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EC number: 600-033-6 | CAS number: 1001416-18-7
- 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
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Guideline study, no deviations
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 009
- Report date:
- 2009
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
- Deviations:
- no
- GLP compliance:
- yes
Test material
- Reference substance name:
- 1-Propanone, 2-hydroxy-2-methyl-, 1-(4-C10-13-alkylphenyl) derivs.
- Cas Number:
- 1001416-18-7
- Molecular formula:
- Not applicable - UVCB
- IUPAC Name:
- 1-Propanone, 2-hydroxy-2-methyl-, 1-(4-C10-13-alkylphenyl) derivs.
Constituent 1
Sampling and analysis
- Analytical monitoring:
- no
Test solutions
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: Since the substance was hardly soluble in water test concentrations were prepared separately in Milli-RO water. Two 1 litre test bottles were filled with 250 ml of test substance mixtures with initial loading rates of 200 mg/l. These mixtures were stirred in dark glass closed bottles for 24 hours.
Subsequently, 16 ml synthetic sewage feed, 200 ml activated sludge and Milli-RO water up to 500 ml were added resulting in a loading rate of 100 mg/l. This loading rate was tested in duplicate. Optimum contact between the test substance and test medium was ensured applying continuous aeration and stirring.
Activated sludge:
Source: Municipial sewage treatment plant (Waterschap de Maaskant, The Netherlands), receiving predominantly domestic sewage.
The sludge was sieved, washed and diluted with ISO medium. A small amount of the sludge was weighed and dried overnight at ca. 105 °C to determine the amount of suspended solids (3.8 g/l of sludge, as used for the test). The pH was 7.9 at the day of the testing. The batch of sludge was used one day after collection; therefore 50 ml of synthetic sewage feed was added per litre of activated sludge at the end of the collection day. The sludge was kept aerated at test temperature until use.
Composition of ISO Medium:
CaCl2.2H2O 211.5 mg/l
MgSO4.7H2O 88.8 mg/l
NaHCO3 46.7 mg/l
KCl 4.2 mg/l
Dissolved in tap water, purified by reverse osmosis
Composition of synthetic sewage feed:
16 g peptone
11 g meat extract
3 g urea
0.7 g NaCl
0.4 g CaCl.2H2O
0.2 g MgSO4.7H2o
2.8 g K2HPO4
Dissolved in Milli-Q water, made up to one litre and filtered
- Eluate:
- Differential loading:
- Controls:
- Chemical name of vehicle (organic solvent, emulsifier or dispersant):
- Concentration of vehicle in test medium (stock solution and final test solution(s) including control(s)):
- Evidence of undissolved material (e.g. precipitate, surface film, etc):
Test organisms
- Test organisms (species):
- activated sludge of a predominantly domestic sewage
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 3 h
Test conditions
- Test temperature:
- 20.1 - 20.5 °C
- pH:
- 8.1
- Nominal and measured concentrations:
- Nominal concentrations were used
- Details on test conditions:
- TEST SYSTEM
Test vessel: Dark glass bottles, 1 litre
- Aeration: continuously during 3 h contact time
- Renewal rate of test solution: no
- No. of vessels per concentration (replicates): 2
- No. of vessels per control (replicates): 1
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Milli-RO water (tap water purified by reverse osmosis)
OTHER TEST CONDITIONS
- Adjustment of pH: no
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : After the 3 h contact time , a well mixed sample of the contents was poured into 300 ml oxygen bottle, and the flask was sealed with an oxygen electrode connected to a recorder, forcing the air out of the vessel.. Oxygen consumption was measured and recorded for approximately 10 minutes. - Reference substance (positive control):
- yes
- Remarks:
- 3,5-Dichlorophenol
Results and discussion
Effect concentrations
- Duration:
- 3 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- The substance was not toxic to waste water (activated sludge) bacteria at a loading rate of 100 mg/l (based on nominal concentrations).
- Executive summary:
The toxicity of the substance towards waste water bacteria was assessed in an assay according to OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test, 1984). Since the substance was hardly soluble in water test concentrations were prepared separately in Milli-RO water. Two 1 litre test bottles were filled with 250 ml of test substance mixtures with initial loading rates of 200 mg/L. These mixtures were stirred in dark glass closed bottles for 24 hours. Subsequently, 16 ml synthetic sewage feed, 200 ml activated sludge and Milli-RO water up to 500 ml were added resulting in a loading rate of 100 mg/L. This loading rate was tested in duplicate. Optimal contact between the test substance and test medium was ensured applying continuous aeration and stirring. Thereafter oxygen consumption was measured and recorded for approximately 10 minutes.
No significant inhibition of respiration rate of the sludge was recorded at a loading rate of 100 mg/L. The duplicate measurement confirmed the results of the first measurement. Therefore no further testing was necessary.
The EC50 of the substance exceeded a loading rate of 100 mg/L (based on nominal concentrations).
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