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EC number: 217-164-6 | CAS number: 1760-24-3
- 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
Hydrolysis
Administrative data
Link to relevant study record(s)
- Endpoint:
- hydrolysis
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 111 (Hydrolysis as a Function of pH)
- GLP compliance:
- no
- Specific details on test material used for the study:
- 5E-02 M stock solutions of test material in acetonitrile were prepared in a nitrogen-purged glove bag. Sample vials were stored over anhydrous calcium sulphate in secondary airtight containers
- Analytical monitoring:
- yes
- Details on sampling:
- direct sample infusion
- Buffers:
- Ammonium acetate/acetic acid and imidazole/imidazole hydrochloric acid buffers of varying concentrations between 5-50 mM and 5-25 mM, respectively. All buffer solutions were purged with argon gas for at least 15 mins to exclude oxygen and carbon dioxide.
- Details on test conditions:
- pH range 3.8-7.1
temperature range 10.3-35.1 °C, thermostatted to ± 1 °C using a circulating water bath - pH:
- 4
- Temp.:
- 24.7 °C
- pH:
- 5
- Temp.:
- 24.7 °C
- pH:
- 7
- Number of replicates:
- multiple at pH and temperature of interest.
- Statistical methods:
- Unconstrained nonlinear regression analysis was used to obtain estimates for the rate constants by fitting the dataset to multiple equation kinetic models. Analysis using Origin® 6.0 data analysis software (Microcal Software, Inc.) employing the Levenburg-Marquardt minimization algorithm.
After supplying the data and kinetic model, each model parameter was initially estimated from linear regression of the natural log transformed (EDA-Pr)Si(OMe)3 intensities vs time. - Preliminary study:
- No data
- Transformation products:
- yes
- No.:
- #1
- No.:
- #2
- Key result
- pH:
- 4
- Temp.:
- 24.7 °C
- DT50:
- 0.1 h
- Remarks on result:
- other: calulated using the Arrhenius parameters, as a function of pH and temperature at zero buffer concentration
- Key result
- pH:
- 5
- Temp.:
- 24.7 °C
- DT50:
- 0.32 h
- Remarks on result:
- other: calulated using the Arrhenius parameters, as a function of pH and temperature at zero buffer concentration
- Key result
- pH:
- 7
- Temp.:
- 24.7 °C
- DT50:
- 0.025 h
- Remarks on result:
- other: calulated using the Arrhenius parameters, as a function of pH and temperature at zero buffer concentration
- Conclusions:
- Hydrolysis half-lives at 24.7°C of 0.1 h at pH 4, 0.32 h at pH 5 and 0.025 h at pH 7 were determined in a reliable study conducted according to an appropriate test protocol, but not in compliance with GLP.
Reference
Table 1. Results calulated using the Arrhenius parameters, as a function of pH and temperature at zero buffer concentration
pH | Temperature (°C) | Half-life (hr) |
4 | 10.0 | 0.23 |
4 | 24.7 | 0.10 |
4 | 37.0 | 0.066 |
5 | 10.0 | 1.5 |
5 | 24.7 | 0.32 |
5 | 37.0 | 0.26 |
7 | 10.0 | 0.10 |
7 | 24.7 | 0.025 |
7 | 37.0 | 0.0090 |
Table 2. Observed Rate Constants for Hydrolysis Reactions of DAPMS Used For Modelling the Effect pH and Buffer Concentration at 25 °C.
Run | pH | [buffer], mMa | k1 x 103, s-1 | k2 x 103, s-1 | k3 x 103, s-1 |
19 | 3.78 | 10.6 | 3.32(0.08)b | 7.00(0.75) | 17.2(9.2) |
7 | 4.14 | 5.3 | 1.59(0.04) | 3.33(0.41) | 10.8(4.5) |
8 | 4.02 | 53 | 3.13(0.08) | 6.31(0.90) | 12.6(3.7) |
18 | 4.69 | 26.5 | 0.974(0.026) | 2.04(0.31) | 6.23(5.16)c |
24 | 4.97 | 26.5 | 0.728(0.018) | 1.50(0.19) | 2.67(0.85) |
6 | 5.21 | 5.3 | 0.493(0.028) | 0.974(0.146) | 1.19(1.11)c |
5 | 5.11 | 26.5 | 0.524(0.017) | 0.876(0.089) | 3.92(3.73)c |
9 | 6.15 | 10 | 1.88(0.07) | 1.29(0.12) | 2.87(0.72) |
13 | 6.07 | 25 | 1.71(0.04) | 1.23(0.11) | 2.23(1.47) |
17 | 6.44 | 10 | 3.48(0.11) | 1.86(0.14) | 3.78(1.18) |
14 | 6.4 | 25 | 3.48(0.12) | 1.93(0.22) | 4.93(3.87) |
15d | 6.39 | 25 | 3.50(0.12) | 2.42(0.31) | 4.89(5.99)c |
16e | 6.42 | 25 | 4.05(0.22) | 2.96(0.60) | 7.53(11.0)c |
10 | 6.79 | 10 | 4.45(0.21) | 2.89(0.25) | 5.04(1.32) |
25 | 6.7 | 25 | 5.73(0.31) | 2.56(0.37) | 5.06(4.29)c |
29 | 7.08 | 5 | 7.98(0.19) | 5.11(0.23) | 8.17(1.95) |
30 | 7.08 | 5 | 8.35(0.19) | 5.13(0.23) | 8.10(1.93) |
a pH 3.8-5.2: HOAc/NH4OAc; pH>6: Imidazole/Imidazole-HCl.
b Uncertainties in parenthesis reflect 95% confidence interval (CI) from non-linear regression analysis.
c Wide 95% CI approaching or exceeding 100% relative to value of k3
d Initial silane concentration= 2.56x10-5 M
e Initial silane concentration= 2.04x10-4 M
Between pH 3.8 and 5.2, it was observed exclusively that k1 < k2 < k3 as expected, while above pH 6.0 the general trend k2< k1 ≈ k3
Table 3. Calculatedf Half-lives for Observed Hydrolysis Reaction of DAPMS for the Rate Limiting Step at 25 °C
Run | pH | [buffer], mM | t1/2, h |
19 | 3.78 | 10.6 | 0.752 |
8 | 4.02 | 53 | 0.797 |
7 | 4.14 | 5.3 | 1.569 |
18 | 4.69 | 26.5 | 2.562 |
24 | 4.97 | 26.5 | 3.428 |
5 | 5.11 | 26.5 | 4.762 |
6 | 5.21 | 5.3 | 5.062 |
Table 4. Calculatedf Half-lives for Observed Hydrolysis Reaction of DAPMS for the Rate Limiting Step at 25 °C
Run | pH | [buffer], mM | t1/2, h |
13 | 6.07 | 25 | 2.029 |
9 | 6.15 | 10 | 1.934 |
15 | 6.39 | 25 | 1.031 |
14 | 6.40 | 25 | 1.293 |
16 | 6.42 | 25 | 0.843 |
17 | 6.44 | 10 | 1.342 |
25 | 6.70 | 25 | 0.975 |
10 | 6.79 | 10 | 0.863 |
29 | 7.08 | 5 | 0.488 |
30 | 7.08 | 5 | 0.486 |
fcalculated by the study reviewer
Table 5. Results of Multiple Linear Regression Analysis of DAPMS Kinetic Experiments in pH Range 3.8-5.2 at 25 °C
Constant (units) | 1st hydrolysis step | 2nd hydrolysis step | 3rd hydrolysis step |
kH3O+ (M-1 s-1) | 16.8 | 36.0 | 75.0 |
kNH3 (s-1) | 1.36x10-2 | 5.24x10-3 | N/A (a) |
k0, est. (s-1) | 2.7x10-4 | 5.2x10-4 | 5.1x10-3 |
(a) Data not sufficiently precise for pH>6.4 to yield reliable estimate
Table 6. Arrhenius Parameters for the Hydronium and Hydroxide Ion Catalyzed Hydrolysis Reactions of DAPMS.
| A, s-1 | Ea, kJ/mol | r2 |
k1H3O+ | 3.30E+03 | 34.1 | 0.9986 |
k2H3O+ | - | - | 0.9536 |
k3H3O+ | - | - | 0.9502 |
k1NH | 9.19E+08 | 65.1 | 0.9998 |
k2NH | 1.57E+08 | 62.1 | 0.9978 |
k3NH | 6.11E+11 | 80.4 | 0.9998 |
Description of key information
Hydrolysis half-lives: 0.1 h at pH 4, 0.32 h at pH 5, 0.025 h at pH 7 and 24.7°C (OECD 111)
Key value for chemical safety assessment
- Half-life for hydrolysis:
- 0.025 h
- at the temperature of:
- 24.7 °C
Additional information
Measured half-life values of 0.1 h at pH 4 and 24.7°C, 0.025 h at pH 7 and 24.7°C, and 0.32 h at pH 5 and 24.7°C were determined for the substance in accordance with OECD 111. The result is considered to be reliable and has been assigned as key study. At pH >7, the half-life became too rapid (<90 s) to measure using the methodology of this study.
In other secondary sources to which reliability could not be assigned, a hydrolysis half-life of 0.016 h at pH 7 and 24.7°C was reported. Also, a hydrolysis half-life of 0.4 h at 25°C was reported, information on the pH was not stated.
In addition, hydrolysis in soil conditioned 0.01 M CaCl2 solution and in wet soil was investigated in preparation for an adsorption/desorption study (see IUCLID dossier Section 5.4.1, Landsberg 2017). The measured half-lives in soil conditioned 0.01 M CaCl2 solution were as follows: Eurosoil 2 (pH 7.9) 0.015 h, Eurosoil 3 (pH 6.0) 0.084 h, Eurosoil 4 (pH 7.5) 0.021 h, LUFA 2.4 (pH 7.8) 0.015 h, LUFA 5M (pH 7.7) 0.015 h. Concentrations in soil samples were found to decrease within 5 minutes, indicating that the substance is unstable; half-lives were not determined.
The complete hydrolysis of CAS No. 1760-24-3 involves consecutive removal of the three methoxy groups; it is therefore a three-step process. The quoted half-lives refer to degradation of parent substance. In addition, separate rate constants for the three consecutive hydrolysis reactions have been measured. For the acid catalysed rate constants, the second and third reaction steps were found to be approximately twice as fast as the previous step (k1<k2<k3). For the base catalysed rate constants, the second step was found to be approximately 1.5-fold slower than the first step which was about the same as the third step (k2<k1≈k3). Therefore, rapid formation of the final product is expected across the pH range.
It is noted that the half-life is slower at pH 5 than at pH 7 and pH 4. In general, alkoxysilane hydrolysis is slowest at around pH 7 and faster as the pH is raised or lowered. However, a possible intramolecular catalysis mechanism caused by free amine groups has been identified for this substance which speeds up the hydrolysis at pH 7 relative to that observed for similar alkoxysilanes. However, still with the similar general pH-dependent behaviour observe for alkoxysilane hydrolysis. This different mechanism is proposed as the cause of a minimum rate at pH < 7 (at pH ≥ 5.21 < 6.07).
As the hydrolysis reaction may be acid or base catalysed, the rate of reaction is expected to be slowest at pH 7 and increase as the pH is raised or lowered. For an acid-base catalysed reaction in buffered solution, the measured rate constant is a linear combination of terms describing contributions from the uncatalyzed reaction as well as catalysis by hydronium, hydroxide, and general acids or bases.
kobs= k0+ kH3O+[H3O+] + kOH-[OH-] + ka[acid] + kb[base]
Therefore, at low pH:
kobs≈kH3O+[H3O+]
At pH 4 [H3O+]=10-4 mol dm-3 and at pH 2 [H3O+]=10-2 mol dm-3; therefore, kobs at pH 2 should be approximately 100 times greater than kobs at pH 4.
The half-life of a substance at pH 2 is calculated based on:
t1/2(pH 2) = t1/2(pH 4) / 100
The calculated half-life of N-(3-(trimethoxysilyl)propyl)ethylenediamine at pH 2 is therefore 0.001 hours (3.6 seconds). However, it is not appropriate or necessary to attempt to predict accurately when the half-life is less than 5-10. As a worst-case it can therefore be considered that the half-life for the substance at pH 2 and 25°C is approximately 5 seconds.
Reaction rate increases with temperature, therefore hydrolysis will be faster at physiologically relevant temperatures compared to standard laboratory conditions. Under ideal conditions, hydrolysis rate can be recalculated according to the equation:
DT50(XºC) = DT50(T) x e(0.08.(T-X))
Where T = temperature for which data are available and X = target temperature.
Thus, for N-(3-(trimethoxysilyl)propyl)ethylenediamine the hydrolysis half-life at 37.5ºC and pH 7 (relevant for lungs and blood) is 0.0089 hours (32 seconds). At 37.5ºC and pH 2 (relevant for conditions in the stomach following oral exposure), it is not appropriate to apply any further correction for temperature to the limit value and the hydrolysis half -life is therefore approximately 5 seconds.
The products of hydrolysis are N-(3-(trihydroxysilyl)propyl)ethylenediamine and methanol.
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