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EC number: 608-818-5 | CAS number: 32997-86-7
- 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:
- April - September 2018
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 D (Ready Biodegradability: Closed Bottle Test)
- Version / remarks:
- 1992
- GLP compliance:
- yes (incl. QA statement)
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of activated sludge: three sewage treatment plants
- Pretreatment: filtered through glass wool (discarding first 200 mL). It will be mixed and aerated for 5 days. The filtrate will be diluted by using deionized water (ratio 1:1)
- Preperation: The inoculum will be prepared by adding the required amount of activated sludge (Maximum COD 6000 mg/L as per ISO 5815-1:2003(E)) and dilution water (based on the COD) in a cleaned glass beaker. The inoculum will be stored at about 20 ± 2°C
- Initial cell/biomass concentration: 7.10 mg/L based on ThOD - Duration of test (contact time):
- 28 d
- Initial conc.:
- 7.1 mg/L
- Based on:
- ThOD
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium: Standart OECD medium
- Additional substrate: no
- Solubilising agent: no
- Test temperature: 19.7 - 20.6°C
- pH: 7 - 7.5
- pH adjusted: no
- Aeration of dilution water: yes
TEST SYSTEM
- Culturing apparatus: BOD bottles
- Number of culture flasks/concentration: 3
- Measuring equipment: The dissolved oxygen content in the Control sample (Glucose-glutamic acid), Blank and test solutions were measured initially by Winkler titration. Parallel groups of BOD bottles were prepared for the determination of the reference substances in simultaneous experimental series. All the bottles were incubated at 20 ± 2°C. The BOD bottles were assembled, including inoculum blanks, to allow at least duplicate measurements of oxygen consumption to be made at the desired test intervals, at day 0, 7, 14, 21 and 28 days.
CONTROL AND BLANK SYSTEM
- Inoculum blank: 0.6 mL ATU solution + Inoculum made up to 300 mL.
- Control solution: Glucose-glutamic acid [6 mL] + 0.6 mL ATU solution + Inoculum made up to 300 mL.
- Toxicity control: 50 mL of Reference item solution + 0.6 mL ATU solution + Inoculum made up to 300 mL. - Reference substance:
- acetic acid, sodium salt
- Preliminary study:
- During the preliminary study, determination of oxygen concentrations was performed at the start of the experiment (day 0) and on day 5 and 7. The temperature in the test room varied between 19.8 and 20.8°C. Measured pH values at the start of the test (using pH strips- found to be 7 - 7.5) and measured oxygen concentrations and oxygen depletions were measured. The relative biodegradation values were calculated from the O2 measurements performed during the test period of 7 days revealed 41.63%, 48.69% and 41.76% biodegradation of test item at three different concentrations of 2.37 mg/L, 7.10 mg/L and 11.83 mg/L (mean values of duplicates on day 7).
- Test performance:
- During the definitive study, determination of oxygen concentrations were performed at the start of the experiment (day 0) and on day 7, 14, 21 and 28. The temperature in the test room varied between 19.7 and 20.6°C. Measured pH values at the start of the test (using pH strips- found to be 7 - 7.5). The relative biodegradation values were calculated from the O2 measurements performed during the test period of 14 days of three bottles revealed 79.18 %, 83.81 % and 83.81% biodegradation of test item at 7.10 mg/L concentrations based on ThOD (mean values of duplicates on day 14). The test item reached a maximum biodegradability of 82.27% based on ThOD (mean values of three bottles) within 14 days of biodegradation exceeding 60%. The test item was fully degraded within 28 days test period. Oxygen depletion in the inoculum blank obtained was 0.19 mg O2/L which is below 1.5 mg O2/L after 28 days. The residual concentrations of oxygen in the test bottles were found to be > 0.5 mg/L at all durations. All differences of duplicate biodegradation values expressed as mg O2/L were less than 20% (-4.55 to 4.74%). Since all criteria for acceptability of the test were met, this study was considered to be valid.
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 82.27
- Sampling time:
- 14 d
- Parameter:
- % degradation (O2 consumption)
- Value:
- 100
- Sampling time:
- 28 d
- Results with reference substance:
- The reference substance (sodium acetate) attained a 71.53% biodegradation level (of greater than 60% degradation) within 14 days based on ThOD.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- The test item was readily biodegradable for maximum of 82.27% at 14 days under the conditions of the closed bottle method (OECD 310D).
- Executive summary:
The ready biodegradability of the test item was determined using the closed bottle method (OECD guideline No. 301 D, 1992). The ThOD of the test item was calculated to be 0.65 mg of O2/mg. The ThOD of sodium acetate (reference substance) was calculated to be 0.78 mg of O2/mg. The values for the test and reference substances were determined using the molecular formula and the purity of the substances. The test item stocks were prepared in the test media by mixing to accelerate dissolution of the test substance in mineral medium. Required volumes of the stock solution corresponding to the test concentrations and microbial organisms were added to the test medium. During the definitive test, determination of oxygen concentrations were performed at the start of the experiment (day 0) and on day 7, 14, 21 and 28. The relative biodegradation values were calculated from the O2 measurements performed during the test period of 14 days of three bottles revealed 79.18%, 83.81% and 83.81% biodegradation of test item at 7.10 mg/L concentrations based on ThOD (mean values of duplicates on day 14). The test item reached a maximum biodegradability of 82.26% based on ThOD (mean values of three bottles) with 14 days of biodegradation exceeding 60%.The test item was fully degradad within the 28 day test period. Oxygen depletion in the inoculum blank obtained was 0.19 mg O2/L which is below 1.5 mg O2/L after 28 days. The residual concentrations of oxygen in the test bottles were found to be > 0.5 mg/L at all durations. All differences of duplicate biodegradation values expressed as mg O2/L were less than 20% (-4.55 to 4.74%).The reference substance (sodium acetate) attained a 71.53% biodegradation level (more than 60% degradation) within 14 days based on ThOD. Since all criteria for acceptability of the test were met, this study was considered to be valid. The test item was readily biodegradable for maximum of 82.27% at 14 days under the conditions of the closed bottle method.
Reference
Description of key information
The test item was readily biodegradable for maximum of 82.26% after 14 days under the conditions of the closed bottle method (OECD 310D). After 28 days the test item was fully degraded.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
The ready biodegradability of the test item was determined using the closed bottle method (OECD guideline No. 301 D, 1992). The ThOD of the test item was calculated to be 0.65 mg of O2/mg. The ThOD of sodium acetate (reference substance) was calculated to be 0.78 mg of O2/mg. The values for the test and reference substances were determined using the molecular formula and the purity of the substances. The test item stocks were prepared in the test media by mixing to accelerate dissolution of the test substance in mineral medium. Required volumes of the stock solution corresponding to the test concentrations and microbial organisms were added to the test medium. During the definitive test, determination of oxygen concentrations were performed at the start of the experiment (day 0) and on day 7, 14, 21 and 28. The relative biodegradation values were calculated from the O2 measurements performed during the test period of 14 days of three bottles revealed 79.18%, 83.81% and 83.81% biodegradation of test item at 7.10 mg/L concentrations based on ThOD (mean values of duplicates on day 14). The test item reached a maximum biodegradability of 82.26% based on ThOD (mean values of three bottles) with 14 days of biodegradation exceeding 60%.The test item was fully degradad within the 28 day test period. Oxygen depletion in the inoculum blank obtained was 0.19 mg O2/L which is below 1.5 mg O2/L after 28 days. The residual concentrations of oxygen in the test bottles were found to be > 0.5 mg/L at all durations. All differences of duplicate biodegradation values expressed as mg O2/L were less than 20% (-4.55 to 4.74%).The reference substance (sodium acetate) attained a 71.53% biodegradation level (more than 60% degradation) within 14 days based on ThOD.Since all criteria for acceptability of the test were met, this study was considered to be valid. The test item was readily biodegradable for maximum of 82.27% at 14 days under the conditions of the closed bottle method.
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