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EC number: 227-579-4 | CAS number: 5895-46-5
- 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 vitro
Administrative data
- Endpoint:
- in vitro cytogenicity / chromosome aberration study in mammalian cells
- 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
- Study period:
- 14 October 2005 to 12 May 2006
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Study conducted to GLP in compliance with agreed protocols, with no or minor deviations from standard test guidelines and/or minor methodological deficiencies, which do not affect the quality of the relevant results. These data have been read-across from a structurally similar compound.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 006
- Report date:
- 2006
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.10 (Mutagenicity - In Vitro Mammalian Chromosome Aberration Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- in vitro mammalian chromosome aberration test
Test material
- Reference substance name:
- Dicerium tricarbonate
- EC Number:
- 208-655-6
- EC Name:
- Dicerium tricarbonate
- Cas Number:
- 537-01-9
- IUPAC Name:
- dicerium tricarbonate
- Details on test material:
- Dicerium tricarbonate
Constituent 1
Method
Species / strain
- Species / strain / cell type:
- primary culture, other: human lymphocytes
- Details on mammalian cell type (if applicable):
- Blood samples were obtained from healthy donors not receiving medication. Blood samples were drawn by venous puncture and collected in heoparinized tubes. The tubes were sent to RCC-CCR to initate cell cultures within 24h after blood collection. If necessary, the blood was stored before use at 4 deg C.
- Metabolic activation:
- with and without
- Metabolic activation system:
- liver S9 fraction of rats induced with phenobarbital/napthoflavone
- Test concentrations with justification for top dose:
- Experiment 1: 45.6 - 7020 ug/mL with and without metabolic activiation
Experiment 2: 87.0 - 2500 ug/mL iwth and without metabolic activation - Vehicle / solvent:
- - Vehicle(s)/solvent(s) used: deionised water
- Justification for choice of solvent/vehicle: the solvent was chosen to its solubility properties and its relative non-toxicity to the cell cultures
- Vehicle controls tested: medium with solvent or vehicle alone
- volume of vehicle/solvent in the medium: 10% (v/v)
Controlsopen allclose all
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- Remarks:
- medium with solvent or vehicle alone
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- ethylmethanesulphonate
- Remarks:
- Migrated to IUCLID6: 660 ug/mL (5.32 mM) (Expt 1 and II) and 800 ug/mL (6.45 mM) (Expt 1) without metabolic activation
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- cyclophosphamide
- Remarks:
- Migrated to IUCLID6: 45 ug/mL (0.396 mM) (Expt 1) and 37.5 ug/mL (0.132 mM) (Expt II) with metabolic activation
- Details on test system and experimental conditions:
- * METHOD OF APPLICATION: in suspension
* DURATION: (see detailed table 2 below)
- Exposure duration: 4, 22 or 46 hours
- Expression time: 0, 18 or 46 hours
- Selection time : 3 hours before harvesting
- Fixation time: 22 or 46 hours
* SPINDLE INHIBITOR: colcemid
* STAIN: stained with Giemsa
* NUMBER OF REPLICATES: two
* NUMBER OF CELLS EVALUATED: 100 well spread metaphase plates per culture were scored for cytogenetic damage.
* DETERMINATION OF CYTOTOXICITY:
- Method: To describe a cytotoxic effect the mitotic index (% cells in mitosis) was determined in 1000 cells/culture.
* OTHER: SCORING METHOD: The slides were evaluated using NIKON microscopes with 100 x oil immersion objectives. Breaks, fragments, deletions, exchanges and chromosomal disintegrations were recorded as structural chromosome aberrations. Gaps were recorded as well, but they were not included in the calculation of the aberration rates - Evaluation criteria:
- A test item is classified as non-mutagenic if:
- the number of induced structural chromosome aberrations in all evaluated dose groups is in the range of the historical control data (0.0 - 4.0 % aberrant cells, exclusive gaps).
- no significant increase of the number of structural chromosome aberrations is observed.
A test item is classified as mutagenic if:
- the number of induced structural chromosome aberrations is not in the range of the historical control data (0.0 - 4.0 % aberrant cells, exclusive gaps), and
- either a concentration-related or a significant increase of the number of structural chromosome aberrations is observed. - Statistics:
- Statistical significance was confirmed by means of the Fisher´s exact test (p < 0.05)
Results and discussion
Test results
- Species / strain:
- primary culture, other: human lymphocytes
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity, but tested up to precipitating concentrations
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- TEST-SPECIFIC CONFOUNDING FACTORS:
- Precipitation: In experiment I, visible precipitation of the test item in the culture medium was observed at 427.7 µg/mL and above in the absence and presence of S9 mix. In addition, precipitation occurred in experiment II in the absence and presence of S9 mix at 152.3 µg/mL and above
- No relevant increase in the osmolarity or pH values was observed.
COMPARISON WITH HISTORICAL CONTROL DATA:
The aberration rates of the cells after treatment with the test item (0.0 - 2.0 % aberrant cells, exclusive gaps) were close to the range of the solvent control values (0.0 - 1.5 % aberrant cells, exclusive gaps) and clearly within the range of the historical control data: 0.0 - 4.0 % aberrant cells, exclusive gaps.
See detailed results in tables 3 and 4 below. - Remarks on result:
- other: all strains/cell types tested
- Remarks:
- Migrated from field 'Test system'.
Any other information on results incl. tables
Table 3: Results of chromosome analysis without metabolic activation
* Inclusive cells carrying exchanges P Precipitation occurred S Aberration frequency statistically significant higher than corresponding control values 1 Deionised water 10 % (v/v) 2 EMS 800.0µg/mL 3 EMS 660.0µg/mL
Table 4: Results of chromosome analysis with metabolic activation
* Inclusive cells carrying exchanges P Precipitation occurred S Aberration frequency statistically significant higher than corresponding control values 1 Deionised water 10 % (v/v) 2 CPA45.0 µg/mL 3 CPA37.5 µg/mL |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information):
negative with metabolic activation
negative without metabolic activation
In conclusion, it can be stated that under the experimental conditions reported, the test item did not induce structural chromosomal aberrations as deterimined by the chromosome aberration test in human lymphocytes in vitro. - Executive summary:
In a mammalian cell cytogenetics assay (chromosome aberration assay) (Schulz, 2006), primary lymphocyte cultures were exposed to Cerium carbonate (65.62% of purity), in distilled water, at concentrations of 45.6 - 7020 µg/mL or 87.0 - 2500 µg/mL with and without metabolic activation. The substance was tested up to precipitating concentrations. Positive controls induced the appropriate response. There was no evidence of chromosome aberration induced over background. Therefore, the substance is considered to be non-clastogenic in this chromosome aberration test when tested up to precipitating concentrations.
This study is classified as acceptable. This study satisfies the requirement for Test Guideline EU Method B.10 for in vitro cytogenetic mutagenicity data.
These data have been read-across from the analogue substance cerium carbonate.
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