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EC number: 610-490-3 | CAS number: 500011-88-1
- 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:
- December 2006 - April 2007
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 007
- Report date:
- 2007
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- adopted 13 April 2004
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Version / remarks:
- adopted 29 December 1992
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- ethyl 2-(3-chloropyridin-2-yl)-5-oxopyrazolidine-3-carboxylate
- EC Number:
- 610-490-3
- Cas Number:
- 500011-88-1
- Molecular formula:
- C11H12ClN3O3
- IUPAC Name:
- ethyl 2-(3-chloropyridin-2-yl)-5-oxopyrazolidine-3-carboxylate
- Test material form:
- solid
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Remarks:
- HPLC/VW detector
- Details on sampling:
- - Sampling method: Samples from the test media of all test concentrations and the control were taken at the start of the test and at the end of the test.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: 100 mg test item was mixed with a small volume of test medium in a beaker. This was stirred on a magnetic stirrer for 30 minutes. The volume was then made up to 100 mL with test medium in a volumetric flask (1000 mg/L). The stock solution was further diluted with test medium to prepare the test concentrations.
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: water flea
- Age at study initiation: Less than 24 hours
- Source: Local pond at Peenya 2nd stage, Bangalore, INDIA. Bred at Department of Safety Assessment , Advinus Therapeutics Private Limited, Bangalore, INDIA (For ~10 years)
- Feeding during test: No
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
Test conditions
- Test temperature:
- 20.2-20.4ºC
- pH:
- 7.59-7.93
- Dissolved oxygen:
- > 85% of saturation value
- Nominal and measured concentrations:
- Nominal concentrations: 0.20, 0.44, 0.97, 2.13, 4.69 and 10.31 mg/L
Mean measured concentrations: 0.17, 0.38, 0.82, 1.88, 4.45 and 9.83 mg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: 250 mL glass beakers
- Fill volume: 150 mL
- Aeration: No
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
- No. of vessels per positive control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Reconstituted water prepared according to guideline
- Culture medium different from test medium: No
- Intervals of water quality measurement: Dissolved oxygen concentration and pH were measured at the start and end of the test. The measurements of the test solutions at the start were taken in the absence of Daphnia and the end measurements were made in the presence of Daphnia, after pooling the test solutions from 4 replicates of each group.
OTHER TEST CONDITIONS
- Adjustment of pH: No
- Photoperiod: 16/8 hours light/dark cycle
- Light intensity: 1030-1040 Lux
EFFECT PARAMETERS MEASURED: The immobility of daphnids was determined by visual controls after 24 and 48 hours. The number of immobile daphnids in each group was recorded.
RANGE-FINDING STUDY
- Test concentrations: 0 (negative control); 0.001, 0.01, 0.1, 1.0, 10.0, 100 mg/L
- Results used to determine the conditions for the definitive study: No immobility of the Daphnids was observed in the negative control at either 24 or 48 hours post exposure. The percent immobilization, for the test item concentrations of 0.001, 0.01, 0.1, 1.0, 10 and 100 mg/L was 0, 0, 0, 40, 90 and 100%, respectively, after 48 hours of exposure. Based on the range finding results, the definitive test was conducted using the nominal concentrations of 0.20, 0.44, 0.97, 2.13, 4.69 and 10.31 mg/L (factor 2.2). - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate (0.32 mg/L)
Results and discussion
Effect concentrations
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 1.22 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- act. ingr.
- Basis for effect:
- mobility
- Results with reference substance (positive control):
- - Results with reference substance valid? Yes
There were 25 and 75 percent immobilization of Daphnia in the positive control group at 24 and 48 hours post exposure, respectively, demonstrating the sensitivity of the test procedure.
Any other information on results incl. tables
Table 1: Definitive test - Immobilisation rates after 24 and 48 hours exposure
Total number of Daphnia in each replicate at start: 5
Group | Nominal concentration [mg/L] | Mean measured concentration [mg/L] | No. of Daphnia immobilised | % Immobilisation | ||||||||
24 h | 48 h | 24 h | 48 h | |||||||||
R1 | R2 | R3 | R4 | R1 | R2 | R3 | R4 | |||||
G1 | Negative control | - | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
G2 | 0.20 | 0.17 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
G3 | 0.44 | 0.38 | 0 | 0 | 1 | 0 | 2 | 1 | 2 | 0 | 5 | 25 |
G4 | 0.97 | 0.82 | 1 | 0 | 0 | 0 | 2 | 3 | 2 | 2 | 5 | 45 |
G5 | 2.13 | 1.88 | 1 | 0 | 1 | 0 | 3 | 2 | 3 | 3 | 10 | 55 |
G6 | 4.69 | 4.45 | 1 | 2 | 1 | 1 | 4 | 3 | 4 | 3 | 25 | 70 |
G7 | 10.31 | 9.83 | 3 | 2 | 3 | 3 | 5 | 5 | 5 | 5 | 55 | 100 |
G8 | Positive control | - | 2 | 1 | 1 | 1 | 4 | 5 | 3 | 3 | 25 | 75 |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- There was no mortality in the negative control at the end of the test and the dissolved oxygen concentration of the test medium was greater than 85% of the air saturation value (6.6 mg/L).
- Conclusions:
- Under the test conditions, the calculated EC50 value for the test item at 48 hours was 1.22 mg/L based on the mean measured concentration and immobility with fiducial limits being 0.78 and 1.91 mg/L.
- Executive summary:
The acute Toxicity of the test item to Daphnia magna was determined in a static 48-hour immobilisation test. The test was conducted in accordance with OECD Guideline 202 and EEC Guideline Part C.2.
The daphnids were exposed to six nominal concentrations of 0.20, 0.44, 0.97, 2.13, 4.69 and 10.31 mg/L (factor was 2.2) over a 48 hour period. The mean measured concentrations were 0.17, 0.38, 0.82, 1.88, 4.45 and 9.83 mg/L for these nominal concentrations. A concurrent negative control (dilution water only) and a positive control (potassium dichromate) were also tested. HPLC analysis of the test solutions showed a reduction in the measured concentration of the test item in the test media at the end of the treatment period compared to the nominal concentration. Hence, the results are reported based on the mean measured concentration of the test item.
The number of Daphnia immobilised was recorded at 24 and 48 hours after initiation. The exposure of daphnids to the mean measured concentrations of 0.17, 0.38, 0.82, 1.88, 4.45 and 9.83 mg/L resulted in 0, 25, 45, 55, 70 and 100% immobilization, respectively, at the end of 48 hours. No immobility was observed in the negative control.The calculated EC50 value for the test item at 48 hours was 1.22 mg/L based on the mean measured concentration and immobility with fiducial limits being 0.78 and 1.91 mg/L
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