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EC number: 253-462-2 | CAS number: 37321-62-3
- 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:
- 22 Oct - 25 Oct 2018
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
Data source
Referenceopen allclose all
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 019
- Report date:
- 2019
- Reference Type:
- other: Analytical report
- Title:
- Unnamed
- Year:
- 2 019
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Groupe interministeriel des produits chimiques (15 Nov 2018)
Test material
- Reference substance name:
- Dodecanoic acid, ester with 1,2-propanediol
- EC Number:
- 253-462-2
- EC Name:
- Dodecanoic acid, ester with 1,2-propanediol
- Cas Number:
- 37321-62-3
- Molecular formula:
- C15H30O3 C27H52O4
- IUPAC Name:
- Dodecanoic acid, ester with 1,2-propanediol
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 0.95; 1.53; 2.44; 3.91; 6.25 and 10 mg/L
- Sampling method: Lauroglycol monoester and Lauroglycol diester was measured at 0 and 48 hours. Diester: 2 mL of sample were pipetted into a 15 mL conical bottom glass tube and 2 mL of ethyl acetate were added. Samples were vortexed and layers were allowed to separate for one minute. 1 mL of the upper layer was pipetted into a GCMS vial. Monoester: 2 mL of sample were pipetted into a 15 mL conical bottom glass tube and 2 mL of hexane were added. Samples were vortexed and centrifuged for 2 min at 1500 rpm. 1 mL of the upper layer was pipetted into a GCMS vial and 50 μL of derivative agent BSTFA + 1 % TMCS were added.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: The test solutions were prepared by water accommodated fractions (WAF) approach according to OECD monograph No. 23. WAFs were prepared individually. Measured quantities of test item were added directly to test medium and mixed for 18 hours to achieve an equilibrated concentration of dissolved and dispersed or emulsified components in the aqueous phase. The test solutions have not been filtered. The test solutions used were therefore emulsions of the test element.
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: waterflea (bred at testing facility)
- Strain/clone: clone 5
- Age of parental stock (mean and range, SD): 6 - 24 hours
CULTURE CONDITIONS:
- Medium: Elendt M4
- Temperature: 20 °C ± 2
- Light/dark cycle: 16 h/8 h
- pH: Between 6 and 9
- Type and amount of food: Pseudokirchneriella subcapitata and Chlorella vulgaris suspensions
- Feeding frequency: daily
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
Test conditions
- Test temperature:
- 20.6 - 20.8 °C
- pH:
- 7.9 - 8.0
- Dissolved oxygen:
- 8.0 - 9.1 mg/L
- Nominal and measured concentrations:
- nominal (loading rates): 0.95; 1.53; 2.44; 3.91; 6.25 and 10 mg/L
measured: see below table 2 under "Any other information on results - Details on test conditions:
- TEST SYSTEM
- Test vessel: glass flasks
- Fill volume: 100 mL size with 50 mL of test solution
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: OECD medium in accordance with OECD 202
- Intervals of water quality measurement: pH, dissolved oxygen and temperature were recorded at the beginning and the end of the test.
OTHER TEST CONDITIONS
- Photoperiod: dark/ light cycle 16/ 8 hours
- Light intensity: 300 lux
EFFECT PARAMETERS MEASURED (with observation intervals if applicable): After 24 and 48 hours, the number of immobile daphnids in each replicates was recorded.
RANGE-FINDING STUDY
- Test concentrations: 1, 10 and 100 mg/L
- Results used to determine the conditions for the definitive study: 100% immobilised daphnids were observed for 10 and 100 mg/L. No immobilisation was dertermined for 1 mg/L. - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
Results and discussion
Effect concentrations
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 6.59 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other:
- Remarks:
- 95% CL: 6.33 - 6.85 mg/L
- Results with reference substance (positive control):
- - Results with reference substance valid?
yes
- Relevant effect levels: EC50 (24h) = 1.851 (95% CL 1.753 – 1.948) - Reported statistics and error estimates:
- The probits method is used for the estimation of the effect concentration.
Any other information on results incl. tables
Table 1: Validity criteria for OECD 202.
Criterion from the guideline |
Outcome |
Validity criterion fulfilled |
In the control, including the control containing the solubilising agent, not more than 10% of the daphnids should have been immobilized. |
0% immobility was recorded after 48 hours exposure |
yes |
The dissolved oxygen concentration at the end of the test should be ≥ 3 mg/L in control and test vessels. |
The dissolved oxygen concentration in the lowest concentration producing the maximum effect at the end of the test was 8.0 mg/L |
yes |
Table 2: Immobilized daphnids 48 hours after exposure
ID |
Target concentration [mg test item.L-1] |
Immobilized daphnids 48 hours after exposure |
Total of immobilized daphnids |
Mean of immobilized daphnids (%) |
|||
Replicates |
|||||||
A |
B |
C |
D |
||||
C05 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
C06 |
0.95 |
0 |
0 |
0 |
0 |
0 |
0 |
C07 |
1.53 |
0 |
0 |
0 |
0 |
0 |
0 |
C08 |
2.44 |
0 |
0 |
0 |
0 |
0 |
0 |
C09 |
3.91 |
0 |
0 |
0 |
0 |
0 |
0 |
C10 |
6.25 |
1 |
1 |
2 |
3 |
7 |
35 |
C11 |
10 |
5 |
5 |
5 |
5 |
20 |
100 |
Table 3: Analytical results
Treatment |
Control |
Test substance |
||||||
ID |
C05 |
C06 |
C07 |
C08 |
C09 |
C10 |
C11 |
|
Actual loading rate [mg test item.L-1] |
0 |
0.92 |
1.72 |
2.41 |
4.03 |
6.19 |
10.29 |
|
0h analyzed concentrati on |
[mg monoester.L-1] |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
0.599 |
0.365 |
[mg diester.L-1] |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
1.981 |
|
48h analyzed concentrati on |
[mg monoester.L-1] |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
[mg diester.L-1] |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
Limit of quantification (LOQ) =0.1 mg.L-1 for monoester, and 0.5 mg.L-1 for diester.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- For further details please refer to “Any other information on results incl. tables”.
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