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EC number: 402-600-1 | CAS number: 765-12-8
- 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:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP; guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 998
- Report date:
- 1998
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- olive oil
- Duration of treatment / exposure:
- The animais of the vehicle control and the dose groups were treated twice at a 24-hour interval and samples of bone marrow were taken 24 hours after the last treatment. Animals of the positive control groups were treated only once and samples of bone marrow were taken after 24 hours.
- Frequency of treatment:
- two intraperitoneal administrations
Doses / concentrations
- Remarks:
- Doses / Concentrations:
250, 500, 1000 ml/kg
Basis:
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- cyclophosphamide, vincristine sulphate
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- yes
- Vehicle controls validity:
- valid
- Negative controls validity:
- valid
- Positive controls validity:
- valid
Any other information on results incl. tables
As a negative control, olive oil (the selected vehicle) was administered to male mice by the same route, and gave frequencies of micronucleated polychromatic erythrocytes within the historical control range.
Both of the positive control chemicals, i.e. cyclophosphamide for clastogenic effects and vincristine for induction of spindle poison effects, led to the expected increase in the rate of polychromatic erythrocytes containing small or large micronuclei.
Animals which were administered the vehicle or the positive control substances, cyclophosphamide or vincristine, did not show any clinical signs of toxicity.
The administration of the test substance Triethylenglykoldivinylether led to evident signs of toxicity. The intraperitoneal administration of Triethylenglykoldivinylether did not lead to any increase in the number of polychromatic erythrocytes containing either small or large micronuclei. The rate of micronuclei was always in the same range as that of the negative control in all dose groups and at all sacrifice intervals. A slight inhibition of erythropoiesis, determined from the ratio of polychromatic to normochromatic erythrocytes, was detected at the highest dose of 1,000 mg/kg body weight.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
Under the experimental conditions of the study, the test substance does not have any chromosome-damaging (clastogenic) effect and there were no indications of any impairment of chromosome distribution in the course of mitosis. - Executive summary:
The substance Triethylenglykoldivinylether was tested for clastogenicity and for the ability to induce spindle poison effects in NMRI mice using the micronucleus test method. For this purpose, the test substance, dissolved in olive oil was administered twice intraperitoneally to male animals at dose levels of 250 mg/kg, 500 mg/kg and 1,000 mg/kg body weight in a volume of 10 ml/kg body weight in each case. As a negative control, olive oil (the selected vehicle) was administered to male mice by the same route, and gave frequencies of micronucleated polychromatic erythrocytes within the historical control range. Both of the positive control chemicals, i.e. cyclophosphamide for clastogenic effects and vincristine for induction of spindle poison effects, led to the expected increase in the rate of polychromatic erythrocytes containing small or large micronuclei. Animals which were administered the vehicle or the positive control substances, cyclophosphamide or vincristine, did not show any clinical signs of toxicity. The administration of the test substance Triethylenglykoldivinylether led to evident signs of toxicity. The intraperitoneal administration of Triethylenglykoldivinylether did not lead to any increase in the number of polychromatic erythrocytes containing either small or large micronuclei. The rate of micronuclei was always in the same range as that of the negative control in all dose groups and at all sacrifice intervals. Thus, the test substance Triethylenglykoldivinylether does not have any chromosome-damaging (clastogenic) effect, and there were no indications of any impairment of chromosome distribution in the course of mitosis.
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