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EC number: 215-445-8 | CAS number: 1326-83-6 This substance is identified in the Colour Index by Colour Index Constitution Number, C.I. 53186.
- 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:
- 2019-04-30 to 2019-05-02
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- 2004
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Version / remarks:
- 2008
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 850.1010 (Aquatic Invertebrate Acute Toxicity Test, Freshwater Daphnids)
- Version / remarks:
- 2016
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 100 mg/L
- Sampling method: For the determination of the test item concentration, samples were taken from the test item treated group and from the control group (4 x 10 mL at the start and 4 x 10 mL at the end of the study).
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION:
The test solution used in the test was prepared by mechanical dispersion without using any solubilizing agent. An amount of 0.0314 g test item was dissolved in 314 mL dilution water (ISO medium see 5.4) in order to obtain the nominal concentration of 100 mg/L. Thereafter this solution was placed into an ultrasonic bath for approximately 5 minutes. The test solution was freshly prepared in the testing laboratory just before introduction of test animals (start of the experiment). No precipitation or particles were observed. - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Daphnia magna (Straus)
- Strain/clone: Straus
- Age at study initiation: Less than 24 h old at the beginning of the test.
- Sex: female
- Method of breeding: The Daphnia are bred in the Laboratory of TOXI-COOP ZRT.
- Source: Laboratory of Hydrobiology (Central Agricultural Office, Directorate of Plant-, and Soil Protection) 2100 Gödöllő, Kotlán S. u. 3. Hungary
- Feeding during test :Test animals were not fed during the exposure.
ACCLIMATION
- Acclimation period and conditions: Test animals were bred under similar (or the same) conditions as that used during the exposure period (holding water, temperature, background colour etc.), therefore additional acclimatisation before the test was not necessary. Brood daphnids were maintained in dilution water at the test temperature for at least 48 hours prior to the start of the test.
- Food and Feeding: The Daphnia were fed with concentrated algal suspension of Raphidocelis subcapitata during the holding.
- Health during acclimation (any mortality observed): Apparently healthy animals were used in this test with a known history
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
- Hardness:
- 249 mg/L (as CaCO3)
- Test temperature:
- 21.0 – 21.3 °C (in the test vessels)
20.3 – 21.4 °C (within the climate chamber) - pH:
- 7.29 - 8.10
- Dissolved oxygen:
- 8.03 –8.38 mg/L
- Salinity:
- Not applicable.
- Conductivity:
- No data.
- Nominal and measured concentrations:
- Nominal concentrations: 100 mg/L
Measured concentrations: The analytically measured test item concentration remained within ± 20 % of the nominal during the test period of 48 hours; therefore, biological results are based on the nominal concentration. - Details on test conditions:
- TEST SYSTEM
- Test vessel: Glass beaker
- Material, size, fill volume: glass, volume approx. 50 mL filled with approx. 40 mL
- Aeration: No
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: According to OECD guideline 202
OTHER TEST CONDITIONS
- Adjustment of pH: No
- Photoperiod: 16 h light: 8 h dark
- Light intensity: The measured light intensity was 749 lux in the climate chamber at the start of the test.
EFFECT PARAMETERS MEASURED: Determination of immobility or mortality of the Daphnia was determined by visual observation after 24 and 48 hours of exposure. Those animals not able to swim within 15 seconds after gentle agitation of the test beaker are considered to be immobile. In addition to immobility any abnormal behaviour or appearance is reported.
RANGE-FINDING STUDY
- Test concentrations: 100 mg/L
- Results used to determine the conditions for the definitive study: In the preliminary test ten daphnids (divided into 2 replicates) were exposed to the test item at a concentration of 100 mg/L for 48 hours. The test solution used in the test was prepared by mechanical dispersion. 0.0306 g of test item was dissolved in 306 mL dilution water (ISO medium) in order to obtain the concentration of 100 mg/L. This test solution was placed into an ultrasonic bath for approximately 5 minutes. Based on the results of the preliminary test, the test item had no toxic effect on the daphnids up to a concentration of 100 mg/L. Based on the results of the non-GLP Preliminary Range-Finding Test, a single nominal concentration of 100 mg/L (limit test concentration) and a concurrent control were tested in the main study. - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
- Key result
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks:
- mortality
- Duration:
- 48 h
- Dose descriptor:
- LOEC
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks:
- mortality
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks:
- mortality
- Details on results:
- No immobilisation or any abnormal behaviour of test animals was observed in the control group and no immobilization or any abnormal behavior of the test animals was observed at the test concentration of 100 mg/L after 48 hours of exposure.
- Results with reference substance (positive control):
- - Results with reference substance valid?
Yes
- 24h EC50: 1.58 mg/L (95% conf. limits: 1.34 – 1.85 mg/L) - Reported statistics and error estimates:
- A limit test was performed and no toxic effects were observed, therefore statistical analysis was not necessary. The NOEC and LOEC values of the test item were determined directly from the raw data.
- Validity criteria fulfilled:
- yes
- Conclusions:
- In this acute immobilisation study with Daphnia magna according to OECD guideline 202, the 48-h NOEC was determined to be 100 mg/L and the 48-h LOEC value was determined to be >100 mg/L (corresponding to 16 and >16 mg/ dyestuff/L, repsectively).
- Executive summary:
The influence of the test item Solubilized Sulphur Black 1 liquid on the mobility respectively survival of Daphnia magna was assessed in an acute immobilisation test according to OECD guideline 202. Young Daphnia were exposed to aqueous test media containing the test item for 48 hours. Based on results obtained in a non-GLP preliminary experiment Daphnia were exposed to a single concentration of 100 mg/L (limit concentration), corresponding to 16 mg dyestuff/L. A concurrent control group was run. A static test was performed as the test item was previously shown to be stable in the ISO medium for 48 hours. The quantification of the test item was performed by a previously validated analytical method. Samples were taken from the test concentration and the control at the start and at the end of the test. The analytically measured test item concentration remained within ± 20 % of the nominal during the test period of 48 hours; therefore, biological results are based on the nominal concentration. Twenty Daphnia (divided into 4 replicates) were tested each, exposed to 100 mg/L test item and in the control. The immobilisation of the test animals was recorded 24 and 48 hours after treatment. No immobilisation or any abnormal behaviour of test animals was observed in the control group and no immobilization or any abnormal behavior of the test animals was observed at the test concentration of 100 mg/L after 48 hours of exposure (equivalent to 16 mg dyestuff/L). The 48 -h NOEC was determined to be 100 mg/L and the 48 -h LOEC value was determined to be > 100 mg/L (corresponding to >16 mg/dyestuff/L). All validity criteria were met and therefore the study can be considered as valid.
Reference
Analytical results
The quantification of the test item in the test solutions was performed by a previously validated analytical method (Study Code: 805-100-4366) by the analytical laboratory of TOXI-COOP ZRT. Samples were taken from the test concentration and the control at the start and at the end of the experiment and analysed by VIS spectrophotometric method.
The measured concentration of the test item in the test solution was 96 % of the nominal value at the start and 100 % of the nominal value at the end of the test. There is evidence that the concentration of the tested substance was maintained within ± 20 % of the nominal concentration throughout the test. Therefore the analysis of the results was based on the nominal concentration value. Test item was not detected in the control group.
Nominalconcentrationmg/L |
Start (April 30, 2019) |
End (May 02, 2019) |
||
Mean of the measured concentrations (mg/L) (n=4) |
Measured concentration in % of the nominal
|
Mean of the measured concentrations (mg/L) (n=4) |
Measured concentration in % of the nominal |
|
100 |
95.6±0.70 |
96 |
100.4±0.47 |
100 |
Control |
<LOD |
- |
<LOD |
- |
Description of key information
In an acute immobilisation study with Daphnia magna according to OECD guideline 202, no immobilization or any abnormal behavior of the test animals was observed at the limit concentration of 100 mg/L (equivalent to 16 mg dyestuff/L). The 48 -h NOEC was determined to be 100 mg/L and the 48-h LOEC value was determined to be > 100 mg/L.
Key value for chemical safety assessment
Additional information
The influence of the test item Solubilized Sulphur Black 1 liquid on the mobility respectively survival of Daphnia magna was assessed in an acute immobilisation test according to OECD guideline 202. Young Daphnia were exposed to aqueous test media containing the test item for 48 hours. Based on results obtained in a non-GLP preliminary experiment Daphnia were exposed to a single concentration of 100 mg/L (limit concentration, corresponding to 16 mg dyestuff/L). A concurrent control group was run. A static test was performed as the test item was previously shown to be stable in the ISO medium for 48 hours. The quantification of the test item was performed by a previously validated analytical method. Samples were taken from the test concentration and the control at the start and at the end of the test. The analytically measured test item concentration remained within ± 20 % of the nominal during the test period of 48 hours; therefore, biological results are based on the nominal concentration. Twenty Daphnia (divided into 4 replicates) were tested each, exposed to 100 mg/L test item and in the control. The immobilisation of the test animals was recorded 24 and 48 hours after treatment. No immobilisation or any abnormal behaviour of test animals was observed in the control group and no immobilization or any abnormal behavior of the test animals was observed at the test concentration of 100 mg/L after 48 hours of exposure. The 48-h NOEC was determined to be 100 mg/L and the 48-h LOEC value was determined to be > 100 mg/L. All validity criteria were met and therefore the study can be considered as valid
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