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EC number: 222-426-8 | CAS number: 3468-11-9
- 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
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:
- 2016-12-15 to 2017-03-17
- 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)
- Version / remarks:
- 2011
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- - sampling method: analytical samples were taken in the main at 0h (initial value), after 24h, 48h and 72h from aged solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION:
- Stock solution: 18.8 mg of test item was mixed with test AAP-medium and homogenised by shaking for 5 minutes of ultrasonication; Final volume is 1000mL
- Dilutions of stock solution: 3 dilutions were made from the stock solution with test AAP-medium, to reach a final volume of 500mL per dilution
- Controls: test water without addition of the test item - Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
- Common name: Pseudokirchneriella subcapitata
- Strain: No. 61.81 SAG
- Source: available in study report
- Age of inoculum (at test initiation): 3 to 4 days old pre-culture - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Post exposure observation period:
- Microscopic evaluation of the cells at the end of exposure (morphological appearance check)
- Test temperature:
- 22.4 – 23.0 °C
- pH:
- pH range of control (0h-72h): 7.28 - 7.84
pH range of samples (0h-72h): 7.34 - 7.91 - Nominal and measured concentrations:
- Nominal concentrations tested (spaced by a factor of 2.5): 18.8, 7.52, 3.01, 1.20, 0.481 mg/L and a control
Measured concentrations (geometric mean concentrations): 6.54, 2.56, 1.03, 0.373, 0.152 mg/L and n.d. - Details on test conditions:
- TEST SYSTEM
- Test vessel: Erlenmeyer flasks of 100mL volume with aluminium caps filled with 50mL test solution
- Initial cells density: 0.5 x 10^4 cells/mL
- Control end cells density: 33.22 x 10^4 cells/mL
- No. of organisms per vessel: 0.5 x 10^4 cells/mL, employed for the individual replicates
- No. of treatment groups: 6 (5 dose rates of the test item and a control)
- No. of replicates: 3 for each test item concentration and 6 for the control
GROWTH MEDIUM
- Standard medium used: yes (according to Annex 3 of OECD 201)
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: OECD AAP-medium
OTHER TEST CONDITIONS
- Sterile test conditions: yes
- Photoperiod: continuous illumination from the side
- Light intensity: 88.8 µE/m2 s
EFFECT PARAMETERS MEASURED: influence of test item on yield and growth rate of organisms
RANGE-FINDING STUDY
- Test concentrations: Control, 100, 10.0, 1.00, 0.100 and 0.0100 mg/L.
- Results used to determine the conditions for the definitive study: after 72 h at termination of the test no inhibition of growth rate or yield was observed for concentrations up to and including 1.00 mg/L. For higher test item concentrations: inhibition of growth rate peaked (reached the highest point) at 142.4 % at a nominal concentration of 100 mg/L and the inhibition of yield peaked at 102.0 % at a nominal concentration of 100 mg/L. - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate tested at least twice a year
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 1.56 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 0.841 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 0.981 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- other: Yield inhibition
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 0.636 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- other: Yield inhibition
- Duration:
- 72 h
- Dose descriptor:
- EC20
- Effect conc.:
- 1.04 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- EC20
- Effect conc.:
- 0.746 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- other: Yield inhibition
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 0.373 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- other: Growth rate and Yield inhibition
- Details on results:
- - Exponential growth in the control (for algal test): yes
- Morphology of algae cells: the cells were considered normal for the control and up to and including a nominal test item concentration of 3.01 mg/L. No cells were observed at 7.52 and 18.8 mg/L nominal test item concentration. - Results with reference substance (positive control):
- - Results with reference substance valid? yes, the EC50 values calculated in this reference test were considered to be within an acceptable range therefore it can be considered that the test organism is sensitive.
- Test rates: static main test with nominal concentrations of 0.0512, 0.128, 0.320, 0.800 and 2 mg/L and control
- Conclusions: significant inhibitory effects were determined for all parameters at test item concentrations of 0.800 mg/L (nominal) and above
- EC50 (growth rate): 1.64 mg/L (nominal); EC50 (yield inhibition): 0.976 mg/L (nominal)
- EC10 (growth rate): 0.695 mg/L (nominal); EC10 (yield inhibition): 0.354 mg/L (nominal) - Validity criteria fulfilled:
- yes
- Conclusions:
- After an exposure of 72 h, the test item was found to inhibit the growth of Pseudokirchneriella subcapitata. The reported EC50-values (based on measured concentrations, geom. mean) are 1.56 mg/L for growth rate inhibition and 0.981 mg/L when yield inhibition was studied. The 72-hour EC10-values (based on measured concentrations, geom. mean) for inhibition of growth rate and yield were 0.841 and 0.636 mg/L, respectively.
- Executive summary:
For this endpoint, one study is available in which the effect of the test item on growth of freshwater green algae Pseudokirchneriella subcapitata after 72 hours exposure was assessed according to OECD 201. The organisms were exposed over a period of 72 hours to 5 concentrations of the test item (nominal concentrations of: 18.8, 7.52, 3.01, 1.20, 0.481 mg/L and control; corresponding to measured concentrations (geom. mean): 6.54, 2.56, 1.03, 0.373, 0.152 mg/L and n.d.).
The test item was found to inhibit the growth of Pseudokirchneriella subcapitata. The 72-hour EC50-values (based on measured concentrations) for both inhibition of growth rate (ErC50) and yield (EyC50) were 1.56 and 0.981 mg/L. The EC10-values (based on measured concentrations) for inhibition of growth rate and yield after 72 hours were 0.841 and 0.636 mg/L, respectively.
Validity criteria were fulfilled with this test set-up.
Reference
Results non-GLP dose range finding test:
Concentration (mg/L) | % inhibition after 72h | |
Growth rate | Yield | |
Control | 0 | 0 |
0.01 | -7.5 | -29.3 |
0.1 | -8.7 | -37.1 |
1 | -6.3 | -23.8 |
10 | 123.5 | 101.5 |
100 | 142.4 | 102 |
Biological results main study:
Percentage inhibition of growth rate:
Conc. |
% Inhibition of growth rate |
||
[mg/L] |
0 h – 24 h |
0 h – 48 h |
0 h – 72 h |
Control |
0.0 |
0.0 |
0.0 |
0.481 |
-1.8 |
-1.8 |
1.3 |
1.20 |
-10.3 |
-3.6 |
-0.2 |
3.01 |
14.7 |
16.7 |
20.3 |
7.52 |
36.4 |
79.9 |
83.8 |
18.8 |
107.9 |
109.9 |
132.3 |
Average cell number for each sampling time and concentration
Conc. |
Average cell numbers/mL [104/mL] |
|||
[mg/L] |
0 h |
24 h |
48 h |
72 h |
Control |
0.52 |
1.50 |
6.34 |
33.22 |
0.481 |
0.52 |
1.49 |
6.55 |
31.43 |
1.20 |
0.52 |
1.62 |
6.94 |
33.74 |
3.01 |
0.52 |
1.25 |
4.18 |
14.35 |
7.52 |
0.52 |
1.00 |
0.87 |
1.04 |
18.8 |
0.52 |
0.48 |
0.41 |
0.14 |
Analytical results: determination of test item concentrations
Nominal concentration (mg/L) | Sampling | Measured concentration (mg/L) | % of nominal | Geometric mean (mg/L) |
Control | 0h fresh | n.d | ||
24h aged | n.d | |||
48h aged | n.d | |||
72h aged | n.d | |||
0.481 | 0h fresh | 0.436 | 91 | 0.152 |
24h aged | 0.215 | 45 | ||
48h aged | 0.107 | 22 | ||
72h aged | 0.0507 | 11 | ||
1.2 | 0h fresh | 1.08 | 90 | 0.373 |
24h aged | 0.538 | 45 | ||
48h aged | 0.275 | 23 | ||
72h aged | 0.122 | 10 | ||
3.01 | 0h fresh | 2.89 | 96 | 1.03 |
24h aged | 1.51 | 50 | ||
48h aged | 0.723 | 24 | ||
72h aged | 0.368 | 12 | ||
7.52 | 0h fresh | 7.51 | 100 | 2.56 |
24h aged | 3.72 | 49 | ||
48h aged | 1.74 | 23 | ||
72h aged | 0.879 | 12 | ||
18.8 | 0h fresh | 19.3 | 103 | 6.54 |
24h aged | 9.83 | 52 | ||
48h aged | 4.67 | 25 | ||
72h aged | 2.09 | 11 |
Description of key information
For this endpoint, one study is available in which the effect of the test item on growth of freshwater green algae Pseudokirchneriella subcapitata after 72 hours exposure was assessed according to OECD 201.
The 72-hour EC50-values (geometric mean, measured concentrations) for both inhibition of growth rate (ErC50) and yield (EyC50) were 1.56 and 0.981 mg/L. The EC10-values (geometric mean, measured concentrations) for inhibition of growth rate and yield after 72 hours were 0.841 and 0.636 mg/L, respectively.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 1.56 mg/L
- EC10 or NOEC for freshwater algae:
- 0.841 mg/L
Additional information
The organisms were exposed over a period of 72 hours to 5 concentrations of the test item (nominal concentrations of: 18.8, 7.52, 3.01, 1.20, 0.481 mg/L and control. This corresponds to measured concentrations (geom. mean): 6.54, 2.56, 1.03, 0.373, 0.152 mg/L and n.d.).
Validity criteria were fulfilled with this test set-up.
The test item was found to inhibit the growth of Pseudokirchneriella subcapitata.
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