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EC number: - | 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:
- Experimental dates : August and September 2019
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Remarks:
- As the test substance is a surfactant, the CMC was determined rather than the standard solubility.
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- The method used in this study to determine the Critical Micelle Concentration, is a drop tensiometer, method describe in the book “Surfactants and interfacial Phenomena”, from Milton J. Rosen and Joy T. Kunjappu (Wiley). The surface tension is determined by the software for various concentrations. The surfactant concentration after each measurement is automatically increased and the measurement procedure is repeated. Below the critical micelle concentration, the surface tension decreases when the concentration of surfactant increases. Once the CMC has been reached or exceeded, the surface tension remains constant. The critical micelle concentration is determined by the slope change of the surface tension curve. It is determined by the software using the curve derivative.
- GLP compliance:
- no
- Type of method:
- other: CMC by drop tensiometer
- Water solubility:
- 0.036 g/L
- Conc. based on:
- other: CMC
- Temp.:
- 21 °C
- pH:
- ca. 7
- Executive summary:
As the test substance is a surfactant, the CMC was determined rather than the standard solubility.
The drop tensiometer was used to measure the surface tension for different solution concentrations.
The CMC was deduced from the graph as 0.036 g/L (36 mg/L).
- Endpoint:
- water solubility
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 06 August 2008 - 20 August 2008
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- significant methodological deficiencies
- Remarks:
- The test substance is a surfactant; the measured solubility exceeds the CMC.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.6 (Water Solubility)
- Deviations:
- no
- Principles of method if other than guideline:
- not relevant
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- flask method
- Specific details on test material used for the study:
- Expiry date April 10, 2009
- Water solubility:
- 33 g/L
- Temp.:
- 20 °C
- pH:
- >= 5.8 - <= 6.5
- Conclusions:
- Very soluble.
- Executive summary:
The purpose of this study was to evaluate the solubility of test item in water according to OECD 105 and EU A6 guidelines.
The water solubility of the substance at 20ºC was determined to be 33.3 g/L (standard deviation ±1.66g/L) using the flask shaking method.
- Endpoint:
- water solubility
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 29-JUL-09 to 09-APR-10
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- Study conducted 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. The study report was conclusive, done to a valid guideline and the study was conducted under GLP conditions.
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.6 (Water Solubility)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Deviations:
- no
- Principles of method if other than guideline:
- not relevant
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- flask method
- Remarks on result:
- not determinable
- Details on results:
- Please see section Remarks on results including tables and figures.
- Conclusions:
- The tests led to inconsistent values. During preparation of test item solutions the formation of an emulsion were observed. This turbidity could be caused by formation of micelles of the test item
in aqueous solutions, hence a method based on the critical micelle concentration (CMC) method is advised, but beyond the scope of this study. - Executive summary:
The purpose of this study was to evaluate the solubility of test item in aqueous solutions at pH 5.0, 7.0 and 9.0, which is specified by the saturation mass concentration of the test item in aqueous solutions at a given temperature.
The determination of the water solubility of test item was performed according to the EEC Directive 92/69, A.6 “Water Solubility” (1992) and the OECD guideline No. 105,“Water Solubility” (1995) using the flask shaking method.
The tests led to inconsistent values. During preparation of test item solutions the formation of an emulsion were observed. This turbidity could be caused by formation of micelles of the test item in aqueous solutions, hence a method based on the critical micelle concentration (CMC) method is advised, but beyond the scope of this study.
- Endpoint:
- water solubility
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- Experimental dates : August and September 2019
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Remarks:
- As the test substance is a surfactant, the CMC was determined rather than the standard solubility.
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- The method used in this study to determine the Critical Micelle Concentration, is a drop tensiometer, method describe in the book “Surfactants and interfacial Phenomena”, from Milton J. Rosen and Joy T. Kunjappu (Wiley). The surface tension is determined by the software for various concentrations. The surfactant concentration after each measurement is automatically increased and the measurement procedure is repeated. Below the critical micelle concentration, the surface tension decreases when the concentration of surfactant increases. Once the CMC has been reached or exceeded, the surface tension remains constant. The critical micelle concentration is determined by the slope change of the surface tension curve. It is determined by the software using the curve derivative.
- GLP compliance:
- no
- Type of method:
- other: CMC by drop tensiometer
- Water solubility:
- 0.196 g/L
- Conc. based on:
- other: CMC
- Temp.:
- 21 °C
- Executive summary:
As the test substance is a surfactant, the CMC was determined rather than the standard solubility.
The drop tensiometer was used to measure the surface tension for different solution concentrations.
The CMC was deduced from the graph as 0.196 g/L (196 mg/L).
Referenceopen allclose all
Surface tension of water before measurement = 71.7 mN/m
Critical Micelle Concentration = 0.036 g/L
Surface tension at CMC = 30.4 mN/m
Increasement of surface tension after 1g/ L corresponds to non solubility observed during preparation of solutions of concentration over 1g/ L. This behavior doesn’t impact the determination of the CMC of the sample.
sample No. | Shaking time at 30ºC | Concentration analyzed (mg/L) | Concentration calculated (g/L) | Water solubility calculated (rounded) (g/L) |
1 | 72 | 816,92 | 32,68 | 33,28 SD=1,66 |
2 | 795,408 | 31,82 | ||
3 | 48 | 833,457 | 33,34 | |
4 | 823,046 | 32,92 | ||
5 | 24 | 810,802 | 32,43 | |
6 | 913,022 | 36,52 |
The saturation mass concentration is calculated from the bold values
The saturation concentration of the substance at 30 °C was estimated by a simplified flask method in the preliminary test to be higher than 10-2g/L. Therefore, the flask shaking test was performed.
After a shaking time of 24 hours, 48 hours and 72 hours, respectively, at 30 °C, the samples were equilibrated for another 24 hours at 20 °C. Afterwards, the samples were centrifuged, diluted and analyzed by LC-MS/MS.
The tests led to inconsistent values. During preparation of test item solutions the formation of emulsions was observed. The test item solutions were turbid or the solutions were separated into two phases.
Summaries of obtained results for the different pH values are given in Table 2, Table 4 and Table 6 (see below).
A typical chromatogram of a standard solution is given in Figure 1(see attachment).A typical chromatogram of a sample solution after 72 hours of incubation at pH 7.0 is shown in Figure 2(see attachment). A LC chromatogram of a blank solution is shown in Figure 3(see attachment). The calibration curve and data are shown in Figure 4 and in Table 7(see attachment). The r² fit was 0.9941 (optimum 1.0000). This reflects the linearity of the LC-MS/MS -system within the calibration range of 6.78 ng/mL to 203.4 ng/mL of the test item.
Table 1 Data of the Performance of the Solubility Test at pH 5.0
Sample Solution No. |
P1-1 |
P2-1 |
P1-2 |
P2-2 |
P1-3 |
P2-3 |
Weighed sample of the test item [mg] |
4.445 |
4.395 |
4.301 |
4.192 |
4.819 |
4.910 |
Added volume of buffer solution pH 5.0 |
10 |
10 |
10 |
10 |
10 |
10 |
Agitation time at 30 °C [hours] |
72 |
72 |
48 |
48 |
24 |
24 |
pH value of test item solution at the end of the test |
4.73 |
5.02 |
5.03 |
5.08 |
5.04 |
5.01 |
Dilution factor before quantification |
1000 |
1000 |
1000 |
1000 |
1000 |
1000 |
Centrifugation [g] |
32049 |
32049 |
32049 |
32049 |
32049 |
32049 |
Table 2 Results of the Water Solubility of the substance at pH 5.0
Sample No. |
Shakingtime at30 °C |
Concentration analyzed |
Concentration calculated |
Water solubility calculated (rounded) |
|
|
[µg/L] |
[mg/L] |
[mg/L] |
P1-1 |
72 |
101.729 |
101.73 |
|
P2-1 |
110.236 |
110.24 |
|
|
P1-2 |
48 |
74.982 |
74.98 |
108.4 |
P2-2 |
132.886 |
132.89 |
SD =21.76 |
|
P1-3 |
24 |
99.514 |
99.51 |
|
P2-3 |
131.272 |
131.27 |
|
SD = standard deviation
Table 3 Data of the Performance of the Solubility Test at pH 7.0
Sample Solution No. |
P3-1 |
P4-1 |
P3-2 |
P4-2 |
P4-3 |
P4-3 |
Weighed sample of the test item [mg] |
7.035 |
6.322 |
5.762 |
8.270 |
6.415 |
7.378 |
Added volume of buffer solution pH 7.0 |
10 |
10 |
10 |
10 |
10 |
10 |
Agitation time at 30 °C [hours] |
72 |
72 |
48 |
48 |
24 |
24 |
pH value of test item solution at the end of the test |
6.65 |
7.03 |
7.02 |
7.03 |
6.99 |
7.03 |
Dilution factor before quantification |
1000 |
1000 |
1000 |
1000 |
1000 |
1000 |
Centrifugation [g] |
32049 |
32049 |
32049 |
32049 |
32049 |
32049 |
Table 4 Results of the Water Solubility of the substance at pH 7.0
Sample No. |
Shakingtime at30 °C |
Concentration analyzed |
Concentration calculated |
Water solubility calculated (rounded) |
|
|
[µg/L] |
[mg/L] |
[mg/L] |
P3-1 |
72 |
320.882 |
320.88 |
|
P4-1 |
246.639 |
246.64 |
|
|
P3-2 |
48 |
233.734 |
233.73 |
320.2 |
P4-2 |
518.695 |
518.69 |
SD =104.80 |
|
P3-3 |
24 |
331.155 |
331.16 |
|
P4-3 |
270.150 |
270.15 |
|
SD = standard deviation
Table 5 Data of the Performance of the Solubility Test at pH 9.0
Sample Solution No. |
P5-1 |
P6-1 |
P5-2 |
P6-2 |
P5-3 |
P6-3 |
Weighed sample of the test item [mg] |
34.73 |
33.36 |
33.52 |
31.77 |
32.13 |
33.82 |
Added volume of buffer solution pH 9.0 |
10 |
10 |
10 |
10 |
10 |
10 |
Agitation time at 30 °C [hours] |
72 |
72 |
48 |
48 |
24 |
24 |
pH value of test item solution at the end of the test |
8.98 |
8.78 |
8.92 |
8.97 |
8.87 |
9.03 |
Dilution factor before quantification |
1000 |
1000 |
1000 |
1000 |
1000 |
1000 |
Centrifugation [g] |
32049 |
32049 |
32049 |
32049 |
32049 |
32049 |
Table 6 Results of the Water Solubility of the substance at pH 9.0
Sample No. |
Shakingtime at30 °C |
Concentration analyzed |
Concentration calculated |
Water solubility calculated (rounded) |
|
|
[µg/L] |
[mg/L] |
[mg/L] |
P5-1 |
72 |
8.513 |
8.51 |
|
P6-1 |
706.067 |
706.07 |
|
|
P5-2 |
48 |
< 6.78 |
6.78 |
< 123.6 |
P6-2 |
< 6.78 |
6.78 |
SD =285.34 |
|
P5-3 |
24 |
< 6.78 |
6.78 |
|
P6-3 |
< 6.78 |
6.78 |
|
SD = standard deviation
Surface tension of water before measurement = 71.3 mN/m
Critical Micelle Concentration = 0.196 g/L
Surface tension at CMC = 41.5 mN/m
The small "depression" observed around the CMC (0,3 g/ L) can be associated to the presence of tensioactive impurities.
Description of key information
High apparent solubility, with formation of emulsions.
Critical micelle concentration (CMC) = 36 mg/L (at 21°C)
Key value for chemical safety assessment
- Water solubility:
- 36 mg/L
- at the temperature of:
- 21 °C
Additional information
An experimental study (Harlan 2008) was performed according to OECD 105, flask method and under GLP conditions. Validity criteria were fulfilled, and the substance was found to be very soluble with 33.3 g/L.
However, in second study (Harlan 2010) using also the flask method, the tests led to inconsistent values. During preparation of test item solutions the formation of emulsions was observed. This turbidity could be caused by formation of micelles of the test item in aqueous solutions.
This is consistent with the low surface tension, presented under IU section 4.10.
Therefore the 2008 study was considered as not reliable.
The determination of the critical micelle concentration (CMC) was therefore considered as more relevant. In the Processium 2019 study, the result was found very low (36 mg/L). This is considered as the key value for purpose of CSA.
As a conclusion, the 2008 result suggests that stable emulsions can be formed.
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