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EC number: - | 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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
96 h LC50 2.2 mg/L (Cyprinus carpio), OECD 203, EU Method C.1 and OECD 23
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 2.2 mg/L
Additional information
In the key study, the toxicity of the test material to Carp (Cyprinus carpio) was investigated in accordance with the standardised guidelines OECD 203, EU Method C.1 and OECD 23 under GLP conditions. The study was awarded a reliability score of 1 in accordance with the principles for assessing data quality set forth by Klimisch et al. (1997).
The batch of test material tested was not completely soluble in test medium at the initial loading rate prepared. Preparation of test solutions started with a loading rate of 100 mg/L, applying two days of magnetic stirring to ensure maximum dissolution of the test material in the test medium was reached. The resulting dispersion was filtered twice through a 0.45 µm membrane filter to remove the undissolved test material. The resulting Water Soluble Fraction (WSF) was used as highest test concentration and used to prepare the lower test concentrations by subsequent dilution in test medium.
A final LC50 test was performed based on the results obtained in a preceding range-finding test. Seven carp per test group were exposed to an untreated control and to test concentrations representing 10, 18, 32, 56 and 100 % of a WSF prepared at a loading rate of 100 mg/L. The total test period was 96 hours and a static test system was applied. Samples for analytical confirmation of actual exposure concentrations were taken at the start and the end of the test and on days with complete mortality observed in a particular test group.
Analysis of the samples taken at the start of the final test showed measured concentrations of 0.68, 1.14, 2.0, 2.83 and 5.87 mg/L for the test groups representing 10, 18, 32, 56 and 100 % WSF, respectively. A slight decrease was observed in the two highest solutions with complete mortality after 24 and 48 hours, respectively. A somewhat higher decrease was observed at the end of the test period in the three lowest test groups with surviving fish. The range tested based on average measured concentrations corresponded with 0.49, 0.97, 1.6, 2.9 and 5.8 mg/L. The concentration measured in the undiluted WSF was comparable to the water solubility (determined to be 5.89 mg/L).
The study met the acceptability criteria and was considered valid.
The 96 h LC50 was 2.2 mg/L based on average exposure concentrations with 0 % mortality at 1.6 mg/L and 100 % mortality at 2.9 mg/L and was reached after 48 hours of exposure.
Further information is available in the form of a disregarded study. The test was carried out using methodology similar to that outlined in the standardised guideline OECD 203 under GLP conditions, however there were shortcomings. The test material was not wholly soluble in water and was used as an homogeneous emulsion. There was no attempt to remove impurities such as xylene and no analysis of test material levels took place during the study. Effects are considered likely to be the result of physical contact with oil droplets combined with toxicity of impurities. The study was awarded a reliability score of 3 in accordance with the principles for assessing data quality set forth by Klimisch et al. (1997).
Salmo gairdneri were exposed to the test material for 96 hours. The LC50 was calculated to be 1.0 mg/L with 95 % confidence limits of 1.4 to 2.7 mg/L.
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