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EC number: 248-698-8 | CAS number: 27859-58-1
- 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
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- Solubility in organic solvents / fat solubility
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- 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
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- Nanomaterial radical formation potential
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- 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
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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:
- 12 May 1999 to 23 June 1999
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
- Deviations:
- yes
- Remarks:
- see below
- Principles of method if other than guideline:
- The study followed the same principles as the OECD 301 F guideline, however it did not include the abiotic and the toxicity checks, and pre-adapted inoculum was employed.
The ready biodegradability of the test material was investigated as part of a study in which a total of six substances was tested. - GLP compliance:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, adapted
- Details on inoculum:
- - Source of inoculum/activated sludge: The inoculum used was the return activated sludge from the Mentor Waste Water Treatment plant (Mentor, OH), collected on the 12 May 1999. The inoculum was adapted to the test material for 14 days before the test initiation.
- Laboratory culture: Yes
- Method of cultivation: The sludge was aerated and stirred for 2-3 hours in a flask, homogenised in a Waring blender at low/medium speed for two minutes, and allowed to stand for to one hour. The supernatant was then pipetted out and used for inoculum pre-adaptation.
- Pre-adaptation of the inoculum: Sludge supernatant supplemented with ~25 mg/L vitamin free casamino acids and ~25 mg/L yeast extract. A two litre flask containing 100 mL of supplemented sludge supernatant and 900 mL test medium was prepared and the test material was added incrementally during the adaptation period, at concentrations approximately equivalent to 4, 8 and 8 mg carbon/L on days 0, 7, and 11 , respectively,
The mixture was aerated throughout the adaptation period by shaking at 150 rpm and 22 °C. On day 14, the adapted culture was homogenised in a blender for ~15 seconds and used as the inoculum. A composite culture was prepared by mixing equal amount of all homogenised cultures.
- Initial cell/biomass concentration: The bacterial count in the culture was estimated using Easicult®. The inoculum level was 10 % using the acclimated composite culture. The microbial level in the test mixture was 10³. - Duration of test (contact time):
- 28 d
- Initial conc.:
- 100 mg/L
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium: Mineral medium was freshly prepared by using deionized water and the four stock solutions listed below. The 900 mL medium in each bioreactor contained 10 mL of stock solution A, and 1 mL each of the stock solutions B, C, and D and 887 mL of deionized water. One hundred mL of the acclimated inoculum was later added to each reactor to reach a final volume of one litre.
Stock solution A: 8.5 g/L KH2PO4, 21.75 g/L K2HPO4, 50.30 g/L Na2HPO4.7H2O and 0.50 g/LNH4Cl
Stock solution B: 36.40 g/L CaCl2.2H2O
Stock solution C: 22.50 g/L MgSO4.7H2O
Stock solution D: 0.25 g/L FeCl3.6H2O and 0.40 g/L Na2EDTA
- Test temperature: 23 ± 1 °C
- pH: The pH values of the initial medium in each bioreactor as well as the final pH values of the test mixtures were monitored to ensure biodegradation was not inhibited by extreme pHs. The pH of the test medium in each test vessel (reactor) was measured before the test/reference materials were added and then again at the end of the 28 day test period.
- Aeration of dilution water: The mixture was continuously stirred in a closed flask.
- Other: Magnetic stirring was provided for all test mixtures throughout the test period.
TEST SYSTEM
- Culturing apparatus: Reactor flasks, controlled by eight-channel respirometer reactor modules were used. Each reactor flask is equipped with an electrolytic cell assembly which generates oxygen to replace the amount consumed by the test mixture in the flask.
- Number of culture flasks/concentration: 2
- Measuring equipment: The consumption of oxygen was monitored using an electrolytic respirometer system. A BI-1000 electrolytic respirometer system was used; the oxygen uptake in all flasks was monitored continuously and recorded automatically every 4 hours throughout the test period using the BI Data Acquisition Software.
CONTROL AND BLANK SYSTEM
- Inoculum blank: The composite culture was used as the inoculum for procedure check and inoculum blank.
- Abiotic sterile control: No
- Toxicity control: No
STATISTICAL METHODS: No statistical analysis was performed - Reference substance:
- benzoic acid, sodium salt
- Key result
- Value:
- 18.3
- Sampling time:
- 28 d
- Remarks on result:
- other: The test material has been determined not to be readily biodegradable.
- Details on results:
- The test material was observed to biodegrade 18.3 % over the 28 day test period (average of two values, 11.0 and 25.5 %).
The BOD values of the test material are the values after the correction for background from the inoculum blank. The percent biodegradation level was the ratio of BOD and ThOD. The biodegradation rates of the duplicates agreed within 20 %.
The average oxygen uptake value of the two inoculum blanks was 30.7 mg and under the specified criteria of <60 mg.
The pH values were within the overall acceptable range of 6.0 to 8.5, indicating that the levels of biodegradation were not limited by extreme pHs.
All of the test validity criteria were met. - Results with reference substance:
- The reference substance, sodium benzoate, reached a level of 94.3 % in the test period. Sodium benzoate degraded readily, reaching the pass level of 60 % within 3 days.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- Under the conditions of the study, the test material has been determined not to be readily biodegradable.
- Executive summary:
As part of an investigation to determine the ready biodegradability of a number of substances, the ready biodegradability of the test material was investigated in a respirometry test that followed the same principle as that in the standardised guideline OECD 301 F, except that it did not include the abiotic and toxicity checks and pre-adapted inoculum was employed. The study was conducted under GLP conditions.
The inoculum was adapted to the test material for 14 days before test initiation and the degradability was expressed as the ratio of the measured Biological Oxygen Demand (BOD) and the Theoretical Oxygen Demand (ThOD; calculated from the elemental analysis of the substance).
The initial test material concentration was 100 mg/L and the temperature throughout the 28 day test was 23 ± 1 °C. Oxygen consumption was measured with a BI-1000 electrolytic respirometer system; the oxygen uptake in all flasks were monitored continuously and recorded automatically every 4 hours throughout the test period. Sodium benzoate was employed as reference material.
The level of biodegradation at the end of the 28 day test period for the test material was 18.3 % (average of two replicates). The reference substance reached a biodegradation level of 94.3 % in the same test period.
Under the conditions of the study, the test material has been determined not to be readily biodegradable.
Reference
Table 1: Theoretical Oxygen Demand (ThOD)
Test Vessel |
Substance |
Specific ThOD (mg/mg) |
Sample weight (mg) |
ThOD |
BI 1 - 1 |
Sodium benzoate |
1.825 |
105.1 |
191.8 |
BI 1 - 4 |
Test material |
1.139 |
110.2 |
125.5 |
BI 2 - 1 |
Sodium benzoate |
1.825 |
107.4 |
196.0 |
BI 2 - 4 |
Test material |
1.139 |
107.2 |
122.1 |
Table 2: Accumulated Oxygen Demands and Final Biodegradation Levels (Day 28)
Test Vessel |
Substance |
Obs. Oxygen uptake |
BOD |
ThOD |
Biodeg. |
BI 1 - 1 |
Sodium benzoate |
209.2 |
173.0 |
191.8 |
90.2 |
BI 1 - 4 |
Test material |
50.0 |
13.8 |
125.5 |
11.0 |
BI 2 - 1 |
Sodium benzoate |
217.7 |
192.6 |
196.0 |
98.3 |
BI 2 - 4 |
Test material |
56.2 |
31.1 |
122.1 |
25.5 |
Description of key information
The test material has been determined not to be readily biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
Additional information
As part of an investigation to determine the ready biodegradability of a number of substances, the ready biodegradability of the test material was investigated in a respirometry test that followed the same principle as that in the standardised guideline OECD 301 F, except that it did not include the abiotic and toxicity checks and pre-adapted inoculum was employed. The study was conducted under GLP conditions. The study was awarded a reliability score of 1 in accordance with the criteria for assessing data quality as set forth by Klimisch et al. (1997).
The inoculum was adapted to the test material for 14 days before test initiation and the degradability was expressed as the ratio of the measured Biological Oxygen Demand (BOD) and the Theoretical Oxygen Demand (ThOD; calculated from the elemental analysis of the substance).
The initial test material concentration was 100 mg/L and the temperature throughout the 28 day test was 23 ± 1 °C. Oxygen consumption was measured with a BI-1000 electrolytic respirometer system; the oxygen uptake in all flasks were monitored continuously and recorded automatically every 4 hours throughout the test period. Sodium benzoate was employed as reference material.
The level of biodegradation at the end of the 28 day test period for the test material was 18.3 % (average of two replicates). The reference substance reached a biodegradation level of 94.3 % in the same test period.
Under the conditions of the study, the test material has been determined not to be readily biodegradable.
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