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Diss Factsheets
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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
Ecotoxicological Summary
Administrative data
Hazard for aquatic organisms
Freshwater
- Hazard assessment conclusion:
- PNEC aqua (freshwater)
- PNEC value:
- 0.21 µg/L
- Assessment factor:
- 1 000
- Extrapolation method:
- assessment factor
Marine water
- Hazard assessment conclusion:
- PNEC aqua (marine water)
- PNEC value:
- 0.021 µg/L
- Assessment factor:
- 1 000
- Extrapolation method:
- assessment factor
STP
- Hazard assessment conclusion:
- no hazard identified
Sediment (freshwater)
- Hazard assessment conclusion:
- no hazard identified
Sediment (marine water)
- Hazard assessment conclusion:
- no hazard identified
Hazard for air
Air
- Hazard assessment conclusion:
- no hazard identified
Hazard for terrestrial organisms
Soil
- Hazard assessment conclusion:
- no hazard identified
Hazard for predators
Secondary poisoning
- Hazard assessment conclusion:
- no potential for bioaccumulation
Additional information
The aquatic PNECs for dialuminium titanium pentaoxide were derived from short-term studies conducted using freshwater aquatic species from three different trophic levels. It should be noted that the low PNEC values stem from the limited aqueous solubility of dialuminium titanium pentaoxide rather than a high intrinsic toxicity. The PNECs are as follows: PNEC aqua (freshwater)= >0.210 µg/l PNEC aqua (marine water)= >0.0210 µg/l PNEC aqua (intermittent releases)= >2.10 µg/l The derivation of PNECs for the other compartments was not considered necessary as aluminium and titanium occur ubiquitously in the environment at concentrations which are high compared to that which is likely to arise from dialuminium titanium pentaoxide. |
Conclusion on classification
This substance does not warrant any classification. The acute toxicity of the substance to aquatic organisms was measured up to the limit of solubility. Although the lowest LC50 for the substance is less than 1 mg/l, it is judged that the substance should not be classified as toxic to aquatic life based on observed solubility levels. It is likely that the true LC50 is far greater but this would be in excess of the maximum solubility of the substance and as such this concentration could not be achieved in laboratory tests or in the environment. As the aquatic toxicity tests were conducted according to the OECD series on testing and assessment number 23 (guidance document on aquatic toxicity testing of difficult substances and mixtures) with a maximum loading rate of 100 mg/l, the concentration of the substance dissolved in the aquatic toxicity tests is considered to be equivalent to the concentration that would occur in a 7 -day transformation/dissolution test at a high loading rate. Further to this in a 14 -day solubility test at 40 degrees Celsius with a maximum loading rate of 1000 mg/l, the solubility of the test substance was found to be less than 0.1 mg/l. This evidence strongly indicates that the test substance will not be soluble in the environment at a concentration that will result in significant toxicity. As such, no classification is triggered based on the available data, according to EEC directive 79/831/EEC Annex VI, Part II (D) as described in Commission Directive 93/21/EEC or regulation (EC) No 1272/2008. No hazards for the environment have been identified. In addition dialuminium titanium pentaoxide is not a PBT (or vPvB) substance (see section 2.3). |
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