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EC number: 700-631-8 | CAS number: 102601-34-3
- 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:
- from 2012-11-23 to 2013-05-23
- 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
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 100 mg/L
- Sampling method: At the start of the experiment one sample was taken from the control and eight parallel samples were taken from the test solution, while at the end of the study one sample was taken from the control and two parallel samples were taken from each of the four replicates of the 100 mg/L test item group.
- Sample storage conditions before analysis: at room temperature - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: The test solution used in the test was prepared by mechanical dispersion. 0.1055 g of test item was dissolved in 1000 mL of the dilution water (Elendt M4 medium) in order to give the concentration of 100 mg/L.
- Controls:
Blank control performed with the test solution without test substance
Positive control: performed with the reference substance: potassium dichromate
- Evidence of undissolved material: no - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Water flea
- Strain: Daphnia magna (Straus)
- Source: Laboratory of Hydrobiology (Central Agricultural Office, Directorate of Plant-, and Soil Protection) 2100 Gödöllő, Kotlán S. u. 3. (Hungary)
- Age at study initiation: < 24 h
- Method of breeding: The Daphnia are bred in the Laboratory of TOXI-COOP ZRT.
- Feeding during test: no
ACCLIMATION
- Acclimation period: Test animals were bred under similar conditions as that used during the exposure period, therefore additional acclimatisation before the test was not necessary.
- Acclimation conditions: same as the test (see above)
- Type and amount of food: concentrated algal suspension of Pseudokirchneriella subcapitata during holding - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
- Post exposure observation period:
- none
- Hardness:
- The reconstituted water (Elendt M4 Medium) had a total hardness of 225.526 mg/L (as CaCO3).
- Test temperature:
- 20.2 – 20.3 °C
- pH:
- 7.59 – 7.68 in the control group and 9.15 – 9.41 in the test item treated group
- Dissolved oxygen:
- 7.16 – 7.98 mg/L
- Nominal and measured concentrations:
- Nominal concentration: 0 (control), 100 mg/L
Measured concentrations:
Start of the test: 96, 98, 117, and 118 mg/L
End of the test: 110, 111, 112 and 113 mg/L
Measured test item concentrations were 96 - 118 % of the nominal at the start and 110-113 % of the nominal at the end of the test - Details on test conditions:
- TEST SYSTEM
- Test vessel: glass beaker
- Volume: 50 mL
- Aeration: no
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Reconstituted water (Elendt M4 medium, according to OECD 202)
- Culture medium different from test medium: no
- Intervals of water quality measurement: The water temperature, dissolved oxygen concentration and pH were measured in each test concentration and control at the start and in each test vessel at the end of the test. Additionally, the ambient temperature was measured continuously using a min/max thermometer in the climate chamber.
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16 hours light (artificial illumination at an intensity of approximately 979 lux) and 8 hours darkness.
- Light intensity: approximately 979 lux
EFFECT PARAMETERS MEASURED
Immobility or mortality of the Daphnia was determined by visual observation after 24 and 48 hours of exposure.
TEST CONCENTRATIONS
- Justification for using less concentrations than requested by guideline: Limit test due to results of a range finding test
- Range finding study: yes
- Test concentrations: 0.01, 0.1, 1, 10, 50 and 100 mg test item/L
- Results used to determine the conditions for the definitive study: No immobility or any sub-lethal effects were detected in the treatment group or in the control group during the 48-h exposure period. - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- - Behavioural abnormalities: no
- Mortality of control: no
- Any observations that might cause a difference between measured and nominal values: no
- Effect concentrations exceeding solubility of substance in test medium: no effects observed
The EC50 (48h) of the test item to Daphnia magna was determined to be greater than 100 mg/L based on nominal concentration and the NOEC (48h) was determined to be >= 100 mg/L - Results with reference substance (positive control):
- - Results with reference substance valid? yes
- EC50/LC50: 24h EC50: 1.03 mg/L, (95 % confidence limits: 0.82 – 1.29 mg/L)
Potassium dichromate is tested at least twice a year to demonstrate satisfactory test conditions. - Reported statistics and error estimates:
- not applicable (as no effects observed)
- Validity criteria fulfilled:
- yes
- Conclusions:
- The EC50 (48 h) of the test item to Daphnia magna was determined to be greater than 100 mg/L according to OECD 202 (2004) in a static test system under GLP conditions. The results are based on the nominal concentration.
- Executive summary:
The EC50 (48h) of the test item to Daphnia magna was determined according to OECD 202 (2004) in a static test system under GLP conditions. Young Daphnia were exposed to aqueous test media containing the test item for 48 hours under defined conditions. Based on the results of the preliminary test (static test), the test item has no toxic effect on the daphnids up a concentration of 100 mg/L. Therefore, the main test was performed at a concentration level of 100 mg/L and a concurrent control. A static test was performed because the test item was stable in test water during the test period of 48 hours. The test item concentration of the test solutions was measured by LC/MS method at the start and end of the test. As the performed analytical determinations confirmed that the test item concentration remained within the range of ± 20 % of the nominal concentration, the biological results are reported based on the nominal concentration of the test item. Twenty Daphnia (divided into four replicates) were tested at the test concentration and in the untreated control. Each test vessel contained approximately 40 mL test medium. The test medium (dilution water) was the Elendt M4 Medium according to OECD guideline. Temperature and pH were measured with the suitable instruments at the start and at the end of the test. All of the measured values remained in the acceptable ranges. For the evaluation of the quality of the Daphnia clone and the experimental conditions, potassium dichromate is tested at least twice a year to demonstrate satisfactory test conditions. The 24h EC50 of the reference substance is determined to be 1.03 mg/L. The immobilisation of the test animals was recorded 24 and 48 hours after treatment. A limit test was performed therefore statistical analysis to determine the EC50 value was not necessary. The EC50 (48h) of the test item to Daphnia magna was determined to be greater than 100 mg/L based on nominal concentration.
Reference
Immobilization of the test animals
Nominal Concentration |
Replicate |
Number of |
Number of immobilised animals |
|
24 h |
48 h |
|||
Control |
1 |
5 |
0 |
0 |
2 |
5 |
0 |
0 |
|
3 |
5 |
0 |
0 |
|
4 |
5 |
0 |
0 |
|
100.0 |
1 |
5 |
0 |
0 |
2 |
5 |
0 |
0 |
|
3 |
5 |
0 |
0 |
|
4 |
5 |
0 |
0 |
Description of key information
The EC50 (48h) of the test item to Daphnia magna was determined to be greater than 100 mg/L (reference 6.1.3-1) according to OECD 202 (2004) in a static test system under GLP conditions.
Key value for chemical safety assessment
Additional information
The EC50 (48h) of the test item to Daphnia magna was determined according to OECD 202 (2004) in a static test system under GLP conditions. Young Daphnia were exposed to aqueous test media containing the test item for 48 hours under defined conditions. Based on the results of the preliminary test (static test), the test item has no toxic effect on the daphnids up a concentration of 100 mg/L. Therefore, the main test was performed at a concentration level of 100 mg/L and a concurrent control. A static test was performed because the test item was stable in test water during the test period of 48 hours. The test item concentration of the test solutions was measured by LC/MS method at the start and end of the test. As the performed analytical determinations confirmed that the test item concentration remained within the range of ± 20 % of the nominal concentration, the biological results are reported based on the nominal concentration of the test item. Twenty Daphnia (divided into four replicates) was tested at the test concentration and in the untreated control. Each test vessel contained approximately 40 mL test medium. The test medium (dilution water) were the Elendt M4 Medium according to OECD guideline. Temperature and pH were measured with the suitable instruments at the start and at the end of the test. All of the measured values remained in the acceptable ranges. For the evaluation of the quality of the Daphnia clone and the experimental conditions, potassium dichromate is tested at least twice a year to demonstrate satisfactory test conditions. The 24h EC50 of the reference substance is determined to be 1.03 mg/L. The immobilisation of the test animals was recorded 24 and 48 hours after treatment. A limit test was performed therefore statistical analysis to determine the EC50 value was not necessary. The EC50 (48h) of the test item to Daphnia magna was determined to be greater than 100 mg/L based on nominal concentration.
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