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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
Toxicity to aquatic algae and cyanobacteria
Administrative data
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 16 Oct - 19 Oct 2018
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 019
- Report date:
- 2019
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Freshwater Alga and Cyanobacteria, Growth Inhibition Test)
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- interministerial group of chemical products (GIPC)
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, 3.05, 9.76, 31.25 and 100 mg/L at 0 and 72 hours.
- Sampling method: Test item solutions and control were sampled and immediately analysed. 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: Test solutions were prepared individually 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 24 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.
- Controls: yes (test medium)
Test organisms
- Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
- Source (laboratory, culture collection): The algal stock culture was provided by the CCAP (Culture Collection of Algae and Protozoa), reference CCAP 1405/1.
- Method of cultivation: The Pseudokirchneriella subcapitata stock culture was maintained on sloped agar tubes at 4°C and regularly transferred to fresh medium at the laboratory. A pre-culture was prepared from the stock culture and maintained in an exponential growth by successive transfers every 3 to 4 days.
ACCLIMATION
- Culturing media and conditions (same as test or not): OECD medium
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
Test conditions
- Test temperature:
- 21.63 - 22.69 °C
- pH:
- 7.66 - 8.81
- Nominal and measured concentrations:
- nominal (loading rates): 0.95, 3.05, 9.76, 31.25 and 100 mg/L
measured: see below table 2 under "Any other information on results - Details on test conditions:
- TEST SYSTEM
- Test vessel: glass Erlenmeyer flasks of 250 mL
- Type (delete if not applicable): closed with air-permeable stoppers made of polyether foam
- Fill volume: 80 mL
- Initial cells density: 5000 cells per mililiters
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
- other: The flasks were repositioned each day to minimize differences in test conditions.
GROWTH MEDIUM
- Standard medium used: OECD medium in accordance with OECD 201
TEST MEDIUM / WATER PARAMETERS
- Intervals of water quality measurement: pH was recorded at the beginning and the end of the test.
OTHER TEST CONDITIONS
- Photoperiod: continuous illumination
- Light intensity and quality: 7700 - 85000 lux
- other: Algae were maintained suspended under continuous orbital stirring.
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: Cell biomass was measured every day in each flask using an electronic particle counter.
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 3.2
- Range finding study
- Test concentrations: 0.02, 0.2, 2 and 20 mg/L
- Results used to determine the conditions for the definitive study: Growth rate inhibition: 7.59% Inhibition at 0.02 mg/L, 2.91% Inhibition at 0.2 mg/L, 3.65% at 2 mg/L and 56.01% at 20 mg/L - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 9.76 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 31.25 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other:
- Remarks:
- 95% CL 27.93 - 33.29 mg/L
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 14.96 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other:
- Remarks:
- 95% CL 11.86 – 26.98 mg/L
- Details on results:
- - Observation of abnormalities (for algal test): No abnormal appearance of the algae at the start and at the end of the test for all concentrations.
- Results with reference substance (positive control):
- - Results with reference substance valid? yes
- EC50 (72h) = 1.07 mg/L (95% CL 0.94 – 1.2); starting date 18 May 2018 - Reported statistics and error estimates:
- EC10 (Effect Concentration for 10% effect), EC50 and confidence limits were obtained by calculation according to Regtox® Macro (“Vindimian”), using the Hill model.
The statistical evaluation (NOEC - No Observed Effect Concentration - and the LOEC - Lowest Observed Effect Concentration - determination) was conducted with R software.
Any other information on results incl. tables
The components were not detectable at low concentrations and the evaluation of the endpoints were based on nominal loading rates.
Table 1: Validity criteria for OECD 201.
Criterion from the guideline |
Outcome |
Validity criterion fulfilled |
The biomass in the control cultures should have increased exponentially by a factor of at least 16 within the 72-hour test period. |
The growth multiplication factor in the control within the 72-hour test period was 288. |
yes |
The mean coefficient of variation for section-by-section specific growth rates (days 0-1, 1-2 and 2-3, for 72-hour tests) in the control cultures must not exceed 35% |
The mean coefficient of variation for section-by-section specific growth rates (days 0-1, 1- 2 and 2-3) in the control was 11.2%. |
yes |
The coefficient of variation of average specific growth rates during the whole test period in replicate control cultures must not exceed 7% in tests with Pseudokirchneriella subcapitata and Desmodesmus subspicatus. For other less frequently tested species, the value should not exceed 10%. |
The coefficient of variation of the average specific growth rates in the control during the whole test period was less than 6.16%. |
yes |
Table 2: Results for the controls after 72h
|
Number of cells at 0 h |
Measure at 24 h (cells / mL) |
Measure at 48 h (cells / mL) |
Measure at 72 h (cells / mL) |
Specific growth rate 0 h – 24 h |
Specific growth rate 24 h – 48 h |
Specific growth rate 48 h – 72 h |
Growth rate (day-1) after 72h |
CV growth 72h (%) |
Yield (cells / mL) after 72h |
CV yield 72h (%) |
Control |
5000 |
33112 |
210200 |
1705000 |
1.890 |
1.848 |
2.093 |
1.944 |
6.2 |
1700000 |
28.7 |
5000 |
23328 |
129500 |
1133000 |
1.540 |
1.714 |
2.169 |
1.808 |
1128000 |
|||
5000 |
23432 |
137700 |
738800 |
1.545 |
1.771 |
1.680 |
1.665 |
733800 |
|||
5000 |
26112 |
243400 |
1629000 |
1.653 |
2.232 |
1.901 |
1.929 |
1624000 |
|||
5000 |
33032 |
247400 |
1702000 |
1.888 |
2.014 |
1.929 |
1.943 |
1697000 |
|||
5000 |
24616 |
179900 |
1743000 |
1.594 |
1.989 |
2.271 |
1.951 |
1738000 |
|||
Mean |
5000 |
27272 |
191350 |
1441800 |
1.685 |
1.928 |
2.007 |
1.873 |
1436800 |
Table 3: Results for all test concentrations after 72h
Nominal loading rates (mg test item/L after 72h) |
Number of cells at 0 h |
Measure at 24 h (cells / mL) |
Measure at 48 h (cells / mL) |
Measure at 72 h (cells / mL) |
Growth rate (day-1) after 72h |
CV growth 72h (%) |
Growth rate inhibition (%) compared to control after 72h |
Yield (cells / mL) after 72h |
CV yield 72h (%) |
Yield inhibition (%) compared to control after 72h |
0.950 |
5000 |
33144 |
344800 |
1453000 |
1.891 |
9.1 |
-0.92 |
1448000 |
50.0 |
-0.78 |
5000 |
29952 |
137600 |
2412000 |
2.060 |
-9.94 |
2407000 |
-67.53 |
|||
5000 |
34920 |
142800 |
856800 |
1.715 |
8.48 |
851800 |
40.72 |
|||
Mean |
5000 |
32672 |
208400 |
1573933 |
1.888 |
-0.79 |
1568933 |
-9.20 |
||
3.050 |
5000 |
22968 |
391500 |
865300 |
1.718 |
9.2 |
8.30 |
860300 |
46.8 |
40.12 |
5000 |
36248 |
265800 |
2421000 |
2.061 |
-10.01 |
2416000 |
-68.15 |
|||
5000 |
25264 |
253600 |
1719000 |
1.947 |
-3.91 |
1714000 |
-19.29 |
|||
Mean |
5000 |
28160 |
303633 |
1668433 |
1.908 |
-1.87 |
1663433 |
-15.77 |
||
9.760 |
5000 |
22488 |
133300 |
1123000 |
1.805 |
3.6 |
3.66 |
1118000 |
18.0 |
22.19 |
5000 |
17272 |
128500 |
791500 |
1.688 |
9.89 |
786500 |
45.26 |
|||
5000 |
16224 |
140400 |
1073000 |
1.790 |
4.47 |
1068000 |
25.67 |
|||
Mean |
5000 |
18661 |
134067 |
995833 |
1.761 |
6.01 |
990833 |
31.04 |
||
31.700 |
5000 |
5888 |
1280 |
127100 |
1.079 |
13.9 |
42.43 |
122100 |
44.4 |
91.50 |
5000 |
14913 |
1240 |
62480 |
0.842 |
55.07 |
57480 |
96.00 |
|||
5000 |
0* |
1280 |
67760 |
0.869 |
53.62 |
62760 |
95.63 |
|||
Mean |
5000 |
6934 |
1267 |
85780 |
0.930 |
50.37 |
80780 |
94.38 |
||
100.420 |
5000 |
0* |
1760 |
120 |
0.000 |
- |
100.00 |
0 |
- |
100.00 |
5000 |
0* |
17400 |
160 |
0.000 |
100.00 |
0 |
100.00 |
|||
5000 |
0* |
1400 |
80 |
0.000 |
100.00 |
0 |
100.00 |
|||
Mean |
5000 |
0 |
6853 |
120 |
0.000 |
100.00 |
0 |
100.00 |
Table 4: Analytical results
Treatment |
Control |
Test substance |
|||||
ID |
C06 |
C07 |
C08 |
C09 |
C10 |
C11 |
|
Actual loading rate [mg test item.L-1] |
0 |
0.95 |
3.05 |
9.76 |
31.7 |
100.42 |
|
0h analyzed concentrati on |
[mg monoester.L-1] |
< LOQ |
< LOQ |
< LOQ |
0.32 |
3.66 |
16.17 |
[mg diester.L-1] |
< LOQ |
< LOQ |
< LOQ |
1.95 |
8.91 |
25.37 |
|
72h analyzed concentrati on [mg test item.L-1] |
[mg monoester.L-1] |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
0.26 |
[mg diester.L-1] |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
4.81 |
Limit of quantification (LOQ) =0.1 mg.L-1 for monoester, and 1 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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