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EC number: 444-860-9 | CAS number: 474510-57-1
- 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
- Bioaccumulation potential:
- no bioaccumulation potential
Additional information
Chemistry
The test material (340.4Da) is a yellowish powder, slightly soluble in water (9.9 mg/l). The melting point is at 84.3 °C and a vapour pressure of < 0.00016 hPa indicates very low volatility. The log Pow is 2.3 (at pH 4.5).
Absorption
In acute oral and dermal toxicity studies, rats were administered to the test substance. Mortality did not occur in any of the studies. Clinical signs of toxicity (transient), i.e. hunched posture, ruffled fur and emaciation were observed after oral administration in male and female animals. Gross necropsy did not reveal any findings. The LD50 is therefore considered to be > 2000 mg/kg bw.
The NOAEL in male and female rats in a subacute oral repeated dose study is 30 mg/kg bw due to adverse local irritative effects in the stomach, decreased body weight gain and lowered motor activity in the 90 mg/kg bw/day group. Discoloured feces, increased liver weights as well as liver cell hypertrophy in the (mid and) high dose group indicate systemic absorption of the substance. The test substance cannot undergo pH-dependent hydrolysis (pH 4, 7, 9), thus, it expected that the unchanged (parent) substance is taken up into the system. According to the model of Fitzpatrick [1], the test item is slightly skin permeable.
Metabolism
Treatment-related diffuse liver cell hypertrophy was recorded at 90 mg/kg body weight/day and was considered to be adaptive. This hypertrophy was associated with follicular cell hypertrophy in thyroid glands in some males and females at 90 mg/kg body weight/day. Most probably the enhanced liver cell metabolism resulted in an acceleration of thyroid hormone breakdown with consequent thyroid follicular cell hypertrophy. Xenobiotic induced thyroid hormone breakdown is often associated with an enhanced expression of CYPs P450 and UDP-glucuronyltransferases. Thus, it can be assumed that the test item will be conjugated with UGT, e.g. at its hydroxylgroups. Reduction of the keto-groups followed by conjugation is also plausible.
Excretion
In regard to the low molecular weight the primary elimination pathway of the test substance will be the urinary excretion of the glucuronidation product. Additionally, yellowish discoloured feces after repeated dose administration could be a hint for fecal excretion of unchanged material.
[1] Modelling skin permeability in risk assessment––the future, D. Fitzpatrick et al, Chemosphere 55 (2004) 1309–1314
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