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EC number: 700-146-1 | CAS number: 1141487-54-8
- 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:
- 2010-09-29 to 2010-10-27
- 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
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-D (Determination of the "Ready" Biodegradability - Manometric Respirometry Test)
- Version / remarks:
- , 2008
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- , signed 2011-02-17
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
not applicable - Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge: sewage treatment plant Ruhrverband Kläranlage, Sunthelle 6, 57392 Schmallenberg, Germany (mainly fed with municipal wastewater)
- Method of cultivation: aerobic
- Storage conditions: kept aerobic until use
- Storage length: samples withdrawn on 2010-09-29
- Concentration of sludge: 29.6 mg dry mass/litre (7.39 mg dry mass/ 250 mL) - Duration of test (contact time):
- 28 d
- Initial conc.:
- 100 mg/L
- Based on:
- test mat.
- Initial conc.:
- 20 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Remarks:
- ; the measurement and recording of the oxygen demand was carried out continuously using SAPROMAT respirometer (VOITH Inc.)
- Details on study design:
- TEST CONDITIONS
- Composition of medium: for the preparation of the stock solutions for mineral medium the following reagents (analytical grade) were used:
a) KH2PO4: 8.50 g/L; K2HPO4: 21.75 g/L; Na2HPO4 X 2 H20: 33.40 g/L; NH4Cl: 0.50 g/L
b) CaCl2 X 2 H2O: 36.40 g/L
c) MgSO4 X 7 H2O: 22.50 g/L
d) FeCl3 X 6 H2O: 0.25 g/L
Deionized water, free from inhibitory concentrations of toxic substances (e.g. Cu2+ ions) was used.
The mineral medium applied in the test contained 10 mL/L and 1 mL/L of the mineral stock solution a and b-d, respectively.
- Test temperature: 22 °C +/- 1 °C
- pH: before test start the pH values of all solutions were determined (7.4 +/- 0.2) and at the end of the test the pH values of all solutions were determined again (pH: 100 mg/L test item: 6.8 and 7.5; 20 mg/L test item: 7.5 and 7.6; inoculum blank: 7.6; abiotic control: 7.5 and 7.5; procedural control 8.2 and 8.3; toxicity control: 7.9 and 8.0).
- Continuous darkness: yes
- Other: the suspension was aerated during the whole test.
TEST SYSTEM
- Culturing apparatus: 500 mL glass vessels at a medium volume of 250 mL
- Number of culture flasks/concentration: 2 vessels containing 100 mg/l of the test item (25 mg/250 mL) and inoculum; 2 vessels 20 mg/L of the test item and inoculum
100 mg test item correspond to 304 mg ThOD, which is clearly above the demanded value of at least 50 - 100 mg ThOD/L. Some substances with high ThODs have gently inclined degradation curves, even when they are completely degradable. However, for these substances it is hard to reach the threshold value within the 10 -day window. Therefore, an additional assay with 20 mg test item (61 mg ThOD, therefore , meeting the required concentration of 50 - 100 mg ThOD/L) was conducted.
- Test performed in closed vessels
- Method used to create aerobic conditions: suspension was aerated during the whole test.
- Measuring equipment: measurement and recording of the oxygen demand was carried out continuously using SAPROMAT respirometer (VOITH Inc.)
SAMPLING
- Sampling frequency: measurement and recording of the oxygen demand was carried out continuously using SAPROMAT respirometer (VOITH Inc.)
CONTROL AND BLANK SYSTEM
- Inoculum blank: 2 vessels containing only inoculum
- Abiotic control: 2 vessels containing test item (100 mg/L and a sterilising inoculum
- Toxicity control: 2 vessels containing test item (100 mg/L), reference item (100 mg/L) and inoculum
- Procedural control: 2 vessels containing reference item (100 mg/L) and inoculum
STATISTICAL METHODS:
The theoretical oxygen demand was calculated on the basis of the sum formula of the test and reference item by ThOD [g/g] = 16 * (2 C + 1/2 H + 1/2 Na-O)/Molecular weight.
The ThOD values for Na-benzonate, the test item and the toxicity control were determined as follows:
ThOD (test item)): 3.04 mg O2/mg test item
ThOD (Na-benzoate): 1.67 mg O2/mg reference item
ThOD (toxicity control): 2.35 mg O2/mg substance mixture
The biochemical oxygen demand (BOD) was calculated on the basis of the test raw data by BOD [mg/mg] = mg O2 uptake corrected by blank per mg test item.
The percent degradation was calculated according to the following formula:
Dt = [(Ct - Cb)/ThOD] X 100
Dt: degradation (%) at time t;
Ct: mean oxygen consumption (mg/L) in the test suspension at time t;
Cb: mean oxygen consumption (mg/L) in the blanks at time t;
ThOD: Theoretical oxygen demand of the test suspension (mg/L).
No further information on the study design was stated. - Reference substance:
- benzoic acid, sodium salt
- Remarks:
- Purity: 99 %; 100 mg/L medium
- Preliminary study:
- not applicable
- Test performance:
- No unusual observations during test.
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 49
- St. dev.:
- 2
- Sampling time:
- 28 d
- Remarks on result:
- other: Concentration tested: 100 mg/L of the test material
- Parameter:
- % degradation (O2 consumption)
- Value:
- 79
- St. dev.:
- 7
- Sampling time:
- 28 d
- Remarks on result:
- other: Concentration tested: 20 mg/L of the test material
- Parameter:
- % degradation (O2 consumption)
- Value:
- 37
- St. dev.:
- 2
- Sampling time:
- 14 d
- Remarks on result:
- other: Concentration tested: 100 mg/L of the test material
- Parameter:
- % degradation (O2 consumption)
- Value:
- 66
- St. dev.:
- 11
- Sampling time:
- 14 d
- Remarks on result:
- other: Concentration tested: 20 mg/L of the test material
- Details on results:
- The biodegradation within the 10-day-window was 72 % and 43 % in the assays with 20 mg/L and 100 mg/L, respectively. The 10-day-window starts at day 7 - 8 (20 mg/L) and day 8 (100 mg/L), respectively.
No abiotic degradation of the test item was noticable after 28 days of incubation. The biodegradation of the item mixture in the toxicity control was found to be 49 % after 14 days of incubation. Thus, the demanded threshold value of 25 % is exceeded and the test item can be identified as non toxic in a ready biodegradability test.
Due to a biodegradation of the test item below 60 % within the test duration, the test item at a concentration of 100 mg/L (ThOD of 304 mg O2/100 mg test item/L) failed the threshold value. Nevertheless, some substances with high ThOD have gently inclined degradation curves, even when they are completely degradable. For these substances it is hard to reach the threshold value within the 10 -day window. therefore, an additional assay with 20 mg test item (61 mg ThOD, therefore, meeting the required concentration of 50 - 100 mg ThOD/L) was conducted which passed the threshold of above 60 % biodegradtion in the 10 -day-window within a 28 day test duration.
In conclusion, according to the guideline, the test item can be identified as readily biodegradable under the chosen test conditions.
Validity and interpretation:
The test is considered valid, as
- the difference of extremes of replicate values of the removal of the test item at the end of the test was less than 20 %,
- the percentage degradation of the reference item has exceeded the pass level of 60 % by day 14,
- the oxygen uptake of the inoculum blank is < 60 mg/L in 28 days and the pH value was inside the range of 6.0 - 8.5. - Results with reference substance:
- The reference item sodium benzoate was degraded to 82 % within the first 14 days.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- In conclusion, according to EU Method C.4-D (2008), the test item can be considered as readily biodegradable under the chosen test conditions.
- Executive summary:
The biodegradability of the test item was tested according to EU Method C.4 -D (2008) at a concentration of 20 mg/L (61 mg ThOD) and 100 mg/L (304 mg ThOD) respectively. The biodegradation of the test item was found to be 79% after 28 days. The 10-d window was fulfilled (72 % biodegradation (20 mg test substance/L; ThOD 61 mg) that starts at day 7/8.
Hence, the substance is readily biodegradable under the test conditions. No inhibitory effects of the test item were observed (more than 25 % degradation occurred within 14 days) in the toxicity control.
Reference
Description of key information
Biodegradation in water - manometric respirometry test (OECD 301F; GLP compliant): readily biodegradable (79 % after 28 days). The 10-d window was fulfilled.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
One study on biodegradation in water was conducted. A manometric respirometry test (OECD 301F; GLP) was initiated with the test item resulting in 79 % degradation after 28 days (20 mg/L; ThOD 61 mg). The 10-d window was fulfilled (72 % biodegradation (20 mg test substance/L) that starts at day 7/8). As inoculum a non-adapted, domestic, activated sludge was used. The test item is considered to be readily biodegradable under the chosen test conditions.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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