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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
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EC number: 243-929-9 | CAS number: 20634-12-2
- 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
Description of key information
Additional information
The general principles applied for read across between metal substances are that ecotoxicity and the potential for adverse environmental effects are based on the metal ion in cases where the counter ions can reasonably be expected to be non-toxic, as is the case for many simple metals salts (e.g. anions such as SO42-, NO3-, OH-).
When reading across between different metal substances, the oxidation state of the metal ion needs to be carefully considered. For metals, chemical speciation can affect both the fate of the substance in the environment and its toxicity. For some metals (e.g. chromium and arsenic), large differences in environmental toxicity between difference oxidation states have been observed. For platinum substances, the database of ecotoxicity data is not as extensive as for other metal substances, but there may be a difference in toxicity between platinum (II) and platinum (IV) substances. For this reason, read-across between different substances is limited to metal compounds in which the metal exists in the same oxidation state.
Based on the available ecotoxicity data for platinum substances, it is evident that the ecotoxicity of platinum substances is not controlled by the concentration of platinum in the substance alone. It would appear that there may be a similar situation as has been observed for palladium, in that the chloride complexes may exhibit greater toxicity than complexes with other ligands. It is not, however, currently possible to identify a clear cut-off between chloro-platinum compounds and other platinum complexes, or to provide a mechanistic explanation of the effect. However, due to the observed differences in toxicity between chloride complexes and substances without chloride ligands, and similar behaviour observed for some other precious metals, for platinum substances without a chloro ligand data are only read across from other substances that do not contain a chloro ligand.
Data for both tetraammine platinum hydrogen carbonate and platinum tetraammine diacetate are therefore read across to tetraammineplatinum dinitrate, as all are platinum (II) substances that do not contain a chloro ligand. The lowest reported effect level is included as the key value for each endpoint.
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.