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Reaction products of 1-(substitutedphenyl)urea coupled with diazotated potassium sodium substituted-5-{[2-(substituted)ethyl]sulfonyl}benzenesulfonate, further condensed with 2,4,6-trichloro-1,3,5-triazine, further converted with disubstituted benzene-1,4-disulfonic acid in aq. sodium hydroxide
EC number: - | 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

Hydrolysis
Administrative data
Link to relevant study record(s)
- Endpoint:
- hydrolysis
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- The study was conducted between 29 September 2015 and 24 February 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 111 (Hydrolysis as a Function of pH)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.7 (Degradation: Abiotic Degradation: Hydrolysis as a Function of pH)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Radiolabelling:
- no
- Analytical monitoring:
- yes
- Details on sampling:
- The sample solutions were taken from the waterbath at various times and the pH of each solution recorded.
- Buffers:
- See below
- Details on test conditions:
- The test system used sterile buffer solutions at pH’s 4, 7 and 9.
Performance of the Test
Preparation of the Test Solutions
Sample solutions were prepared in stoppered glass flasks at a nominal concentration of 100 mg/L in the buffer solutions.
The test solutions were split into individual vessels for each data point.
The solutions were shielded from light whilst maintained at the test temperature.
Preliminary Test / Tier 1
Sample solutions at pH 4, 7 and 9 at a nominal concentration of 100 mg/L were maintained at 50.0 ± 0.5 °C for a period of at least 120 hours.
Tier 2
Results from the Preliminary Test / Tier 1 showed it was necessary to undertake further testing at pH 7 and pH 9. - Duration:
- 120 h
- Temp.:
- 50 °C
- Initial conc. measured:
- 100 mg/L
- Number of replicates:
- Two
- Positive controls:
- no
- Negative controls:
- no
- Statistical methods:
- No data
- Preliminary study:
- Preliminary Test / Tier 1
pH 4 at 50.0 ± 0.5 ºC
Less than 10% hydrolysis after 5 days at 50 °C, equivalent to a half-life of greater than 1 year at 25 °C.
pH 7 at 50.0 ± 0.5 ºC
The extent of hydrolysis indicated that further testing (Tier 2) was required to estimate the rate constant and half-life at 25 °C.
pH 9 at 50.0 ± 0.5 ºC
The extent of hydrolysis indicated that further testing (Tier 2) was required to estimate the rate constant and half-life at 25 °C. - Transformation products:
- not measured
- pH:
- 4
- Temp.:
- 25 °C
- DT50:
- > 1 yr
- pH:
- 7
- Temp.:
- 25 °C
- Hydrolysis rate constant:
- 0.007 h-1
- DT50:
- 99.4 h
- pH:
- 9
- Temp.:
- 25 °C
- Hydrolysis rate constant:
- 0 h-1
- DT50:
- 182 d
- Details on results:
- Tier 2
pH 7 at 40.0 ± 0.5 ºC
Slope = -1.75E-02
kobs = 4.03E-02 hour-1
t½ = 17.2 hours
pH 7 at 50.0 ± 0.5 ºC
Slope = -3.55E-02
kobs = 8.18E-02 hour-1
t½ = 8.47 hours
pH 7 at 60.0 ± 0.5 ºC
Slope = -0.127
kobs = 0.291 hour-1
t½ = 2.38 hours
pH 9 at 50.0 ± 0.5 ºC
Slope = -2.33E-03
kobs = 5.36E-03 hour-1
t½ = 129 hours
pH 9 at 60.0 ± 0.5 ºC
Slope = -9.03E-03
kobs = 2.08E-02 hour-1
t½ = 33.3 hours
pH 9 at 70.0 ± 0.5 ºC
Slope = -2.73E-02
kobs = 6.29E-02 hour-1
t½ = 11.0 hours
pH 7 Arrhenius Data
From the graph of the data, the rate constant and half-life at 25 °C have been estimated to be as follows:
k = 6.97E-03 hour-1
t½ = 99.4 hours
pH 9 Arrhenius Data
From the graph of the data, the rate constant and half-life at 25 °C have been estimated to be as follows:
k = 1.59E-04 hour-1
t½ =4.36E+03 hours
= 182 days
Identification of Hydrolysis Products – Tier 3
Due to the complex nature of the test item, no attempt was made to elucidate the structure of the hydrolysis product. Furthermore, as the use of ion-pairing reagents is not acceptable in HPLC-MS and the test item is extremely complex, any further analysis would result in the parent test item components and the hydrolysis product essentially co-eluting.
That said, as the test item is a reactive dye, it can be postulated that the hydrolysis products are most likely due to removal of one or more of the reactive groups, possibly the terminal sulphooxy- groups, with the central, dye group remaining essentially unaffected. This would also be the reason why the hydrolyzed solutions retained a similar, orange color compared to the non-hydrolyzed solutions. - Validity criteria fulfilled:
- yes
- Conclusions:
- The estimated rate constants and half-lives at 25 °C of the test item are:
At pH 4 the estimated half-life at 25 °C was >1 year
At pH 7 the estimated rate constant at 25 °C was 6.97E-03. The estimated half-life at 25 °C was 99.4 hours.
At pH 9 the estimated rate constant at 25 °C was 1.59E-04. The estimated half-life at 25 °C was 182 days
As the pH 7 and pH 9 results indicate that the rate of hydrolysis increases with a decrease in pH, it can be concluded that the test item will hydrolyse extremely rapidly at pH 4. However, as this wasn’t indicated by the pH 4 results, it is likely that the main “test item” peak in the pH 4 standards and samples was due to a stable, hydrolysis product (as opposed to the parent test item). - Executive summary:
Hydrolysis as a Function of pH. Assessment of hydrolytic stability was carried out using a procedure designed to be compatible with Method C7 Abiotic Degradation, Hydrolysis as a Function of pH of Commission Regulation (EC) No 440/2008 of 30 May 2008 and Method 111 of the OECD Guidelines for Testing of Chemicals, 13 April 2004. The estimated rate constants and half-lives at 25 °C are shown in the following table:
pH
Rate constant (hr-1)
Estimated half-life at 25 °C
4
-
>1 year
7
6.97 x 10-3
99.4 hours
9
1.59 x 10-4
182 days
As the pH 7 and pH 9 results indicate that the rate of hydrolysis increases with a decrease in pH, it can be concluded that the test item will hydrolyse extremely rapidly at pH 4. However, as this wasn’t indicated by the pH 4 results, it is likely that the main “test item” peak in the pH 4 standards and samples was due to a stable, hydrolysis product (as opposed to the parent test item).
Reference
Tier 2
The mean peak areas relating to the standard and sample solutions are shown in the following table:
Tier 2
Solution |
Mean peak area |
Standard 101 mg/L, pH 7 |
9.7861 x 106 |
Standard 101 mg/L, pH 7 |
9.7915 x 106 |
Initial Sample A, pH 7, 50 ºC |
1.0237 x 107 |
Initial Sample B, pH 7, 50 ºC |
1.0175 x 107 |
2 Hour Sample A, pH 7, 50 ºC |
7.7457 x 106 |
2 Hour Sample B, pH 7, 50 ºC |
7.7066 x 106 |
4 Hour Sample A, pH 7, 50 ºC |
5.9876 x 106 |
4 Hour Sample B, pH 7, 50 ºC |
5.9388 x 106 |
5.5 Hour Sample A, pH 7, 50 ºC |
4.9347 x 106 |
5.5 Hour Sample B, pH 7, 50 ºC |
4.9076 x 106 |
Standard 100 mg/L, pH 7 |
1.2080 x 107 |
Standard 101 mg/L, pH 7 |
1.2186 x 107 |
24 Hour Sample A, pH 7, 50 ºC |
1.4822 x 106 |
24 Hour Sample B, pH 7, 50 ºC |
1.4805 x 106 |
26 Hour Sample A, pH 7, 50 ºC |
1.3197 x 106 |
26 Hour Sample B, pH 7, 50 ºC |
1.3179 x 106 |
28 Hour Sample A, pH 7, 50 ºC |
1.1785 x 106 |
28 Hour Sample B, pH 7, 50 ºC |
1.1872 x 106 |
Standard 105 mg/L, pH 7 |
1.0573 x 107 |
Standard 103 mg/L, pH 7 |
1.0222 x 107 |
Initial Sample A, pH 7, 40 ºC |
1.0016 x 107 |
Initial Sample B, pH 7, 40 ºC |
1.0004 x 107 |
3 Hour Sample A, pH 7, 40 ºC |
8.5062 x 106 |
3 Hour Sample B, pH 7, 40 ºC |
8.4418 x 106 |
5 Hour Sample A, pH 7, 40 ºC |
7.7111 x 106 |
5 Hour Sample B, pH 7, 40 ºC |
7.6385 x 106 |
Solution |
Mean peak area |
Standard 107 mg/L, pH 7 |
9.0253 x 106 |
Standard 106 mg/L, pH 7 |
9.2483 x 106 |
3 Hour Sample A, pH 7, 60 ºC |
3.8943 x 106 |
3 Hour Sample B, pH 7, 60 ºC |
3.8901 x 106 |
4 Hour Sample A, pH 7, 60 ºC |
2.6513 x 106 |
4 Hour Sample B, pH 7, 60 ºC |
2.6521 x 106 |
5 Hour Sample A, pH 7, 60 ºC |
2.0477 x 106 |
5 Hour Sample B, pH 7, 60 ºC |
2.0386 x 106 |
5.5 Hour Sample A, pH 7, 60 ºC |
1.7922 x 106 |
5.5 Hour Sample B, pH 7, 60 ºC |
1.7857 x 106 |
Standard 107 mg/L, pH 7 |
1.0194 x 107 |
Standard 106 mg/L, pH 7 |
1.0274 x 107 |
Initial Sample A, pH 7, 60°C |
1.0258 x 107 |
Initial Sample B, pH 7, 60°C |
1.0207 x 107 |
1 Hour Sample A, pH 7, 60 ºC |
7.2085 x 106 |
1 Hour Sample B, pH 7, 60 ºC |
7.0282 x 106 |
2 Hour Sample A, pH 7, 60 ºC |
5.2002 x 106 |
2 Hour Sample B, pH 7, 60 ºC |
5.1387 x 106 |
Standard 107 mg/L, pH 7 |
9.1421 x 106 |
Standard 106 mg/L, pH 7 |
9.1094 x 106 |
24 Hour Sample A, pH 7, 40 ºC |
2.9884 x 106 |
24 Hour Sample B, pH 7, 40 ºC |
2.9530 x 106 |
27 Hour Sample A, pH 7, 40 ºC |
2.6082 x 106 |
27 Hour Sample B, pH 7, 40 ºC |
2.5818 x 106 |
29 Hour Sample A, pH 7, 40 ºC |
2.4038 x 106 |
29 Hour Sample B, pH 7, 40 ºC |
2.3733 x 106 |
Standard 102 mg/L, pH 7 |
8.4321 x 106 |
Standard 104 mg/L, pH 7 |
8.4813 x 106 |
48 Hour Sample A, pH 7, 40 ºC |
1.2223 x 106 |
48 Hour Sample B, pH 7, 40 ºC |
1.2317 x 106 |
Solution |
Mean peak area |
Standard 102 mg/L, pH 9 |
1.2443 x 107 |
Standard 102 mg/L, pH 9 |
1.2471 x 107 |
Initial Sample A, pH 9, 50 ºC |
1.2928 x 107 |
Initial Sample B, pH 9, 50 ºC |
1.3116 x 107 |
Standard 102 mg/L, pH 9 |
1.2608 x 107 |
Standard 101 mg/L, pH 9 |
1.2579 x 107 |
45 Hour Sample A, pH 9, 50 ºC |
1.0333 x 107 |
45 Hour Sample B, pH 9, 50 ºC |
1.0332 x 107 |
Standard 100 mg/L, pH 9 |
1.2572 x 107 |
Standard 105 mg/L, pH 9 |
1.3221 x 107 |
118.5 Hour Sample A, pH 9, 50 ºC |
6.9992 x 106 |
118.5 Hour Sample B, pH 9, 50 ºC |
6.9138 x 106 |
Standard 102 mg/L, pH 9 |
1.2723 x 107 |
Standard 101 mg/L, pH 9 |
1.2602 x 107 |
167 Hour Sample A, pH 9, 50 ºC |
5.4056 x 106 |
167 Hour Sample B, pH 9, 50 ºC |
5.4571 x 106 |
Standard 100 mg/L, pH 9 |
1.2621 x 107 |
Standard 103 mg/L, pH 9 |
1.2824 x 107 |
288 Hour Sample A, pH 9, 50 ºC |
2.9182 x 106 |
288 Hour Sample B, pH 9, 50 ºC |
2.8804 x 106 |
Standard 110 mg/L, pH 9 |
1.3863 x 107 |
Standard 104 mg/L, pH 9 |
1.2999 x 107 |
336 Hour Sample A, pH 9, 50 ºC |
2.1118 x 106 |
336 Hour Sample B, pH 9, 50 ºC |
2.2353 x 106 |
Standard 106 mg/L, pH 9 |
1.2127 x 107 |
Standard 101 mg/L, pH 9 |
1.1564 x 107 |
Initial Sample A, pH 9, 60 /70 ºC |
1.1416 x 107 |
Initial Sample B, pH 9, 60 / 70 ºC |
1.1715 x 107 |
Standard 105 mg/L, pH 9 |
1.1916 x 107 |
Standard 102 mg/L, pH 9 |
1.2047 x 107 |
24 Hour Sample A, pH 9, 60 ºC |
8.1738 x 106 |
24 Hour Sample B, pH 9, 60 ºC |
8.0143 x 106 |
22 Hour Sample A, pH 9, 70 ºC |
3.0048 x 106 |
22 Hour Sample B, pH 9, 70 ºC |
3.0003 x 106 |
26 Hour Sample A, pH 9, 70 ºC |
2.4392 x 106 |
26 Hour Sample B, pH 9, 70 ºC |
2.3609 x 106 |
Solution |
Mean peak area |
Standard 105 mg/L, pH 9 |
1.3472 x 107 |
Standard 103 mg/L, pH 9 |
1.3222 x 107 |
49 Hour Sample A, pH 9, 60 ºC |
4.6617 x 106 |
49 Hour Sample B, pH 9, 60 ºC |
4.6961 x 106 |
43 Hour Sample A, pH 9, 70 ºC |
8.5175 x 105 |
43 Hour Sample B, pH 9, 70 ºC |
8.0930 x 105 |
49 Hour Sample A, pH 9, 70 ºC |
6.2715 x 106 |
49 Hour Sample B, pH 9, 70 ºC |
6.0995 x 106 |
The test item concentrations at the given time points are shown in the following tables:
pH7 at 40.0 ± 0.5 ºC
Time (Hours) |
Concentration (g/L) |
% of mean initial concentration |
||
A |
B |
A |
B |
|
0 |
0.101 |
0.100 |
- |
- |
3 |
8.54 x 10-2 |
8.47 x 10-2 |
85.0 |
84.3 |
5 |
7.74 x 10-2 |
7.68 x 10-2 |
77.0 |
76.3 |
24 |
3.48 x 10-2 |
3.44 x 10-2 |
34.6 |
34.2 |
27 |
3.04 x 10-2 |
3.01 x 10-2 |
30.2 |
29.9 |
29 |
2.80 x 10-2 |
2.76 x 10-2 |
27.9 |
27.5 |
48 |
1.49 x 10-2 |
1.50 x 10-2 |
14.8 |
14.9 |
pH7 at 50.0 ± 0.5 ºC
Time (Hours) |
Concentration (g/L) |
% of mean initial concentration |
||
A |
B |
A |
B |
|
0 |
0.105 |
0.105 |
- |
- |
2 |
7.97 x 10-2 |
7.93 x 10-2 |
75.9 |
75.5 |
4 |
6.16 x 10-2 |
6.11 x 10-2 |
58.7 |
58.2 |
5.5 |
5.08 x 10-2 |
5.05 x 10-2 |
48.4 |
48.1 |
24 |
1.23 x 10-2 |
1.23 x 10-2 |
11.7 |
11.7 |
26 |
1.09 x 10-2 |
1.09 x 10-2 |
10.4 |
10.4 |
28 |
9.75 x 10-3 |
9.82 x 10-3 |
9.28 |
9.35 |
pH7at 60.0 ± 0.5 ºC
Time (Hours) |
Concentration (g/L) |
% of mean initial concentration |
||
A |
B |
A |
B |
|
0 |
0.106 |
0.106 |
- |
- |
1 |
7.48 x 10-2 |
7.30 x 10-2 |
70.4 |
68.7 |
2 |
5.40 x 10-2 |
5.34 x 10-2 |
50.8 |
50.2 |
3 |
4.53 x 10-2 |
4.52 x 10-2 |
42.6 |
42.6 |
4 |
3.08 x 10-2 |
3.08 x 10-2 |
29.0 |
29.0 |
5 |
2.38 x 10-2 |
2.37 x 10-2 |
22.4 |
22.3 |
6 |
2.08 x 10-2 |
2.08 x 10-2 |
19.6 |
19.5 |
pH9at 50.0 ± 0.5 ºC
Time (Hours) |
Concentration (g/L) |
% of mean initial concentration |
||
A |
B |
A |
B |
|
0 |
0.106 |
0.107 |
- |
- |
45 |
8.34 x 10-2 |
8.34 x 10-2 |
78.2 |
78.2 |
118.5 |
5.56 x 10-2 |
5.50 x 10-2 |
52.2 |
51.5 |
167 |
4.33 x 10-2 |
4.37 x 10-2 |
40.6 |
41.0 |
288 |
2.33 x 10-2 |
2.30 x 10-2 |
21.9 |
21.6 |
336 |
1.68 x 10-2 |
1.78 x 10-2 |
15.7 |
16.7 |
pH9 at 60.0 ± 0.5 ºC
Time (Hours) |
Concentration (g/L) |
% of mean initial concentration |
||
A |
B |
A |
B |
|
0 |
9.95 x 10-2 |
0.102 |
- |
- |
24 |
7.06 x 10-2 |
6.92 x 10-2 |
70.0 |
68.7 |
49 |
3.63 x 10-2 |
3.66 x 10-2 |
36.0 |
36.3 |
pH9 at 70.0 ± 0.5 ºC
Time (Hours) |
Concentration (g/L) |
% of mean initial concentration |
||
A |
B |
A |
B |
|
0 |
9.95 x 10-2 |
0.102 |
- |
- |
22 |
2.60 x 10-2 |
2.59 x 10-2 |
25.7 |
25.7 |
26 |
2.11 x 10-2 |
2.04 x 10-2 |
20.9 |
20.2 |
43 |
6.64 x 10-3 |
6.31 x 10-3 |
6.58 |
6.26 |
49 |
4.89 x 10-3 |
4.75 x 10-3 |
4.85 |
4.72 |
The Arrhenius plots wereconstructed using the data shown in the following tables:
pH 7 Arrhenius Data
T (ºC) |
T (K) |
kobs(hr-1) |
Ln kobs |
|
40 |
313.15 |
3.19 x 10-3 |
4.03 x 10-2 |
-3.21 |
50 |
323.15 |
3.10 x 10-3 |
8.18 x 10-2 |
-2.50 |
60 |
333.15 |
3.00 x 10-3 |
0.291 |
-1.23 |
pH 9 Arrhenius Data
T (ºC) |
T (K) |
kobs(hr-1) |
Ln kobs |
|
50 |
323.15 |
3.10 x 10-3 |
5.36 x 10-3 |
-5.23 |
60 |
333.15 |
3.00 x 10-3 |
2.08 x 10-2 |
-3.87 |
70 |
343.15 |
2.91 x 10-3 |
6.29 x 10-2 |
-2.77 |
Validation
Linearity
The linearity of the detector response with respect to concentration was assessed for each pH (4, 7 and 9) over the nominal concentration range of 25 to 200mg/L (n =7). The correlation curves were satisfactory with first order correlation coefficients (r) of 1.0000, 0.9999 and 0.9997 being obtained for pH 4, 7 and 9 respectively.Specificity
Matrix matched blank solutions (relevant buffer solution) were injected with every set of samples and no peak was detected at the sample retention timeof the test itempeak.
Precision
The precision of the analytical method was assessed at a nominal concentration of 100 mg/L (n = 5). The results were satisfactory withrelative standard deviation (RSD)results of 4.53% at pH 4, 1.99% at pH 7 and 1.91% at pH 9.
Repeatability of Injection
The repeatability of injection was assessedusing a standard solutionatanominal concentration of 100mg/L (n = 10). The results were satisfactory with relative standard deviationresultsof ≤1.54%.
Recovery(Accuracy)
Recovery of analysis of the sample extraction procedure was assessed at a nominal sample concentration of 100 mg/L (n = 5), at each of pH 4, pH 7 and pH 9. The results are presented in the following table:
Sample ID |
pH |
Nominal concentration (mg/L) |
Measured concentration (mg/L) |
Recovery |
Mean recovery (%) |
Standard deviation |
RSD (%) |
4a |
4 |
106 |
104 |
97.8 |
96.0 |
4.35 |
4.53 |
4b |
4 |
141 |
141 |
99.2 |
|||
4c |
4 |
104 |
104 |
100 |
|||
4d |
4 |
109 |
101 |
92.2 |
|||
4e |
4 |
100 |
90.5 |
90.5 |
|||
7a |
7 |
144 |
146 |
101 |
98.3 |
1.95 |
1.99 |
7b |
7 |
116 |
113 |
97.0 |
|||
7c |
7 |
123 |
123 |
99.6 |
|||
7d |
7 |
114 |
111 |
97.0 |
|||
7e |
7 |
105 |
102 |
96.8 |
|||
9a |
9 |
109 |
111 |
101 |
103 |
1.97 |
1.91 |
9b |
9 |
110 |
117 |
106 |
|||
9c |
9 |
105 |
108 |
103 |
|||
9d |
9 |
101 |
102 |
102 |
|||
9e |
9 |
106 |
108 |
102 |
Description of key information
The estimated rate constants and half-lives at 25 °C of the test item are:
- At pH 4 the estimated half-life at 25 °C was >1 year
- At pH 7 the estimated rate constant at 25 °C was 6.97E-03. The estimated half-life at 25 °C was 99.4 hours.
- At pH 9 the estimated rate constant at 25 °C was 1.59E-04. The estimated half-life at 25 °C was 182 days.
As the pH 7 and pH 9 results indicate that the rate of hydrolysis increases with a decrease in pH, it can be concluded that the test item will hydrolyse extremely rapidly at pH 4. However, as this wasn’t indicated by the pH 4 results, it is likely that the main “test item” peak in the pH 4 standards and samples was due to a stable, hydrolysis product (as opposed to the parent test item)
Key value for chemical safety assessment
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.
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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