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EC number: 208-807-1 | CAS number: 542-28-9
- 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
Additional information
With high probability acutely not harmful to aquatic organisms. The inhibition of the degradation activity of activated sludge is not anticipated when introduced in appropriate low concentrations.
This aquatic toxicity assessment was based on the following data:
The acute toxicity of the test substance to zebra fish was measured in a GLP guideline study according to OECD 203. Under the test conditions no visible or lethal effects in zebra-fish at or below 120 mg/L (limit test) were observable (BASF SE 17F0426/11X322, 2013). Based on these data, the test substance is considered to be "with high probability acutely not harmful to fish".
In a static GLP test according to EU method C.2 the acute toxicity of the substance to Daphnia magna was investigated (BASF 1998). After 48 hours no effects were observed in the highest nominal test concentration of 100 mg/L, indicating that the EC0 and EC50 are well above 100 mg/L. Due to the analytics, an arithmetic mean concentration of 74.7 mg/L was estimated. As already stated no effects occured in the highest concentration. Therefore, it is assumed that the substance is not harmful to aquatic invertebrates. Due to product saftey reasons the measured arithmetic mean value of 74.7 mg/L is used for the subsequent hazard assessment of the substance.
The toxicity of the test substance to the green algae Pseudokirchneriella subcapitata was investigated in a GLP guideline study according to OECD 201 (BASF SE 60E0426/11X323, 2013). In this study, the EC10 (72h) on the growth rate was determined to exceed the highest measured concentration of 142 mg/L (based on time weighted average). Based on this outcome, the test substance is considered to be "with high probability not harmful to aquatic algae".
As key study regarding toxicity to microorganisms a non-GLP test according to OECD guideline 209 was performed using domestic activated sludge as inoculum. After 30 minutes of exposure no respiration inhibition could be observed resulting in a EC0 of 1000 mg/L (BASF 90/1170/08/1, 1990). As a further result an EC10 (16h) of 95 mg/L from a test with Pseudomonas putida is available (BASF 1990). For PNEC derivation the EC0 values from the OECD 209 test is used as the test is more realistic for the assessment of toxicity to sewage works.
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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