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EC number: 919-949-5 | CAS number: -
- 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:
- July 28 - Nov 20, 2021
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Version / remarks:
- adopted on March 23, 2006; Annex 5 corrected: July 28, 2011
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.3 (Algal Inhibition test)
- Version / remarks:
- Commission Regulation (EU) 2016/266 of 7 December 2015 amending, for the purpose of its adaptation to technical progress, Regulation (EC) No 440/2008 laying down test methods pursuant to Regulation (EC) No 1907/2006 of the European Parliament and of the Council on the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- PREPARATION OF THE TEST MATERIAL
A preparation with a test item concentration of 100 mg/L was freshly prepared.
For that purpose, the test item was weighed in a calibrated flask and vehicle was added. The preparation was stirred with a magnetic stirrer for 24 hours. Then the formulation was passed through a filter membrane (pore size: 0.2 µm). The filtrate was used for the preparation of the different test item concentrations. The pH was not adjusted. - Analytical monitoring:
- yes
- Details on sampling:
- samples were taken at 0 and 72 h
- Vehicle:
- yes
- Details on test solutions:
- Vehicle:
Nutrient (mg/L)
NH4Cl 15.0
MgCl2 * 6H2O 12.0
CaCl2 * 2H2O 18.0
MgSO4 * 7H2O 15.0
KH2PO4 1.60
FeCl3 * 6H2O 0.0640
Na2EDTA * 2H2O 0.100
H3BO3 0.185
MnCl2 * 4H2O 0.415
ZnCl2 0.00300
CoCl2 * 6H2O 0.00150
CuCl2 * 2H2O 0.00001
Na2MoO4 * 2H2O 0.00700
NaHCO3 50.0
- pH: 7.9-8.6
- Total hardness: 24 mg/L as CaCO3 (calculated)
Preparation of the Test Item:
The test medium (reconstituted water and test item) was freshly prepared.
Therefore, the calibrated flask with test medium was treated in an ultrasonic device for 1 hour. Subsequently, the preparation was stirred with a magnetic stirrer for further 23 hours. Afterwards, the formulation was passed through a membrane filter with a pore size of 0.2 µm. The filtrate was used for the study.
The present study was performed as a static test in open vessels with the following nominal concentrations:
0.05, 0.16, 0.51, 1.63, 5.22, 16.70 and 53.44 mg/L
For the control, reconstituted water was used. - Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
- Common name: Unicellular green algae
- Strain: Pseudokirchneriella subcapitata
- Source (laboratory, culture collection): Pseudokirchneriella subcapitata, strain 61.81 SAG was obtained from „Pflanzenphysiologisches Institut der Universität Göttingen“, Germany.
- Method of cultivation:The permanent algae cultures, the pre-culture and the algae cultures of the study were cultivated in an air-conditioned room with a water temperature of 21.0 – 24.0°C, controlled at
± 2°C. For cultivation, 300 mL Erlenmeyer flasks filled with 100 mL algae suspension were covered with air permeable stoppers (Heinz Herenz Medizinalbedarf GmbH, Hamburg, Germany). The cultures were shaken continuously at about 120 rpm (Universalschüttler SM25, Edmund Bühler GmbH, Hechingen, Germany) and lit between 4440 and 8880 Lux. Fluorescent tubes (Lumilux T5 nws FLH1 HO 80W/840, Osram GmbH, München, Germany) installed above the flasks served for lighting.
ACCLIMATION
- Acclimation period: 72h
- Culturing media and conditions (same as test or not): same as test
- Any deformed or abnormal cells observed: no - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 72 h
- Post exposure observation period:
- -
- Hardness:
- 24 mg/L as CaCO3 (calculated)
- Test temperature:
- 21.0 to 22.2°C
- pH:
- 7.95 to 9.06.
- Nominal and measured concentrations:
- Nominal concentrations: 0.05, 0.16, 0.51, 1.63, 5.22, 16.70 and 53.44 mg/L
Measured @ 0h: < LOD, 0.019, 0.062, 0.192, 0.602, 1.964, 6.518, 20.282 mg/L
Measured @ 24h: < LOD, 0.019, 0.060, 0.191, 0.602, 1.944, 6.165, 20.208 mg/L
Measured [%]
from initial 100.0, 96.8, 99.5, 100.0, 99.0, 94.6, 99.6 - Details on test conditions:
- TEST SYSTEM
- Test vessel: 300 mL Erlenmeyer flasks
- Type: open
- Material, size, headspace, fill volume: 300 mL Erlenmeyer glas flasks filled with 100 mL cell suspension
- Aeration: no
- Initial cells density: 10 000 cells per ml
- Control end cells density: 1 379 910 cells per ml
- No. of vessels per concentration (replicates): 6
- No. of vessels per control (replicates): 6
GROWTH MEDIUM
- Standard medium used: yes
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: reconstituted water according to OECD TG 201
- Culture medium different from test medium: no
OTHER TEST CONDITIONS
- Sterile test conditions: yes
- Adjustment of pH: no
- Light intensity and quality: The mean light intensities were 5390 Lux ± 3.8% and 5402 Lux ± 1.8% prior to and at the end of the exposure period, respectively.
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: electronic particle counter
Nominal concentrations: 0.05, 0.16, 0.51, 1.63, 5.22, 16.70 and 53.44 mg/L - Reference substance (positive control):
- no
- Remarks:
- The accuracy and reliability of the test method is demonstrated periodically as recommended by OECD Guideline No. 201 and the Council Regulation (EC) No. 761/2009. Therefore, potassium dichromate (Art. 104864) was tested as positive control.
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 1.2 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- EC20
- Effect conc.:
- 2.113 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 6.236 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 0.232 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- other: Yield
- Duration:
- 72 h
- Dose descriptor:
- EC20
- Effect conc.:
- 0.418 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- other: Yield
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 1.296 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- other: Yield
- Details on results:
- The recoveries of test item concentrations in all test media without algae ranged from 94.6% to 100.0% from the initially measured concentrations over the time period of 72h and, thus, the test item was stable in the test medium during the study. It can be concluded from the analytical results, that the test item sticks on the algae surface, resulting in a decrease of the recoveries in the samples with algae especially at lower concentrations.
Therefore, it is reasonable to conclude, that the test item is chemically stable in the test medium and that the algae are sufficiently exposed to the test item at concentrations of ± 20% of the initially measured concentrations during the experimental phase of the study. Therefore, the EC values were calculated based on the initially measured concentrations.
Under the conditions of the present study, the test item showed a 72h EC50 of 6.236 mg/L for the growth rate and 1.296 mg/L for the yield of the unicellular green alga Pseudokirchneriella subcapitata. - Results with reference substance (positive control):
- The accuracy and reliability of the test method is demonstrated periodically as recommended by OECD Guideline No. 201 and the Commission Regulation (EU) 2016/266. Therefore, potassium dichromate was tested as positive control.
Study design:
The study comprised of one control group with six replicates and five test item groups with three replicates each. The test item concentrations of 0.1, 0.2, 0.4, 0.8 and 1.6 mg/L were dissolved in 100 mL reconstituted water. The initial algae cell density in each replicate was 10 000 cells per mL. The growth of the algae was determined over an exposure period of 72 hours and compared with the growth of the control group.
Results:
The test item Art. 104864 (Potassium dichromate) showed 72h EC50 of 0.80 mg/L for growth rate and 0.35 mg/L for yield. The EC50 for growth rate and yield obtained in this study are in the range of ± two standard deviation of the current historical means.
Therefore, this study confirms the sensitivity and reliability of the test system used in the test facility. - Validity criteria fulfilled:
- yes
- Conclusions:
- Under the conditions of the present study, the test item showed a 72h EC50of 6.236 mg/L for the growth rate and 1.296 mg/L for the yield of the unicellular green alga Pseudokirchneriella subcapitata.
Reference
Nominal and corresponding analytical concentrations of samples inoculatedwithalgae are given in the following table:
Nominal test item concentration |
Analytical results |
72h [%]3)from initial measured concentration |
|||
0h1) |
72h |
||||
Measured [mg/L] |
[%]3)from nominal concentration |
Measured [mg/L] |
[%]3)from nominal concentration |
||
0.0 |
< LOD |
- |
< LOD |
- |
- |
0.05 |
0.019 |
38.0 |
0.014 |
28.0 |
73.7 |
0.16 |
0.062 |
38.8 |
0.049 |
30.6 |
79.0 |
0.51 |
0.192 |
37.6 |
0.147 |
28.8 |
76.6 |
1.63 |
0.602 |
36.9 |
0.453 |
27.8 |
75.2 |
5.22 |
1.964 |
37.6 |
1.612 |
30.9 |
82.1 |
16.70 |
6.518 |
39.0 |
5.659 |
33.9 |
86.8 |
53.44 |
20.282 |
38.0 |
19.838 |
37.1 |
97.8 |
LOD = Limit of detection (0.003 mg/L)
1)Measured without algae
2)Single measurement
3)Rounded to the first decimal place
The recoveries of concentrationswithalgae slightly decreased especially in the lower concentrations over the time period of 72h from 97.8% down to 73.7% of the initially measured concentrations. The recovery concentration in the highest concentration (53.44 mg/L) with algae remained stable over the testing period. No test item was measured in the control medium.
Nominal and corresponding concentrations of analytical control sampleswithoutalgae are given in the following table:
Nominal test item concentration |
Analytical results |
72h [%]2)from initial measured concentration |
|||
0h |
72h |
||||
Measured [mg/L] |
[%]2)from nominal concentration |
Measured [mg/L] |
[%]2)from nominal concentration |
||
0.0 |
< LOD |
- |
< LOD |
- |
- |
0.05 |
0.019 |
38.0 |
0.019 |
38.0 |
100.0 |
0.16 |
0.062 |
38.8 |
0.060 |
37.5 |
96.8 |
0.51 |
0.192 |
37.6 |
0.191 |
37.5 |
99.5 |
1.63 |
0.602 |
36.9 |
0.602 |
36.9 |
100.0 |
5.22 |
1.964 |
37.6 |
1.944 |
37.2 |
99.0 |
16.70 |
6.518 |
39.0 |
6.165 |
36.9 |
94.6 |
53.44 |
20.282 |
38.0 |
20.208 |
37.8 |
99.6 |
LOD = Limit of detection (0.003 mg/L)
1)Single measurement
2)Rounded to the first decimal place
The recoveries of test item concentrations in all test mediawithoutalgae ranged from 94.6% to 100.0% from the initially measured concentrations over the time period of 72h and, thus, the test item was stable in the test medium during the study. It can be concluded from the analytical results, that the test item sticks on the algae surface, resulting in a decrease of the recoveries in the samples with algae especially at lower concentrations.
Therefore, it is reasonable to conclude, that the test item is chemically stable in the test medium and that the algae are sufficiently exposed to the test item at concentrations of ± 20% of the initially measured concentrations during the experimental phase of the study. Therefore, the EC values were calculated based on the initially measured concentrations.
For the test item Art. 278727 (AP-3-OL) the following EC, LOEC and NOEC values were determined:
Parameter (0-72h) |
Growth rate [mg/L] |
Yield [mg/L] |
EC10 95% confidence interval |
1.200 (0.959 – 1.443) |
0.232 (0.159 – 0.307) |
EC20 95% confidence interval |
2.113 (1.793 – 2.426) |
0.418 (0.317 – 0.519) |
EC50 95% confidence interval |
6.236 (5.673 – 6.859) |
1.296 (1.105 – 1.520) |
LOEC |
0.602 |
0.602 |
NOEC |
0.192 |
0.192 |
Under the conditions of the present study, the test item showed a 72h EC50of 6.236 mg/L for the growth rate and 1.296 mg/L for the yield of the unicellular green alga Pseudokirchneriella subcapitata.
Description of key information
Under the conditions of the present study, the test item showed a 72h EC50of 6.236 mg/L for the growth rate and 1.296 mg/L for the yield of the unicellular green alga Pseudokirchneriella subcapitata.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 6.236 mg/L
- EC10 or NOEC for freshwater algae:
- 1.2 mg/L
Additional information
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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