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EC number: 233-788-1 | CAS number: 10361-37-2
- 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
Endpoint summary
Administrative data
Key value for chemical safety assessment
Additional information
in vitro clastogenicity
Based on the outcome of guideline-compliant studies barium dichloride does not induce chromosome aberrations in mammalian cells, when tested up to toxic and/or precipitating concentrations in two independent experiments in the absence and presence of a rat liver metabolic activation system (S9 mix).
Overall it can be concluded that barium dichloride does not induce chromosome aberrations in vitro in somatic mammalian cells. Therefore the conduct of in vivo clastogenicity experiments is not required.
in vitro gene mutation
Anonymous (1994)
The authors state that barium dichloride induces gene mutations in cultured mouse lymphoma cells (L5178Y) in the presence of S9 in a statistical significant manner. However, the mutation frequency increased from 32 per 106
cells in the control culture to a maximum of 59 per 106 cells at 1000µg/mL (with a RTG of 10%). Being a statistical significant increase in mutation frequency, the biological fignificance however is considered questionable, since the highest MF is still well below the value recommended by the IWGT (Moore et al., 2003; Moore et al., 2006; Moore et al., 2007) of 154 per 106 cells. Furthermore a comparison with historical data for the performing laboratory is not possible, since the data was not given in the study report.
Due to the questionable biological relevance, the statistical significant increase in mutation frequency in both barium dichloride cultures with metabolic activation is not considered as clear positive response. Therefore it was decided to repeat the whole experiment under clearly defined conditions, which a highly pure test item under guideline and GLP compliant conditions.
Lloyd (2010)
It is concluded that barium dichloride did not induce gene mutations in the TK locus of L5178Y mouse lymphoma cells when tested up to toxic and/or precipitating concentrations in two independent experiments in the absence and presence of a rat liver metabolic activation system (S9 mix).
Overall it can be concluded that barium dichloride does not induce gene mutations in vitro in bacteria and somatic mammalian cells. Therefore the conduct of in vivo gene mutation experiments is not required.
References
Moore M et al. (2003)
Mouse lymphoma thimidine kinase gene mutation assay: International workshop on Genotoxicity tests workgroup report – Plymouth, UK 2002. Mutation Research (2003), 540, 127-140.
Moore M M, Honma M, Clements J, Bolcsfoldi G, Burlinson B et al. (2006)
Mouse lymphoma thymidine kinase gene mutation assay: follow up meeting of the International Workshop on Genotoxicity Testing – Aberdeen, Scotland, 2003 – Assay acceptance criteria, positive controls, and date evaluation. Environmental and Molecular Mutagenesis 2006, 47, 1-5.
Moore M M, Honma M, Clements J, Bolcsfoldi G, Burlinson B et al. (2007)
Mouse lymphoma thymidine kinase gene
mutation assay: meeting of the International Workshop on Genotoxicity
Testing, San Francisco, 2005, recommendations for 24-h treatment.
Mutation Research 2007, 627, 36-40.
Justification for classification or non-classification
None of the in vitro genotoxicity studies rated as reliable showed any effect in bacterial reverse mutation assays, in mammalian cell gene mutation tests (TK assay) or in mammalian cell chromosome aberration tests, thus the classification criteria according to regulation (EC) 1272/2008 as germ cell mutagen are not met.
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