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Diss Factsheets
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EC number: 208-909-6 | CAS number: 546-68-9
- 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
Testing of biodegradability in water is not scientifically justified as titanium tetraisopropanolate is hydrolytically unstable. Key study without restrictions on hydrolysis OECD 111 demonstrates that a complete hydrolysis (half-life < 3minutes) will take place with no significant reaction products other than isopropyl alcohol (IPA) and hydrated titanium dioxides.
In addition, biodegradability testing is not necessary to be tested for this substance as all the decomposition products have been identified. The most relevant degradation product (IPA) is also known to be readily biodegradable (> 70 % at 20-d biodegradation, Price et al. 1974). IPA is not toxic to aquatic environment and has no adsorption or bioaccumulation potential since it has a low log Kow value 0.05 (< 3). The other non-hazardous degradation product (TiO2) of this substance is inorganic and insoluble and therefore not relevant to be considered further in CSA. Ti compounds are not expected to bioconcentrate in soils, sediments or aquatic organisms (HSDB 2012).
Because this substance is highly water reactive use of water is avoided in the use applications, and direct exposure of the aquatic compartment is unlikely (see sections 9&10 of CSR). Only, when the target substance is used as a catalyst in industrial esterification processes, water is used to remove the catalyst from the process. The decomposition of the titanate catalyst will take place, and IPA and TiO2 are released to water compartment. Therefore, it is justified to use the biodegradability of the main degradation product (IPA) in the exposure assessment when relevant (see sections 9&10 of CSR).
As the rapid hydrolysis is the driving force for the fate and pathways of this substance, this abiotic degradation can be used to demonstrate fast degradation for the purposes of C&L.
Based on these facts, CSA does not indicate the need to investigate further the biodegradation in water, soil or sediments.
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.
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