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EC number: 235-985-8 | CAS number: 13080-86-9
- 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:
- 26 Oct - 09 Nov 2017
- 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)
- Version / remarks:
- 2004
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Health Care Inspectorate of the Ministery of Health, Welfare and Sport, Utrecht, The Netherlands
Test material
- Reference substance name:
- 4,4'-[isopropylidenebis(4,1-phenyleneoxy)]dianiline
- EC Number:
- 235-985-8
- EC Name:
- 4,4'-[isopropylidenebis(4,1-phenyleneoxy)]dianiline
- Cas Number:
- 13080-86-9
- Molecular formula:
- C27H26N2O2
- IUPAC Name:
- 4,4'-[isopropylidenebis(4,1-phenyleneoxy)]dianiline
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: All test concentrations and the control
- Sampling method: Samples were taken at the start of the test and after 24 h from the freshly prepared solutions and at renewal (t= 24 h) and the end of the test from the 24 h old solutions. 2.0 mL were taken from the approximate centre of the test vessels.
- Sample storage conditions before analysis: not applicable
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: Preparation of test solutions started with a loading rate of 100 mg/L applying a three-day period of magnetic stirring to ensure maximum dissolution of the test item in medium. Thereafter, the aqueous Saturated Solution (SS) was collected by filtration through a 0.45 µm membrane filter (RC55, Whatman) and used as the highest test concentration. Lower test concentrations were prepared by subsequent dilutions of the SS in test medium.
- Controls: Yes
- Eluate: No
- Differnetial loading: No
- Evidence of undissolved material: No; 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: water flea
- Strain/clone: Straus, 1820
- Source: In-house laboratory culture with a known history
- Age of parental stock (mean and range, SD): 4 weeks
- Feeding during test: No feeding
- Food type: Suspension of fresh water algae
- Frequency: Daily
ACCLIMATION
- Acclimation period: 4 weeks
- Acclimation conditions (same as test or not): same
- Health during acclimation (any mortality observed): Daphnids originated from a healthy stock, 2nd to 5th brood, showing no signs of stress such as mortality >20%, presence of males, ephippia or discoloured animals and there was no delay in the production of the first brood.
METHOD FOR PREPARATION AND COLLECTION OF EARLY INSTARS OR OTHER LIFE STAGES: < 24 hours, from parental daphnids of more than two weeks old
Study design
- Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
Test conditions
- Hardness:
- 180 mg/L expressed as CaCO3
- Test temperature:
- 20 - 21 °C
- pH:
- 7.7 - 8.0 (Control)
7.7 - 8.0 (Test item concentrations) - Dissolved oxygen:
- 9.0 - 9.2 (Control)
8.5 - 9.1 (Test item concentrations) - Nominal and measured concentrations:
- 1.0, 10 and 100% of a SS prepared as a concentration of 100 mg/L
0.00040, 0.00078 and 0.0016 mg/L (measured concentration based on TWA) - Details on test conditions:
- TEST SYSTEM
Test vessel:
- Type: open
- Material, size, headspace, fill volume: glass, 100 mL, headspace: 20 mL, fill volume: 80 mL
- Aeration: No
- Renewal rate of test solution (frequency/flow rate): After 7 days of cultivation half of the medium was replaced twice a week.
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4 (for highest test item concentration 100 mg/L) and 2 (for the other test item concentrations 1.0 and 10 mg/L)
- No. of vessels per control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: M7 medium (adjusted ISO medium) according to the guideline
- Culture medium different from test medium: no
- Intervals of water quality measurement: pH and dissolved oxygen were measured at the beginning, after 24 h and at the end of the test, for the control and the highest test concentration. Additionally, in the intermediate test concentrations upon renewal of the test solutions. The temperature was measured continuously in a temperature control vessel, beginning at the start of the test and in the fresh and spent test solutions upon renewal.
OTHER TEST CONDITIONS
- Photoperiod: 16 h photoperiod daily
EFFECT PARAMETERS MEASURED: Immobility (including mortality) was measured and recorded at 24 h and at 48 h.
RANGE-FINDING STUDY: no range-finding test was performed - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
Results and discussion
Effect concentrations
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 0.002 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Remarks:
- filtered solution
- Basis for effect:
- mobility
- Details on results:
- - Mortality of control: No
- Abnormal responses: No
- Others: Analytical and biological results are summarized in table 1 and 2 within the section "Any other information on results incl. tables" - Results with reference substance (positive control):
- In conclusion, the actual responses in this reference test with K2Cr2O7 are within the ranges of the expected responses at the different concentrations, i.e. the 48 h EC50 was between 0.3 and 1.0 mg/L. Hence, the sensitivity of this batch of D. magna was in agreement with the historical data collected at Charles River Den Bosch. The 48 h EC50 was 0.41 mg/L with a 95% confidence interval between 0.34 and 0.46 mg/L.
Any other information on results incl. tables
Table 1: Analytical Results: Measured Concentrations
Test item 1 |
Measured concentration (mg/L) |
Average exposure concentration (mg/L) |
|||
t= 0 h (fresh) |
t= 24 h (old) |
t= 24 h (fresh) |
t= 48 h (old) |
||
1.0 |
0.00040 2 |
0.00040 2 |
0.00040 2 |
0.00040 2 |
0.00040 |
10 |
0.00040 2 |
0.00040 2 |
0.00335 |
0.00040 2 |
0.00078 |
100 |
0.00354 |
0.00040 2 |
0.00332 |
0.00134 |
0.0016 |
1 4,4’-[isopropylidenebis(4,1-phenyleneoxy)]dianiline
2 Taken as half of the limit of detection, i.e. LOD/2 = 0.00040 mg/L.
Table 2: Biological Results: Number of Introduced Daphnids and Incidence of Immobility
Time (h) |
Replicate |
4,4’-[isopropylidenebis(4,1-phenyleneoxy)]dianiline % SS prep. at 100 mg/L |
|||
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 |
0 |
B |
0 |
0 |
0 |
0 |
|
C |
0 |
|
|
0 |
|
D |
0 |
|
|
0 |
|
Total immobilised |
0 |
0 |
0 |
0 |
|
Effect % |
0 |
0 |
0 |
0 |
|
|
|
|
|
||
48 |
A |
0 |
0 |
0 |
0 |
B |
0 |
0 |
0 |
0 |
|
C |
0 |
|
|
0 |
|
D |
0 |
|
|
0 |
|
Total immobilised |
0 |
0 |
0 |
0 |
|
Effect % |
0 |
0 |
0 |
0 |
Table 3: Validity criteria for OECD 202
Criterion from the guideline |
Outcome |
Validity criterion fulfilled |
In the control, including the control containing the solubilising agent, not more than 10% of the daphnids should have been immobilized. |
No mortality |
Yes |
The dissolved oxygen concentration at the end of the test should be ≥ 3 mg/L in control and test vessels. |
>3 mg/L |
Yes |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- For further details please refer to “Any other information on results incl. tables”.
- Conclusions:
- In conclusion, the 48 h EC50 for Daphnia magna exposed to 4,4’-[isopropylidenebis(4,1-phenyleneoxy)]dianiline was beyond the range tested, i.e. exceeded an average concentration of 0.0016 mg/L being considered the maximum soluble concentration of the test item in test medium at a concentration of 100 mg/L.
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