Laser Diode Thermal Desorption-Atmospheric Pressure Chemical ...

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Laser Diode Thermal Desorption-Atmospheric Pressure Chemical Ionization Tandem Mass Spectrometry Analysis of Selected Steroid Hormones in Wastewater: Method Optimization and Application Paul B. Fayad†, Michèle Prévost‡ and Sébastien Sauvé†*

† ‡

Department of Chemistry, Université de Montréal, Montreal, QC, Canada Department of Civil, Geological and Mining Engineering, École Polytechnique de

Montréal, Montreal, QC, Canada

*Corresponding author. Phone: 514-343-6749. Fax: 514-343-7586. E-mail: [email protected].

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Table of content: Page S-3 to S-4: Principles of the LDTD-APCI source. Page S-5, Figure S-1: Molecular structures of selected steroid hormones and their acronyms. Page S-6, Table S-1: MS/MS Parameters for the Analysis of Selected Steroid Hormones Analytes in Both Negative (NI) and Positive (PI) Ionization Mode. Page S-7, Figure S-2: Choice of deposition solvent in the plate wells on peak area intensities for the selected steroid hormones. Page S-8, Figure S-3: Effect of carrier gas flow on peak area intensities in NI mode of the selected steroid hormones. Page S-9, Figure S-4: Effect of laser pattern on peak area intensities for PROG in PI mode. Page S-10, Figure S-5: SPE recovery values for matrix-free (pure water) and in matrix (spiked effluent wastewater) samples of the selected steroid hormones in PI and NI mode.

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Principles of the LDTD-APCI Source. The Arrhenius plots comparing the logarithm of the kinetic rates of the temperature dependencies of vaporization (dissociation of intermolecular bonds) and molecular decomposition (dissociation of intramolecular bonds) against the inverse temperature (1/T) would identify an intersection point at some value of 1/T, above which the vaporization of the uncharged molecular species would be favored and below which decomposition would be observed.1,2 The heating rate of the LDTD laser is 3000C/sec which allows the samples to be quickly heated at high temperatures, minimizing the time spent in the decomposition region and favoring vaporization which generates a greater amount of the uncharged molecular species. The characterization of the thermal desorption processes associated with rapid sample heating and thin film deposition for the LDTD-APCI source have been shown on prednisone, a corticosteroid steroid hormone, that decomposed at a temperature of 234C but was fully analyzed by LDTD-APCI-MS/MS at a desorption temperature of 170C. Also sulfadiazine, a sulfonamide antibiotic, shows a desorption temperature observed between 95C and 140C though its bulk melting point is 252-256C.3 Unlike traditional LC-APCI, the LDTD-APCI ionization is performed in the absence of solvent reacting molecules as no liquid phase is introduced into the corona discharge region. Similarly to classical chemical ionization, the species present in the APCI region of the LDTD originate from gas-phase reactions involving proton transfer, governed by proton affinity in positive mode (PI) and gas-phase acidity in negative mode (NI), as well as charge exchange.4 The solvent used for analyte deposition in LDTD-APCI will not induce signal suppression due to competition for protonation as can be the case in classical LC-APCI mobile-phase components.5-7 In the absence of any mobile phase, it is the water traces in

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the carrier gas that will generate ionization in LDTD-APCI, since proton transfer in the PI mode mostly occurs between water cluster, H3O+(H2O)n where n = 0-4,8 and more basic analytes (higher proton affinity). Higher efficiency protonation in LDTD-APCI is accomplished in the presence of the smallest hydronium species because of their low proton affinity, i.e. H3O+ and (H2O)H3O+. Larger water clusters will form when the humidity (water saturation) in the ionization region is increased and negatively impact the analyte ionization process.9 The larger hydronium cluster, with higher proton affinity, will affect sensitivity towards low proton affinity molecules and decrease their fragmentation because of an excess of energy in protonation reactions.10 The main advantage of using APCI with the LDTD is that it is less susceptible to matrix effects and ionization suppression than with electrospray ionization.11

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OH

O

H

H

H

H

H

H

HO

H

OH

H

HO

H

HO

Estrone (E1)

Estradiol (E2)

Estriol (E3)

OH

OH

OH

H

H

H

H

OH

H

H

H

H O

O

HO

Norethindrone (NOR)

Levonorgestrel (LEVO)

17-ethynylestradiol (EE2)

H

O O

OH H H

H

H

O

H

CH 3

Medroxyprogesterone (MPROG)

H

O

Progesterone (PROG)

Figure S-1. Molecular structures of selected steroid hormones and their acronyms.

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Table S-1. MS/MS Parameters for the Analysis of Selected Steroid Hormones Analytes in Both Negative (NI) and Positive (PI) Ionization Mode. Compound E1 E2

NI

271 [M–H]‾

PI

255 [M-H2O+H]+

133 144 159

31 ± 3 21 ± 3 100

68 68 68

18 40 19

NI

273 [M–H]‾

145 147 185

57 ± 9 82 ± 12 100

-67 -67 -67

61 43 47

PI

257 [M-H2O+H]+

E3

NI

287 [M–H]‾

EE2

NI

295 [M–H]‾

135 146 161 143 171 143 145 183

52 ± 5 22 ± 1 100 67 ± 12 100 63 ± 12 100 58 ± 13

65 65 65 -97 -97 -82 -82 -82

17 37 16 54 40 70 45 44

PI

279 [M-H2O+H]+

133 159

100 69 ± 11

46 46

16 20

NI

297 [M–H]‾

143 145

72 ± 15 100

-74 -74

43 43

PI

281 [M-H2O+H]+

133 159

100 22 ± 6

48 48

23 22

LEVO

PI

313 [M+H]+

109 185 245

83 ± 19 45 ± 8 100

64 64 64

27 20 18

MPROG

PI

345 [M+H]+

97 123

26 ± 4 100

74 74

23 25

NOR

PI

299 [M+H]+

91 109

85 ± 16 100

69 69

35 26

PROG

PI

315 [M+H]+

E2-13C2

EE2-13C2

Precursor ion (m/z) 269 [M–H]‾

Product ion (m/z) 143 145 143 145 183

Relative intensity ratioa (%) 45 ± 6 100 51 ± 13 66 ± 20 100

Ionisation mode NI

TL (V) -84 -84 -74 -74 -74

CE (eV) 57 41 47 37 49

97 98 ± 17 65 20 109 100 65 24 a The most abundant product ion was used for quantification whereas the other product ions were used for to confirm the presence of the steroid hormones.

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E1 E3

6.0E+04

EE2 E2

5.0E+04

Peak Area

4.0E+04

3.0E+04

2.0E+04

1.0E+04

0.0E+00 5

10

15

20

25

30

40

50

60

80

Laser Power (%)

Figure S-2. Negative ionization mode (NI) maximum peak intensity for a concentration of 2 mg/L was observed at a maximum 20% laser power for steroid hormones EE2 and E2 and was significantly different from other laser power (n=3; P  0.5). The optimum laser power for E1 was 20% and 25%, while for E3 it was 15% and 20%, which were not statistically different from each other in both cases (n=3; P  0.5). A laser power of 20% was chosen in NI mode, in order to have a single method applicable to all selected compounds and because it was common to all four selected steroid hormones.

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E3 E1

1.2E+05

EE2 E2

1.0E+05

Peak Area

8.0E+04

6.0E+04

4.0E+04

2.0E+04

0.0E+00 1.0

2.0

3.0

4.0

5.0

6.0

7.0

8.0

9.0

10.0

Gas Flow (L/min)

Figure S-3. Carrier gas flow was optimal between 2 to 3 L/min and gave significantly higher peak area response (n=3; P  0.5) in NI mode. A gas flow of 3 L/min provided the best signal-to-noise ratio combined with small signal variability (RSD  10%; n=3). Estriol (E3) was the only exception with an optimal gas flow of 2 L/min.

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1.4E+06 1.2E+06

Peak Area

1.0E+06 8.0E+05 6.0E+05 4.0E+05 2.0E+05 0.0E+00

3 sec – 20%

1 sec – 20%

2 sec – 20%

3 sec – 20% 3 sec – 2% 1 sec

0.5 sec

0.5 sec

1 sec

1 sec

Laser Pattern

Figure S-4. Four different laser patterns (n=3) were used and compared for PROG in PI mode.

The optimal conditions giving the maximum peak area intensity and good

variability (RSD  10%) for desorption laser power and patter consisted of a 1 sec initial ramp from 0 to 20% and held for 3 sec at 20% before shutting off.

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Matrix-free In matrix

160 140

Recovery (%)

120 100 80 60 40

PROG (PI)

NOR (PI)

MPROG (PI)

LEVO (PI)

EE2-13C2 (PI)

EE2-13C2 (NI)

EE2 (PI)

EE2 (NI)

E3 (NI)

E2 (PI)

E2 (NI)

0

E1 (NI)

20

Compound (ionisation mode)

Figure S-5. Recovery values (n=3) for matrix-free (pure water) and in matrix (spiked effluent wastewater) samples at 50 ng/L in both NI and PI modes using Strata-X SPE cartridges for all selected steroid hormones including IS and surrogate.

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REFRENCES

(1) Beuhler, R. J.; Flanigan, E.; Greene, L. J.; Friedman, L. J. Am. Chem. Soc. 2002, 96 , 3990-3999. (2) Daves, G. D. Acc. Chem. Res. 1979, 12 , 359-365. (3) Picard, P.; Tremblay, P.; Paquin, E. R. Laser Diode Thermal Desorption Ionization Source (LDTD): Fundamental Aspects. 56th ASMS Conference on Mass Spectrometry, Denver, CO. 2008. Available at: http://www.ldtdionsource.com/eng/documentations/publications.asp (4) Harrison, H. G. Chemical Ionization Mass Spectrometry; CRC Press Inc: Boca Raton, FL, 1983.pp. 156. (5) Ma, Y. C.; Kim, H. Y. Journal of the American Society for Mass Spectrometry 1997, 8 , 1010-1020. (6) Geerdink, R. B.; Kooistra-Sijpersma, A.; Tiesnitsch, J.; Kienhuis, P. G. M.; Brinkman, U. A. T. J. Chromatogr. A 1999, 863 , 147-155. (7) Dams, R.; Benijts, T.; Duff, K.; Bell, D. Rapid Commun. Mass Spectrom. 2002, 16 , 1072-1077. (8) Zook, D. R.; Grimsrud, E. P. J. Phys. Chem. 1988, 92 , 6374-6378. (9) Sinha, V.; Custer, T. G.; Kluepfel, T.; Williams, J. Int. J. Mass Spectrom. 2009, 282 , 108-111.

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(10) Tani, A.; Hayward, S.; Hansel, A.; Hewitt, C. N. Int. J. Mass Spectrom. 2004, 239 , 161-169. (11) Matuszewski, B. K.; Constanzer, M. L.; Chavez-Eng, C. M. Anal. Chem. 2003, 75 , 3019-3030.

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