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EC number: 236-818-1 | CAS number: 13497-18-2
- 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:
- supporting study
- Study period:
- 02 Nov 2016 - 13 Jun 2017
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- test procedure in accordance with generally accepted scientific standards and described in sufficient detail
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- - The hydrolysis test was conducted as a preliminary test within the purposes of an adsorption study according to OECD 106 (see cross reference). Soil samples from 5 different soil types (neutral pH) were weighed into test vessels with 0.01 M CaCl2-solution. After agitation overnight the aqueous phase was filtrated and fortified with the test item. Samples were shaken and at defined sampling points, samples were analyzed to determine hydrolysis of the test item.
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Staatliches Gewerbeaufsichtsamt Hildesheim, Germany
- Radiolabelling:
- no
- Analytical monitoring:
- yes
- Remarks:
- LC-MS/MS
- Details on sampling:
- - Determination timepoints of hydrolysis in aqueous phase: 0, 0.25, 0.5, 1, 2, 4, 6, 24 h (except of LUFA soil 2.4 the 24 h measurement did not take place)
- Sampling method: soil samples from 5 different soil types were weighed into the test vessels and an appropriate volume of 0.01 M CaCl2-solution was added. After agitation overnight (12 h minimum) the aqueous phase was filtrated and fortified with the test item. Samples were shaken on an overhead shaker. At defined sampling points, samples were stabilized with acetonitrile (factor 1.1). Samples were analyzed to determine hydrolysis of the test item.
- Sample storage conditions before analysis: no storage - Buffers:
- - Type and final molarity of buffer: 0.01 M CaCl2-solution
- Estimation method (if used):
- The response of the test item was determined as a function of time. The ln responses were plotted against time and the slope of the resulting regression graph gives the rate constant k [1/unit of time]:
K = - slope
The half-life (T½) [unit of time] of the reaction is given by:
T1/2= (0.693/kobs) - Details on test conditions:
- TEST SYSTEM
- Type of test flasks: 20 mL headspace vials
- Sterilisation method: none
- Lighting: not specified
- Details on test procedure for unstable compounds: see details on sampling
- If no traps were used, is the test system closed/open: closed
- Is there any indication of the test material adsorbing to the walls of the test apparatus: no
- other: soil samples from 5 different soil types were weighed into the test vessels and an appropriate volume of 0.01 M CaCl2-solution was added
OTHER TEST CONDITIONS
- Adjustment of pH: no - Duration:
- 24 h
- Temp.:
- 20 °C
- Initial conc. measured:
- 1 mg/L
- Remarks:
- Hydrolysis was measured in 5 different soils with pH between 5.5 and 7.2
- Number of replicates:
- two per soil
- Transformation products:
- not measured
- pH:
- 7.1
- Temp.:
- 20 °C
- Hydrolysis rate constant:
- 0 s-1
- DT50:
- 1.8 h
- Remarks on result:
- other: Eurosoil 2
- pH:
- 5.5
- Temp.:
- 20 °C
- Hydrolysis rate constant:
- 0 s-1
- DT50:
- 5.6 h
- Remarks on result:
- other: Eurosoil 3
- pH:
- 6.7
- Temp.:
- 20 °C
- Hydrolysis rate constant:
- 0 s-1
- DT50:
- 1.9 h
- Remarks on result:
- other: Eurosoil 4
- pH:
- 7.1
- Temp.:
- 20 °C
- Hydrolysis rate constant:
- 0 s-1
- DT50:
- 1 h
- Remarks on result:
- other: LUFA 2.4
- pH:
- 7.2
- Temp.:
- 20 °C
- Hydrolysis rate constant:
- 0 s-1
- DT50:
- 1.9 h
- Remarks on result:
- other: LUFA 5M
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The test item is prone to fast hydrolysis therefore a Tier 1 test (preliminary study) in order to determine the hydrolysis half-lives of the substance in soil eluates was performed within the purposes of an adsorption study according to OECD guidance 106. The hydrolysis rate and a hydrolytic half-life were determined in soil-conditioned 0.01 M CaCl2 solution for each soil and spiked with the test item. Half-lives between 1 - 5.6 h were determined for the substance depending on the soil.
- Endpoint:
- hydrolysis
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 08 Aug - 05 Sep 2013
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- test procedure in accordance with generally accepted scientific standards and described in sufficient detail
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- - The test item is prone to hydrolysis. Therefore in the frame of the biodegradation test (see cross reference) according to OECD guideline 301, a preliminary test on the hydrolysis of the substance was performed. The hydrolysis test was performed in purified water for 2 h duration. The test item hydrolyses to ethanol and a silanol hydrolysis product. Ethanol was analytically monitored at several timepoints in order to gather information on the hydrolysis rate of the test item.
- GLP compliance:
- yes
- Radiolabelling:
- no
- Analytical monitoring:
- yes
- Details on sampling:
- - Sampling intervals for the parent/transformation products: right after preparation of the test solution and after 0.5, 1 and 2 h
- Sampling method: 1 mL of test solution was taken out of the vessel at sampling points
- Sample storage conditions before analysis: no storage - Details on test conditions:
- TEST MEDIUM
- Test solution: water + test item (31 µL (corresp. to 30 mg) test item in 300 mL purified water)
- Kind and purity of water: purified water
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Temperature: RT
- Other: each test solution was stirred by a stirrer - Duration:
- 2 h
- pH:
- 9.5
- Initial conc. measured:
- 100 mg/L
- Remarks:
- Temperature: room temperature mentioned in report
- Number of replicates:
- 2
- Positive controls:
- no
- Negative controls:
- no
- Transformation products:
- yes
- No.:
- #1
- Details on hydrolysis and appearance of transformation product(s):
- - Formation of transformation product during test: the produced amount of ethanol reached to the theoretical amount after 0.5 h from preparation of the test solutions, showing that the test item was completely hydrolyzed after 0.5 h.
- Remarks on result:
- other: see field "details on results"
- Details on results:
- Half of the test material was hydrolyzed right after the preparation of the solution at timepoint 0. 97-99% of the test material was hydrolyzed after 0.5 h.
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The test item is prone to hydrolysis. Therefore in the frame of the biodegradation test according to OECD guideline 301, a preliminary test on the hydrolysis of the substance was performed. Since the test item hydrolyses to ethanol and a silanol hydrolysis product, ethanol was analytically monitored at several timepoints in order to gather information on the hydrolysis rate of the test item. Half of the test material was hydrolzed right after the preparation of the solution at timepoint 0. 97-99% of the test material was hydrolyzed after 0.5 h.
- Endpoint:
- hydrolysis
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 11 Aug - 02 Sep 2021
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 111 (Hydrolysis as a Function of pH)
- Version / remarks:
- 2004
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.7 (Degradation: Abiotic Degradation: Hydrolysis as a Function of pH)
- Version / remarks:
- 2008
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Staatliches Gewerbeaufsichtsamt Hildesheim, Hildesheim, Germany (2020-08-27)
- Radiolabelling:
- no
- Analytical monitoring:
- yes
- Details on sampling:
- - Sampling intervals for the parent/transformation products: Samples were taken at test start (0 h) and at a minimum of 12 spaced points, normally between 10 and 90% of hydrolysis, if possible. If, after an incubation time of 10 min, hydrolysis of at least 75% was determined, the number of spaced points was reduced. For the transformation product ethanol the remaining 10 mL of the sample were prepared.
- Temperature check: every 10 minutes automatically (pH 4 and pH 9), once per hour (pH 7), and at least once per day manually
- Sample storage conditions before analysis: The time between test item application and transfer to thermostat / analysis did not exceed 10 min if possible, but at least not more than 2.5% of the total study time. - Buffers:
- - pH: 4, 7, 9
- Type and composition of buffer pH 4: 0.36 g of sodium hydroxide and 11.511 g of mono potassium citrate were dissolved in 1000 mL purified water.
- Type and composition of buffer pH 7: 7.708 g of ammonium acetate were dissolved in 1000 mL purified water.
- Type and composition of buffer pH 9: 0.852 g sodium hydroxide, 3.7276 g potassium chloride and 3.0916 g boric acid were dissolved in 1000 mL purified water.
- other: Buffers were purged with nitrogen for 5 min and then the pH was checked to a precision of at least 0.1 at the test temperatures. Buffers were sterilized by filtration through 0.2 µm. - Details on test conditions:
- TEST SYSTEM
- Type, material and volume of test flasks, other equipment used: 15 mL Centrifuge tubes (pH 4 and pH 9), 15 mL sterile centrifuge tubes (pH 7)
- Test concentration: 30 mg/L in buffer solution at pH 4, 7, 9 with 10% acetonitrile dried as co-solvent
- Sterilisation method: buffers were sterilized by filtration (see section "Buffers"), due to the fast hydrolysis at pH 4 and 9, no sterility is deemed necessary at these test conditions. At pH 7, the study was performed under sterile test conditions.
- Temperature: 10, 20, 30 ± 0.5 °C.
- Measures taken to avoid photolytic effects: Photolytic effects were avoided by using an opaque water bath. The study was conducted protected from direct sunlight.
- If no traps were used, is the test system closed/open: closed
TEST MEDIUM
- Volume used/treatment: 10.33 mL
- Kind and purity of water: Purified water, MERCK, In-house device Milli-Q Advantage A10, ≥ 18.2 MΩ/cm ≤ 50 ppb TOC
- Preparation of test medium: 9.297 mL of the respective buffer solution pH 4, 7 or 9 were given into the test vessels. 1.033 mL of the test item solution (300 mg/L in acetonitrile, dried) was spiked into the vessels and the vessels were closed. For control samples, 9 mL of the respective buffer solution was spiked with 1 mL acetonitrile, dried without test item. Prior to application the buffers pH 4 and 9 were tempered to test temperature.
- Identity and concentration of co-solvent: Acetonitrile, 10% (v/v) - Remarks:
- The test was conducted until 90% decomposition was reached.
- Number of replicates:
- One replicate per sampling date, single injected
- Negative controls:
- yes
- Remarks:
- buffer solution at the respective pH value with 10% acetonitrile, dried as co-solvent
- Preliminary study:
- Due to the fast hydrolysis of the test item, no preliminary test was deemed to be necessary.
- Transformation products:
- yes
- Remarks:
- Ethanol was identified as major transformation product and quantified. Additional transformation products were postulated on basis of the expected de-ethoxylation processes and monitored on their masses traces of m/z 258, 286, 314, 342, 370, and 398 Da.
- No.:
- #1
- Details on hydrolysis and appearance of transformation product(s):
- - Formation and decline of each transformation product during test: Ethanol was identified as major transformation product and quantified. In sum nine possible transformation products, originated from de-ethoxylation, could be postulated. These nine possible structures were analysed based on their six possible molecular masses and additionally by their retention time differences based on the molecule symmetry. The monitored masses traces are m/z 258 Da, 286 Da, 314 Da, 342 Da, 370 Da and 398 Da. For all test conditions the ln concentration vs. time plots have regression graphs with slopes significantly non zero.
- Pathways for transformation: A confirmation of pseudo first order reaction kinetics with coefficients of determination > 0.8 was achieved for all test conditions.
- Other: First order reaction kinetics were applied for data computation. - pH:
- 4
- Temp.:
- 10 °C
- Hydrolysis rate constant:
- 0.001 s-1
- DT50:
- 14.3 min
- Type:
- (pseudo-)first order (= half-life)
- pH:
- 4
- Temp.:
- 20 °C
- Hydrolysis rate constant:
- 0.002 s-1
- DT50:
- 7.7 min
- Type:
- (pseudo-)first order (= half-life)
- pH:
- 4
- Temp.:
- 30 °C
- Hydrolysis rate constant:
- 0.002 s-1
- DT50:
- 4.73 min
- Type:
- (pseudo-)first order (= half-life)
- pH:
- 7
- Temp.:
- 10 °C
- Hydrolysis rate constant:
- 0 s-1
- DT50:
- 25.8 h
- Type:
- (pseudo-)first order (= half-life)
- pH:
- 7
- Temp.:
- 20 °C
- Hydrolysis rate constant:
- 0 s-1
- DT50:
- 11.9 h
- Type:
- (pseudo-)first order (= half-life)
- pH:
- 7
- Temp.:
- 30 °C
- Hydrolysis rate constant:
- 0 s-1
- DT50:
- 3.69 h
- Type:
- (pseudo-)first order (= half-life)
- pH:
- 9
- Temp.:
- 10 °C
- Hydrolysis rate constant:
- 0.001 s-1
- DT50:
- 12.5 min
- Type:
- (pseudo-)first order (= half-life)
- pH:
- 9
- Temp.:
- 20 °C
- Hydrolysis rate constant:
- 0.002 s-1
- DT50:
- 5.62 min
- Type:
- (pseudo-)first order (= half-life)
- pH:
- 9
- Temp.:
- 30 °C
- Hydrolysis rate constant:
- 0.004 s-1
- DT50:
- 2.7 min
- Type:
- (pseudo-)first order (= half-life)
- Details on results:
- TEST CONDITIONS
- pH, temperature, and other experimental conditions maintained throughout the study: Yes, for details see section "any other information on results incl. tables".
MAJOR TRANSFORMATION PRODUCTS
At pH4:
- Range of maximum concentrations in % of the applied amount and day(s) of incubation when observed: for details see section "any other information on results incl. tables"
- Range of maximum concentrations in % of the applied amount at end of study period: for details see section "any other information on results incl. tables"
At pH7:
- Range of maximum concentrations in % of the applied amount and day(s) of incubation when observed: for details see section "any other information on results incl. tables"
- Range of maximum concentrations in % of the applied amount at end of study period:for details see section "any other information on results incl. tables"
At pH9:
- Range of maximum concentrations in % of the applied amount and day(s) of incubation when observed: for details see section "any other information on results incl. tables"
- Range of maximum concentrations in % of the applied amount at end of study period: for details see section "any other information on results incl. tables" - Validity criteria fulfilled:
- yes
- Conclusions:
- The study according to the OECD guideline 111 showed that the test item hydrolyses fast at pH 4 and 9 (t1/2 ≤ 1 h) and all tested temperatures. At pH 7 the test item showed a hydrolysis rate of t1/2 = 11.9 h at 20 °C.
Ethanol was identified as major transformation product and quantified. Additional transformation products were postulated on basis of the expected de-ethoxylation processes with the masses (m/z) 258, 286, 314, 342, 370, and 398 Da and qualitatively determined.
Referenceopen allclose all
Table 1: Characteristics of soils used.
|
Soils |
||||
|
Eurosoil 2 |
Eurosoil 3 |
Eurosoil 4 |
LUFA soil 2.4 |
LUFA soil 5M |
FAO soil unit (Eurosoils) Soil Type (LUFA Soils) |
Rendzina |
Dystric Cambisol |
Orthic Luvizol |
|
|
pH (0.01 M CaCl2) |
7.1 |
5.5 |
6.7 |
7.1 |
7.2 |
Organic Carbon [%] |
3.72 |
3.01 |
1.31 |
1.74 |
0.92 |
Clay (<0.002 mm) [%] |
22.6 |
17.0 |
20.3 |
25.2 |
10.2 |
Silt (0.002-0.063 mm) [%] |
64.1 |
36.8 |
75.7 |
42.3 |
31.1 |
Sand (0.063-2 mm) [%] |
13.4 |
46.4 |
4.1 |
32.6 |
58.7 |
Cation Exchange Capacity [mval/100g] |
28.9 |
16.6 |
17.3 |
22 |
10 |
Table 2: Analytical determination of Hydrolysis in Aqueous Phase (initial nominal concentration of parent substance 1 mg/L)
Time [h] | Eurosoil 2 | Eurosoil 3 | Eurosoil 4 | LUFA 2.4 | LUFA 5M | |||||
Mean c [mg/L] | % | Mean c [mg/L] | % | Mean c [mg/L] | % | Mean c [mg/L] | % | Mean c [mg/L] | % | |
0 | 0.99 | - | 0.99 | - | 0.983 | - | 0.99 | - | 0.99 | - |
0.25 | 0.893 | 90 | 0.944 | 95 | 0.891 | 91 | 0.887 | 90 | 0.873 | 88 |
0.5 | 0.797 | 81 | 0.901 | 91 | 0.838 | 85 | 0.722 | 73 | 0.78 | 79 |
1 | 0.695 | 70 | 0.856 | 86 | 0.746 | 76 | 0.573 | 58 | 0.666 | 67 |
2 | 0.508 | 51 | 0.76 | 77 | 0.562 | 57 | 0.318 | 32 | 0.501 | 51 |
4 | 0.31 | 31 | 0.675 | 68 | 0.384 | 39 | 0.0904 | 9 | 0.288 | 29 |
6 | 0.153 | 15 | 0.535 | 54 | 0.208 | 21 | 0.0144 | 1 | 0.135 | 14 |
24 | 0.000111 | 0.011 | 0.0501 | 5 | 0.000147 | 0.015 | - | - | 0.000125 | 0.013 |
Mean c = mean concentration of two test item replicates, internal standard taken into account
Table 5: Produced amount of ethanol over 2 h.
Sampling point |
Production of ethanol (GC) |
|||||
Right after preparation |
0.5 h |
1 h |
2 h |
|||
Water + test item |
1 |
mg |
10 |
19.3 |
19.2 |
19.7 |
% |
51 |
99 |
98 |
101 |
||
2 |
mg |
12 |
18.9 |
19.1 |
19.2 |
|
% |
62 |
97 |
98 |
99 |
||
Theoretical amount (mg) |
19.5 |
Table 1: pH – value of the test system.
Intended pH-value |
Measured pH‑value |
||
at 10 °C |
at 20 °C |
at 30 °C |
|
4.0 ± 0.1 |
4.027 |
4.041 |
4.019 |
7.0 ± 0.1 |
6.914 |
6.879 |
6.870 |
9.0 ± 0.1 |
9.098 |
9.039 |
9.045 |
Table 2: Temperature monitoring for the test system.
Test |
Intended Temperature |
Measured Temperature |
|
Mean ± SD |
Min. / Max. |
||
pH 4 |
10.0 ± 0.5 |
10.1 ± 0.1 |
9.90 / 10.3 |
20.0 ± 0.5 |
20.0 ± 0.02 |
19.9 / 20.0 |
|
30.0 ± 0.5 |
30.01 ± 0.005 |
30.00 / 30.02 |
|
pH 7 |
10.0 ± 0.5 |
10.1 ± 0.1 |
9.84 / 10.4 |
20.0 ± 0.5 |
20.1 ± 0.03 |
20.1 / 20.2 |
|
30.0 ± 0.5 |
30.0 ± 0.01 |
30.0 / 30.0 |
|
pH 9 |
10.0 ± 0.5 |
10.1 ± 0.06 |
9.98 / 10.2 |
20.0 ± 0.5 |
20.0 ± 0.02 |
20.0 / 20.0 |
|
30.0 ± 0.5 |
29.9 ± 0.005 |
29.91 / 29.92 |
Table 3: Mass Balance for major transformation product ethanol at pH 4 and 10 °C.
Hydrolysis Time [min] |
Ethanol
[mmol/L] |
As Test Item1
[mmol/L] |
MB
[%] |
|
0.00 |
0.0751 |
0.0811 |
125 |
|
1.00 |
0.0830 |
0.0800 |
125 |
|
2.00 |
0.0943 |
0.0770 |
124 |
|
4.00 |
0.123 |
0.0717 |
123 |
|
7.25 |
0.158 |
0.0513 |
103 |
|
10.0 |
0.179 |
0.0552 |
113 |
|
14.0 |
0.225 |
0.0477 |
114 |
|
18.0 |
0.253 |
0.0397 |
109 |
|
22.0 |
0.287 |
0.0315 |
106 |
|
26.0 |
0.299 |
0.0260 |
101 |
|
34.0 |
0.336 |
0.0171 |
97 |
|
42.0 |
0.354 |
0.0115 |
94 |
|
50.0 |
0.385 |
0.00672 |
94 |
|
1 = molecular factor taken into account
MB = Mass balance
Table 4: Mass Balance for major transformation product ethanol at pH 4 and 20 °C.
Hydrolysis Time [min] |
Ethanol
[mmol/L] |
As Test Item1
[mmol/L] |
MB
[%] |
0.00 |
0.0736 |
0.0740 |
115 |
0.50 |
0.0913 |
0.0710 |
114 |
1.00 |
0.106 |
0.0707 |
117 |
2.00 |
0.122 |
0.0629 |
110 |
3.00 |
0.146 |
0.0548 |
105 |
5.00 |
0.183 |
0.0415 |
95 |
7.00 |
0.219 |
0.0414 |
103 |
9.00 |
0.258 |
0.0344 |
102 |
11.0 |
0.279 |
0.0246 |
93 |
13.0 |
0.309 |
0.0193 |
93 |
17.0 |
0.330 |
0.0150 |
92 |
21.0 |
0.361 |
0.0105 |
92 |
25.0 |
0.375 |
0.00891 |
93 |
1= molecular factor taken into account
MB= Mass balance
Table 5: Mass Balance for major transformation product ethanol at pH 4 and 30 °C.
Hydrolysis Time [min] |
Ethanol
[mmol/L] |
As Test Item1
[mmol/L] |
MB
[%] |
0.00 |
0.0632 |
0.0672 |
113 |
0.50 |
0.0783 |
0.0654 |
114 |
1.00 |
0.0911 |
0.0619 |
112 |
1.50 |
0.123 |
0.0598 |
117 |
2.00 |
0.128 |
0.0426 |
93 |
2.50 |
0.141 |
0.0441 |
98 |
3.00 |
0.169 |
0.0474 |
110 |
3.50 |
0.179 |
0.0429 |
106 |
4.50 |
0.209 |
0.0388 |
107 |
6.00 |
0.239 |
0.0305 |
102 |
9.00 |
0.294 |
0.0174 |
97 |
12.5 |
0.332 |
0.0116 |
97 |
15.0 |
0.352 |
0.00737 |
96 |
1= molecular factor taken into account
MB= Mass balance
Table 6: Mass Balance for major transformation product ethanol at pH 7 and 10 °C.
Hydrolysis Time [min] |
Ethanol
[mmol/L] |
As Test Item1
[mmol/L] |
MB
[%] |
0 |
0.0570 |
0.0602 |
100 |
120 |
0.0845 |
0.0679 |
115 |
240 |
0.0984 |
0.0575 |
103 |
360 |
0.111 |
0.0633 |
115 |
480 |
0.171 |
0.0520 |
113 |
899 |
0.216 |
0.0500 |
120 |
1077 |
0.216 |
0.0348 |
99 |
1257 |
0.232 |
0.0383 |
108 |
1440 |
0.270 |
0.0351 |
112 |
1680 |
0.232 |
0.0328 |
100 |
1906 |
0.242 |
0.0312 |
100 |
2884 |
0.308 |
0.0220 |
103 |
3346 |
0.334 |
0.0127 |
96 |
1= molecular factor taken into account
MB= Mass balance
Table 7: Mass Balance for major transformation product ethanol at pH 7 and 20 °C.
Hydrolysis Time [min] |
Ethanol
[mmol/L] |
As Test Item1
[mmol/L] |
MB
[%] |
0 |
0.0570 |
0.0619 |
103 |
60 |
0.0886 |
0.0497 |
90 |
120 |
0.108 |
0.0503 |
96 |
180 |
0.187 |
0.0534 |
118 |
240 |
0.157 |
0.0467 |
102 |
420 |
0.193 |
0.0378 |
98 |
480 |
0.204 |
0.0371 |
100 |
899 |
0.340 |
0.0312 |
126 |
1077 |
0.374 |
0.0187 |
117 |
1257 |
0.387 |
0.0164 |
116 |
1443 |
0.326 |
0.0188 |
105 |
1661 |
0.355 |
0.00903 |
98 |
1= molecular factor taken into account
MB= Mass balance
Table 8: Mass Balance for major transformation product ethanol at pH 7 and 30 °C.
Hydrolysis Time [min] |
Ethanol
[mmol/L] |
As Test Item1
[mmol/L] |
MB
[%] |
0.00 |
0.0570 |
0.0619 |
103 |
30.0 |
0.0823 |
0.0516 |
91 |
62.0 |
0.0994 |
0.0543 |
99 |
90.0 |
0.146 |
0.0523 |
107 |
118 |
0.147 |
0.0459 |
99 |
150 |
0.185 |
0.0468 |
109 |
178 |
0.180 |
0.0345 |
90 |
238 |
0.226 |
0.0315 |
97 |
298 |
0.245 |
0.0267 |
97 |
357 |
0.260 |
0.0214 |
93 |
478 |
0.317 |
0.0161 |
97 |
902 |
0.400 |
0.00353 |
101 |
1= molecular factor taken into account MB= Mass balance |
Table 9: Mass Balance for major transformation product ethanol at pH 9 and 10 °C.
Hydrolysis Time [min] |
Ethanol
[mmol/L] |
As Test Item1
[mmol/L] |
MB
[%] |
0.00 |
0.0645 |
0.0682 |
113 |
0.50 |
0.0917 |
0.0687 |
120 |
1.00 |
0.0916 |
0.0697 |
122 |
3.00 |
0.118 |
0.0620 |
117 |
5.00 |
0.138 |
0.0560 |
113 |
6.42 |
0.172 |
0.0539 |
118 |
10.0 |
0.171 |
0.0475 |
109 |
13.0 |
0.210 |
0.0272 |
89 |
16.2 |
0.238 |
0.0257 |
94 |
20.1 |
0.252 |
0.0249 |
96 |
26.7 |
0.287 |
0.0217 |
100 |
33.0 |
0.313 |
0.0161 |
98 |
40.0 |
0.328 |
0.00559 |
86 |
1= molecular factor taken into account
MB= Mass balance
Table 10: Mass Balance for major transformation product ethanol at pH 9 and 20 °C.
Hydrolysis Time [min] |
Ethanol
[mmol/L] |
As Test Item1
[mmol/L] |
MB
[%] |
0.00 |
0.0649 |
0.0860 |
126 |
0.50 |
0.0910 |
0.0836 |
129 |
1.00 |
0.1122 |
0.0803 |
129 |
2.00 |
0.137 |
0.0680 |
119 |
3.00 |
0.161 |
0.0621 |
116 |
4.00 |
0.194 |
0.0567 |
116 |
5.00 |
0.210 |
0.0498 |
111 |
6.00 |
0.254 |
0.0415 |
109 |
8.00 |
0.278 |
0.0297 |
99 |
10.0 |
0.298 |
0.0296 |
103 |
13.2 |
0.346 |
0.0164 |
97 |
16.0 |
0.366 |
0.0130 |
96 |
20.0 |
0.406 |
0.00703 |
97 |
1= molecular factor taken into account
MB= Mass balance
Table 11: Mass Balance for major transformation product ethanol at pH 9 and 30 °C.
Hydrolysis Time [min] |
Ethanol
[mmol/L] |
As Test Item1
[mmol/L] |
MB
[%] |
0.00 |
0.0929 |
0.0651 |
116 |
0.50 |
0.111 |
0.0653 |
120 |
1.00 |
0.137 |
0.0534 |
109 |
1.50 |
0.165 |
0.0522 |
114 |
2.00 |
0.186 |
0.0468 |
111 |
2.50 |
0.217 |
0.0404 |
110 |
3.00 |
0.232 |
0.0392 |
112 |
3.50 |
0.254 |
0.0315 |
106 |
4.00 |
0.265 |
0.0289 |
105 |
5.00 |
0.292 |
0.0219 |
101 |
6.50 |
0.321 |
0.0145 |
97 |
8.00 |
0.348 |
0.0099 |
97 |
11.0 |
0.374 |
0.00397 |
95 |
1= molecular factor taken into account
MB= Mass balance
Table 12: Validity criteria.
Validity criterion |
Required |
This study |
First order kinetic |
To confirm first order behavior, the regression graph should have a correlation factor of ≥ 0.8. |
pH 4 |
Temperature |
The test temperature should be within± 0.5 °C of the nominal temperature. |
Fulfilled |
Test systems |
The pH values of the buffer solutions should be in the range of ± 0.1 pH at test temperature. |
Fulfilled |
Sensitivity |
Sensitivity of the analytical method should be sufficient to quantify test item concentrations at least down to a 90% reduction of the initial concentration. |
Fulfilled |
Description of key information
DT50 = 11.9 h at pH 7 and 20 °C (OECD 111)
Key value for chemical safety assessment
- Half-life for hydrolysis:
- 11.9 h
- at the temperature of:
- 20 °C
Additional information
A reliable hydrolysis study according to OECD guideline 111 and GLP criteria is available for the registered substance. The study showed that the test item hydrolyses fast at pH 4 and 9 (t1/2 ≤ 1 h at 20 °C) and at pH 7 the test item showed a hydrolysis rate of t1/2 = 11.9 h at 20 °C. Ethanol was identified as major transformation product and quantified. Additional transformation products were postulated on basis of the expected de-ethoxylation processes with the masses (m/z) 258, 286, 314, 342, 370, and 398 Da and qualitatively determined.
The following additional information is available on the registered substance:
A preliminary test on the hydrolysis of 3-(triethoxysilyl)-N-[3-(triethoxysilyl)propyl]-1-propanamine (CAS No. 13497-18-2) was performed in the frame of the biodegradation test according to OECD guideline 301 and GLP. The hydrolysis test was performed in purified water with duration of 2 h. The test item hydrolyses to ethanol and the respective silanol hydrolysis product. Ethanol was analytically monitored at time points 0, 0.5, 1 and 2 h in order to gather information on the hydrolysis rate of the test item. More than half of the test material (51 – 62%) was hydrolyzed right after the preparation of the solution at time point 0. 97-99% of the test material was hydrolyzed after 0.5 h, showing that the substance hydrolyses rapidly in water at alkaline pH (9.5) and room temperature.
Furthermore, a hydrolysis study was conducted as a preliminary test within the purposes of an adsorption study according to OECD 106. The half-life of the substance was determined in soil eluates of 5 different soil types having neutral pH values (5.5 - 7.2). The parent substance was analytically monitored via LC-MS at time points 0, 0.25, 0.5, 1, 2, 4, 6 and 24 h. The hydrolysis half-lives were between 1 - 5.6 h, indicating rapid hydrolysis of the substance in soils of neutral pH.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.

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