Registration Dossier
Registration Dossier
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 296-229-0 | CAS number: 92368-90-6
- 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 2000-10-17 and 2000-10-19
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Version / remarks:
- 1992
- Deviations:
- yes
- Remarks:
- The EC50 value was calculated as geometric mean of EC0 and EC100 and furthermore the lower concentrations were not analytically determined.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- yes
- Remarks:
- The EC50 value was calculated as geometric mean of EC0 and EC100 and furthermore the lower concentrations were not analytically determined.
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- Sampling schedule of the chemical analysis:
- Stock solution: at 0 hours
- Control: at 0 and 48 hours
- Test concentrations: at 0 and 24 hours
The test concentrations 0.5, 1 and 2 mg/L were not analytically determined as the measured concentrations to be expected were below the quantitation limit of the TOC determination method (2 mg/L).
- Stock solution: The stock solution was prepared to give the desired series of test concentrations. To achieve this 54.2 mg of the test substance were added to 1 litre of dilution water. - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Preparation of the test solution: The dilution water was treated with an ultra turrax for 60 seconds and afterwards stirred for 24 h an a magnetic stirrer.
- Test water: M4 Medium
- Method: stock solution
- Controls: yes. Blank control
- Evidence of undissolved material: yes. The undissolved particles of the test substance were removed by filtration. - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- ACCLIMATION
- Acclimation period: A population of parthenogenetic females of synchronized age structure is maintained since more than 15 years in the test facility.
- Acclimation conditions: constant temperature conditions (20 +/- 1 °C) at a 16 : 8 hour
light-dark photoperiod (illumination: < 1000 lux). The culture water (so-called “M4 medium”) is partly renewed once a week.
- Type and amount of food: The Daphnia are exclusively fed with unicellular green algae (Scenedesmus subspicatus CHODAT)
- Feeding frequency: ad libitum
- Health during acclimation (any mortality observed): Mortalities of parent Daphnia during the culture period are recorded daily in a semiquantitative way, no mortality is observed. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Post exposure observation period:
- Not performed
- Hardness:
- 15.4 °dH (274.9 mg/L CaCO3)
- Test temperature:
- 20 - 20.5 °C
- pH:
- 7.6 - 7.8
- Dissolved oxygen:
- 8.4 - 8.7 mg/L
95.1 - 98.4 % - Salinity:
- No data
- Conductivity:
- No data
- Nominal and measured concentrations:
- - Nominal concentrations: 0.5, 1, 2, 4 and 8 mg/L
- Measured concentrations: Measured concentrations of the nominal concentrations 4 and 8 mg/L, which were checked for their TOC, ranged from 105 -120 % of nominal values at 0 hours, and correspond to 120% of nominal values at 24 hours, respectively. TOC values were calculated corresponding to the analytical recovery rate of the highest test concentration as the concentration to be measured was below the quantitation limit of the TOC method (2 mg/L). - Details on test conditions:
- TEST SYSTEM
- Test vessel: Glass beakers
- Volume of the test vessels: 50 mL
- Aeration: None
- Type of system: static
- No. of organisms per vessel: 10 neonates per vessel
- No. of vessels per concentration (replicates): 2
- No. of vessels per control (replicates): 0
- No. of vessels per vehicle control (replicates): 2
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Reconstituted water (so-called “M4 medium”, originally described in Water Research 24 (9): 1157-1167), prepared according to the recommendations of Bundesgesundheitsamt Berlin. This standard dilution water is used for both, the maintenance of the test animals and the preparation of stock and test solutions of the test substance.
- Culture medium different from test medium: No
- Intervals of water quality measurement: Temperature, oxygen, and pH value were measured after 24 and 48 hours.
OTHER TEST CONDITIONS
- Adjustment of pH: No
- Photoperiod: 16 : 8 hours (light-dark)
- Illumination: < 1000 lux
EFFECT PARAMETERS MEASURED: Alteration of the normal mobility behaviour and the loss of locomotory actions of the neonates, observed at 24 and 48 hours.
TEST CONCENTRATIONS
- Range finding study: yes
- Test concentrations (nominal): 0.5, 1, 2, 4 and 8 mg/L
- Measured concentrations: Measured concentrations of the nominal concentrations 4 and 8 mg/L, which were checked for their TOC, ranged from 105 — 120 % of nominal values at 0 hours, and correspond to 120% of nominal values at 24 hours, respectively. TOC values were calculated (corresponding to the analytical recovery rate of the highest test concentration) as the concentration to be measured was below the quantitation limit of the TOC method (2 mg/L). - Reference substance (positive control):
- no
- Duration:
- 24 h
- Dose descriptor:
- EC0
- Effect conc.:
- 1 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 24 h
- Dose descriptor:
- EC100
- Effect conc.:
- 2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- EC0
- Effect conc.:
- 1.2 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- EC100
- Effect conc.:
- 2.3 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Key result
- Duration:
- 48 h
- Dose descriptor:
- other: Geometric mean EC0/EC100
- Effect conc.:
- 1.7 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- Behavioural abnormalities:
- Mortality of control: No mortality
- Other adverse effects control: No found
- Abnormal responses: No data was provided.
- Effect concentrations exceeding solubility of substance in test medium: No - Results with reference substance (positive control):
- Not performed
- Reported statistics and error estimates:
- Not performed
- Validity criteria fulfilled:
- yes
- Conclusions:
- The EC50 was calculated to be 1.7 mg/L (geom. mean of EC100 and EC0), the EC100 was determined to be 2.3 mg/L (geom. mean measured) and the EC0 was determined to be 1.2 mg/L (geom. mean measured).
- Executive summary:
In a static key immobilization test Daphnia magna (< 24 h old) were exposed to the test item for 48 hours according to OECD 202 (1992) under GLP conditions. The Daphnia were exposed to a range of concentrations, nominally 0.5, 1, 2, 4 and 8 mg/L of the test substance dissolved in water. Measured concentrations ranged from 105 - 120 % of nominal values at 0 hours, and correspond to 120% of nominal values at 48 hours, respectively. The EC50 was calculated to be 1.7 mg/L (geom. mean of EC100 and EC0), the EC100 was determined to be 2.3 mg/L (geom. mean measured) and the EC0 was determined to be 1.2 mg/L (geom. mean measured).
Reference
Table 1: Immobilisation of Daphnia magna after 24 and 48 h
Nominal concentration test substance [mg/L] |
Immobile daphnids |
|||
absolute |
Cumulative % |
|||
24 h |
48 h |
24 h |
48 h |
|
Control |
0 |
0 |
0 |
0 |
0.5 |
0 |
0 |
0 |
0 |
1 |
0 |
0 |
0 |
0 |
2 |
20 |
0 |
100 |
100 |
4 |
20 |
0 |
100 |
100 |
8 |
20 |
0 |
100 |
100 |
Table 2: Results - Analysis
Nominal concentration test substance [mg/L] |
Chemical analysis |
|||
TOC values [mg/L] |
Test substance [mg/L] |
|||
0 h |
48 h |
0 h |
48 h |
|
Control |
< 2 |
< 2 |
- |
- |
0.5 |
0.44 |
0.5 |
0.53 |
0.6 |
1 |
0.9 |
1 |
1.1 |
1.2 |
2 |
1.8 |
2 |
2.1 |
2.4 |
4 |
4 |
4* |
4.8 |
4.8* |
8 |
7 |
8* |
8.4 |
9.6* |
TOC values were calculated (corresponding to the analytical recovery rate of the highest test concentration) as the concentration to be measured was below the quantitation limit of the TOC method ( 2 mg/L).
* The figures marked by asterisk have already been measured after 24 hours of exposure because of early 100 % immobilisation rates of the daphnids.
Description of key information
In a static immobilization test to Daphnia magna according to OECD 202 the EC50 was determined to be 1.7 mg/L after 48 hours exposure under GLP conditions.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 1.7 mg/L
Additional information
A static Daphnia magna immobilization test were performed according to OECD 202 (1992) under GLP conditions. The Daphnia were exposed to a range of concentrations, nominally 0.5, 1, 2, 4 and 8 mg/L of the test substance dissolved in water. Measured concentrations ranged from 105 - 120 % of nominal values at 0 hours, and correspond to 120% of nominal values at 48 hours, respectively. The EC50 was calculated to be 1.7 mg/L (geom. mean of EC100 and EC0), the EC100 was determined to be 2.3 mg/L (geom. mean measured) and the EC0 was determined to be 1.2 mg/L (geom. mean measured).
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.

EU Privacy Disclaimer
This website uses cookies to ensure you get the best experience on our websites.