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EC number: 945-942-1 | 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
Water solubility
Administrative data
Link to relevant study record(s)
- Endpoint:
- water solubility
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 10 August 2017 to 20 September 2017
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Version / remarks:
- 1995
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.6 (Water Solubility)
- Version / remarks:
- 2014
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 830.7840 (Water Solubility)
- Version / remarks:
- 1998
- Deviations:
- no
- GLP compliance:
- yes
- Type of method:
- column elution method
- Key result
- Water solubility:
- 2.45 mg/L
- Conc. based on:
- test mat.
- Temp.:
- 20 °C
- pH:
- >= 7.9 - <= 8
- Details on results:
- - Preliminary Test: The content of test material dissolved in the water sample was 2.24 mg/L.
- Main Study: The results for the samples taken at a flow rate of 12 and 24 mL/h are given in Table 1. The coefficient of variation (CV) (n = 10 at a flow rate of 24 mL/h and n=6 at a flow rate of 12 mL/h) was ≤ 30 % at both flow rates. It demonstrated that the system was equilibrated at all flow rates. The concentrations of last four measurements of the 12 mL/h test were clearly above the rest of the aliquots (approximately one order of magnitude). This effect was not observed for the m/z 118 for Sn and m/z 182 for W (see paragraph 8.1.1). Therefore, they were not considered for the determination of the Mean Concentration. The maximum difference (MD) on the mean values of the samples at both flow rates was also ≤ 30 %. Based on this, the water solubility of the test material is given as the mean value of these measurements. The turbidity of the eluates was < 0.2 NTU. According to this, no undissolved particles were detected in the eluates. Small responses in the samples from the blank column were observed. Responses were similar to the responses in the analytical blanks. - Conclusions:
- Under the conditions of this study, the water solubility of the test material at 20 °C was 2.45 mg/L. The pH of the aqueous samples was 7.9 and 8.0.
- Executive summary:
The water solubility of the test material was investigated in accordance with the standardised guidelines OECD 105, EU Method A.6. and OPPTS 830.7840, under GLP conditions.
The column elution method was applied for the determination of the water solubility ofthe test material in the main study as the content of test material dissolved in the water sample was 2.24 mg/L, in the preliminary test.
The coefficient of variation (CV) (n = 10 at a flow rate of 24 mL/h and n=6 at a flow rate of 12 mL/h) was≤ 30 % at both flow rates. It demonstrated that the system was equilibrated at all flow rates. The concentrations of last four measurements of the 12 mL/h test were clearly above the rest of the aliquots (approximately one order of magnitude). This effect was not observed for the m/z 118 for Sn and m/z 182 for W. Therefore, they were not considered for the determination of the Mean Concentration. The maximum difference (MD) on the mean values of the samples at both flow rates was also≤ 30 %. Based on this, the water solubility of the test material is given as the mean value of these measurements. The turbidity of the eluates was < 0.2 NTU. According to this, no undissolved particles were detected in the eluates. Small responses in the samples from the blank column were observed. Responses were similar to the responses in the analytical blanks.
Under the conditions of this study, the water solubility of the test material at 20 °C was 2.45 mg/L. The pH of the aqueous samples was 7.9 and 8.0.
Reference
Table 1: Main study - water solubility of the test material
Flow rate |
Sample no. |
Concentration analysed |
pH |
||||
Individual |
Mean1 |
CV |
Mean2 |
MD |
|
||
24 |
1 |
2.11 |
2.18 |
3.7 |
2.45 |
22 |
8.0 |
2 |
2.07 |
||||||
3 |
2.29 |
||||||
4 |
2.27 |
||||||
5 |
2.28 |
||||||
6 |
2.18 |
||||||
7 |
2.23 |
||||||
8 |
2.13 |
||||||
9 |
2.11 |
||||||
10 |
2.14 |
||||||
12 |
1 |
2.63 |
2.73 |
4.2 |
|
|
7.9 |
2 |
2.63 |
||||||
3 |
2.70 |
||||||
4 |
2.68 |
||||||
5 |
2.81 |
||||||
6 |
2.92 |
||||||
7 |
6.663 |
||||||
8 |
22.53 |
||||||
9 |
33.33 |
||||||
10 |
35.53 |
1 Mean of the concentrations obtained at one flow rate.
2 Mean of the concentrations obtained at both flow rates.
3 Values not used
for calculation of the mean concentration since not in the same order of
magnitude as the first six measured concentrations.
Description of key information
Under the conditions of this study, the water solubility of the test material at 20 °C was 2.45 mg/L. The pH of the aqueous samples was 7.9 and 8.0.
Key value for chemical safety assessment
- Water solubility:
- 2.45 mg/L
- at the temperature of:
- 20 °C
Additional information
The water solubility of the test material was investigated in accordance with the standardised guidelines OECD 105, EU Method A.6. and OPPTS 830.7840, under GLP conditions. The study was awarded a reliability score of 1 in accordance with the criteria set forth by Klimisch et al. (1997).
The column elution method was applied for the determination of the water solubility ofthe test material in the main study as the content of test material dissolved in the water sample was 2.24 mg/L, in the preliminary test.
The coefficient of variation (CV) (n = 10 at a flow rate of 24 mL/h and n=6 at a flow rate of 12 mL/h) was≤ 30 % at both flow rates. It demonstrated that the system was equilibrated at all flow rates. The concentrations of last four measurements of the 12 mL/h test were clearly above the rest of the aliquots (approximately one order of magnitude). This effect was not observed for the m/z 118 for Sn and m/z 182 for W. Therefore, they were not considered for the determination of the Mean Concentration. The maximum difference (MD) on the mean values of the samples at both flow rates was also≤ 30 %. Based on this, the water solubility of the test material is given as the mean value of these measurements. The turbidity of the eluates was < 0.2 NTU. According to this, no undissolved particles were detected in the eluates. Small responses in the samples from the blank column were observed. Responses were similar to the responses in the analytical blanks.
Under the conditions of this study, the water solubility of the test material at 20 °C was 2.45 mg/L. The pH of the aqueous samples was 7.9 and 8.0.
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