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EC number: 944-815-8 | 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
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
- Report date:
- 2018
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:
- Reaction product aqueous Phosphoric Acid, 1-Methoxypropan-2-ol and 4,4'-Isopropylidenediphenol-Epichlorohydrin
- EC Number:
- 944-815-8
- Molecular formula:
- Not possible to assign for a complex UVCB substance
- IUPAC Name:
- Reaction product aqueous Phosphoric Acid, 1-Methoxypropan-2-ol and 4,4'-Isopropylidenediphenol-Epichlorohydrin
- Test material form:
- liquid
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- Samples for possible analysis were taken from all test concentrations and the control according to the schedule as follows:
Frequency: At 0 and 48 hours (start and end of test)
Volume: 3 mL from the approximate centre of the test vessels
Storage: Samples were stored in a freezer (≤-15°C) until analysis at the analytical laboratory of the Test Facility
At the end of the exposure period, the replicates were pooled at each concentration before sampling. Additionally, reserve samples of 3 mL were taken for possible analysis. If not used, these samples were stored in a freezer (≤-15°C).
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION:
The batch of the test item was a clear yellow viscous liquid UVCB and not completely soluble in test medium at the loading rates initially prepared. No correction was made for the purity/composition of the test item. Preparation of test solutions was performed under dimmed light conditions with glassware wrapped in aluminium foil to minimize exposure to light.
Preparation of test solutions started with loading rates individually prepared at 1.0, 10 and 100 mg/L. A 31-minute period of ultrasonic waves followed by an overnight period of magnetic stirring was applied to ensure maximum dissolution of the test item in test medium. The obtained mixtures were centrifuged at 10000 rpm for 10 minutes. Subsequently, the supernatant was drained from the pelleted undissolved material using a pipette and the obtained Water Accommodated Fractions (WAFs) were used as test concentrations. All test solutions were clear and colorless at the end of the preparation procedure.
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Daphnia magna (crustacea, Cladocera)
- Strain/clone: Straus 1820
- Source: In-house laboratory culture with a known history
- Age of parental stock (mean and range, SD): 2 to 4 weeks
- Feeding during test: None
ACCLIMATION
- Acclimation period: Parental cultures up to 4 weeks old
- Acclimation conditions (same as test or not): Same as test
- Type and amount of food: Fresh water algae
- Feeding frequency: Daily
- Health during acclimation (any mortality observed): Only Daphnids from healthy stock used (2nd to 5th brood, showing no signs of stres such as mortality > 20%, presence of males, ephippia or discoloured animals and no delay in the production of the first brood).
METHOD FOR PREPARATION AND COLLECTION OF EARLY INSTARS OR OTHER LIFE STAGES: Daphnia less than 24 hours old.
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
Test conditions
- Hardness:
- 180 mg/L as CaCO3
- Test temperature:
- Varied between 19 and 21°C during the test constant within +/- 1°C.
- pH:
- Remained within pH 6-9 and did not vary by more than 1.5 units.
- Dissolved oxygen:
- Dissolved oxygen >/= 3 mg/L at the end of the test
- Salinity:
- Not specified
- Conductivity:
- Not specified
- Nominal and measured concentrations:
- Nominal: Control, 1, 10 and 100 mg/L (loading rates)
Measured: 0 and 46 mg/L (at a loading rate of 100 mg/L and not measured at loading rates of 1 or 10 mg/L) - Details on test conditions:
- TEST SYSTEM
- Test vessel: All-glass vessels
- Type (delete if not applicable): open
- Material, size, headspace, fill volume: 50 mL test/control solutions in 60 mL vessels
- Aeration: No
- No. of organisms per vessel: 5 per vessel
- No. of vessels per concentration (replicates): 100 mg/L; 20 per test group and 1 and 10 mg/L; 10 per test group.
- No. of vessels per control (replicates): 4
- No. of vessels per vehicle control (replicates): NA
- Biomass loading rate: 10 mL per Daphnid
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Analytical grade salts were added to tap water purified by reverse osmosis. The culture medium was M7 as per the OECD guideline)
OTHER TEST CONDITIONS
- Adjustment of pH: Not performed
- Photoperiod: Test conducted in darkness
- Light intensity: Not applicable
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : Immobility measured at 24 and 48 hours. Immobile are those animals not able to swim within 15 seconds after gentle agitation of the test vessel, even if they can still move their antennae.
VEHICLE CONTROL PERFORMED: No
RANGE-FINDING STUDY
- Test concentrations: Combined range finder/limit test performed at 1, 10 and 100 mg/L loading rates - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 48 h
- Dose descriptor:
- EL50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat. (dissolved fraction)
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 46 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat. (dissolved fraction)
- Basis for effect:
- mobility
- Details on results:
- Measured concentrations:
Samples taken from the highest test concentration were analysed. The measured concentration was 46 mg/L at the start of the test. During the exposure period, the concentration remained stable, i.e. was at 112% relative to initial at the end of the test. Based on these results, effect parameters were expressed as the initially measured concentration and the loading rate. This measured concentration was determined to be the maximum solubility of the potentially soluble constituents of the UVCB substance. As such the EC50 values exceeded the limit of solubility.
Immobility:
No immobility was observed in the control and at the two lowest test concentrations throughout the exposure period. At the end of the test, 30% immobility was observed at the highest concentration tested. - Results with reference substance (positive control):
- - Results with reference substance valid?
Yes
- Relevant effect levels: 48 hour EC50 was 0.59 mg/L (with the historical range of 0.53 to 0.72 mg/L).
- Limit test: No
- Dose-response test: Yes (concentrations of 0.1, 0.18, 0.32, 0.56, 1.0 and 1.8 mg/L).
- ECx: EC50 - Reported statistics and error estimates:
- Not performed as EC50 greater than the highest concentration/loading rate tested.
Any other information on results incl. tables
Number of introduced Daphnids and incidence of immobility in the test:
Time (h) |
Replicate |
Test substance |
|||
Control |
1.0 |
10 |
100 |
||
0 |
A |
5 |
5 |
5 |
5 |
B |
5 |
5 |
5 |
5 |
|
C |
5 |
- |
- |
5 |
|
D |
5 |
- |
- |
5 |
|
Total introduced |
20 |
10 |
10 |
20 |
|
24 |
A |
0 |
0 |
0 |
2 |
B |
0 |
0 |
0 |
1 |
|
C |
0 |
- |
- |
0 |
|
D |
0 |
- |
- |
0 |
|
Total immobilised |
0 |
0 |
0 |
3 |
|
Effect % |
0 |
0 |
0 |
15 |
|
|
|
|
|
||
48 |
A |
0 |
0 |
0 |
2 |
B |
0 |
0 |
0 |
1 |
|
C |
0 |
- |
- |
1 |
|
D |
0 |
- |
- |
2# |
|
Total immobilised |
0 |
0 |
0 |
6 |
|
Effect % |
0 |
0 |
0 |
30 |
Test sample analysis:
Time of sampling |
Date of sampling |
Date of |
Loading rate2 |
Analyzed concentration |
Relative to |
0 |
19 Jun 2018 |
27 Jun 2018 |
0 |
n.d. |
|
|
|
|
100 |
45.6 |
|
48 |
21 Jun 2018 |
27 Jun 2018 |
0 |
n.d. |
n.a. |
|
|
|
100 |
51.1 |
112 |
1 Samples were stored in the freezer (≤ -15°C) until the day of analysis.
2 A water accommodated fraction (WAF) prepared at the loading rate.
n.d. Not detected.
n.a. Not applicable.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- In conclusion the 48 hour EL50 for Daphnia magna exposed to the test substance was greater than the highest loading rate tested (100 mg/L). Based on analytical measurements conducted of dissolved constituents the EC50 was greater than 46 mg/L (initial measured concentration). This was determined to be the the limit of solubility for the dissolved fraction.
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