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EC number: 203-232-2 | CAS number: 104-74-5
- 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
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- Auto flammability
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- 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
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- 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
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- no
- GLP compliance:
- no
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 0 (control), 0.125, 0.25, 0.5, 1 and 2 mg/l
- Sampling method:The stock solution was prepared by dissolving 5 mg of test chemical in 50 ml of M7 medium to get the final concentration of 100 mg/L. The remaining test solutions were prepared by dilution from the above stock solution.
- Sample storage conditions before analysis: sample was analysed immediately after preperation - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
-Method: 5 mg of test item was transferred and made up to 50 mL in a volumetric flask using M7 medium (Stock solution). From the stock solution 0 (control), 0.125, 0.25, 0.5, 1 and.2 mg/L were prepared using M7 medium in a glass test vessel.
- Controls: M7 Medium (Control),
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): Not applicable
- Concentration of vehicle in test medium (stock solution and final test solution(s) or suspension(s) including control(s)): Not applicable - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Water flea
- Source: Daphnia magna were obtained from Denmark Technical University and maintained at Unique Ecotox Research Laboratory, Nagpur.
- Age at study initiation (mean and range, SD): <24 hr
- Length at study initiation (length definition, mean, range and SD): 0.45 cm
- Feeding during test : No
Others: A population of Daphnia magna of synchronized age structure has been maintained for more than 2 months in the test facility under constant temperature conditions (18 to 22°C) at a 16 : 8 hour light-dark photoperiod (illumination: > 1000 lux). The culture media (M7 medium') was partly renewed twice a week. During the maintenance of test organism, test daphnids were fed with unicellular green algae (Selenestrum capricornutum).
ACCLIMATION
- Acclimation period: 48 hours prior test
- Acclimation conditions (same as test or not): Yes (Test daphnids were acclimatized)
- Type and amount of food: Food was provided during acclimatization.
- Health during acclimation (any mortality observed): healthy no mortality was observed
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- 225 mg CaCO3/L
- Test temperature:
- 20 °C
- pH:
- Control 7.3 - 7.6
- Dissolved oxygen:
- 7.4-8.1 mg/L
- Salinity:
- Not applicable
- Nominal and measured concentrations:
- Nominal concentrations: 0 (control), 0.125, 0.25, 0.5, 1 and 2 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 100 mL Beakers
- Type (delete if not applicable): Loosely covered with glass lid to reduce the loss of water due to evaporation and to avoid the entry of dust into the solutions.
- Material, size, headspace, fill volume: Glass, volume 100 mL
- Volume of solution: 30 ml
- Aeration: no
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 2
- No. of vessels per control (replicates): 2
- No. of vessels per vehicle control (replicates): Not applicable
- Biomass loading rate: 5 daphnids/30 mL test medium
OTHER TEST CONDITIONS
- Adjustment of pH: No
- Photoperiod: Dark conditions
- Light intensity: 1086 Lux
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : immobilisation
VEHICLE CONTROL PERFORMED: Not applicable
- Spacing factor for test concentrations:2
RANGE-FINDING STUDY
Based on the available data on the test chemical range finding test was not conducted directly main study was intaited to draw the conclusion on test substance toxicity. - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 0.16 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- - Mortality of control:
No mortality in control
- Other adverse effects control: None
- Immobilisation of control: No immobilisation
- Abnormal responses: None in control - Results with reference substance (positive control):
- - Results with reference substance valid?
Yes valid
EC50: 0.650 mg/L
Lower limit = 0.631 mg/L - Reported statistics and error estimates:
- 48h EC50 value were calculated by probit analysis using STAT Plus Software, version 8.
- Validity criteria fulfilled:
- yes
- Remarks:
- In the control, there was no daphnid found immobilized or other clinical signs throughout the test. The dissolved oxygen concentration at the end of the test was ≥ 3 mg/ L in control and test vessels
- Conclusions:
- Based on the effect on mobility of test daphnids, the 48-h EC50 of test chemical to daphnid, Daphnia magna was reported to be 0.16 mg/L.
- Executive summary:
This study was designed (as per OECD 202, adopted in 2004) to assess the acute toxicity of test chemical following exposure of daphnids up to 48h by static method. The test daphnids were acclimatized 48 hours prior to the test chemical exposure. After exposure on day 0, daphnids were observed for immobilization at 24 and 48 h. M7 medium was used as control, and the same was used for test chemical formulation . 100 mL glass beakers having a solution volume of 30 mL were used in the test. . Main study (using a spacing factor of 2) was conducted using 0 (control), 0.125, 0.25, 0.5, 1 and 2 mg/L concentrations. 2 replicates/concentration having 5 daphnids/replicate was used for the main study. UV-Visible spectrophotometer method was used for active ingredient analysis along with stability of the test item in the test medium. Test item was found to be stable in the test medium. The active ingredient content results were considered acceptable (80-120%) as during main study 0 h and after 48 hours of exposure, which were found in acceptable range. Hence the results were based on nominal concentration since the deviation in the initial measured concentration didn’t exceed 20%. Environmental parameters such as pH (7.3 -7.6), temperature (20-21°C), dissolve oxygen (7.4 - 8.1 mg/L), hardness (225 mg CaCO3/L), light intensity of 1086 lux, photoperiod (16 h light- 8 h dark) was maintained in acceptable range throughout the test. Thus, fulfilling the validity criteria. Feed was not provided during the test. Normal behavioural response and no immobilization (0% mortality) were observed up to 48 h followed by control groups but 40%, 60%, 100%, 100% and 100% immobilisation were observed in the test concentrations of 0.125, 0.25, 0.5, 1 and 2 mg/L, respectively. The 48-h EC50 of test chemical to daphnid, Daphnia magna are 0.16 mg/l. The 24-h EC50 of reference item (Potassium dichromate) to daphnid, Daphnia magna(found to be in acceptable range) is 1.33 mg/L. Hence, the results of the test with reference item establish the acceptability of the test system response, test procedures followed, and results obtained with test item. Thus, test chemical was considered as toxic to aquatic invertebrates at environmental relevant concentrations and hence, considered to be classified in 'aquatic acute/chronic category 1' as per the CLP classification criteria.
Reference
Concentration After Analytical Determination
|
0 Hour |
0 Hour |
48 Hours |
48 hours |
|
Sr. No |
Concentration’s(mg/L) |
Absorbance (mean) |
Analytical concentrations |
Absorbance (mean) |
Analytical concentrations |
1 |
control |
0 |
0 |
0 |
0 |
2 |
0.125 |
0.002 |
0.14 |
0.002 |
0.12 |
3 |
0.25 |
0.004 |
0.24 |
0.003 |
0.25 |
4 |
0.5 |
0.006 |
0.41 |
- |
- |
5 |
1 |
0.01 |
0.95 |
- |
- |
6 |
2 |
0.02 |
1.68 |
- |
- |
Conclusion: The test concentrations were measured and found to remain within ±20% of nominal. Hence, the EC50(0.16 mg/L) was expressed based on nominal concentrations.
Result tables:
Nominal conc. (mg/l) |
Number of Daphnids/replicate |
Immobility |
|||||||||||||
0h |
24h |
48h |
Cumulative Immobilization |
Percent Inhibition |
|||||||||||
control |
5 |
R1=0 |
R2=0 |
R3=0 |
R4=0 |
R1=0 |
R2=0 |
R3=0 |
R4=0 |
R1=0 |
R2=0 |
R3=0 |
R4=0 |
- |
- |
0.125 |
5 |
R1=0 |
R2=0 |
R3=0 |
R4=0 |
R1=0 |
R2=0 |
R3=0 |
R4=0 |
R1=2 |
R2=2 |
R3=2 |
R4=2 |
8 |
40 |
0.25 |
5 |
R1=0 |
R2=0 |
R3=0 |
R4=0 |
R1=0 |
R2=0 |
R3=0 |
R4=0 |
R1=2 |
R2=3 |
R3=4 |
R4=3 |
12 |
60 |
0.5 |
5 |
R1=0 |
R2=0 |
R3=0 |
R4=0 |
R1=1 |
R2=1 |
R3=1 |
R4=1 |
R1=4 |
R2=4 |
R3=4 |
R4=4 |
20 |
100 |
1 |
5 |
R1=0 |
R2=0 |
R3=0 |
R4=0 |
R1=1 |
R2=1 |
R3=1 |
R4=1 |
R1=4 |
R2=4 |
R3=4 |
R4=4 |
20 |
100 |
2 |
5 |
R1=0 |
R2=0 |
R3=0 |
R4=0 |
R1=1 |
R2=2 |
R3=1 |
R4=0 |
R1=4 |
R2=3 |
R3=4 |
R4=5 |
20 |
100 |
Any abnormal behavior(if any) |
Slow movement as compared to control |
Slow movement as compared to control |
Immobiltiy observed in higher concentration |
|
|
Table: pH, temperature and DO values
0 hour
Nominal conc. (mg/l) |
Temperature(° C) |
DO(mg/l) |
pH |
|||||||||
control |
R1=19.3 |
R2=19.3 |
R3=19.3 |
R4=19.3 |
R1=8.0 |
R2=8.0 |
R3=8.0 |
R4=8.0 |
R1=7.3 |
R2=7.3 |
R3=7.3 |
R4=7.3 |
0.125 |
R1=20.1 |
R2=20.1 |
R3=20.1 |
R4=20.1 |
R1=7.8 |
R2=7.8 |
R3=7.8 |
R4=7.8 |
R1=7.8 |
R2=7.8 |
R3=7.8 |
R4=7.8 |
0.25 |
R1=20.2 |
R2=20.2 |
R3=20.2 |
R4=20.2 |
R1=7.7 |
R2=7.7 |
R3=7.7 |
R4=7.7 |
R1=7.9 |
R2=7.9 |
R3=7.9 |
R4=7.9 |
0.5 |
R1=20.4 |
R2=20.4 |
R3=20.4 |
R4=20.4 |
R1=7.7 |
R2=7.7 |
R3=7.7 |
R4=7.7 |
R1=7.9 |
R2=7.9 |
R3=7.9 |
R4=7.9 |
1 |
R1=20.5 |
R2=20.5 |
R3=20.5 |
R4=20.5 |
R1=7.5 |
R2=7.5 |
R3=7.5 |
R4=7.5 |
R1=8.0 |
R2=8.0 |
R3=8.0 |
R4=8.0 |
2 |
R1=20.5 |
R2=20.5 |
R3=20.5 |
R4=20.5 |
R1=7.4 |
R2=7.4 |
R3=7.4 |
R4=7.4 |
R1=8.1 |
R2=8.1 |
R3=8.1 |
R4=8.1 |
24 Hours
Nominal conc. (mg/l) |
Temperature(° C) |
DO(mg/l) |
pH |
|||||||||
control |
R1=19.5 |
R2=19.5 |
R3=19.5 |
R4=19.5 |
R1=7.7 |
R2=7.7 |
R3=7.7 |
R4=7.7 |
R1=7.4 |
R2=7.4 |
R3=7.4 |
R4=7.4 |
0.125 |
R1=19.9 |
R2=19.9 |
R3=19.9 |
R4=19.9 |
R1=7.9 |
R2=7.9 |
R3=7.9 |
R4=7.9 |
R1=7.9 |
R2=7.9 |
R3=7.9 |
R4=7.9 |
0.25 |
R1=20.0 |
R2=20.0 |
R3=20.0 |
R4=20.0 |
R1=7.8 |
R2=7.8 |
R3=7.8 |
R4=7.8 |
R1=8.0 |
R2=8.0 |
R3=8.0 |
R4=8.0 |
0.5 |
R1=20.1 |
R2=20.1 |
R3=20.1 |
R4=20.1 |
R1=7.7 |
R2=7.7 |
R3=7.7 |
R4=7.7 |
R1=7.9 |
R2=7.9 |
R3=7.9 |
R4=7.9 |
1 |
R1=20.1 |
R2=20.1 |
R3=20.1 |
R4=20.1 |
R1=7.6 |
R2=7.6 |
R3=7.6 |
R4=7.6 |
R1=8.0 |
R2=8.0 |
R3=8.0 |
R4=8.0 |
2 |
R1=20.1 |
R2=20.1 |
R3=20.1 |
R4=20.1 |
R1=7.7 |
R2=7.7 |
R3=7.7 |
R4=7.7 |
R1=8.1 |
R2=8.1 |
R3=8.1 |
R4=8.1 |
48 hours
Nominal conc. (mg/l) |
Temperature(° C) |
DO(mg/l) |
pH |
|||||||||
control |
R1=19.9 |
R2=19.9 |
R3=19.9 |
R4=19.9 |
R1=8.0 |
R2=8.0 |
R3=8.0 |
R4=8.0 |
R1=7.6 |
R2=7.6 |
R3=7.6 |
R4=7.6 |
0.125 |
R1=19.8 |
R2=19.8 |
R3=19.8 |
R4=19.8 |
R1=8.1 |
R2=8.1 |
R3=8.1 |
R4=8.1 |
R1=7.5 |
R2=7.5 |
R3=7.5 |
R4=7.5 |
0.25 |
R1=19.7 |
R2=19.7 |
R3=19.7 |
R4=19.7 |
R1=7.9 |
R2=7.9 |
R3=7.9 |
R4=7.9 |
R1=7.4 |
R2=7.4 |
R3=7.4 |
R4=7.4 |
0.5 |
R1=- |
R2=- |
R3=- |
R4=- |
R1=- |
R2=- |
R3=- |
R4=- |
R1=- |
R2=- |
R3=- |
R4=- |
1 |
R1=- |
R2=- |
R3=- |
R4=- |
R1=- |
R2=- |
R3=- |
R4=- |
R1=- |
R2=- |
R3=- |
R4=- |
2 |
R1=- |
R2=- |
R3=- |
R4=- |
R1=- |
R2=- |
R3=- |
R4=- |
R1=- |
R2=- |
R3=- |
R4=- |
Description of key information
This study was designed (as per OECD 202, adopted in 2004) to assess the acute toxicity of test chemical following exposure of daphnids up to 48h by static method. The test daphnids were acclimatized 48 hours prior to the test chemical exposure. After exposure on day 0, daphnids were observed for immobilization at 24 and 48 h. M7 medium was used as control, and the same was used for test chemical formulation . 100 mL glass beakers having a solution volume of 30 mL were used in the test. . Main study (using a spacing factor of 2) was conducted using 0 (control), 0.125, 0.25, 0.5, 1 and 2 mg/L concentrations. 2 replicates/concentration having 5 daphnids/replicate was used for the main study. UV-Visible spectrophotometer method was used for active ingredient analysis along with stability of the test item in the test medium. Test item was found to be stable in the test medium. The active ingredient content results were considered acceptable (80-120%) as during main study 0 h and after 48 hours of exposure, which were found in acceptable range. Hence the results were based on nominal concentration since the deviation in the initial measured concentration didn’t exceed 20%. Environmental parameters such as pH (7.3 -7.6), temperature (20-21°C), dissolve oxygen (7.4 - 8.1 mg/L), hardness (225 mg CaCO3/L), light intensity of 1086 lux, photoperiod (16 h light- 8 h dark) was maintained in acceptable range throughout the test. Thus, fulfilling the validity criteria. Feed was not provided during the test. Normal behavioural response and no immobilization (0% mortality) were observed up to 48 h followed by control groups but 40%, 60%, 100%, 100% and 100% immobilisation were observed in the test concentrations of 0.125, 0.25, 0.5, 1 and 2 mg/L, respectively. The 48-h EC50 of test chemical to daphnid, Daphnia magna are 0.16 mg/l. The 24-h EC50 of reference item (Potassium dichromate) to daphnid, Daphnia magna(found to be in acceptable range) is 1.33 mg/L. Hence, the results of the test with reference item establish the acceptability of the test system response, test procedures followed, and results obtained with test item. Thus, test chemical was considered as toxic to aquatic invertebrates at environmental relevant concentrations and hence, considered to be classified in 'aquatic acute/chronic category 1' as per the CLP classification criteria.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 0.16 mg/L
Additional information
This study was designed (as per OECD 202, adopted in 2004) to assess the acute toxicity of test chemical following exposure of daphnids up to 48h by static method. The test daphnids were acclimatized 48 hours prior to the test chemical exposure. After exposure on day 0, daphnids were observed for immobilization at 24 and 48 h. M7 medium was used as control, and the same was used for test chemical formulation . 100 mL glass beakers having a solution volume of 30 mL were used in the test. . Main study (using a spacing factor of 2) was conducted using 0 (control), 0.125, 0.25, 0.5, 1 and 2 mg/L concentrations. 2 replicates/concentration having 5 daphnids/replicate was used for the main study. UV-Visible spectrophotometer method was used for active ingredient analysis along with stability of the test item in the test medium. Test item was found to be stable in the test medium. The active ingredient content results were considered acceptable (80-120%) as during main study 0 h and after 48 hours of exposure, which were found in acceptable range. Hence the results were based on nominal concentration since the deviation in the initial measured concentration didn’t exceed 20%. Environmental parameters such as pH (7.3 -7.6), temperature (20-21°C), dissolve oxygen (7.4 - 8.1 mg/L), hardness (225 mg CaCO3/L), light intensity of 1086 lux, photoperiod (16 h light- 8 h dark) was maintained in acceptable range throughout the test. Thus, fulfilling the validity criteria. Feed was not provided during the test. Normal behavioural response and no immobilization (0% mortality) were observed up to 48 h followed by control groups but 40%, 60%, 100%, 100% and 100% immobilisation were observed in the test concentrations of 0.125, 0.25, 0.5, 1 and 2 mg/L, respectively. The 48-h EC50 of test chemical to daphnid, Daphnia magna are 0.16 mg/l. The 24-h EC50 of reference item (Potassium dichromate) to daphnid, Daphnia magna(found to be in acceptable range) is 1.33 mg/L. Hence, the results of the test with reference item establish the acceptability of the test system response, test procedures followed, and results obtained with test item. Thus, test chemical was considered as toxic to aquatic invertebrates at environmental relevant concentrations and hence, considered to be classified in 'aquatic acute/chronic category 1' as per the CLP classification criteria.
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