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EC number: 423-300-7 | CAS number: 128554-52-9
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
Description of key information
Concentration levels of test substance that induced effects on crustaceans exceeded the maximum solubility of test substance in water (<0.64 mg/l).
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 4.5 mg/L
Additional information
The test substance was assessed for acute toxicity to invertebrates according to EU Method C2 under static conditions for 48 hours.
After a limit test, two full tests were performed with daphnids exposed to 4.5 to 100 mg/l and 0.1 to 4.5 mg/l, respectively. In the limit test, the test solution was prepared using Tween 80 as a dispersent. No additives were used in the full tests. The test consisted of two vessels per group containing 10 daphnids per vessel. Samples for analysis were taken at the start and the end of the full tests and analysed for determination of Total Organic carbon (TOC).
A part of the organisms became immobilised during the limit test in both the filtered and the unfiltered solution.
During the first full test, no effect on mobility of Daphnia magna was observed at any of the concentrations during the first 24 hours of exposure, while significant numbers became immobilised in all test solutions during the last part of the 48-hour test period. There was no clear relation between response and test concentration. In the second full test, however, no immobilisation was induced by any of the concentrations tested, including 4.5 mg/l.
TOC analyses showed that during the second full test, Daphnia magna were exposed to a higher average concentration of test substance in the water phase of the nominal concentration of 4.5 mg/l, while no effect on mobility was observed.
In conclusion, concentration levels of test substance that induced effects on crustaceans exceeded the maximum solubility of test substance in water (<0.64 mg/l). These effects were not test concentration related, but probably caused due to physical damage to or mechanical obstruction of the swimming apparatus of the organisms exposed caused by flocculation of the undissolved fraction of the test substance. Hence, the 48h EC50 for Daphnia magna was beyond the maximum solubility of the test substance in water.
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