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Diss Factsheets
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EC number: 701-350-3 | 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
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Toxicity to microorganisms
Administrative data
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Mar 14 2019 to June 20, 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 guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test (Carbon and Ammonium Oxidation))
- Deviations:
- no
- GLP compliance:
- yes
Test material
- Reference substance name:
- 3-sec-[C15-18-(branched and linear)-alk-2-enyl]pyrrolidine-2,5-dione
- EC Number:
- 701-350-3
- Molecular formula:
- Not possible to assign, UVCB
- IUPAC Name:
- 3-sec-[C15-18-(branched and linear)-alk-2-enyl]pyrrolidine-2,5-dione
- Test material form:
- liquid
- Details on test material:
- - Appearance: brown liquid
- Storage: room temperature, in the dark
Constituent 1
- Specific details on test material used for the study:
- Test material is a UVCB
Test solutions
- Vehicle:
- no
- Details on test solutions:
- The test solution for the study was made up of 4 test groups listed below:
The test mixtures was made up of 2 sets of solutions; the first solution contained the test substance, inoculum, synthetic sewage feed and deionized water while the second solution contained the test substance, synthetic sewage feed and deionized water.
The blank control was made up of 2 sets of solutions; the first solution contained inoculum, synthetic sewage feed, and deionized water while the second solution contained inoculum, synthetic sewage feed, ATU and deionized water.
The reference mixtures was made up of 2 sets of solutions; The first solution contained reference substance, inoculum, synthetic sewage feed, and deionized water, while the second solution reference substance, inoculum, synthetic sewage feed, ATU and deionized water.
Abiotic control ontained Test substance, synthetic sewage feed and deionized water.
Test organisms
- Test organisms (species):
- activated sludge
- Details on inoculum:
- Activated sludge obtained from Aeration tank of Datansha Sewage Treatment Plant of Guangzhou with batch number: IAs20190513-1 was used for the study.
Treatment: Coarse particles and impurities were removed from the sludge, then re-suspended in chlorine-free tap water. The activated sludge suspension concentration was determined. Before the study, the sludge suspension concentration was adjusted to 3.0 g/L, and was cultivated, 50 mL of synthetic sewage feed per litre of activated sludge was fed and aerated under the test temperature of 20°C±2°C. The pH value was determined as 7.12 before used.
Study design
- Water media type:
- other: Deionized water
- Limit test:
- yes
- Total exposure duration:
- 3 h
Test conditions
- Test temperature:
- 20.6°C - 2 l .9°C
- pH:
- pH values of each group at the start and the end of the test were in the range of 7.4 5 - 7. 60 and 7. 66 - 7.99.
- Details on test conditions:
- The test was perfonned at a temperature within the range 20°C±2°C.
The test solutions were aerated with 1 L test vessels inserted into the outlet pipe. The reference substance, test substance, synthetic sewage feed, ATU and deionized water were added into the corresponding test vessels, respectively. The blank controls were prepared in the meantime. After starting the test, 250 mL of activated sludge suspensions were respectively added into each test vessel in tum, with a final volume of 500 mL, aerating and agitating to stay suspending. After the exposure times of three hours, the above test solutions were transferred to 500 mL bottles, then the dissolved oxygen concentrations of each test group and the test temperatures were detennined and recorded. The pH values of each test solution at the start and end of the test were determined. - Reference substance (positive control):
- yes
Results and discussion
Effect concentrations
- Key result
- Duration:
- 3 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 1 000 mg/L
Any other information on results incl. tables
Results of the range-finding test (Total oxygen uptake)
Test Substance (mg/L) |
Replicate | Initial DO (mg/L) |
Initial DO caculation (mg/L) |
Terminal DO for calculation (mg/L) |
Timer Intervals (S) | Specific oxygen Uptake rate [mg/(g.h)] |
Inhibition (%) | Average (%) |
10 | 1 | 8.18 | 4.44 | 2.04 | 150 | 38.40 | -6.5 | - |
100 | 1 | 8.42 | 5.20 | 2.05 | 210 | 36 | 0.2 | - |
1000 | 1 | 8.43 | 4.33 | 1.91 | 180 | 32.27 | 10.5 | |
1000 | 2 | 8.50 | 4.81 | 1.94 | 210 | 32.80 | 9.1 | 7.3 |
1000 | 3 | 8.42 | 4.56 | 1.92 | 180 | 35.20 | 2.4 | |
3h-EC50(mg/L) >1000 |
Results of the range-finding test (Abiotic control)
Test Substance (mg/L |
Replicate | Initial DO (mg/L) |
Initial DO caculation (mg/L) |
Terminal DO for calculation (mg/L) |
Timer Intervals (S) | Specific oxygen Uptake rate [mg/(g.h)] |
Average [mg/(L.h)] |
1000 | 1 | 8.68 | 8.68 | 8.69 | 420 | -0.1 | 0 |
2 | 8.68 | 8.69 | 8.69 | 420 | 0 | ||
3 | 8.67 | 8.69 | 8.69 | 420 | 0 |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- Under the present test conditions, the 3h-EC50 of the test substance for the total oxygen uptake was higher than 1000 mg/L.
- Executive summary:
The study was conducted to determine the EC50 value of the respiration Inhibition of the test substance on activated sludge. The study was conducted in accordance with OECD 209 guidelines and GLP. The test mixture contained the test substance, inoculum, synthetic sewage feed and deionized water. A blank control, reference mixtures and abiotic control were used in the study. Test substance had exposure concentrations of 10 mg/L, 100 mg/L and 1000 mg/L (three replicates) and the abiotic control had a concentration of 1000 mg/L in three replicates. After an exposure time of three hours, the test results showed that the 3h-EC50 of the test substance for the total oxygen uptake was higher than 1000 mg/L. The average of oxygen uptake rates of the abiotic control was 0 mg/(L·h), which revealed that there was no obvious abiotic oxygen consumption during the study period. The test temperature were in the range of 20.8°C - 21.5°C during the test, and the pH values of test mixtures at the start and the end of the test were in the range of 7.41 - 7.48 and 7.49 - 7.61, the pH values of a biotic control at the start were in the range of 7.40 - 7.41, and the end of the test were in the range of 4.98 - 5.1.
The absence of inhibition of oxygen consumption by the test substance in the range-finding test demonstrated that a definitive test was unnecessary.
Therefore, under the present test conditions, the 3h-EC50 of the test substance for the total oxygen uptake was > 1000 mg/L.
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