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EC number: 700-319-1 | CAS number: 117646-83-0
- 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
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- The study was conducted between 18 August 2015 and 16 September 2015.
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: 1= Reliable without restriction o GLP guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 015
- Report date:
- 2015
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-{2-[(2-ethylhexyl)oxy]ethoxy}ethyl prop-2-enoate
- Cas Number:
- 117646-83-0
- Molecular formula:
- C15H28O4
- IUPAC Name:
- 2-{2-[(2-ethylhexyl)oxy]ethoxy}ethyl prop-2-enoate
- Test material form:
- other: liquid
- Details on test material:
- Identification:
M120
Physical state/Appearance:
clear colorless liquid
Batch:
NC-5635-01
Purity:
99.4%
Expiry Date:
5 December 2015
Storage Conditions:
room temperature in the dark
Constituent 1
Study design
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic (adaptation not specified)
- Duration of test (contact time):
- 28 d
Initial test substance concentration
- Initial conc.:
- 10 other: mg carbon/L
- Based on:
- DOC
Results and discussion
% Degradation
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 69
- Sampling time:
- 28 d
Any other information on results incl. tables
Definitive Test
Inorganic carbon values for the test item, procedure control, toxicity control and inoculum control vessels at each analysis occasion,
Percentage biodegradation values of the test and reference items and the toxicity control, and Total and Inorganic Carbon values in the culture vessels on Day 0 are all given in the tables below.
Validation Criteria
The total CO2evolution in the inoculum control vessels on Day 28 was 35.98 mg/L and therefore satisfied the validation criterion given in the OECD Test Guidelines.
The IC content of the test item suspension in the mineral medium at the start of the test (see Table 3) was below 5% of the TC content and hence satisfied the validation criterion given in the OECD Test Guidelines.
The difference between the values for CO2production at the end of the test for the replicate vessels was <20% and hence satisfied the validation criterion given in the OECD Test Guidelines.
Biodegradation
Acidification of the test vessels on Day 28 followed by the final analyses on Day 29 was conducted according to thethods specified in the Test Guidelines. This acidification effectively kills the micro-organisms present and drives off any dissolved CO2present in the test vessels. Therefore any additional CO2detected in the Day 29 samples originated from dissolved CO2that was present in the test vessels on Day 28 and hence the biodegradation value calculated from the Day 29 analyses is taken as being the final biodegradation value for the test item.
The results of the inorganic carbon analysis of samples from the first absorber vessels on Day 29 showed a decrease in all replicate vessels with the exception of test item replicate 2 and the toxicity control vessel. This decrease was considered to be due to sampling/analytical variation.
Inorganic carbon analysis of the samples from the second absorber vessels on Day 29 confirmed that no significant carry-over of CO2into the second absorber vessels occurred.
The test item attained 69% biodegradation after 28 days. Under the strict terms and conditions of OECD Guideline No. 301B the test item cannot be considered to be readily biodegradable as the test item failed to satisfy the 10-Day window validation criterion, whereby 60% biodegradation must be attained within 10 days of the biodegradation exceeding 10%. However, the test item has exhibited the potential for rapid biodegradation.
The toxicity control attained 70% biodegradation after 14 days and 105% biodegradation after 28 days thereby confirming that the test item did not exhibit an inhibitory effect on the sewage treatment micro-organisms used in the test. Biodegradation values in excess of 100% were considered to be due to sampling/analytical variation.
Sodium benzoate attained 65% biodegradation after 14 days and 74% biodegradation after 28 days thereby confirming the suitability of the inoculum and test conditions.
Inorganic Carbon Values on Each Analysis Occasion
Day |
Inorganic Carbon (mg IC) |
|||||||||||||
Inoculum Control |
Procedure Control |
Test Item |
Toxicity Control |
|||||||||||
R1 |
R2 |
R1 |
R2 |
R1 |
R2 |
R1 |
||||||||
Abs1 |
Abs 2 |
Abs 1 |
Abs 2 |
Abs 1 |
Abs 2 |
Abs 1 |
Abs 2 |
Abs 1 |
Abs 2 |
Abs 1 |
Abs 2 |
Abs 1 |
Abs 2 |
|
0 |
1.28 |
1.05 |
1.05 |
1.05 |
1.40 |
0.93 |
1.17 |
0.93 |
1.05 |
1.05 |
1.05 |
1.17 |
1.05 |
1.05 |
2 |
7.66 |
- |
8.35 |
- |
2.44 |
- |
23.66 |
- |
9.40 |
- |
10.79 |
- |
32.13 |
- |
6 |
12.34 |
- |
11.65 |
- |
28.83 |
- |
33.45 |
- |
18.45 |
- |
16.95 |
- |
49.82 |
- |
8 |
15.02 |
- |
14.79 |
- |
29.58 |
- |
38.18 |
- |
21.79 |
- |
29.81 |
- |
60.09 |
- |
10 |
13.23 |
- |
16.53 |
- |
35.00 |
- |
36.82 |
- |
27.93 |
- |
37.51 |
- |
64.07 |
- |
14 |
21.08 |
- |
18.70 |
- |
39.44 |
- |
39.10 |
- |
33.89 |
- |
39.33 |
- |
61.77 |
- |
21 |
23.55 |
- |
23.21 |
- |
45.97 |
- |
49.12 |
- |
47.77 |
- |
42.59 |
- |
71.99 |
- |
28 |
30.24 |
- |
28.67 |
- |
49.84 |
- |
54.10 |
- |
50.29 |
- |
48.38 |
- |
83.89 |
- |
29 |
24.38 |
1.51 |
27.50 |
1.51 |
48.21 |
1.63 |
47.76 |
1.51 |
42.42 |
1.51 |
50.10 |
2.44 |
88.81 |
1.74 |
R1 – R2= Replicates 1 and 2
Abs= CO2 absorber vessels
Percentage Biodegradation Values
Day |
% Biodegradation |
||
Procedure Control |
Test Item |
Toxicity Control |
|
0 |
0 |
0 |
0 |
2 |
17 |
7 |
40 |
6 |
64 |
19 |
63 |
8 |
63 |
36 |
75 |
10 |
70 |
59 |
82 |
14 |
65 |
56 |
70 |
21 |
81 |
73 |
81 |
28 |
75 |
66 |
91 |
29* |
74 |
69 |
105 |
* Day 29 values corrected to include any carry-over of CO2 detected in Absorber 2
Total and Inorganic Carbon Values in the Culture Vessels on Day 0
Test vessel |
Total Carbon* (mg/L) |
Inorganic Carbon* (mg/L) |
IC Content (% of TC) |
Test Item 10 mg C/L R1 |
9.26** |
-0.53 |
0 |
Test Item 10 mg C/L R2 |
9.47** |
-0.29 |
0 |
R1 – R2 = Replicates 1 and 2
*Corrected for control values. Negative values are due to measured concentrations being less than control values
**Total carbon value given is the sum of the TC value obtained from analysis and the nominal TC contribution of the test item
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable, but failing 10-day window
- Conclusions:
- The test item attained 69% biodegradation after 28 days. Under the strict terms and conditions of OECD Guideline No. 301B the test item cannot be considered to be readily biodegradable as the test item failed to satisfy the 10-Day window validation criterion, whereby 60% biodegradation must be attained within 10 days of the biodegradation exceeding 10%. However, the test item has exhibited the potential for rapid biodegradation.
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