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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: - | 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
Adsorption / desorption
Administrative data
Link to relevant study record(s)
Description of key information
A number of physical-chemical properties of the pure substance, which is a solid powder of medium dustiness, are given here because they are needed in the modelling of environmental concentrations. The substance’s water solubility is very high (>176 g/L at 20 °C) and its vapour pressure (2 x 10-22 Pa at 25 °C) and octanol-water partitioning coefficient (log KOW is -2 at 20 °C) are very low. Though the dye has a low KOW, the substance exhibits a significant sorption capacity and this was reflected by choosing a KOC value of 1,000,000 L/kg.
This KOC value has been used to derivate the PNECs applying the Partitioning Method.
Key value for chemical safety assessment
- Koc at 20 °C:
- 1 000 000
Additional information
The HPLC method for Koc estimation is a guideline-conform study under GLP. However, the protocol as given by OECD Guideline 121 states "If the actual results show that the log Koc of the test substance is outside the calibration range the test should be repeated using different, more appropriate reference substances". As during this study the retention time of the test item was outside the retention times of the calibration substances (i.e. outside log Koc range 1.5 to 5.0), and the test still was not repeated, this has to be considered as some relvant deviation from the study protocol. Still, as stated in the study report, the chromatography of the test item resulted in one main peaks with well-defined and reproducible retention times, the HPLC method was therefore considered to be suitable for the purpose of the study. Furthermore in the study report QSPR computations of the estimated Koc of the test item are given, and these computed values are in alignment with the HPLC data.
Based on a weight of evidence approach the study result from the HPLC method Koc < 18 therefore can be condsidered as acceptable. The result from the HPLC method is Koc < 18, which basically was being confirmed by the result from the QSPR computation Koc = 1.2. Based on the mobility classification system of McCall (1981) the substance falls within the bracket Koc 0 - 50, and therefore is to be considered as of very high mobility.
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.