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EC number: 230-907-9 | CAS number: 7365-45-9
- 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 fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- from 2012-08-07 to 2014-02-03
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- Version / remarks:
- 1992
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 100 mg/L
- Sampling method: Three replicate samples were taken from the treatment and the control groups at the start and at the end of the test.
- Sample storage conditions before analysis: at room temperature - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: The test solution used in the test was prepared by mechanical dispersion. An amount of 0.5 g test item was dissolved in 5000 mL dilution water (ISO medium) in order to give the concentration of 100 mg/L.
- Evidence of undissolved material: no
- Control: The dilution water (ISO medium) without addition of test item was used as control solution. - Test organisms (species):
- Danio rerio (previous name: Brachydanio rerio)
- Details on test organisms:
- TEST ORGANISM
- Common name: Zebrafish
- Source: Fish Laboratory of TOXI-COOP ZRT. (8237 Tihany, Klebelsberg K. u. 3., Hungary)
- Age at study initiation: juveniles
- Length at study initiation: 2.0 ± 1 cm
- Feeding during test: no
ACCLIMATION
- Acclimation period: not required as bred in laboratory
- Acclimation conditions: same
- Type and amount of food: appropriate, commercial food
- Health during acclimation (any mortality observed): no mortality occurred in seven days before the start of experiment. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 96 h
- Post exposure observation period:
- none
- Hardness:
- approximate theoretical total hardness of 249 mg/L (as CaCO3)
- Test temperature:
- 23.3 – 23.8 °C
- pH:
- 7.52 – 7.92 (without adjustment)
- Dissolved oxygen:
- 84.6 – 97.5 %
- Nominal and measured concentrations:
- - Nominal concentration: 100 mg/L
- Measured concentrations: three replicates at the start and at the end of the test.
- 98.8, 99.1 and 99.5 mg/L (99 - 100 % of nominal concentration) at start of the test
- 102.5, 102.5 and 102.7 mg/L (103 % of nominal concentration) at the end of the test - Details on test conditions:
- TEST SYSTEM
- Test vessel: aquarium
- Type: closed
- Volume: 5 L
- Aeration: no
- No. of organisms per vessel: 10
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 1
- Biomass loading rate: <= 1.0 g/L
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: reconstituted water (ISO medium, prepared according to Annex 2 of the OECD guideline 203)
- Culture medium different from test medium:
- Intervals of water quality measurement: The water temperature, pH value and dissolved oxygen concentration were determined at the start of the test and on the subsequent days (once daily) in the test concentration and the control.
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16 h light and 8 h dark
EFFECT PARAMETERS MEASURED
Observations at approximately 3, 6, 24, 48, 72 and 96 hours after start of the test for signs of intoxication and mortality.
The body length of each fish were measured at the end of the test in order to check their compliance with the size range recommended for the species by the test guideline (OECD No. 203). The measured values were within the range of 2.10 - 2.40 cm.
TEST CONCENTRATIONS
- Range finding study: yes
- Test concentrations: 100 mg/L
- Results used to determine the conditions for the definitive study: No mortality observed in a pre-experiment with 100 mg/L - Reference substance (positive control):
- no
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Details on results:
- - Behavioural abnormalities: not observed
- Observations on body length and weight: Observed, but normal development
- Other biological observations: no
- Mortality of control: no
- 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 effects observed.
The 96h-LC50 was determined to be > 100 mg/L and the NOEC was determined to be >= 100 mg/L. - Results with reference substance (positive control):
- not applicable
- Reported statistics and error estimates:
- not applicable as no effects observed
- Sublethal observations / clinical signs:
Table 1: Cumulative mortality data in the definitive test
Test Group
Cumulative mortality
(initial population = 10 fish / test group)3h
6h
24h
48h
72h
96h
Control
0
0
0
0
0
0
100 mg/L
0
0
0
0
0
0
- Validity criteria fulfilled:
- yes
- Conclusions:
- The acute toxicity of the test substance to Zebrafish (Brachydanio rerio) was determined according to OECD 203 (1992) under GLP conditions. The 96h-LC50 was determined to be > 100 mg/L.
- Executive summary:
The acute toxicity of the test substance to Zebrafish (Brachydanio rerio) was determined according to OECD 203 (1992) under GLP conditions. Young fish were exposed to aqueous test media containing the test item for 96 hours. Based on results obtained in a preliminary experiment fish were exposed to a single concentration of 100 mg/L (limit test). A concurrent control group was run. A static test was performed as the test item was previously shown to be stable in the test medium over the test period. The measured concentration were determined between 99 - 103 % of the nominal concentration. The analytically measured test item concentration remained within ± 20 % of the nominal during the test period of 96 hours; therefore the biological results are based on the nominal concentration. The fish were observed at approximately 3, 6, 24, 48, 72 and 96 hours after start of the test for signs of intoxication and mortality. Measurements of pH, dissolved oxygen and temperature were carried out daily. All validity criteria were met. Mortality and any sub-lethal effects were not observed during the 96-h exposure period either in the treated or in the control group. The 96h-LC50 was determined to be > 100 mg/L.
Reference
Description of key information
The acute toxicity of the test substance to Zebrafish (Brachydanio rerio) was determined according to OECD 203 (1992) under GLP conditions. The 96h-LC50 was determined to be > 100 mg/L (reference 6.1.1-1).
Key value for chemical safety assessment
Additional information
The acute toxicity of the test substance to Zebrafish (Brachydanio rerio) was determined according to OECD 203 (1992) under GLP conditions. Young fish were exposed to aqueous test media containing the test item for 96 hours. Based on results obtained in a preliminary experiment fish were exposed to a single concentration of 100 mg/L (limit test). A concurrent control group was run. A static test was performed as the test item was previously shown to be stable in the test medium over the test period. The measured concentration were determined between 99 - 103 % of the nominal concentration. The analytically measured test item concentration remained within ± 20 % of the nominal during the test period of 96 hours; therefore the biological results are based on the nominal concentration. The fish were observed at approximately 3, 6, 24, 48, 72 and 96 hours after start of the test for signs of intoxication and mortality. Measurements of pH, dissolved oxygen and temperature were carried out daily. All validity criteria were met. Mortality and any sub-lethal effects were not observed during the 96-h exposure period either in the treated or in the control group. The 96h-LC50 was determined to be > 100 mg/L.
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