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Diss Factsheets
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EC number: 235-120-4 | CAS number: 12070-08-5
- 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
Endpoint summary
Administrative data
Description of key information
Additional information
Titanium carbide was not tested for terrestrial toxicity and read-across to titanium dioxide and titanium trichloride was used for these endpoints.
For titanium substances, the read-across strategy is predicated on the assumed presence and bioavailability of a common metal anion in environmental media after exposure to titanium compounds. This is a reasonable assumption for the majority of inorganic compounds.
For environmental endpoints, it is the relative mobility and resulting bioavailability in various environmental compartments that determines the potential toxicity to ecological receptors. In the absence of data for titanium carbide, the most simplistic and conservative approach to hazard evaluation, using the read-across strategy, is to assume that titanium carbide which is to be evaluated shows the same systemic hazards as titanium dioxide and TiCl3, which show a higher release of titanium ions compared to titanium carbide (T/D test, solubility below the detection limit of 0.4 µg/L). (Bioelution results (KMHC, 2012) are in this case of minor relevance as earthworms and woodlice digest food by enzymatic degradation during gut passage without influence of gastric fluids.)
Titanium dioxide is not toxic to soil macroorganisms: Bulk titanium dioxide was not toxic to Eisenia fetida in an earthworm reproduction test (OECD 222) at a concentration of 1000 mg/kg soil dw, and no effects were noted in a feeding study with Porcellio scaber at concentrations up to 3000 mg TiO2/kg food.
Relevant key studies for the endpoints toxicity to terrestrial plants and toxicity to terrestrial microorganisms are not available. However, additional testing is not required for both endpoints. In accordance with REACH Annex IX, 9.4, column 2, the equilibrium partitioning method (EPM) based on aquatic data may be applied to assess the hazard to soil organisms in the absence of reliable toxicity data for soil microorganisms and terrestrial plants. However, since no hazard was identified for aquatic organisms, consequently no hazard is identified for terrestrial organisms via EPM. In addition, the available key studies on earthworms and soil arthropods do not indicate toxic effects for soil organisms. Furthermore, the results of the T/D test indicate that Ti need not be expected to be bioavailable in the soil matrix.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.