Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
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: 201-245-8 | CAS number: 80-05-7
- 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
Genetic toxicity: in vitro
Administrative data
- Endpoint:
- in vitro cytogenicity / chromosome aberration study in mammalian cells
- Remarks:
- Type of genotoxicity: chromosome aberration; DNA damage
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Acceptable, well-documented study which meets basic scientific principles.
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 989
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Chinese hamster ovary (CHO-WBL) cells were used for detection of sister chromatid exchanges (SCEs) and chromosome aberrations (CAs). Bisphenol A was tested in each assay with and without exogenous metabolic activation.
For the SCE trials without metabolic activation, cells were exposed to Bisphenol A (0, 0.6, 2.4, 8.0, 15, 20, 25, 30, 40, or 50 µg/mL) for approximately 25 hours; for the trails with metabolic activation, exposure was for two hours. For both testing conditions, BrdU was added two hours after dosing and Colcemid was added during the last 2 to 2.5 hours of incubation. Mitotic cells were fixed on slides, stained with Hoechst 33258, and examined for SCEs by fluorescence microscopy.
In the CA assay without metabolic activation, cells were exposed to Bisphenol A (0, 20, 30, 40, or 50 µg/mL) for eight hours, then cells were washed and treated with Colcemid for 2 to 2.5 hours. With metabolic activation, the cells were exposed to Bisphenol A and the metabolic activation mixture for two hours, washed, incubated for eight hours, then treated with Colcemid for 2 to 2.5 hours. Cells were harvested, fixed on slides, and stained with Giemsa for analysis and classification of CAs. - GLP compliance:
- no
- Type of assay:
- other: in vitro mammalian chromosome aberration test; sister chromatid exchange assay in mammalian cells
Test material
- Reference substance name:
- 4,4'-isopropylidenediphenol
- EC Number:
- 201-245-8
- EC Name:
- 4,4'-isopropylidenediphenol
- Cas Number:
- 80-05-7
- Molecular formula:
- C15H16O2
- IUPAC Name:
- 4-[2-(4-hydroxyphenyl)propan-2-yl]phenol
- Details on test material:
- - purity: ≥97 %
Constituent 1
Method
Species / strain
- Species / strain / cell type:
- Chinese hamster Ovary (CHO)
- Additional strain / cell type characteristics:
- not applicable
- Metabolic activation:
- with and without
- Metabolic activation system:
- 15 µL/mL S9 (obtained from livers of Aroclor 1254-treated male Sprague Dawley rats), 1.5 mg/mL NADP, and 2.7 mg/mL isocitric acid in serum-free medium
- Test concentrations with justification for top dose:
- For SCE assay: 0, 0.6, 2.4, 8.0, 15, 20, 25, 30, 40, or 50 µg/mL
For CA assay: 0, 20, 30, 40, or 50 µg/mL - Vehicle / solvent:
- DMSO
Controls
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- Remarks:
- DMSO solvent
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: Mitomycin C for assays without metabolic activation; cyclophosphamide for assays with metabolic activation
- Details on test system and experimental conditions:
- If a treatment resulted in a delay of the cell cycle progression, a later harvest was performed in an attempt to collect a sufficient number of metaphase II cells for scoring. In these cases, the reincubated cells were harvested after an additional 6 to 8 hour incubation for the SCE assay and the cell growth period was extended to about 20 hours for the CA assay.
- Evaluation criteria:
- For the SCE assay, 50 cells were scored per dose in the initial trial, and 25 were scored in the repeat trials.
For the CA assay, 100 to 200 cells from each of the three highest scorable doses were analyzed. All aberrations were individually classified (e.g., chromatid breaks, triradials, etc., as described by Galloway et al. [1985, 1987]); however, these data were combined as the percent of cells with simple (deletions), complex (exchanges), and total (simple, complex, and other) aberrations. Only the total percent cells with aberrations was considered in the statistical evaluation. Gaps and endoreduplications were recorded but were not included in the statistical analyses. - Statistics:
- In the SCE assay, an increase of 20% or greater in SCEs per chromosome over the solvent control was considered significant. A significant increase in the CA assay was based on a binomial sampling assumption; the P values were adjusted according to Dunnett's method to take into account multiple dose comparisons. The trend test for both assays used a linear regression analysis: SCEs per chromosome vs. the log dose, and the percentage of cells with aberrations vs. the log dose.
Results and discussion
Test results
- Species / strain:
- Chinese hamster Ovary (CHO)
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- BPA, at 8 ug/mL, produced a small increase (22%) in the first SCE trial without metabolic activation. Cell cycle delay was observed at this dose, and this response was not observed in the second trial, even though higher doses (15 to 30 ug/mL) were analyzed. The trial with metabolic activation did not induce SCEs when tested up to toxic levels of BPA, and it was concluded that BPA does not induce SCE.
In the CA trial without metabolic activation, BPA did not induce CAs when tested with delayed harvest and up to toxic levels. In the first CA trial with metabolic activation, a positive response was observed at 50 ug/mL, a dose where cell confluence was reduced by approximately 70%. This response did not repeat in the second trial, and it was concluded that BPA was negative in the CA assay. - Remarks on result:
- other: strain/cell type: CHO-WBL
- Remarks:
- Migrated from field 'Test system'.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information):
negative
The authors concluded that BPA does not induce SCEs or CAs in CHO cells. - Executive summary:
Chinese hamster ovary (CHO-WBL) cells were used for detection of sister chromatid exchanges (SCEs) and chromosome aberrations (CAs). Bisphenol A was tested in each assay with and without exogenous metabolic activation. For the SCE trials without metabolic activation, cells were exposed to Bisphenol A (0, 0.6, 2.4, 8.0, 15, 20, 25, 30, 40, or 50 µg/mL) for approximately 25 hours; for the trails with metabolic activation, exposure was for two hours. For both testing conditions, BrdU was added two hours after dosing and Colcemid was added during the last 2 to 2.5 hours of incubation. Mitotic cells were fixed on slides, stained with Hoechst 33258, and examined for SCEs by fluorescence microscopy. Bisphenol A, at 8 µg/mL, produced a small increase (22%) in the first SCE trial without metabolic activation. Cell cycle delay was observed at this dose, and this response was not observed in the second trial, even though higher doses (15 to 30 µg/mL) were analyzed. The trial with metabolic activation did not induce SCEs when tested up to toxic levels of BPA, and it was concluded that BPA does not induce SCE.
In the CA assay without metabolic activation, cells were exposed to Bisphenol A (0, 20, 30, 40, or 50 ug/mL) for eight hours, then cells were washed and treated with Colcemid for 2 to 2.5 hours. With metabolic activation, the cells were exposed to Bisphenol A and the metabolic activation mixture for two hours, washed, incubated for eight hours, then treated with Colcemid for 2 to 2.5 hours. Cells were harvested, fixed on slides, and stained with Giemsa for analysis and classification of CAs. In the CA trial without metabolic activation, Bisphenol A did not induce CAs when tested with delayed harvest and up to toxic levels. In the first CA trial with metabolic activation, a positive response was observed at 50 ug/mL, a dose where cell confluence was reduced by approximately 70%. This response did not repeat in the second trial, and it was concluded that Bisphenol A was negative in the CA assay.
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.