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Reaction mass of sodium [2,4-dihydro-4-[(2-hydroxy-5-nitrophenyl)azo]-5-methyl-2-phenyl-3H-pyrazol-3-onato(2-)][1-[(2-hydroxy-5-nitrophenyl)azo]-2-naphtholato(2-)]chromate(1-) and sodium bis[1-[(2-hydroxy-5-nitrophenyl)azo]-2-naphtholato(2-)]chromate(1-) and sodium bis[2,4-dihydro-4-[(2-hydroxy-5-nitrophenyl)azo]-5-methyl-2-phenyl-3H-pyrazol-3-onato(2-)]chromate(1-)
EC number: 915-758-6 | CAS number: -
- 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:
- 2016-09-21 to 2017-05-10
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 017
- Report date:
- 2017
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- 2004-11-23
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Version / remarks:
- No 440/2008
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- Reaction mass of sodium [2,4-dihydro-4-[(2-hydroxy-5-nitrophenyl)azo]-5-methyl-2-phenyl-3H-pyrazol-3-onato(2-)][1-[(2-hydroxy-5-nitrophenyl)azo]-2-naphtholato(2-)]chromate(1-) and sodium bis[1-[(2-hydroxy-5-nitrophenyl)azo]-2-naphtholato(2-)]chromate(1-) and sodium bis[2,4-dihydro-4-[(2-hydroxy-5-nitrophenyl)azo]-5-methyl-2-phenyl-3H-pyrazol-3-onato(2-)]chromate(1-)
- EC Number:
- 915-758-6
- Molecular formula:
- C32H18CrN6O8.Na / C32H22CrN10O8.Na / C32H20CrN8O8.Na
- IUPAC Name:
- Reaction mass of sodium [2,4-dihydro-4-[(2-hydroxy-5-nitrophenyl)azo]-5-methyl-2-phenyl-3H-pyrazol-3-onato(2-)][1-[(2-hydroxy-5-nitrophenyl)azo]-2-naphtholato(2-)]chromate(1-) and sodium bis[1-[(2-hydroxy-5-nitrophenyl)azo]-2-naphtholato(2-)]chromate(1-) and sodium bis[2,4-dihydro-4-[(2-hydroxy-5-nitrophenyl)azo]-5-methyl-2-phenyl-3H-pyrazol-3-onato(2-)]chromate(1-)
- Test material form:
- solid
- Details on test material:
- Appearance:
- physical state: solid
- color: dark brown
Constituent 1
- Specific details on test material used for the study:
- STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: Room temperature
Sampling and analysis
- Analytical monitoring:
- no
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Waterflea
- Strain/clone: Daphnia magna STRAUS
- Source: The clone of Daphnia magna STRAUS 1820 used was supplied by the Institut National de Recherche Chimique Appliquee, France, in 1978. From this date on this clone was cultured and bred continuously in the Ecotoxicology Laboratory of Experimental Toxicology and Ecology, BASF SE, Ludwigshafen Germany.
- Age of parental stock (mean and range, SD): approx. 20 - 30 parthenogenetically reproducing females for a maximum of 4 weeks.
- Age at start of exposure: < 24 hours (at least 3rd brood progeny)
- Feeding during test: No feeding during the exposure period.
ACCLIMATION
- Acclimation conditions (same as test or not): The Daphnia are cultured under the identical conditions as the test including test media (Elendt M4), water quality, and temperature (20 ± 1 °C).
METHOD FOR PREPARATION AND COLLECTION OF EARLY INSTARS OR OTHER LIFE STAGES:
All individuals in each mass culture originate from a single female and are thus genetic clones. After approximately 14 days the adults have produced at least 3 broods and the young can be used in tests. Offspring are removed from the mass cultures at least once daily during the normal work week to ensure that young daphnia are <24-h old (first instar) at start of the exposure.
Study design
- Test type:
- semi-static
- Water media type:
- freshwater
- Remarks:
- A synthetic fresh water (Elendt M4) is used as media for culture and test purposes. For the composition of this M4 medium see OECD 202.
- Limit test:
- yes
- Total exposure duration:
- 48 h
Test conditions
- Hardness:
- 2.20 - 3.20 mmol/L
- Test temperature:
- 19.7 - 20.1 °C
- pH:
- 7.5 - 8.5
- Dissolved oxygen:
- 8.7 - 9.4 mg/L
- Conductivity:
- 550 - 650 µS/cm
- Nominal and measured concentrations:
- 100 mg/L (nominal)
- Details on test conditions:
- TEST SYSTEM
- Test vessel: Numbered glass beakers (nominal volume 100 mL)
- Fill volume: 50 mL
- Aeration: ~ 24 hours prior to use.
- Renewal rate of test solution (frequency): 24 h
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
- Biomass loading rate: 0.1 animals/mL
TEST MEDIUM / WATER PARAMETERS
- Total organic carbon: <2 mg/L
- Ca/Mg ratio: about 4:1
- Conductivity: 550 - 650 µS/cm
- Culture medium different from test medium: no
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16 hours light : 8 hours darkness
- Light intensity: 161 - 677 lux at a wave length of 400 - 750 nm
EFFECT PARAMETERS MEASURED: Mobility after 0, 24, and 48 h
VEHICLE CONTROL PERFORMED: no
RANGE-FINDING STUDY
- Test concentrations: In a preliminary test (experimental conduct in accordance with GLP, without a GLP status, a concentration of 100 mg/L caused no immobilisation or symptoms after 48 hours.
- Results used to determine the conditions for the definitive study: yes - Reference substance (positive control):
- yes
- Remarks:
- Sodium chloride
Results and discussion
Effect concentrations
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- other: loading rate
- Basis for effect:
- mobility
- Details on results:
- VALIDITY CRITERIA
This test was fully compliant with all the following validity criteria required by the corresponding test guidelines and is considered valid.
• ≤10% immobilisation in the control
• O2 concentration ≥3 mg/L in control and test vessels
Any other information on results incl. tables
Table 1: Number of mobile Daphnids
Nominal concentration [mg/L] |
Number of mobileDaphniaat each observation period |
|||||||||||||
Replicate 1 |
Replicate 2 |
Replicate 3 |
Replicate 4 |
∑ |
∑ |
|||||||||
0 |
24 |
48 |
0 |
24 |
48 |
0 |
24 |
48 |
0 |
24 |
48 |
24 h |
48 h |
|
0 (control) |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
20 |
20 |
100 |
5 |
5 |
5 |
5 |
5 |
4 |
5 |
5 |
5 |
5 |
5 |
5 |
20 |
19 |
Number of test animals per replicate: 5 Number of test animals per test group: 20 |
Table 2: Total organic carbon (TOC) content
Loading rate [mg/L] | after 0 h [mg/L] | after 24 h [mg/L] |
0 (control) | 0.9 | 1.1 |
100 | 3 | 3.1 |
The TOC in the treatment group was higher than in the control test medium. The higher TOC is likely due to soluble organic components from the test substance. The TOC value confirms qualitatively that the daphnids in the WAF were exposed to soluble organic components from the test substance.
Table 3: DIissolution Behavior
Test Group [mg/L] |
0 hour | 24 hours | 48 hours | |
Old test solution | New test solution | |||
0 (control) | 0 | 0 | 0 | 0 |
100 | 1 | 1 | 1 | 1 |
Explanation of abbreviations:
0: no remarkable observations, clear test medium
1: coloration caused by the test substance (yellow)
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- The test item is with high probability not acutely harmful to aquatic invertebrates.
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