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EC number: 947-919-1 | 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:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- No purity; Limited information on test design
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
- GLP compliance:
- no
- Remarks:
- Non-GLP testing facility.
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge: Station Epuration Gembloux 2nd Stage (28 Oct 2011)
- Concentration of sludge: > 10^6 CFU/mL
- Type and size of filter used: Glass fibre filter - Duration of test (contact time):
- 28 d
- Initial conc.:
- >= 10 - <= 20 mg/L
- Based on:
- DOC
- Parameter followed for biodegradation estimation:
- CO2 evolution
- Details on study design:
- TEST CONDITIONS
- Composition of medium: Stock solution (prepared with High Quality Water = water containing less than 1 mg/L of DOC): Phospate buffer solutions pH 7.4, Magnesium sulphate solution 0.091 M, Calcium chloride solution 0.25 M, Ferric chloride solution 0.001 M
- Test temperature: 22 ± 2 °C
- Aeration of dilution water: Air free from carbon dioxide passes through the solutions using a flow of 50 to 100 mL/min.
TEST SYSTEM
- Culturing apparatus: 2 L brown glass flasks
- Number of culture flasks/concentration: 2
- Method used to create aerobic conditions: 2 L flasks were mounted with an aeration tube on a magnetic stirrer.
- Details of trap for CO2 and volatile organics if used: The released CO2 from biodegradation reacts with Ba(OH)2 and is trapped under Barium carbonate precipitate (in 250 mL flasks). Then the amount of CO2 is determined by back titration of the remaining Ba(OH)2 with HCl and phenolphthalein as indicator.
SAMPLING
- Sampling frequency: every two to three days for the first 10 days and every three to five days until the day 28
- Sampling method: At day 28, the pH of the solution in the container has to be measured, the 1 to 10 mL of concentrated HCl has to be added to the container in order to eject the CO2 from the test container. Last titration is carried out the day 29. - Reference substance:
- other: Na Benzoate 20 mg C/L
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 94.6
- Sampling time:
- 28 d
- Details on results:
- Within the 10-day time window the 60% level was passed. Therefore, the test substance is regarded as readily biodegradable.
- Results with reference substance:
- Degradation: 91.3% after 29 days, 60% pass level was reached.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1989
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Guideline study with acceptable restrictions: Analytical purity of test substance is not stated. Temperature adjustment in the course of oxygen measurements.
- Qualifier:
- according to guideline
- Guideline:
- other: ISO/DIS method 10708: Water quality - Evaluation in an aqueous medium if the "ultimate" aerobic biodegradability of organic compounds - Method by determining the biochemical oxygen demand / two-phase closed bottle test)
- Deviations:
- yes
- Remarks:
- Temperature adjustment in the course of oxygen measurements
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 301 D (Ready Biodegradability: Closed Bottle Test)
- Deviations:
- yes
- Remarks:
- Temperature adjustment in the course of oxygen measurements
- GLP compliance:
- no
- Remarks:
- But the study adhered GLP comparable quality conditions (DIN ISO 9001 certified laboratory)
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge: sewage treatment plant Hochdahl predominantly municipal sewage serving for a population equivalent of approx. 27000.
- Preparation of inoculum for exposure: the mineral medium was inoculated with activated sludge and after addition of a magnetic stirrer stabilised under laboratory conditions for approx. one week. The bottles were aerated with compressed air until O2-saturation was reached and then spiked with a predetermined amount of test substance.
- Concentration of sludge: 2.5 - 3.5 mg/L test medium - Duration of test (contact time):
- 28 d
- Initial conc.:
- 100 mg/L
- Based on:
- COD
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium: according to OECD 301 guidelines prepared in deionised water
- Test temperature: 20 - 25 °C; before each oxygen measurement, the temperature was adjusted to 20 ± 0.5 °C half an hour before each measurement.
TEST SYSTEM
- Culturing apparatus: glass test bottles with a total volume of approx. 300 mL. The test vessels have a known volume of aqueous test mixture (2/3) and air (1/3).
- Number of culture flasks/concentration: 3
- Measuring equipment: O2-electrode (WTW; FRG; microprocessor oximeter OXI 2000 with electrode model TriOxmatic EO 200)
- Test performed in closed vessels due to significant volatility of test substance: performed in closed bottles
- Other: The bottles were aerated with compressed air by means of a sintered glass tube until O2 saturation was reached and then spiked with the test material. The bottles were stoppered and incubated on a shaker. The chemical oxygen demand (COD) was determined in a variant of the ISO method 6060 (closed system with a pressure equaliser / Kelkenberg method, Z. f. Wasser und Abwasserforschung 8, 146 (1975)).
SAMPLING
- Sampling frequency: sampled on day 7, 14, 21 and 28
CONTROL AND BLANK SYSTEM
- Inoculum blank: yes, 3 replicates
- Abiotic sterile control: no
- Toxicity control: no - Reference substance:
- acetic acid, sodium salt
- Remarks:
- concentration: 100 mg ThOD/L
- Parameter:
- % degradation (O2 consumption)
- Value:
- 90
- Sampling time:
- 28 d
- Remarks on result:
- other: Mean from all test bottles
- Details on results:
- Within the 14-day time window the 60% level was passed. Therefore, the test substance is judged as readily biodegradable.
- Results with reference substance:
- 92% of the reference substance was degraded after 7 days, 101% after 14 and 21 days and 102% after 28 days. The results with the reference substance show that the study is valid according to the ISO Guideline 10708.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Justification for type of information:
- Refer to analogue justification provided in IUCLID section 13.
- Reason / purpose for cross-reference:
- read-across source
- Parameter:
- % degradation (O2 consumption)
- Value:
- 90
- Sampling time:
- 28 d
- Remarks on result:
- other: Mean from all test bottles
- Details on results:
- Within the 14-day time window the 60% level was passed. Therefore, the test substance is judged as readily biodegradable.
- Executive summary:
Within the 14-day time window the 60% level was passed. Therefore, the test substance is judged as readily biodegradable (90% within 28 d, OECD 301 D).
Referenceopen allclose all
Table 1: Degradation (%) of reference substance and test substance
Day |
Reference 1 |
Reference 2 |
Reference Mean |
Test 1 |
Test 2 |
Test mean |
0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
2 |
5.5 |
5.4 |
5.5 |
30.9 |
29.8 |
30.4 |
4 |
24.3 |
24.2 |
24.2 |
52.5 |
52.6 |
52.6 |
7 |
51.6 |
49.6 |
50.6 |
66.8 |
66.7 |
66.7 |
10 |
67.4 |
63.3 |
65.4 |
74.1 |
75.3 |
74.7 |
14 |
79.9 |
75.0 |
77.4 |
80.8 |
82.4 |
81.6 |
16 |
83.3 |
79.3 |
81.3 |
82.5 |
85.9 |
84.2 |
18 |
85.3 |
82.2 |
83.7 |
83.2 |
87.9 |
85.5 |
21 |
89.0 |
85.3 |
87.1 |
84.7 |
89.7 |
87.2 |
23 |
92.3 |
87.4 |
89.8 |
85.0 |
90.7 |
87.8 |
25 |
94.3 |
88.9 |
91.6 |
85.8 |
91.4 |
88.6 |
28 |
96.1 |
91.0 |
93.5 |
86.4 |
94.2 |
90.3 |
29 |
97.1 |
92.1 |
91.3 |
87.3 |
95.3 |
94.6 |
Table 1: Oxidation of the test substance
sample |
% oxidation |
|||
|
day 7 |
day 14 |
day 21 |
day 28 |
a) |
83 |
91 |
95 |
96 |
b) |
71 |
80 |
86 |
86 |
c) |
69 |
82 |
87 |
88 |
mean |
74 |
84 |
89 |
90 |
Description of key information
Readily biodegradable (94.6% within 28 d, OECD 301 B, CO2 evolution)
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
Two studies are available, in which the ready biodegradability of the target substance Fatty acids, C18-unsaturated, 2-hexyldecyl ester was investigated according to internationally accepted OECD testing guidelines. The key study was conducted with the target substance and the supporting study was conducted with the structurally related source substance fatty acids, C16-18, 2-hexyldecyl esters (CAS 101227-09-2). The source substance is characterized by similar fatty acid and alcohol components and is therefore considered a suitable representative for the assessment of the ready biodegradability of the target substance. Read-across was conducted in accordance with Regulation (EC) No 1907/2006 Annex XI, 1.5 and a detailed justification of the analogue approach is provided in IUCLID section 13.
In the key study, the target substance (10 – 20 mg/L DOC) was inoculated with activated sludge (> 10E+06 CFU/mL) for 28 d according to OECD guideline 301 B. The amount of CO2 produced by the degradation of the substance was trapped with Ba(OH)2 and precipitated as BaCO3 and quantified by back titration of the remaining Ba(OH)2 in the absorber flasks using HCl and phenolphthalein as indicator. Biodegradability was expressed in percent CO2 of theoretical CO2 (ThCO2).
The 60% level was reached within the 10-d window. Biodegradation reached a mean of 93.5% by Day 28 and 94.6% by Day 29. Therefore, the test substance is regarded as readily biodegradable according to the OECD criteria.
In the supporting study, 100 mg/L test item (based on ThOD/L) was inoculated with 2.5 – 3.5 mg/L activated sludge for 28 d in a closed bottle test according to OECD guideline 301 D. Biodegradation was quantified and expressed in terms of O2 consumption.
The 60% pass level was attained within the 14-d window and a mean degradation of 90% was recorded after 28 d. Therefore, the substance is readily biodegradable according to the OECD criteria.
Based on the structural similarities between the target and source substance and the reliable results on the target substance, it can be concluded that Fatty acids, C18-unsaturated, 2-hexyldecyl ester is readily biodegradable according to OECD criteria.
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