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EC number: 233-566-4 | CAS number: 10236-47-2
- 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 July 18th to July 20th, 2017
- 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
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 850.1010 (Aquatic Invertebrate Acute Toxicity Test, Freshwater Daphnids)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source and lot/batch No.of test material: 016G050
- Expiration date of the lot/batch: 21/07/2016
- Purity test date: 21/07/2016
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: Controlled room temperature (15-25°C, below 70 RH%), protected from light and humidity.
- Stability under test conditions: stable during test period. - Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 0(control) and 100 mg/L
- Sampling method: Samples were taken from the test solution and from the control solution at the beginning and at the end of the test. The samples were properly diluted and analyzed by a HPLC-UV/Vis detection method.
- Sample storage conditions before analysis: The test solution was continuously stirred until sampling in order to ensure its homogeneity during analytical sampling. - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: A stock solution with a nominal concentration of 100 mg/L was prepared with direct addition of the test item, mixed into the test medium (ISO Medium) using ultrasonic bath (11 minutes). As a Limit test was carried out, further dilution of stock solution was not performed.
- Controls: The dilution water (ISO-medium) was used without addition of the test item.
- Evidence of undissolved material (e.g. precipitate, surface film, etc.): no. - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Daphnia magna
- Source: István Szent University, 2100 Gödöllő, Páter Károly u.1, Hungary
- Age of the animals: less than 24 h old at the beginning of the test
- Feeding during test: no
ACCLIMATION
- Acclimation period: There was no acclimation because the culturing conditions were the same as in the test. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
- Hardness:
- 245 mg/L (as CaCO3)
- Test temperature:
- 20.3 – 20.5ºC
- pH:
- 7.75 – 7.89
- Dissolved oxygen:
- 7.4 – 8.4 mg/L
- Nominal and measured concentrations:
- - Nominal concentrations: 0 (control), 100 mg/L.
- Measured concentrations: 0 (control), 99.4 mg/L (at the start of test); 101 mg/L (at the end of test). - Details on test conditions:
- TEST SYSTEM
- Test vessel: beaker
- Material, size, headspace, fill volume: glass beaker, 50 mL size, 40 mL fill volume.
- 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 (ISO medium, according to OECD 202)
- Culture medium different from test medium: no.
OTHER TEST CONDITIONS
- Adjustment of pH: no.
- Photoperiod: 16-hour light and 8-hour dark cycle
- Light intensity: not specified.
EFFECT PARAMETERS MEASURED (with observation intervals if applicable):
The immobility or mortality of the Daphnia was determined by visual observation 24 and 48 hours after the start of the test. Those animals not able to swim within 15 seconds after gentle agitation of the test beaker were considered to be immobile.
RANGE-FINDING STUDY
- Test concentrations: 0 (control), 0.1, 1, 10, 100 mg/L.
- Results used to determine the conditions for the definitive study: Because toxic response was not observed during the preliminary concentration range-finding test, a Limit Test was carried out using only one test concentration (100 mg/L) and one control group in a static system. - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate is tested at least twice a year to demonstrate satisfactory test conditions.
- 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
- Duration:
- 48 h
- Dose descriptor:
- EC100
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Key result
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- LOEC
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 24 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 abnormal behaviour, appearance or any other effect on test animals were detected.
- Mortality of control: 0/20
- Other adverse effects control: no.
- Abnormal responses: no.
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: no.
- Effect concentrations exceeding solubility of substance in test medium: no. - Results with reference substance (positive control):
- - Results with reference substance valid? yes
- The date of the last study (Study Code: 17/058-023DA) with reference item Potassium dichromate (batch no.: A0345704) is: 08 - 09 March 2017.
- Relevant effect levels: The 24h EC50: 0.64 mg/L, (95 % confidence limits: 0.59 – 0.68 mg/L). - Reported statistics and error estimates:
- No statistical analysis was performed because of the lack of toxic effects. The EC50, NOEC, LOEC and EC100 values were determined directly from the raw data.
- Validity criteria fulfilled:
- yes
- Remarks:
- There was no immobilization in the control group and the dissolved oxygen concentration at the end of the test in control and test vessels was more than 3 mg/L.
- Conclusions:
- The 48h-EC50 of the test item in Daphnia magna was found to be higher tan 100 mg/L and the NOEC was 100 mg/L, both based on mobility.
- Executive summary:
An acute immobilisation test on Daphnia magna was performed in accordance with OECD Guideline 202 / EU method C.2, under GLP conditions. Based on the results obtained in a preliminary range-finding test, a Limit Test was carried out using only one test concentration (100 mg/L) and one control group in a static system. Test concentrations were analytically determined (validated method) at the beginning and at the end of the test and did not deviate more than 20%. Twenty animals, divided into four groups (glass beaker) of five animals each were exposed to the test item or the control for 48 h. Positive controls (potassium dichromate) are performed at least twice a year to ensure the quality of the results. All validity criteria were met. The 48h-EC50 was determined to be higher than 100 mg/L and the 48h-NOEC was determined to be 100 mg/L, both based on mobility.
Reference
Table 2. Number and % of immobilised animals.
Test Group |
Number of treated animals |
Number of immobilised animals |
|||
24 hours |
48 hours |
||||
number |
percent |
number |
percent |
||
Control |
20 |
0 |
0 |
0 |
0 |
100 mg/L |
20 |
0 |
0 |
0 |
0 |
Table 3. Temperature measured in the test vessels (ºC)
Test group |
Replicate |
Measuring |
||
0 h |
24 h |
48 h |
||
Control |
1 |
20.5 |
20.3 |
20.4 |
2 |
20.5 |
20.3 |
20.4 |
|
3 |
20.5 |
20.3 |
20.4 |
|
4 |
20.5 |
20.3 |
20.4 |
|
100 mg/L |
1 |
20.5 |
20.3 |
20.4 |
2 |
20.5 |
20.3 |
20.4 |
|
3 |
20.5 |
20.3 |
20.4 |
|
4 |
20.5 |
20.3 |
20.4 |
Table 4. Oxygen concentrationmeasured in the test vessels (mg/L)
Test group |
Replicate |
Measuring |
|
0 h |
48 h |
||
Control |
1 |
8.4 |
8.3 |
2 |
8.4 |
8.2 |
|
3 |
8.4 |
8.3 |
|
4 |
8.4 |
8.3 |
|
100 mg/L |
1 |
7.4 |
8.2 |
2 |
7.4 |
8.3 |
|
3 |
7.4 |
8.3 |
|
4 |
7.4 |
8.2 |
Table 5. pH measured in the test vessels
Test group |
Replicate |
Measuring |
|
0 h |
48 h |
||
Control |
1 |
7.75 |
7.80 |
2 |
7.75 |
7.82 |
|
3 |
7.75 |
7.83 |
|
4 |
7.75 |
7.83 |
|
100 mg/L |
1 |
7.78 |
7.87 |
2 |
7.78 |
7.88 |
|
3 |
7.78 |
7.88 |
|
4 |
7.78 |
7.89 |
Table 6. Immobilisation of the test animals (detailed results).
Test group |
Number of |
Number of immobilised animals |
|
24 h |
48 h |
||
Control |
5 |
0 |
0 |
5 |
0 |
0 |
|
5 |
0 |
0 |
|
5 |
0 |
0 |
|
100 mg/L |
5 |
0 |
0 |
5 |
0 |
0 |
|
5 |
0 |
0 |
|
5 |
0 |
0 |
Description of key information
Key study. Method according to OECD 202, GLP study. The 48h-EC50 was determined to be higher than 100 mg/L and the 48h-NOEC was determined to be 100 mg/L, both based on mobility.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 100 mg/L
Additional information
An acute immobilisation test on Daphnia magna was performed in accordance with OECD Guideline 202 / EU method C.2, under GLP conditions. Based on the results obtained in a preliminary range-finding test, a Limit Test was carried out using only one test concentration (100 mg/L) and one control group in a static system. Four groups of five daphnids each were exposed to the test item or the control for 48 h. All validity criteria were met. The 48h-EC50 was determined to be higher than 100 mg/L and the 48h-NOEC was determined to be 100 mg/L, both based on mobility.
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