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EC number: 204-649-2 | CAS number: 123-76-2
- 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
EC50 (48h) > 100 mg/l (nominal)
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 100 mg/L
Additional information
The toxicity of test material to daphnids was evaluated according to the OECD Guideline 202. Twenty daphnids, divided in groups of five, were exposed to different concentrations of the substance ranging from 2200 and 10000 mg/l. After 24 h in darkness, the immobilization of the daphnids was measured. The daphnids that were unable to swim for 15 s after gentle stirring were considered immobile; EC50 (24h) = 6234 ± 466 mg/l (nominal)
A second study is performed according to the OECD 202 and EU Method C.2 and under GLP conditions. This study is performed as a limit test in order to evaluate the toxicity of the test item in an acute immobilisation test under static conditions towards Daphnia magna. Daphnia magna Straus was chosen in the guideline as a typical species of zoo-plankton. Young daphnia, aged less than 24 hours at the start of the test, are exposed to the test item for a period of 48 hours. Immobilisation is recorded at 24 hours and 48 hours and compared with control values. Not more than 10 % of the control daphnia should show immobilisation or other signs of disease or stress, for example, discoloration or unusual behaviour such as trapping at surface of water. The results are analysed in order to determine the EC50at 48 h is determined.
A positive control was tested in a separate study to assure that the test conditions are reliable.
The limit test was chosen based on the results of the range finding test. Ten daphnids per concentration were exposed to 0 -1 -10 -100 mg/l and the immobilisation was observed at 24 and 48 hours. One daphnid was found immobilised at the highest tested concentration at 24 hours and at 48 hours. No daphnids were immobilised in the rest of the tested concentrations.
Therefore, for the main study only one concentration at 100 mg/l was chosen. For the test concentration and the blank control, 20 daphnia were exposed to the test item for 48 hours in a static test system. After 24 and 48 hours, the immobilised daphnia were counted.
At the start and at the end of the test, the content of the test item in the test solutions was determined using HPLC.
The measured concentration was 93 % of the nominal concentrations at the beginning of the test and 104 % of the nominal concentrations at the end of the test. Therefore, the determination of the biological results was based on the nominal concentration.
None of the animals was immobilised in the blank control and the tested concentration.
The EC50 at 48 h (nominal) is therefore > 100 mg/l.
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