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EC number: 616-651-4 | CAS number: 787582-75-6
- 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:
- 2007-11-23 to 2007-12-06
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Version / remarks:
- 31st July 1992
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- 2004-04-13
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- no
- Remarks:
- The development of an analytical method with a sufficiently low detection and quantification limit would be very time and cost intensive. Due to the absence of any adverse effects at the saturation concentration, the study was performed without analytic.
- Vehicle:
- no
- Details on test solutions:
- The test medium (reconstituted water and test material) 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. The formulation was then passed through a single use syringe filter (pore size 0.2 µm). The filtrate was used for the study.
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Water flea
- Strain/clone: Strauss
- Age at study initiation: not older than 24 h
- Source: Merck KGaA, Darmstadt, Institute of Toxicology
- Feeding during test : no
ACCLIMATION
- Acclimation period: no - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
- Hardness:
- about 14 ° dH (about 250 mg/L CaCO3)
- Test temperature:
- 18 - 22°C
- pH:
- 7.9 +/- 0.3
- Dissolved oxygen:
- 95.2 - 98.6 %
- Nominal and measured concentrations:
- Nominal concentration: 100 mg/L (limit test)
due to the low water solubility and the fact that the study was a limit test, no further analysis was initiated. - Details on test conditions:
- TEST SYSTEM
- Test vessel: glass vessels
- Type: open
- Material: glass
- Volume of solution: 10 mL
- Aeration: no
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
- Biomass loading rate: 5 daphnia/10 mL
TEST MEDIUM / WATER PARAMETERS
- Preparation of dilution water: Reconstituted water according to ELENDT (1990):
Macro nutrients (mg/L):
CaCI2 x 7 H20 293.80
MgSO4 x 7 H20 123.30
NaHCO3 64.80
KCI 5.80
Na2SiO3 x 9H20 10.00
NaNO3 0.27
KH2PO4 0.14
K2HPO4 0.18
Trace elements (mg/L):
B 0.5000
Fe 0.2000
Mn 0.1000
Li, Rb and Sr 0.0500
Mo 0.0250
Br 0.0125
Cu and Zn 0.0063
Co and I 0.0025
Se 0.0010
V 0.0003
Macro nutrients (mg/L): Na2EDTA x 2H20 2.50
Vitamins (µg/L):
Thiamine 75.00
B12 1.00
Biotin 0.75
After preparation, the reconstituded water was aerated for 24 hours.
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16 hours light - 8 hours dark
- Light intensity: no details available
EFFECT PARAMETERS MEASURED
mobility of Daphnia: after 24 and 48h
pH, O2 was measured at start and end of experiment, temperature was measured constantly
RANGE-FINDING STUDY
no details available - 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
- Other adverse effects control: no
- Immobilisation of control: no
- Abnormal responses: no
- Any observations that might cause a difference between measured and nominal values: no
Daphnia magna exposed to a nominal concentration of 100 mg/L (limit test) for 48 hours in an open static system were not affected. The test material concentration in the aqueous medium was not quantified at the start and at the end of this study as a very low water solubility was calculated for this test item (ca. 0.059 µg/L). Therefore, the development of an analytical method with a sufficiently low detection and quantification limit would be very time and cost intensive. Due to the absence of any adverse effects at the saturation concentration, the study was performed without analytical concentration verification. For the test material, the following EC50 values for Daphnia magna were determined: 24h-EC50: > 100 mg/L nominal, 48h-EC50: > 100 mg/L nominal. - Results with reference substance (positive control):
- no details available
- Validity criteria fulfilled:
- yes
- Conclusions:
- Under the given experimental conditions, the test material showed a 24h and 48h EC50 value > 100 mg/L nominal.
- Executive summary:
The objective of this study was to determine the acute toxicity of the test item using Daphnia magna according to OECD 202 and EU Method C.2. For this purpose, juvenile Daphnia magna were exposed to an aqueous test material solution over 48 hours under defined conditions. The study comprised of four test vessels per concentration containing five Daphnia magna each, i.e. 20 Daphnia magna per concentration (test medium group) and control group. Daphnia were exposed to a nominal test material concentration of 100 mg/L (limit test) in an open static system.The test material concentration in the aqueous medium was not quantified at the start and at the end of this study as a very low water solubility was calculated for this test item (< 0.085 mg/L). Therefore, the development of an analytical method with a sufficiently low detection and quantification limit would be very time and cost intensive. Due to the absence of any adverse effects at the saturation concentration, the study was performed without analytical concentration verification. Daphnia magna exposed to an aqueous preparation of the nominal concentration of 100 mg/L were not affected. For the test material, the following EC50 values for Daphnia magna were determined: 24h-EC50: > 100 mg/L nominal, 48h-EC50: > 100 mg/L nominal.
Reference
Description of key information
The test material showed a 24h and 48h EC50 value > 100 mg/L nominal (reference 6.1.3 -1).
Key value for chemical safety assessment
Additional information
The objective of the study was to determine the acute toxicity of the test item using Daphnia magna according to OECD 202 and EU Method C.2. For this purpose, juvenile Daphnia magna were exposed to an aqueous test material solution over 48 hours under defined conditions. The study comprised of four test vessels per concentration containing five Daphnia magna each, i.e. 20 Daphnia magna per concentration (test medium group) and control group. Daphnia were exposed to a nominal test material concentration of 100 mg/L (limit test) in an open static system.The test material concentration in the aqueous medium was not quantified at the start and at the end of this study as a very low water solubility was calculated for this test item (ca. 0.059 µg/L). Therefore, the development of an analytical method with a sufficiently low detection and quantification limit would be very time and cost intensive. Due to the absence of any adverse effects at the saturation concentration, the study was performed without analytical concentration verification. Daphnia magna exposed to an aqueous preparation of the nominal concentration of 100 mg/L were not affected. For the test material, the following EC50 values for Daphnia magna were determined: 24h-EC50: > 100 mg/L nominal, 48h-EC50: > 100 mg/L nominal (reference 6.1.3 -1).
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