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EC number: 259-515-6 | CAS number: 55184-72-0
- 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
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2002
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- Well documented GLP study, no dose verification analysis
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- no
- Vehicle:
- yes
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: the test solutions were prepared with 100 µL acetone/L
- Controls: beside an untreated control, a solvent control was set up
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): acetone
- Concentration of vehicle in test medium (stock solution and final test solution(s) including control(s)): 100 µL/L in the final test solution
- Evidence of undissolved material (e.g. precipitate, surface film, etc): none - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Water flea (Daphnia magna Straus)
- Source: Aquatic Research Organisms, Hampton New Hampshire, USA in August 2000
- Age at study initiation (mean and range, SD): less than 24 hours old
- Method of breeding: The Daphnia were cultured in media consisting of reconstituted fresh water containing live Selenastrum algal cells and YCT suspension.
- Feeding during test: not fed during the test
ACCLIMATION
- Acclimation conditions (same as test or not): similar
- Type and amount of food: Selenastrum capricornutum algal cells and YCT suspension - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- 80 mg/L as CaCO3
- Test temperature:
- 20.1 - 20.8 °C
- pH:
- 7.3 - 7.7
- Dissolved oxygen:
- 4.1 to 9.2 mg/L. The 4.1 mg/L concentration was measured in the highest test concentration after 48 hours of exposure. Since 100 % immobilization was observed in this treatment level at 48 hours, the DO concentration is considered as not relevant for the immobilization. All other DO values were above 5.6 mg/L (this values was measured after 48 hours in the second highes treatment level).
- Nominal and measured concentrations:
- Nominal concentrations: 0 (control), 0 (solvent control), 0.5, 1.3, 3.2, 8 and 20 mg CT-737-2/L corresponding to 0, 0, 0.35, 0.91, 2.24, 5.6 and 14 mg a.i./L
- Details on test conditions:
- TEST SYSTEM
- Test vessel:
- Type (delete if not applicable): 50 mL glass beakers
- Material, size, headspace, fill volume: 50 mL fill volume
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
- No. of vessels per vehicle control (replicates): NA
- Biomass loading rate: NA
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: reconstituted fresh water
- Alkalinity: 36 mg/L as CaCO3
-Specific conductivity: 439 µS
- Intervals of water quality measurement: at start and 48 hours
OTHER TEST CONDITIONS
- Photoperiod: 16:8 hours light dark cycle
- Light intensity: 12.7 - 13.9 micromole per square meter per second
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
EC50 at 24 and 48 hours
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2.5
- Justification for using less concentrations than requested by guideline: NA - Reference substance (positive control):
- no
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 14 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- other: Immobilization
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 20 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: Immobilization
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 4.9 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- other: Immobilization
- Remarks on result:
- other: 95% C.I.: 3.99 - 5.95 mg a.i./L
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 7 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: Immobilization
- Remarks on result:
- other: 95 % C.I.: 5.7 - 8.5 mg CT-737-02/L
- Details on results:
- - Behavioural abnormalities: After 24 hours of exposure, 5/20 daphnids were lethargic at 20 mg CT-737-02/L, after 48 hours all daphnis of this treatment level were immobilized. After 48 hours of lethargic behaviour was observed in all non-immobilized daphnids of the 8 mg CT-737-02/L treatment level.
- Mortality of control: none
- Other adverse effects control: one control daphnia was lethargic after 24 hours but normal after 48 hours.
- Abnormal responses: none - Reported statistics and error estimates:
- The computer program ToxCalc was used, but the method for the calculation was not mentioned .
- Validity criteria fulfilled:
- yes
- Conclusions:
- 48-hour EC50 = 4.9 mg active ingredient/L
- Executive summary:
The acute toxicity of CT-737 -02 - which contains about 70% a.i. - to Daphnia magna was determined in a static GLP test. The test was performed according to OECD 202. The test was started with a control, solvent control and nominal 0.5, 1.3, 3.2, 8.0 and 20 mg CT-737 -02/L corresponding to 0 (control), 0 (solvent control), 0.35, 0.91, 2.24, 5.6 and 14 mg a.i./L. For each test concentration and the control, 4 replicates with 5 daphinds each were set up in 50 mL vessels filled with 50 mL test solution. The test was performed in a 16:8 hour light dark cycle. Dose-verification analysis was not performed and hence, the concentrations were reported as nominal concentrations. After 48 hours of exposure, 0, 0, 0, 0, 0, 65 and 100 % of the daphnids were immobilized at 0 (control), 0 (solvent control), 0.35, 0.91, 2.24, 5.6, and 14 mg a.i./L.
The corresponding 48 h EC50 value is 4.9 mg a.i./L.
This study is considered to be acceptable for the risk assessment.
Reference
Table 1 Immobilization of Daphnids exposed to CT-737 -02
Concentration [mg CT-737 -02/L] | 24 hour observation # immobilized/20(Percent mortality) | 24 hour observation Orientation | 48 hour observation Cumulative # immobilized/20(Percent mortality) | 48 hour observation Orientation |
0 (control) | 0 (0%) | 1 LETH, 19 N | 0 (0%) | 20 N |
0 (solvent control) | 0 (0%) | 20 N | 0 (0%) | 20 N |
0.5 | 0 (0%) | 20 N | 0 (0%) | 20 N |
1.3 | 0 (0%) | 20 N | 0 (0%) | 20 N |
3.2 | 0 (0%) | 20 N | 0 (0%) | 20 N |
8.0 | 0 (0%) | 20 N | 13 (65%) | 7 LETH |
20 | 1 (5%) | 5/20 LETH | 20 (100%) | - |
N: none, normal
LETH: Lethargic
Description of key information
EC50 freshwater invertebrates = 4.9 mg a.i./ L
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 4.9 mg/L
Additional information
For the data endpoint “Short-term toxicity to aquatic invertebrates” one experimental Klimisch 2 study is available.
The GLP study from Cytec (Glover 2002) was classified as Klimisch 2 study. In this study the acute toxicity of formulated product - which contains 70% a.i.- to Daphnia magna was determined in a static test. The test was performed according to guideline OECD 202. Only minor deviations were observed. The test was started with a control, solvent control nominal 0.5, 1.3, 3.2, 8 and 20 mg formulated product/L corresponding to 0 (control), 0 (solvent control), 0.35, 0.91, 2.24, 5.6 and 14 mg a.i./L. For each test concentration and the control, 4 replicates with 5 daphnids each were set up in 50 mL vessels. The test was performed in 16:8 h light dark cycle. Dose-verification analysis was not performed and hence, the concentrations were reported as nominal concentrations. After 48 hours of exposure, 0, 0, 0, 0, 0, 65 and 100 % of the daphnids were immobilized at 0 (control), 0 (solvent control),0.35, 0.91, 2.24, 5.6 and 14 mg a.i./L. The corresponding 48 h EC50 value is 4.9 mg a.i./L.
The results of this study are considered as relevant for the risk assessment and the CSA.
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