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Diss Factsheets
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EC number: 200-262-8 | CAS number: 56-23-5
- 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
Long-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
Long-term toxicity to fish: NOEC = 2.5 mg/L for the zebrafish, 14 d-prolonged toxicity, flow-through (OECD TG 204); study Röderer (1990)
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 2.5 mg/L
Additional information
The value for the key parameter is based on the lowest observed value in a study considered to be reliable (key study: Röderer, 1990) using zebrafish Brachydanio rerio in a 14 -day prolonged toxicity test using a flow-trough system. This protocol is not considered as a true chronic test but rather a subchronic one.
The second study (Black, 1982) using rainbow trout and fathead minnow in short term toxicity tests on embryo and sacfry stages is regarded unreliable. According to Eurochlor assessment, this study has been criticised for testing widely spaced concentrations and giving few details of control performance (UK Department of the Environment, 1994) and the methods were non-standard and not well validated. However, they were conducted under flow-through conditions, with control of volatile loss and with analysis. Therefore, the long-term LC50 values quoted can be used with care. The 9 day-LC50 (4 days post-hatch) for P. promelas was 4 mg/l; for S. gairdneri, the 27 day-LC50 (4 days post-hatch) was 1.97 mg/l. A NOEC (which is required for the PNEC calculation) is not cited in the paper. The lowest concentration tested which had no discernible effect on survival of S. gairdneri (0.07 mg/l) is not valid as a NOEC, because of the wide interval between concentrations. The conclusion is that the apparent NOEC was within the range 0.07 to 1.1 mg/l. However, the lower end of this range is approximately the same as the NOEC for freshwater algae. Therefore, the S. gairdneri study is sufficient to demonstrate that fish are no more sensitive than other trophic levels and the study can be used for that purpose without needing to define a NOEC for PNEC calculation.
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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