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EC number: 203-885-3 | CAS number: 111-59-1
- 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:
- 2017
- 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)
- Deviations:
- no
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- EU Method C.4-C (Determination of the "Ready" Biodegradability - Carbon Dioxide Evolution Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- Name: 9-Octadecenoic acid (9Z)-, propyl ester
Product Description: Propyl oleate
CAS No.: 111-59-1
Physical state: pale yellow to yellow liquid at 20 °C
Batch No.: 37584
Re-certification date of batch: 08 March 2018
Purity: > 99 % (fatty acid propyl esters, max water content 0.3 % (w/w))
Free Fatty Acid, % Oleic: 0.1
Color, Gardner: 3
Iodine Value, cg I2/g 75
Cloud Point, degrees C 0
Saponification Number, mg KOH/g 177
Moisture, % 0,07
Stability: stable under test conditions
Storage condition of test material: Room temperature, protected from light - Oxygen conditions:
- aerobic
- Inoculum or test system:
- sewage, predominantly domestic, non-adapted
- Details on inoculum:
- Activated sludge from the municipal wastewater treatment plant Breisgauer Bucht was used as inoculum with a concentration corresponding to 30 mg dry solids per litre. The treatment plant clarifies predominantly domestic wastewater and has a capacity of 600.000 inhabitant equivalents. Sampling date of activated sludge was on 4 July 2017. The dry solid content of the activated sludge was 3.9 g/L. It was determined by weight measurements after drying at 105°C for 5 hours (mean of triplicate measurements). The activated sludge was washed twice with tap water by settling the sludge, decanting the supernatant and re-suspending the sludge.
- Duration of test (contact time):
- 28 d
- Initial conc.:
- 20 mg/L
- Based on:
- TOC
- Parameter followed for biodegradation estimation:
- CO2 evolution
- Reference substance:
- benzoic acid, sodium salt
- Test performance:
- Toxicity control: The degradation extent in the toxicity control was 73.5% within 14 days. According to the criterion of the guideline, the test substance had no inhibitory effect on the inoculum.
Reference item: The reference compound sodium benzoate reached the pass levels for ready biodegradability within 4 days (see table 1).
Blank: The mean CO2-evolution of the blank flasks was 31.6 mg/L on day 28 after acidification.
Test parameters:
- Before adding the test item, the IC in the reactor was determined, but only insignificant amounts of IC (0.39 mg/L) were found.
- The IC-concentration of the NaOH in the second CO2-absorber flasks in line, used as protective flasks, was below 7 ppm and was not considered in the data processing, because CO2 absorption from room air was its source.
- The temperature was 19.2 – 22.3°C throughout the whole study and therefore temporarily below the required range of 22 ± 2°C. Since the CO2 evolution in the blank flasks was in the tolerated range and the biodegradation of the reference compound reached 60% within 4 days, it is concluded that the deviation had no effect on the validity of the test.
- The aeration rate was in the tolerated range of 1.6 – 5.5 bubbles/second (counted bubbles: 2.8 – 5.4 bubbles/second).
Criteria of validity
- The IC content in the test vessel was less than 5% of the TOC introduced with the test item.
- The CO2 evolution in the inoculum blank at the end of the test was below 40 mg/L.
- The difference of extremes of replicate values of the test item at the end of the test was less than 20%.
- The biodegradation of the reference compound reached the pass level of 60% ThCO2 by day 4.
- The degradation extent in the toxicity control was above 25% in 14 days based on ThCO2.
The test is valid according to OECD Test Guideline 301 B (July 1992). - Key result
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 88
- Sampling time:
- 28 d
- Remarks on result:
- other: mean of three replicate values
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 72.9
- Sampling time:
- 7 d
- Remarks on result:
- other: mean of three replicate values
- Details on results:
- The degradation of the test item at the end of the test was 88.0% (28 d after acidification, mean of three replicates). The test item reached the criteria for ready biodegradability (60% of ThCO2 within a 10-d window).
The degradation of the toxicity control after 14 days was 73.5%. The test item had no inhibitory effect on the inoculum according to the criterion of the guideline. - Results with reference substance:
- The biodegradation of the reference compound reached the pass level of 60% ThCO2 by day 4.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- In a Klimisch 1 OECD 301 B study the degradation of the test item at the end of the test was 88.9 % (28 d after acidification, mean of three replicates). The test item reached the criteria for ready biodegradability (60% of ThCO2 within a 10-d window).
- Executive summary:
In a Klimisch 1 OECD 301 B study the degradation of the test item at the end of the test was 88.9 % (28 d after acidification, mean of three replicates). The test item reached the criteria for ready biodegradability (60% of ThCO2 within a 10-d window). The degradation of the toxicity control after 14 days was 73.5%. The test item had no inhibitory effect on the inoculum according to the criterion of the guideline. The test is valid according to OECD 301 B (July 1992).
Reference
Results
Table 1: Ultimate biodegradation after x days [% of ThCO2]
reactor | day | 0 | 4 | 7 | 11 | 14 | 21 | 28 | 29 |
19 | Test flasks | 0 | 19.6 | 65.5 | 77.9 | 76.0 | 80.1 | 81.7 | 80.3 |
20 | 0 | 58.7 | 75.9 | 88.4 | 84.8 | 90.2 | 94.2 | 91.1 | |
21 | 0 | 55.6 | 77.0 | 89.6 | 88.3 | 90.0 | 95.9 | 92.5 | |
4 | Reference flasks | 0 | 75.4 | 86.3 | 88.4 | 89.5 | 90.6 | 93.1 | 96.8 |
5 | 0 |
77.7 |
82.7 |
84.7 |
87.1 |
86.0 |
90.4 |
94.6 |
|
6 |
|
0 |
72.8 |
80 .7 |
86.7 |
87.8 |
87.6 |
88.9 |
91.8 |
22 |
Toxicity control - test item & reference item |
0 |
41.1 |
58.9 |
72.6 |
73.5 |
78.4 |
83.5 |
81.1 |
Table 2: Mean CO2 evolution of blanks after x days
Day | 0 | 4 | 7 | 11 | 14 | 21 | 28 | 29 |
CO2 -evolution [mg/l] | 0 | 9.6 | 14.2 | 18.5 | 21.7 | 25.6 | 30.5 | 31.6 |
Description of key information
In a Klimisch 1 OECD 301 B study the degradation of the test item at the end of the test was 88.9 % (28 d after acidification, mean of three replicates). The test item reached the criteria for ready biodegradability (60% of ThCO2 within a 10-d window).
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
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