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EC number: 808-234-2 | CAS number: 1211443-61-6
- 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:
- 10 Mar - 26 Mar 2014
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 014
- Report date:
- 2014
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
Test material
- Reference substance name:
- 2-chloro-7-cyclopentyl-N,N-dimethyl-7H-pyrrolo[2,3-d]pyrimidine-6-carboxamide
- Cas Number:
- 1211443-61-6
- Molecular formula:
- C14 H17 Cl N4 O
- IUPAC Name:
- 2-chloro-7-cyclopentyl-N,N-dimethyl-7H-pyrrolo[2,3-d]pyrimidine-6-carboxamide
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- - Sampling method: Samples for analysis were taken from all test concentrations and the control. In addition, filter containing undissolved residue was retained for possible analysis. Samples were taken at t=0 h and t=48 h at a volume of 2.0 ml from the approximate center of the test vessels. At the end of the exposure period, the replicates were pooled at each concentration before sampling.
- Sample storage conditions before analysis: Samples were stored in a freezer until analysis.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: Preparation of test solutions started with a loading rate of 100 mg/l applying a 2-day period of magnetic stirring followed by filtration through a 0.45 μm membrane filter (rc55, Whatman) to remove undissolved fraction. The obtained Water Soluble Fraction was used as the highest concentration. The lower test concentrations were prepared by subsequent dilutions of the highest concentration in test medium.
- Eluate: no
- Differential loading: no
- Controls: blank control, reference control prepared with test medium
- Evidence of undissolved material: The final test solutions were all clear and colourless.
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Freshwater flea
- Source: In-house laboratory culture
- Age of parental stock: > 2 weeks old
- Breeding conditions: About 250 newborn daphnids (less than 3 days old) were placed into 5 L of medium in an all-glass culture vessel. The daphnids were bred in M7 medium at 18-22 °C and were fed daily with a suspension of fresh water algae. After 7 days of cultivation half of the medium was renewed twice a week. The maximum age of the cultures was 4 weeks. The hardness of the medium was 180 mg CaCO3 per L and the pH was 7.7 ± 0.3.
- Health during breeding: no signs of stress such as mortality >20%, presence of males, ephippia or discoloured animals and no delay in the production of the first brood
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
Test conditions
- Hardness:
- 180 mg CaCO3 per L
- Test temperature:
- 19 - 20 °C
- pH:
- Control: 7.9 - 8.2
Treatment: 7.8 - 8.2 - Dissolved oxygen:
- Control: 9.1 - 9.5
Treatment: 9.0 - 9.5 - Nominal and measured concentrations:
- Nominal: Control; Solutions containing 10, 18, 32, 56 and 100% of the WSF prepared at a loading rate of 100 mg/l.
Measured: not detected (Control), 32, 57 and 102 mg/l in solutions containing 32, 56 and 100% of WSF, respectively - Details on test conditions:
- TEST SYSTEM
- Test vessel: 100 ml, all-glass, containing 80 ml of test solution
- Aeration: No aeration of the test solutions.
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: M7 medium; preparation according to guideline
- Intervals of water quality measurement: The pH, dissolved oxygen concentration and temperature was measured at the beginning and at the end of the test, for all concentrations and the control. In addition after 24 hours, immediately after counting the immobilized daphnids oxygen levels were measured in the test container with the solution of lowest concentration at which all the Daphnia magna were immobilized. Temperature was measured continuously in a temperature control vessel beginning at the start of the test.
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16 h light / 8 h darkness
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : Immobility of the daphnids was recorded at 24 hours and at 48 hours.
RANGE-FINDING STUDY
- Test concentrations: 20 daphnids each exposed to control and nominal loading rate of 100 mg/L; 10 daphnids each exposed to solutions of 1.0 and 10 mg/L
- Results used to determine the conditions for the definitive study: No immobility was observed at any of the test concentrations besides the highest where all daphnids were immobilised. Microscopic observation performed at the end of the test revealed that the immobilised daphnids were still alive but were covered with test substance and stuck with each other. Therefore, the observed effect was considered to be of mechanical nature. Therefore, the expected EC50 was between 10 and 100 mg/l. - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
Results and discussion
Effect concentrations
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 89 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% CI: 76 - 104 mg/L
- Remarks:
- nominal concentrations were analytically confirmed
- Details on results:
- - Behavioural abnormalities: no abnormalities reported
- Immobility of control: No immobilisation of the control was observed after 48 h. - Results with reference substance (positive control):
- - Results with reference substance valid?
yes
- Concentrations: control, 0.10, 0.18, 0.32, 0.56, 1.0 and 1.8 mg/L
- EC50 (48 h) = 0.29 mg/L (95% CI: 0.25 - 0.34 mg/L) - Reported statistics and error estimates:
- The 24 and 48h-EC50-value was calculated from the webits of the percentages of affected daphnids and the logarithms of the corresponding test substance concentrations (initially measured) using the maximum likelihood estimation method. ToxRat Professional v 2.10.05 (ToxRat Solutions® GmbH, Germany) was used to perform the analyses.
Any other information on results incl. tables
Table 1: Number of introduced daphnids and incidence of immobility in the final test
Time (h) |
Replicate |
Nominal concentration of the test substance (mg/L) |
|||||
Control |
10 |
18 |
32 |
56 |
100 |
||
0 |
A |
5 |
5 |
5 |
5 |
5 |
5 |
B |
5 |
5 |
5 |
5 |
5 |
5 |
|
C |
5 |
5 |
5 |
5 |
5 |
5 |
|
D |
5 |
5 |
5 |
5 |
5 |
5 |
|
Total introduced |
20 |
20 |
20 |
20 |
20 |
20 |
|
24 |
A |
0 |
0 |
0 |
0 |
0 |
0 |
B |
0 |
0 |
0 |
0 |
0 |
0 |
|
C |
0 |
0 |
0 |
0 |
0 |
0 |
|
D |
0 |
0 |
0 |
0 |
0 |
0 |
|
Total immobilised |
0 |
0 |
0 |
0 |
0 |
0 |
|
Effect % |
0 |
0 |
0 |
0 |
0 |
0 |
|
48 |
A |
0 |
0 |
0 |
0 |
2 |
5 |
B |
0 |
0 |
0 |
0 |
0 |
3 |
|
C |
0 |
0 |
0 |
0 |
0 |
2 |
|
D |
0 |
0 |
0 |
0 |
1 |
3 |
|
Total immobilised |
0 |
0 |
0 |
0 |
3 |
13 |
|
Effect % |
0 |
0 |
0 |
0 |
15 |
65 |
Table 2: Concentrations of the test substance in test medium - final test
Time of sampling (h) |
% of water-soluble fraction (1) |
Analysed concentration (mg/L) |
Relative to initial |
0 |
0 |
n.d. |
- |
32 |
32.4 |
- |
|
56 |
56.9 |
- |
|
100 |
102 |
- |
|
48 |
0 |
n.d. |
n.a. |
32 |
32.3 |
100 |
|
56 |
55.8 |
98 |
|
100 |
101 |
99 |
(1) Percentage of a water soluble fraction (WSF) prepared at a loading rate of 100 mg/l.
n.d. Not detected.
n.a. Not applicable.
Table 3: Validity criteria
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. |
0% |
yes |
The dissolved oxygen concentration at the end of the test should be ≥ 3 mg/L in control and test vessels. |
8.1 - 8.2 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:
- The EC50 (48 h) was reported as 89 mg/L (95% CI: 76 - 104 mg/L).
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