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EC number: 607-813-5 | CAS number: 25830-77-7
- 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
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 12 August 2016 - 26 August 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 016
- Report date:
- 2016
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- 2004
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Version / remarks:
- 2008
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: Guidance document on aquatic toxicity testing of difficult items and mixtures, OECD series on testing and assessment number 23
- Version / remarks:
- 2000
- Deviations:
- no
- GLP compliance:
- yes
Test material
- Reference substance name:
- 2-[(3S)-2,6-dioxooxan-3-yl]isoindole-1,3-dione
- EC Number:
- 607-813-5
- Cas Number:
- 25830-77-7
- Molecular formula:
- C13 H9 N O5
- IUPAC Name:
- 2-[(3S)-2,6-dioxooxan-3-yl]isoindole-1,3-dione
- Test material form:
- solid
- Details on test material:
- - Appearance: white solid
- Storage conditions: in refrigerator (2-8°C) protected from light
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- Samples were taken from all test concentrations and the control according to the schedule below.
Frequency: at t=0 and t=48
Volume: 3.2 mL from the approximate centre of the test vessels
Storage: Samples were stored in a freezer until analysis (≤ -15ºC) .
At the end of the exposure period, the replicates were pooled at each concentration before sampling.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION:
- Method: A saturated solution (SS) was prepared at a loading rate of 100 mg/L applying three days of magnetic stirring to ensure maximum dissolution of the test item in test medium. The resulting aqueous mixture was filtered through a membrane and the obtained saturated solution was used as the highest test concentration. The pH was adjusted from 5.7 to 6.1 with a 1 M NaOH (Merck, Darmstadt, Germany) solution. Hereafter, lower test concentrations were prepared by subsequent dilutions of the SS in test medium. Due to the light sensitivity of the test item, preparation of test solutions was performed under dimmed light and used glassware was wrapped in aluminium foil. All final test solutions were clear and colourless.
- Controls: test medium without test item or other additives (blank-control), \ test medium without test item but with the additive used in the treatment of the stock solutions (solvent-control).
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Daphnia magna
- Source: in-house laboratory culture with a known history. At least third generation, obtained by acyclical parthenogenesis under specified breeding conditions. 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.
- Age at study initiation: < 24 hours, from parental daphnids of more than two weeks old.
- Feeding during test: no
ACCLIMATION
- Acclimation period: no
BREEDING:
- Method: each batch was started with newborn daphnids, i.e. less than 3 days old, by placing about 250 of them into 5 litres of medium in an all-glass culture vessel. After 7 days of cultivation half of the medium was renewed twice a week.
- Medium other than test medium: yes, M7
- Feeding: daily, a suspension of fresh water algae.
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
Test conditions
- Test temperature:
- 20°C throughout the test
- pH:
- 7.1 - 8.1 throughout the test
- Dissolved oxygen:
- 8.5 - 9.0 mg O2/L
- Nominal and measured concentrations:
- A combined limit/range-finding test was conducted. Only the controls and the highest concentrations were analysed.
Nominal test concentrations: 1.0, 10 and 100 mg/L
Measured test concentration: 85 mg/L
Test concentrations remained stable throughout the test - Details on test conditions:
- TEST SYSTEM
- Test vessel: 100 ml, all-glass, open, fill volume: 80 mL
- Aeration: no
- No. of organisms per vessel: 5
- No. of vessels per intermediate concentration (replicates): 2
- No. of vessels per control and highest concentration (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- Standard medium used: yes, adjusted ISO medium
- Source/preparation of dilution water: RO-water
- Culture medium different from test medium: yes, M7
OTHER TEST CONDITIONS
- Adjustment of pH: yes, pH of all test solutions was adjusted from 5.7 to 6.1 with a 1 M NaOH (Merck, Darmstadt, Germany) solution
- Photoperiod: 0 hours, daily
EFFECT PARAMETERS MEASURED: mobility at 24 and 48 hours.
- Additional measurements: pH and dissolved oxygen at the beginning and at the end of the test, for the highest concentration and the control. Temperature of the medium: continuously in a temperature control vessel beginning at the start of the test. - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate (July 2016)
Results and discussion
Effect concentrations
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- - No immobility was observed at any of the concentrations tested (see table 2 below)
- No biological, behavioural or other abnormalities were observed.
- Measured concentration at t=48 was 95% from initial loading rate
Individual pH, temperature and dissolved oxygen values remained within acceptable limits throughout the duration of the study. - Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- 48h-EC50: 0.39 mg/L, 95%-CI 0.33-0.44 mg/L
- Other: results fell within the historical range. - Reported statistics and error estimates:
- The 24h-EC50 and 48h-EC50 could not be determined because the observed effects were below 50%, i.e. no effects were observed.
Any other information on results incl. tables
Table 1 Concentrations of the test item in test medium
Time of sampling1 [hours] |
Percentage of SS2 [%] |
Analysed concentration [mg/L] |
Relative to initial [%] |
|
|
|
|
0 |
0 |
n.d. |
|
|
100 |
85.2 |
|
|
|
|
|
48 |
0 |
n.d. |
n.a. |
|
100 |
81.0 |
95 |
|
|
|
|
1Samples were stored in the freezer (≤ -15°C) until the day of analysis.
2Percentage of a saturated solution prepared at a loading rate of 100 mg/L.
n.d.Not detected.
n.a.Not applicable.
Table 2 Number of introduced daphnids and incidence of immobility in the test
Time (h) |
Replicate |
Phthaloyl-L-glutamic acid anhydride % 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 (1) |
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 |
( ) between brackets: number of daphnia observed trapped at the surface of the test solutions. These organisms were reimmersed into the respective solutions before recording of mobility.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- 1). In the control, < 10% of the daphnids became immobilised or showed other signs of disease or stress. 2). The oxygen concentration at the end of the test was ≥ 3 mg/L in control and test vessels.
- Conclusions:
- The 48h-EC50 was beyond the range tested, i.e. exceeded an analytically confirmed nominal concentration of 100 mg/L.
- Executive summary:
This study was performed to assess the effect of the test substance on the mobility of Daphnia magna after 48 hours. The study was conducted in accordance with OECD Guidline for Testing of Chemicals No. 202 and GLP under static conditions.
In a combined limit/range-finding test, 20 Daphnia magna (less than 24 hours old) were exposed to the test substance for 48 hours in all-glass, open vessels. The exposure was performed in dark.Test solutions were prepared at nominal concentrations of 1.0, 10 and 100 mg/L. The incidence of immobilisation was recorded for each test and control group at 24 hours and at 48 hours. Samples from the controls and the highest concentrations were taken and analysed to determine the test concentrations. The measured concentration at t=0 for the highest concentration was 85 mg/L and remained stable during the exposure period (95% of initial at t=48).
No immobility was observed at the controls or any of the concentrations. The 48h-EC50 was beyond the range tested, i.e. exceeded an analytically confirmed nominal concentration of 100 mg/L.
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