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EC number: 203-199-4 | CAS number: 104-40-5
- 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 and sediment: simulation tests
Administrative data
- Endpoint:
- biodegradation in water and sediment: simulation tests
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Data is from peer reviewed journal
Data source
Reference
- Reference Type:
- publication
- Title:
- BIODEGRADATION OF 4-NONYLPHENOL IN SEAWATER AND SEDIMENT
- Author:
- R. Ekelund,. Granmo, K. Magnusson, M. Berggren and Bergman
- Year:
- 1 993
- Bibliographic source:
- Environmental Pollution 79 (1993) 59-61
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: refer below principle
- Principles of method if other than guideline:
- Biodegradation of 14C-labelled nonylphenol has been estimated by collection and quantification of the formed labelled carbon dioxide.
- GLP compliance:
- not specified
Test material
- Reference substance name:
- p-nonylphenol
- EC Number:
- 203-199-4
- EC Name:
- p-nonylphenol
- Cas Number:
- 104-40-5
- Molecular formula:
- C15H24O
- IUPAC Name:
- 4-nonylphenol
- Test material form:
- liquid: viscous
- Details on test material:
- - Name of test material (as cited in study report): p-nonylphenol
- Molecular formula (if other than submission substance): C15-H24-O
- Molecular weight (if other than submission substance): 220.354
- Smiles notation (if other than submission substance): c1(ccc(O)cc1)CCCCCCCCC
- InChl (if other than submission substance): 1S/C15H24O/c1-2-3-4-5-6-7-8-9-14-10-12-15(16)13-11-14/h10-13,16H,2-9H2,1H3
- Substance type: Organic
- Physical state: viscous liquid
Constituent 1
- Radiolabelling:
- yes
Study design
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- other: Sediment
- Details on source and properties of surface water:
- Details on collection (e.g. location: coastal area
sampling depth: below the halocline - Details on source and properties of sediment:
- No data available
- Details on inoculum:
- No data available
- Duration of test (contact time):
- 8 wk
Initial test substance concentrationopen allclose all
- Initial conc.:
- 1 other: liter
- Based on:
- other: seawater
- Initial conc.:
- 50 other: ml
- Based on:
- other: sediment
- Parameter followed for biodegradation estimation:
- other: Quantification of the formed labelled carbon dioxide.
- Details on study design:
- TEST CONDITIONS
- Composition of medium: 4-nonylphenol + seawater +sediment
- Additional substrate: No data available
- Solubilising agent (type and concentration if used): Acetone
- Test temperature: 1 1° ± 2°C
- pH: 3 with sulphuric acid
- pH adjusted: yes
- CEC (meq/100 g): No data available
- Aeration of dilution water: No data available
- Suspended solids concentration: No data available
- Continuous darkness: Incubation occurs in darkness
- Other:
TEST SYSTEM
- Culturing apparatus: Erlenmeyer flasks
- Number of culture flasks/concentration: 5 culture Erlenmeyer flasks
- Method used to create aerobic conditions: No data available
- Method used to create anaerobic conditions: No data available
- Measuring equipment: No data available
- Test performed in closed vessels due to significant volatility of test substance: No data available
- Test performed in open system: No data available
- Details of trap for CO2 and volatile organics if used: No data available
- Other: No data available
SAMPLING
- Sampling frequency: one
- Sampling method: No data available
- Sterility check if applicable: No data available
- Sample storage before analysis: No data available
- Other: No data available
CONTROL AND BLANK SYSTEM
- Inoculum blank: No data available
- Abiotic sterile control: No data available
- Toxicity control: No data available
- Other: No data available
STATISTICAL METHODS: No data available
Reference substance
- Reference substance:
- not specified
Results and discussion
Mean total recoveryopen allclose all
- Compartment:
- other: water, material (mass) balance
- % Recovery:
- 49
- Compartment:
- other: sediment, material (mass) balance
- % Recovery:
- 51
% Degradation
- % Degr.:
- 49
- Parameter:
- other: quantification of the formed labelled carbon dioxide
- Sampling time:
- 8 wk
- Remarks on result:
- other: other details not known
- Mineralization rate (in CO2):
- 46 other: %
- Other kinetic parameters:
- other: no data
- Transformation products:
- no
- Details on transformation products:
- From the flasks with sediment, 49% of the added activity was regained, 46% in the CO2 fraction and 3% in the organic solvent.
- Evaporation of parent compound:
- not specified
- Volatile metabolites:
- not specified
- Residues:
- not specified
Applicant's summary and conclusion
Validity criteria
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The p-nonyl-phenol (104-40-5) was found to be 49% degradated in 8 weeks as 46% in the CO2 fraction and 3% in the organic solvent present.
- Executive summary:
The biodegradation in water and sediment test were performed. 2 litres of Erlenmeyer flasks was taken and added 1 litre of seawater and 50 ml of sieved (1 mm) soft bottom sediment.
Half of the flasks containing seawater and sediment were bubbled with nitrogen gas for 15 min. An amount of 0.06 µCi14C-NP dissolved in acetone was added to each of a number of small glass plates and the solvent was evaporated at room temperature. One glass plate with14C-NP was added to each of the prepared E-flasks which were sealed and shaken vigorously. The N2-bubbled flasks were not shaken. Samples were taken after 16 weeks. Four replicates of each kind, and the14CO2formed, was collected and estimated. For this purpose the contents in the flasks were acidified to pH 3 with sulphuric acid, 1 ml of cod liver oil was added to prevent NP from evaporating and a jar containing 10 ml of 5 M KOH. The jar with KOH was then taken out and it was provided with a piece of ice and a smaller jar containing 2 ml of concentrated H2SO4.The KOH jar was placed in a bigger glass jar together with a scintillation vial 4 ml of Carbosorb. The glass jar was closed air-tight and shaken at 10°C for 4 h. To determine the recovery of ,14CO2, about 0.004 µCi of14C-carbonate were added. The exchange of14CO2was also determined from E-flasks which had been incubated for 8 weeks at +11°C in darkness after the addition of14C-carbonate.
The degradation rate in the presence of sediment and oxygen was high from the beginning and was half as rapid at very low concentrations of oxygen. The higher rate in the presence of sediment is due probably to the larger number of microorganisms, which increases the probability that bacterial cells able to degrade NP are present.
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