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EC number: 947-760-8 | 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
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- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
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- 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
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 20 Feb - 7 Jun 2018
- Reliability:
- 1 (reliable without restriction)
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- 2-ethylhexyl 12-hydroxyoctadecanoate
- EC Number:
- 249-793-7
- EC Name:
- 2-ethylhexyl 12-hydroxyoctadecanoate
- Cas Number:
- 29710-25-6
- Molecular formula:
- C26H52O3
- IUPAC Name:
- 2-ethylhexyl 12-hydroxyoctadecanoate
- Test material form:
- other: oil
- Details on test material:
- a-ethyl-hexyl-oxystearate
Constituent 1
- Specific details on test material used for the study:
- Batch A9859
DOM July 5 2016
Recertification July 2018
Study design
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- sewage, predominantly industrial, adapted
- Details on inoculum:
- Source The source of test organisms was activated sludge freshly obtained from a municipal sewage treatment plant: 'Waterschap Aa en Maas', 's-Hertogenbosch, The Netherlands, receiving predominantly domestic sewage.
Treatment The freshly obtained sludge was kept under continuous aeration until further treatment. Before use, the sludge was coarsely sieved (1 mm) and washed with mineral medium. After treatment the concentration of suspended solids (SS) was determined to be 3 g/L in the concentrated sludge as used for the test. The magnetically stirred sludge was used as inoculum at the amount of 3 mL per litre of mineral medium, leading to a SS concentration of 8 mg/L. - Duration of test (contact time):
- >= 28 d
Initial test substance concentration
- Initial conc.:
- >= 15.3 mg/L
- Based on:
- TOC
Parameter followed for biodegradation estimation
- Parameter followed for biodegradation estimation:
- CO2 evolution
Reference substance
- Reference substance:
- other: silica
Results and discussion
% Degradationopen allclose all
- Key result
- Parameter:
- % degradation (CO2 evolution)
- Value:
- >= 52
- Sampling time:
- 28 d
- Key result
- Parameter:
- % degradation (CO2 evolution)
- Value:
- >= 58
- Sampling time:
- 72 h
- Details on results:
- The relative biodegradation values calculated from the measurements performed during the test period revealed 52% and 58% biodegradation of the test substnace (based on ThCO2), for the duplicate vessels tested. Thus, the criterion for ready biodegradability (at least 60% biodegradation) was not met.
In the silica blank, slightly higher background CO2 production was observed. The test item bottles were compared with the silica blanks.
In the toxicity control, the test substance was found not to inhibit microbial activity.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- inherently biodegradable
- Conclusions:
- In conclusion, the test substance was not readily biodegradable under the conditions of the modified Sturm test presently performed. However, since the results of the present test indicate that the pass level criterion was almost fulfilled the results can be used to indicate inherent biodegradability.
- Executive summary:
The objective of the study was to evaluate the test item test substance for its ready biodegradability in an aerobic aqueous medium with microbial activity introduced by inoculation with activated sludge.
The study procedures described in this report were in compliance with the OECD guideline No. 301 B, 1992. At the request of the Sponsor, the test item was coated on silica particles. Additional blanks were included to correct for the possible effects of using silica.
The test substance was a clear yellowish liquid (UVCB) and was not sufficiently soluble to allow preparation of an aqueous solution at a concentration of 1 g/L. The Total Organic Carbon (TOC) content of the test item was determined to be 78.61%. Based on the TOC content the ThCO2of the test item was calculated to be 2.88 mg CO2/mg. The test item was tested in duplicate at a target concentration of 15.3 mg/L, corresponding to 12 mg TOC/L.
The study consisted of eight bottles:
· 2 inoculum blanks (no test item),
· 2 silica blanks (silica, no test item),
· 2 test bottles (silica, test material),
· 1 procedure control (sodium acetate) and
· 1 toxicity control (silica, test material and sodium acetate).
Aliquots of 34.3 µL were pipetted directly onto weighed amounts of silica in clear glass weighing bottles. After careful mixing, the silica containing the test item was added directly to the 2 litre test bottles containing medium with microbial organisms and mineral components. Subsequently, Milli-RO water was added to each weighing bottle containing the silica in order to quantitatively add all silica to the test medium.The test solutions were continuously stirred during the test, to ensure optimal contact between the test item and the test organisms.Test duration was28 days for the inoculum blank, silica blank, and test item (last CO2measurement on day 29) and 14 days for the procedure and toxicity control (last CO2measurement on day 15).
The relative biodegradation values calculated from the measurements performed during the test period revealed 52% and 58% biodegradation of test material (based on ThCO2), for the duplicate vessels tested. Thus, the criterion for ready biodegradability (at least 60% biodegradation) was not met.
In the silica blank, slightly higher background CO2production was observed. The test item bottles were compared with the silica blanks.
In the toxicity control, the test material was found not to inhibit microbial activity.
Since all criteria for acceptability of the test were met, this study was considered to be valid.
In conclusion, the test material was not readily biodegradable under the conditions of the modified Sturm test presently performed. However, since the results of the present test indicate that the pass level criterion was almost fulfilled the results can be used to indicate inherent biodegradability.[1]
[1]OECD Guidelines For The Testing Of Chemicals. Revised Introduction To The OECD Guidelines For Testing Of Chemicals, Section 3, Part 1, Chapter 2.5, Paragraph 36. (adopted July 23 March 2006).
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