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Reaction mass of Sodium 2-(2 or 3-{[(chloroacetyl)amino]methyl}-4-{[4-(cyclohexylamino)-9,10-dioxo-9,10-dihydroanthracen-1-yl]amino}phenoxy)-5-methylbenzenesulfonate and Sodium 2-(3 or 2-{[(chloroacetyl)amino]methyl}-4-{[4-(cyclohexylamino)-9,10-dioxo-9,10-dihydroanthracen-1-yl]amino}phenoxy)-5-methylbenzenesulfonate
EC number: 942-981-6 | 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
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:
- 22 December, 1993 to 09 March, 1994
- 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
- GLP compliance:
- yes
- Specific details on test material used for the study:
- None
- Analytical monitoring:
- yes
- Details on sampling:
- Composite samples of each test concentration were drawn by mixing identical volumes of the test solutions taken from the approximate centre of the test vessels. They were taken immediately before exposure and after 48 hrs exposure and kept at 18 to 22 °C until analysis.
- Vehicle:
- yes
- Details on test solutions:
- Stock solution:
1.00 g test substance were mixed with 9.01 g water, by means of a marble mill, during 24 hours. 2.00 g of this blend were mixed and made up to 2000 ml with water.
Preparation of test solutions:
Calculated amounts of the stock solution to produce the desired test concentrations were given into the water and were homogeneously distributed. After an equilibration time of 7 hours the daphnia were transferred into the beakers. The test substance was homogeneously distributed in the test vessels at all test concentrations at the begin of the test. At the end of exposure a deposit was observed at all test concentrations. Values are based on measured concentrations at 0 h. - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Daphnia magna
- Strain: Straus 1820
- Source: CIBA-GEIGY Ltd., testing facility
- Breeding: Cultures of daphnia are maintained in glass vessels containing approx. 2.5 L of reconstituted water (see below) at 20±1 °C (water is renewed partially thrice weekly). At each renewal the daphnia are fed with a suspension of green algae (Scenedesmus subspicatus) supplemented by a suspension of TETRAMIN-extract in such quantities that the food is consumed after 24h.
- Pretreatment: 24 hours before the begin of the exposure reproductive daphnia are separated from the young by sieving all individuals through a 800 pm sieve.
This operation is repeated 6 hours before the exposure and the young (6-24h of age) are retained for the test. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
- Remarks on exposure duration:
- None
- Post exposure observation period:
- Not available
- Hardness:
- 240 mg CaC03/L
- Test temperature:
- 20±1 °C
- pH:
- 7.8 - 8.0
- Dissolved oxygen:
- ≥8.8 mg/L
- Salinity:
- Not available
- Nominal and measured concentrations:
- Nominal: 4.4, 9.6, 21, 46 and 100 mg test substance/L
Actual : 3.9, 7.9, 18.1, 35.8 and 78.1 mg test substance/L - Details on test conditions:
- Type of vessel: Beakers covered with watch glasses 100 ml solution per beaker
Test procedure: static
Duration: 48 hours
Temperature: 20.5 – 21.0 °C
Oxygen concentration: ≥ 8.8 mg/L
pH-value: 7.23 – 7.95
Exposure to light: 16 hours photoperiod / 8 hours darkness daily
Feeding: None during the test
Test vessels: four 100 mL glass beakers per concentration, each filled with 50 mL, one additional replicate for measurements without test organisms
Loading: 10 mL of test solution for each animal
Number of animals: 20 per concentration in 4 replicates of 5
Observations: Immobilizations were recorded after 24 and 48 hours exposure.
Measurements: The oxygen content, pH and temperature were measured at 0 and 48 hours.
Calculâtions/Statistical Analysis: None - Reference substance (positive control):
- not specified
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 78 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 78 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 78 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- EC0
- Effect conc.:
- 78 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Duration:
- 48 h
- Dose descriptor:
- EC100
- Effect conc.:
- > 78 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Details on results:
- None
- Results with reference substance (positive control):
- Not available
- Reported statistics and error estimates:
- None
- Validity criteria fulfilled:
- yes
- Conclusions:
- The EC50 (48 h) for immobilisation was determined to be >78 mg/L. The corresponding NOEC (48 h) was 78 mg/L.
- Executive summary:
An acute toxicity test on Daphnia magna (Daphnia magna Straus 1820) was performed on FAT 20077/C according to the 92/69/EEC C.2 Acute toxicity for Daphnia method.
In a static assay, 20 daphnia’s were exposed to nominal concentrations of 4.4, 9.6, 21, 46 and 100 mg/L. The corresponding measured concentions were determined to be 0, 3.6, 7.4, 16.3, 34.6 and 75.2 mg/L.
The percentage immobilisations observed with test concentrations 0, 3.6, 7.4, 16.3, 34.6 and 75.2 mg/L were 5, 5, 0, 10, 5 and 0, respectively.
Based on these findings, the following results were obtained:
EC50 (48 h) calculated: >78 mg/l
NOEC (48 h): 78 mg/l
EC0 (48 h): >78 mg/l
EC100 (48h): >78 mg/l
Reference
The rate immobilisations observed with test concentrations 0, 3.6, 7.4, 16.3, 34.6 and 75.2 mg/L were 5 %, 5 %, 0 %, 10 %, 5 % and 0 %, respectively.
Description of key information
An acute toxicity test on Daphnia magna (Daphnia magna Straus 1820) was performed on FAT 20077/C according to the 92/69/EEC C.2 Acute toxicity for Daphnia method.
In a static assay, 20 daphnia’s were exposed to nominal concentrations of4.4, 9.6, 21, 46 and 100 mg/L.The corresponding measured concentions were determined to be 0, 3.6, 7.4, 16.3, 34.6 and 75.2 mg/L.
The percentage immobilisations observed with test concentrations 0, 3.6, 7.4, 16.3, 34.6 and 75.2 mg/L were 5, 5, 0, 10, 5 and 0, respectively.
Based on these findings, the following results were obtained:
EC50 (48 h) calculated: >78 mg/l
NOEC (48 h): 78 mg/l
EC0 (48 h): >78 mg/l
EC100 (48h): >78 mg/l
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 78 mg/L
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