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EC number: 614-257-7 | CAS number: 68071-40-9
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 19 Sep - 06 Oct 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 017
- Report date:
- 2017
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- 13 Apr 2004
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Landesanstalt für Umwelt, Messungen und Naturschutz Baden-Württemberg, Germany (10 Dec 2015)
Test material
- Reference substance name:
- Reaction product of 2-Propenoic acid and Oxirane, mono[(C12-16-alkyloxy)methyl] derivs.
- EC Number:
- 614-257-7
- Cas Number:
- 68071-40-9
- Molecular formula:
- C18H34O4, C20H38O4 and C22H42O4 (mainly)
- IUPAC Name:
- Reaction product of 2-Propenoic acid and Oxirane, mono[(C12-16-alkyloxy)methyl] derivs.
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: Control and limit concentration of 10.0 mg/L (nominal)
- Sampling method: Analytical samples were taken from the test item loading rates and control at test start (0 h), after 24 h from fresh and aged solutions, and after 48 h from aged solutions. For each sampling also a retain sample was taken.
- Sample storage conditions before analysis: All samples were stored deep frozen until they were transferred to the analytical laboratory.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: The test item is a UVCB consisting of compounds with low water solubilities. Therefore, the test item was applied as water accommodated fraction (WAF) after filtration. A stock solution was prepared by directly weighing 10 mg test item into 1000 mL test medium. This stock solutions was stirred in the dark at room temperature for 24 h (based on the OECD Series on Testing and Assessment N° 23). The solution was clear and transparent. After 24 h of stirring, insoluble particles of the test item were separated from the liquid phase by filtration through a filter with ≤ 0.45 µm mean pore size (according to OECD Series on Testing and Assessment N° 23). Transfer of undissolved test item was avoided. The resulting filtrate was used as application solution. The preparation was repeated after 24 h.
- Controls: 4 replicates without test item.
- Evidence of undissolved material: The solution was clear and transparent.
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: water flea
- Strain/clone: clone V
- Source: Federal Environment Agency, Berlin, Germany
- Age of parental stock (mean and range, SD): Freshly hatched daphnia < 24 h old were used for the test.
- Breeding conditions: D. magna was bred as single culture (1 daphnid per 100 mL) in Elendt M4 medium. The pH-value of the aerated water was within a range of 6.0 - 9.0. The dissolved oxygen was above 60% saturation and the total hardness 140 - 250 mg/L (as CaCO3), corresponding to 7.8 - 14 ° dH. The daphnia were reared at a temperature of 20 ± 2 °C in a climatic chamber with 16 h of illumination and 8 h of darkness. The medium was changed three times per week.
- Food type during breeding: The animals were fed with single cell green algae.
- Frequency: At least three times a week.
- Feeding during test: No.
METHOD FOR PREPARATION AND COLLECTION OF EARLY INSTARS OR OTHER LIFE STAGES
A pipette was used to separate the young daphnia from the adults.
Study design
- Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
Test conditions
- Hardness:
- 13 ° dH = 232 mg/L CaCO3
- Test temperature:
- 20.5 ± 0.9 °C
- pH:
- 7.92 ± 0.09
- Dissolved oxygen:
- 8.8 ± 0.3 mg/L
- Nominal and measured concentrations:
- control and 10.0 mg/L (nominal)
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 100 mL glass beakers filled with 50 mL test medium.
- Renewal rate of test solution: 24 h (1 time during test).
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- Culture medium different from test medium: Culture medium same as test medium (Elendt M4).
- Intervals of water quality measurement: The test temperature and the pH-values as well as the oxygen concentration of the test solutions were measured at all test item loading rates at t = 0 h and t = 24 h in fresh test solutions and after t = 24 h and t = 48 h in aged test solutions in one separate replicate per test item loading rate without test organisms.
OTHER TEST CONDITIONS
- Photoperiod: 16 h light/ 8 h dark
EFFECT PARAMETERS MEASURED:
- Immobilisation: after 24 and 48 h
RANGE-FINDING STUDY
- Results used to determine the conditions for the definitive study: Based on the results of a non-GLP range-finding test a limit test with 10.0 mg/L and a control were tested in the definite test. - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
Results and discussion
Effect concentrationsopen allclose all
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EL50
- Effect conc.:
- > 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- WAF
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- NOELR
- Effect conc.:
- >= 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- WAF
- Basis for effect:
- mobility
- Details on results:
- After 24 and 48 h of exposure no immobilization was observed in the control and 10.0 mg/L loading rate. Since no immobilization occurred during the test, no statistical analysis was performed. The EL50 could not be determined and the NOELR was derived from the highest loading rate tested at which the immobilization was not higher than the allowed control immobilization (≤ 10%).
- Results with reference substance (positive control):
- - Results with reference substance valid? Yes, the results comply with OECD 202 and are in line with historical data.
- Relevant effect levels: EC50 (24 h) = 1.0 - 2.0 mg/L potassium dichromate
- Other: The reference test dates 20 Sep 2016. - Reported statistics and error estimates:
- Since no immobilisation occurred during the test, no statistical analysis was performed.
The NOELR was established based on the highest loading rate at which the immobilisation is not higher than the allowed control immobilisation (≤ 10% immobilisation).
Any other information on results incl. tables
ANALYTICAL RESULTS
The test item is a UVCB consisting of several components with similar chemistry. No adequate method for a sufficiently accurate quantitative analysis of the individual components was available. As indication of the concentration of the test item in the respective test solutions, the content of total organic carbon (TOC) in the solutions was measured. In addition, the TOC content of the test item as a bulk material was determined.
TOC analysis proved the presence of the test item in the solutions but was found to be unsuitable for quantitative purposes. Thus, the effects were evaluated based on the nominal loading rates.
TOC analysis showed that the measured concentrations of the fresh samples ranged from 64.5 – 147% of the nominal loading rate. In the aged samples the measured content was 147% of the nominal loading rate (Table 1).
Table 1. TOC measurement.
Test Item Loading rate Nominal [mg/L] |
TOC content Nominal [mg/L]1) |
Sampling |
TOC measured in test solution |
||
[mg/L]* |
% of nominal |
Geometric mean [%] |
|||
Control |
0 |
0 h fresh 24 h fresh 48 h aged |
< LOQ < LOQ < LOQ |
- |
- |
10.0 |
6.82 |
0 h fresh 24 h fresh 48 h aged |
4.4 10.0 10.0 |
64.5 147 147 |
125 |
- = Not calculated; n.d. = not detectable; LOQ = 0.30 mg/L TOC
1)= Based on analysed TOC-content of test item (mass of carbon was 68.2% of total mass)
*= Control corrected.
Applicant's summary and conclusion
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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