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EC number: 220-941-2 | CAS number: 2943-75-1
- 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
Surface tension
Administrative data
Link to relevant study record(s)
- Endpoint:
- surface tension
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- the study does not need to be conducted because water solubility is below 1 mg/L at 20°C
- Endpoint:
- surface tension
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 2011-07-01 to 2011-07-04
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- The study was conducted in accordance with an appropriate test method but not in compliance with GLP.
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.5 (Surface Tension)
- Deviations:
- no
- GLP compliance:
- no
- Type of method:
- plate method
- Surface tension:
- 42.18 mN/m
- Temp.:
- 20 °C
- Conc.:
- 100 mg/L
- Remarks on result:
- other: Non-buffered result
- Surface tension:
- 52.78 mN/m
- Temp.:
- 20 °C
- Conc.:
- 100 mg/L
- Remarks on result:
- other: Buffered result at pH 7
- Conclusions:
- A surface tension of octylsilanetriol; a hydrolysis product of the registered substance was determined as 53mN/m using a relevant test method. The hydrolysis product (octylsilanetriol) was determined to be potentially surface active using a relevant test method. Significant condensation of the test substance was observed in water and there was no indication of the test substance or organic groups as product of hydrolysis in aqueous solution, thus the result is difficult to interpret. However, the surface activity observed was assumed to be as a result of a very small amount of the hydrolysis product which remained on the surface of the aqueous solution.
Referenceopen allclose all
Test Conditions (de-ionized water):
When preparing the test solution (100 mg/l), the substance was observed to react rapidly with water with the generation of HCl and a flocculent white precipitate. After stirring for 4 hours and heating to 60°C the precipitate did not disappear. Before measurement at 20°C the precipitate was removed by filtration.
The concentration of the test substance was determined using the method for total carbon in the solution according to DIN EN 1484 H3. No carbon could be detected (detection limit < 3 mg/l). Additionally a 1H-NMR spectrum was measured. There was no signal of CH2Si or CH2 groups of an octyl chain. Therefore there is no indication of the test substance or organic groups as products of hydrolysis in the aqueous solution (detection limit < 10 mg/l).
Due to the very low concentration of dissolved material, it is difficult to interpret the result of the study.
The test substance was expected to hydrolyse rapidly generating HCl which will lower the pH of the solution. The condensation reaction of the silanol hydrolysis product are expected to be promoted at lower pH. Therefore the study was repeated in a pH 7 buffer solution as test medium.
Table 1: Surface tension result for non-neutralised (non-buffered solution)
No |
Time after transferring to the measurement vessel [min] |
Measured surface tension [mN/m] |
Corrected surface tension [mN/m] |
1 |
30 |
42.20 |
- |
2 |
35 |
42.18 |
- |
3 |
40 |
42.15 |
- |
4 |
45 |
42.18 |
- |
5 |
50 |
42.18 |
- |
Total mean value |
42.18 |
- |
|
Mean value (state of equilibrium) |
42.18 |
- |
Test Conditions (pH 7 buffer solution):
When preparing the test solution (100 mg/l) with the buffer solution at pH 7, the substance was observed to react at rapidly with water with flocculent white precipitate being generated. After 3 days the precipitate did not disappear. Before measurement at 20°C the precipitate was removed by filtration.
A 1H-NMR spectrum of the test solution was measured. There was no signal of CH2Si or CH2 groups of an octyl chain. Therefore there is no indication of the test substance or organic groups as products of hydrolysis in the aqueous solution (detection limit < 10 mg/l).
It was assumed that a very small amount of the hydrolysis product of the test substance remained on the surface of the aqueous solution. This was considered a possible reason for the effect of surface tension.
Table 2: Surface tension result for neutralised (buffered solution)
No |
Time after transferring to the measurement vessel [min] |
Measured surface tension [mN/m] |
Corrected surface tension [mN/m] |
1 |
30 |
52.82 |
- |
2 |
35 |
52.78 |
- |
3 |
40 |
52.80 |
- |
4 |
45 |
52.76 |
- |
5 |
50 |
52.76 |
- |
6 |
55 |
52.78 |
- |
7 |
60 |
52.78 |
- |
Total mean value |
52.78 |
- |
|
Mean value (state of equilibrium) |
52.78 |
- |
Description of key information
Surface tension [triethoxy(octyl)silane]: not relevant due to low water solubility <1 mg/L
Surface tension
[octylsilanetriol]: 53 mN/m (EU Method A.5)
Key value for chemical safety assessment
Additional information
The surface tension study for triethoxy(octyl)silane (CAS 2943 -75-1) was waived based on low water solubility (i.e. water solubility is <1 mg/L) of the registered substance, but the surface tension of the hydrolysis product was read-across from related substance; octyltrichlorosilane (CAS 5283-66-9).
In contact with water, triethoxy(octyl)silane will hydrolyse moderately rapidly to form octylsilanetriol and ethanol. Similarly, octyltrichlorosilane will hydrolysed very rapidly in contact with water to form octylsilanetriol and hydrochloric acid. Both substances (triethoxy(octyl)silane and octyltrichlorosilane) have the same silanol hydrolysis product; octylsilanetriol. Therefore, since both substances share the same silanol hydrolysis product, it is considered valid to read-across between the two substances.
The hydrolysis product, octylsilanetriol was determined to be potentially surface active (surface tension of 53 mN/m) using a relevant test method. Significant condensation of the test substance was observed in water and there was no indication of the test substance or organic group as product of hydrolysis in aqueous solution, thus the result is difficult to interpret. However, the surface activity observed was assumed to be as a result of a very small amount of the hydrolysis product which remained on the surface of the aqueous solution.
The surface activity of the hydrolysis product is observed to be weak and non-ionic, although there is the potential of formation of emulsions and micelles. The critical micelle concentration (CMC) of the substance is assumed to be very high. The polymerisation of the substance is a more pronounced effect than the formation of micelles at high concentration.
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