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EC number: 701-196-7 | 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:
- 07 April 2010 - 23 April 2010
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- The study was carried out according to OECD guideline 202 and GLP. However, the concentrations were not confirmed by a specific analytical method, but by DOC determinations. Analytical measurements from the chronic Daphnia study (Migchielsen, 2013) indicated a significant decrease of the test substance concentration after two days. Nevertheless, the results can be used to conclude that the daphnia is the most sensitive species and the chronic Daphnia study is critical for the dossier. Therefore, the present study can be used with restrictions and a reliability 2 was assigned.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- yes
- Remarks:
- A dilution factor of 2.5 was chosen to encompass the effect levels and the no observable effect levels. This did not affect the study results.
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Deviations:
- yes
- Remarks:
- A dilution factor of 2.5 was chosen to encompass the effect levels and the no observable effect levels. This did not affect the study results.
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- All concentralions and the control were analytically verified in the fresh media (0 h) and old media (48 h) by analysis of organic carbon (DOC,) accordlng to DIN EN 1484) For the old media, separale replicates of the limit concentration and the control without test organisms were prepared and lncubated under test conditions.
- Vehicle:
- no
- Details on test solutions:
- The stock soIution (80 mg/L was welghed out} was freshly prepared with dilution water, treated with ultrasound for 1 h at 45 °C and thereafter stirred with approximately 1100 rpm for 1 h at room temperature. From this stock solution the following nominal test concentrations were prepared: 0.82 - 2.1 - 5.1 - 13 - 32 - 80mg/L (dilution factor 2.5).
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: water flea
- Strain:Daphnia magna STRAUS (Clone 5)
- Source: Institut fuer Wasser-, Boden- und Lufthygiene (WaBoLu) and bred in the test laboratory
- Age at study initiation: 2 - 24h
- Feeding during test: No
ACCLIMATION
- Acclimation period: At least 2h in dilution water - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- 262 mg CaCO3/L
- Test temperature:
- 20.5 °C
- pH:
- 7.6 - 7.9
- Dissolved oxygen:
- 7.2 - 8.9 mg/L
- Nominal and measured concentrations:
- Nominal concentrations: 0 (blank control), 0.82, 2.1, 5.1, 13, 32.0, 80.0 mg/L (dilution factor 2.5).
Measured concentrations: (mean DOC concentration of duplicate measurements) at t = 0h: 4.3 (blank control), 5.5, 6.1, 7.5, 10, 19 and 39 mg DOC/L
Measured concentrations: (mean DOC concentration of duplicate measurements) at t = 48h: 6.5 (blank control), 5.5, 5.9, 7.4, 11, 19 and 41 mg DOC/L
TOC content of the substance taken from the study report of the ready biodegradability test (Brunswik-Titze, 2004): 48.85% (measurement by IFU Gewerbliches Institut für Fragen des Umweltschutzes GmbH, Grießheimer Weg 7a, D-79423 Heitersheim, Germany)
From the DOC measurementsit can be concluded that the DOC concentrations were maintained during the test. - Details on test conditions:
- TEST SYSTEM
- Test vessel: Glass beakers (4 cm ID x 7 cm H), 50 mL capacity
- Fill volume: 20 mL
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
ISO Test water according to OECD 202
OTHER TEST CONDITIONS
- Adjustment of pH: No
- Photoperiod: 16/8 h light/dark cycle
- Light intensity: 20 µE/m^2/s
EFFECT PARAMETERS MEASURED: Immobilisation after 24 and 48h
TEST CONCENTRATIONS
- Spacing factor for test concentrations:2.5
- Range finding study A non GLP preliminary range finding test was conducted under static test conditions with the nominal test concentrations of 10 and 100 mg/L.
- Results used to determine the conditions for the definitive study: 100% immobility was observed at 100 mg/L (nominal) and 55% immobility was observed at 10 mg/L (nominal). - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 12 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% CL 11 - 13 mg/L
- Validity criteria fulfilled:
- yes
- Remarks:
- 1) No observed effects in control group. 2) The dissolved oxygen concentration was > 3 mg/L.
- Conclusions:
- The nominal 48h-EC50 value to Daphnia magna was 12 mg/L
- Executive summary:
The acute toxicity of the test substance to Daphnia magna was investigated according to OECD guideline 202 and GLP.
The nominal 96h-LC50 value to Daphnia magna was 12 mg/L
From the DOC analysis it can be concluded that the DOC concentrations were maintained during the test.
The validity criteria were fulfilled.
The concentrations were not confirmed by a specific analytical method, but by DOC determinations. Analytical measurements from the chronic Daphnia study (Migchielsen, 2013) indicated a significant decrease of the test substance concentration after two days. Nevertheless, the results can be used to conclude that the daphnia is the most sensitive species and the chronic Daphnia study is critical for the dossier. Therefore, the present study can be used with restrictions and a reliability 2 was assigned.
Reference
Table: Immobilization rates of the definitive test after 24 and 48h of exposure
Nominal concentration (mg/L) | Immobilisation (%) | |||||||||
24 h | 48 h | |||||||||
Replicates | Replicates | |||||||||
1 | 2 | 3 | 4 | Mean | 1 | 2 | 3 | 4 | Mean | |
80 | 60 | 100 | 80 | 80 | 80 | 100 | 100 | 100 | 100 | 100 |
32 | 40 | 100 | 100 | 20 | 65 | 80 | 100 | 100 | 80 | 90 |
13 | 40 | 40 | 0 | 20 | 25 | 60 | 60 | 60 | 60 | 60 |
5.1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
2.1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
0.82 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Control | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Description of key information
The nominal 48h-EC50 value to Daphnia magna was 12 mg/L.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 12 mg/L
Additional information
The acute toxicity of the test substance to Daphnia magna was investigated according to OECD guideline 202 and GLP.
The nominal 48h-EC50 value to Daphnia magna was 12 mg/L.
From the DOC analysis it can be concluded that the DOC concentrations were maintained during the test.
The validity criteria were fulfilled.
The concentrations were not confirmed by a specific analytical method, but by DOC determinations. Analytical measurements from the chronic Daphnia study (Migchielsen, 2013) indicated a significant decrease of the test substance concentration after two days. Nevertheless, the results can be used to conclude that the daphnia is the most sensitive species and the chronic Daphnia study is critical for the dossier. Therefore, the present study can be used with restrictions and a reliability 2 was assigned.
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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