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EC number: 823-920-1 | CAS number: 5341-95-7
- 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:
- January 09, 2019 to February 15, 2019
- 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:
- 1992
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- sewage, domestic, non-adapted
- Details on inoculum:
- Preparation of Inoculum
The secondary effluent of a treatment plant (Jin-ju munsan public sewage treatment facility, Republic of Korea) was used as the inoculum. After collection, it was kept aerobic during transport and coarse particles were removed by settling for 1 hour. The inoculum was pre-conditioned by aerating for 7 days at the test temperature (22±2˚C).
Preparation of Mineral Medium
The stock solutions for mineral medium were prepared acc. to the guideline.
Deionized water was sterilized by autoclaving for 15 minutes at 121˚C.
Interpretation of results
If the percentage degradation of the test item is more than 60% by BOD measurement within 28 days, the test item is regarded as readily biodegradation. This level must be reached within 10 days of biodegradation exceeding 10%. - Duration of test (contact time):
- >= 1 - <= 28 d
- Initial conc.:
- >= 99.8 - <= 100.1 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- Preparation of Test Bottles & Test Conditions
Test bottles (500 mL-BOD bottles, WTW), all glassware and associated materials used in this test were sterilized by autoclaving for 15 minutes at 121˚C. The amounts of test item, reference item and mercury(II) chloride were directly weighed into the test bottles. The sodium hydroxide (two tablets) was used to absorb the carbon dioxide formed by the microorganisms, and test bottles were tightly sealed with the OxiTop®-C measuring heads. All procedures for preparation of test bottles were carried out in the clean bench to maintain sterile condition.
The test bottles were placed in a completely dark, temperature-controlled incubation under continuous stirring on inductive stirring system (Oxitop® Control, WTW).
Test bottles were prepared as follows: A volume of 10.0 mL inoculum equivalent to about 61.0 mL/L was added to the all test bottles except for bottle 6 (abiotic sterile control). Finally, the test bottles were made up to 164 mL with mineral medium prepared. The BOD values of all test bottles determined by OxiTop® controller (WTW) were measured automatically over a period of 28 days at 22.0±2.0˚C and test temperature were recorded daily during the test period. At the end of incubation (28 days), the pH of all test bottles was measured and recorded.
Interpretation of results
If the percentage degradation of the test item is more than 60% by BOD measurement within 28 days, the test item is regarded as readily biodegradation. This level must be reached within 10 days of biodegradation exceeding 10%. - Reference substance:
- benzoic acid, sodium salt
- Test performance:
- Test Conditions
The test temperature was maintained at 21.7±0.08˚C over a period of 28 days, and the pH value of the test suspensions (bottle 1, 2) was 7.5 at the end of the test, respectively. Test conditions were maintained within the acceptable limit and met the test guideline recommendations. - Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- >= 85.1 - <= 86.4
- St. dev.:
- 0.9
- Sampling time:
- 28 d
- Details on results:
- Microbial Degradation of Reference Item and Test Item
The results of the BOD concentrations and the percentage microbial degradation of the reference, and the test item over a period of 28 days are are presented in any other information on results.
In the procedure control, the percentage microbial degradation of the reference item was 87.5% at 14 days, thus confirming suitability of the inoculum.
The percentage microbial degradation of the toxicity control containing both the test item and the reference item was 76.1% at 14 days. This result confirms that the test item was not inhibitory to the activity of the microbial inoculum because the percentage degradation in the toxicity control was more than 25% within 14 days.
In inoculum blank, the BOD concentrations ranged from 0.0 to 8.4 mgO2/L within 28 days, indicating this value was within the acceptable range (less than 60 mgO2/L) specified by test guidelines.
In test suspensions, on the basis of the mean value, the 10-window began at 1.5 days and the percentage microbial degradation of the test item at the end of the 10-window (11.5 days) was 84.5%. The difference (% CV; Coefficient of Variation) of these values was 2.3 %.
At the end of the 28 days exposure period, the percentage degradation was 85.8% and difference was 1.0%. - Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- The test item is readily degradable by micro-organisms in the aquatic environmental according to the pass level of biodegradability specified by the guideline, fulfilling all criteria: 85.8±0.9% degradation within 28 days.
- Executive summary:
The test item 2,3-butanediol((2R,3S)-rich) was investigated to determine the ready biodegradability over a period of 28 days in accordance with OECD Guidelines (Test No. 301 Ready Biodegradability, 301 F) and in compliance with GLP.
The secondary effluent of a treatment plant (Jin-ju munsan public sewage treatment facility, Republic of Korea) was used as the inoculum. After collection, it was kept aerobic during transport and coarse particles were removed by settling for 1 hour. The inoculum was pre-conditioned by aerating for 7 days at the test temperature (22±2˚C). The initial test item concentration was 100 mg/L (2 replicates) and the concentration of inoculum was 61 mL/L. An inoculum blank (2 replicates), procedure, abiotic and toxicity control (1 replicate) were run in parallel. The BOD values of all test bottles determined by OxiTop® controller (WTW) were measured automatically over a period of 28 days at 22.0±2.0˚C and test temperature were recorded daily during the test period.
The results were as follows: The test temperature during the test period was maintained at 21.7±0.08˚C and the pH values measured in the test suspensions were 7.5 at the end of incubation (28 days), indicating the test conditions were within the acceptable limit. The percentage microbial degradation of the reference itemwas 87.5% at 14 days, thus confirming suitability of the inoculum. In toxicity control,the percentage microbial degradationwas 76.1% at 14 days,thus it was confirmed thatthe test item had obviously no inhibitory effect on the activity of the inoculum. In test suspensions,the percentage microbialdegradation of the test item was 84.5% at the end of the 10-d window (11.5 days) and was 85.8% at end of the test (28 days). The pass level for ready biodegradability is 60% of ThOD, which have to be reached a 10-d window within the 28 days of the test.
Therefore, 2,3-butanediol((2R,3S)-rich) was classified as readily degradable by micro-organisms in the aquatic environmental according to the pass level of biodegradability specified by the OECD 301F (1992).
Reference
The Percentage Microbial Degradation of Test Item and Reference Item by BOD
Time (days) |
% Degradationa) |
||||
Test suspensions |
Procedure control |
Toxicity control |
|||
Bottle 1 |
Bottle 2 |
Mean±SDb) |
Bottle 5 |
Bottle 7 |
|
0 |
0.0 |
0.0 |
0.0±0.0 |
0.0 |
0.0 |
1 |
0.0 |
0.0 |
0.5±0.7 |
37.1 |
17.8 |
2 |
20.2 |
18.8 |
19.5±1.0 |
50.6 |
25.6 |
3 |
40.4 |
39.1 |
39.8±0.9 |
62.3 |
32.5 |
4 |
56.4 |
55.0 |
55.7±1.0 |
70.7 |
38.9 |
5 |
65.1 |
62.2 |
63.7±2.1 |
76.1 |
42.7 |
6 |
69.2 |
67.8 |
68.5±1.0 |
79.1 |
47.4 |
7 |
74.8 |
73.5 |
74.2±0.9 |
79.1 |
51.3 |
8 |
79.4 |
78.1 |
78.8±0.9 |
82.7 |
56.0 |
9 |
82.0 |
79.6 |
80.8±1.7 |
84.5 |
59.8 |
10 |
83.5 |
81.2 |
82.4±1.6 |
84.5 |
62.9 |
11 |
85.0 |
82.2 |
83.6±2.0 |
85.7 |
67.5 |
12 |
86.6 |
83.8 |
85.2±2.0 |
85.7 |
70.6 |
13 |
86.6 |
83.8 |
85.2±2.0 |
85.7 |
73.6 |
14 |
88.1 |
85.3 |
86.7±2.0 |
87.5 |
76.1 |
15 |
88.1 |
85.3 |
86.7±2.0 |
87.5 |
79.1 |
16 |
88.1 |
86.8 |
87.5±0.9 |
87.5 |
80.8 |
17 |
88.1 |
86.8 |
87.5±0.9 |
87.5 |
81.3 |
18 |
89.1 |
86.8 |
88.0±1.6 |
89.3 |
83.0 |
19 |
89.1 |
86.8 |
88.0±1.6 |
89.3 |
83.8 |
20 |
89.1 |
88.4 |
88.8±0.5 |
89.3 |
84.6 |
21 |
87.7 |
86.9 |
87.3±0.6 |
89.4 |
85.2 |
22 |
89.2 |
86.9 |
88.1±1.6 |
89.4 |
86.9 |
23 |
88.5 |
87.3 |
87.9±0.8 |
90.4 |
87.3 |
24 |
88.5 |
87.3 |
87.9±0.8 |
90.4 |
87.3 |
25 |
87.1 |
85.8 |
86.5±0.9 |
88.7 |
87.4 |
26 |
87.1 |
85.8 |
86.5±0.9 |
88.7 |
87.4 |
27 |
86.4 |
85.1 |
85.8±0.9 |
87.9 |
87.0 |
28 |
86.4 |
85.1 |
85.8±0.9 |
87.9 |
87.6 |
a) Degradation (%) based on the theoretical oxygen demand
b) Standard Deviation
Description of key information
Readily biodegradable by micro-organisms, fulfilling all criteria: 85.8±0.9% degradation within 28 days.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
- Type of water:
- freshwater
Additional information
In the reliable key study, the test item 2,3 -butanediol((2R,3S)-rich) was investigated to determine the ready biodegradability over a period of 28 days in accordance with OECD Guidelines (Test No. 301 Ready Biodegradability, 301 F) and in compliance with GLP. The secondary effluent of a treatment plant (Jin-ju munsan public sewage treatment facility, Republic of Korea) was used as the inoculum. After collection, it was kept aerobic during transport and coarse particles were removed by settling for 1 hour. The initial test item concentration was 100 mg/L (2 replicates) and the concentration of inoculum was 61 mL/L. An inoculum blank (2 replicates), procedure, abiotic and toxicity control (1 replicate) were run in parallel.
The results were as follows: The test temperature during the test period was maintained at 21.7±0.08˚C and the pH values measured in the test suspensions were 7.5 at the end of incubation (28 days), indicating the test conditions were within the acceptable limit. The percentage microbial degradation of the reference item was 87.5% at 14 days, thus confirming suitability of the inoculum. In toxicity control, the percentage microbial degradation was 76.1% at 14 days, thus it was confirmed that the test item had obviously no inhibitory effect on the activity of the inoculum. In test suspensions, the percentage microbial degradation of the test item was 84.5% at the end of the 10-d window (11.5 days) and was 85.8% at end of the test (28 days).
Therefore, 2,3-butanediol((2R,3S)-rich) was classified as readily degradable by micro-organisms in the aquatic environmental according to the pass level of biodegradability specified by the OECD 301F (1992).
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