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EC number: 947-748-2 | 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
- Study period:
- 22 Nov 2017 - 18 Jan 2018
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- Two concentrations were tested but not in duplicates. Respective validity criterion on difference of extremes of replicate cannot be evaluated.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
- Deviations:
- yes
- Remarks:
- Only one vessel per test concentration was set up. The guideline advises that determinations should be carried out at least in duplicates.
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Department of Health of the Government of the United Kingdom, London, United Kingdom
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- natural water: freshwater
- Details on inoculum:
- - Source of inoculum: Surface water was collected from Malmesbury Pond, Sandymoor, Runcorn on 13 November 2017.
- Preparation of inoculum for exposure: The sample was filtered to remove coarse particles and aerated at 22 ± 2°C prior to use. The surface water was then added to test media so as to achieve a final concentration of 100 mL/L of test media.
- Storage length: After preparing the inoculum for exposure, it was areated until 17 November 2018 (start of pre-conditioning period).
- Concentration of surface water: 100 mL surface water per L of test media
- Initial cell/biomass concentration: not reported - Duration of test (contact time):
- 56 d
- Initial conc.:
- 11.6 mg/L
- Based on:
- test mat.
- Initial conc.:
- 23.2 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- CO2 evolution
- Details on study design:
- TEST CONDITIONS
- Composition of medium: according to guideline
- Test temperature: 22 ± 2°C. The temperature slightly exceeded the 24°C upper tolerance limit on Day 21. This deviation was corrected at the time and did not recure during the remainder of the study.
- Photoperiod: continuous darkness
TEST SYSTEM
- Culturing apparatus: 3 L flat bottomed flasks
- Number of culture flasks/concentration: 1
- Method used to create aerobic conditions: CO2-free air was passed through two dreschel bottles, per test vessel, containing barium hydroxide of known concentration and volume.
SAMPLING
- Sampling frequency: Days 1, 3, 5, 8, 10, 14, 19, 23, 28, 35, 42, 49, 56 and 57
CONTROL AND BLANK SYSTEM
- Inoculum blank: yes, two bottles
- Toxicity control: yes, one bottle
- Reference control: yes, one bottle - Reference substance:
- benzoic acid, sodium salt
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 28.5
- Sampling time:
- 28 d
- Remarks on result:
- other: Test concentration: 11.6 mg/L
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 45.1
- Sampling time:
- 28 d
- Remarks on result:
- other: Test concentration: 23.2 mg/L
- Details on results:
- The test item did not fulfill the criteria for ready biodegradability according to OECD criteria (60% of ThCO2 within a 10-d window).
The degradation extent in the toxicity control was 85.5% degradation after 14 days. The test material is therefore considered to have no inhibitory effect on the inoculum according to the criterion of the guideline.
For details on biodegradation rates, please refer to Table 1 in section "Any other information on results incl. tables". - Results with reference substance:
- The reference control achieved 63.8% degradation after 14 d (pass level: 60%). The degradation after 28 d was 71.1%.
- Validity criteria fulfilled:
- yes
- Remarks:
- However the validity criterion on the % difference of extremes of replicates could not be evaluated since two concentrations were tested but not in duplicates. For further details please refer to “Any other information on results incl. tables”.
- Interpretation of results:
- not readily biodegradable
Reference
Table 1: Cumulative degradation
Cumulative degradation [%] |
||||
Day of titration |
Reference substance |
Test item at 11.6 mg/L |
Test item 23.2 mg/L |
Toxicity control |
1 |
22.4 |
* |
* |
3.5 |
3 |
44.0 |
5.5 |
* |
39.1 |
5 |
50.1 |
6.8 |
1.6 |
61.0 |
8 |
54.9 |
11.4 |
19.1 |
71.2 |
10 |
58.0 |
9.6 |
22.2 |
76.5 |
14 |
63.8 |
14.6 |
27.9 |
85.5 |
19 |
66.7 |
19.4 |
35.8 |
94.1 |
23 |
68.9 |
20.9 |
39.7 |
99.4 |
28 |
71.1 |
28.5 |
45.1 |
101.8 |
35 |
70.2 |
32.7 |
51.2 |
111.6 |
42 |
76.4 |
29.8 |
51.9 |
114.9 |
49 |
79.8 |
32.3 |
57.3 |
120.6 |
56 |
83.4 |
31.1 |
58.8 |
122.3 |
57 |
87.2 |
32.1 |
60.6 |
124.5 |
Table 2: Validity criteria
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%. |
cannot be verified since only single vessels were tested per concentration |
n/a |
Percentage degradation of the reference compound has reached the pass levels by day 14. |
63.8% |
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. |
85.5% |
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. |
< 5% |
yes |
The total CO2 evolution in the inoculum blank at the end of the test should not normally exceed 40 mg/L medium. Critical threshold level: 70 mg/L |
50.3 mg/L |
yes; the value is within the critical threshold level of 70 mg/L |
Description of key information
Fatty acids lanolin, di, tri- and tetraesters with pentaerythritol and rape fatty acid is not readily biodegradable according to OECD criteria.
Key value for chemical safety assessment
Additional information
Experimental data is available for the biodegradation of Fatty acids lanolin, di, tri- and tetraesters with pentaerythritol and rape fatty acid. The study was conducted under GLP conditions according to OECD 301B (CO2 evolution). The substance was tested in two different initial concentrations of 11.6 and 23.2 mg/L based on test material. The study deviated from the guideline in that only a single vessel was tested per concentration level. The study was performed under aerobic conditions using surface pond water as inoculum. After 28 days, degradation rates of 28.5% and 45.1% were achieved for the concentration levels of 11.6 mg/L and 23.2 mg/L, respectively. Fatty acids lanolin, di, tri- and tetraesters with pentaerythritol and rape fatty acid is therefore not readily biodegradable according to OECD criteria.
Within this study, microorganism toxicity also was assessed. The toxicity control achieved a degradation rate of 85.5% after 14 d. The substance is therefore considered not inhibitory to microorganisms.
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