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EC number: 603-101-3 | CAS number: 125962-78-9
- 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: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2003-04-28 to 2003-07-23
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
- Version / remarks:
- July 17, 1992
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-D (Determination of the "Ready" Biodegradability - Manometric Respirometry Test)
- Version / remarks:
- EEC Publication No. L 383 A, December 1992
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge: Activated sludge (microorganisms) from a domestic waste water treatment plant in Groß-Zimmern, Germany
- Preparation of inoculum for exposure: The activated sludge used for this study was washed by centrifugation and the supernatant liquid phase was decanted. The solid material was resuspended in tap water and again centrifuged. This procedure was repeated twice. An aliquot of the final sludge suspension was weighed, dried and the ratio of wet sludge to its dry weight was determined. Based on this ratio, calculated aliquots of washed sludge suspension, corresponding to 1.5 g dry material per litre were mixed with test water and then aerated until use. - Duration of test (contact time):
- 28 d
- Initial conc.:
- 102.4 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium: Reconstituted water
- Test temperature: 21 - 22 °C
- pH: 7.6 (measured at the start of the test)
- pH adjusted: no
- Aeration of dilution water: no
- Continuous darkness: yes
TEST SYSTEM
- Culturing apparatus: Manometric Test System with test flasks containing a volume of 500 mL.
- Number of culture flasks/concentration: 2
- Measuring equipment: BSB/BOD-Sensor-System
- Test performed in closed vessels: the flasks were closed gas-tight by a measuring head
- Test performed in open system: no
SAMPLING
- Sampling frequency: everyday of exposure period
CONTROL AND BLANK SYSTEM
- Test item: 2
- Inoculum blank: 2
- Abiotic sterile control: 1
- Toxicity control: 1
- Procedure control: 1 - Reference substance:
- aniline
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- >= 3 - <= 5
- Sampling time:
- 28 d
- Details on results:
- After correction for the mean biochemical oxygen demand of the inoculum controls at the end of the 28-day exposure period degradation rates of 5 % and 3 % were found.
- Results with reference substance:
- The reference item Aniline was sufficiently degraded to 79 % after 14 days and to 96 % after 28 days of incubation, based on ThODNH4. The percentage biodegradation of the reference item confirms the suitability of the used activated sludge inoculum.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- not readily biodegradable
- Conclusions:
- The degradation rate of the test material did not reach 60 % within the 10-day window and after 28 days of incubation. Thus, the test item is not readily biodegradable.
- Executive summary:
The ready biodegradability of the test item in a Manometric Respirometry Test according to OECD TG 301 F and EU Method C.4-D was determined with aerobic activated sludge from a domestic wastewater treatment plant for 28 days under GLP. The biodegradation was followed by the oxygen uptake of the microorganisms during exposure. As a reference item aniline was tested simultaneously under the same conditions as the test item, and functioned as a procedure control. The oxygen concentration was measured using a BSB/BOD-Sensor-System and the flasks were closed gas-tight by a measuring head. The validity criterion was fulfilled. The reference item Aniline was sufficiently degraded to 79 % after 14 days and to 96 % after 28 days of incubation, based on ThODNH4. The percentage biodegradation of the reference item confirms the suitability of the used activated sludge inoculum. In the toxicity control containing both, the test item and the reference item Aniline, 31 % biodegradation was noted within 14 days and 38 % biodegradation was determined after 28 days of incubation, based on ThODNH4. The test item can be assumed to be not inhibitory on the activated sludge microorganisms because degradation was > 25 % within 14 days. After correction for the mean biochemical oxygen demand of the inoculum controls at the end of the 28-day exposure period degradation rates of 5 % and 3 % were found. The degradation rate of the test material did not reach 60 % within the 10-day window and after 28 days of incubation. Thus, the test item is not readily biodegradable.
Reference
Validity Criteria of the Study
Inoculum Control: The oxygen demand of the inoculum control (medium and inoculum) was 29.5 mg O2/L and thus not greater than 60 mg O2/L within 28 days.
pH-Value: The pH-value of the test item flasks at the end of the test was 7.9, and thus within the range of pH 6.0 - 8.5.
Reference Item: The percentage degradation of the reference item Aniline, based on ThODNH4, reached the level for ready biodegradability (about 60 %) within 8 days.
Test Item: The difference of duplicate values for the degradation of the test item at any time during the test period was less than 20 %.
Individual Results
Biodegradation of Test Item: After correction for the mean biochemical oxygen demand of the inoculum controls at the end of the 28-day exposure period degradation rates of 5 % and 3 % were found.
Biodegradation of Reference Item Aniline: The reference item Aniline was sufficiently degraded to 79 % after 14 days and to 96 % after 28 days of incubation, based on ThODNH4. The percentage biodegradation of the reference item confirms the suitability of the used activated sludge inoculum.
Biodegradation in the Toxicity Control: In the toxicity control containing both, the test item and the reference item Aniline, 31 % biodegradation was noted within 14 days and 38 % biodegradation was determined after 28 days of incubation, based on ThODNH4. According to the test guidelines the test item can be assumed to be not inhibitory on the activated sludge microorganisms because degradation was > 25 % within 14 days.
Abiotic Control Oxygen Demand: In the abiotic control no oxygen demand was determined during the exposure period of 28 days.
Table 1: Cumulative biochemical oxygen demand (mg O2/L) in test flasks during the test period of 28 days
Time (days) | Flask 1 | Flask 2 | Flask 3 | Flask 4 | Flask 5 | Flask 6 | Flask 7 |
1 | 1.5 | 0 | 2.9 | 0 | 0 | 0 | 0 |
2 | 2.9 | 0 | 5.9 | 0 | 0 | 0 | 0 |
3 | 5.9 | 1.5 | 7.4 | 2.9 | 0 | 0 | 0 |
4 | 11.8 | 2.9 | 8.8 | 5.9 | 11.8 | 0 | 8.8 |
5 | 10.3 | 5.9 | 8.8 | 7.4 | 54.6 | 0 | 31.0 |
6 | 10.3 | 7.4 | 10.3 | 11.8 | 143.0 | 0 | 124.0 |
7 | 13.3 | 10.3 | 11.8 | 13.3 | 159.0 | 0 | 139.0 |
8 | 14.7 | 10.3 | 11.8 | 16.2 | 171.0 | 0 | 149.0 |
9 | 19.2 | 11.8 | 16.2 | 16.2 | 182.8 | 0 | 160.8 |
10 | 23.6 | 13.3 | 13.3 | 14.7 | 188.7 | 0 | 168.2 |
11 | 25.1 | 13.3 | 14.7 | 16.2 | 194.6 | 0 | 174.1 |
12 | 28.0 | 14.7 | 17.7 | 19.2 | 202.0 | 0 | 181.4 |
13 | 29.5 | 19.2 | 16.2 | 20.6 | 206.4 | 0 | 185.9 |
14 | 31.0 | 21.6 | 19.2 | 22.1 | 213.8 | 0 | 190.3 |
15 | 32.4 | 23.6 | 20.6 | 22.1 | 218.2 | 0 | 193.2 |
16 | 32.4 | 24.7 | 22.1 | 22.1 | 224.1 | 0 | 196.2 |
17 | 32.4 | 25.1 | 20.6 | 23.6 | 225.6 | 0 | 196.2 |
18 | 35.4 | 27.3 | 22.1 | 23.6 | 231.5 | 0 | 200.6 |
19 | 35.4 | 29.5 | 22.1 | 22.1 | 237.4 | 0 | 205.0 |
20 | 36.9 | 31.0 | 22.1 | 23.6 | 240.3 | 0 | 206.5 |
21 | 38.3 | 32.4 | 23.6 | 25.1 | 243.3 | 0 | 208.0 |
22 | 39.8 | 32.4 | 25.1 | 26.5 | 246.2 | 0 | 212.4 |
23 | 41.4 | 35.4 | 25.1 | 26.5 | 249.2 | 0 | 215.4 |
24 | 41.3 | 35.4 | 29.5 | 28.0 | 255.1 | 0 | 218.5 |
25 | 41.3 | 35.4 | 28.0 | 28.0 | 258.0 | 0 | 221.6 |
26 | 41.3 | 36.9 | 28.0 | 29.5 | 259.5 | 0 | 224.8 |
27 | 42.8 | 36.9 | 28.0 | 29.5 | 265.4 | 0 | 228.6 |
28 | 42.8 | 36.9 | 29.5 | 29.5 | 265.4 | 0 | 232.4 |
flasks 1 and 2: Test item
flasks 3 and 4: Inoculum control
flask 5: Aniline (Procedure control)
flask 6: Abiotic control
flask 7: Toxicity control
Table 2: Percentage biodegradation (BOD/ThODNH4) of test item, of Aniline and of the toxicity control
Time (days) |
| Percentage Biodegradation |
| |
Test item | Aniline | Toxicity control | ||
flask 1 | flask 2 | flask 5 | flask 7 | |
1 | 0 | 0 | -1 | 0 |
2 | 0 | -1 | -1 | -1 |
3 | 0 | -1 | -2 | -1 |
4 | 2 | -2 | 2 | 0 |
5 | 1 | -1 | 19 | 4 |
6 | 0 | -1 | 54 | 21 |
7 | 0 | -1 | 60 | 23 |
8 | 0 | -1 | 64 | 25 |
9 | 1 | -2 | 68 | 27 |
10 | 3 | 0 | 71 | 29 |
11 | 3 | -1 | 73 | 29 |
12 | 3 | -1 | 75 | 30 |
13 | 4 | 0 | 77 | 31 |
14 | 4 | 0 | 79 | 31 |
15 | 4 | 1 | 80 | 32 |
16 | 4 | 1 | 82 | 32 |
17 | 4 | 1 | 83 | 32 |
18 | 4 | 2 | 85 | 33 |
19 | 5 | 3 | 88 | 34 |
20 | 5 | 3 | 89 | 34 |
21 | 5 | 3 | 89 | 34 |
22 | 5 | 2 | 90 | 35 |
23 | 6 | 3 | 91 | 35 |
24 | 4 | 2 | 92 | 35 |
25 | 5 | 3 | 94 | 36 |
26 | 4 | 3 | 94 | 36 |
27 | 5 | 3 | 97 | 37 |
28 | 5 | 3 | 96 | 38 |
ThODNH4 of Test item: 2.77 mg O2/mg test item
ThODNH4 of Aniline: 2.41 mg O2/mg Aniline
Table 3: pH-values at the end of the test
Flask No. | Treatment | pH-value |
1 | Test item | 7.9 |
2 | Test item | 7.9 |
3 | Inoculum control | 7.7 |
4 | Inoculum control | 7.7 |
5 | Procedure control (Aniline) | 7.8 |
6 | Abiotic control | 7.8 |
7 | Toxicity control | 7.9 |
Description of key information
The degradation rate of the test material did not reach 60 % within the 10-day window and after 28 days of incubation. Thus, the test item is not readily biodegradable (reference 5.2.1-1).
Key value for chemical safety assessment
- Biodegradation in water:
- not biodegradable
- Type of water:
- freshwater
Additional information
The ready biodegradability of the test item in a Manometric Respirometry Test according to OECD TG 301 F and EU Method C.4-D was determined with aerobic activated sludge from a domestic wastewater treatment plant for 28 days under GLP. The biodegradation was followed by the oxygen uptake of the microorganisms during exposure. As a reference item aniline was tested simultaneously under the same conditions as the test item, and functioned as a procedure control. The oxygen concentration was measured using a BSB/BOD-Sensor-System and the flasks were closed gas-tight by a measuring head. The validity criterion was fulfilled. The reference item Aniline was sufficiently degraded to 79 % after 14 days and to 96 % after 28 days of incubation, based on ThODNH4. The percentage biodegradation of the reference item confirms the suitability of the used activated sludge inoculum. In the toxicity control containing both, the test item and the reference item Aniline, 31 % biodegradation was noted within 14 days and 38 % biodegradation was determined after 28 days of incubation, based on ThODNH4. The test item can be assumed to be not inhibitory on the activated sludge microorganisms because degradation was > 25 % within 14 days. After correction for the mean biochemical oxygen demand of the inoculum controls at the end of the 28-day exposure period degradation rates of 5 % and 3 % were found. The degradation rate of the test material did not reach 60 % within the 10-day window and after 28 days of incubation. Thus, the test item is not readily biodegradable.
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