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EC number: 256-905-8 | CAS number: 51000-52-3
- 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
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: The study was conducted according to an O.E.C.D. Testing Guideline with GLP compliance.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 991
- Report date:
- 1991
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- not specified
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Vinyl neononanoate
- EC Number:
- 259-160-7
- EC Name:
- Vinyl neononanoate
- Cas Number:
- 54423-67-5
- Molecular formula:
- C11H20O2
- IUPAC Name:
- Vinyl Neononanoate
- Reference substance name:
- Neononanoic acid vinyl ester
- IUPAC Name:
- Neononanoic acid vinyl ester
- Details on test material:
- As per IUCLID5 Sections 1.1 -1.4.
Constituent 1
Constituent 2
Test animals
- Species:
- mouse
- Strain:
- Swiss Webster
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Male and female Swiss-Webster mice weighing approximately 20 to 30 grams were obtained from Charles River Laboratories. The animals were housed in filter-top cages in a ventilated cage rack with 5 male or female mice in each cage. Food (Purina Rodent Laboratory Chow No. 5001C) and water were provided ad libitum, and the mice were acclimated for up to seven days before initial dosing.
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- The test substance was delivered neat.
- Details on exposure:
- The test substance and controls were administered i.p. to male and female mice at each dose level on each of three consecutive days. Doses administered were: 0.01, 0.02, 0.03, and 0.04 ml per mouse (0.3, 0.6, 0.9, and 1.3 mi/kg for male mice and 0.3, 0.6, 0.9, and 1.2 mi/kg for female mice).
- Duration of treatment / exposure:
- 3 days
- Frequency of treatment:
- 1/day
- Post exposure period:
- 24 hours
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0.3, 0.6 0.9, 1.3 ml/kg
Basis:
nominal conc.
- No. of animals per sex per dose:
- 5
- Control animals:
- yes
- Positive control(s):
- 0.4 mg/kg triethylenemelamine
Examinations
- Tissues and cell types examined:
- erythrocytes
- Details of tissue and slide preparation:
- Slides of peripheral blood smears were made for all surviving animals approximately 24 hours after the last dosing by the following procedure. Approximately 2-3 il of serum was placed on a slide pre-cleaned with 95% ethanol. Each mouse was sacrificed by cervical dislocation, and approximately 2-3 .tl of blood per slide was obtained from the mid- ventral tail vein of a mouse and placed on top of the serum. The blood was mixed with the serum and spread on the slide to produce a thin, even film, then the slide was allowed to air-dry on a flat surface. After the slide was dry, the erythrocytes were fixed by placing the slide in absolute methanol for approximately five minutes, then, allowed to air-dry vertically. Three slides were prepared per mouse. The slides were stained for 20 minutes in 5% Giemsa stain in phosphate buffer containing 3% methanol and 3% 0.1M citric acid, rinsed by dipping them in deionized water until clear, and allowed to air dry vertically. Coverslips were attached with Permount before the erythrocytes are analyzed.
- Evaluation criteria:
- • Positive. A test material is considered to have elicited a positive response in the mouse erythrocyte micronucleus test if there is a significant dose-related increase in micronuclei and if one or more of the doses induces a statistically significant (p <0.05) increase in micronuclei induction.
• Negative. A test material is considered to have elicited a negative response if the criteria for a positive response are not met. - Statistics:
- Binomial comparison of Kastenbaum and Bowman (1970), and the Cochran-Armitage trend test (Armitage, 1955; Cochran, 1984) as described in Margolin and Risko (1986).
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- PCE ratios were reduced 50-60% relative to untreated controls.
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- The %o micronuclei per PCEs or per NCEs were not significantly elevated for any dosage group of male or female mice. Thus, it is concluded that vinyl neononanoate was not clastogenic in this assay.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
Vinyl neononanoate did not induce chromosome damage in vivo in mice at dose levels that were cytotoxic to the bone marrow cells. - Executive summary:
Vinyl neononanoate was assessed for its ability to induce chromosome damage in vivo in mice by an O.E.C.D. 474 Testing Guideline study conducted with GLP compliance. Following i.p.administration for three consecutive days vinyl neononanoate did not induce chromosome damage in vivo in mice at dose levels that were cytotoxic to the bone marrow cells. Therefore, vinyl neononanoate is not genotoxic in this in vivo assay.
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