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EC number: 418-480-9 | CAS number: 138526-69-9 1-BROM-3,4,5-TRIFLUORBENZOL; 1-BROMO-3,4,5-TRIFLUOROBENZENE
- 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:
- 1995
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Version / remarks:
- 1992
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- 1984
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- Water samples were taken from the control and the 1.0, 3.2, 10, 32 and 100 mg/L test groups at 0 hours and the control and 1.0, 1.8, 3.2, 5.6. 1 0, 1 8, 32, 56 and 100 mg/l test groups at 48 hours (replicates R, and R: pooled) for quantitative analysis.
- Vehicle:
- no
- Details on test solutions:
- The test material (500 mg) was directly weighed into 5 litres (final volume) of reconstituted water and dispersed with the aid of ultrasonic disruption and shaking to prepare the 100 mg/L test concentration. This procedure was carried out as quickly as possible, the head space of the preparation vessel kept to a minimum and the vessel surrounded with dry ice in an order to lower the temperature as much as possible. These precautions were taken in an attempt to prevent losses of test material due to its suspected volatile nature. Dilutions were made from this 100 mg/L concentration in reconstituted water to prepare further test concentrations.
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Water flea
- Strain/clone: Daphnia magna (Straus)
- Source: Institut National de Recherche Chimique Appliquee, France - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- 270 mg CaCO3/L
- Test temperature:
- 21 °C
- pH:
- 7.6 - 7.7
- Dissolved oxygen:
- 7.9 - 8.6 mg/L
- Nominal and measured concentrations:
- Nominal concentrations: 1.0, 1.8, 3.2, 5.6, 10, 18, 32, 56 and 100 mg/L
Analytical measurements revealed that the test samples have been sufficiently stable. - Details on test conditions:
- TEST SYSTEM
- Test vessel: 300 mL conical flasks
- Type: Closed. The test vessels were sealed with ground glass stoppers to reduce evaporation and possible losses of test material.
- Fill volume: 300 mL
- No. of organisms per vessel: 10
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: reconstituted water
OTHER TEST CONDITIONS
- Photoperiod: 16 h light/8 h dark
EFFECT PARAMETERS MEASURED:
The number of immobilised Daphnia were recorded after 24 and 48 hours.
RANGE-FINDING STUDY
- Test concentrations: 0.10, 1.0, 10, 100 mg/L
- Results used to determine the conditions for the definitive study: Immobilisation observed at 10 and 100 mg/L - Reference substance (positive control):
- no
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- 5.8 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% CI 5.2 - 6.4 mg/L
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 3.4 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% CI 2.9 - 3.8 mg/L
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 1.6 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- - Behavioural abnormalities:
no
- Validity criteria fulfilled:
- yes
- Conclusions:
- The acute toxicity to the freshwater invertebrate Daphnia magna has been investigated according to OECD Guideline 202 in a static test. The test substance concentration was monitored during the test. Based on measured concentrations, the 48 h-EC50 was determined to be 3.4 mg/L.
- Executive summary:
The effects of the test item to Daphnia magna were determined in an acute immobilisation test according to OECD 202.
Following a preliminary range-finding study, twenty daphnids (2 replicates of 10 animals) were exposed to an aqueous dispersion of the test material at concentrations of 1.0, 1.8, 3.2, 5.6, 10, 18, 32, 56 and 100 mg/L for 48 hours under static test conditions. The numbers of immobilised daphnids were recorded after 24 and 48 hours.
The 48-hour EC50 for the test material to Daphnia magna based on nominal test concentrations was 4.8 mg/L with 95% confidence limits of 4.0 - 5.7 mg/L. The NOEC was 1.8 mg/L. Analysis of the test solutions throughout the study showed a marked decline in test concentrations and so it was considered justifiable to base the results on measured concentrations also. The 48-hour EC50, based on measured concentrations was 3.4 mg/L with 95% confidence limits of 2.9 - 3.8 mg/L. The NOEC was 1.6 mg/L.
Reference
Description of key information
The acute toxicity to the freshwater invertebrate Daphnia magna has been investigated according to OECD Guideline 202 in a static test. The test substance concentration was monitored during the test. Based on measured concentrations, the 48 h-EC50 was determined to be 3.4 mg/L (reference 6.1.3-1).
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 3.4 mg/L
Additional information
The effects of the test item to Daphnia magna were determined in an acute immobilisation test according to OECD 202.
Following a preliminary range-finding study, twenty daphnids (2 replicates of 10 animals) were exposed to an aqueous dispersion of the test material at concentrations of 1.0, 1.8, 3.2, 5.6, 10, 18, 32, 56 and 100 mg/L for 48 hours under static test conditions. The numbers of immobilised daphnids were recorded after 24 and 48 hours.
The 48-hour EC50 for the test material to Daphnia magna based on nominal test concentrations was 4.8 mg/L with 95% confidence limits of 4.0 - 5.7 mg/L. The NOEC was 1.8 mg/L. Analysis of the test solutions throughout the study showed a marked decline in test concentrations and so it was considered justifiable to base the results on measured concentrations also. The 48-hour EC50, based on measured concentrations was 3.4 mg/L with 95% confidence limits of 2.9 - 3.8 mg/L. The NOEC was 1.6 mg/L (reference 6.1.3-1).
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