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Diss Factsheets
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EC number: 271-212-0 | CAS number: 68526-55-6
- 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
Sediment toxicity
Administrative data
Link to relevant study record(s)
Description of key information
In the absence of experimental data the Equilibrium Partitioning Method has been used to derive a sediment PNEC on the basis of the aquatic data when appropriate.
Key value for chemical safety assessment
Additional information
Sediment toxicity data was only available for a few category members. All the studies identified reported on the acute toxicity to sediment organisms, and so do not fulfil the REACH information requirement for chronic toxicity data nor provide sufficient data to derive sediment PNEC.
Three studies on the toxicity of tetradec-1 -ene were identified (Roddie, 1997; Dorn and Wong, 2002; Harris, 2003). These studies report 10 day LC50 for the sediment organisms Corophium volutator and Leptocheirus plumulosis in the range 86.95 -2004 mg/kg. Two studies on the toxicity of hexadec-1 -ene were identified (Dorn and Wong, 2002; Roddie, 1997). These studies report 10 day LC50 for the sediment organisms Corophium volutator and Leptocheirus plumulosis in the range 706 - 4780 mg/kg. Two studies on the toxicity of alkenes C15 - 18 were identified (Daniel et al, 2006; Whale, 1995). These studies report 10 day LC50 for the sediment organisms Corophium volutator and Leptocheirus plumulosis in the range 357 - >1000 mg/kg. Four studies on the toxicity of alkenes C16 - 18 were identified (Jewell et al., 2005; Daniel et al., 2006;Roddie, 1999; Jewell et al., 2004). These studies report 10 day LC50s for the sediment organisms Corophium volutator and Leptocheirus plumulosis in the range 182 - 3773 mg/kg dry weight. The studies used a variety of natural and artificial sediments, but none included analytical monitoring to confirm the exposure concentrations. Due to this, these studies should be considered as indicative of the concentrations of these test items that may cause acute sediment toxicity.
In the absence of experimental data the Equilibrium Partitioning Method has been used to derive a sediment PNEC on the basis of the aquatic data when appropriate. Using this PNEC the chemical safety assessment according to Annex I has not indicated a need to investigate further the effects of the substance and/or degradation products on sediment organisms and therefore new sediment testing is not required. For category members where a sediment PNEC could not be derived using the Equilibrium Partitioning Method due to a lack of aquatic toxicity the chemical safety assessment according to Annex I has also not indicated a need to investigate further the effects of the substance and/or degradation products on sediment organisms and therefore new testing is not required.
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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