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Diss Factsheets
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EC number: 942-993-1 | 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 aquatic invertebrates
Administrative data
Link to relevant study record(s)
Description of key information
EL50 (invertebrates) = > 100 mg/L ; WAF loading 48hour-freshwater, OECD TG 202, WIL Research B.V. 2015
Key value for chemical safety assessment
Additional information
The acute toxicity to Daphnia magna was carried out according to OECD TG 202 Daphnia sp., Acute Immobilisation Test and EU Method C.2 guidelines. Twenty Daphnia magna per test group (4 replicates, 5 per vessel) were exposed to an untreated control group and to a WAF prepared at a test item loading rate of 100 mg/L. In the combined range-finding test ten daphnia per test group (2 replicates, 5 per vessel) were exposed to WAFs prepared at loading rates of 1.0 and 10 mg/L. All test concentrations were individually prepared and magnetically stirred for two days to ensure that maximum dissolution was obtained. This resulted in clear solutions all containing a floating layer of undissolved test item droplets. The Water Accommodated Fractions (WAFs) were subsequently collected after a three-hour stabilisation period. The final test solutions were all clear and colourless. A limit test was combined with a range-finding test. No significant effects on mobility of the organisms were observed at any of the WAFs tested. Samples for Total Organic Carbon (TOC) analyses were taken at the start and the end of the test period. TOC-analysis showed a measured organic carbon concentration of 0.75 mg C/L at the start of the test in the WAF prepared at a loading rate of 100 mg/L. The concentration measured after 48 hours had slightly decreased to 0.52 mg C/L. Analyses of the control group at the start and after 48 hours showed negligible concentrations of 0.09 and 0.06 mg C/L, respectively. These results should be considered as indicative only. The detection limit of the equipment was approximately 1 mg C/L and thus results at or below 1 mg C/L should be considered as estimates. The study met the acceptability criteria. The 48h-EL50 exceeded the WAF prepared at a loading rate of 100 mg/L and is therefore considered to be >100 mg/L.
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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