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Diss Factsheets
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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
Toxicity to microorganisms
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to microorganisms, other
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Neither the results nor the methods were clearly presented or explained. Concentrations greater than 320 mg/L could not be tested.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- DIN 38412-8 (Pseudomonas Zellvermehrungshemmtest)
- Deviations:
- not specified
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Vehicle:
- yes
- Test organisms (species):
- Pseudomonas putida
- Test type:
- static
- Water media type:
- not specified
- Limit test:
- no
- Total exposure duration:
- 18 h
- Details on test conditions:
- Type: other: liquid broth cultures
- Reference substance (positive control):
- no
- Key result
- Duration:
- 18 h
- Dose descriptor:
- EC10
- Effect conc.:
- > 320 mg/L
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The biodegradability of Bisphenol A in liquid broth culture to Pseudomonas putida was studied. In this study, an EC10 of >320 mg/L was reported. While this study is not the same as the activated sludge respiration test that would typically be performed to satisfy this data need, Bisphenol A is readily biodegradable and does not show high toxicity to microbial populations. The Weight of Evidence suggests that no additional studies are necessary for the assessment of microbial populations exposed to Bisphenol A.
- Executive summary:
The biodegradability of Bisphenol A in liquid broth culture to Pseudomonas putida was studied. In this study, an EC10 of >320 mg/L was reported. While this study is not the same as the activated sludge respiration test that would typically be performed to satisfy this data need, Bisphenol A is readily biodegradable and does not show high toxicity to microbial populations. The Weight of Evidence suggests that no additional studies are necessary for the assessment of microbial populations exposed to Bisphenol A.
- Endpoint:
- toxicity to microorganisms, other
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study method details are lacking.
- Principles of method if other than guideline:
- Method: 79/931/EEC, Annex V of the 6th Amendment
- GLP compliance:
- not specified
- Analytical monitoring:
- not specified
- Vehicle:
- not specified
- Test organisms (species):
- Pseudomonas fluorescens
- Test type:
- not specified
- Water media type:
- not specified
- Limit test:
- no
- Total exposure duration:
- 16 h
- Details on test conditions:
- Type: aquatic
- Reference substance (positive control):
- not specified
- Key result
- Duration:
- 16 h
- Dose descriptor:
- IC50
- Effect conc.:
- 54.5 mg/L
- Nominal / measured:
- not specified
- Conc. based on:
- not specified
- Basis for effect:
- growth inhibition
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The biodegradability of Bisphenol A was studied in a number of tests. One of them evaluated the inhibition of growth of the bacteria, Pseudomonas fluorescens. In this microbial inhibition test, the IC50 for the inhibition of growth of Pseudomonas by Bisphenol A was 54.5 mg/L.
- Executive summary:
The biodegradability of Bisphenol A was studied in a number of tests. One of them evaluated the inhibition of growth of the bacteria, Pseudomonas fluorescens. In this microbial inhibition test, the IC50 for the inhibition of growth of Pseudomonas by Bisphenol A was 54.5 mg/L. While this study is not the same as the activated sludge respiration test that would typically be performed to satisfy this data need, Bisphenol A is readily biodegradable and does not show high toxicity to microbial populations. The Weight of Evidence suggests that no additional studies are necessary for the assessment of microbial populations exposed to Bisphenol A.
Referenceopen allclose all
Nominal Test Concentrations: 0.23, 0.46, 0.93, 1.87, 3.75, 7.50, 15.00, 30.00, 60.00, 120.00, 240.00, 320.00 mg/L. The inhibition concentration was >320 mg C/L. Higher concentrations appeared to stimulate bacterial growth indicating it was an energy source. Bisphenol A had a low solubility and as a result an exact inhibitory concentration could not be determined. Researchers attempted to increase BPA concentrations by dissolving the compound in dimethyl formamide but it precipitated out again when the BPA solution was mixed with the culture medium preventing a turbidimetric determination from being made.
The IC50 of the control was 7 mg/L. The IC50 for inhibition with BPA was 54.5 mg/L.
Description of key information
Two studies are available which were rated with Klimisch 2 (reliable, with restrictions) were used in a weight-of-evidence (WoE) approach to derive PNEC STP. Fabig (1988) reported an 18 h-EC10 of > 320 mg/L (highest test concentration) with Pseudomonas putida. This study is not the same as an activated sludge respiration test according to OECD 209 but there is indication of no toxicity towards P. putida as a microorganism.
Stone and Watkinson (1983) as well is not an OECD 209 study but investigated biodegradation with a bacteria growth inhibition test with Pseudomonas fluorescens. The IC50 was reported as 54.4 mg/L.
Both studies were used in a WoE approach. The REACH guidance document R.10 specifies that studies with P. fluorescens are of limited relevance for STP as this species uses glucose as substrate. However, a growth inhibition test with P. putida may be used for PNEC STP derivation. The study of Fabig (1988) was conducted in accordance with DIN 38412-8 while the recent REACH guidance document R.10 asks for ISO-10712 (1996). Despite the fact that it is not totally certain if the DIN translated directly into the ISO the study is considered sufficiently reliable to be used in a WoE approach. Thus, the EC10 > 320 mg/L was used for PNEC derivation. This approach was also taken in the European Risk Assessment report (2010).
Key value for chemical safety assessment
- EC10 or NOEC for microorganisms:
- 320 mg/L
Additional information
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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