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EC number: 459-520-5 | CAS number: 132182-92-4
- 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
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 20 - 22 July 2004
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 004
- Report date:
- 2004
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- no
- GLP compliance:
- yes
Test material
- Reference substance name:
- -
- EC Number:
- 459-520-5
- EC Name:
- -
- Cas Number:
- 132182-92-4
- Molecular formula:
- Hill formula: C7H3F13O CAS formula: C7H3F13O
- IUPAC Name:
- 1,1,1,2,2,3,4,5,5,5-decafluoro-3-methoxy-4-(trifluoromethyl)pentane
Constituent 1
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source and lot/batch No.of test material: Sumitomo 3M Ltd, lot #1
- Purity: 99.96%
- Synonyms: T-7869
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: room temperature in the dark
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: negative control and test substance solutions, taken at start of test, before renewal, after renewal, and at end of test.
- Sampling method: Samples of new or renewal solution were taken from the middle of the flask used to prepare the exposure solution. For old test solutions, equal volumes were taken from the middle of the test vessels and combined.
- Sample storage conditions before analysis: No
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: Test substance (50 µL/L) was added to dilution water in a 1-L Erlenmeyer flasks, which was closed with a stopper to exclude headspace. The flask was stirred 24 h at 20 ± 1 °C. The middle layer of the settled solution was then transferred to test vessels, which were immediately closed with a glass plate with exclusion of any headspace.
- Controls: Dilution water. A test using potassium dichromate as reference substance was done about the time of the present test to verify reproducibility of the system.
- Chemical name of vehicle: no vehicle
- Evidence of undissolved material: Test solutions were clear and colorless throughout the test.
CONCENTRATION OF TEST SUBSTANCE IN TEST MEDIUM:
To establish range of expected test substance concentrations in this study, triplicate 500 mL flasks were set up as above and stirred for 24 and 48 hours at the test temperature (20 ± 1 °C). After settling for one hour, triplicate samples were taken from the middle of the flasks, and then pretreated and analyzed as described in the section on analytical method. The overall mean after 24 hours was 0.356 mg/L, and after 48 hours was 0.369 mg/L.
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Water flea
- Strain/clone: Clone A
- Source: Kurume internal stock originally obtained from University of Sheffield, United Kingdom
- Age of parental stock: 21 days, fed daily with algae (Chlorella vulgaris) at 0.1 - 0.2 mgC/day.
- Age of organisms used in the test: <24 hrs
- Feeding during test: No
Study design
- Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
Test conditions
- Hardness:
- 42.7 mg CaCO3/L
- Test temperature:
- 19.8 - 20.0 °C
- pH:
- 7.5 - 7.7
- Dissolved oxygen:
- 8.5 - 8.7 mg/L
- Conductivity:
- 17.3 mS/m
- Nominal and measured concentrations:
- Loading rate was 50 µL/L (corresponds to ca. 80 mg/L)
Mean measured concentration was 0.368 mg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: glass Petri plate, 8 cm diamter x 5 cm depth, fill volume ca. 250 mL, no headspace
- Type: closed
- Aeration: No
- Renewal rate of test solution: once per 24 h
- No. of organisms per vessel: five
- No. of vessels per concentration: four
- No. of vessels per control: four
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: dechlorinated tap water
- Total organic carbon: 0.4 mg/L
- Particulate matter: <1 mg/L
- Metals:- Pesticides: - Chlorine: <0.01 mg/L
- Alkalinity: 33 mg/L
- Ca/mg ratio: 4.0
- Intervals of water quality measurement: Most recent dilution water quality assay 12 days before start of test
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16h:8h light:dark
- Light intensity: room lighting
- Temperature control: Test flasks were kept in a thermostatted water bath to maintain temperature.
EFFECT PARAMETERS MEASURED: Immobility at 24-hour intervals.
TEST CONCENTRATIONS
- Spacing factor for test concentrations: none
- Justification for using less concentrations than requested by guideline: limit test
- Range finding study : yes
- Test concentrations: test at ca 80 mg/L loading rate and 31.6% dilution thereof
- Results used to determine the conditions for the definitive study: no toxicity, loss of concentration
over time, loss not mediated by presence/absence of organisms - Reference substance (positive control):
- no
Results and discussion
Effect concentrations
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 0.368 mg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: No immobilization observed in saturated solutions.
- Details on results:
- Individual concentrations are presented in the Illustration. Concentration of new or renewal solutions were generally consistent with the value derived from preliminary testing on attainable medium concentration (0.369 mg/L), but are somewhat higher than the pure-water solubility limit of 0.233 mg/L. Pooled concentrations after 24 hours exposure were similarly consistent with starting concentrations. Nevertheless, a time-weighted average concentration was calculated.
- Results with reference substance (positive control):
- A 48-hour acute toxicity test of potassium dichromate was done as part of regular quality checks around the time of this test. The LC50 was 0.283 mg/L. This was within the control range 0.231 ± 0.121 mg/L, where range is twice the standard deviation.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- Control mortality <10 % (none); dissolved oxygen >3 mg/L (8.5 mg/L)
- Conclusions:
- HFE s-601 is not toxic at the limit of water solubility (OECD 202)
- Executive summary:
The toxicity of HFE s-601 to invertebrates was assessed in a semi-static, limit test according to OECD TG 202. Water soluble fractions were prepared every 24 hours at a loading rate of ca. 80 mg/L. Test vessels were entirely closed with no exposure to air. Measured test substance concentrations were generally consistent between the beginning and ending of the 24-hour periods prior to solution renewal. Overall test substance concentration was reported as a time-weighted average. No mortalities were seen among test organisms or controls. The EC50 of HFE s-601 to Daphnia magna was >0.368 mg/L (saturated solution).
The test was conducted under GLP in accord with internationally accepted test guidelines, with analytical confirmation of test substance concentration. Therefore, this test is considered reliable with restrictions and is suitable for Risk Assessment, Classification & Labeling, and PBT Analysis.
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