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EC number: 309-912-6 | CAS number: 101357-15-7
- 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:
- 2 August 2006 to 8 December 2006
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study conducted to GLP in compliance with agreed protocols, with no or minor deviations from standard test guidelines and/or minor methodological deficiencies, which do not affect the quality of the relevant results.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Deviations:
- yes
- Remarks:
- See the comments in Principle of method if other than guideline.
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.6 (Water Solubility)
- Deviations:
- yes
- Remarks:
- See the comments in Principle of method if other than guideline.
- Principles of method if other than guideline:
- Due to a blockage of the column elution apparatus resulting in a significant loss in solution volume for determination B, only 4 samples were obtained, not the minimum of 5 samples on the saturation plateau as recommended by the method guidelines. This was concluded not to impact on the validity of the test, as determination A was demonstrated to have reached saturation equilibrium over the same time period. Since determination B was the faster flowing apparatus, it would have achieved saturation equilibrium before determination A, and therefore it can be concluded that determination B was at equilibrium at the time of sampling, as supported by the common limit value obtained for all 4 determination B samples. In addition, sufficient data was generated to demonstrate that the test material solubility was not significantly flow rate dependent, the reason that two individual determinations are required for the column elution method.
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- column elution method
- Water solubility:
- < 0.1 mg/L
- Temp.:
- 20 °C
- Remarks on result:
- other: pH values not reported
- Details on results:
- Preliminary test
The preliminary estimate of water solubility was 3.28 x 10^-4 g/l. - Conclusions:
- The water solubility of the test material has been determined to be less than 0.1 mg/l of solution at 20.0 ± 0.5°C.
- Executive summary:
In a general physico-chemical properties study (0370/0351), the water solubility of the test material was determined to be less than 0.1 mg/l of solution at 20.0 ± 0.5°C, according to OECD Test Method 105.
Reference
The mean peak areas relating to the standard and sample solutions are shown in the following table:
Table 1.
Solution |
Mean Peak Area |
Standard 10.0 mg/l |
2.009 x 103 |
Standard 10.2 mg/l |
2.079 x 103 |
Standard Blank |
32.854 |
Sample Blank |
147.658 |
Determination A, Sample 2 |
186.263 |
Determination B, Sample 2 |
209.971 |
Determination A, Sample 3 |
141.815 |
Determination B, Sample 3 |
149.438 |
Determination A, Sample 4 |
158.457 |
Determination B, Sample 4 |
194.56 |
Determination A, Sample 5 |
192.857 |
Standard 10.0 mg/l |
2.195 x 103 |
Standard 10.2 mg/l |
2.197 x 103 |
Standard Blank |
none detected |
Sample Blank |
26.86 |
Determination A, Sample 6 |
25.568 |
The concentration (g/l) of test material in the sample solutions is shown in the following table:
Table 2.
Sample Number |
Sampling time (hour) |
Concentration (g/l) |
Solution pH |
|||
Determination A |
Determination B |
Determination A |
Determination B |
Determination A |
Determination B |
|
1 |
192.5 |
193 |
<1.0 x 10-4 |
<1.0 x 10-4 |
6.4 |
6.6 |
2 |
312 |
312 |
<1.0 x 10-4 |
<1.0 x 10-4 |
6.5 |
6.7 |
3 |
337.5 |
338 |
<1.0 x 10-4 |
<1.0 x 10-4 |
6.5 |
6.2 |
4 |
357.5 |
358 |
<1.0 x 10-4 |
<1.0 x 10-4 |
6.4 |
6.5 |
5 |
383 |
- |
<1.0 x 10-4 |
- |
6.2 |
- |
6 |
454.5 |
- |
<1.0 x 10-4 |
- |
6.5 |
- |
The overall results are shown in the following table:
Table 3.
Determination |
Overall Concentration (g/l) |
A |
<1.0 x 10-4 |
B |
<1.0 x 10-4 |
Overall |
<1.0 x 10-4 |
Validation
The linearity of the detector response with respect to concentration was assessed over the nominal concentration range of 0 to 250 mg/l. This was satisfactory with a correlation coefficient of 0.999 being obtained.
Recovery of analysis of the sample procedure was assessed and proved adequate for the test. Recovery data is shown in the following table:
Table 4.
Nominal concentration (mg/l) |
Recovery range (%) |
Mean recovery (%) |
0.50 |
64.1 to 64.9 |
64.5 |
0.10 |
66.7 to 68.7 |
67.6 |
Discussion
On the analysis of all sample solutions from both determination A and determination B, the instrument responses were approximately equal to that of the respective sample blank, such that a theoretical concentration range of -1.2 x 10-6 to 4.3 x 10-5 g/l was obtained, with no time or flow rate dependent trends; i.e, the test material was shown to be essentially insoluble in water. An overall limit value of less than 1.0 x 10-4 g/l has been reported for the water solubility of the test material, originating from the lowest nominal concentration at which the analytical method extraction procedure was successfully validated.
Due to a blockage of the column elution apparatus resulting in a significant loss in solution volume for determination B, only 4 samples were obtained, not the minimum of 5 samples on the saturation plateau as recommended by the method guidelines. This was concluded not to impact on the validity of the test, as determination A was demonstrated to have reached saturation equilibrium over the same time period. Since determination B was the faster flowing apparatus, it would have achieved saturation equilibrium before determination A, and therefore it can be concluded that determination B was at equilibrium at the time of sampling, as supported by the common limit value obtained for all 4 determination B samples. In addition, sufficient data was generated to demonstrate that the test material solubility was not significantly flow rate dependent, the reason that two individual determinations are required for the column elution method.
Description of key information
The water solubility of the test material has been determined to be less than 0.1 mg/L of solution at 20.0 ± 0.5 °C.
Key value for chemical safety assessment
- Water solubility:
- 0.1 mg/L
- at the temperature of:
- 20 °C
Additional information
In a general physico-chemical properties study (0370/0351), the water solubility of the test material was determined to be less than 0.1 mg/L of solution at 20.0 ± 0.5 °C, according to OECD Test Method 105. The study was awarded a reliability score of 1 in accordance with the criteria set forth by Klimisch et al. (1997).
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