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EC number: 948-916-8 | CAS number: -
- 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:
- 2-6 September 2019
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 019
- Report date:
- 2019
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- Apr. 2004
- Deviations:
- yes
- Remarks:
- Uncritical deviation: no acclimatation period. Switching from M4-medium (husbandry) to Dilution water (test) has been shown not to cause any detrimental effects for test daphnia, therefore no acclimation period of 48 h was performed.
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Version / remarks:
- May 2008
- Deviations:
- yes
- Remarks:
- idem as above
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- vegetable oil mono- and polyunsaturated C16-C22 triglycerides
- Molecular formula:
- C51H92O6 to C69H128O6
- IUPAC Name:
- vegetable oil mono- and polyunsaturated C16-C22 triglycerides
- Reference substance name:
- dimers of vegetable oil mono- and polyunsaturated C16-C22 triglycerides
- Molecular formula:
- C102H186O12 to C138H256O12
- IUPAC Name:
- dimers of vegetable oil mono- and polyunsaturated C16-C22 triglycerides
- Reference substance name:
- trimers of vegetable oil mono- and polyunsaturated C16-C22 triglycerides
- Molecular formula:
- C153H280O18 to C207H388O18
- IUPAC Name:
- trimers of vegetable oil mono- and polyunsaturated C16-C22 triglycerides
- Reference substance name:
- tetramers and higher oligomers of vegetable oil mono- and polyunsaturated C16-C22
- Molecular formula:
- C204H374O24 and higher oligomers
- IUPAC Name:
- tetramers and higher oligomers of vegetable oil mono- and polyunsaturated C16-C22
- Test material form:
- liquid: viscous
Constituent 1
Constituent 2
Constituent 3
Constituent 4
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- - Sampling method: the content of the test item was estimated in the test solutions at the start and the end (48 h) of the test
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: The water-accommodated fraction (WAF) was prepared for the test. This was done by mixing the nominal load of 100 mg/L resp. 108.7 µL/L test item (based on a density of 0.92 g/mL stated in the SDS) with the corresponding amount of dilution water and stirring moderately for 24 hours at 120 rpm on a magnetic stirrer. The lower phase was used unfiltered as test solution
- Evidence of undissolved material: No turbidity of the test solution was visible.
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Species: Daphnia magna Straus
- Strain: Berlin
- Age at study initiation: 0-24 hours
- Sex: female
- Source: Umweltbundesamt Berlin
- Feeding during test: no
- Food type: Desmodesmus subspicatus - during breeding only
ACCLIMATION
- Acclimation period: none: Switching from M4-medium (husbandry) to Dilution water (test) has been shown not to cause any detrimental effects for test daphnia, therefore no acclimation period of 48 h was performed.
METHOD FOR PREPARATION AND COLLECTION OF EARLY INSTARS OR OTHER LIFE STAGES, INCLUDING CULTURING CONDITIONS: Daphnia magna was bred in the LAUS GmbH throughout the year. The animals are kept for the use in toxicity tests. They multiply by parthenogenesis, thus being genetically identical. The keeping is performed similar to the method described in the OECD guideline.
Vessels preserving glasses, nominal volume 2 L
Medium M4-Medium (recipe of ELENDT)
Food green algae (Desmodesmus subspicatus)
Medium renewal twice a week
Photo period 16/8 hours, using neon tubes
Temperature 20 +/- 2 °C
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
- Remarks on exposure duration:
- Observations after 24 and 48 h.
- Post exposure observation period:
- not applicable
Test conditions
- Hardness:
- no data
- Test temperature:
- 18.9 - 20.5°C
- pH:
- 7.5 - 7.6
- Dissolved oxygen:
- 8.3 - 8.4 mg/L
- Salinity:
- not applicable
- Conductivity:
- no data
- Nominal and measured concentrations:
- Loading rate: 100 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: glass beakers
- Type: open
- Fill volume: 50 mL beakers containing 20 +/- 5 mL test solution
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water:For preparation of the dilution water demineralised water was used, with the following specifications: 293.80 mg/L CaCl2*2H2O, 123.30 mg/L MgSO4*7H2O, 64.80 mg/L NaHCO3 and 5.80 mg/L KC. Deviations from the nominal weighted loads were less than 5 %. Exact values are rec-orded in the raw data. After preparation, the dilution water was aerated and the pH was measured. The pH was 7.6.
- Total organic carbon: 0.97 - 1.11 mg/L
EFFECT PARAMETERS MEASURED : immobility every 24 h
RANGE-FINDING STUDY : yes
- Test concentrations: 1, 10 and 100 mg/L in a non-GLP pre-test
- Results used to determine the conditions for the definitive study: yes, no toxicity observed at highest tested dose. - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
Results and discussion
Effect concentrationsopen allclose all
- Key result
- Duration:
- 48 h
- Dose descriptor:
- NOELR
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat. (dissolved fraction)
- Basis for effect:
- other: immobility
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EL50
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat. (dissolved fraction)
- Basis for effect:
- other: immobility
- Results with reference substance (positive control):
- - Results with reference substance valid?
yes
- Relevant effect levels: The value was within the requested range for the 24h-EC50 between 0.6 - 2.1 mg/L of potassium dichromate K2Cr2O7 as specified in the OECD guideline.
- ECx: The 24h-EC50 value was determined as 1.98 mg/L. - Reported statistics and error estimates:
- Since no immobility has occurred, no statistical evaluation was carried out.
Any other information on results incl. tables
Non-GLP pre-test
Nominal Concentration in mg/L |
Immobility 48 hours |
||
absolute |
in % |
||
Blank control |
0 |
0 |
0 |
1 |
0 |
0 |
0 |
10 |
0 |
0 |
0 |
100 |
0 |
0 |
0 |
Main test
Nominal Concentration in mg/L |
Immobility 24 hours |
Immobility 48 hours |
||||||||
absolute |
in % |
absolute |
in % |
|||||||
Blank control |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
100 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Analytical determinations
The concentrations measured in the test solutions are in the same very low range as the blank value. It is detectable but not quantifiable. During the preparation of the WAF, the test solutions were in direct contact with the test item while stirring. This means that the soluble components must have dissolved. Therefore, the results are related to the loading rate; see Guidance Doc. No.23 (§176).
Measured concentrations IC and TC
Nominal |
Measured TC |
Measured TC |
Measured IC |
Measured IC |
mg/L |
mg/L |
mg/L |
mg/L |
mg/L |
Blank control |
10.41 |
11.77 |
9.44 |
10.66 |
100 |
10.30 |
12.34 |
10.10 |
10.70 |
LOQ (Limit of quantification) TC = 822.33 µg/L
LOQ (Limit of quantification) IC = 447.52 µg/L
Calculated concentrations TOC
Nominal |
Calculated concentration TOC (TC-IC) |
Calculated concentration TOC (TC-IC) |
Calculated concentration TOC minus blank control |
Calculated concentration TOC minus blank control t = 48 h |
mg/L |
mg/L |
mg/L |
mg/L |
mg/L |
Blank control |
0.97 |
1.11 |
-- |
-- |
100 |
0.20 |
1.65 |
-0.77 |
0.54 |
Calculated test item concentrations
Nominal |
Calculated Concentration t = 0 h |
Calculated Concentration t = 48 h |
% of Nominal concentration |
% of Nominal concentration |
mg/L |
mg/L |
mg/L |
% |
% |
Blank control |
-- |
-- |
-- |
-- |
100 |
-1.0 |
0.7 |
-1 |
1 |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- A 48h exposure of the test item at 100 mg/L WAF did not induce any immobility of Daphnia magna. Results indicated an NOELR and EL50 >= 100 mg/L.
- Executive summary:
A study performed as limit study in a Water Accommodated Fraction (WAF) test setup exposing the crustacean, Daphnia magna, for 48 h to load of 100 mg/L (loading rate) of the test item. Test was performed according to the OECD guideline 202 and it fulfilled the validity criteria. The test solution was prepared following the water-accommodated fractions (WAF) method at the load of 100 mg/L. Measured concentrations were determined using measurement of total organic carbon (TOC). The concentrations measured in the test solutions are in the same very low range as the blank value. It is detectable but not quantifiable. Therefore, the results are related to the loading rate; see Guidance Doc. No.23 ( § 153). No immobilisation was observed after 48 h, determining a NOELR, LOELR and EL50 greater than 100 mg/L.
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