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EC number: 225-805-6 | CAS number: 5089-70-3
- 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:
- 2008-07-23 to 2009-05-25
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Reason / purpose for cross-reference:
- reference to other study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Version / remarks:
- 27 July 1995
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.6 (Water Solubility)
- Version / remarks:
- December 1992
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- flask method
- Key result
- Water solubility:
- ca. 113 mg/L
- Temp.:
- 20 °C
- pH:
- 4.7
- Remarks on result:
- other: after 2 hours
- Details on results:
- The test substance showed a rapid hydrolysis, therefore a simplified flash test was used.
Because of the low stability of the test item in water the expression “greater than or equal to” was used for the result of the water solubility in the test report. - Conclusions:
- A water solubility value of approximately 113 mg/L at pH 4.7 and. 20°C was measured in a reliable study conducted according to OECD Guideline 105, and in compliance with GLP. Only the preliminary test was carried out as the substance is hydrolytically unstable; the measured value can only be considered approximate for this reason.
Reference
The saturation concentration of (3-chloropropyl)triethoxysilane at room temperature was estimated by a simplified flask method. The pH of the solution was 4.7.
After mixing about 0.13 g of test item with 5 mL of water, the test item was floating as globules in the water. After centrifugation the aqueous phase was diluted with acetone. The determination of the concentration in the above mentioned solution was performed by GC with respect to a calibration curve.
Due to the low stability of (3-chloropropyl)triethoxysilane in water, the water solubility of (3-chloropropyl)triethoxysilane at room temperature could only be roughly estimated by a simplified flask method and was found to be =113 mg/L (after 2 hours). Because of the low stability of the test item in water the expression “greater than or equal to” was used for the result of the water solubility.
An example of calibration data for test item-standards is given in Table 2. The r² fit was 0.9994 (optimum 1.0000). This reflects the linearity of the GC-system within the calibration range of 4.918 µg/mL to 73.77 µg/mL of the test item.
Table 1: Results of the water solubility of (3-chloropropyl)triethoxysilane
Initial weight of test item [g] |
Water added [mL] |
Measured concentration [mg/L] |
Dilution Factor |
Solubility in water [mg/L] |
Mean [mg/L] |
0.14 |
5 |
37.599 |
3 |
112.796 |
113.08 |
0.13 |
5 |
37.790 |
3 |
113.371 |
Table 2 Calibration Data of (3-chloropropyl)triethoxysilane
Concentration [µg/mL] (X) |
Peak Area (Y) |
Deviation (%) |
4.918 |
27.59553 |
11.6 |
9.836 |
55.03376 |
1.3 |
13.7704 |
74.74595 |
-4.3 |
19.672 |
115.84454 |
1.1 |
24.59 |
144.7618 |
0.0 |
36.885 |
213.92059 |
-2.7 |
49.18 |
298.84586 |
1.1 |
73.77 |
447.12851 |
0.2 |
Description of key information
Water solubility [(3-chloropropyl)triethoxysilane]: approximately 113 mg/L at 20 and pH 4.7 (OECD 105)
Water solubility [(3-chloropropyl)silanetriol]: Above approximately 1000 mg/L condensation reactions can occur over time, limiting the concentration dissolved in water. The calculated solubility is 1.0E+06 mg/L (QSAR)
Water Solubility [ethanol]: miscible with water
Key value for chemical safety assessment
- Water solubility:
- 113 mg/L
- at the temperature of:
- 20 °C
Additional information
A measured water solubility value of approximately 113 mg/L at 20 and pH 4.7 was determined for the submission substance using a simplified flask method in accordance with OECD Test Guideline 105 and in compliance with GLP. Due to the hydrolytic instability of the substance in water, a shorter equilibration time of 2 hours and lower initial amount of the substance was used. The result is considered to be reliable to give an indication of the expected water solubility of the substance and is thus selected as key study.
In contact with water, the submission substance hydrolyses moderately rapidly to form (3-chloropropyl)silanetriol and ethanol.
The silanol hydrolysis product, (3-chloropropyl)silanetriol, may undergo condensation reactions in solution to give siloxane dimers, linear and cyclic oligomers and highly cross-linked polymeric particles (sol) that may over time form an insoluble gel and a dynamic equilibrium is established. The overall rate and extent of condensation is dependent on nominal loading, temperature, and pH of the system, as well as what else is present in solution.
The condensation reactions of silanetriols may be modelled as an equilibrium between monomer, dimer, trimer and tetramer, with the linear tetramer cyclising to the thermodynamically stable cyclic tetramer. At higher loadings, cross-linking reactions may occur. The reactions are reversible unless the cyclic tetramer concentration exceeds its solubility, in this case, the cyclic tetramer forms a separate phase, driving equilibrium towards the tetramer. At loadings below 500 mg/L of (3-chloropropyl)silanetriol, the soluble monomer is expected to predominate in solution (>99%), with small amounts of dimer and oligomers. Condensation reactions are expected to become important at loadings above about 1000 mg/L causing the formation of insoluble polymeric particles (sols) and gels over time. Further information is given in a supporting report (PFA 2016am) attached in Section 13.
The hydrolysis product, (3-chloropropyl)silanetriol, is very hydrophilic and hence the calculated solubility is 1.0E+06 mg/L using a QSAR method. This QSAR method for water solubility cannot be validated for silanetriols because the saturation concentration of silanetriols in water is limited by condensation reaction rather than lack of true solubility as discussed above. A prediction of 1E+06 mg/L is indicative but has no practical meaning. The prediction is however considered valid for use in environmental exposure modelling and toxicokinetics modelling because it is considered to adequately describe the hydrophilicity of the substance and hence the partitioning behaviour.
Ethanol is miscible with water (Riddick JA 1986).
References:
PFA (2016am). Peter Fisk Associates, Analogue Report - Silanols and aquatic systems. Reference:404.105.003
Riddick J A (1986). Riddick,J.A.; Bunger,W.B.; Sakano,T.K.; Organic Solvents: Physical Properties and Methods of Purification. Techniques of Chemistry. 4th ED. New York,NY: Wiley-Interscience. 2:PP.1325 1986.
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