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EC number: 931-384-6 | CAS number: -
- 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
Steady state estimates of the BCF was considered to be the most accurate of the available BCF estimates from investigation of an analogue substance (US EPA OPPTS 850.1730 and OECD 305).
Additional information
A bioconcentration study in rainbow trout was conducted according US EPA OPPTS 850.1730 and OECD 305 Guidelines using an analogue substance.
Supply of test water: Continuous flow-through diluter system The length of exposure was 97 days with 35 days uptake and 62 days depuration.
The target concentrations were solvent control, 0.25 ug/L and 2.5 ug/L. The mean measured concentrations were <LOQ, 0.25 ug/L and 2.8 ug/L for the solvent control, low exposure level, and high exposure level respectively.
Based on the mean measured concentrations in water the Steady state BCF for the whole fish at the low exposure level was 426 (266-619 95% CI) and the steady state BCF for the whole fish in the high exposure level was 432 (210-571 95% CI).
Steady-state concentrations of 14C-test material were achieved in the tissues of rainbow trout (Oncorhynchus mykiss) after 31 days. The mean measured water concentrations based on total radioactivity were 0.25 and 2.8 μg/L. Steady-state BCF values for the 0.25 μg/L test concentration, based on total radioactivity test material concentrations were 301, 625 and 436 in edible, non-edible and whole fish tissue, respectively. Steady-state BCF values for the 2.8 μg/L test concentration, based on total radioactivity test material concentrations were 260, 673 and 432 in edible, non-edible and whole fish tissue, respectively. Test material depurated slowly from fish tissue and consequently the study was terminated after reaching 62 days depuration, even though concentrations in the fish tissues remained above 10% of the steady state values. Because the declining concentrations in the tissues did not follow the first order assumptions kinetics required for valid kinetic estimates of BCF, the results of the derived kinetic BCF values were questionable and the steady state estimates of the BCF was considered to be the most accurate of the available BCF estimates from this study.
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