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EC number: 272-657-3 | CAS number: 68901-15-5
- 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:
- 07 May - 04 Jun 1999
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-E (Determination of the "Ready" Biodegradability - Closed Bottle Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 D (Ready Biodegradability: Closed Bottle Test)
- GLP compliance:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- sewage, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum: Taken from the secondary effluent of a domestic sewage treatment plant Odenthal, Germany (collected on 30 Apr 1999).
- Laboratory culture: no
- Pretreatment: Separation of coarse particles by filtration. Aerated for 7 d.
- Concentration of inoculum: 5 mL/L - Duration of test (contact time):
- 28 d
- Initial conc.:
- 3 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium: according to guideline
- Test temperature: 20 ± 1 °C
- Continuous darkness: yes
TEST SYSTEM
- Number of culture flasks/concentration: 2
SAMPLING
- Sampling frequency: On day 0, 7, 14, 21 and 28.
- Sampling method: 2 bottles were removed on each sampling day to measure the oxygen consumption.
CONTROL AND BLANK SYSTEM
- Inoculum blank: yes, 10 bottles
- Abiotic sterile control: no
- Toxicity control: yes, 10 bottles
- Other: Reference substance: yes, 10 bottles - Reference substance:
- benzoic acid, sodium salt
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 24
- Sampling time:
- 28 d
- Remarks on result:
- other: Mean of two replicates
- Results with reference substance:
- 77% after 14 d and 91% after 28 d. The result with the reference substance is valid.
- Validity criteria fulfilled:
- yes
- Remarks:
- For further details please refer to “Any other information on results incl. tables”.
- Interpretation of results:
- inherently biodegradable, not fulfilling specific criteria
- Conclusions:
- 24% biodegradation was observed after 28 d in the study according to OECD guideline 301 D showing that the substance is not readily biodegradable.
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- Non-GLP guideline study
- Qualifier:
- according to guideline
- Guideline:
- other: BOD test for insoluble substances (BODIS), preliminary guideline of the Bundesumweltamt Berlin (1990)
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: ISO 10708: Water quality -- Evaluation in an aqueous medium of the ultimate aerobic biodegradability of organic compounds -- Determination of biochemical oxygen demand in a two-phase closed bottle test
- GLP compliance:
- no
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge: Activated sludge was collected from the aeration tank of the municipal sewage treatment plant, Pforzheim, Germany.
- Laboratory culture: no
- Preparation of inoculum for exposure: Washed twice by centrifugation (10 min, 6000 rpm) with mineral solution. Supernatant was decanted and the pellet was mixed with mineral solution to give a concentration of 3.0 g/L. 2 L of mineral medium were inoculated with 20 mL of the activated sludge. 200 mL were transferred into 9 test vessels together with magnetic stirring bars. Bottles were closed with glass stoppers and shaken without test substances for 1 week in the dark at 20 °C and 100 rpm.
- Concentration of sludge: 3 g/L - Duration of test (contact time):
- 28 d
- Initial conc.:
- >= 4.15 - <= 4.45 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium: according to guideline
- Test temperature: 20 °C
- pH: 6.8 - 7.5 (7 d, before aeration), 7.0 - 7.2 (15 d, before aeration), 7.1 - 7.4 (21 d, before aeration), 7.6 - 7.8 (28 d, before aeration)
- Continuous darkness: yes
- Other: incubated on a rotary shaker at 100 rpm
TEST SYSTEM
- Number of culture flasks/concentration: 3
- Method used to create aerobic conditions: 15 min prior to incubation the dilution water was aerated
- Measuring equipment: Oximeter (WTW Oxi 191)
SAMPLING
- Sampling frequency: On day 7, 15, 21 and 28.
- Other: After the measurements the test assays were aerated for 15 min, measured once more and were incubated for the remaining test period.
CONTROL AND BLANK SYSTEM
- Inoculum blank: yes, 3 bottles
- Abiotic sterile control: no
- Toxicity control: no
- Other: Reference substance: yes, 3 bottles - Reference substance:
- benzoic acid, sodium salt
- Parameter:
- % degradation (O2 consumption)
- Value:
- 24.1
- Sampling time:
- 28 d
- Remarks on result:
- other: Mean of three replicates
- Results with reference substance:
- The reference substance was degraded to 65.1% after 28 d. After 14 d 60% degradation was reached.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- inherently biodegradable, not fulfilling specific criteria
- Conclusions:
- 24.1% biodegradation was observed after 28 d in the study according to the preliminary guideline of the German Environmental Agency (BODIS test) showing that the substance is not readily biodegradable.
Referenceopen allclose all
BIOLOGICAL RESULTS:
Table 1: Degradation of the test substance
|
Degradation [%] |
|||
|
7 d |
14 d |
21 d |
28 d |
Replicate 1 |
6 |
19 |
17 |
24 |
Replicate 2 |
10 |
20 |
18 |
23 |
Mean |
8 |
20 |
18 |
24 |
Reference substance 1 |
68 |
77 |
77 |
92 |
Reference substance 2 |
67 |
77 |
76 |
89 |
Mean |
68 |
77 |
77 |
91 |
Toxicity control 1 |
31 |
39 |
38 |
39 |
Toxicity control 2 |
31 |
39 |
39 |
39 |
Mean |
31 |
39 |
39 |
39 |
VALIDITY CRITERIA:
Table 2: Validity criteria for OECD 301.
Criterion from the guideline |
Outcome |
Validity criterion fulfilled |
Percentage degradation of the reference compound has reached the pass levels by day 14. |
77% by day 14 |
yes |
The toxicity control should degrade to at least 35% (based on DOC) or at least 25% (based on ThOD or ThCO2) within 14 d. |
39% by day 14 |
yes |
Table 1: Degradation rates after 7, 15, 21 and 28 d
|
Biodegradation [%] |
|||
7 d |
15 d |
21 d |
28 d |
|
Test substance 1 |
18.1 |
28.9 |
31.1 |
31.7 |
Test substance 2 |
4.6 |
12.6 |
16.5 |
16.5 |
Test substance 3 |
10.4 |
17.1 |
24.1 |
24.1 |
Mean |
10.9 |
19.5 |
23.9 |
24.1 |
|
|
|
|
|
Reference substance 1 |
55.5 |
63.5 |
63.5 |
63.5 |
Reference substance 2 |
52.0 |
59.9 |
59.9 |
59.9 |
Reference substance 3 |
59.0 |
72.0 |
72.0 |
72.0 |
Mean |
55.5 |
65.1 |
65.1 |
65.1 |
Description of key information
Not readily biodegradable: 24% biodegradation after 28 d (EU Method C.4-E)
Key value for chemical safety assessment
- Biodegradation in water:
- inherently biodegradable, not fulfilling specific criteria
- Type of water:
- freshwater
Additional information
Two studies are available, testing the ready biodegradability of the substance by non-adapted sewage treatment plant microorganisms.
The key study was performed according to the EU Method C.4-E and GLP. The test was run for 28 days and microorganisms were exposed to 3 mg/L test material. O2 consumption was followed for the estimation of the biodegradation. Sodium benzoate was used as a reference substance. A toxicity control was set up with 3 mg/L test item and 2.9 mg/L reference substance in order to examine the toxicity of the substance on microorganisms. 24% of the substance was biodegraded after 28 d, and therefore it is not considered readily biodegradable. The toxicity control attained 39% degradation after 14 d, verifying that the tested item was not inhibitory to the inoculated microorganisms.
An available BODIS test (according to the preliminary guideline of the German Environmental Agency) confirms the result of the key study. The microorganisms were exposed to 4.15 – 4.45 mg/L substance for 28 d and the O2 consumption was followed as an indicator for biodegradation. Benzoic acid (0.104 mg/mL ThOD) was used as a reference substance while no toxicity control was run in parallel. 24.1% biodegradation was observed after 28 d showing that the substance is not readily biodegradable.
In conclusion all available results indicate that the substance is not rapidly biodegradable.
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