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EC number: 202-815-9 | CAS number: 100-06-1
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2017-04-24 to 2017-06-07
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- 2004
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Version / remarks:
- 2008
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- - Duplicate samples taken from each test concentration and the control at the start and at the end of the test (after 48 hours)
- For 48-h stability samples: contents of the respective replicates were combined prior to sampling
- samples frozen at about -20 °C immediately after sampling - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: The highest nominal stock solution of 100 mg/L was prepared with test water just prior to application using ultrasonic treatment for
15 minutes and intense stirring for 15 minutes at room temperature.
- Stock solution: 100 mg/L, prepared with test water just prior to application
- Test media were prepared just before the introduction of the daphnids (i.e., the start of the exposure)
- Controls: Test water without test item tested under the same conditions as the test groups - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Water flea
- Strain/clone: Straus
- Source: Daphnia Collection of the University of Basel/Switzerland in 2015
- Age of parental stock: 6-24 hours old, not first brood progeny
- Feeding during test: no
ACCLIMATION
- Cultivation of the parental daphnids was performed in reconstituted water of the quality identical to the water quality used in the tests (with respect to pH, main ions, and total hardness) - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Post exposure observation period:
- Not applicable
- Hardness:
- 250 mg/L CaCO3 (2.5 mmol/L)
- Test temperature:
- between 20 and 21 °C
- pH:
- - Control: 7.8 - 7.9
- Test item: 7.8 - 7.9 - Dissolved oxygen:
- - Control: 8.5 mg/L
- Test item: 8.5 - 8.7 - Salinity:
- Not measured
- Conductivity:
- Not measured
- Nominal and measured concentrations:
- Nominal: control, 6.25, 12.5, 25, 50 and 100 mg/L
Measured (0 h fresh): < LOQ, n.a., n.a., 25.9, 51.4 and 102 mg/L
Measured (48 h aged): < LOQ, n.a., n.a., 25.2, 50.0 and 99.3 mg/L
n.a. = not analyzed, since these concentrations were below the NOEC determined in this test and thus not relevant for the interpretation of the biological results - Details on test conditions:
- TEST SYSTEM
- Test vessel: 100-mL glass beakers
- Type: covered with glass plates
- Fill volume: 50 mL
- Application: Once within 48 h
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- Reconstituted test water (ISO Test water) according to OECD Guideline No. 202
- Aeration prior the test: yes, until oxygen saturation was reached
- Aeration during the test: no
- Temperature: maintained between 20 and 21 °C
OTHER TEST CONDITIONS
- Photoperiod: 16-hour light to 8-hour dark cycle with a 30-minute transition period
- Light intensity: 15 and 17 μmol m-2 s-1
TEST CONCENTRATIONS
- Range finding study
- Results used to determine the conditions for the definitive study: yes - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 75 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- EC0
- Effect conc.:
- 50 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- EC100
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- - Behavioural abnormalities: See following table
- Observations on body length and weight: No body weight and length was determined
- Other biological observations: No
- Mortality of control: No
- Adverse effects control: No immobilisation was observed for control animals
- Any observations that might cause a difference between measured and nominal values: No. All tested concentration levels were clearly dissolved throughout exposure
- Effect concentrations exceeding solubility of substance in test medium: No - Results with reference substance (positive control):
- - Results with reference substance valid: yes
- 24-hour EC50: 1.2 mg/L - Reported statistics and error estimates:
- The EC50 values could not be calculated by Probit Analysis or Moving Average Interpolation due to the steep concentration-effect relationship. Instead, the EC50 values were calculated by linear interpolation of the immobility between the two consecutive test concentrations with
0 and 60 or 85 % immobility after 24 or 48 hours, respectively, on a semi-logarithmic scale. The 95% confidence limits could not be determined. The 24-hour and 48-hour NOEC, EC0 and EC100 were determined directly from the raw data. - Validity criteria fulfilled:
- yes
- Conclusions:
- The test item had acute toxic effects on Daphnia magna in a 48-hour static test. The 48-hour EC50 was calculated to be 75 mg/L (the 95% confidence limits could not be determined).
- Executive summary:
The acute toxicity of the test item on Daphnia magna was determined in a 48-hour static test according to the OECD Guideline for Testing of Chemicals, No. 202 (2004) and the Commission Regulation (EC) No. 440/2008, Part C.2. The nominal test item concentrations tested were 6.25, 12.5, 25, 50 and 100 mg/L. Additionally, a control (test water without test item) was tested in parallel. The measured concentrations of the test item in the test media of the test concentrations from 25 to 100 mg/L were between 102 and 103 % of the nominal values at the start of the test and between 99 and 101 % at the end of the test. Thus, the test item was stable in the test media over the test period of 48 hours. Therefore, the endpoint values were related on the nominal concentrations of the test item. The 48-hour EC50 was calculated to be 75 mg/L (the 95% confidence limits could not be determined). In conclusion, the test item had acute toxic effects on Daphnia magna in a 48-hour static test.
Reference
Table 1: Effect of the test item on the Mobility of Daphnia magna
Nominal Test Item Concentration [mg/L] |
No. of Daphnids Tested |
Immobilized Daphnids after 24 Hours |
Immobilized Daphnids after 48 Hours |
||
No. |
[%] |
No. |
[%] |
||
Control |
20 |
0 |
0 |
0 |
0 |
6.25 |
20 |
0 |
0 |
0 |
0 |
12.5 |
20 |
0 |
0 |
0 |
0 |
25 |
20 |
0 |
0 |
0 |
0 |
50 |
20 |
0 |
0 |
0 (20D) |
0 |
100 |
20 |
12 (2F) |
60 |
17 (3F) |
85 |
Values in parenthesis: number of mobile test animals with adverse effects
A: daphnids trapped at the water surface
B: daphnids sticking together
C: antennae sticking together
D: daphnids discolored/pale
E: spina stuck
F: slower swimming activity
Table 2: Analytical Results for Test Samples
Sampling Day / Sample Age [d/h] |
Nominal Concentration of Test Item Cnom [mg/L] |
Measured Concentration of Test Item x [mg/L] |
Sample Preparation Factor F |
Determined Concentration of Test Item c [mg/L] |
% of Nominal Concentration |
0/0 (fresh) | Control | n.d. | 1.2 | < LOQ | n.a. |
25 | 21.6 | 1.2 | 25.9 | 103 | |
50 | 42.9 | 1.2 | 51.4 | 103 | |
100 | 85.3 | 1.2 | 102 | 102 | |
2/48 (aged) | Control | n.d. | 1.2 | < LOQ | n.a. |
25 | 21 | 1.2 | 25.2 | 101 | |
50 | 41.7 | 1.2 | 50.0 | 100 | |
100 | 82.8 | 1.2 | 99.3 | 99 |
n.d. = no test item detected
n.a. = not applicable
LOQ: 0.23 mg/L
Remark: The tabulated values of the samples represent rounded results obtained by calculation using the exact raw data.
Description of key information
An EC50 of 75 mg/L (48 h) was determined with a short-term toxicity test in daphnia.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 75 mg/L
Additional information
The acute toxicity of the test item on Daphnia magna was determined in a 48-hour static test according to the OECD Guideline for Testing of Chemicals, No. 202 (2004) and the Commission Regulation (EC) No. 440/2008, Part C.2. The nominal test item concentrations tested were 6.25, 12.5, 25, 50 and 100 mg/L. Additionally, a control (test water without test item) was tested in parallel. The measured concentrations of the test item in the test media of the test concentrations from 25 to 100 mg/L were between 102 and 103 % of the nominal values at the start of the test and between 99 and 101 % at the end of the test. Thus, the test item was stable in the test media over the test period of 48 hours. Therefore, the endpoint values were related on the nominal concentrations of the test item. The 48-hour EC50 was calculated to be 75 mg/L (the 95% confidence limits could not be determined). In conclusion, the test item had acute toxic effects on Daphnia magna in a 48-hour static test.
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