average ± SEM | N/A ± N/A | 0.00 ± 0.00 | |||||||||
Pairwise P | * | ||||||||||
Positive Control | CPA | 10 | 1285 | 2000 | 28 | 40 | 14 | ||||
10 | 1290 | 2000 | 25 | 26.5 | 12.5 | ||||||
10 | 1363 | 2000 | 30 | 31.5 | 15 | ||||||
10 | 1640 | 2000 | 26 | 32 | 13 | ||||||
10 | 1682 | 2000 | 28 | 37 | 14 | ||||||
Average ± SEM | 33.40 ± 2.34 | 13.70 ± 0.44 | |||||||||
Pairwise P | < 0.0001 | ||||||||||
Abbreviations: | |||||||||||
CRO = Corn Oil | |||||||||||
d = dead | |||||||||||
* = Insufficient animals scored to calculate p-value. | |||||||||||
CPA = Cyclophosphamide |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
The genetic toxicity of the test material was determined to be negative in an in vivo micronucleus study conducted in male Fischer 344 rats. - Executive summary:
The genetic toxicity of the test material was determined to be negative in an in vivo micronucleus study. The study was conducted to a protocol which is similar to the standard guideline OECD 475; there were only minor deviations. Five male Fischer 344 rats per dose were exposed to the test material via intraperitoneal injection. The test material was administered up to the level of toxicity. Under the conditions of the test, the genotoxicity of the test material was determined to be negative.
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