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EC number: - | CAS number: -
- 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:
- April 2013 - July 2013
- 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
- Deviations:
- yes
- Remarks:
- See below.
- Principles of method if other than guideline:
- The dissolved oxygen content was not above 60% to 70% of the dissolved oxygen saturation level of 8.9 mgO2/L in several of the vessels.
This deviation was considered to have had no adverse effect on the study as all oxygen consumption values were measured over the linear portion of the traces. - GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- no
- Vehicle:
- no
- Test organisms (species):
- activated sludge of a predominantly domestic sewage
- Details on inoculum:
- - Preparation of inoculum for exposure:
The activated sewage sludge sample was maintained on continuous aeration in the laboratory at a temperature of approximately 21 ºC overnight prior to use in the test. On the day of collection the activated sewage sludge (10 liters) was fed synthetic sewage sludge (500 mL). The pH of the sample on the day of the test was 7.8 measured using a WTW pH/Oxi 340I pH and dissolved oxygen meter. Determination of the suspended solids level of the activated sewage sludge was carried out by filtering a sample (100 mL) of the activated sewage sludge by suction through a pre-weighed GF/A filter paper using a Buchner funnel which was then rinsed 3 times with 10 mL of deionized reverse osmosis water and filtration continued for 3 minutes. The filter paper was then dried in an oven at approximately 105 ºC for at least one hour and allowed to cool before weighing. This process was repeated until a constant weight was attained. The suspended solids concentration was equal to 2.9 g/L prior to use. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 3 h
- Test temperature:
- 20 ± 2 ºC
- pH:
- between 7.0 and 8.0
- Dissolved oxygen:
- 4.6 to 6.9 mg O2/L
- Nominal and measured concentrations:
- Nominal test concentrations of 100 and 1000 mg/L
- Details on test conditions:
- TEST SYSTEM- Test vessel: closed- Aeration: The mixture was aerated with clean, oil-free compressed air via narrow bore glass tubes at a rate of approximately 0.5 - 1 liter per minute.
OTHER TEST CONDITIONS- Adjustment of pH: The pH of this stock solution was measured to be pH 5.2 and was adjusted to pH 7.2 using 1.0 M NaOH.
- Photoperiod: All test vessels were shielded from the light during mixing.
TEST CONCENTRATIONS- Range finding study- Test concentrations: 100 and 1000 mg/L- Results used to determine the conditions for the definitive study: No statistically significant toxic effects were shown at 100 and 1000 mg/L. Therefore, it was considered justifiable not to perform a definitive test. - Reference substance (positive control):
- yes
- Remarks:
- A reference item, 3,5-dichlorophenol, was tested at concentrations of 3.2, 10 and 32 mg/L in order to confirm the suitability of the inoculum.
- 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
- Duration:
- 3 h
- Dose descriptor:
- NOEC
- Effect conc.:
- > 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Details on results:
- The dissolved oxygen concentrations after 30 minutes contact time in several of the vessels was below 60% of the dissolved oxygen saturation level of 8.9 mg O2/L. This deviation to the study plan was considered to have had no adverse effect on the study given that all oxygen consumption values were measured/calculated over the linear portion of the traces.
No statistically significant toxic effects were shown at 100 and 1000 mg/L. Therefore, it was considered justifiable not to perform a definitive test.
It was considered unnecessary and unrealistic to test at concentrations in excess of 1000 mg/L. - Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- Relevant effect levels: The reference item gave a 3-Hour EC50 value of 11 mg/L. - Reported statistics and error estimates:
- One way analysis of variance incorporating Bartlett's test for homogeneity of variance (Sokal and Rohlf, 1981) and Dunnett's multiple comparison procedure for comparing several treatments with a control (Dunnett, 1955) was carried out on the oxygen consumption data for the rangefinding test after 3 hours for the control and all test concentrations to determine any statistically significant differences between the test and control groups. All statistical analyses were performed using the SAS computer software package (SAS, 1999 - 2001).
No statistically significant toxic effects were shown at 100 and 1000 mg/L. Therefore, it was considered justifiable not to perform a definitive test. - Validity criteria fulfilled:
- yes
- Conclusions:
- The effect of the test material on the respiration of activated sewage sludge micro-organisms gave a 3-Hour EC50 value of greater than 1000 mg/L. The No Observed Effect Concentration (NOEC) after 3 hours exposure was 1000 mg/L.
- Executive summary:
A study was performed to assess the effect of the test item on the respiration of activated sewage sludge according to the OECD Guidelines No. 209 and GLP.
Activated sewage sludge was exposed to an aqueous dispersion of the test item at concentrations of 100 and 1000 mg/L (3 replicates of the 1000 mg/L test concentration) for a period of 3 hours at a temperature of 20 ± 2 °C with the addition of a synthetic sewage as a respiratory substrate.
The rate of respiration was determined after 3 hours contact time and compared to data for the control and a reference item, 3,5-dichlorophenol.
The effect of the test item on the respiration of activated sewage sludge gave a 3-Hour EC50 value of greater than 1000 mg/L. The No Observed Effect Concentration (NOEC) after 3 hours exposure was 1000 mg/L.
It was considered unnecessary and unrealistic to test at concentrations in excess of 1000 mg/L.
The reference item gave a 3-Hour EC50 value of 11 mg/L.
Reference
Description of key information
Toxicity to microorganisms
In an OECD 209 study conducted according to GLP, the 3 hour toxicity of the test material to activated sewage sludge micro-organisms is EC50 greater than 1,000 mg/L. The No Observed Effect Concentration (NOEC) after 3 hours exposure was 1000 mg/L. Therefore, it is possible to conclude that no effects were observed on activated sludge microorganisms.
Key value for chemical safety assessment
- EC10 or NOEC for microorganisms:
- 1 000 mg/L
Additional information
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