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EC number: 226-109-5 | CAS number: 5281-04-9
- 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
Additional information on environmental fate and behaviour
Administrative data
- Endpoint:
- additional information on environmental fate and behaviour
- Remarks:
- Dispersion stability in simulated environmental media
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2020
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 020
- Report date:
- 2020
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: OECD 318
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- Calcium 3-hydroxy-4-[(4-methyl-2-sulphonatophenyl)azo]-2-naphthoate
- EC Number:
- 226-109-5
- EC Name:
- Calcium 3-hydroxy-4-[(4-methyl-2-sulphonatophenyl)azo]-2-naphthoate
- Cas Number:
- 5281-04-9
- Molecular formula:
- C18H14N2O6S.Ca
- IUPAC Name:
- calcium 3-hydroxy-4-[(1E)-2-(4-methyl-2-sulfonatophenyl)diazen-1-yl]naphthalene-2-carboxylate
Constituent 1
Results and discussion
Any other information on results incl. tables
At any of the time points mentioned in the TG-318, the influence of Ca is critical. Regardless of pH, the pigment is least stable in 10 mM Ca, representing high water hardness.
After 6h, the samples showed high dispersion stability in 0 mM Ca and 1 mM Ca at pH 4. The stability at all other conditions was intermediate.
After 24 hours the stability in 0 mM Ca and 1 mM Ca at pH 4 remained high. For the samples at oder conditions the stability decreased to the lower end of intermadiate level with exception of the sample in 10 mM Ca at pH 7 which became instable.
Table 1: Full results of the dispersion stability in the presence of NOM
Ca(NO3)2 |
Stability after 6h |
Standard deviation |
Stability after 15h |
Standard deviation |
Stability after 24h |
Standard deviation |
|
[mM] |
[%] |
[%] |
[%] |
[%] |
[%] |
[%] |
|
|
|
|
|
||||
pH 4 |
0 |
100 |
0.4 |
100 |
0.5 |
100 |
0.5 |
pH 4 |
1 |
100 |
0.1 |
100 |
0.1 |
100 |
0.1 |
pH 4 |
10 |
24.3 |
1.7 |
15.6 |
1.6 |
13.1 |
1.8 |
. |
|
|
|
|
|
|
|
pH 7 |
0 |
100 |
0.2 |
100 |
0.2 |
100 |
0.2 |
pH 7 |
1 |
31.6 |
6.9 |
19.6 |
6.1 |
15.8 |
5.7 |
pH 7 |
10 |
19.0 |
2.2 |
10.2 |
0.9 |
8.2 |
0.6 |
. |
|
|
|
|
|
|
|
pH 9 |
0 |
100 |
0.5 |
100 |
0.6 |
100 |
0.5 |
pH 9 |
1 |
35.0 |
2.4 |
22.3 |
1.1 |
19.4 |
0.3 |
pH 9 |
10 |
23.9 |
3.4 |
15.8 |
0.7 |
13.6 |
0.9 |
To rationalize the observed dispersion stability, we finally checked the particle size distribution directly in the environmental medium (exact same sample preparation as for the UV/VIS measurements). We applied the NanoDefine method of Analytical Ultracentrifugation.
The observed size distributions confirm the moderate agglomeration at 1 mM Ca, pH7, with NOM. If the particles would have been significantly dissolved, no size distribution would be observable at all by this method, which relies on the detection of the movement of particles during centrifugal separation.
Additionally, the centrifugation methods include a determination of the remaining absorption after centrifugation, fully consistent with the conventional determination of the dissolved fraction after centrifugation as recommended by the TG-318. The remaining absorption was measured at ca. 0.06. This is a fraction of 4.6% of the initial absorption, but actually is close to the LOD of the built-in UV/Vis detector. Considering the LOD, between 0% and 4.6% of the sample may have been dissolved.
All evidence combined, the results after centrifugation confirm that at least 95.4% of the observed dispersion stability has to be attributed to the particles, not to dissolution.
Applicant's summary and conclusion
- Executive summary:
Elevated apparent dispersion stability may originate from dissolution. The dissolution in environmental media has not yet been assessed, but the particle size distribution was measured in all media. The remaining absorption after centrifugal separation of particles was determined to be not more than 4.6% of the total signal. Thus, dissolution is not the main cause of the observed stability.
Taken together, the dispersion stability of Pigment Red 57:1 depends on pH and water hardness. The stability in 0 mM Ca and 1 mM Ca at pH 4 is high. The stability is at pH 7 and 9 in 1 mM Ca and at pH 4 and 9 in 10 mM Ca is intermediate and at pH 7 in 10 mM Ca is low
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