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Diss Factsheets
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EC number: 946-888-1 | 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:
- May from 08th to 11th, 2018
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- test procedure in accordance with generally accepted scientific standards and described in sufficient detail
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- adopted 13th April 2004
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- For the determination of the test item concentration, samples were taken from the test item treated group and from the control group (4 x 5 ml at the start and 4 x 5 ml at the end of the study).
- Vehicle:
- no
- Details on test solutions:
- The test solution used in the test was prepared by mechanical dispersion. An amount of 0.0501 g test item was dissolved in 501 ml dilution water (ISO medium) in order to obtain the concentration of 100 mg product/l. The test solution was freshly prepared in the testing laboratory just before introduction of test animals (start of the experiment).
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Source: Laboratory of Hydrobiology (Central Agricultural Office, Directorate of Plant-, and Soil Protection), Hungary
- Age of parental stock: less than 24 h old at the beginning of the test.
- Feeding during test: test animals were not fed during the exposure.
ACCLIMATION
- Acclimation period: test animals were bred under similar (or the same) conditions as that used during the exposure period (holding water, temperature, background colour etc.), therefore additional acclimatisation before the test was not necessary. Brood daphnids were maintained in dilution water at the test temperature for at least 48 hours prior to the start of the test.
- Acclimation conditions (same as test or not):
- Type and amount of food: Daphnia were fed with concentrated algal suspension of Raphidocelis subcapitata during the holding. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
- Test temperature:
- 20.3 - 20.7 °C
- pH:
- 7.84 - 8.09
- Dissolved oxygen:
- 7.02 - 7.20 mg/l
- Nominal and measured concentrations:
- 100 mg/l (nominal)
- Details on test conditions:
- TEST SYSTEM
- Test vessel: glass beaker; volume approx. 50 ml filled with approx.40 ml control or test solution.
- No. of organisms per vessel: 5 animals per replicates.
- No. of vessels per concentration: 4 replicates.
- No. of vessels per control: 4 replicates.
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: reconstituted water (ISO medium).
- Theoretical total hardness: 249 mg/l (as CaCO3).
OTHER TEST CONDITIONS
- Photoperiod: 48 h darkness.
EFFECT PARAMETERS MEASURED
The immobility or mortality of the Daphnia was determined by visual observation after 24 and 48 hours of exposure. Those animals not able to swim within 15 seconds after gentle agitation of the test beaker were considered to be immobile.
RANGE-FINDING STUDY
- No. of organisms per vessel: 5 animals per replicates.
- No. of vessels per concentration: 2 replicates
- Test concentrations: 0.1, 1.0, 10.0 and 100.0 mg/l.
- Results used to determine the conditions for the definitive study: only one immobilized daphnid was observed at 100 mg/l after the 48 hours exposure period.
ACCEPTANCE CRITERIA
The immobilisation rate of the introduced Daphnia should not exceed 10 % in the control group.
The dissolved oxygen concentration at the end of the test should be ≥ 3 mg/l in control and test vessels. - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
- 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:
- No immobilisation or any abnormal behaviour of test animals was observed in the control group and no immobilization or any abnormal behavior of the test animals was observed at the test concentration of 100 mg/l after 48 hours of exposure.
APPEARANCE OF TEST MEDIUM
The test solution was clear solution at 0h (start of experiment) and there was not observed any change of the test solution at 24 h and 48 h.
MEASURED CONCENTRATION
The measured concentration of the test item in the test solution was 94 % of the nominal value at the start and 94 % of the nominal value at the end of the test. There is evidence that the concentration of the tested substance was maintained within ± 20 % of the nominal concentration throughout the test. Therefore the analysis of the results was based on the nominal concentration value. Test item was not detected in the control group. - Validity criteria fulfilled:
- yes
- Remarks:
- The immobilisation rate of Daphnia was lower than 10 % in the control group and the dissolved oxygen concentration at the end of the test was ≥ 3 mg/l in control and test vessels.
- Conclusions:
- EC50 (48h) > 100 mg/l (nominal)
- Executive summary:
The substance was assessed using Daphnia magna in a 48-hour Acute Immobilisation Test, conducted according to the OECD guideline 202. Based on results obtained in a non-GLP preliminary experiment, daphnids were exposed to a single concentration of 100 mg/l (limit concentration). A concurrent control group was run.
A static test was performed as the test item was previously shown to be stable in the ISO medium for 48 hours. The analytically measured test item concentration remained within ± 20 % of the nominal during the test period of 48 hours; therefore, biological results are based on the nominal concentration.
Twenty Daphnia (divided into 4 replicates) were tested each, exposed to 100 mg/l test item and in the control. The immobilisation of the test animals was recorded 24 and 48 hours after treatment. Environmental conditions were recorded. All measured values remained within acceptable ranges.
No immobilisation or any abnormal behaviour of test animals was observed in the control group and no immobilization or any abnormal behavior of the test animals was observed at the test concentration of 100 mg/l after 48 hours of exposure.
All validity criteria were met and therefore the study can be considered as valid.
Conclusion
EC50 (48h) > 100 mg/l (nominal)
Reference
Immobilization of the test animals
Nominal concentration [mg/l] | Number Daphnia tested | Number of immobilised Daphnia after | % of immobilised Daphnia after | ||
24 h | 48 h | 24 h | 48 h | ||
Control | 20 | 0 | 0 | 0 | 0 |
100 | 20 | 0 | 0 | 0 | 0 |
Measured concentrations
Nominal concentration [mg/l] | Mean of the measured concentrations (mg/l) | Measured concentration in % of the nominal | ||
Start | End | Start | End | |
100 | 93.6 | 94.3 | 94 | 94 |
RSD (%) | 2.5 | 4.5 | ||
Control | not detected | not detected |
Results of the Preliminary Range-Finding Test
Nominal concentration [mg/l] | Untreated control | 0.1 | 1 | 10 | 100 |
Number of treated animals |
10 | 10 | 10 | 10 | 10 |
Number of immobilised animals(at 48h) |
0 | 0 | 0 | 0 | 1 |
Description of key information
Not harmful/toxic to aquatic invertebrates after short-term exposure (EC50 (48h) > 100 mg/l (nominal))
Key value for chemical safety assessment
Additional information
The substance was assessed using Daphnia magna in a 48-hour Acute Immobilisation Test, conducted according to the OECD guideline 202. Based on results obtained in a non-GLP preliminary experiment, daphnids were exposed to a single concentration of 100 mg/l (limit concentration). A concurrent control group was run. A static test was performed as the test item was previously shown to be stable in the ISO medium for 48 hours. The analytically measured test item concentration remained within ± 20 % of the nominal during the test period of 48 hours; therefore, biological results are based on the nominal concentration.
Twenty Daphnia (divided into 4 replicates) were tested each, exposed to 100 mg/l test item and in the control. The immobilisation of the test animals was recorded 24 and 48 hours after treatment. Environmental conditions were recorded. All measured values remained within acceptable ranges.
No immobilisation or any abnormal behaviour of test animals was observed in the control group and no immobilization or any abnormal behavior of the test animals was observed at the test concentration of 100 mg/l after 48 hours of exposure.
All validity criteria were met and therefore the study can be considered as valid.
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