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. 2021 Jan 8:2021:6628285.
doi: 10.1155/2021/6628285. eCollection 2021.

Determination of Pharmaceutical Residues by UPLC-MS/MS Method: Validation and Application on Surface Water and Hospital Wastewater

Affiliations

Determination of Pharmaceutical Residues by UPLC-MS/MS Method: Validation and Application on Surface Water and Hospital Wastewater

Bui Van Hoi et al. J Anal Methods Chem. .

Abstract

In this study, an analytical method for the simultaneous determination of 7 major pharmaceutical residues in Vietnam, namely, carbamazepine, ciprofloxacin, ofloxacin, ketoprofen, paracetamol, sulfamethoxazole, and trimethoprim, in surface water and hospital wastewater has been developed. The method includes enrichment and clean-up steps by solid phase extraction using mix-mode cation exchange, followed by identification and quantification using an ultrahigh-performance liquid chromatography and tandem mass spectrometry and employing electrospray ionization (UPLC-ESI-MS/MS). Seven target compounds were separated on the reversed phase column and detected in multiple reaction monitoring (MRM) mode within 6 minutes. The present study also optimized the operating parameters of the mass spectrometer to achieve the highest analytical signals for all target compounds. All characteristic parameters of the analytical method were investigated, including linearity range, limit of detection, limit of quantification, precision, and accuracy. The important parameter in UPLC-ESI-MS/MS, matrix effect, was assessed and implemented via preextraction and postextraction spiking experiments. The overall recoveries of all target compounds were in the ranges from 55% to 109% and 56 % to 115% for surface water and hospital wastewater, respectively. Detection limits for surface water and hospital wastewater were 0.005-0.015 µg L-1 and 0.014-0.123 µg L-1, respectively. The sensitivity of the developed method was allowed for determination of target compounds at trace level in environmental water samples. The in-house validation of the developed method was performed by spiking experiment in both the surface water and hospital wastewater matrix. The method was then applied to analyze several surface water and hospital wastewater samples taken from West Lake and some hospitals in Vietnam, where the level of these pharmaceutical product residues was still missed. Sulfamethoxazole was present at a high detection frequency in both surface water (33% of analyzed samples) and hospital wastewater (81% of analyzed samples) samples.

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Conflict of interest statement

The authors declare that they have no conflicts of interest.

Figures

Figure 1
Figure 1
Surface water sampling points at the West Lake.
Figure 2
Figure 2
Extracted ion chromatograms of all standard compounds at 100 µg L−1 except IS at 50 µg L−1.
Figure 3
Figure 3
Stability of the analytical signal of all target compounds for 20 hours of injection.
Figure 4
Figure 4
Stability of target compounds in three thawing-freezing cycles at 10 µg L−1 (low concentration); 200 µg L−1 (middle concentration); 500 µg L−1 (high concentration).
Figure 5
Figure 5
Recoveries of seven pharmaceutical products in surface water on different solid phase extraction materials.
Figure 6
Figure 6
Extracted ion chromatograms of all target compounds in real hospital wastewater sample.

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References

    1. Daughton C. G. Pharmaceuticals in the Environment: Sources and Their Management. 2nd. Vol. 62. Amsterdam, Netherlands: Elsevier B. V.; 2013.
    1. Miller T. H., Bury N. R., Owen S. F., MacRae J. I., Barron L. P. Environmental Pollution. Vol. 239. Elsevier Ltd; 2018. A review of the pharmaceutical exposome in aquatic fauna; pp. 129–146. - DOI - PMC - PubMed
    1. Dogan A., Płotka-Wasylka J., Kempińska-Kupczyk D., Namieśnik J., Kot-Wasik A. Detection, identification and determination of chiral pharmaceutical residues in wastewater: problems and challenges. TrAC Trends in Analytical Chemistry. 2020;122:p. 115710. doi: 10.1016/j.trac.2019.115710. - DOI
    1. López-Serna R., Marín-de-Jesús D., Irusta-Mata R., et al. Multiresidue analytical method for pharmaceuticals and personal care products in sewage and sewage sludge by online direct immersion SPME on-fiber derivatization-GCMS. Talanta. 2018;186:506–512. doi: 10.1016/j.talanta.2018.04.099. - DOI - PubMed
    1. Tan E. S. S., Ho Y. B., Zakaria M. P., Latif P. A., Saari N. Simultaneous extraction and determination of pharmaceuticals and personal care products (PPCPs) in river water and sewage by solid-phase extraction and liquid chromatography-tandem mass spectrometry. International Journal of Environmental Analytical Chemistry. 2015;95(9):1–17. doi: 10.1080/03067319.2015.1058929. - DOI

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