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EC number: 931-341-1 | CAS number: 68955-55-5
- 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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
The LC50 (96 h) for fish is 1.26 mg AO/L, based on the lowest LC50 derived from three reliable studies available. C12-18 AO and C12-14 AO exhibit similar acute toxicity to fish.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 1.26 mg/L
Additional information
Three reliable studies are available for C12-18 amine oxide. In the key study, performed according to OECD TG 203 under GLP [Rowlands (2005)] Rainbow trout (Oncorhynchus mykiss) were exposed to C12-18 AO under semi static conditions for 96 hours. The LC50 (96 h) was 1.26 mg AO/L, based on nominal concentrations. In a supporting study [Mark & Meuwsen (1990)] performed according to OECD TG 203 under GLP,Danio reriowere exposed to C12-18 AO under semi static conditions for 96 hours. The LC50 (96 h) based on nominal concentrations of amine oxide was 1.49 mg AO/L. In the third study [Hoechst (1977)] Golden orfe were exposed to C12-18 AO for 96 hours. The LC50 (96 h) was 4.32 mg AO/L based on nominal test concentrations.
There are four reliable studies available for the C12-14 amine oxide. Iwan GR et al (1975) exposed Fathead minnow (Pimephales promelas) to C12-14 AO under static conditions for 96 hours. The LC50 (96 h) based on nominal concentrations of amine oxide ranged from 2.67 to 3.46 mg AO/L depending on the source and pH of the water used. In a supporting study Bluegill (Lepomis macrochirus) were exposed to C12-14 AO under static conditions for 96 hours. The LC50 value was reported as 3.13 mg AO/L [Macek & Sleight (1972)]. Exposure of rainbow trout (Oncorhynchus mykiss) to C12-14 AO under static conditions for 96 hours resulted in a LC50 of 12.6 mg AO/L [Dommrose AM (1987)], whilst exposure of zebra fish (Danio rerio) to C12-14 AO under static conditions resulted in a 96 -h LC50 of 3 -30 mg AO/L [Hoechst AG (1987)].
Overall, it can be concluded that C12-18 AO and C12-14 AO exhibit similar acute toxicity to fish.
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