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EC number: 231-494-8 | CAS number: 7585-41-3
- 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
Adsorption / desorption
Administrative data
- Endpoint:
- adsorption / desorption: screening
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- the study does not need to be conducted because the physicochemical properties of the substance indicate that it can be expected to have a low potential for adsorption
- Justification for type of information:
- JUSTIFICATION FOR DATA WAIVING
see attached justification
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- data waiving: supporting information
Reference
- 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
- Qualifier:
- according to guideline
- Guideline:
- other: OECD 318
- GLP compliance:
- yes (incl. QA statement)
- Executive summary:
The dispersion stability of Pigment Red 48:1 depends especially on pH and water hardness. In 0 mM Ca at pH 7 and 9 the stability was high. At pH 4 in 0 mM Ca and at pH 9 in 1 mM Ca the stability was intermediate. The stability at all other conditions was low
At any of the time points mentioned in the TG-318, the influence of Ca is critical. Regardless of pH, the pigment is categorized at the 24h-sampling time as “unstable” in 10 mM Ca, representing high water hardness.
After 6h, the samples showed high dispersion stability in 0 mM Ca and at pH 9 in 1 mM Ca. Stability at all other conditions was either intermediate (pH 4 and 7 in 1 mM Ca) or low (all samples in 10 mM Ca).
After 24 hoursthe stability for samplesin 0 mM Ca at pH 7 and 9 was high. For the samples at pH 4 in 0 mM Ca and at pH 9 in 1 mM Ca the stability was intermediate. The stability at all other conditions was low.
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 |
98.8 |
0.4 |
94.7 |
1.5 |
86.6 |
2.9 |
pH 4 |
1 |
34.6 |
6.9 |
12.5 |
3.9 |
7.7 |
2.0 |
pH 4 |
10 |
6.5 |
1.2 |
3.5 |
0.2 |
2.8 |
0.3 |
. |
|
|
|
|
|
|
|
pH 7 |
0 |
99.7 |
0.2 |
97.7 |
0.7 |
95.8 |
1.6 |
pH 7 |
1 |
17.9 |
1.2 |
5.8 |
0.5 |
3.0 |
0.2 |
pH 7 |
10 |
5.6 |
0.4 |
2.0 |
0.4 |
1.2 |
0.4 |
. |
|
|
|
|
|
|
|
pH 9 |
0 |
99.9 |
0.8 |
99.2 |
1.1 |
97.9 |
0.3 |
pH 9 |
1 |
100.0 |
0.1 |
65.1 |
8.5 |
46.4 |
4.9 |
pH 9 |
10 |
5.2 |
0.1 |
2.2 |
0.0 |
1.6 |
0.0 |
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 (SOP AUC-RI). The centrifugation parameters are given in the methods section.
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 c.a 0.031.This is a fraction of 2.1% of the initial absorption, but actually is close to the LOD of the built-in UV/Vis detector. Considering the LOD, between 0% and 2.1% of the sample may have been dissolved.
All evidence combined, the results after centrifugation confirm that at least 97.9% of the observed dispersion stability has to be attributed to the particles, not to dissolution.
- Reason / purpose for cross-reference:
- data waiving: supporting information
Reference
- Endpoint:
- partition coefficient
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2008
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: OECD Guideline 105 and ETAD method
- Principles of method if other than guideline:
- To measure the partition coefficient of pigments utilising the standard OECD Guideline 107 is extremely difficult because of the problems associated with the inherent very low solubilities. The following procedure is used for determining the LogPow of low solubility substances and in particular that of pigments.
The partition coefficient was estimated based on the ratio of the solubilities in n-octanol and in water. The individual solubilities were determined by flask method based on OECD Guideline 105 and the ETAD method.
A defined amount of the pigment (see table 1) was transferred to a 100 ml flask with glass stopper and 60 ml of water (deionised, 18.2 MOcm). This was stirred at 70°C for 2 hours, and then 72 hours in an air conditioned laboratory (T = 23°C). The suspension was then centrifuged (10 000 rpm, 10 min) and filtered once through a standard paper filter, twice through a 0.2 μm membrane filter (Millipore) and twice through a 0.025μm membrane filter (Millipore). If particles were detected in the solution (turbidity), the final filtration step was repeated until a perfectly clear solution was acheived.
The above procedure was conducted in parallel for a total of 2 water (deionised, 18.2 MOcm) samples and of 2 n-octanol (Sigma-Aldrich, spectrophotometric grade) samples. - GLP compliance:
- no
- Type of method:
- shake-flask method to: flask method
- Partition coefficient type:
- octanol-water
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): PIGMENT RED 48:1, PIGMENT RED 48:1, lab sample (non-resin coated), TK 10318
- Analytical purity: 94.3% w/w
- Substance type: Organic
- Physical state: Solid (powder)
- Lot/batch No.: DMG6708
- Expiration date of the lot/batch: January 01st, 2017 - Analytical method:
- high-performance liquid chromatography
- other: UV/Vis
- Key result
- Type:
- log Pow
- Partition coefficient:
- > 0.11
- Temp.:
- 23 °C
- Remarks on result:
- other: The pH was not reported.
- Details on results:
- Solubility in n-octanol: 31-33 µg/L UV/Vis)
Solubility in water: < 25 µg/L (HPLC-DAD)
Weight in n-octanol/water: 54.2-56.8 mg/100mL - Conclusions:
- The partition coefficient of test substance was estimated to be log Pow= >0.11 at 23°C.
Data source
Materials and methods
Results and discussion
Applicant's summary and conclusion
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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