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EC number: 225-004-1 | CAS number: 4602-84-0
- 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:
- 06 December 2016 - 09 December 2016
- 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
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.3 (Algal Inhibition test)
- Version / remarks:
- 2009
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: All concentration levels and the control
- Sampling method: Samples were taken at the start of the test (0 h, without algae) and at the end of exposure (72 h, with algae) - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: A saturated solution with a nominal loading of 1000 mg/L test item was prepared once with demineralised water at 96 ± 1 hour prior to the start of the exposure. The test item was pipetted on to the surface of the demineralised water and gentle stirring (to avoid formation of an emulsion) was carried out with a magnetic stirrer at room temperature for 96 ± 1 hour. After a separation phase of 1 hour at room temperature the saturated solution was taken from the bottom and was used for testing. Then the components of the dilution water were added to the saturated solution.
- Controls: Dilution water
- Evidence of undissolved material (e.g. precipitate, surface film, etc.): The saturated solution was checked after stirring via laser beam (Tyndall effect) for undissolved test item (formation of an emulsion), which was negative. - Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
- Common name: Green algae
- Strain: HINDÄK, SAG 61.81
- Age of inoculum (at test initiation): 4 days old
- Method of cultivation: Fresh stocks are prepared every month on Z-Agar. Cultures were incubated under continuous light (2590 - 5180 lux).
ACCLIMATION
- Culturing media and conditions (same as test or not): No, cells cultured in nutrient medium Z
- Any deformed or abnormal cells observed: No - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Hardness:
- 0.24 mmol Ca+Mg/L
- Test temperature:
- 22.0 - 22.5°C
- pH:
- Start: 7.35 - 7.86
End: 8.13 - 8.95 - Dissolved oxygen:
- Not reported
- Nominal and measured concentrations:
- Nominal concentrations: 1.00, 3.16, 10.0, 31.6 and 100% of the saturated solution, corresponding to the geometric mean measured test item concentration of 0.0299, 0.0472, 0.0832, 1.42 and 6.37 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 250 mL Erlenmeyer flasks, sealed with cotton wool plugs
- Type: Closed
- Material, size, headspace, fill volume: 100 mL test volume
- Aeration: Not reported
- Initial cells density: 6305 cells/mL
- Control end cells density: 2366235 cells/mL after 72 hours
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
GROWTH MEDIUM
- Standard medium used: Yes (OECD TG 201 medium)
TEST MEDIUM / WATER PARAMETERS
- Culture medium different from test medium: Yes, nutrient medium Z used for culture medium and OECD TG 201 medium used for test medium
OTHER TEST CONDITIONS
- Sterile test conditions: yes
- Adjustment of pH: No
- Photoperiod: Continuous light
- Light intensity and quality: Approximately 4440 to 8880 lux
EFFECT PARAMETERS MEASURED:
- Determination of cell concentrations: Fluorimeter
- Chlorophyll measurement: The cell density was measured daily via Chlorophyll a-fluorescence, excitation at 436 nm, emission at 685 nm.
- Other: Microscopic evaluation of the cells at the start and the end of the incubation period was carried out. The cells were checked for unusual cell shapes, colour differences, differences in chloroplast morphology, flocculation, adherence of algae to test containers and agglutination of algae cells.
The pH-values at the start of exposure were measured in one additional replicate of each test item concentration and the control. At the end of exposure, the pH-values were measured from pooled samples of each test item concentration and the control. The room temperature was measured continuously. Light intensity was measured prior to the start of exposure.
TEST CONCENTRATIONS
- Spacing factor for test concentrations: Square root of 10
- Range finding study: Yes, 72 hours exposure
- Test concentrations: 1, 10 and 100% saturated solution, corresponding to measured concentrations of <0.05, 0.480 and 6.30 mg/L, respectively at the test start (0h), and at the end of exposure (72h) were <0.05, 0.416 and 6.19 mg/L without algae, respectively, and <0.05, 0.250 and 6.12 mg/L with algae, respectively.
- Results used to determine the conditions for the definitive study: Yes, at 1, 10 and 100% saturated solution, the growth rate inhibitions were 1, 4 and 100%, respectively, and the yield inhibitions were 1, 21 and 100%, respectively - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 1.49 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: 95% CL: 0.503-4.46 mg/L
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 1.17 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: 95% CL: 0.413-4.15 mg/L
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 0.083 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.:
- 0.334 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- cell number
- Remarks on result:
- other: 95% CL: 0.240-0.461 mg/L
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 0.079 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- cell number
- Remarks on result:
- other: 95% CL: 0.0606-0.121 mg/L
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 0.047 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- cell number
- Details on results:
- - Exponential growth in the control: Yes
Microscopic evaluation of the cells at the start and end of exposure revealed no morphological abnormalities. - Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- EC50: ErC50 = 0.435 mg/L (95% CL: 0.414-0.458 mg/L), EyC50 = 0.230 (95% CL: 0.179-0.322 mg/L)
- Other: ErC50 valid range: 0.764 mg/L (3xSD = 0.513 mg/L), EyC50 valid range: 0.402 (3xSD = 0.293 mg/L) - Reported statistics and error estimates:
- ECx-values with confidence intervals of growth rate inhibition and for yield inhibition after 72 hours were calculated by sigmoidal dose-response regression. Shapiro-Wilk’s test on normal distribution was calculated with a significance level 0.01. Levene’s test on variance homogeneity was calculated with a significance level 0.01. Monotonicity of Concentration/Response was calculated by trend analysis by contrasts (significance level 0.05). The NOEC and LOEC were determined for growth rate using SD Jonckheere-Terpsta test procedure rate with a significance level 0.05 and for yield using Wiliams Multiple t-test with a significance level 0.05.
- Validity criteria fulfilled:
- yes
- Remarks:
- For the control cultures, the increase of cell growth was 375-fold (≥16-fold) , the mean CV for section-by-section specific growth rates was 27.3% (≤35%) and the CV of average specific growth rates during the whole test period was 0.55% (≤7%).
- Conclusions:
- The EC50-values for inhibition of growth rate (ErC50) and yield (EyC50) after 72 hours were 1.49 and 0.334 mg/L, respectively. The EC10-values for inhibition of growth rate (ErC10) and yield (EyC10) after 72 hours were 1.17 and 0.0785 mg/L, respectively. The NOEC-values of growth rate and yield after 72 hours were 0.0832 and 0.0472 mg/L, respectively.
- Executive summary:
The algal toxicity of the test item was assessed in a 72 -hour static test with green alga Pseudokirchneriella subcapitata. Algae were exposed to 1.00, 3.16, 10.0, 31.6 and 100% of a saturated solution, corresponding to the geometric mean measured test item concentrations of 0.0299, 0.0472, 0.0832, 1.42 and 6.37 mg/L, alongside an untreated control and positive control. The EC50-values for inhibition of growth rate (ErC50) and yield (EyC50) after 72 hours were 1.49 and 0.334 mg/L, respectively. The EC10-values for inhibition of growth rate (ErC10) and yield (EyC10) after 72 hours were 1.17 and 0.0785 mg/L, respectively. The NOEC-values of growth rate and yield after 72 hours were 0.0832 and 0.0472 mg/L, respectively. This study is considered to be reliable without restriction (Klimisch 1) as it is GLP-compliant and was conducted according to OECD 201 and EU C.3.
Reference
Table 1. Mean growth rate and yield after 72 hours
Geometric mean measured test item concentration (mg/L) | Mean growth rate (1/d) | Inhibition of growth rate (%) | Mean yield (cells/mL) | Inhibition of yield (%) |
Control | 1.98 | - | 2359930 | - |
0.0299 | (-) 1.97 | 0 | (-) 2312805 | 2 |
0.0472 | (-) 1.96 | 1 | (-) 2250017 | 5 |
0.0832 | (+) 1.94* | 2 | (+) 2104462 | 11 |
1.42 | (+) 1.20 | 39 | (+) 228807 | 90 |
6.37 | (+) n.a. | 100 | (+) n.a. | 100 |
n.a. = not applicable
* A statistically significant difference was found but an inhibition of 2 % is considered to be not biologically significant.
Description of key information
The EC50-values for inhibition of growth rate (ErC50) and yield (EyC50) after 72 hours were 1.49 and 0.334 mg/L, respectively. The EC10-values for inhibition of growth rate (ErC10) and yield (EyC10) after 72 hours were 1.17 and 0.0785 mg/L, respectively. The NOEC-values of growth rate and yield after 72 hours were 0.0832 and 0.0472 mg/L, respectively.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 1.49 mg/L
- EC10 or NOEC for freshwater algae:
- 1.17 mg/L
Additional information
The algal toxicity of the test item was assessed in a 72 -hour static test with green alga Pseudokirchneriella subcapitata (2017). Algae were exposed to 1.00, 3.16, 10.0, 31.6 and 100% of a saturated solution, corresponding to the geometric mean measured test item concentrations of 0.0299, 0.0472, 0.0832, 1.42 and 6.37 mg/L, alongside an untreated control and positive control. The EC50-values for inhibition of growth rate (ErC50) and yield (EyC50) after 72 hours were 1.49 and 0.334 mg/L, respectively. The EC10-values for inhibition of growth rate (ErC10) and yield (EyC10) after 72 hours were 1.17 and 0.0785 mg/L, respectively. The NOEC-values of growth rate and yield after 72 hours were 0.0832 and 0.0472 mg/L, respectively. This study is considered to be reliable without restriction (Klimisch 1) as it is GLP-compliant and was conducted according to OECD 201 and EU C.3.
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