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Diss Factsheets
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EC number: 205-426-2 | CAS number: 140-66-9
- 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
Endpoint summary
Administrative data
Description of key information
Additional information
Melcer et al. (2007) conducted a literature review with regard to physical-chemical properties and environmental fate characteristics of alkylphenols and alkylphenol ethoxylates. The authors found that Octylphenol (OP) released to the atmosphere is likely to be degraded by photo-oxidation, with a half-life of approximately 6 hours, based on calculations using EPISuite v3.12 (U.S. Environmental Protection Agency (US EPA). (2000a) EPISuite. Estimation Program Interface (EPI) Suite Version 3.12. Washington, DC).
Photochemical transformation of Octylphenol in surface waters is also a significant route of abiotic degradation. From experiments conducted by Ahel et al. (1994) according to general accepted scientific standards, a half-life of 10-15 hours could be deduced for continuous clear sky, noon, summer sunlight conditions in the surface layer of natural waters. The photolysis rate in the deeper layers is strongly attenuated, being approximately 1.5 times slower at depths of 20-25 cm than at the surface.
Although sunlight photolysis rates of OP were found to be much slower than reported for some other alkylphenols (Faust and Hoigné, 1987, cited in Ahel et al., 1994), the results suggest that a significant portion (30 %) of these compounds could be photochemically degraded in the surface layer of natural waters within one day.
Hydrolysis is unlikely to be a dominant route of abiotic degradation for Octylphenol, because of the chemical structure and particularly the lack of susceptible functional groups.
This finding is supported by the UK Environmental Risk Assessment (ERA) Report 2005 on 4-tert-octylphenol which states that hydrolysis would not be expected in view of the chemical structure. In addition, based upon the stability of 4-tert-octylphenol during storage and lack of degradation in controls in biodegradation studies, the UK ERAR 2005 concludes that it is likely that abiotic degradation is a negligible removal process. Therefore, hydrolysis is believed to be a negligible removal process for 4-tert-octylphenol in the aquatic environment.
These findings indicate that photo-oxidation and photochemical transformation, in contrast to hydrolysis, can be important removal processes for 4-tert-Octylphenol released to water and air.
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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