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EC number: 232-954-0 | CAS number: 9066-59-5
- 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 germ cell study: cytogenicity / chromosome aberration
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The test parameters documented do not totally comply with the specific testing guideline, but they are sufficient to accept the data. The test was conducted according to internationally accepted testing guidelines. Details about the read across approach are reported in the summary.
Data source
Reference
- Reference Type:
- publication
- Title:
- Safety Evaluation of a Alkaline cellulase
- Author:
- Greenough R.J., Everett D.J. and Stavnsbjerg M.
- Year:
- 1 991
- Bibliographic source:
- Fd Chem. Toxic. Vol. 29, No. 11, pp. 781-785, 1991
Materials and methods
- Principles of method if other than guideline:
- Groups of five male and five female rats were dosed orally by gavage with the test item, for five consecutive days with 0, 0.3, 1.0 or 3.0 g/kg body weight/day and killed 6 hours after the final dose. A further group was given a single i.p. dose of 100 mg methyl methanesulphonate/kg as a positive control. Slides of bone marrow cells were prepared and examined microscopically for chromosomal damage and mitotic indices were derived.
- GLP compliance:
- not specified
- Type of assay:
- chromosome aberration assay
Test material
- Reference substance name:
- Alkaline cellulase
- IUPAC Name:
- Alkaline cellulase
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
Administration / exposure
- Route of administration:
- oral: gavage
- Duration of treatment / exposure:
- Five days
- Frequency of treatment:
- Daily
- Post exposure period:
- Animals were killed 6 hr after the final dose.
One hour before the rats were killed they were treated with democolcine to arrest cells in metaphase.
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 0.3, 1.0 or 3.0 g/kg bw/day
Basis:
- No. of animals per sex per dose:
- Groups of five male and five female.
- Positive control(s):
- A further group of five male and five female rats was given a single i.p. dose of 100 mg methyl methanesulphonate/kg as a positive control and these rats were killed after 24 hr.
Examinations
- Tissues and cell types examined:
- Slides of bone marrow cells were prepared and examined microscopically for chromosomal damage and mitotic indices were derived.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- not specified
- Positive controls validity:
- valid
- Additional information on results:
- There were no significant increases in chromosome aberrations, excluding gaps, in males or females at any dose level of the test item.
Female rats treated with the test item showed increases in aberrations including gaps at all doses but with no clear dose relationship and only statistically significant (chi squared = 5.02; P = 0.025) at 3.0 g/kg/day.
Treatment with the test substance had no effect on the mitotic capacity of bone marrow cells and it was concluded that the substance was not a chromosome mutagen for the rat in vivo.
The positive control rats showed clear chromosome damage.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
The test substance is not a chromosome mutagen for the rat in vivo. - Executive summary:
Groups of five male and five female Sprague-Dawley rats were dosed orally by gavage with the test item, for five consecutive days with 0, 0.3, 1.0 or 3.0 g/kg body weight/day and killed 6 hours after the final dose. A further group was given a single i.p. dose of 100 mg methyl methanesulphonate/kg as a positive control and these rats were killed after 24 hours. Slides of bone marrow cells were prepared and examined microscopically for chromosomal damage and mitotic indices were derived.
The positive control rats showed clear chromosome damage.
There were no significant increases in chromosome aberrations, excluding gaps, in males or females at any dose level. Female rats showed increases in aberrations including gaps at all doses but with no clear dose relationship and only statistically significant at 3.0g/kg/day. Treatment with the test substance had no effect on the mitotic capacity of bone marrow cells.
Conclusion
The test substance is not a chromosome mutagen for the rat in vivo.
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