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EC number: 201-535-4 | CAS number: 84-51-5
- 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
- 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:
- from 1991-02-14 to 1991-09-23
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Guideline-conform study under GLP without deviations
- Reason / purpose for cross-reference:
- reference to other study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- from 1984
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPP 72-2 (Aquatic Invertebrate Acute Toxicity Test)
- Version / remarks:
- from 1982
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 0 (control), 0 (DMSO control), 250 and 500 µg/L (nominal)
- Sampling method: not reported
- Sample storage conditions before analysis: stored cool and dark - Vehicle:
- yes
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: 50 mg 2-ethylanthraquinone was dissolved in 10 mL DMSO to obtain a concentration of 5000 mg/L. This stock solution was diluted with DMSO to obtain a second stock solution of 2500 mg/L. To erlenmeyers of 1 liter, wrapped in aluminiumfoil and containing 800 mL ISO+-water, 80 µL of these stock solutions were added. These solutions were stirred for 2 hours to obtain homogeneous nominal test concentrations of 500 and 250 µg/L. The ISO+-water was prepared and aerated at least 24 hours prior to the test.
- Eluate: not applicable
- Differential loading: not reported
- Controls: A control with DMSO in ISO+-water (0.1 mL/L) and a control with ISO+-water were included in the test.
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): DMSO
- Evidence of undissolved material (e.g. precipitate, surface film, etc): No - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: water flea
- Strain: laboratory culture of the Ecotoxicology Group, DUPHAR B.V
- Source: culture is in house since August 1986 and originates from TNO, the Netherland
- Age at study initiation (mean and range, SD): 0-24 hours
- Feeding during test: The water fleas were not fed during the test.
- Method of breeding: cultured in vessels with 2 liter reconstituted water ( ISO+) which was prepared and aerated at least 24 hours prior to use
- Type and amount of food during breeding: algal suspension of Chlorella pyrenoidosa ( 1 * 10^9 cells per day per vessel) and yeast/Mikromin suspension (1 mL per day per vessel)
- Feeding frequency: daily - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- Hardness of reconstituted dilution water: about 250 mg/L
- Test temperature:
- Control: 23.5 °C at 0 hours, 22.1 °C at 48 hours
DMSO-control: 22.4 °C at 0 hours, 22.4 °C at 48 hours
210 µg/L: 24.8 °C at 0 hours, 22.3 °C at 48 hours
374 µ/L: 24.5 °C at 0 hours, 22.3 °C at 48 hours
The temperature in the test vessels was measured one hour after removal of the test vessels from the climate chamber to the laboratory. Moreover, the thermometer used in this test appeared to overestimate the temperature by about 2°C. Therefore, the actual temperature was about 20-23°C. - pH:
- Control: 7.9 at 0 hours, 7.9 at 48 hours
DMSO-control: 8.0 at 0 hours, 8.0 at 48 hours
210 µg/L: 7.8 at 0 hours, 8.0 at 48 hours
374 µ/L: 7.8 at 0 hours, 8.0 at 48 hours - Dissolved oxygen:
- Control: 9.2 mg/L at 0 hours, 9.1 mg/L at 48 hours
DMSO-control: 9.2 mg/L at 0 hours, 9.3 mg/L at 48 hours
210 µg/L: 8.7 mg/L at 0 hours, 9.2 mg/L at 48 hours
374 µ/L: 8.7 mg/L at 0 hours, 9.2 at 48 hours - Nominal and measured concentrations:
- Nominal test concentrations: 0 µg/L (control), 0 µg/L (DMSO-control), 250 µg/L, 500 µg/L
Mean measured test concentration during test period (controls measured at 0 and 48 hours, test concentrations measured at 0, 24 and 48 hours): < 27 µg/L (control),<27 µg/L (DMSO-control), 210 µg/L, 374 µg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: 250 ml beaker glasses
- Type (delete if not applicable): not reported
- Material, fill volume: glass, 250 mL
- Aeration: not aerated
- Type of flow-through (e.g. peristaltic or proportional diluter): not applicable
- Renewal rate of test solution (frequency/flow rate): no renewal
- No. of organisms per vessel: 10
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 3
- No. of vessels per vehicle control (replicates): 3
- Biomass loading rate: not applicable
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: not reported
- Composition of reconstituted dilution water:
ISO:
Deioised water
CaCl2 · 2H2O: 294 mg/L
MgSO4 · 7 H2O: 123 mg/L
NaHCO3: 64 mg/L
KCl: 5.8 mg/L
ISO+(same as ISO with the following elements in addition):
LiCl: 8.0 µg/L
RbCl: 0.4 µg/L
SrCl2 · 6H2O: 8.0 µg/L
NaBr: 50.0 µg/L
KI: 3.0 µg/L
MnCl2 · 4H2O: 3.0 µg/L
FeCl3: 1.7 µg/L
CuCl2 · 2H2O: 6.0 µg/L
CoCl2 · 6H2O: 1.1 µg/L
Na2MoO4 · 2H2O: 0.1 µg/L
ZnCl2: 1.0 µg/L
V2O5: 1.0 µg/L
NiSO4 · 6H2O: 4.0 µg/L
Al2O3: 1.0 µg/L
NaF: 5.0 µg/L
Na2CrO4 · 4H2O: 1.0 µg/L
PbCl2: 0.4 µg/L
SnCl2: 5.1 µg/L
SeO2: 1.0 µg/L
- Culture medium different from test medium: No
- Intervals of water quality measurement: not reported
OTHER TEST CONDITIONS
- Adjustment of pH: No
- Light intensity: reduced light conditions (less than 100 lux) because additional studies showed that 2-ethylanthraquinone is highly unstable in water under influence of light
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : Immobility (examined at 24 and 48 hours), slower movement, uncontrolled movement, laying down on bottom of test vessel, abnormal shape (examined at 48 hours)
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2
- Justification for using less concentrations than requested by guideline: In a range-finding study, the presence of 2-ethylanthraquinone did not clearly cause mortality at the nominal test concentrations up to 250 µg/L. Therefore, the final test was carried out at 2 concentrations, one slightly above and one slightly below the water solubility level.
- Range finding study: yes
- Test concentrations: up to 250 µg/L
- Results used to determine the conditions for the definitive study: The water fleas were exposed during 48 hours to various concentrations of 2-ethylanthraquinone in test vessels in a range-finding test. In this study the presence of 2-ethylanthraquinone did not clearly cause mortality at the nominal test concentrations up to 250 µg/L. Therefore, the final test was carried out at 2 concentrations, one slightly above and one slightly below the water solubility level. - Reference substance (positive control):
- yes
- Remarks:
- potassium-bichromate (performed every year, last test: February 1990)
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 270 µg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Remarks on result:
- other: 95% CL: [220, 320]
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- < 210 µg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Details on results:
- - Behavioural abnormalities: immobility
- Observations on body length and weight: not reported
- Other biological observations: At 24 and 48 hours after test initiation some of the water fleas were floating on the surface of the test solution. These effects are not considered to be compound related as they occurred in nearly all test vessels.
- Mortality of control: 4/31 (control), 2/29 (DMSO-control)
- Other adverse effects control: not reported
- Abnormal responses: not reported
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: no
- Effect concentrations exceeding solubility of substance in test medium: The EC50.48h is above the solubility level of 2-ethylanthraquinone (245 µ g/L). - Results with reference substance (positive control):
- EC50.48 h: 0.42 mg/L
95% confidence interval: 0.34 - 0.48 mg/L - Validity criteria fulfilled:
- yes
- Conclusions:
- Based on the mean measured test concentrations at the initiation of the test the EC50.48 h was 270 µg/L with 95% confidence interval of 220-320 µg/L. The EC50.48h is above the solubility level of 2-ethylanthraquinone (245 µg/L). The NOEC (no observed effect concentration) was <210 µg/L.
- Executive summary:
The acute toxicity of 2-ethylanthraquinone to water fleas (Daphnia magna, Crustaceae) was tested according to OECD TG 202 at nominal test concentrations of 250 and 500 µg/L in ISO-water. As 2-ethylanthraquinone is highly unstable in water under influence of light, the test was conducted under reduced light conditions (400 lux) to reduce the decrease in test concentration. Samples of the test concentrations were taken 0, 24 and 48 hours after test initiation and analysed with HPLC. During the test, the concentration of
2-ethylanthraquinone remained above 80% of the initial test concentration. Based on the mean measured test concentrations at the initiation of the test the EC50.48 h was 270 µg/L with 95% confidence interval of 220-320 µg/L. The EC50.48h is above the solubility level of 2-ethylanthraquinone (245 µg/L). The NOEC (no observed effect concentration) was <210 µg/L.
Reference
Immobility of Daphnia magna during the acute toxicity test with 2-ethylanthraquinone
Mean measured concentration (µg/L) |
Number of immobile water fleas |
Total number of immobile water fleas |
Number of water fleas tested |
Percentage (%) immobility after 48 hours |
|
|
0-24h |
24-48h |
|
|
|
0 (control) |
2 |
2 |
4 |
31 |
10 |
0 (DMSO-control) |
0 |
2 |
2 |
29 |
|
210 |
2 |
7 |
9 |
30 |
30 |
374 |
27* |
-2* |
25 |
30 |
82 |
*Because of low light intensity a good measurement at 24 hours was not possible, and the number of immobile daphnids was overestimated.
Description of key information
In a short-term toxicity test with daphnia, the EC50 after 48 hours was 270 µg/L and the NOEC was <210 µg/L.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 270 µg/L
Additional information
The acute toxicity of 2-ethylanthraquinone to water fleas (Daphnia magna, Crustaceae) was tested according to OECD TG 202 at nominal test concentrations of 250 and 500 µg/L in ISO-water. The test substance was dissolved in DMSO prior to the preparation of test solutions due to its low water solubility. As 2-ethylanthraquinone is highly unstable in water under influence of light, the test was conducted under reduced light conditions (400 lux) to reduce the decrease in test concentration. Samples of the test solutions were taken 0, 24 and 48 hours after test initiation and analysed with HPLC. During the test, the concentration of
2-ethylanthraquinone remained above 80% of the initial test concentration. Based on the mean measured test concentrations at the initiation of the test the EC50 after 48 h was 270 µg/L with a 95% confidence interval of 220-320 µg/L. The EC50 after 48h was above the solubility level of 2-ethylanthraquinone (245 µg/L). The NOEC (no observed effect concentration) was <210 µg/L.
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