Registration Dossier
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EC number: 201-245-8 | CAS number: 80-05-7 Bisphenol A; BPA
- 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
- 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
Key value for chemical safety assessment
Genetic toxicity in vitro
Description of key information
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (negative)
Additional information
The 2003 EU RAR concluded:
"No human data regarding mutagenicity are available. However, Bisphenol A appears to have demonstrated aneugenic potential in vitro, positive results being observed without metabolic activation in a micronucleus test in Chinese hamster V79 cells and in a non-conventional aneuploidy assay in cultured Syrian hamster embryo cells. Additionally, in cell-free and cellular systems there is information that shows Bisphenol A disrupts microtubule formation. Bisphenol A has been shown to produce adduct spots in a post-labelling assay with isolated DNA and a peroxidase activation system, but it does not appear to produce either gene mutations or structural chromosome aberrations in bacteria, fungi or mammalian cells in vitro. However, some deficiencies in the conduct of these studies have been noted and the negative results cannot be taken as entirely conclusive. Bisphenol A does not appear to be aneugenic in vivo, since a recently conducted, standard mouse bone marrow micronucleus test has given a negative result. Bisphenol A was negative in a briefly reported dominant lethal study in rats but, given the limited details provided, this is not regarded as an adequate negative result. The only other data in somatic cells in vivo are from a 32P-postlabelling assay, which showed that Bisphenol A is capable of producing DNA adduct spots in rat liver following oral administration. These adduct spots were not characterised fully.
Considering all of the available genotoxicity data, and the absence of significant tumour findings in animal carcinogenicity studies (see below), it does not appear that Bisphenol A has significant mutagenic potential in vivo. Any aneugenic potential of Bisphenol A seems to be limited to in vitro test systems and is not of concern. The relevance of the finding that Bisphenol A can produce rat hepatic DNA adduct spots in a postlabelling assay is not entirely clear. However, given the absence of positive results for gene mutation and clastogenicity in cultured mammalian cell tests, it seems unlikely that these are of concern for human health."
The 2008 updated EU RAR concluded:
"New data from a study indicating effects of Bisphenol A on meiosis in female mice cannot be taken as conclusive evidence of an effect of Bisphenol A on germ cell meiosis because of the several methodological weaknesses and flaws identified in the study, the reporting inadequacies, and the known mutagenicity and toxicity profile of Bisphenol A. In addition, these findings have not been confirmed in more recent publications. Thus, the original conclusion that Bisphenol A has no significant mutagenic potential in vivo is still valid."
Additional recent information concerning the observations reported discussed in the 2008 updated EU RAR was discussed in the initial dossier submitted in 2010:
Two in vivo studies (Hunt et al.(2003) and Susiarjo et al. (2007)) evaluated during the 2008 EU RAR reported that short-term oral exposure to low doses of Bisphenol A (≥ 0.020 mg/kg bw/day) in peripubertal or pregnant mice can interfere with meiotic divisions in development of female germ cells (“egg” or “oocyte”). An increase in hyperploid (aneuploid) metaphase II oocytes was observed following treatment with 0.020 mg/kg bw/day. There was not a significant increase in aneuploid embryos.
Two subsequent in vivo studies (Pacchierotti et al.(2008), Eichenlaub-Ritter et al. (2008)) attempted to replicate these findings. Consistent with the previous findings, they detected no significant effects of Bisphenol A exposure on the frequency of aneuploidy in “zygotes” (fertilised oocytes) produced from female mice treated before puberty or as adults with a similar range of doses. In addition, Eichenlaub-Ritter et al. (2008) found no effects of Bisphenol A exposure on aneuploid oocytes and Pacchierotti et al. (2008) found no increase in aneuploid or diploid sperm following exposure of male mice to Bisphenol A. The authors concluded that the aneuploidy predicted by the Hunt group could not be confirmed.
In addition, in a recent study published by the Hunt group, Muhlhauser et al. (2009), the authors could not replicate their initial findings on “congression failure” but report effects on chromosome alignment and/or spindle formation. The authors state “After publishing our findings [Hunt et al., 2003], we initiated studies to assess the effect of long term Bisphenol A exposure on the growing follicle. To our surprise, levels of Bisphenol A that were sufficient to elicit an effect on meiotic chromosome dynamics during the previous two years of study suddenly produced little or no effect. In an analysis of possible changes in experimental protocol, the only change identified was the lot of animal feed.” The authors report frequencies of abnormal oocytes in the absence and presence of Bisphenol A in two different diets (casein based and soy based). The reported frequencies of abnormal oocytes of the Bisphenol A/casein group are lower than the background value reported in the soy-based diet.
Overall, the initial observations reported by the Hunt laboratory were not reproduced in the same laboratory or in other independent laboratories. Therefore, the conclusion from the 2003 EU RAR and the 2008 EU RAR Update is still valid; Bisphenol A has no significant mutagenic potential in vivo.
SCOEL Recommendation 2014 concluded on genotoxicity:
“Considering all of the available genotoxicity data and the absence of significant tumour findings in animal carcinogenicity studies (see Section 3.8), it does not appear that Bisphenol A has significant mutagenic or genotoxic potential in vivo.”
EFSA Opinion 2015 concluded on gentoxicity:
“The available data support that Bisphenol A is not mutagenic (in bacteria or mammalian cells), or clastogenic (micronuclei and chromosomal aberrations). The potential of Bisphenol A to produce aneuploidy in vitro was not expressed in vivo. The positive finding in the postlabelling assays in vitro and in vivo is unlikely to be of concern, given the lack of mutagenicity and clastogenicity of Bisphenol A in vitro and in vivo.
Using a WoE approach, the CEF Panel assigned a likelihood level of “unlikely” to Bisphenol A genotoxicity.”
Justification for classification or non-classification
Bisphenol A is included in Annex VI of Regulation (EC) No 1272/2008. No classification regarding genetic toxicity is 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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