Registration Dossier
Registration Dossier
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 904-653-0 | CAS number: -
- 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
The reaction mass of phenol and 4,4'-isopropylidenediphenol (BPA) contains phenol and BPA. Phenol did not cause skin sensitisation in a modified Buehler test and in a mouse ear swelling test. Sensitisation studies on BPA led to mainly negative results, but as BPA has been assigned an official classification as Skin Sens. 1 according to Annex VI of Regulation (EC) No 1272/2008
Key value for chemical safety assessment
Skin sensitisation
Link to relevant study records
- Endpoint:
- skin sensitisation, other
- Remarks:
- LLNA, non-LLNA
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH
1. HYPOTHESIS FOR THE ANALOGUE APPROACH
This read-across is based on the hypothesis that the properties of the target substance Reaction mass of phenol and 4,4’-isopropylidenediphenol can be predicted by studies conducted with the source substances phenol, 4,4’-isopropylidenediphenol (BPA), and 2-acetone, polymer with phenol, because the target substance Reaction mass of phenol and 4,4’-isopropylidenediphenol contains phenol (40-45%, typical concentration ca. 40%) and 4,4’-isopropylidenediphenol (BPA) (20-40%, typical concentration ca. 33%) as main constituents. Both constituents are data rich substances with distinct hazard properties, so that mainly data on the constituents have been applied to characterize the Reaction mass of phenol and 4,4’-isopropylidenediphenol. Since this is a common approach in mixture hazard assessment, is reasonable to apply it also to multi-constituent substances.
Additionally, some data from a structurally related substance (2-acetone, polymer with phenol) containing the same constituents/impurities at different concentrations are available, which are applied to characterize the environmental fate and ecotoxicity of the impurities present in the Reaction mass of phenol and 4,4’-isopropylidenediphenol.
This read-across hypothesis corresponds to scenario 2 - different compounds have qualitatively and quantitatively the same type of effects - of the read-across assessment framework i.e. properties of the target substance Reaction mass of phenol and 4,4’-isopropylidenediphenol are predicted to be similar to those of the source substances phenol, 4,4’-isopropylidenediphenol (BPA), and 2-acetone, polymer with phenol.
Therefore, read-across from the available studies with the source substances is considered as an appropriate adaptation to the standard information requirements of the REACH Regulation for the target substance Reaction mass of phenol and 4,4’-isopropylidenediphenol, in accordance with the provisions of Annex XI, 1.5 of the REACH Regulation.
2. SOURCE AND TARGET CHEMICAL(S) (INCLUDING INFORMATION ON PURITY AND IMPURITIES)
please refer to justification for read-across attached to Iuclid section 13
3. ANALOGUE APPROACH JUSTIFICATION
please refer to justification for read-across attached to Iuclid section 13
4. DATA MATRIX
please refer to justification for read-across attached to Iuclid section 13 - Reason / purpose for cross-reference:
- read-across: supporting information
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Reading:
- 1st reading
- Group:
- test chemical
- Remarks on result:
- no indication of skin sensitisation
- Remarks:
- Phenol
- Parameter:
- EC3
- Test group / Remarks:
- BPA
- Remarks on result:
- other: not sensitising in LLNA and photoreactive LLNA; however, harmonised classification as Skin Sens 1
- Interpretation of results:
- Category 1 (skin sensitising) based on GHS criteria
- Conclusions:
- No experimental data are available for the target substance Reaction mass of phenol and 4,4’-isopropylidenediphenol. However, based on the general principles of mixture toxicology, data on the main constituents of this multi-constituent substance are used as surrogate. Due to the legal classification of BPA as Skin Sens 1 the target substance Reaction mass of phenol and 4,4’-isopropylidenediphenol is classified as skin sensitiser (Cat 1).
Reference
Endpoint conclusion
- Additional information:
No experimental data are available for the target substance Reaction mass of phenol and 4,4’-isopropylidenediphenol. However, based on the general principles of mixture toxicology, data on the main constituents of this multi-constituent substance are used as surrogate. A justification for read-across is attached to Iuclid section 13.
Data on PHENOL:
In the EU-RAR on phenol (2006; Section 4.1.2.5, page 88) it was concluded that phenol did not cause any signs of skin sensitisation in the tests conducted.
In a modified Buehler test in guinea pigs (Itoh, 1982) no skin sensitization was detected after repeated dermal exposure to phenol. In accord, the results in a mouse ear swelling test suggested no sensitizing properties of phenol (Descotes, 1988).
Data on BPA:
The 2003 EU RAR on BPA concluded that based on the findings from the most robust animal study, BPA may possess a skin sensitisation potential, albeit a limited one, and that the available data suggest that BPA is considered capable of producing skin sensitisation responses in humans.
The 2008 updated EU RAR concluded: "Overall the new information does not confirm the previously reported evidence of a skin sensitisation potential of BPA. While the data do not exclude a skin sensitising activity of BPA at high concentrations (>30%), there is no evidence that this is a concern for workers in current BPA manufacturing plants (such workers are believed to represent the group most likely to be exposed to BPA in dust)."
There is no significant new information on the skin sensitisation of BPA that was not discussed in the 2003 or 2008 EU RARs.
Respiratory sensitisation
Endpoint conclusion
- Endpoint conclusion:
- no study available
- Additional information:
The 2003 EU RAR concluded that there are no data from which to evaluate the potential of BPA to be a respiratory sensitiser.
The 2008 updated EU RAR concluded the same, but added: "However, based on the lack of reports of cases of respiratory sensitisation, there are no grounds for concern for this endpoint."
There is no significant new information on the respiratory sensitisation of BPA that was not discussed in the 2003 or 2008 EU RARs.
Justification for classification or non-classification
The reaction mass is classified as Skin Sens 1 according to CLP based on its content in BPA, which is, despite the contrary conclusion of the EU RAR, classified Skin Sens. 1 according to Annex VI of Regulation (EC) No 1272/2008.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
