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EC number: 201-993-5 | CAS number: 90-43-7
- 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)
- Rationale for reliability incl. deficiencies:
- other: GLP guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
- Deviations:
- yes
- Remarks:
- Concentration of test material was reduced to 0.2 and 1.0 mg/L.
- GLP compliance:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge: A sample of activated sludge mixed Iiquor was obtained from the Midland Municipal Wastewater Treatment Plant (Midland, Michigan. USA) on April 28, 1997.
- Concentration of sludge: mixed liquor suspended solids (MLSS) concentration of the activated sludge sample was determined to be 2190 ± 160 mg/L: Based on this determination, the mineral medium (3 liters) was inoculated with 41 ml of activated sludge to yield a final MLSS concentration of 30 ± 1 mg/L. - Duration of test (contact time):
- 28 d
- Initial conc.:
- 0.2 mg/L
- Based on:
- test mat.
- Initial conc.:
- 1 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- CO2 evolution
- Details on study design:
- TEST CONDITIONS
- Composition of medium: according to guideline
- Test temperature: 23 ± 1°C
- pH adjusted: yes, the pH of the inoculated mineral medium was adjusted from 7.01 to 7.37 with 5N NaOH.
TEST SYSTEM
- Culturing apparatus: 1 L flasks were sealed with rubber stoppers fitted with CO2 traps containing 4 ml of 1N NaOH.
CONTROL AND BLANK SYSTEM
- Inoculum blank: yes
- Abiotic sterile control: yes
- Toxicity control: yes
- Other: non labelled control
- Reference substance:
- benzoic acid, sodium salt
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 33.5
- St. dev.:
- 1.5
- Sampling time:
- 3 d
- Remarks on result:
- other: 0.2 mg [14C]-OPP
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 62.5
- St. dev.:
- 0.5
- Sampling time:
- 11 d
- Remarks on result:
- other: 0.2 mg [14C]-OPP
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 70.8
- St. dev.:
- 0.3
- Sampling time:
- 28 h
- Remarks on result:
- other: 0.2 mg [14C]-OPP
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 35.2
- St. dev.:
- 0.2
- Sampling time:
- 3 d
- Remarks on result:
- other: 1.0 mg [14C]-OPP
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 67.7
- St. dev.:
- 0.8
- Sampling time:
- 11 d
- Remarks on result:
- other: 1.0 mg [14C]-OPP
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 75.7
- St. dev.:
- 0.5
- Sampling time:
- 28 d
- Remarks on result:
- other: 1.0 mg [14C]-OPP
- Details on results:
- 70.8 and 75.7% biodegradation (CO2 formation as percentage of theoretical value) after 28 days at low (0.2 mg/L) and high (1.0 mg/L) concentration
- Results with reference substance:
- Kinetic of control substance: 81% after 2 days
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: GLP guideline study modified (no activated sludge used, Rhine river water used instead)
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 E (Ready biodegradability: Modified OECD Screening Test)
- Deviations:
- yes
- Remarks:
- instead of deionised water, Rhine river water was used
- GLP compliance:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- other: inoculum from Rhine river water
- Duration of test (contact time):
- 28 d
- Parameter:
- % degradation (DOC removal)
- Value:
- 100
- Sampling time:
- 6 d
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Non-GLP guideline study, some test details are missing
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- EU Method C.4-D (Determination of the "Ready" Biodegradability - Manometric Respirometry Test)
- GLP compliance:
- no
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Duration of test (contact time):
- 28 d
- Parameter:
- % degradation (O2 consumption)
- Value:
- ca. 96
- Sampling time:
- 28 d
- Details on results:
- All ten participants in a ring test reported > 60% biodegradation of 2-phenylphenol after 28 days (mean value = 96%).
- Validity criteria fulfilled:
- not specified
- Interpretation of results:
- readily biodegradable
- Endpoint:
- biodegradation in water: inherent biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Non-GLP guideline study, with some reporting deficiencies: the pH, temperature, purity of test and reference substance, batch numbers are not described.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 302 B (Inherent biodegradability: Zahn-Wellens/EMPA Test)
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: DIN 38412
- GLP compliance:
- no
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, industrial, adapted
- Initial conc.:
- 50 - 400 mg/L
- Based on:
- DOC
- Initial conc.:
- 200 - 1 000 mg/L
- Based on:
- COD
- Parameter followed for biodegradation estimation:
- DOC removal
- Parameter:
- % degradation (DOC removal)
- Value:
- 100
- Sampling time:
- 10 d
- Validity criteria fulfilled:
- not specified
- Interpretation of results:
- inherently biodegradable
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 E (Ready biodegradability: Modified OECD Screening Test)
- GLP compliance:
- not specified
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge: domestic sewage from 10 L laboratory system
- Laboratory culture: yes - Duration of test (contact time):
- 16 d
- Initial conc.:
- 20 mg/L
- Based on:
- DOC
- Initial conc.:
- 41.3 other: ml/900ml medium
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- DOC removal
- Details on study design:
- TEST CONDITIONS
- Composition of medium: according to guideline
TEST SYSTEM
- Number of culture flasks/concentration: 2
SAMPLING
- Sampling frequency: Sampling after 0 h, 1 d, 2 d, 3 d, 4 d, 8 d, 9 d, 11 d, 14 d, 15 d and 16 d
CONTROL AND BLANK SYSTEM
- Inoculum blank: 2 - Reference substance:
- aniline
- Parameter:
- % degradation (DOC removal)
- Value:
- 12
- Sampling time:
- 2 d
- Parameter:
- % degradation (DOC removal)
- Value:
- 88
- Sampling time:
- 9 d
- Parameter:
- % degradation (DOC removal)
- Value:
- 94
- Sampling time:
- 9 d
- Parameter:
- % degradation (DOC removal)
- Value:
- 100
- Sampling time:
- 14 d
- Results with reference substance:
- Kinetic of control substance (in %):
= 25 after 2 day(s)
= 100 after 9 day(s) - Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
Referenceopen allclose all
Biodegradation rates of o-phenylphenol (percentage of added radioactivity mineralized to 14CO2):
Day |
Abiotic control |
Biodegradation at different OPP concentrations |
|
1.0 mg [14C]-OPP |
0.2 mg [14C]-OPP |
1.0 mg [14C]-OPP |
|
0 |
0.0% |
0.0% |
0.0% |
3 |
0.2% |
33.5% (± 1.5) |
35.2% (± 0.2) |
11 |
0.3% |
62.5% (± 0.5) |
67.7% (± 0.8) |
28 |
0.6% |
70.8% (± 0.3) |
75.7% (± 0.5) |
Description of key information
Readily biodegradable: 70.8-75.7% (CO2 evolution) in 28 days (OECD 301B)
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
Five studies investigating the biodegradability of OPP (CAS-No. 90-43-7) are available. Ready biodegradability was tested in four studies. The key study was carried out according to OECD guideline 301 B and GLP compliance. Using domestic sludge a biodegradation of 70.8 – 75.7% after 28 days was observed (Gonsior and Tryska, 1997).
The rapid biodegradation of OPP is supported by the results of the three other biodegradation studies. These studies were performed according to OECD guideline 301 F, and EU method C.4-D, respectively. In the test conducted according to OECD guideline 301 F 100% biodegradation was reached between 6 and 9 days (Kanne, 1989). In the test following the procedures of the EU method C.4-D, 96% biodegradation after 28 days was observed (Painter, 1985).
An inherent biodegradation study, which was performed according to OECD guideline 302 B shows a DOC removal of 100% after 10 days (Wellens, 1990).
Based on the results above it can be concluded that OPP is readily biodegradable.
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