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EC number: 258-605-2 | CAS number: 53523-90-3
- 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
Key value for chemical safety assessment
Acute toxicity: via oral route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Acute toxicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Acute toxicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
No study on acute oral toxicity is available for the substance. A range finder study in rats, initially conducted with gavage administration, revealed that the substance was retained in the rat stomach, possibly due to a low solubility under acidic stomach conditions. Subsequently, animals at doses from 500 to 1000 mg/kg bw died or had to be killed interim due to animal welfare obligations. At necropsy a build-up of the test substance (yellow compacted mass) was observed in the stomach. No indications for a systemic effect could be identified. Due to these technical problems and taking into account animal welfare considerations, an acute oral toxicity study with gavage doses up to the highest dose of 2000 mg/kg bw was omitted.
However, a reliable assessment on acute oral toxicity can be made based on the result of a repeated dose (28 -day) toxicity study with diets containing 500, 1000 and 2500 ppm test substance (adjusted for purity), equivalent to an estimated mean achieved dosage of approx. 45, 88 and 212 mg/kg bw/day (adjusted for purity) for males and 45, 88 and 213 mg/kg bw/day (adjusted for purity) for females.
It is important to note that 2500 ppm was the highest dietary concentration that was practical to test, as higher levels were precluded due to the decreased food consumption considered to reflect the palatability of the dietary formulations.
The human relevant NOAEL in the repeated dose study was 2500 ppm (approx. 212 mg/kg bw). Scientific evidence exists that a NOAEL of >/= 200 mg/kg bw will lead to a LD50 for acute oral toxicity of > 2000 mg/kg bw (Bulgheroni et al., Regulatory Toxicology and Pharmacology 53, 16 -19, 2009). This estimation of acute oral toxicity seems to be appropriate here, since the available data demonstrate for the substance a low toxicity profile with no indications for an irritant or genotoxic potential (test battery for skin sensitisation not completed yet) and with no human relevant effects at repeated dose feed studies up to the highest concentration tested (OECD 407: solely rat specific alpha2µ-globulin kidney effects in male rats at highest dose tested and OECD 421: no adverse effects for general toxicity, fertility and developmental toxicity).
Summarizing, the predicted oral LD50 is for the substance > 2000 mg/kg bw.
No study on acute inhalation toxicity is available for the substance.
No study on acute dermal toxicity is available for the substance. According to REACH Regulation (EU) Annex 2016/863 such a study is only required if a substance meets the criteria for classification for acute toxicity or STOT SE by the oral route. Therefore, the conduct of a dermal toxicity study is waived, and the assessment of dermal toxicity is based on the oral toxicity assessment and on the other available information of the test substance.
The substance has a molecular weight of 720. 4 g/mol, which is in a range not favourable for dermal absorption. On the other hand, the good water solubility (240 g/L) might facilitate absorption through the skin. The assessment of acute oral toxicity led to a concluded LD50 of > 2000 mg/kg bw. Furthermore, the available data on skin/eye irritation/corrosion does not give evidence for a skin irritant potential that might facilitate absorption through the skin barrier.
Therefore, it is not expected that systemic availability after dermal exposure would be higher than after oral exposure. Based on the weight of evidences the conclusion can be drawn that for acute dermal toxicity no hazard is expected. This is in line with REACH Annex VIII (8.5.3) (Reg. (EU) 2016/863) that considers toxicity testing by the dermal route as not needed if a substance does not meet the criteria for classification as acute toxic by the oral route, and with further publications (Moore, Regulatory Toxicology and Pharmacology, 2013, 66, 30-37; Creton, St. et al, Critical reviews in Toxicology, 2010, Vol. 40 No.1, pages 50-83).
Justification for classification or non-classification
No classification concluded for Acute Toxicity according to Regulation (EC) No 1272/2008, Annex I.
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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