Abstract
Aminomethylphosphonic acid (AMPA) is the main metabolite of glyphosate (GLYP) and phosphonic acids in detergents. GLYP is a synthetic herbicide frequently used worldwide alone or together with its analog glufosinate (GLUF). The general public can be exposed to these potentially harmful chemicals; thus, sensitive methods to monitor them in humans are urgently required to evaluate health risks. We attempted to simultaneously detect GLYP, AMPA, and GLUF in human urine by high-resolution accurate-mass liquid chromatography mass spectrometry (HRAM LC-MS) before and after derivatization with 9-fluorenylmethoxycarbonyl chloride (Fmoc-Cl) or 1-methylimidazole-sulfonyl chloride (ImS-Cl) with several urine pre-treatment and solid phase extraction (SPE) steps. Fmoc-Cl derivatization achieved the best combination of method sensitivity (limit of detection; LOD) and accuracy for all compounds compared to underivatized urine or ImS-Cl-derivatized urine. Before derivatization, the best steps for GLYP involved 0.4 mM ethylenediaminetetraacetic acid (EDTA) pre-treatment followed by SPE pre-cleanup (LOD 37 pg/mL), for AMPA involved no EDTA pre-treatment and no SPE pre-cleanup (LOD 20 pg/mL) or 0.2–0.4 mM EDTA pre-treatment with no SPE pre-cleanup (LOD 19–21 pg/mL), and for GLUF involved 0.4 mM EDTA pre-treatment and no SPE pre-cleanup (LOD 7 pg/mL). However, for these methods, accuracy was sufficient only for AMPA (101–105%), while being modest for GLYP (61%) and GLUF (63%). Different EDTA and SPE treatments prior to Fmoc-Cl derivatization resulted in high sensitivity for all analytes but satisfactory accuracy only for AMPA. Thus, we conclude that our HRAM LC-MS method is suited for urinary AMPA analysis in cross-sectional studies.
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The data that support the reported findings of this study are available from AAF and XL.
References
Bai SH, Ogbourne SM. Glyphosate: environmental contamination, toxicity and potential risks to human health via food contamination. Environ Sci Pollut Res Int. 2016;23(19):18988–9001.
Masiol M, Gianni B, Prete M. Herbicides in river water across the northeastern Italy: occurrence and spatial patterns of glyphosate, aminomethylphosphonic acid, and glufosinate ammonium. Environ Sci Pollut Res Int. 2018;25(24):24368–78.
Duke SO. Glyphosate degradation in glyphosate-resistant and -susceptible crops and weeds. J Agric Food Chem. 2011;59(11):5835–41.
Jaworska J, Van Genderen-Takken H, Hanstveit A, van de Plassche E, Feijtel T. Environmental risk assessment of phosphonates, used in domestic laundry and cleaning agents in The Netherlands. Chemosphere. 2002;47(6):655–65.
Battaglin WA, Meyer M, Kuivila K, Dietze J. Glyphosate and its degradation product AMPA occur frequently and widely in US soils, surface water, groundwater, and precipitation. JAWRA J Am Water Resour Assoc. 2014;50(2):275–90.
Chen MX, Cao ZY, Jiang Y, Zhu ZW. Direct determination of glyphosate and its major metabolite, aminomethylphosphonic acid, in fruits and vegetables by mixed-mode hydrophilic interaction/weak anion-exchange liquid chromatography coupled with electrospray tandem mass spectrometry. J Chromatogr A. 2013;1272:90–9.
Han Y, Song L, Zhao P, Li Y, Zou N, Qin Y, et al. Residue determination of glufosinate in plant origin foods using modified Quick Polar Pesticides (QuPPe) method and liquid chromatography coupled with tandem mass spectrometry. Food Chem. 2016;197(Pt A):730–6.
Hogendoorn EA, Ossendrijver FM, Dijkman E, Baumann RA. Rapid determination of glyphosate in cereal samples by means of pre-column derivatisation with 9-fluorenylmethyl chloroformate and coupled-column liquid chromatography with fluorescence detection. J Chromatogr A. 1999;833(1):67–73.
Grandcoin A, Piel S, Baures E. Aminomethylphosphonic acid (AMPA) in natural waters: its sources, behavior and environmental fate. Water Res. 2017;117:187–97.
Grunewald K, Schmidt W, Unger C, Hanschmann G. Behavior of glyphosate and aminomethylphosphonic acid (AMPA) in soils and water of reservoir Radeburg II catchment (Saxony/Germany). J Plant Nutr Soil Sci. 2001;164(1):65–70.
Conrad A, Schroter-Kermani C, Hoppe HW, Ruther M, Pieper S, Kolossa-Gehring M. Glyphosate in German adults - time trend (2001 to 2015) of human exposure to a widely used herbicide. Int J Hyg Environ Health. 2017;220(1):8–16.
Hoppe HW. Determination of glyphosate residues in human urine samples from 18 European countries. Medical Laboratory Bremen, D-28357 Bremen/Germany; 2013.
Jayasumana C, Gunatilake S, Siribaddana S. Simultaneous exposure to multiple heavy metals and glyphosate may contribute to Sri Lankan agricultural nephropathy. BMC Nephrol. 2015;16:103.
McGuire MK, McGuire MA, Price WJ, Shafii B, Carrothers JM, Lackey KA, et al. Glyphosate and aminomethylphosphonic acid are not detectable in human milk. Am J Clin Nutr. 2016;103(5):1285–90.
Mills PJ, Kania-Korwel I, Fagan J, McEvoy LK, Laughlin GA, Barrett-Connor E. Excretion of the herbicide glyphosate in older adults between 1993 and 2016. Jama. 2017;318(16):1610–1.
Parvez S, Gerona RR, Proctor C, Friesen M, Ashby JL, Reiter JL, et al. Glyphosate exposure in pregnancy and shortened gestational length: a prospective Indiana birth cohort study. Environ Health. 2018;17(1):23.
Curwin BD, Hein MJ, Sanderson WT, Striley C, Heederik D, Kromhout H, et al. Urinary pesticide concentrations among children, mothers and fathers living in farm and non-farm households in Iowa. Ann Occup Hyg. 2007;51(1):53–65.
Rendon-von Osten J, Dzul-Caamal R. Glyphosate residues in groundwater, drinking water and urine of subsistence farmers from intensive agriculture localities: a survey in Hopelchen, Campeche, Mexico. Int J Environ Res Public Health. 2017;14(6).
Acquavella JF, Alexander BH, Mandel JS, Gustin C, Baker B, Chapman P, et al. Glyphosate biomonitoring for farmers and their families: results from the Farm Family Exposure Study. Environ Health Perspect. 2004;112(3):321–6.
Hori Y, Fujisawa M, Shimada K, Sato M, Kikuchi M, Honda M, et al. Quantitative determination of glufosinate in biological samples by liquid chromatography with ultraviolet detection after p-nitrobenzoyl derivatization. J Chromatogr B Analyt Technol Biomed Life Sci. 2002;767(2):255–62.
Chen D, Miao H, Zhao Y, Wu Y. A simple liquid chromatography-high resolution mass spectrometry method for the determination of glyphosate and aminomethylphosphonic acid in human urine using cold-induced phase separation and hydrophilic pipette tip solid-phase extraction. J Chromatogr A. 2019;1587:73–8.
Kazui Y, Seto Y, Inoue H. Phosphorus-specific determination of glyphosate, glufosinate, and their hydrolysis products in biological samples by liquid chromatography–inductively coupled plasma–mass spectrometry. Forensic Toxicol. 2014;32(2):317–22.
Mesnage R, Moesch C, Grand R, Lauthier G, Vendômois J, Gress S, et al. Glyphosate exposure in a farmer’s family. J Environ Prot. 2012;9:1001–3.
Connolly A, Jones K, Galea KS, Basinas I, Kenny L, McGowan P, et al. Exposure assessment using human biomonitoring for glyphosate and fluroxypyr users in amenity horticulture. Int J Hyg Environ Health. 2017;220(6):1064–73.
Connolly A, Basinas I, Jones K, Galea KS, Kenny L, McGowan P, et al. Characterising glyphosate exposures among amenity horticulturists using multiple spot urine samples. Int J Hyg Environ Health. 2018;221(7):1012–22.
Jensen PK, Wujcik CE, McGuire MK, McGuire MA. Validation of reliable and selective methods for direct determination of glyphosate and aminomethylphosphonic acid in milk and urine using LC-MS/MS. J Environ Sci Health B. 2016;51(4):254–9.
Watanabe D, Ohta H, Yamamuro T. Solid-phase extraction of phosphorous-containing amino acid herbicides from biological specimens with a zirconia-coated silica cartridge. J Chromatogr B Analyt Technol Biomed Life Sci. 2014;969:69–76.
Tsao YC, Lai YC, Liu HC, Liu RH, Lin DL. Simultaneous determination and quantitation of paraquat, diquat, glufosinate and glyphosate in postmortem blood and urine by LC-MS-MS. J Anal Toxicol. 2016;40(6):427–36.
Saito T, Miura N, Namera A, Oikawa H, Miyazaki S, Nakamoto A, et al. Mixed-mode C–C 18 monolithic spin-column extraction and GC–MS for simultaneous assay of organophosphorus compounds, glyphosate, and glufosinate in human serum and urine. Forensic Toxicol. 2012;30(1):1–10.
Kruger M, Schledorn P, Schrödl W, Hoppe H-W, Lutz W, Shehata AA. Detection of glyphosate residues in animals and humans. J Environ Anal Toxicol. 2014;4(2):1–5.
Jauhiainen A, Rasanen K, Sarantila R, Nuutinen J, Kangas J. Occupational exposure of forest workers to glyphosate during brush saw spraying work. Am Ind Hyg Assoc J. 1991;52(2):61–4.
Raina-Fulton R. A review of methods for the analysis of orphan and difficult pesticides: glyphosate, glufosinate, quaternary ammonium and phenoxy acid herbicides, and dithiocarbamate and phthalimide fungicides. J AOAC Int. 2014;97(4):965–77.
Li X, Franke AA. Improvement of bisphenol A quantitation from urine by LCMS. Anal Bioanal Chem. 2015;407(13):3869–74.
Li X, Franke AA. Improved profiling of estrogen metabolites by orbitrap LC/MS. Steroids. 2015;99:84–90.
Franke A, Halm B, Ashburn L. Isoflavones in children and adults consuming soy. Arch Biochem Biophys. 2008;476:161–70.
Liao MF, Chaou WT, Tsao LY, Nishida H, Sakanoue M. Ultrasound measurement of the ventricular size in newborn infants. Brain and Development. 1986;8(3):262–8.
Xu J, Smith S, Smith G, Wang W, Li Y. Glyphosate contamination in grains and foods: an overview. Food Control. 2019;106710.
Cessna A, Darwent A, Townley-Smith L, Harker K, Kirkland K. Residues of glyphosate and its metabolite AMPA in field pea, barley and flax seed following preharvest applications. Can J Plant Sci. 2002;82(2):485–9.
Cessna A, Darwent A, Townley-Smith L, Harker K, Kirkland K. Residues of glyphosate and its metabolite AMPA in canola seed following preharvest applications. Can J Plant Sci. 2000;80(2):425–31.
Medalie L, Baker NT, Shoda ME, Stone WW, Meyer MT, Stets EG, et al. Influence of land use and region on glyphosate and aminomethylphosphonic acid in streams in the USA. Sci Total Environ. 2020;707:136008.
Kolpin DW, Thurman EM, Lee EA, Meyer MT, Furlong ET, Glassmeyer ST. Urban contributions of glyphosate and its degradate AMPA to streams in the United States. Sci Total Environ. 2006;354(2–3):191–7.
Aparicio VC, De Geronimo E, Marino D, Primost J, Carriquiriborde P, Costa JL. Environmental fate of glyphosate and aminomethylphosphonic acid in surface waters and soil of agricultural basins. Chemosphere. 2013;93(9):1866–73.
U.S. Geological Survey. Surface water use in the United States 29015. Available from: https://www.usgs.gov/special-topic/water-science-school/science/surface-water-use-united-states?qt-science_center_objects=0#qt-science_center_objects
IARC. IARC monographs on the evaluation of the carcinogenic risks to humans-volume 112: some organophosphate insecticides and herbicides. IARC, World Health Organization: Lyon, France; 2017.
Benbrook CM. Trends in glyphosate herbicide use in the United States and globally. Environ Sci Eur. 2016;28(1):3.
Hanke I, Singer H, Hollender J. Ultratrace-level determination of glyphosate, aminomethylphosphonic acid and glufosinate in natural waters by solid-phase extraction followed by liquid chromatography-tandem mass spectrometry: performance tuning of derivatization, enrichment and detection. Anal Bioanal Chem. 2008;391(6):2265–76.
Ibanez M, Pozo OJ, Sancho JV, Lopez FJ, Hernandez F. Residue determination of glyphosate, glufosinate and aminomethylphosphonic acid in water and soil samples by liquid chromatography coupled to electrospray tandem mass spectrometry. J Chromatogr A. 2005;1081(2):145–55.
Ehling S, Reddy TM. Analysis of glyphosate and aminomethylphosphonic acid in nutritional ingredients and milk by derivatization with fluorenylmethyloxycarbonyl chloride and liquid chromatography-mass spectrometry. J Agric Food Chem. 2015;63(48):10562–8.
Skeff W, Recknagel C, Schulz-Bull DE. The influence of salt matrices on the reversed-phase liquid chromatography behavior and electrospray ionization tandem mass spectrometry detection of glyphosate, glufosinate, aminomethylphosphonic acid and 2-aminoethylphosphonic acid in water. J Chromatogr A. 2016;1475:64–73.
Ibanez M, Pozo OJ, Sancho JV, Lopez FJ, Hernandez F. Re-evaluation of glyphosate determination in water by liquid chromatography coupled to electrospray tandem mass spectrometry. J Chromatogr A. 2006;1134(1–2):51–5.
Gros P, Ahmed AA, Kuhn O, Leinweber P. Influence of metal ions on glyphosate detection by FMOC-Cl. Environ Monit Assess. 2019;191(4):244.
Connolly A, Leahy M, Jones K, Kenny L, Coggins MA. Glyphosate in Irish adults - a pilot study in 2017. Environ Res. 2018;165:235.
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This study received funding from the National Cancer Institute (P30 CA71789).
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Deidentified urine samples in this study were obtained from pre- and post-menopausal women, who provided written, informed consent, from a study that was approved by the University of Hawaii Office of Research Compliance and has since been discontinued. Quality control samples were pooled according to menopausal status.
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Franke, A.A., Li, X. & Lai, J.F. Analysis of glyphosate, aminomethylphosphonic acid, and glufosinate from human urine by HRAM LC-MS. Anal Bioanal Chem 412, 8313–8324 (2020). https://doi.org/10.1007/s00216-020-02966-1
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DOI: https://doi.org/10.1007/s00216-020-02966-1