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Diss Factsheets
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EC number: 949-740-4 | 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:
- 06 June 2019 to 07 June 2019
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: OECD Guideline 115: Surface Tension of Aqueous Solutions
- Deviations:
- no
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: EU Method A.5 Surface Tension
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Date of Inspection: 21 August 2018 Date of Issue: 19 November 2018
- Type of method:
- other: critical micelle concentration (CMC)
- Remarks:
- CMC is being used as a surrogate water solubility value as the test item is surface active
- Key result
- Water solubility:
- 5.15 mg/L
- Conc. based on:
- test mat.
- Temp.:
- 20 °C
- pH:
- >= 4.7 - <= 6.1
- Conclusions:
- The critical micelle concentration of the test item was determined to be 5.15 mg/L at 20.0 ± 0.5°C.
- Executive summary:
The critical micelle concentration of the test item has been determined to be 5.15 mg/L at 20.0 ± 0.5 °C, by determining the surface tension of a range of aqueous sample solutions of differing concentration, using a procedure based on Method A.5 Surface Tension of Commission Regulation (EC) No 440/2008 of 30 May 2008 and Method 115 of the OECD Guidelines for Testing of Chemicals, 27 July 1995. As the surface tension test confirmed that the substance is a surfactant, traditional water solubility tests are not applicable. For surfactants, critical micelle concentration is considered an effective surrogate value for water solubility
Reference
Table 1
Concentration (mg/L) |
Age of Solution (min) |
Reading (mN/m) |
Temperature (°C) |
1.09 x 103 |
70 |
31.0 |
20.0 |
73 |
31.0 |
20.0 |
|
76 |
31.0 |
20.0 |
|
327 |
87 |
32.0 |
20.0 |
91 |
31.5 |
20.0 |
|
94 |
31.5 |
20.0 |
|
109 |
105 |
31.5 |
20.0 |
108 |
32.0 |
20.0 |
|
111 |
32.0 |
20.0 |
|
32.7 |
123 |
32.5 |
20.0 |
126 |
32.0 |
20.0 |
|
130 |
32.5 |
20.0 |
|
10.9 |
141 |
34.0 |
20.0 |
144 |
33.5 |
20.0 |
|
147 |
33.5 |
20.0 |
|
3.27 |
158 |
38.5 |
20.0 |
161 |
38.0 |
20.0 |
|
165 |
38.0 |
20.0 |
|
1.09 |
203 |
47.0 |
20.0 |
207 |
47.5 |
20.0 |
|
212 |
50.5 |
20.0 |
|
216 |
53.0 |
20.0 |
|
220 |
54.5 |
20.0 |
|
223 |
56.0 |
20.0 |
|
245 |
62.0 |
20.0 |
|
249 |
62.0 |
20.0 |
|
252 |
62.0 |
20.0 |
|
0.327 |
264 |
65.0 |
20.0 |
267 |
64.5 |
20.0 |
|
271 |
65.0 |
20.0 |
|
0.109 |
370 |
73.0 |
20.0 |
373 |
72.5 |
20.0 |
|
376 |
72.5 |
20.0 |
Mean surface tension values were based on the last three readings for a particular concentration which were considered to be constant.
The concentration (mg/L), log10 [concentration(mg/L)/ and mean surface tension values for the sample solutions are shown in the following table:
Table 2
Concentration (mg/L) |
Log10Concentration |
Mean Surface Tension (mN/m) |
Solution pH |
1.09 x 103 |
3.04 |
31.0 |
4.7 |
327 |
2.51 |
31.7 |
5.7 |
109 |
2.04 |
31.8 |
6.1 |
32.7 |
1.51 |
32.3 |
6.0 |
10.9 |
1.04 |
33.7 |
5.9 |
3.27 |
0.514 |
38.2 |
5.6 |
1.09 |
0.037 |
62.0 |
5.6 |
0.327 |
-0.486 |
64.8 |
5.5 |
0.109 |
-0.963 |
72.7 |
5.6 |
The plot of log10[concentration(mg/L)] versus surface tension (mN/m) is shown in Figure 1, attached as an Illustration.
Line 1 (red) was generated from linear regression of 2 sample solution concentrations for which surface tension was shown to be concentration dependent and Line 2 (green) was generated from the linear regression of 4 sample solution concentrations for which the surface tension was observed to be essentially independent of concentration.
The intersection of these two lines gave the critical micelle concentration and was calculated by solving the two equations:
Line 1 equation: y = -26.6x + 51.873
Line 2 equation: y = -0.796x + 33.511
The sample solution at 10.9 mg/L was not used in generating the two lines. At this concentration the surface tension appeared to be transitioning to Line 2 at a shallower gradient than Line 1.
The sample solution at 0.109 mg/L was not used in generating the two lines. At this concentration the surface tension was only slightly affected and was approaching that of purified water.
It was decided to not use the 1.09 mg/L sample result in creating the concentration dependent line. Using all three results from the 3.27, 1.09 and 0.327 mg/L samples didn’t product a line with a satisfactory looking fit. Additionally, the 1.09 mg/L was the only sample that didn’t give consistent values in three measurements, requiring nine; this is an effect that is frequently seen when the surface tension becomes concentration dependent. Concentrations towards the ends of the concentration dependent line typical generate more consistent measurements. For these reason, the results from the 3.27 and 0.327 mg/L samples were considered more reliable.
The CMC was determined to be 5.15 mg/L.
Description of key information
Critical micelle concentration: 5.15 mg/L at 20°C; OECD 115; Fox, J. M. (2019)
Key value for chemical safety assessment
- Water solubility:
- 5.15 mg/L
- at the temperature of:
- 20 °C
Additional information
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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