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EC number: 217-588-1 | CAS number: 1897-45-6
- 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
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- Carcinogenicity
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- Specific investigations
- Exposure related observations in humans
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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:
- 18 Sep 2002 to 19 Sep 2002
- 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:
- 1993
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- - Test substance: Test solutions were prepared by the direct addition of a known weight of the test substance to a total volume of 500 ml aerated dechlorinated water, synthetic sewage and activated sludge. During the test. 0.07302 g of the test substance were used to prepare the test solutions.
- Reference substance: A nominal 500 mg/L stock solution of the reference substance, 3,5-dichlorophenol, was prepared in deionised water. This stock solution was adjusted as necessary to be within the range pH 6 to 8 and was observed to be clear and colourless. The final pH of this stock on the day of use was measured as 6.52 and no subsequent adjustment was required. - Test organisms (species):
- activated sludge
- Details on inoculum:
- - Collecting date and location: Activated sludge was obtained from Buckland Sewage Treatment Works, Newton Abbot, Devon, UK, 1 day prior to the study. This works treats sewage of predominantly domestic origin.
- Method of preparation: On return to the laboratory, the activated sludge was settled and the concentrated sludge washed with aerated dechlorinated water. The washed settled sludge was fed with 50 mL of OECD synthetic sewage feed per litre of sludge per day and aerated at room temperature, until it was used in the test.
- Synthetic sewage: A synthetic sewage mixture described by the OECD guideline was prepared containing the following constituents per litre of deionised water: 15.2 g of peptone, 10.5 g of meat extract, 2.9 g of urea, 0.7 g of NaCl, 0.4 g of CaCl2.2H2O, 0.2 g of MgSO4.7H2O and 2.8 g of K2HPO4. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 3 h
- Test temperature:
- 20 ± 2°C
- pH:
- - Start of the test: 6.98 - 7.04
- End of the test: 7.45 - 7.78 - Nominal and measured concentrations:
- Nominal concentration (both test substance and reference substance): 1.0, 3.2, 10, 32 and 100 mg/L. See Table 1 in 'Any other information on materials and methods incl. tables'
- Details on test conditions:
- TEST SYSTEM
- Aeration: Yes
- Replication: One vessel for each of the test substance concentration and positive control concentration and 2 vessles for the blank control.
- Final solids concentration: 1600 mg/L
TEST MEDIUM / WATER PARAMETERS
- pH: The pH of each flask was measured at the start and end of the test.
- Temperature: Flasks were set up at 10 minute intervals and aerated at 20 ± 2°C for 3 hours. The temperatures of the flask contents were measured at the end of the 3 hours aeration using a mercury-in-glass thermometer.
EFFECT PARAMETERS MEASURED:
- The respiration rate of each culture was measured after 3 hours and compared with the mean respiration rate of the two control cultures. The rate of oxygen uptake was measured in a confined perspex cell into which a polarographic oxygen electrode was inserted. The electrode was connected to a meter whose output was recorded on a potentiometric chart recorder. The dissolved oxygen concentration after the 3 hour
aeration period was at least 6.5 mg O2/L
- The respiration rate was calculated between approximately 7.5 and 4.0 mg O2/L, or over approximately a 6 minute period where respiration was low. The rates of oxygen uptake were expressed as mg O2/L/h. - Reference substance (positive control):
- yes
- Remarks:
- 3,5-dichlorophenol
- Key result
- Duration:
- 3 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Key result
- Duration:
- 3 h
- Dose descriptor:
- EC50
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Details on results:
- The respiration rate of the two controls were 26.0 and 27.0 mg O2/L/h respectively. In test flasks dosed with the test substance, 22% inhibition observed at the highest test concentration (100 mg/L), 11% inhibition at 3.2 mg/L and < 10% inhibition was observed in the remaining concentrations. An overview of the results is provided in Table 2 in 'Any other information on results incl. tables'.
- Results with reference substance (positive control):
- The reference substance, 3,5-dichlorophenol, caused substantial inhibition of the respiration rate of the activated sludge. From the results obtained the 3 hour EC50 value was estimated to be 6.4 mg/L. This is within the expected normal range of 2 to 25 mg/L indicating the sludge was responding normally and confirming the viability of the sludge organisms. The respiration rates in the two control flasks were within 15% of each other. Therefore, the mean control respiration rate was used in calculation of the percentage inhibition. An overview of the results is provided in Table 2 in 'Any other information on results incl. tables'.
- Validity criteria fulfilled:
- not specified
- Conclusions:
- After the incubation period of three hours, the test substance had ≤ 22% inhibition on the respiration rate of activated sludge at concentrations up to and including 100 mg/L, the highest concentration tested. Based on the findings, the 3-hour EC50 was determined to be ≥100 mg/L and NOEC was determined to be 10 mg/L.
- Executive summary:
The inhibitory effects of the test substance on the respiration of activated sludge micro-organisms were studied according to OECD TG No. 209 (1993) at nominal concentrations of 1.0, 3.2, 10, 32 and 100 mg/L. The study was conducted in compliance with GLP criteria. There were two separate controls and 3,5-dichlorophenol as a reference substance at concentrations of 1.0, 3.2, 10, 32 and 100 mg/L. Each flask contained an excess of the synthetic sewage, sufficient activated sludge to give final solids concentrations of 1600 mg/L, an appropriate quantity of either the test substance or 3,5-dichlorophenol stock solution and aerated dechlorinated water to give a final flask contents volume of 500 mL. The test was carried out at a temperature of 20 ± 2°C. After the incubation period of three hours, The respiration rate of the two controls were 26.0 and 27.0 mg O2/L/h respectively. In test flasks dosed with the test substance 22% inhibition observed at the highest test concentration (100 mg/L), 11% inhibition at 3.2 mg/L and <10% inhibition was observed in the remaining concentrations. Based on the findings, the 3-hour NOEC of the test substance was determined to be 10 mg/L and the EC50 was ≥ 100 mg/L. The EC50 of the reference substance was determined to be 6.4 mg/L.
Reference
Table 2. Inhibition results
Test substance |
Nominal concentration (mg/L) |
pH |
Respiration rate (mg O2/L/h) |
% mean control respiration ratea |
% inhibition |
|
Start |
End |
|||||
Control |
Control |
7.00 |
7.57 |
26.0 |
- |
- |
3,5-DCP |
100 |
6.98 |
7.45 |
1.5 |
5.6 |
94 |
3,5-DCP |
32 |
7.01 |
7.63 |
3.5 |
13.0 |
87 |
3,5-DCP |
10 |
7.00 |
7.62 |
8.5 |
31.5 |
68 |
3,5-DCP |
3.2 |
7.01 |
7.78 |
21.0 |
77.8 |
22 |
3,5-DCP |
1.0 |
7.01 |
7.68 |
26.5 |
98.1 |
< 10 |
The test substance |
100 |
7.01 |
7.51 |
21.0 |
77.8 |
22 |
The test substance |
32 |
7.04 |
7.57 |
24.0 |
88.9 |
11 |
The test substance |
10 |
7.00 |
7.59 |
26.0 |
96.3 |
< 10 |
The test substance |
3.2 |
7.01 |
7.58 |
25.0 |
92.6 |
< 10 |
The test substance |
1.0 |
7.00 |
7.60 |
26.0 |
96.3 |
< 10 |
Control |
Control |
7.01 |
7.59 |
28.0 |
- |
- |
a Mean control respiration rate = 27 mg O2/L/h
b 3,5-dichlorophenol
Description of key information
3-h NOEC ≥ 10 mg/L, Activated sludge, inhibition of total respiration, OECD TG 209, Wallace 2002
3-h EC50 > 100 mg/L, Activated sludge, inhibition of total respiration, OECD TG 209, Wallace 2002
Key value for chemical safety assessment
- EC10 or NOEC for microorganisms:
- 10 mg/L
Additional information
The inhibitory effects of the test substance on the respiration of activated sludge micro-organisms were studied according to OECD TG No. 209 (1993) at nominal concentrations of 1.0, 3.2, 10, 32 and 100 mg/L. The study was conducted in compliance with GLP criteria. There were two separate controls and 3,5-dichlorophenol as a reference substance at concentrations of 1.0, 3.2, 10, 32 and 100 mg/L. Each flask contained an excess of the synthetic sewage, sufficient activated sludge to give final solids concentrations of 1600 mg/L, an appropriate quantity of either the test substance or 3,5-dichlorophenol stock solution and aerated dechlorinated water to give a final flask contents volume of 500 mL. The test was carried out at a temperature of 20 ± 2°C. After the incubation period of three hours, The respiration rate of the two controls were 26.0 and 27.0 mg O2/L/h respectively. In test flasks dosed with the test substance 22% inhibition observed at the highest test concentration (100 mg/L), 11% inhibition at 3.2 mg/L and <10% inhibition was observed in the remaining concentrations. Based on the findings, the 3-hour NOEC of the test substance was determined to be 10 mg/L and the EC50 was ≥ 100 mg/L. The EC50 of the reference substance was determined to be 6.4 mg/L.
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