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EC number: 943-224-2 | CAS number: -
- 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
Short-term toxicity endpoints are available for freshwater fish, daphnia and algae which cover 3 trophic levels. From the results obtained the freshwater algae Pseudokirchneriella subcapitata emerges as the most sensitive species to the test substance with an ErC50of >0.274 mg/L. Short-term toxicity to fish The acute toxicity of dialuminium titanium pentaoxide to medaka (Oryzias latipes) was determined in a study carried out under semi-static conditions in accordance with OECD guideline 203 ''Fish, Acute Toxicity Test''. As the test substance is a poorly soluble inorganic compound, the test organisms were exposed to the test substance dissolved at the maximum saturation level, separated by filtration from a system loaded at a nominal rate of 100 mg/L. Concentrations of dissolved aluminium and titanium were determined by ICP-MS which were then used to calculate equivalent concentrations of the test substance. The test organisms were kept in 5 L aquaria and test solutions were renewed every 24 hours. After 96 hours of exposure no mortality or abnormal effects were observed. The 96hr LC50of dialuminium titanium pentaoxide was determined to be >0.468 mg/L based on aluminium analysis and >0.360 mg/L based on titanium analysis. All validity criteria were met and this study is considered reliable without restriction. Short-term toxicity to daphnia The acute toxicity of dialuminium titanium pentaoxide toDaphnia magnawas determined in a study which was carried out in accordance with OECD guideline 202 ''Daphniasp., Acute Immobilisation Test''. As the test substance is a poorly soluble inorganic compound, test organisms were exposed to the test substance dissolved at the maximum saturation level separated by filtration from a system loaded at a nominal rate of 100 mg/L. Concentrations of dissolved aluminium and titanium were determined by ICP-MS and were then used to calculate equivalent concentrations of the test substance. Test solutions were renewed every 24 hours. After 48 hours of exposure no immobilisation or abnormal symptoms were observed. The 48hr EC50of dialuminium titanium pentaoxide was determined to be >0.824 mg/L based on aluminium analysis and >0.687 mg/L based on titanium analysis. All validity criteria were met and this study is considered reliable without restriction. Algal growth inhibition test The inhibitory effect of dialuminium titanium pentaoxide on algal growth was determined in a 72 hour growth inhibition test withPseudokirchneriella subcapitata, conducted in accordance with OECD guideline 201. The algae were exposed to the test substance at loading rates of 0 (control), 10, 18, 32, 56 and 100 mg/L. Concentrations of dissolved aluminium and titanium were determined by ICP-MS which were then used to calculate equivalent concentrations of the test substance present in the test solutions. Test media were not renewed during the 72 hours. The 72hr ErC50 based on aluminium analysis was determined to be >0.388 mg/L. The 72hr ErC50 based on titanium analysis was determined to be >0.274 mg/L in the standard growth medium and >0.210 mg/L in the enhanced growth medium. The 72hr NOECr based on titanium analysis was determined to be 0.210 mg/L in enhanced growth medium. The NOECr for the standard medium occurred at the 10 mg/L loading rate, while the NOEC for the enhanced medium occurred at 100 mg/L. As concentrations of test substance measured were comparable in the 100 mg/L treatments of both the standard and enhanced media, it was suggested that the effect of the test substance in the standard medium was due to decreased bioavailability of nutrients caused by aluminium and titanium forming complexes with components of the test media. This is not considered to be a toxicological effect and as such is not used for derivation of NOEC of endpoints. No unusual cell shape or agglutination was observed at any test concentration after 72 hours. |
Additional information
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