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EC number: 446-630-3 | CAS number: 181587-01-9
- 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
Bioaccumulation: aquatic / sediment
Administrative data
Link to relevant study record(s)
- Endpoint:
- bioaccumulation in aquatic species: fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 26 Jan - 14 Feb 2004
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 305 B (Bioaccumulation: Semi-static Fish Test)
- Version / remarks:
- adopted in 1996
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Ministry of Health, Welfare and Sport, The Netherlands, 22 Apr 2002
- Radiolabelling:
- yes
- Details on sampling:
- - Sampling intervals/frequency for test organisms: At each sampling, two fish were collected from the control and four fish from each test concentration. During the uptake phase, fish were collected at test start and after 3, 6, 12, 24, 48, 72, 102, 126 and 144 h. During the depuration phase, fish were collected in 24 h intervals.
- Sampling intervals/frequency for test medium samples: 10 mL of the test solutions were sampled from each test aquarium. During the uptake phase, water samples were taken at test start and after 24, 48, 72, 102, 126 and 144 h. During the depuration phase, water samples were taken every 24 h.
- Sample storage conditions before analysis: Water samples were directly transferred to scintillation flasks for radioanalysis. Fish samples were stored at – 20 °C.
- Details on sampling and analysis of test organisms and test media samples: The whole fish were individually combusted in a Packard sample oxidizer for 2 min. The resulting 14CO2 was trapped in 6 mL of Carbosorb solution and eluted into a scintillation vial for radioanalysis. The 10 mL water samples were mixed with 10 mL of insta-gel XF (Packard) for analysis. - Vehicle:
- yes
- Details on preparation of test solutions, spiked fish food or sediment:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: The stock solution for low concentration was prepared from one primary stock solution of 100 mg of test substance non-radiolabeled per liter of dilution water plus acetone 2%. 50 mL of this solution was transferred and made up to 500 mL with dilution water and then, 43 µL of [14C]-test substance was added to this solution, resulting in a solution with 10 mg of test substance/L and 51,141,328 dpm/mg of radioactivity. Then, 15 mL of this solution was transferred to the test aquarium, resulting in 0.01 mg of test substance/L and 32,537,000 dpm/mg. The average concentration of test solution during the assimilation phase confirmed by radioanalysis was 0.01 mg/L.
The stock solution for high concentration was prepared by transferring 43 µL of [14C]-test substance and 50 mg of active ingredient (non-radiolabeled test substance) in 500 mL of dilution water plus acetone 2 %, resulting in a solution with 100 mg of test substance/L and 5,114,132 dpm/mg of radioactivity. Then, 15 mL of this solution was transferred to the test aquarium, resulting in 0.10 mg of test substance/L and 3,771,460 dpm/mg. The average concentration during the uptake phase confirmed by radioanalysis was 0.11 mg/L.
- Controls: In the LC50 preliminary test, the concentration of 0.2% acetone did not show any effect in fish, so a solvent control in the bioconcentration test was not necessary.
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): acetone
- Concentration of vehicle in test medium (stock solution and final test solution(s) at different concentrations and in control(s)): 0.004% - Test organisms (species):
- Danio rerio (previous name: Brachydanio rerio)
- Details on test organisms:
- TEST ORGANISM
- Common name: zebrafish
- Source: The fish were acquired from suppliers maintained and acclimated under controlled laboratorial conditions.
- Weight at study initiation (range): 0.321 - 0.933 g (uptake phase), 0.316 - 0.871 g (depuration phase)
- Description of housing/holding area: 250 L tanks
- Feeding during test
- Food type: standard commercial fish food TetraMin with 45% of protein, 1 - 2 h before test solution renewal
ACCLIMATION
- Acclimation period: 72 h
- Acclimation conditions (same as test or not): same as test
- Type and amount of food: standard commercial fish food TetraMin with 45% of protein - Route of exposure:
- aqueous
- Test type:
- semi-static
- Water / sediment media type:
- natural water: freshwater
- Total exposure / uptake duration:
- 6 d
- Total depuration duration:
- 4 d
- Test temperature:
- 23.4 - 24.1 °C
- pH:
- 7.5 - 7.68
- Dissolved oxygen:
- 7.0 - 7.18 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: aquarium
- Material, size, fill volume: stainless steel, 45 x 25 x 25.5 cm, 15 L
- Aeration: Only the dilution water was aerated.
- Renewal rate of test solution (frequency/flow rate): every 24 h
- No. of organisms per vessel: 80 fish per test aquarium, 40 fish per control aquarium
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Water distributed by the Municipal Service of Water and Sewage Treatment was dechlorinated and aerated before use.
- Intervals of water quality measurement: Temperature, dissolved oxygen and pH were recorded at test start and after 24, 48, 72, 102, 126 and 144 h during the uptake phase and at the start and every 24 h during the depuration phase.
OTHER TEST CONDITIONS
- Photoperiod: 16 h light
RANGE-FINDING / PRELIMINARY STUDY
- In order to find the high and low concentrations for the bioconcentration test, a 96-hour toxicity test was carried out in semi-static system according to OECD Methodologies, in order to determine the acute toxicity to Danio rerio.
- Results used to determine the conditions for the definitive study: The 96 h LC50 value of the test substance was 1.06 mg/L. - Type:
- BCF
- Value:
- 8.92 dimensionless
- Basis:
- whole body w.w.
- Calculation basis:
- steady state
- Remarks on result:
- other: Conc.in environment / dose:0.01 mg/L
- Type:
- BCF
- Value:
- 10.24 dimensionless
- Basis:
- whole body w.w.
- Calculation basis:
- steady state
- Remarks on result:
- other: Conc.in environment / dose:0.11 mg/L
- Elimination:
- yes
- Parameter:
- other: DT50 for 0.01 mg/L
- Depuration time (DT):
- 31.06 h
- Elimination:
- yes
- Parameter:
- other: DT50 for 0.11 mg/L
- Depuration time (DT):
- 35.46 h
- Elimination:
- yes
- Parameter:
- other: DT90 for 0.01 mg/L
- Depuration time (DT):
- 103.19 h
- Elimination:
- yes
- Parameter:
- other: DT90 for 0.11 mg/L
- Depuration time (DT):
- 117.8 h
- Details on kinetic parameters:
- - Uptake rate constant (k1): 0.1991 ± 0.0557 (low concentration), 0.2002 ± 0.0768 (high concentration)
- Depuration (loss) rate constant (k2): 0.0223 ± 0.0013 (low concentration), 0.0195 ± 0.0045 (high concentration)
- Computation/data analysis: The parameters were determined by BIOCINE software. - Validity criteria fulfilled:
- no
- Remarks:
- See Table 1 in 'any other information on results incl. tables'
Reference
- Mortality of control: 4.5% during the test period
- Test substance accumulation in whole fish after six days of exposure: 0.089 and 1.09 mg/kg for low and high concentrations, respectively.
- Elimination by the end of the depuration period: 88.76% and 83.49% elimination in fish kept at low and high concentrations, respectively.
Table 1: Validity criteria for OECD 305
Criterion from the guideline |
Outcome |
Validity criterion fulfilled |
The temperature variation is less than ± 2 °C |
Temperature ranged from 23.4 to 24.1 °C |
Yes |
The concentration of dissolved oxygen does not fall below 60% saturation |
Oxygen ranged from 6.99 to 7.18 mg/L ( ~83% - 85% saturation) |
Yes |
The concentration of the test substance in the chambers is maintained within ± 20% of the mean of the measured values during the uptake phase |
Concentrations ranged from 86% - 143% for the low concentration, and from 66% - 144% for the high concentration of the respective mean measured value |
No |
The mortality or other adverse effects/disease in both control and treated fish is less than 10% at the end of the test; where the test is extended over several weeks or months, death or other adverse effects in both sets of fish should be less than 5% per month and not exceed 30% in all. |
Fish mortality was 4.5% |
Yes |
Description of key information
BCF = 8.92 - 10.24 for Danio rerio (OECD 305 B)
Key value for chemical safety assessment
Additional information
The bioaccumulation characteristics of the substance were investigated in one study according to OECD 305 B and GLP. In a semi-static system, zebrafish (Danio rerio) were exposed to 0.01 mg/L (low concentration) and 0.11 mg/L (high concentration) for 6 days. The exposure period was followed by a depuration phase of 4 days. The depuration half-life (DT50) of the substance was 31 h and 35.5 h for the low and high concentration, respectively. The BCF was determined to be 8.92 for the low and 10.24 for the high concentration.
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