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EC number: 816-856-0 | CAS number: 5205-01-6
- 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
Link to relevant study record(s)
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2018-10-10 to 2018-10-19
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Freshwater Alga and Cyanobacteria, Growth Inhibition Test)
- Deviations:
- yes
- Remarks:
- No impact on the experimentation results has been recorded.
- Principles of method if other than guideline:
- Deviation: A deviation occurred (EX045115) during experimentation, in the analytical sequence in the autosampler of the GC instrument has been put the vial of the blank instead of the vial of standard check 1. The standard check 1 has been put at the end of the sequence. No impact on the experimentation results has been recorded.
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 2000, 625, 195.31, 61.04, 19.07 mL/L and control.
- Sampling method: Determination of concentration and stability of the test item has been determined using GC technique equipped with FID detector according to validated analytical method (other study report). The sample is considered stable if the measured concentration of the test item at the end of the test has been maintained within ± 20 % to the concentrations at the beginning of the test, according to OECD 201.
- Sample storage conditions before analysis: The samples are stored at room temperature until the beginning of the analytical study. - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: The test item has been prepared at 2000 mg/L in culture medium. The test has been performed on the diluted nominal solutions. The total volume of the culture medium and the concentration of the algae inoculum added were the same in all vessels.
- Controls: Flasks were filled only with culture medium and algae.
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): Culture medium was used.
- Evidence of undissolved material (e.g. precipitate, surface film, etc.): Not reported. - Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
- Common name: Green alga
- Strain: SAG 61.81
- Source (laboratory, culture collection): laboratory culture
ACCLIMATION
- Culturing media and conditions (same as test or not): The algal suspension in breeding has been kept in culture medium in sterile 250 mL Erlenmeyer flasks in the following conditions until the beginning of the test.
Temperature: 23°C ± 2°C
Lighting: lighting greater than 4300 lux
Stirring: Steady with electrical stirrer
- Any deformed or abnormal cells observed: No - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Test temperature:
- 23.0 - 23.2 °C
- pH:
- Control:
test start: 7.84 - 7.84
test end: 7.82 - 7.91
Treatments:
test start: 7.71 - 7.86
test end: 7.19 - 8.10 - Nominal and measured concentrations:
- Nominal: 2000, 625, 195.31, 61.04, 19.07 mg/L
Measured (T=0): 2096.71, 644.76, 199.77, 63.33, 20.11 mg/L
Measured (T=72): 2001.69, 614.70, 189.06, 59.81, 19.08 mg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: Erlenmeyer flask
- Material, size, headspace, fill volume: Glass, 250 mL
- Aeration: No
- Initial cells density: 10^4 cells/mL
- Control end cells density: 1.8 - 1.9 10^6
- No. of organisms per vessel: 10^4 cell/mL
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
GROWTH MEDIUM
- Standard medium used: yes
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: The culture medium has been used as dilution water
OTHER TEST CONDITIONS
- Sterile test conditions: yes
- Adjustment of pH: No
- Photoperiod: Continuous
- Light intensity and quality: Fluorescent lamp 8000 lux
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: Burker chamber, every 24 h
- Other: At the end of the test, microscopic observation was performed to verify a normal and healthy appearance of the inoculum culture and to observe any abnormal appearance of the algae.
TEST CONCENTRATIONS
- Range finding study: yes
- Test concentrations: 5 different concentrations have been prepared and tested with ten-fold dilutions from 100 mg/L to 0.1 mg/L.
- Results used to determine the conditions for the definitive study: yes - Reference substance (positive control):
- no
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 1 295 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 24.5 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- - Exponential growth in the control (for algal test): yes
- Observation of abnormalities (for algal test): no - Validity criteria fulfilled:
- yes
- Conclusions:
- The toxicity of 3-methyl-1,3-butandiol acetate was determined in an OECD 201 study with Pseudokirchneriella subcapitata and in compliance with GLP. Algae were exposed to the test substance in five different concentrations (2000, 625, 195.31, 61.04, 19.07 mg/L) for 72h. Test concentrations were analytically verified via GC-FID. The EC50 and Ec10 values after 72h were determined with 1295 mg/L and 24.5 mg/L based on nominal concentration.
Reference
Table 1: Stability of test item
Nominal conc. |
Measured conc. (mg/L) T=0 |
Measured conc. (mg/L) T=72 h |
% concentration variation |
Stability |
Treated (19.07 mg/L) |
20.11 |
19.08 |
5.11 |
Stable |
Treated (61.04 mg/L) |
63.33 |
59.81 |
5.56 |
Stable |
Treated (195.31 mg/L) |
199.77 |
189.06 |
5.36 |
Stable |
Treated (625.00 mg/L) |
644.76 |
614.70 |
4.66 |
Stable |
Treated (2000.00 mg/L) |
2096.71 |
2001.69 |
4.53 |
Stable |
Table 2: Validity criteria of the test
Parameter |
Days |
Result % |
Validity criteria |
Conformity |
Growth rate |
0-1 |
1.82 |
>0.92 |
CONFORM |
1-2 |
1.25 |
|||
2-3 |
2.13 |
|||
%CVss |
0-1 |
3.88 |
<35% |
|
1-2 |
9.55 |
|||
2-3 |
3.77 |
|||
%CVwp |
0-3 |
0.48 |
<7% |
Table 3: Algae density (cells/mL) in treated groups
Time (days) |
1 |
2 |
3 |
Treated group 2000.00 mg/L |
|||
0 |
1.0 E+04 |
1.0 E+04 |
1.0 E+04 |
1 |
1.3 E+04 |
1.2 E+04 |
1.2 E+04 |
2 |
5.5 E+04 |
5.5 E+04 |
7.2 E+04 |
3 |
6.3 E+04 |
6.7 E+04 |
7.8 E+04 |
Treated group 625.00 mg/L |
|||
0 |
1.0 E+04 |
1.0 E+04 |
1.0 E+04 |
1 |
1.3 E+04 |
1.3 E+04 |
1.5 E+04 |
2 |
1.3 E+05 |
1.4 E+05 |
1.4 E+05 |
3 |
3.2 E+05 |
3.5 E+05 |
3.6 E+05 |
Treated group 195.31 mg/L |
|||
0 |
1.0 E+04 |
1.0 E+04 |
1.0 E+04 |
1 |
2.2 E+04 |
2.2 E+04 |
2.5 E+04 |
2 |
1.8 E+05 |
1.9 E+05 |
1.9 E+05 |
3 |
4.7 E+05 |
4.5 E+05 |
4.6 E+05 |
Treated group 61.04 mg/L |
|||
0 |
1.0 E+04 |
1.0 E+04 |
1.0 E+04 |
1 |
2.7 E+04 |
2.7 E+04 |
2.3 E+04 |
2 |
1.5 E+05 |
1.6 E+05 |
1.7 E+05 |
3 |
8.5 E+05 |
8.5 E+05 |
8.8 E+05 |
Treated group 19.07 mg/L |
|||
0 |
1.0 E+04 |
1.0 E+04 |
1.0 E+04 |
1 |
4.0 E+04 |
3.2 E+04 |
4.3 E+04 |
2 |
1.5 E+05 |
1.7 E+05 |
1.9 E+05 |
3 |
9.3 E+05 |
9.8 E+05 |
1.1 E+06 |
Table 4: Algae density (cells/mL) in control groups
Time (days) |
1 |
2 |
3 |
4 |
5 |
6 |
Control group |
||||||
0 |
1.0 E+04 |
1.0 E+04 |
1.0 E+04 |
1.0 E+04 |
1.0 E+04 |
1.0 E+04 |
1 |
5.8 E+04 |
6.3 E+04 |
6.8 E+04 |
5.7 E+04 |
6.0 E+04 |
6.5 E+04 |
2 |
2.3 E+05 |
1.9 E+05 |
2.3 E+05 |
2.3 E+05 |
2.2 E+05 |
2.0 E+05 |
3 |
1.8 E+06 |
1.8 E+06 |
1.9 E+06 |
1.8 E+06 |
1.9 E+06 |
1.9 E+06 |
Table 5: Inhibition of growth rate (%)
Parameter |
Treated (mg/L) |
||||
2000.00 |
625.00 |
195.31 |
61.04 |
19.07 |
|
%Ir |
62.87 |
32.10 |
26.46 |
14.45 |
11.81 |
Table 6: Determination of pH in control groups
ph Control |
|||||
Replicate |
pH (Start) |
pH (end) |
delta pHc |
Validity criteria |
Conformity |
1 |
7.86 |
7.87 |
0.01 |
delta<1.5 |
VALID |
2 |
7.86 |
7.84 |
0.02 |
||
3 |
7.85 |
7.91 |
0.06 |
||
4 |
7.84 |
7.86 |
0.02 |
||
5 |
7.87 |
7.85 |
0.02 |
||
6 |
7.84 |
7.82 |
0.02 |
Description of key information
ErC50 (72h) = 1295 mg/L
ErC10 (72h) = 24.5 mg/L
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 1 295 mg/L
- EC10 or NOEC for freshwater algae:
- 24.5 mg/L
Additional information
The toxicity of 3-methyl-1,3-butandiol acetate was determined in an OECD 201 study with Pseudokirchneriella subcapitata and in compliance with GLP. Algae were exposed to the test substance in five different concentrations (2000, 625, 195.31, 61.04, 19.07 mg/L) for 72h. Test concentrations were analytically verified via GC-FID. The EC50 and Ec10 values after 72h were determined with 1295 mg/L and 24.5 mg/L based on nominal concentration.
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