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EC number: 404-600-7 | CAS number: 129009-88-7 EVERZOL ORANGE GR; ORANGE HF-SNK; REAKTIV ORANGE FD 19969 FW
- 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 Sep. 03, 1997 to Nov. 07, 1997
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- - Sampling method: Water samples were taken at study start and study end from all tested concentrations.
- Sample preparation: The samples were diluted with mobile phase
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method of administration: Test substance was weighed into a graduated flask, filled up with test water and stirred for about 5 min with a magnetic stirrer. The amounts corresponding to the test concentrations were pipetted into a graduated flask, made up to a total volume of 200 mL with test water, and then transferred to the test chambers - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Water flea
- Strain: Clone 5 (IRChA, France)
- Source: Stock culture of Hoechst Marion Roussel Deutschland GmbH, Global Preclinical Development - Drug Safety, 65926 Frankfurt am Main.
- Age at study initiation (mean and range, SD): 0-24 h
- Method of breeding: 100 mL beakers (height 90 mm, diameter 50 mm), filled with 70 mL test water (according to Elendt, M4) served as culture vessels. One daphnid was used per culture vessel. The animals were used for breeding up to an age of 42 d. The reproduction rate and the state of health of the animals were monitored daily apart from weekends.
- Food type: monocellular green algae (Scenedesmus subspicatus).
- Frequency: Three times a week - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
- Remarks on exposure duration:
- None
- Post exposure observation period:
- No
- Hardness:
- No data
- Test temperature:
- 20.5-21.2 °C
- pH:
- 7.8-8.3
- Dissolved oxygen:
- 8.4-9.0 mg/L
- Salinity:
- No data
- Nominal and measured concentrations:
- Nominal: 0, 22, 50, 100, 220, 500 mg/L
Measured (mean): 0, 19.4, 48, 86, 193, 479 mg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: Beakers
- Material, size, headspace, fill volume: 250 mL beakers (height 110 mm, diameter 70 mm, water level about 75 mm), each filled with 200 mL
test water
- Aeration: Aerated until saturated with oxygen
- Renewal rate of test solution: No
- No. of organisms per vessel: 10 daphnids/vessel
- No. of vessels per concentration (replicates): 2
- No. of vessels per control (replicates): 2
- Keeping water: Reconstituted fresh water
- Method of administration: Direct weighing
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Demineralized water with a conductance of < 1 µS /cm was used for preparing the artificial fresh water (according to Elendt)
OTHER TEST CONDITIONS
- Photoperiod: 12 h light/12 h dark
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : Number of immobile daphnids after 24 h and 48 h - Reference substance (positive control):
- no
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 117.4 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 87.88-158.9
- Duration:
- 48 h
- Dose descriptor:
- EC0
- Effect conc.:
- 22 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: -
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- 362 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 292-468.2
- Duration:
- 24 h
- Dose descriptor:
- EC0
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: -
- Duration:
- 48 h
- Dose descriptor:
- EC100
- Effect conc.:
- 500 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: -
- Details on results:
- - Other biological observations: No
- Mortality of control: No
- No immobility was observed in control group - Results with reference substance (positive control):
- Not applicable
- Reported statistics and error estimates:
- ECSO values were determined after 24 and 48 h by means of the probit analysis (after the method according to LINDER und WEBER, confidence limit according to FIELLER).
- Validity criteria fulfilled:
- yes
- Conclusions:
- Under the test conditions, the 48 h EC50 value of the test substance was determined to be 117.4 mg/L.
- Executive summary:
A study was performed to assess the acute toxicity of test substance to Daphnia magna (water flea) over 48 h under static conditions. The study was conducted in accordance with OECD Guideline 202 and EU Method C.2. in compliance with GLP.
Daphnids were exposed to the concentrations tested were 22, 50, 100, 220 and 500 mg/L and a negative control (0 mg/L). The substance concentration was determined in all tested groups at the test start and after 48 h of exposure. Observations were made on the immobilisation rate after 24 and 48 h of exposure.
All tested concentrations were present as clear orange solutions. The values determined were in a range of ± 20 % of the theoretical value.
The 24 and 48 h EC50 values were determined to be 362.8 and 117.4 mg/L respectively. In the control group no immobility was observed. Immobility was observed at 50, 100, 220 and 500 mg/L. The 22 mg/L group showed no effect in comparison to the negative control.
Reference
Table 1. Immobility-Results
Concentration mg/L |
Immobility after 24 h |
Immobility after 48 h |
||
Absolute |
% |
Absolute |
% |
|
22 |
0/20 |
0 |
0/20 |
0 |
50 |
0/20 |
0 |
3/20 |
15 |
100 |
0/20 |
0 |
14/20 |
70 |
220 |
3/20 |
15 |
10/20 |
50 |
500 |
15/20 |
75 |
20/20 |
100 |
Description of key information
The 48 h EC50 value of the test substance was determined to be 117.4 mg/L
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Dose descriptor:
- EC50
- Effect concentration:
- 117.4 mg/L
Additional information
A study was performed to assess the acute toxicity of test substance to Daphnia magna (water flea) over 48 h under static conditions. The study was conducted in accordance with OECD Guideline 202 and EU Method C.2.
Daphnids were exposed to the concentrations tested were 22, 50, 100, 220 and 500 mg/L and a negative control (0 mg/L). Analysis was performed for the test concentration plus a control at the test start and after 48 h of exposure. Observations were made on the immobilisation rate, after 24 and 48 h of exposure.
All tested concentrations were present as clear orange solutions. The substance concentration was determined in all tested groups. The values determined were in a range of ± 20 % of the theoretical value.
The 24 and 48 h EC50 values were determined to be 362.8 and 117.4 mg/L respectively. In the control group no immobility was observed. Immobility was observed at 50, 100, 220 and 500 mg/L. The 22 mg/L group showed no effect in comparison to the negative control.
The 48 h EC50 value of the test substance was determined to be 117.4 mg/L (Dr. Zok S, 1997)
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