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EC number: 254-959-7 | CAS number: 40530-60-7
- 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:
- 31.1.2000 to 03.02.2000
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Deviations:
- no
- GLP compliance:
- no
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source and lot/batch No.of test material: 99 Labor Mischung 1
- Expiration date of the lot/batch: 01/2005
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: room temperature
- Solubility of the test substance in the solvent/vehicle: insoluble - Analytical monitoring:
- no
- Details on sampling:
- - Concentration for the range-finding test: 0.01 / 0.1 / 1.0 / 10 and 100 mg/l
- Concentrations for the definitive test: 4.3 / 9.4 / 21 / 45 and 100 mg test item /l. - Vehicle:
- no
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Water Flea
- Strain: Daphnia magna Straus
- Method of breeding: Cultures of Daphnia magna are held in glass vessels containing approximately 3 litres of reconstituted water at 18 - 22 °C. The water is renewed partially three times per week. The daphnids are fed with a suspension of green algae (Scenedesmus subspicatus) supplemented by a Tetramine-extract in such quantities that the food is consumed within 24 h.
Pre-treatment:
24 h before the start of the exposure, reproductive daphnids were separated from the young daphnids by sieving all individuals through a 1000 µm sieve. For each test concentration 20 daphnids divided into two groups of 10 animals were used. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- 152 mg CaCO2 /l
- Test temperature:
- 19.4 - 21.0 °C
- pH:
- 8.0
- Nominal and measured concentrations:
- Nominal concentrations: 4.3 / 9.4 / 21 / 45 and 100 mg test item /l.
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 250 ml beakers containing 50 - 100 ml test medium.
- Material, size, headspace, fill volume: 3 litres of reconstituted water at 18 - 22 °C.
- Aeration: No aeration
- Renewal rate of test solution: The water is renewed partially three times per week.
- No. of organisms per vessel: 10 animals per beaker
- No. of vessels per concentration (replicates): All tests were run in duplicate.
- No. of vessels per control (replicates): Duplicate
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Test medium prepared using bidistilled water. The test medium used the following composition: NaHCO3: 65 mg/l, MgSo4*7H2O: 123.3 mg/l, KCL: 5.8 mg/l, CaCl2*2H2O: 294 mg/l, Na2SiO3: 4.3 mg/l, NaNo3: 274 microgr/L, Kh2PO4: 143 microgr/L and K2HPO4: 184 microgr/L.
- Alkalinity: 0.8 mmol*l
- Ca/Mg ratio: 4:1
- Na/K ratio: 10:1
- Culture medium different from test medium: No
OTHER TEST CONDITIONS
- Photoperiod: 14 hours light and 10 hours dark.
TEST CONCENTRATIONS
- Spacing factor for test concentrations: >2
- Range finding study
- Test concentrations for range finding study: 0.01 / 0.1 / 1 / 10 and 100 mg/l
- Results used to determine the conditions for the definitive study: Yes - Reference substance (positive control):
- yes
- Remarks:
- (Potassium dichromate is tested at least every 3 month)
- Duration:
- 24 h
- Dose descriptor:
- EC0
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: no confidence limits
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: no confidence limits
- Duration:
- 24 h
- Dose descriptor:
- EC100
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: no confidence limits
- Duration:
- 48 h
- Dose descriptor:
- EC0
- Effect conc.:
- 9.4 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: No confidence limits
- Duration:
- 48 h
- Dose descriptor:
- EC100
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- No Daphnia were immobilised in the control and in the lower test concentration of 4.3 and 9.4 mg/l after an exposure period of 48 h. At a test concentration of 21 mg/l one daphnid was immobilised after 48 h. Four daphnids were immobilised at 45 mg/l and a total of seven daphnids were immobilised at a test concentration of a 100 mg/l following the 48 h test period.
The EC0 value after 48 h was determined to be 9.4 mg/l.
The EC50 value after 48 h was determined as above 100 mg/l.
The EC100 value after 48 h is higher than 100 mg/l.
No remarkable observations were made concerning the appearance of the test media. - Results with reference substance (positive control):
- For evaluation of the quality of the daphnids clone and the experimental conditions, potassium dichromate is tested every 3 months as a positive control.
The result of the latest positive control test in October 2006 is: EC50= 0.9 mg/l - Validity criteria fulfilled:
- yes
- Conclusions:
- The EC50 of FAT 93503/A to Daphnia magna following an exposure priod of 48 h was determined to be >100 mg/l.
- Executive summary:
The purpose of this acute toxicity study of FAT 93503/A to Daphnia magna Straus was to determine the EC50-value for acute toxicity to aquatic invertebrates (Concentration at which 50 % of the daphnids test population was immobilised). This study was performed according to the OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test). The test duration is 48 h in a static condition test. A range-finding test was done with the following test concentrations: 0.01, 0.1, 1.0, 10 and 100 mg/l. Immobilisation of daphnids occurred at a 100 mg/l, hence the test concentrations for the definitive test were chosen as: 4.3, 9.4, 21, 45 and 100 mg/l. For each test concentration 20 daphnids divided into two groups of 10 animals were used. All test were run in duplicate. Additionally, a blank control without test item was carried out test concentrations were prepared from a stock solution. No daphnids were immobilised in the control and in the lower test concentration of 4.3 and 9.4 mg/l after an exposure period of 48 h. At a test concentration of 21 mg/l one daphnid was immobilised after 48 hours. Four daphnids were immobilised at 45 mg/l and a total of seven daphnids were immobilised at a test concentration of a 100 mg/l following the 48 h test period. The EC0 value after 48 h was determined to be 9.4 mg/l. The EC50 value after 48 h was determined as above 100 mg/l. The EC100 value after 48 h is higher than 100 mg/l. In conclusion, the ecotoxicological classification of FAT 93503/A is "non-toxic" to Daphnia magna following an exposure period of 48 h.
Reference
Description of key information
The acute toxicity study of FAT 93503/A to Daphnia magna Straus is determined according to the OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test). The test duration is 48 hours under static test conditions. A range-finding test was done with the following test concentrations: 0.01, 0.1, 1.0, 10 and 100 mg/l. Immobilisation of daphnids occurred at a 100 mg/l, hence the test concentrations for the definitive test were chosen as: 4.3, 9.4, 21, 45 and 100 mg/l. For each test concentration 20 daphnids divided into two groups of 10 animals were used. All test were run in duplicate. Additionally, a blank control without test item was carried out. Test concentrations were prepared from a stock solution. No daphnids were immobilised in the control and in the lower test concentration of 4.3 and 9.4 mg/l after an exposure period of 48 h. At a test concentration of 21 mg/l one Daphnia was immobilised after 48 h. Four daphnids were immobilised at 45 mg/l and a total of seven daphnids were immobilised at a test concentration of a 100 mg/l following the 48 h test period.
-The EC0 value after 48 h was determined to be 9.4 mg/l.
-The EC50 value after 48 h was determined as above 100 mg/l.
-The EC100 value after 48 hours is higher than 100 mg/l.
In conclusion, the ecotoxicological classification of FAT 93503/A is "non-toxic" to Daphnia magna following an exposure period of 48 h.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 100 mg/L
Additional information
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