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EC number: 218-746-2 | CAS number: 2224-15-9
- 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
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Version / remarks:
- Adopted: 29 July 2016
- GLP compliance:
- yes
- Type of assay:
- mammalian erythrocyte micronucleus test
Test material
- Reference substance name:
- 2,2'-[ethylenebis(oxymethylene)]bisoxirane
- EC Number:
- 218-746-2
- EC Name:
- 2,2'-[ethylenebis(oxymethylene)]bisoxirane
- Cas Number:
- 2224-15-9
- Molecular formula:
- C8H14O4
- IUPAC Name:
- 2,2'-[ethylenebis(oxymethylene)]bisoxirane
- Test material form:
- liquid
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- ICR
- Details on species / strain selection:
- ICR mice are commonly used in toxicity studies with a large historical control data base.
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: ORIENTBIO INC., Republic of Korea
- Age at the start of administration:
Dose range finding study: 8 weeks old
Additional dose range finding study: 8 weeks old
Main study: 8 weeks old
- Weight at the start of administration:
Dose range finding study: males: 33.5–38.2 g ; females: 27.7–31.0 g
Additional dose range finding study: females: 26.9–30.4 g
Main study: males: 33.8–38.2 g ; females: 26.9–30.4 g
- Assigned to test groups randomly: yes
- Housing: polycarbonate cage
- Diet: ad libitum
- Water: ad libitum
ENVIRONMENTAL CONDITIONS
- Temperature (°C): permissible range: 19–25
- Humidity (%): permissible range: 40–70
- Air changes (per hr): 10-15
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: water
- Justification for choice of solvent/vehicle: preliminary solubility test was conducted
- Concentration of test material in vehicle:
dose-range finding study: 25.0, 50.0, 100 and 200 mg/mL
additional dose-range finding and main study: 3.13, 6.25, 12.5, 25.0 mg/mL
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 mg/kg bw/day
- Remarks:
- males
- Dose / conc.:
- 62.5 mg/kg bw/day
- Remarks:
- males
- Dose / conc.:
- 125 mg/kg bw/day
- Remarks:
- males
- Dose / conc.:
- 250 mg/kg bw/day
- Remarks:
- males
- Dose / conc.:
- 0 mg/kg bw/day
- Remarks:
- females
- Dose / conc.:
- 31.3 mg/kg bw/day
- Remarks:
- females
- Dose / conc.:
- 62.5 mg/kg bw/day
- Remarks:
- females
- Dose / conc.:
- 125 mg/kg bw/day
- Remarks:
- females
- Control animals:
- yes
- Positive control(s):
- mitomycin C
- Route of administration: intraperitoneal
- Doses / concentrations: 2 mg/kg bw
Examinations
- Evaluation criteria:
- The results of the study were considered to be positive when the following conditions were met:
- at least one of the test substance groups exhibits a statistically significant increase in the incidence of MNPCE compared to the negative control group
- the incidence of MNPCE is increased in a dose-dependent manner
- the incidence of MNPCE is increased outside the range of the distribution of the historical control data - Statistics:
- Statistical analysis on the incidence of MNPCE, ratio of PCE to total erythrocytes and body weight was performed using SAS Program (version 9.3, SAS Institute Inc., U.S.A.).
For the incidence of MNPCE data, Mann-Whitney test was used for the comparison of the negative control group to each test substance group or the positive control group (significance levels: 0.05 and 0.01, two-tailed). Then, when significant in the test substance group, Cochran-Armitage trend test was employed for the comparison of the negative control group to each test substance group (significance levels: 0.05 and 0.01, two-tailed).
For the ratio of PCE to total erythrocytes and body weight data, Bartlett’s test was used for the comparison of homogeneity of variance of the negative control group to each test substance group (significance level: 0.05). One-way analysis of variance (ANOVA) was employed for homogeneous data (significance level: 0.05). In the comparison of the negative control group to the positive control group, Folded-F test was used for homogeneity of variance (significance level: 0.05).
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- positive
- Toxicity:
- no effects
- Negative controls validity:
- valid
- Positive controls validity:
- valid
Any other information on results incl. tables
As a result of the dose range finding study, deaths were observed at 500 mg/kg or more in males. In addition, deaths were observed at all dose levels in females. Therefore, an additional dose range finding study was conducted in females to determine the high dose of the main study.
An additional dose range finding study was conducted using the same method and conditions as the dose range finding study. The high dose of the test substance was set at 250 mg/kg and it was sequentially diluted by applying a geometric ratio of 2 to produce 3 lower dose levels (125, 62.5 and 31.3 mg/kg).
Applicant's summary and conclusion
- Executive summary:
This study was designed to evaluate the potential of the test substance, 2,2’-[ethylenebis(oxymethylene)]bisoxirane, to induce micronuclei in bone marrow cells of mice when the test substance was administered twice to 8-week-old ICR mice via gastric intubation at 24 h intervals.
The dose range finding study was conducted at dose levels of 250, 500, 1,000 and 2,000 mg/kg to determine the high dose level for the main study and differences in clinical signs and mortality between the sexes. As a result of the dose range finding study, deaths were observed at 500 mg/kg or more in males. In addition, deaths were observed at all dose levels in females. Therefore, an additional dose range finding study was conducted to determine the high dose of the main study in females. The high dose of the test substance was set at 250 mg/kg and it was sequentially diluted by applying a geometric ratio of 2 to produce 3 lower dose levels (125, 62.5 and 31.3 mg/kg).
As a result of the additional dose range finding study, neither death nor severe clinical sign was observed. Therefore, the high dose level of the main study was set at 250 mg/kg and it was sequentially diluted by applying a geometric ratio of 2 to produce 2 lower dose levels (125 and 62.5 mg/kg) in males. In females, the high dose level of the main study was set at 125 mg/kg and it was sequentially diluted by applying a geometric ratio of 2 to produce 2 lower dose levels (62.5 and 31.3 mg/kg). In addition, positive and negative control groups were set. The main study was conducted with males and females, since differences in clinical signs and mortality were observed between the sexes.
In the main study, there was no statistically significant difference in the body weight and the ratio of polychromatic erythrocytes (PCE) among total erythrocytes in any test substance group of males and females compared to the negative control group. However, there were statistically significant differences and dose-related effects on the incidence of micronucleated polychromatic erythrocytes (MNPCE) in PCE in all test substance groups of males and in the 125 mg/kg group of females compared to the negative control group.
The incidence of MNPCE in PCE in the positive control group was statistically significantly increased in males and females compared to the negative control group.
Based on these results, the test substance, 2,2’-[ethylenebis(oxymethylene)]bisoxirane, had potential to induce micronuclei formation in bone marrow cells of mice under the conditions of this study.
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