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EC number: 203-095-9 | CAS number: 103-28-6
- 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
- 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:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Remarks:
- for read across
- Justification for type of information:
- Data for the target chemical is summarized based on the structurally similar read across chemicals
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- according to guideline
- Guideline:
- other: refer principle below
- Principles of method if other than guideline:
- Biodegradation of test chemical was estimated by applying weight of evidence approach using experimental data from structurally and functionally similar read across chemicals.
- GLP compliance:
- not specified
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- other: sludge
- Details on inoculum:
- 1. Fresh activated sludge from a biological waste water treatment plant treating predominantly domestic sewage (City og Geneva, Aire) was used.
The sludge is collected in the morning, washed three times in the mineral medium (by centrifuging at 1000g for 10 min, discarding the supernatant and resuspending in the mineral medium) and kept aerobic until being used on the same day.
Determination of the dry weight of suspended solids
The dry weight of suspended solids is determined by taking two 50 ml samples of the homogenized sludge, evaporating water on a steam bath, drying in an oven at 105-110°C for two hours and weighing the residue
2. concentration of activated sludge is 30 mg.L
3. Domestic waste water, surface soil and soil samples from polluted sites receiving predominantly domestic waste was collected and were mixed to get diluted suspension. The inoculum was kept aerobic until being used for experiment by supplying organic and inorganic sources required by micro flora to sustain at controlled laboratory conditions. - Duration of test (contact time):
- 28 d
- Initial conc.:
- 100 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Remarks:
- BOD
- Parameter followed for biodegradation estimation:
- TOC removal
- Parameter followed for biodegradation estimation:
- test mat. analysis
- Remarks:
- GC
- Details on study design:
- 1. Preparation of the flasks:
Test substance samples (25 mg, corresponding to 100 mg/L in a 250 ml flask) are weighed in small aluminium boats and added directly to the test flasks of the SAPROMAT, whereas reference substance samples (sodium benzoate) are added as 0.1ml of a 25 mg/ml solution in mineral medium.
All flasks are filled with 250ml of mineral medium. Samples of test or reference substance, or both, are added. Then, a volume of suspended sludge corresponding to 7.5 mg dry weight (generally 1 to 3 ml) is added. Except when the test substance has an acid or alkaline character, the pH of each flask is not measured but assumed to be the same as the mineral medium, in order not to remove any floating undissolved test substance from the test medium by dipping the glass electrode in it. Neutral test substances, even sodium benzoate, were shown not to affect the pH of the medium by more than 0.1 pH unit. About 2g of soda lime is placed in an attachment of the stopper, the flasks are closed and placed in the water bath of the SAPROMAT. After temperature and pressure equilibration, the oxygen meters of the instrument are set to zero (time zero of the experiment).
2. Standard type
3. The test system included control, test item and reference item. The concentration of test and reference item (Sodium Benzoate) chosen for the study was 100 mg/L, while that of inoculum was 10ml/l. ThOD (Theoretical oxygen demand) of test and reference item were determined by calculation. % Degradation was calculated using the values of BOD and ThOD for test item and reference item. - Parameter:
- % degradation (O2 consumption)
- Value:
- 89
- Sampling time:
- 29 d
- Remarks on result:
- other: other details not available
- Parameter:
- other: BOD
- Value:
- 95
- Sampling time:
- 28 d
- Remarks on result:
- other: other details not available
- Parameter:
- % degradation (TOC removal)
- Value:
- 98
- Sampling time:
- 28 d
- Remarks on result:
- other: other deatils not available
- Parameter:
- % degradation (test mat. analysis)
- Remarks:
- GC
- Value:
- 100
- Sampling time:
- 28 d
- Remarks on result:
- other: other details not available
- Parameter:
- % degradation (O2 consumption)
- Value:
- 81.15
- Sampling time:
- 28 d
- Remarks on result:
- other: other deatils not available
- Validity criteria fulfilled:
- not specified
- Interpretation of results:
- readily biodegradable
- Conclusions:
- By applying weight of evidence approach and considering results of experimental data from structurally and functionally similar read across chemicals which are mentioned above the biodegradation of test chemical was determined to be >80% in 28 days. On the basis of percent degradation it is concluded that test chemical is readily biodegradable.
- Executive summary:
Biodegradation of test chemical was estimated by applying weight of evidence approach using experimental data from structurally and functionally similar read across chemicals. The studies are as mentioned below:
In first experimental study the Ready biodegradability of test chemical was determined by the Manometric Respirometry test according to the OECD Guidelines No. 301 F. Fresh activated sludge from a biological waste water treatment plant treating predominantly domestic sewage (City og Geneva, Aire) was used. The sludge is collected in the morning, washed three times in the mineral medium (by centrifuging at 1000g for 10 min, discarding the supernatant and resuspending in the mineral medium) and kept aerobic until being used on the same day. The dry weight of suspended solids is determined by taking two 50 ml samples of the homogenized sludge, evaporating water on a steam bath, drying in an oven at 105-110°C for two hours and weighing the residue. In the study, a measured volume of the inoculated mineral medium, containing a known concentration of the test substance (100 mg/L) as the nominal sole source of organic carbon, is stirred in a closed flask at a constant temperature (22±1°C) for upto 28 days. The consumption of oxygen is determined by measuring the quantity of oxygen (produced electrolytically) required to maintain constant the gas volume in the respirometer flask. The respirometer used during this study is a SAPROMAT D 12. Sodium benzoate was used as a reference substance for the study. Test chemical undergoes 89% biodegradation after 29 days (88% after 28 days) in the test conditions. Biodegradation starts on day 2 and reaches 76% at the end of the 10 day window (days 2 to 12). Thus, test chemical was considered to be readily biodegradable according to this test.
Another experimental study was reviewed from the authoritative database (J check) in this study the biodegradation screening test was conducted for 28 days (4 weeks) for evaluating the percentage biodegradability of the test substance. Concentration of inoculum i.e, sludge is 30 mg/l and initial test substance conc. used in the study was 100 mg/l. The percentage degradation of test substance was determined to be 95% by BOD, 98% by TOC and 100% by GC. Thus, the substance was considered to be readily biodegradable in water.
In last experimental study, 28-days Manometric respirometry test following the OECD guideline 301F was performed to determine the ready biodegradability of the test chemical. % Degradation was calculated using the values of BOD and ThOD for test item and reference item. The BOD28value of test chemical was observed to be 1.967 mgO2/mg. ThOD was calculated as 2.424 mgO2/mg. Accordingly, the % degradation of the test item after 28 days of incubation at 20 ± 1°C according to manometric respirometry test was determined to be 81.15%.Based on the results, the test item, under the test conditions, was determined to be readily-Biodegradable at 20 ± 1°C over a period of 28 days.
By applying weight of evidence approach and considering results of experimental data from structurally and functionally similar read across chemicals which are mentioned above the biodegradation of test chemical was determined to be >80% in 28 days. On the basis of percent degradation it is concluded that test chemical is readily biodegradable.
Reference
1. Theoretical Oxygen demand
Molecular formula: C10H12O2
Molecular weight: 164.20 g/mol
Theoretical Oxygen demand (ThOD): 2.34 mgO2/mg
Biodegradability
Biological Oxygen Demand (BOD, mg O2/L, adjusted to nominal concentrations):
|
Days |
2 |
7 |
12 |
21 |
28 |
29 |
|
BOD Sludge |
1stflask |
B1 |
5.0 |
12.0 |
14.0 |
18.0 |
21.0 |
21.0 |
2ndflask |
B2 |
7.0 |
13.0 |
15.0 |
18.0 |
21.0 |
21.0 |
|
Mean |
B |
6.0 |
12.0 |
14.0 |
18.0 |
21.0 |
21.0 |
|
BOD Test substance |
1stflask |
C1 |
58.2 |
145.3 |
191.8 |
218.9 |
226.8 |
226.8 |
2ndflask |
C2 |
60.3 |
173.8 |
191.3 |
218.6 |
229.3 |
231.3 |
|
1stflask corrected |
C1-B |
52.2 |
132.8 |
177.3 |
200.9 |
205.8 |
205.8 |
|
2ndflask corrected |
C2-B |
54.3 |
161.3 |
176.8 |
200.6 |
208.3 |
210.3 |
|
% degradation |
1stflask |
D1 |
22 |
57 |
76 |
86 |
88 |
88 |
2ndflask |
D2 |
23 |
69 |
76 |
86 |
89 |
90 |
|
Mean |
D |
23 |
63 |
76 |
86 |
88 |
89 |
B= (B1+B2)/2
D1= 100*(C1-B)/ThOD*[S]
D2= 100*(C2-B)/ThOD*[S]
D= (D1+D2)/2
[S]: initial test substance concentration (mg/L)
2. no additional information
3. The apparatus used in this study is Respirometer BOD Sensor System (Code: F102B0133;non-automatic pressure measurement sensor system)and Respirometric incubator (FOC 120i)) by VELP Scientifica.
Test System |
Mineral media |
Concentration of Benzyl butyrate (mg/l) |
Concentration of Sodium Benzoate (mg/l) |
Concentration of Inoculum (ml/l) |
|
1. Inoculum Blank (Control) |
B1 |
√ |
- |
- |
10 ml |
B2 |
√ |
- |
- |
10 ml |
|
2. Test Suspension |
B1 |
√ |
100 |
- |
10 ml |
B2 |
√ |
100 |
- |
10 ml |
|
3. Procedure Control (Reference Item) |
B1 |
√ |
- |
100 |
10 ml |
B2 |
√ |
- |
100 |
10 ml |
Description of key information
By applying weight of evidence approach and considering results of experimental data from structurally and functionally similar read across chemicals which are mentioned above the biodegradation of test chemical was determined to be >80% in 28 days. On the basis of percent degradation it is concluded that test chemical is readily biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
Biodegradation of test chemical was estimated by applying weight of evidence approach using experimental data from structurally and functionally similar read across chemicals. The studies are as mentioned below:
In first experimental study the Ready biodegradability of test chemical was determined by the Manometric Respirometry test according to the OECD Guidelines No. 301 F. Fresh activated sludge from a biological waste water treatment plant treating predominantly domestic sewage (City og Geneva, Aire) was used. The sludge is collected in the morning, washed three times in the mineral medium (by centrifuging at 1000g for 10 min, discarding the supernatant and resuspending in the mineral medium) and kept aerobic until being used on the same day. The dry weight of suspended solids is determined by taking two 50 ml samples of the homogenized sludge, evaporating water on a steam bath, drying in an oven at 105-110°C for two hours and weighing the residue. In the study, a measured volume of the inoculated mineral medium, containing a known concentration of the test substance (100 mg/L) as the nominal sole source of organic carbon, is stirred in a closed flask at a constant temperature (22±1°C) for upto 28 days. The consumption of oxygen is determined by measuring the quantity of oxygen (produced electrolytically) required to maintain constant the gas volume in the respirometer flask. The respirometer used during this study is a SAPROMAT D 12. Sodium benzoate was used as a reference substance for the study. Test chemical undergoes 89% biodegradation after 29 days (88% after 28 days) in the test conditions. Biodegradation starts on day 2 and reaches 76% at the end of the 10 day window (days 2 to 12). Thus, test chemical was considered to be readily biodegradable according to this test.
Another experimental study was reviewed from the authoritative database (J check) in this study the biodegradation screening test was conducted for 28 days (4 weeks) for evaluating the percentage biodegradability of the test substance. Concentration of inoculum i.e, sludge is 30 mg/l and initial test substance conc. used in the study was 100 mg/l. The percentage degradation of test substance was determined to be 95% by BOD, 98% by TOC and 100% by GC. Thus, the substance was considered to be readily biodegradable in water.
In last experimental study, 28-days Manometric respirometry test following the OECD guideline 301F was performed to determine the ready biodegradability of the test chemical. % Degradation was calculated using the values of BOD and ThOD for test item and reference item. The BOD28value of test chemical was observed to be 1.967 mgO2/mg. ThOD was calculated as 2.424 mgO2/mg. Accordingly, the % degradation of the test item after 28 days of incubation at 20 ± 1°C according to manometric respirometry test was determined to be 81.15%.Based on the results, the test item, under the test conditions, was determined to be readily-Biodegradable at 20 ± 1°C over a period of 28 days.
By applying weight of evidence approach and considering results of experimental data from structurally and functionally similar read across chemicals which are mentioned above the biodegradation of test chemical was determined to be >80% in 28 days. On the basis of percent degradation it is concluded that test chemical is readily biodegradable.
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