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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
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- Additional physico-chemical information
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- Nanomaterial aspect ratio / shape
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- Nanomaterial pour density
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- Endpoint summary
- Stability
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- Environmental data
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- 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
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- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
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- Toxicological Summary
- Toxicokinetics, metabolism and distribution
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- Additional toxicological data

Phototransformation in water
Administrative data
Link to relevant study record(s)
- Endpoint:
- phototransformation in water
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Study type:
- other: direct and indirect photolysis
- Principles of method if other than guideline:
- Measurement of direct and indirect photolysis in the presence of dissolved organic matter
- GLP compliance:
- not specified
- Radiolabelling:
- no
- Light source:
- other: Suntest CPS+ solar simulator (Atlas Devices)
- DT50:
- 22 h
- Test condition:
- River fulvic acids
- DT50:
- 17.4 h
- Test condition:
- Lake fulvic acids
- DT50:
- 32.2 h
- Test condition:
- Artificial wetlands
- DT50:
- 235 h
- Test condition:
- Control in deionised water
- Transformation products:
- not measured
- Conclusions:
- Bisphenol A has a half-life of 235 h for direct photolysis and 17.4 to 32.2 h for indirect photolysis.
- Executive summary:
Bisphenol A has a half-life of 235 h for direct photolysis and 17.4 to 32.2 h for indirect photolysis.
Reference
DIRECT PHOTOLYSIS:
Some loss of bisphenol A was reported in the controls (Milli-Q water, no DOM) held under light. A pseudo-first order rate constant of 8.07E-7 / sec was calculated. This yields a half-life of 235 hours or 9.8 days.
INDIRECT PHOTOLYSIS:
Observed rate constants (Kobs) and half-lives (t1/2):
River fulvic acids: Kobs = 86.2 E-7 /sec; t1/2 = 22.0 hours
Lake fulvic acids: Kobs = 111 E-7 /sec; t1/2 = 17.4 hours
Artificial wetlands: Kobs = 59.8 E-7 /sec; t1/2 = 32.2 hours
CONCLUSION:
Bisphenol A degradation in the presence of dissolved organic matter (DOM) under natural sunlight may result in photo-degradation rate coefficients that are significantly higher than, or at least on the order of, those reported for biodegradation. Depending upon the latitude of the water body, the season, and the DOM levels present in the water body, this translates into half-lives on the order of or faster than degradation by microorganisms.
Description of key information
Bisphenol A has a half-life of 0.5 to 10 days for direct photolysis and 0.7 to 1.3 days for indirect photolysis.
Key value for chemical safety assessment
- Half-life in water:
- 0.5 d
Additional information
Bisphenol A may undergo both direct and indirect photolysis in water. Direct photolysis half-lives of 0.5 to 10 days have been reported from laboratory experiments. Indirect photolysis (in the presence of various dissolved organic matter) half-lives of about 0.7 to 1.3 days have been reported from laboratory experiments.
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