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EC number: 947-452-3 | 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:
- 04 June - 06 June, 2019
- 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:
- yes
- Remarks:
- Experimental temperature 20.0 – 23.8 °C [not in the desired range (18.0 – 22.0°C)]. Experimental temperature f 20.0 – 23.8 °C [fluctuated by more than ± 1 °C]. As no immobility was observed in the blank control these deviations was stated as uncritical.
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- see report attached
- Vehicle:
- yes
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: A stock solution containing 100.6 mg/L test item in dilution water was prepared. The lower treatments (4.6 / 10 / 22 / 46 mg/L nominal) were prepared by dilution of this stock solution with dilution water. The appearance of the final solutions was clear and free of turbidity.
The concentrations 46 mg/L (2x) and 100 mg/L (5x) were diluted, because they were not in the calibrated range.
- Controls:
Blank control 4 vessels, each containing 20 ± 5 mL dilution water and 5 daphnia
- Chemical name of vehicle: Water
- Concentration of vehicle in test medium:
stock solution containing 100.6 mg/L test item
final test solutions 4.6 / 10 / 22 / 46 mg/L nominal
- Evidence of undissolved material (e.g. precipitate, surface film, etc.): the final solutions were clear and free of turbidity - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Daphnia magna
- Strain/clone: STRAUS
- Age at study initiation (mean and range, SD): between 0 and 24 hours
- Method of breeding: In-house breeding
- Feeding during test
- Food type: green algae (Desmodesmus subspicatus)
- Photo period: 16/8 hours, using neon tubes
- Medium: M4-Medium (recipe of ELENDT)
- Medium renewal: twice a week - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Remarks on exposure duration:
- Observation times 24 and 48 hours
- Test temperature:
- 20.0 – 23.8 °C
- pH:
- 7.5 - 7.8
- Dissolved oxygen:
- 8.7 - 8.9
- Nominal and measured concentrations:
- 4.6 / 10 / 22 / 46 / 100 mg/L (nominal concentration)
4.09 / 9.59 / 22.84 / 47.20 / 11.46 mg/l (measured concentration t= 48h) - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate K2Cr2O7
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- ca. 46 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- LOEC
- Effect conc.:
- ca. 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Validity criteria fulfilled:
- yes
- Remarks:
- Immobilisation in the controls may not exceed 10 % [It was 0 %]. The concentration of dissolved oxygen at the end of the test must be at least 3 mg/L [It was 8.7 mg/L].
- Conclusions:
- 48h-EC50 > 100 mg/L
- Executive summary:
Guidelines
One valid experiment was performed according to the OECD Guideline 202.
Discussion
The study was performed using 5 concentrations ranging from 4.6 to 100 mg/L nominal concentration. For each test concentration and the blank control, 20 daphnia were exposed to the test item for 48 hours in a static test system. After 24 and 48 hours, the immobilised daphnia were counted. Three concentrations showed toxicity between 5 and 35 % immobilisation. None of the animals was immobilised in the blank control. Because of the immobilisation of 35 % in the highest tested concentration at 48 h, the 48h-EC50was set as higher than the highest tested concentration. At the beginning and at the end of the test, the content of the test item in the test solutions was determined using a photometer. The concentrations determined at the start of the test laid between 82 % and 101 % of the nominal concentration. At the end of the test the determined concentrations laid between 89 % and 111 % of the nominal concentration. Therefore, the determination of the biological results was based on the nominal concentration. Potassium dichromate K2Cr2O7(CAS No. 7778-50-9) was used as positive control in a current reference study to assure that the test conditions are reliable. No observations were made which might cause doubts concerning the validity of the study outcome. All validity criteria were met.
The result of the test is considered valid.
Results
The following results were determined for the test item (species:Daphnia magna).
48h-NOEC = 46 mg/L
48h-LOEC = 100 mg/L
24h-EC50 > 100 mg/L
48h-EC50 > 100 mg/L
Reference
FINDINGS
Immobility
In the blank control, none of the daphnia was immobilised (see table below).
Table: Immobility
Conc (mg/l) |
Immobility 24 hours |
Immobility 48 hours |
||||||||||
Absolute |
% |
Absolute |
% |
|||||||||
Blank |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
||
4.6 |
0 |
0 |
0 |
0 |
0 |
1 |
0 |
0 |
0 |
5 |
||
10 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
||
22 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
||
46 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
0 |
0 |
5 |
||
100 |
0 |
0 |
0 |
1 |
5 |
0 |
3 |
2 |
2 |
35 |
||
pH and O2
The pH values and the concentration of dissolved oxygen in the test media and the blank
control are given in the following table:
Table: pH and O2-values
Conc (mg/l) |
pH |
O2-Concentration in mg/L |
||
0 h |
48 h |
0 h |
48 h |
|
Blank |
7.8 |
7.7 |
8.9 |
8.7 |
4.6 |
7.8 |
7.7 |
8.9 |
8.7 |
10 |
7.8 |
7.7 |
8.9 |
8.8 |
22 |
7.8 |
7.7 |
8.9 |
8.7 |
46 |
7.7 |
7.7 |
8.9 |
8.7 |
100 |
7.5 |
7.7 |
8.9 |
8.7 |
Analytical Determinations
At the beginning and at the end of the test, the content of the test item in the test solutions was determined using a photometer. The concentrations determined at the start of the test laid between 82 % and 101 % of the nominal concentration. At the end of the test the determined concentrations laid between 89 % and 111 % of the nominal concentration.
Therefore, the determination of the biological results was based on the nominal concentration (see Guidance Doc. No.23 (§176)). The measured QC sample (10 mg/L) was taken into account at the beginning (96.7 %) and the end of the test (96.4 %). The concentrations 46 mg/L (2x) and 100 mg/L (5x) were diluted, because they were not in the calibrated range.
The measured concentrations for treatment and blank control are given in the following table:
Table: Raw Data and Measured Concentration
Nominal concentration |
Absorbance t = 0 h |
Absorbance t = 48 h |
Meas. Conc. T= 0 h* |
Meas. Conc. T= 48 h* |
|
|
|
mg/l |
mg/l |
Blank control |
0.0000 |
0.0000 |
0.016 |
0.16 |
0.0000 |
0.0001 |
0.016 |
0.025 |
|
4.6 |
0.0387 |
0.0419 |
3.640 |
3.940 |
0.386 |
0.0419 |
3.630 |
3.940 |
|
10 |
0.0926 |
0.0982 |
8.715 |
9.245 |
0.0925 |
0.0982 |
8.706 |
9.245 |
|
22 |
0.2147 |
0.2321 |
20.341 |
22.013 |
0.2147 |
0.2321 |
20.341 |
22.013 |
|
46 |
0.2357 |
0.2398 |
22.359 |
22.754 |
0.2356 |
0.2397 |
22.350 |
22.744 |
|
100 |
0.261 |
0.2267 |
19.517 |
21.494 |
0.2060 |
0.2266 |
19.507 |
21.484 |
|
QC (10 mg/l) |
0.1027 |
0.1024 |
9.670 |
9.642 |
0.1027 |
0.1023 |
9.670 |
9.632 |
*Without dilution factor and recovery of the QC samples
Table: Measured Concentrations and % of Nominal Concentration
Nominal conc. (mg/l) |
Meas. Conc t = 0 h (mg/l) |
Meas. Conc t = 48 h (mg/l) |
% of Nominal Conc. t = 0 h |
% of Nominal Conc. t = 48 h |
Blank |
0.02 |
0.02 |
- |
- |
4.6 |
3.76 |
4.09 |
82 |
89 |
10 |
9.01 |
9.59 |
90 |
96 |
22 |
21.04 |
22.84 |
96 |
104 |
46 |
46.24 |
47.20 |
101 |
103 |
100 |
100.89 |
111.46 |
101 |
111 |
LOQ |
0.5 |
0.5 |
- |
- |
LOQ = limit of quantification
RESULTS AND STATISTICS
The estimation of the biological results was accomplished using the software ToxRat® Professional, version 3.3.0.
VALIDITY
- Immobilisation in the controls may not exceed 10 %.
Immobilisation in the controls was 0 %.
- The concentration of dissolved oxygen at the end of the test must be at least 3 mg/L.
The lowest concentration of dissolved oxygen at the end of the test was 8.7 mg/L.
Description of key information
EC50 (48h) > 100 mg/l
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 100 mg/L
Additional information
The acute toxicity of the test item to aquatic invertebrated was investigated on Daphnia magna STRAUS according to the OECD Guideline 202.
the test was performed using 5 concentrations ranging from 4.6 to 100 mg/L nominal concentration. For each test concentration and the blank control, 20 daphnia were exposed to the test item for 48 hours in a static test system.
After 24 and 48 hours, the immobilised daphnia were counted. None of the animals was immobilised in the blank control. Because of the immobilisation of 35 % in the highest tested concentration at 48 h, the 48h-EC50 was set as higher than the highest tested concentration (EC50 48h >100 mg/l)
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