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EC number: 610-104-3 | CAS number: 43100-47-6
- 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
Toxicokinetic assessment
There were no studies available in which the toxicokinetic properties of the test substance were investigated. The test substance (molecular weight = 586.6 g/mol) is a white solid with a Log Pow > 6.5 (measured, BASF 2008) and 11.11 (EPI Suite calculation, BASF 2014), a water solubility of < 0.1 mg/L at 20°C (BASF 2008), and a vapor pressure of 2.12*10^-17 hPa (calculated).
Absorption
Based on the physico-chemical data (low water solubility, molecule size, Log Pow) it is assumed that there is no or only very slow absorption after oral ingestion of the test article. This is supported by the available acute oral toxicity study (BASF 2008) which did not reveal any signs of systemic toxicity and resulted in a LD50 of greater than 2000 mg/kg. Furthermore, in the available Combined repeated dose toxicity study with the reproduction/developmental toxicity screening test (BASF 2015) which was performed with rats at dose levels of 100, 300 or 1000 mg/kg bw/day, no effects on body weight, food consumption, clinical pathology, organ weights, histopathology, reproductive function and reproductive performance were reported with a NOAEL of greater than 1000 mg/kg bw/day. The lack of systemic toxicity in these studies suggests poor bioavailability upon oral ingestion. As a result an accumulation of the test article in the body can be excluded.
Dermal absorption is equally unlikely, due to the size of the chemical, the Log Pow of > 10 and the very low water solubility. Highly lipophilic substances that come into contact with the skin can readily penetrate the lipid rich stratum corneum but are not well absorbed systemically. Although they may persist in the stratum corneum, they will eventually be cleared as the stratum corneum is sloughed off. Furthermore, dermal uptake of chemicals with a molecular weight >500 is not favored (ECHA GD 7c, 2008). This is in line with the available toxicity data after dermal exposure. In an acute dermal toxicity study (BASF 2015) and in a LLNA (BASF 2008), no indications of systemic availability after dermal application were detected. In conclusion, a dermal uptake of the test substance is expected to be low.
No reliable inhalation studies are available. However, given its very low vapor pressure and low water solubility, systemic availability after exposure to dust particle of the test substance is expected to be low. In addition, particle size distribution analysis revealed that 77.6% of the test substance consists of particles larger than 100 µm. Therefore, the majority of generated particles will not penetrate into the broncho-alveolar tract.
Excretion
In view of the absence of relevant findings and the expected low bioavailability, it can be assumed that the test substance is rapidly excreted. Since the test substance has a molecular weight larger than 500 g/mol and a low solubility in water, it is expected to be excreted predominantly via the feces (ECHA GD 7c, 2008).
Overall conclusion
The physico-chemical data suggest low oral and dermal absorption of the test substance which is supported by the findings of available toxicity studies. Therefore, bioavailability of the test substance is predicted to be low and rapid excretion via the feces is expected.
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