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EC number: - | 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 03 - Jul 18, 2018
- 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
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- At the start of the exposure and at the renewal (24 and 48 h), samples of the freshly prepared test item concentrations were taken and analyzed.
At renewal and at the end of the exposure (24 and 48 h), sampled of the 24 h old media were taken directly from the test vessels and analyzed. - Vehicle:
- yes
- Remarks:
- dilution water
- Details on test solutions:
- Saturated solution
A saturated solution (100 mg test item/L were weighed out) was freshly prepared with culture medium (see Table 2) one day prior to the start of the exposure (day -1) and prior to the renewal of the test solutions (day 0 hours). The stock solution was stirred for 24 ± 1 hour at approx. 1100 rpm at room temperature. After a separation phase of 1 hour at room temperature, the test solution was removed from the middle of the flask. The test item solution was checked via laser beam (Tyndall effect) for undissolved test item. No Tyndall-effect was detected and no undissolved test item was present during the test.
Test concentrations
The saturated solution and further 4 dilution levels of the saturated solution in a geometric series with a separation factor of 2, prepared by dilution of the saturated solution with dilution water, were tested as follows:
6.25 - 12.5 - 25.0 - 50.0 - 100% of the saturated solution, corresponding to the geometric mean measured concentrations: 45.6 – 85.2 – 388 – 1223 – 2836 µg/L.
The test item concentrations mentioned above were selected based on the results of a non-GLP preliminary range finding test.
Control
Dilution water without test item incubated under the same conditions as the test groups - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Daphnia magna STRAUS (Clone 5)
- Source: Institut für Wasser-, Boden und Lufthygiene (WaBoLu), Berlin, Germany
- Age: < 24 h
FEEDING DURING TEST
- Food type: 5 x per week ad libitum with a mix of unicellular green algae - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- 0 h: 262 mg CaCO3/L
24 h: 258 mg CaCO3/L - Test temperature:
- 19.0 - 20.3 °C
- pH:
- 0 h: 8.27
24 h: 7.90 - Dissolved oxygen:
- 0 h: 9.41 mg/L
24 h: 9.06 mg/L - Conductivity:
- 0 h: 603 µS/cm
24 h: 619 µS/cm - Details on test conditions:
- Test vessels: Glass beakers, 50 mL capacity, loosely covered with watch glasses
Test volume: 20 mL
Number of daphnids and replicates:
20 daphnids, divided into 4 replicates, each with 5 daphnids were used for each concentration level and control.
Application:
20 g test solution per replicate was weighed out into each test vessel. This corresponds to 20 mL per test vessel. The daphnids were inserted with a small amount of dilution water (start of the exposure) or test solution (water renewal) by pipette.
Renewal of the test solutions:
The test solutions were renewed after 24 h. For this purpose, a second set of test vessels was filled with the freshly prepared test solutions and the daphnids were transferred by pipette. - Reference substance (positive control):
- no
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 61.3 µg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% CL: 58.9 - 63.8
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- 85.2 µg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% CL: 45.6 - 349
- Results with reference substance (positive control):
- - Results with reference substance valid?
Yes
- Limit test: No
- ECx: EC50 (24 hours): 0.6 - 2.4 mg/L (according to AQS 9/2); EC50 (24 hours): 0.6 - 2.1 mg/L (according to OECD 202)
- Other: An acute immobilization test was conducted with the reference substance once per month to prove the validity of the test system. - Validity criteria fulfilled:
- yes
- Conclusions:
- The toxic effect of the test item to Daphnia magna was assessed in a semi-static concentration-response test. The 48-hour EC10 was determined to be 47.1 µg test item/L and the 48-hour EC50 value was calculated to be 61.3 µg test item/L. The initial concentrations and the maintenance of the exposure concentrations during the test were verified in the analytical part. All reported results refer to geometric mean measured concentrations.
Reference
Purpose
The purpose of this study was to determine the influence of the test
item on the mobility of Daphnia magna. For this purpose, young daphnids
(< 24 hours old) were exposed to various concentrations under defined
conditions for 48 hours.
Study Design
The information 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 study was conducted
under semi-static conditions over a period of 48 hours with a saturated
solution of the test item with a nominal loading of 100 mg test item/L
and further four dilution levels (nominal: 6.25 – 12.5 – 25.0 – 50.0 -
100%) of the saturated solution prepared in a geometric series with a
separation factor of 2.
Twenty daphnids (divided into 4 replicates with 5 daphnids each) were
exposed to each dilution level and the control.
The concentrations of the test item were analytically verified via
LC-MS/MS in the fresh media at the start of the exposure and at the
renewal of the test solutions (0 and 24 hours) and in the old media at
the renewal and at the end of the test (24 and 48 hours) in all dilution
levels and in the control.
The recorded effects were the mobility of the daphnids after 24 and 48
hours. The test method of application and the test system are
recommended by the test guidelines and Daphnia magna is the recommended
test species.
The purpose of the analytical part of this study was to verify the
concentrations of the test item in the test medium.
Results
Biological Results
The percentage of immobility, determined in all dilution levels of the
test item and in the control after 24 and 48 hours is given below:
Mean Measured Concentration [mg test item / L] |
% of immobilised daphnids after |
|
24 hours |
48 hours |
|
2836 |
100 |
100 |
1223 |
100 |
100 |
388 |
100 |
100 |
85.2 | 50 |
100 |
45.6 |
0 |
5 |
Control | 0 |
0 |
The effect concentrations (EC10 / 50 / 100), based on the
geometric mean measured concentrations of the test material are given
below:
Effect concentrations |
Duration / [h] |
Geometric Mean measured the test material concentrations / [µg/L] |
EC10 (with confidence limits) |
24 |
72.1 (< 45.6 - 334) |
48 |
47.1 (< 45.6 – 49.5) |
|
EC50 (with 95% confidence limits) |
24 |
85.2 (45.6 - 349) |
48 |
61.3 (58.9 – 63.8) |
|
EC100 |
24 |
388 |
48 |
85.2 |
Analytical Results
The concentrations of the test item were analytically verified via
LC-MS/MS in the fresh media at the start of the exposure and at the
renewal of the test solutions (0 and 24 hours) and in the old media at
the renewal and at the end of the test (24 and 48 hours) in all dilution
levels and in the control.
Sampling |
0 h (fresh) |
24 h (old) |
24 h (fresh) |
48 h (old) |
|||
Dilution level of the saturated solution [%] |
Measured conc. [µg/L] |
Measured conc. [µg/L] |
[%] |
Measured conc. [µg/L] |
Measured conc. [µg/L] |
[%] |
Geometric mean measured concentration [mg/L] |
100 |
5174 |
1554 |
30 |
Not determined due to 100 % mortality after 24 hours |
2836 |
||
50 |
2125 |
704 |
33 |
1223 |
|||
25 |
862 |
175 |
20 |
388 |
|||
12.5 |
448 |
24.5 |
5 |
481 |
< LOQ |
85.2 |
|
6.25 |
192 |
< LOQ |
225 |
< LOQ |
45.6 |
||
Control |
< LOQ |
< LOQ |
< LOQ | < LOQ |
Conclusion
The toxic effect of the test item to Daphnia magna was assessed in a
semi-static concentration-response test. The 48-hour EC10was
determined to be 47.1 µg test item/L and the 48-hour EC50 value was
calculated to be 61.3 µg test item/L.
The initial concentrations and the maintenance of the exposure
concentrations during the test were verified in the analytical part. All
reported results refer to geometric mean measured concentrations.
Description of key information
OECD 202: EC50 (48 h) = 61.3 µg/L
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 61.3 µg/L
Additional information
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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