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EC number: 470-180-7 | CAS number: 61196-40-5
- 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
Toxicity to microorganisms
Administrative data
Link to relevant study record(s)
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2004-12-13 to 2005-02-07
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
- Version / remarks:
- 1984
- Deviations:
- no
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- EU Method C.11 (Biodegradation: Activated Sludge Respiration Inhibition Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- Due to the low solubility of the test item in test water, adequate amounts of the test item were directly weighed into each test flask.
- Test organisms (species):
- anaerobic bacteria from a domestic water treatment plant
- Details on inoculum:
- The sludge was washed by centrifugation and the supernatant liquid phase was decanted. The solid material was resuspended in tap water and again centrifuged. The latter procedure was repeated twice. An aliquot of washed sludge suspension was made up with tap water. To this mixture, 50 mL synthetic sewage feed per litre was added daily, starting one day prior to use, and the sludge was kept at room temperature under continuous aeration until use. Immediately before use, an aliquot of the final sludge suspension was weighed, dried and the ratio of wet sludge (g) to its dry weight (g) determined. Based on this ratio, calculated aliquots of washed sludge suspension, corresponding to 2.5 g dry material per litre, were made up with tap water.
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 3 h
- Test temperature:
- 19-20 °C
- pH:
- 7.4
- Dissolved oxygen:
- 8.7 - 2.3 mg/L
- Nominal and measured concentrations:
- nominal 10, 32, 100, 320 and 1000 mg/L
- Details on test conditions:
- The test was performed in 500 mL glass flasks.
For the measurement of the respiration rate a well-mixed sample of each test medium was poured into a Karlsruher flask after exactly 3 hours incubation time, and was not further aerated. The oxygen concentration was measured with an oxygen electrode, and was recorded for about ten minutes. During measurement, the samples were continuously stirred on a magnetic stirrer. The oxygen consumption (in mg oxygen / L / minute) was determined from the most linear part of the respiration curve, and were determined in the range between approximately 8.7 - 2.3 mg oxygen / L.
The pH and the oxygen concentrations were determined at the start and at the end of the incubation period in all treatments. The water temperature was measured in one control medium at the start and the end of the incubation period. - Reference substance (positive control):
- yes
- Remarks:
- 3,5-Dichlorophenol
- Key result
- Duration:
- 3 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Results with reference substance (positive control):
- The 3-hour EC50 of 3,5-Dichlorophenol was calculated to be 7.1 mg/L.
Based on the results of the reference substance the test is considered valid. - Validity criteria fulfilled:
- yes
- Conclusions:
- The test item is not toxic to activated sludge under the conditions of this test.
- Executive summary:
The purpose of the 3-hour toxicity test was to evaluate the influence of the test item on the activity of activated sludge by measuring the respiration rate under defined conditions and according to OECD TG 209. The respiration rate (oxygen consumption) of an aerobic activated sludge fed with a standard amount of synthetic sewage was measured in the presence of various concentrations of the test item after an incubation period of 3 hours. The inhibitory effect of the test item at the particular concentrations was expressed as percentage of the mean respiration rate of two controls. The respiration rates of the test item treated activated sludge was in the range of control and slightly inhibited. For the test concentrations of 10 mg/L, 32 mg/L and 100 mg/L, the maximum difference from control was 12.6 %. For the test concentrations of 320 mg/L and 1000 mg/L the differences were 1.1 % and 21.8 %, respectively. Test item concentrations exceeding 1000 mg/L were not tested. The 3-hour EC50 was determined to be greater than 1000 mg/L by Probit analysis using the inhibition rates of the 1000, 320, 100, 32 and 10 mg/L test concentrations.
In conclusion, the test item is not toxic to activated sludge under the conditions of this test.
Reference
Description of key information
Toxicity to microorganisms was assessed in an OECD TG 209 compliant study and EC50 was greater than 1000 mg/L (reference 6.1.7-1).
Key value for chemical safety assessment
- EC10 or NOEC for microorganisms:
- 1 000 mg/L
Additional information
Toxicity to microorganisms
The purpose of the 3-hour toxicity test was
to evaluate the influence of the test item on the activity of activated
sludge by measuring the respiration rate under defined conditions and
according to OECD TG 209. The respiration rate (oxygen consumption) of
an aerobic activated sludge fed with a standard amount of synthetic
sewage was measured in the presence of various concentrations of the
test item after an incubation period of 3 hours. The inhibitory effect
of the test item at the particular concentrations was expressed as
percentage of the mean respiration rate of two controls. The respiration
rates of the test item treated activated sludge was in the range of
control and slightly inhibited. For the test concentrations of 10 mg/L,
32 mg/L and 100 mg/L, the maximum difference from control was 12.6 %.
For the test concentrations of 320 mg/L and 1000 mg/L the differences
were 1.1 % and 21.8 %, respectively. Test item concentrations exceeding
1000 mg/L were not tested. The 3-hour EC50 was determined to be greater
than 1000 mg/L by Probit analysis using the inhibition rates of the
1000, 320, 100, 32 and 10 mg/L test concentrations.
In conclusion, the test item is not toxic to activated sludge under the conditions of this test.
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