sitagliptin and photo-transformation products in

1
SGT_09H_HPLC_PHOTO7 # 957 RT: 2.28 AV: 1 SB: 6 1.77-2.18 , 2.38-2.75 NL: 1.46E6 F: FTMS + p ESI d Full ms2 [email protected] [50.0000-260.0000] 60 80 100 120 140 160 180 200 220 240 260 m/z 0 10 20 30 40 50 60 70 80 90 100 174.0527 234.0741 0 10 20 30 40 50 60 70 80 90 100 406.1306 C 16 H 17 O 2 N 5 F 5 8.5 RDBE 2.2725 ppm 235.0807 C 13 H 11 ONF 2 8.0 RDBE 1.4294 ppm 172.0571 C 8 H 8 ONF 2 4.5 RDBE 1.7281 ppm 120.0810 C 8 H 10 N 4.5 RDBE 1.6228 ppm 318.1816 NL: 6.13E5 SGT_09H_HPLC_PHOTO7_2 0191114#1104 RT: 2.40 AV: 1 F: FTMS + p ESI d Full ms2 [email protected] [50.0000-435.0000] NL: 1.47E6 Sitagliptin and photo-transformation products in freshwater by LC-HRMS (Orbitrap) Enelton Fagnani (1,2) , Olga Gómez Navarro (2)* , Nicola Montemurro (2) , Sandra Pérez (2) (1) School of Technology, University of Campinas (UNICAMP), Paschoal Marmo 1888, 13484-332 Limeira-SP, Brazil (2) Department of Environmental Chemistry, Institute of Environmental Assessment and Water Research from the Spanish Council for Scientific Research (IDAEA-CSIC), Jordi Girona 18-26, 08034 Barcelona, Spain * [email protected] Tel.: +34-934-006-100, Fax: +34-932-045-904 Grant #2018/09875 - 3 Acknowledgements The identified photo-TPs of SGT in lab experiments were not found in these first Llobregat river samples. SGTs photo-TPs will be searched in samples from future sampling campaigns. References Matuszewski et al. Anal. Cheml. 75 (2003) 3019-3030, doi: 10.1021/ac020361s Meckelke et al. Anal. Bioanal. Chem. 411 (2019) 2555-2567, doi: 10.1007/s00216-019-01696-3 Hermes et al. Environ. Sci. Technol. 54 (2020) 10588-10598, doi: 10.1021/acs.est.0c01454 Conclusion Sitagliptin (SGT, logP: 1.26) is an organofluorinated pharmaceutical used to treat Type 2 Diabetes. In the past years, its consumption has increased and biological recalcitrance has been recognized. SGT has very low human metabolic rate, entering the wastewater treatment plants (WWTPs) unchanged. In addition, conventional treatments barely degrade SGT which can therefore be found in the aquatic system at concentrations of ng L -1 or higher. Natural solar photolysis assumes importance as a possible degradation process for many pharmaceutical products, including SGT. Exposure to sunlight activates degradation processes with the consequent production of photo-transformation products (photo-TP) that can accumulate in freshwater. Since photo-TPs may have greater ecotoxicity than their precursors, their study and identification is essential to assess the health of a watercourse. In this work, the fate of SGT and its photo-TPs both in lab-scale photolysis simulation and in freshwater samples will be studied. Introduction Methodology Solar sunlight simulator Irradiation time: 3 and 9 h Suntest CSP Haereus (600W/m 2 ) Quartz cubette Al foil Multi-layer SPE cartridge LC-MS/MS Q-Exactive Orbitrap Photolysis of SGT 41 0 20´58.5”N 2 0 02´46.7”E SGT UV spectrum Sampling campaign (Llobregat river) Extraction For a wide range of log Kow No pH adjustments are needed SGT photo-TPs production 1 ppm or 10 ppm Results and Discussion Lab photolysis simulation Kinetic degradation for SGT and photo-TPs In lab simulation, SGT was identified even after 9h of photolysis, proving its high recalcitrance. However, 10 photo-TPs were also identified. Llobregat river samples SGT was identified and quantified at a concentration of 398 ng L -1 . MS/MS spectrum SGT 233 (amide hydrolysis) MS/MS spectrum SGT MS/MS spectrum SGT 405 (-F+OH) Loss of NH 3 Triazole-piperazine moiety Benzyl site with primary amine TP 405 Benzyl site with primary amine TP 233 Triazole-piperazine moiety Photo-TP identified in lab simulation were not found in Llobregat river samples. 50 100 150 200 250 300 350 400 m/z 0

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D:\ENELTON\...\SGT_09H_HPLC_PHOTO7 09/26/19 14:39:37

SGT_09H_HPLC_PHOTO7 #957 RT: 2.28 AV: 1 SB: 6 1.77-2.18 , 2.38-2.75 NL: 1.46E6F: FTMS + p ESI d Full ms2 [email protected] [50.0000-260.0000]

60 80 100 120 140 160 180 200 220 240 260

m/z

0

10

20

30

40

50

60

70

80

90

100

Re

lative

Ab

un

da

nce

174.0527

234.0741

SGT_09H_HPLC_PHOTO7_20191114 11/14/19 17:32:41

50 100 150 200 250 300 350 400

m/z

0

10

20

30

40

50

60

70

80

90

100

0

10

20

30

40

50

60

70

80

90

100

Re

lative

Ab

un

da

nce

406.1306

C 16 H17 O2 N5 F 5

8.5 RDBE2.2725 ppm

235.0807

C 13 H11 O N F 2

8.0 RDBE1.4294 ppm

172.0571

C 8 H8 O N F 2

4.5 RDBE1.7281 ppm

120.0810

C 8 H10 N

4.5 RDBE1.6228 ppm

318.1816

406.1306

346.1095

389.1033269.1107 329.0826

NL: 6.13E5

SGT_09H_HPLC_PHOTO7_20191114#1104 RT: 2.40 AV: 1 F: FTMS + p ESI d Full ms2 [email protected] [50.0000-435.0000]

NL: 1.47E6

SGT_09H_HPLC_PHOTO7_20191114#1306 RT: 2.85 AV: 1 F: FTMS + p ESI d Full ms2 [email protected] [50.0000-435.0000]

Sitagliptin and photo-transformation products in freshwater by LC-HRMS (Orbitrap)

Enelton Fagnani(1,2), Olga Gómez Navarro (2)*, Nicola Montemurro(2), Sandra Pérez(2)

(1) School of Technology, University of Campinas (UNICAMP), Paschoal Marmo 1888, 13484-332 Limeira-SP, Brazil(2) Department of Environmental Chemistry, Institute of Environmental Assessment and Water Research from the Spanish Council for Scientific Research

(IDAEA-CSIC), Jordi Girona 18-26, 08034 Barcelona, Spain* [email protected] Tel.: +34-934-006-100, Fax: +34-932-045-904

Grant #2018/09875-3

Acknowledgements

The identified photo-TPs of SGT in lab experiments were not found in these first Llobregat river samples. SGTs photo-TPs will be searched in samples from future sampling campaigns.

ReferencesMatuszewski et al. Anal. Cheml. 75 (2003) 3019-3030, doi: 10.1021/ac020361s

Meckelke et al. Anal. Bioanal. Chem. 411 (2019) 2555-2567, doi: 10.1007/s00216-019-01696-3

Hermes et al. Environ. Sci. Technol. 54 (2020) 10588-10598, doi: 10.1021/acs.est.0c01454

Conclusion

Sitagliptin (SGT, logP: 1.26) is an organofluorinated pharmaceutical used to treat Type 2 Diabetes. In the past years, its consumption has increased andbiological recalcitrance has been recognized. SGT has very low human metabolic rate, entering the wastewater treatment plants (WWTPs) unchanged.In addition, conventional treatments barely degrade SGT which can therefore be found in the aquatic system at concentrations of ng L-1 or higher.Natural solar photolysis assumes importance as a possible degradation process for many pharmaceutical products, including SGT. Exposure to sunlightactivates degradation processes with the consequent production of photo-transformation products (photo-TP) that can accumulate in freshwater.Since photo-TPs may have greater ecotoxicity than their precursors, their study and identification is essential to assess the health of a watercourse.In this work, the fate of SGT and its photo-TPs both in lab-scale photolysis simulation and in freshwater samples will be studied.

Introduction

Methodology

Solar sunlightsimulator

Irradiation time: 3 and 9 h

Suntest CSP Haereus

(600W/m2)

Quartzcubette

Al foil

Multi-layer SPE cartridge

LC-MS/MS Q-Exactive Orbitrap

Photolysis of SGT

41020´58.5”N 2002´46.7”E

SGT UV spectrumSampling campaign(Llobregat river)

ExtractionFor a wide range of log Kow

No pH adjustments are needed

SGT photo-TPs production1 ppm or 10 ppm

Results and Discussion

Lab photolysis simulation

Kinetic degradation for SGT and photo-TPs

In lab simulation, SGT was identified even after 9h ofphotolysis, proving its high recalcitrance. However, 10photo-TPs were also identified.

Llobregat river samples

SGT was identified and quantified at a concentration of 398 ng L-1.

MS/MS spectrum SGT 233 (amide hydrolysis)

MS/MS spectrum SGT

MS/MS spectrum SGT 405 (-F+OH)

Loss of NH3

Triazole-piperazinemoiety

Benzyl site withprimary amine

TP 405

Benzyl site withprimary amine

TP 233

Triazole-piperazinemoiety

Photo-TP identified in lab simulation were not found in Llobregat river samples.

SGT_09H_HPLC_PHOTO7_20191114 11/14/19 17:32:41

50 100 150 200 250 300 350 400

m/z

0

10

20

30

40

50

60

70

80

90

100

0

10

20

30

40

50

60

70

80

90

100

Re

lative

Ab

un

da

nce

406.1306

C 16 H17 O2 N5 F 5

8.5 RDBE2.2725 ppm

235.0807

C 13 H11 O N F 2

8.0 RDBE1.4294 ppm

172.0571

C 8 H8 O N F 2

4.5 RDBE1.7281 ppm

120.0810

C 8 H10 N

4.5 RDBE1.6228 ppm

318.1816

406.1306

346.1095

389.1033269.1107 329.0826

NL: 6.13E5

SGT_09H_HPLC_PHOTO7_20191114#1104 RT: 2.40 AV: 1 F: FTMS + p ESI d Full ms2 [email protected] [50.0000-435.0000]

NL: 1.47E6

SGT_09H_HPLC_PHOTO7_20191114#1306 RT: 2.85 AV: 1 F: FTMS + p ESI d Full ms2 [email protected] [50.0000-435.0000]