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EC number: 944-181-2 | 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

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
- 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)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- no
- Details on sampling:
- No analytical verification or sampling conducted.
- Vehicle:
- no
- Details on test solutions:
- Since the test item is a UVCB (with some constituents likely to be poorly soluble), the test solutions were prepared, separately for each test concentration, through 96-h stirring followed by filtration. The respective amounts of a test item stock solution, prepared in solvent (ethanol) were added to empty glass vessels. So that the total amount of solvent is equal in all test vessels (i.e. equal to that of the highest concentration), the corresponding additional amount of pure solvent was added as well.
After complete evaporation of the solvent (no solvent remaining), the Daphnia medium was added. These mixtures were moderately stirred for 96 h, followed by filtration. The resulting solutions were used as test solutions in the toxicity test.
In the blank controls, pure solvent (ethanol) in a quantity equal to the one used for the highest test concentration was added and evaporated before addition of the Daphnia medium, followed by 96-h stirring and filtration. - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Daphnia magna
- Strain/clone: Straus (1820)
- Source: Not specified
- Age of parental stock (mean and range, SD): Not first brood progeny
- Feeding during test: No
- Food type: NA
- Amount: NA
- Frequency: NA
ACCLIMATION
- Acclimation period: Not specified
- Acclimation conditions (same as test or not): Same as test
- Type and amount of food: Suspension of Desmodesmus subspicatus in Elendt M4 medium with an optical density OD680 of about 15 units.
- Feeding frequency: Not specified
- Health during acclimation (any mortality observed): Not specified
METHOD FOR PREPARATION AND COLLECTION OF EARLY INSTARS OR OTHER LIFE STAGES: Not specified (although age less than 24 hours). - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- 252 mg/L (as CaCO3)
- Test temperature:
- Target: 18 to 22 °C, controlled at ±1 °C
- pH:
- 6 to 9. The pH should normally not vary by more than 1.5 units in one test.
- Dissolved oxygen:
- > 5 mg/L
- Salinity:
- Not specified
- Conductivity:
- <1.5 μS/cm
- Nominal and measured concentrations:
- Nominal (loading rates): 1.94, 4.27, 9.39, 20.7, 45.5 and 100 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 100 mL Glass beaker
- Type (delete if not applicable): Covered with a glass plate.
- Material, size, headspace, fill volume: 50 mL per vessel
- Aeration: No
- No. of organisms per vessel: 20
- No. of vessels per concentration (replicates): 2
- No. of vessels per control (replicates): 3
- No. of vessels per vehicle control (replicates): NA
- Biomass loading rate: Not specified
TEST MEDIUM / WATER PARAMETERS
- Elendt M4 medium as per OECD guideline
OTHER TEST CONDITIONS
- Adjustment of pH: Not conducted
- Photoperiod: 16 hour light.
- Light intensity: Not specified
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : Immobility (24 and 48 hours). Any abnormal behaviour or appearance was noted.
VEHICLE CONTROL PERFORMED: Controls included.
RANGE-FINDING STUDY
- Test concentrations: 1, 10 and 100 mg/L
- Results used to determine the conditions for the definitive study: Yes, results showed high immobility at 100 mg/L. - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
- Duration:
- 48 h
- Dose descriptor:
- EL50
- Effect conc.:
- 106 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat. (total fraction)
- Basis for effect:
- mobility
- Remarks on result:
- other: Confidence limits: 78.7 to 171 mg/L
- Details on results:
- A repeat definitive test was conducted as the inital test showed different results compared with the range-finder. The repeat test showed consistency with the initial definitive test and was reported as the main test.
- Results with reference substance (positive control):
- The EC50 value for the control of sensitivity for 24 h of exposure with potassium dichromate was estimated to be 0.84 mg/L (data from 24 January 2017), which lies within the recommended range of 0.6 to 2.1 mg/L according to OECD Guideline 202.
- Reported statistics and error estimates:
- A regression model was used (Weibull) and Chi squared test to determine the EC10 and EC50 where appropriate.
- Validity criteria fulfilled:
- yes
- Remarks:
- Control immobilisation was < 10% and O2 concentrations at the end of the test were satisfactory.
- Conclusions:
- The 48 hour EL50 value based on nominal loading rates of the substance to Daphnia magna was 106 mg/L.
Reference
Daphnia immobilisation:
Loading rate (mg/L) |
Replicate |
Number of individuals |
Immobile Daphnids (No./vessel) 24 hour |
Immobile Daphnids (No./vessel) 48 hour |
% immobile Daphnids after 24 hours |
% immobile Daphnids after 48 hours |
0 |
A |
20 |
0 |
1 |
0 |
5 |
B |
20 |
1 |
1 |
5 |
5 |
|
C |
20 |
0 |
0 |
0 |
0 |
|
1.94 |
A |
20 |
0 |
1 |
0 |
5 |
B |
20 |
0 |
0 |
0 |
0 |
|
4.27 |
A |
20 |
0 |
1 |
0 |
5 |
B |
20 |
0 |
0 |
0 |
0 |
|
9.39 |
A |
20 |
0 |
0 |
0 |
0 |
B |
20 |
0 |
0 |
0 |
0 |
|
20.7 |
A |
20 |
0 |
2 |
0 |
10 |
B |
20 |
0 |
1 |
0 |
5 |
|
45.5 |
A |
20 |
1 |
4 |
5 |
20 |
B |
20 |
1 |
4 |
5 |
20 |
|
100 |
A |
20 |
3 |
9 |
15 |
45 |
B |
20 |
4 |
11 |
20 |
55 |
Description of key information
The 48 hour EL50 value based on nominal loading rates of the substance to Daphnia magna was 106 mg/L. This is used as the key value for chemical safety assessment. No testing on marine species has been conducted and is not required.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 106 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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