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Diss Factsheets
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EC number: 701-315-2 | 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
Acute rangefinder studies conducted with fish, Daphnia and algae showed no toxicity at the highest concentration tested (10 mg L-1). Definitive studies were not conducted due to the poor solubility of the test item, as it was not possible to get significant amounts of the test item into solution.
In an activated sludge respiration inhibition test a 3h-NOEC of 3.2 mg L-1, 3h-EC10 of 31 mg L-1 and 3h-EC50 of >100 mg L-1 were determined based on inhibition of total respiration (without the nitrification inhibitor ATU). A 3h-NOEC of 1 mg L-1, 3h-EC10 of 20 mg L-1 and 3h-EC50 of >100 mg L-1 were determined based on inhibition of heterotrophic respiration (with the addition of ATU). In this study the test solutions were not filtered as filtered solutions are less relevant when assessing toxicity in a STP, and it is considered likely that the difference in results between this study and the other aquatic toxicity studies is due to the presence of undissolved test item.
Additional information
Rangefinder studies showed no toxicity at nominal concentrations up to 10 mg L-1 (highest concentration tested) for fish, Daphnia and algae. Analytical monitoring of both the organic ligand and platinum showed very low concentrations of platinum and the organic ligand could be detected in solution. As the test item is very poorly soluble and it was not possible to get more of the test item into solution, aquatic toxicity is not expected at the limit of solubility and this was demonstrated in the rangefinding studies. Definitive studies were not conducted for fish, Daphnia or algae.
An activated sludge respiration inhibition test was conducted with the test item. A 3h-NOEC of 3.2 mg L-1, 3h-EC10 of 31 mg L-1 and 3h-EC50 of >100 mg L-1 were determined based on inhibition of total respiration (without the nitrification inhibitor ATU). A 3h-NOEC of 1 mg L-1, 3h-EC10 of 20 mg L-1 and 3h-EC50 of >100 mg L-1 were determined based on inhibition of heterotrophic respiration (with the addition of ATU). In this study the test solutions were not filtered as filtered solutions are less relevant when assessing toxicity in a STP, and it is considered likely that the difference in results between this study and the other aquatic toxicity studies is due to the presence of undissolved test item.
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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