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EC number: 811-605-1 | CAS number: 37318-95-9
- 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 B (Ready Biodegradability: CO2 Evolution Test)
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-C (Determination of the "Ready" Biodegradability - Carbon Dioxide Evolution Test)
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Ministerium für Arbeit, Integration und Soziales des Landes Nordrhein-Westfalen
- 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, Schmallenberg, Germany (February 14th, 2017)
- Preparation of inoculum for exposure: The sludge was washed in mineral medium and centrifuged (at 1100 g for 10 minutes). The supernatant was discarded. The concentrated sludge was suspended in mineral medium to a concentration of 2.6 g suspended solids/L. The sludge was aerated with CO2-free air over night to purge the system of carbon dioxide. A sample was withdrawn just before use for the determination of the dry weight of the suspended solids.
- Concentration of sludge: 29 mg dry mass/litre (87 mg dry mass/3 L) - Duration of test (contact time):
- 28 d
- Initial conc.:
- 20 mg/L
- Based on:
- other: ThOC
- Parameter followed for biodegradation estimation:
- CO2 evolution
- Details on study design:
- TEST CONDITIONS
- Composition of medium: Mineral medium
- Test temperature: 22 °C (± 2 °C)
- pH: 7.4 of mineral medium
- Aeration of dilution water: with CO2-free air
- Suspended solids concentration: 29 mg/L in the final 3 litres
- Continuous darkness: yes
- Other: To each test vessel 2400 mL mineral medium was added. A volume of 34.3 mL of the prepared activated sludge to give a concentration of suspended solids of 29 mg/L in the final 3 litres of inoculated mixture was added. After aeartion with CO2-free air overnicht, two absorption bottles, each containing 200 mL of 0.05 M sodium hydroxide solution were connected in series to each 5-litre flask. Test item was added on a weight basis. The volume of suspensions in all flasks was filled up to 3 litres by the addition of mineral medium.
TEST SYSTEM
- Culturing apparatus: 5-litre flasks
- Number of culture flasks/concentration: 2
- Method used to create aerobic conditions: The vessels were aerated by the passage of carbon dioxide free air at a controlled rate during the incubation period.
- Test performed in closed vessels due to significant volatility of test substance: yes
- Details of trap for CO2 and volatile organics if used: The CO2 is trapped in sodium hydroxide and is measured as inorganic carbon.
SAMPLING
- Sampling frequency: Days of sampling for CO2 measurement were day 2, 5, 9, 12, 14, 21, 28, and 29.
- Sampling method: The samples of suspensions (IC measurement) were filtered through ROTH PET filters (0.45 μm) as soon as they are taken. The samples of the hydroxide absorbers were measured without any manipulation to avoid CO2 enrichment.
The measurements of the TIC concentration were carried out using a TC analyser (Shimadzu TOC-V-CPH).
- Sample storage before analysis: Analysis was done directly after sampling.
CONTROL AND BLANK SYSTEM
- Inoculum blank: 2
- Abiotic sterile control: 1
- Toxicity control: 1 - Reference substance:
- benzoic acid, sodium salt
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 99
- Sampling time:
- 28 d
- Results with reference substance:
- In the positive control, 79% was degraded after 14 d confirming the suitability of the inoculum.
- Validity criteria fulfilled:
- yes
- Remarks:
- For further details please refer to “Any other information on results incl. tables”.
- Interpretation of results:
- readily biodegradable
- Conclusions:
- The pass level of 60% was reached in a ready biodegradation test (OECD 301B) within 28 days. The 10-day window was reached. Thus, the substance is readily biodegradable.
Reference
In the toxicity control, more than 25% biodegradation occurred within 14 days (83.7%). Therefore, the test item was assumed not to inhibit microbial activity.
Table 1: Percent degradation (IC) after 14 days. Degradation (%) on the basis of IC in the sodium hydroxide traps after 14 days of incubation.Single and mean values of the replicates and standard deviation.
vessel |
Test suspension |
Abiotic control |
Procedural control |
Toxicity control |
1 |
75.0 |
0.3 |
79.1 |
83.7 |
2 |
86.4 |
|||
Mean |
80.7 |
0.3 |
79.1 |
83.7 |
SD |
8.0 |
Table 2: Percent degradation (IC) after 28 days. Degradation (%) on the basis of IC in the sodium hydroxide traps after 28 days of incubation and the following acid dissolving. Single and mean values of the replicates and standard deviation.
vessel |
Test suspension |
Abiotic control |
Procedural control |
Toxicity control |
1 |
96.4 |
-2.5 |
84.4 |
96.5 |
2 |
102.4 |
|||
Mean |
99.4 |
-2.5 |
84.4 |
96.5 |
SD |
4.2 |
Table 3: Validity criteria for OECD 301B
Criterion from the guideline |
Outcome |
Validity criterion fulfilled |
Difference of extremes of replicate values of the removal of the test chemical at the plateau, at the end of the test or at the end of the 10-d window, as appropriate, is less than 20%. |
With 6 % the difference of extremes of replicate values of the removal of the test item at the end of the test was less than 20 %. |
yes |
Percentage degradation of the reference compound has reached the pass levels by day 14. |
The percentage degradation of the reference item has exceeded the pass level of 60 % 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. |
The biodegradation of the item mixture in the toxicity control was found to be 84 % after 14 days of incubation. |
yes |
The IC content of the test substance suspension in the mineral medium at the beginning of the test must be less than 5% of the TC. |
With 2.0 %, the mean IC content in the mineral medium of the suspensions containing test item at the beginning of the test fall below the demanded threshold value of 5 % of the TC. |
yes |
The total CO2 evolution in the inoculum blank at the end of the test should not normally exceed 40 mg/L medium. |
With 16.0 mg CO2 per liter (4.4 mg C/L), the total CO2 evolution in the inoculum blank at the end of the test is below the demanded value. |
yes |
Description of key information
Readily biodegradable: 99% in 28 d (CO2 evolution), OECD 301B
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
- Type of water:
- freshwater
Additional information
One study is available investigating the ready biodegradability Dodecanoic acid, ester with 1,2,3-propanetriol (CAS 37318-95-9). This study was conducted according to OECD 301B (GLP) using activated sludge from a municipal sewage treatment plant being exposed to the test substance at a concentration of 20 mg/L ThOC for 28 days. After 28 days, the test substance reached 99% biodegradation based on Co2 evolution. The 10-day window was met. No inhibitory effects of the test item were observed in the toxicity control (more than 25 % degradation occurred within 14 days). Thus, the substance is readily biodegradable according to the OECD criteria.
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