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EC number: 454-790-0 | 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
- Study period:
- Sep 07-09, 2004
- 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:
- yes
- Details on sampling:
- - Concentrations: all concentrations tested
- Sampling method: -
- Sample storage conditions before analysis: no - Vehicle:
- no
- Details on test solutions:
- 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.
- Hardness: about 14° dH (about 250 mg/L CaCO3)
- pH: 7.9 ± 0.3, after an aeration for 24 hours.
References:
ELENDT, B.-P. Selenium deficiency in Crustacea. An ultrastructural approach to antennal damage in Daphnia magna Straus.
Protoplasma 154, 25-33, 1990 - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Daphnia magna (Straus)
- Strain: Straus
- Source: in house
- Age at study initiation (mean and range, SD): not older than 24 hours
- Feeding during test: yes
- Food type: suspension of fresh water algae
- Amount: sufficient
- Frequency: once a week - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- 14 ° dH (about 250 mg/L CaCO3)
- Test temperature:
- 20-21 °C
- pH:
- 7.8- 8.0
- Dissolved oxygen:
- > 85 %
- Nominal and measured concentrations:
- nominal: 0.00, 2.00, 4.40, 9.68, 21.30, and 46.85 mg/L
measured: 0, 0.03, 0.09, 0.25, 0.67, 1.52, mg/L - Details on test conditions:
- -- Preparation
The test medium (reconstituted water and test material) was freshly prepared. Therefore, the test material was solved in the vehicle, reconstituted water. The test media were changed after 24 hours.
-- Administration
At the start of the experimental phase, 5 Daphnia magna were placed into 10 ml of reconstituted water (control group) or test medium (test material groups). The Daphnia magna were not fed, and the control medium and test medium were not aerated during the test. The test vessels were labeled to assure unique identification.
-- Replicates: 4
-- Concentrations: 5
-- Dose levels
Daphnia magna were exposed to the vehicle and to test material concentrations of nominal 2.00, 4.40, 9.68, 21.30, and 46.85 mg/L were used.
-- Observation schedule
The mobility was determined by visual control and recorded after 24 and 48 hours.
-- pH and oxygen concentration
The pH-values and dissolved oxygen concentration (O2) were measured in the control and all test material concentrations at the beginning and at the end of the experimental part.
-- Temperature
During the experimental part, the temperature was registered in a control vessel with an electronic thermometer containing a maximum and minimum memory display.
-- Archive statement
All raw data, specimens and the final report are stored in the archives of the test facility. - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- 0.78 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 0.64-0.94
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 0.27 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 0.22-0.34
- Details on results:
- C daphnia
imm/expos. imm/expos.
24h 48h
0.00 0/20 0/20
2.00 0/20 0/20
4.40 0/20 1/20
9.68 0/20 7/20
21.30 6/20 20/20
46.85 20/20 20/20 - Validity criteria fulfilled:
- yes
- Conclusions:
- The 48 hours analytical EC50 to Daphnia magna is 0.27 mg/L.
- Executive summary:
Purpose
The purpose of this assay was to identify the aquatic toxicity potential of the test material in Daphnia magna to provide a rational basis for hazard estimation for the test item in aquatic environments.
Study design
For this purpose, young Daphnia magna were exposed to aqueous test material concentrations under defined conditions. There was a very poor recovery of the test material after 48 hours and a closed semistatic test system was chosen. The study comprised of four vessels per concentration containing five Daphnia magna, i.e., 20 Daphnia per concentration (per test medium group). The Daphnia were observed for immobilization up to 48 hours. Daphnia magna were exposed to the vehicle and to test material concentrations of nominal 2.00, 4.40, 9.68, 21.30, and 46.85 mg/L were used. The GLP study was performed according to OECD TG 202.
Results
Analytical controls were carried out. There was a poor recovery of the test material after 48 hours, and a closed semistatic test system was chosen. The test media were changed after 24 hours. The limit of quantification of the analytical method was 0.006 mg/L.
The analytically determined concentrations were about 1.5- 3.3 % of the nominal concentrations directly after preparation and even 1.5- 3.6% of the nominal concentrations after 24 hours. That means that the test material concentrations stayed in the same range.
The solubility of the test material in the test medium was very poor and a semistatic test system was chosen. So the nominal EC50 values had to be calculated with the mean analytical concentrations. Nominal and corresponding mean analytical concentrations with motility data are given in the following table.
Nominal concentration Immobilization immobilized / exposed
[mg/L] 24 hours 48 hours 0.00 0/20 0/20 2.00 0/20 0/20 4.40 0/20 1/20 9.68 0/20 7/20 21.30 6/20 20/20 46.68 20/20 20/20 For the test material the following EC50 values for Daphnia magna were determined:
24 h EC50 = 0.78 mg/L (0.64 - 0.94 mg/L)
48 h EC50 = 0.27 mg/L (0.22 - 0.34 mg/L)
Conclusions
The 48 hours analytical EC50 to Daphnia magna is 0.27 mg/L.
Reference
Description of key information
The informtion for this endpoint study record was obtained from an experimental study. The OECD GLP criteria were met and the methods applied are fully compliant with OECD TG 202.
The 48 hours analytical EC50 to Daphnia magna is 0.27 mg/L.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 0.27 mg/L
Additional information
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