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Environmental fate & pathways

Hydrolysis

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Reference
Endpoint:
hydrolysis
Type of information:
experimental study
Adequacy of study:
key study
Study period:
Experimental starting date: 03 August 2017. Experimental completion date: 18 October 2017.
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)
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)
Analytical monitoring:
yes
Remarks:
HPLC
Details on sampling:
Samples
For duplicate aliquots of the stock solution for the initial time point and duplicate incubated vessels (samples A and B) removed at each time point, 5 mL aliquots of each sample solution were mixed with 10 mL of purified water*, before diluting to a total volume of 20 mL using acetonitrile (dilution factor of 4).

Standards
Duplicate standard solutions at a nominal concentration of 250 mg/L of test item were prepared in 25:25:50% v/v relevant buffer solution:acetonitrile:purified water*.

Matrix blanks
25:25:50% v/v relevant buffer solution:acetonitrile:purified water*.

* For pH 9 matrix, the purified water contained 1% v/v phosphoric acid.
Buffers:
The test system used sterile buffer solutions at pH’s 4, 7 and 9.
The buffer solutions were subjected to filtration through 0.2 µm filters, ultrasonication and degassing with nitrogen to minimize dissolved oxygen content.
Details on test conditions:
Preparation of the Test Solutions
Stock solutions of test item were prepared at a nominal concentration of 1.0 g/L in the three buffer solutions. The concentration of each solution did not exceed the lesser of 0.01 mol/L or half the water solubility. The stock solutions were split into individual glass vessels, sealed with minimal headspace, for each data point. These sample solutions were shielded from light whilst maintained at the test temperature.

Preliminary Test (Tier 1)
Sample solutions at pH 4, pH 7 and pH 9 were maintained at 50.0 ± 0.5 °C for the following periods of time: up to 120 h for the pH 4 samples, 720 h for the pH 7 samples and 29 h for the pH 9 samples.

Tier 2
Results from the Preliminary Test/Tier 1 showed it was necessary to undertake further testing at pH 7 and pH 9. pH 7 sample solutions were maintained up to 452 h at 60.0 ± 0.5 °C and 120 h at 70.0 ± 0.5 °C. pH 9 sample solutions were maintained up to 216 h at 30.0 ± 0.5 °C and 55 h at 40.0 ± 0.5 °C.
Duration:
120 h
pH:
4
Temp.:
50 °C
Initial conc. measured:
1 g/L
Duration:
120 h
pH:
7
Temp.:
50 °C
Initial conc. measured:
0.995 g/L
Duration:
452 h
pH:
7
Temp.:
60 °C
Initial conc. measured:
1 g/L
Duration:
120 h
pH:
7
Temp.:
70 °C
Initial conc. measured:
1.01 g/L
Duration:
29 h
pH:
9
Temp.:
50 °C
Initial conc. measured:
0.985 g/L
Duration:
55 h
pH:
9
Temp.:
40 °C
Initial conc. measured:
0.993 mg/L
Duration:
216 h
pH:
9
Temp.:
30 °C
Initial conc. measured:
0.972 mg/L
Number of replicates:
2
Preliminary study:
pH 4 at 50 ºC
Less than 10% hydrolysis after 120 hours (5 days) at 50 °C, which is equivalent to a half-life greater than 1 year at 25 °C. Therefore, no further testing was required as the test item was confirmed to be hydrolytically stable at pH 4.

pH 7 at 50 ºC
The extent of hydrolysis after 120 hours indicated that further testing (Tier 2) was required to estimate the rate constant and half-life at 25 °C.

pH 9 at 50 ºC
The extent of hydrolysis after 2 hours indicated that further testing (Tier 2) was required to estimate the rate constant and half-life at 25 °C.
Transformation products:
yes
No.:
#1
No.:
#2
Details on hydrolysis and appearance of transformation product(s):
Based on the chemical structure of the test item, the hydrolysis products were considered to be methacrylic acid (CAS 79-41-4) and glycerol (CAS 56-81-5). The reaction is hydrolysis of an ester into a carboxylic acid and an alcohol.
pH:
7
Temp.:
50 °C
Hydrolysis rate constant:
0.001 h-1
DT50:
514 h
Type:
(pseudo-)first order (= half-life)
pH:
7
Temp.:
60 °C
Hydrolysis rate constant:
0.004 h-1
DT50:
164 h
Type:
(pseudo-)first order (= half-life)
pH:
7
Temp.:
70 °C
Hydrolysis rate constant:
0.012 h-1
DT50:
57.7 h
Type:
(pseudo-)first order (= half-life)
pH:
9
Temp.:
50 °C
Hydrolysis rate constant:
0.069 h-1
DT50:
10 h
Type:
(pseudo-)first order (= half-life)
pH:
9
Temp.:
40 °C
Hydrolysis rate constant:
0.024 h-1
DT50:
29.6 h
Type:
(pseudo-)first order (= half-life)
pH:
9
Temp.:
30 °C
Hydrolysis rate constant:
0.008 h-1
DT50:
91.5 h
Type:
(pseudo-)first order (= half-life)
Details on results:
Validation
The linearity of the detector response with respect to concentration was assessed over the nominal concentration range of 10 to 350 mg/L in 25:25:50% v/v relevant buffer solution:acetonitrile:purified water.. These were satisfactory with a goodness of fit coefficient (r2) of 1.000 being obtained for all three matrices.

Discussion
In most sequences, the analysis of the matrix blank solutions showed a small peak at the approximate retention time of the test item. The peak decreased significantly or even disappeared in the second injection of the blank solution, suggesting that it was caused by carryover. It has to be noted that this carryover did not exceed 10% of the sample response and affected both standard and sample solutions. It has therefore been considered that its overall effect on the results was not significant.
The 216 hours data points for pH 9 at 30 °C were not used in calculating the half-life as they were significantly inconsistent with the other data points. The reason for this was not known.
The kinetics of the study have been determined to be consistent with that of a pseudo-first order reaction, as the graphs of log10 concentration versus time are straight lines.

pH 4 at 50 ºC

Time (Hours)

Concentration (g/L)

% of Mean Initial Concentration

A

B

A

B

0

1.00

1.00

-

-

24

0.997

0.994

99.5

99.1

120

1.02

1.04

102

104

pH 7 at 50 ºC

Time (Hours)

Concentration (g/L)

% of Mean Initial Concentration

A

B

A

B

0

0.995

0.994

-

-

24

0.957

0.960

96.2

96.5

120

0.844

0.833

84.8

83.8

240

0.710

0.710

71.4

71.4

362½

0.604

0.601

60.8

60.4

480

0.499

0.504

50.1

50.7

600¼

0.441

0.433

44.3

43.5

720

0.387

0.378

38.9

38.0

pH 7 at 60 ºC

Time (Hours)

Concentration (g/L)

% of Mean Initial Concentration

A

B

A

B

0

1.00

0.995

-

-

48

0.783

0.793

78.4

79.5

96

0.630

0.618

63.1

62.0

144

0.516

0.505

51.7

50.6

192

0.408

0.409

40.9

41.0

264

0.300

0.303

30.1

30.3

360

0.206

0.208

20.6

20.8

452

0.146

0.146

14.7

14.7

pH 7 at 70 ºC

Time (Hours)

Concentration (g/L)

% of Mean Initial Concentration

A

B

A

B

0

1.01

1.00

-

-

7

0.902

0.897

89.9

89.3

24

0.734

0.725

73.2

72.2

31

0.637

0.667

63.4

66.4

48

0.532

0.527

53.0

52.5

72

0.402

0.392

40.0

39.1

96

0.308

0.311

30.7

31.0

120

0.234

0.236

23.3

23.5

pH 9 at 50 ºC

Time (Hours)

Concentration (g/L)

% of Mean Initial Concentration

A

B

A

B

0

0.985

0.984

-

-

2

0.829

0.824

84.2

83.7

4

0.697

0.699

70.8

71.0

6

0.593

0.594

60.2

60.3

8

0.514

0.513

52.2

52.1

23

0.186

0.186

18.8

18.9

26

0.152

0.156

15.5

15.9

29

0.130

0.129

13.2

13.1

pH 9 at 40 ºC

Time (Hours)

Concentration (g/L)

% of Mean Initial Concentration

A

B

A

B

0

0.993

0.994

-

-

0.899

0.917

90.5

92.3

5

0.854

0.855

85.9

86.1

0.793

0.789

79.9

79.4

24

0.522

0.523

52.6

52.6

31

0.445

0.443

44.7

44.6

48

0.316

0.310

31.8

31.2

55

0.271

0.273

27.2

27.5

pH 9 at 30 ºC

Time (Hours)

Concentration (g/L)

% of Mean Initial Concentration

A

B

A

B

0

0.972

0.969

-

-

24

0.802

0.790

82.6

81.4

48

0.645

0.645

66.5

66.4

72

0.532

0.531

54.8

54.7

96

0.445

0.440

45.9

45.4

120

0.372

0.367

38.3

37.8

168

0.276

0.277

28.4

28.5

216*

0.038

0.041

3.96

4.23

*Not used – See Discussion.

The Arrhenius plots for pH 7 and pH 9 were constructed using the data shown in the following tables:

pH 7 Arrhenius Data

T (ºC)

T (K)

1/T (K-1)

kobs(h-1)

ln kobs

50

323

3.10 x 10-3

1.35 x 10-3

-6.61

60

333

3.00 x 10-3

4.24 x 10-3

-5.46

70

343

2.91 x 10-3

1.20 x 10-2

-4.42

pH 9 Arrhenius Data

T (ºC)

T (K)

1/T (K-1)

kobs(h-1)

ln kobs

30

303

3.30 x 10-3

7.58

-4.88

40

313

3.19 x 10-3

2.35

-3.75

50

323

3.10 x 10-3

6.92

-2.67

Validity criteria fulfilled:
yes
Conclusions:
The estimated rate constants and half-lives at 25 °C of the test item are shown below:
Ph 4
Estimated rate constant at 25 °C: not applicable.
Estimated half-life at 25 °C: > 1 year
Ph 7
Estimated rate constant at 25 °C: 5.83 x 10^-5 h-1
Estimated half-life at 25 °C: > 1 year (496 days)
Ph 9
Estimated rate constant at 25 °C: 4.15 x 10^-5 h-1
Estimated half-life at 25 °C: 6.97 days
Executive summary:

The hydrolytic stability of 2,3-dihydroxypropyl methacrylate as a function of pH was determine dusing a procedure designed to be compatible with Method C.7 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 results are as follows:

pH

Estimated rate constant at 25 °C

Estimated half-life at 25 °C

4

Not applicable

>1 year

7

5.83 x10-5h-1

>1 year (496 days)

9

4.15 x 10-3h-1

6.97 days

Description of key information

The estimated rate constants and half-lives at 25 °C of the test item are shown below:

pH 4

Estimated rate constant at 25 °C: not applicable.

Estimated half-life at 25 °C: > 1 year

pH 7

Estimated rate constant at 25 °C: 5.83 x 10^-5 h-1

Estimated half-life at 25 °C: > 1 year (496 days)

pH 9

Estimated rate constant at 25 °C: 4.15 x 10^-5 h-1

Estimated half-life at 25 °C: 6.97 days

Key value for chemical safety assessment

Additional information