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Diss Factsheets
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EC number: 476-880-9 | CAS number: -
- 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
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 A (Ready Biodegradability: DOC Die Away Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-A (Determination of the "Ready" Biodegradability - Dissolved Organic Carbon (DOC) Die-Away Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic (adaptation not specified)
- Details on inoculum:
- - Source of inoculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): wastewater treatment plant (ARA Ergolz II, Füllinsdorf, Switzerland)
- Preparation of inoculum for exposure:
The sludge was washed twice with tap water by centrifugation and the supernatant liquid phase was decanted. A homogenized aliquot of the final sludge suspension was weighed, thereafter dried and the ratio of wet to dry weight was calculated.
Based on this ratio, calculated amounts of wet sludge were suspended in test water to obtain a concentration equivalent to 4 g (±10%) dry material per liter. During the holding period of four days, the sludge was aerated at room temperature. Before use, the dry weight of this diluted activated sludge was determined again, and defined amounts were added to test water to obtain a final concentration of 30 mg dry material per liter. - Duration of test (contact time):
- ca. 28 d
- Initial conc.:
- ca. 25.1 mg/L
- Based on:
- DOC
- Parameter followed for biodegradation estimation:
- DOC removal
- Details on study design:
- TEST CONDITIONS
- Test temperature: 21 - 24 ºC
- pH: The pH measured in all flasks at the end of exposure (Day 28) was 7.3 – 7.5
- Continuous darkness: The test flasks were incubated in a dark room.
TEST SYSTEM
- Culturing apparatus: 2000-mL Erlenmeyer flasks
- Number of culture flasks/concentration: two
- Other: Each flask was loosely covered with aluminum foil to allow the exchange of air between the flask and the surrounding atmosphere. The test media were continuously stirred by magnetic stirrers.
SAMPLING
One sample of about 10 mL was taken from each test flask per sampling date. Prior to sampling, water evaporation losses were determined by weighing the flasks and were compensated by adding purified water. Deposits on the test vessels were resuspended.
Sampling dates:
Test item and inoculum control: Exposure Day 0, 3, 7, 10, 13, 21 and 28
Procedure control: Exposure Day 0, 3, 7, 13 and 28
Toxicity control: Exposure Day 0, 7, 13 and 28
CONTROL AND BLANK SYSTEM
- Inoculum blank: yes
- Toxicity control: yes - Reference substance:
- benzoic acid, sodium salt
- Key result
- Parameter:
- % degradation (DOC removal)
- Value:
- 4
- Sampling time:
- 28 d
- Details on results:
- In the test flasks, containing the test item and activated sludge (inoculum), the mean concentration of DOC (dissolved organic carbon) varied between 23 and 27 mg/L over the exposure period of 28 days, and was not significantly different from the initial mean DOC concentration of 25 mg/L, measured on Day 0. Expressed as percentage DOC-removal, mean values in the range from -6 to 8% were noted. Therefore, the test substance was not biodegradable under the test conditions within 28 days.
- Results with reference substance:
- The reference item sodium benzoate was completely biodegraded (100%) within seven days of exposure, thus confirming suitability of the activated sludge.
- Validity criteria fulfilled:
- yes
- Remarks:
- (the test item is not inhibitory to activated sludge at the tested concentration because degradation was >35% within 14 days; the reference item was completely biodegraded within 7 days)
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- The test substance was not biodegradable under the test conditions within 28 days.
- Executive summary:
The test item was investigated for its ready biodegradability in a "28-Day DOC Die-Away Test" according to EU Commission Directive 92/69 EEC, C.4-A (1992) and OECD Guideline for Testing of Chemicals, No. 301 A (1992). In the test flasks, containing the test item and activated sludge (inoculum), the mean concentrations of dissolved organic carbon (DOC) were not significantly different from the initial mean DOC concentration measured on Day 0. Therefore, the test substance was not biodegradable under the test conditions within 28 days. The reference item sodium benzoate was completely biodegraded (100%) within seven days of exposure, thus confirming suitability of the activated sludge. In the toxicity control, containing the test item, the reference item sodium benzoate and activated sludge (inoculum), the initial DOC decreased by 55% within 13 days of exposure. Thus, according to the test guidelines, the test item was not inhibitory to activated sludge at the tested concentration of 82 mg/L because degradation was >35% within 14 days.
Reference
In the toxicity control, containing the test item (corresponding to 48% of total DOC), the reference item (corresponding to 52% of total DOC) and activated sludge (inoculum), the initial DOC concentration of 56 mg/L measured on Day 0 decreased to 25 mg/L on Day 13. Biodegradation amounted to 55% within 13 days of exposure. Thus, according to the test guidelines, it is assumed that the test item is not inhibitory to activated sludge at the tested concentration of 82 mg/L because degradation was >35% within 14 days.
Description of key information
Key study: OECD 301-A and EU method C.4-A. GLP study.
The test substance was not biodegradable under the test conditions within 28 days.
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
Additional information
Key study: OECD 301-A and EU method C.4-A. GLP study.
In the test flasks, containing the test item and activated sludge (inoculum), the mean concentrations of dissolved organic carbon (DOC) were not significantly different from the initial mean DOC concentration measured on Day 0. Therefore, the test substance was not biodegradable under the test conditions within 28 days.
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