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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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
- GLP compliance:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Duration of test (contact time):
- 28 d
- Initial conc.:
- 100 mg/L
- Based on:
- test mat.
- Reference substance:
- aniline
- Parameter:
- other: O2 consumption, TOC removal
- Value:
- 89
- Sampling time:
- 28 d
- Details on results:
- BIODEGRADATION OF BISPHENOL A AFTER 28 DAYS:
O2 consumption: 89%
TOC removal: 99%
Primary biodegradation (by HPLC): 100%
The 10 day window was met.
Based on the described results, BPA can be considered to be readily biodegradable.
Kinetic of test substance (in %):
= 0 after 0 day(s)
= 0 after 7 day(s)
= 62 ... 64 after 14 day(s)
= 75 ... 83 after 21 day(s)
= 85 ... 93 after 28 day(s)
Kinetic of control substance (in %):
= 60 after 7 day(s)
= 93 after 14 day(s) - Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Executive summary:
Bisphenol A was found to be readily biodegradable in a OECD Guideline 301F Manometric Respirometry test. After 28 days, bisphenol A was biodegraded by 85 to 93% within the 10-day window.
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
- GLP compliance:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Duration of test (contact time):
- 28 d
- Initial conc.:
- 25 mg/L
- Based on:
- test mat.
- Initial conc.:
- 7 mg/L
- Based on:
- test mat.
- Reference substance:
- benzoic acid, sodium salt
- Parameter:
- % degradation (O2 consumption)
- Remarks:
- O2 consumption, DOC removal, CO2 formation
- Value:
- >= 74.7 - <= 81.4
- Sampling time:
- 28 d
- Details on results:
- TEMPERATURE CONTROL DURING TESTS I AND II:
The temperature of Test I was maintained at 27.1 +/- 0.6 deg.C, higher than the mandated 22 deg.C, due to a faulty temperature control in the incubator.
The temperature of Test II was maintained at 22.5 +/- 0.2 deg.C throughout the test.
The results show negligible differences in the extent of O2 consumption, CO2 evolution, and DOC removal at the two temperatures.
BIODEGRADATION OF BISHPENOL A:
Time to 10% degradation:
In the reaction mixtures with BPA, the time to 10% degradation (based on O2 consumption) was reached across all BPA reaction vessels by days 5.6 to 6.1 (Test I) and days 4.7 to 5.2 (Test II).
Time to 60% degradation:
The time to 60% degradation was reached by days 9.1 to 11.1 (Test I) and by days 7.2 to 8.7 (Test II).
O2 consumption:
The extent of O2 consumption reached 73.7 to 77.6 % (Test I) and 77.1 to 92.3% (Test II) at the end of the 10-day window.
Degradation at day 28 reached 74.7 to 81.4% at day 28 (Test I) and 78.2 to 81.0% (Test II).
Theoretical CO2 evolution:
Based on theoretical CO2 evolution, degradation at day 28 reached 75.9 to 76.2% at day 28 (Test I) and 76.3 to 81.2% (Test II).
Dissolved organic carbon (DOC) removal:
Based on DOC removal, degradation at day 28 reached 79.3 to 81.2% at day 28 (Test I) and 77.1 to 93.5% (Test II).
Control performance:
The vessels with benzoate reached the 10 day window by days 2.2 to 2.5 and reached 96.8 to 98.3% degradation at day 28, indicating that the microbes were performing properly.
In the toxicity controls, BPA at the concentrations used (7 or 25 mg/L) was non-toxic to the inoculum based on the degradation of benzoate reaching 92.2 to 96.8% by day 28.
Carbon dioxide was the only degradation product measured. - Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- Bisphenol A was found to be readily biodegradable in an OECD Guideline 301F Manometric Respirometry test conducted following full Good Laboratory Practices.
- Executive summary:
Bisphenol A was found to be readily biodegradable in an OECD Guideline 301F Manometric Respirometry test conducted following full Good Laboratory Practices. In Test II conducted at 22 °C, the extent of biodegradation reached 77.1 to 92.3% (Test II) at the end of the 10-day window based on O2 consumption and 76 to 81% of theoretical CO2 formation by day 28.
Referenceopen allclose all
Description of key information
Bisphenol A is readily biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
- Type of water:
- freshwater
Additional information
Across a number of tests using international guidelines for measuring aerobic biodegradation under stringent test conditions, Bisphenol A is shown to be readily biodegradable.
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