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EC number: 247-384-8 | CAS number: 25973-55-1
- 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
Link to relevant study record(s)
Description of key information
Key value for chemical safety assessment
Additional information
The test substance is a light yellow powder with a molecular weight of 351.49 g/mol. The log P o/w value is 7.25 and the solubility in water is < 1 µg/l (20°C, pH 6.3). The particle size was examined to be < 10 µm = 37.9 % and < 4 µm = 7.2% (MMD = 11.5 µm).
In an acute oral toxicity study, TIF: RAIf (SPF) rats were administered doses of up to 7750 mg/kg body weight per gavage (CIBA-Geigy study, Siss 6481, 1978). No mortalities occurred and the LD50 oral was set to be > 7750 mg/kg body weight. However, according to the physico-chemical properties (molecular weight, log P o/w) the test substance is expected to be absorbed through the gastrointestinal tract (ECHA R7c). This is supported by two independent subchronic studies conducted in beagle dogs (Inbifo, No. A 0176/049, 1970) and albino rats (TNO, No. R 2640, 1968). The test substance was administered via the diet in doses of 15 - 240 mg/kg body weight and 10 - 173 mg/kg body weight, respectively. In both studies significant food depression occurred and one dog starved. No further mortalities occurred. Both studies report liver effects induced by the test substance down to the lowest dose levels applied. Furthermore, effects on kidneys and discolouration of the urine were observed, indicating a systemic availability of the test substance. Based on the lipophilic properties of the test substance, the liver appears to be the main site of metabolism. The metabolites are assumed to be excreted predominantly via the renal pathway.
The dermal uptake of the test substance is unlikely due to its physico-chemical parameters. However, in a dermal repeated dose study conducted in albino rabbits (University of Miami, No. 69, 1977) with 140 mg/kg body weight, discolouration of the urine was observed. Indicating a systemic availability, it is not clear, whether the test substance was absorbed via the dermal route or the uptake was artificial because of inappropriate experimental design. Furthermore, the test substance did not exhibit any acute dermal toxicity (Geigy (U. K.) Ltd., 8/69/S. L., 1969), skin irritative / corrosive (CIBA-Geigy, No. 874135, 1987), eye irritative (CIBA-Geigy, No. 874134, 1987) or skin sensitisation properties (CIBA-Geigy, No. 874136, 1987), respectively.
Inhalative absorption of the test substance is likely due to the particle size and the physico-chemical parameters (poor water solubility and log P o/w). In contrast, an acute inhalative toxicity study (CIBA-Geigy, Siss 3502, 1973) did not reveal signs for bioavailability via the respiratory pathway. Tif. RAI rats were exposed using a nose-only system to a technically maximal achievable analytical substance concentration of 0.4 mg/l for 4 hours and did not show any clinical sign of toxic effects of the test substance.
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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