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Diss Factsheets
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EC number: 284-325-5 | CAS number: 84852-15-3
- 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
Hydrolysis
Administrative data
Link to relevant study record(s)
Description of key information
In accordance with REACH Annex XI, there is sufficient weight of evidence from several independent sources of information leading to the conclusion that hydrolysis is not an important abiotic degradation pathway for 4-nonylphenol. Therefore, hydrolysis testing for 4-nonylphenol is not scientifically necessary.
Key value for chemical safety assessment
Additional information
As stated in the ECHA Guidance Document R.7B, p. 233, hydrolysis is not an important fate process for petroleum substances since hydrocarbons do not undergo reaction with water. 4-nonylphenol is also a substance among the hydrocarbons consisting of an alkylchain with nine C atoms attached to a phenolring. This means that also for 4-nonylphenol, branched, it can be assumed that hydrolysis is not a dominant route of abiotic degradation.
This assumption is in accordance with Melcer et al., 2007 (p. 11). This study did not expect hydrolysis to be important for alkylphenols because of their chemical structures and the lack of functional groups susceptible to hydrolytic attack.
This assumption is also supported by the EU Risk Assessment Report 2002 (p.54) which states that hydrolysis is a negligible removal processes for nonylphenol in the aquatic environment. This assumption is based upon the stability of nonylphenol during storage and several biodegradation studies reviewed by the UK rapporteur on behalf of the European Union where no degradation was observed in the control experiments. The authors of these studies concluded that abiotic degradation was likely to be negligible (Corti et al., 1995; Trocmé et al., 1988; both cited in the EU Risk Assessment Report 2002).
According to Corti et al., 1995, who observed biodegradation of 4-(1-nonyl)phenol by cultures of a Candida maltosa strain isolated from aerobic sludge samples, no significant abiotic degradation was observed in uninoculated sterile controls. Trocmé et al., 1988, were able to demonstrate that 4-nonylphenol is degraded microbiologically after induction of the microorganisms in an incubation experiment with a reconstituted soil system (compost + sandstone). 4-nonylphenol was more persistent under semi-sterile conditions, with 100 % residual 4-nonylphenol after 15 days, than in the non-sterilized treatment, where only 51 % of the initial concentration was present after 15 days. Trocmé showed that the disappearance of 4-nonylphenol was limited to biodegradation and residue binding.
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