Page 8 - Shimadzu Journal vol.2 Issue1
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Human Health




            being reported in a study of human exposure to BPA through   4. Conclusion
            drinking water.  An example of the analysis of BPA in type I   A fast and sensitive UHPLC-MS-MS method was developed for the
                       15
            purified laboratory water is shown in Fig. 4. It should be noted   quantitative analysis of BPA in water and BPA and its major
            that even many laboratory water purification systems produce   metabolite BPA-G in serum. Unlike GC-MS-MS assays, BPA may be
            water contaminated with BPA, since they often contain   measured using UHPLC-MS-MS without derivatization, and BPA-G
            polysulfone filters that leach BPA monomer. 12     may be measured directly without hydrolysis to BPA and then
                                                               derivatization. These advantages simplify analysis and shorten
                                                               sample preparation times. Compared with previous LC-MS-MS
                                                               assays for BPA and BPA-G, the new UHPLC-MS-MS assay takes
                                                               only 3.5 min (approximately 4-fold faster than HPLC-MS-MS) and
                                                               requires only 25 µL serum instead of 500 µL or more. Simpler
                                                               sample preparation, faster analysis and smaller sample sizes will
                                                               enable biological and environmental studies of the effects of BPA
                                                               to be carried out more efficiently than was possible previously.

                                                               Acknowledgements
                                                               We would like to thank Dr. Gail Prins of the University of Illinois
                                                               College of Medicine for providing the serum samples and Dr. Amy
                                                               Luke of Loyola University Chicago for providing water samples.
                                                               We thank Mr. Zane Hauck for assistance with sample preparation
                                                               and Shimadzu for making the Nexera and LCMS-8050 instruments
                Fig. 4. Negative ion electrospray UHPLC-MS-MS   available for these studies.
                      analysis of a system blank and BPA in type I
                      high purity laboratory water.
                                                               5. References
                                                                1.  L.N. Vandenberg, R. Hauser, M. Marcus, N. Olea, W.V.
            Our method for measuring BPA and BPA-G in serum was applied
            to an on-going study of in utero and neonatal exposures of mice   Welshons. Reprod Toxicol, 2007, 24, 139–177
            and rats to BPA. The need for a method that utilizes small volumes   2.  E. Teuten, J. Saquing, D. Knappe et al. Philos Trans R Soc Lond
                                                   5
            of serum was prompted by studies such as Prins et al.  that had to   B Biol Sci, 2009, 364, 2027–2045.
            pool sera from 8 to 10 rat pups to obtain 500 µL serum for a   3.  J.R. Rochester. Reprod Toxicol. 2013, 42C,132-155.
            single analysis of unconjugated BPA and then another 500 µL   4.  L.N. Vandenberg, I. Chahoud, J.J. Heindel, V. Padmanabhan,
            serum for analysis of total BPA (after hydrolysis of BPA-G). In our   F.J. Paumgartten, G. Schoenfelder. Environ Health Perspect.
            study, 25 µL serum from a single mouse was analyzed for both   2010, 118, 1055-70.
            BPA and BPA-G as shown in Fig. 5.                   5.  G.S. Prins, S.H. Ye, L. Birch, S.M. Ho, K. Kannan K. Reprod
                                                                  Toxicol. 2011, 31, 1-9.
                                                                6.  M.J. Rocha, C. Cruzeiro, E. Rocha. J. Water Health, 2013, 11,
                                                                  281-96.
                                                                7.  M. Di Carro, C. Scapolla, C. Liscio, E. Magi. Anal. Bioanal.
                                                                  Chem. 2010, 398, 1025-1034.
                                                                8.  W.L. Chen, G.S. Wang, J.C. Gwo, C.Y. Chen. Talanta. 2012,
                                                                  89, 237-245.
                                                                9.  I. Kosarac, C. Kubwabo, K. Lalonde, W. Foster. J. Chromatogr.
                                                                  B Analyt. Technol. Biomed. Life Sci. 2012, 898, 90-94.
                                                               10.  J.L. Coughlin, B. Winnik, B. Buckley. Anal. Bioanal. Chem.
                                                                  2011, 401, 995-1002.
                                                               11.  M.Z. Lacroix, S. Puel, S.H. Collet, T. Corbel, N. Picard-Hagen,
                                                                  P.L. Toutain, C. Viguié, V. Gayrard. Talanta, 2011, 85,
                                                                  2053-2059.
 The lower limit of quantitation for BPA in water was 0.01 ng/mL,   Fig. 5. UHPLC-MS-MS with negative ion electrospray and SRM   12.  Y.S. Choi, S. Cho, C. Lee, H.M. Luu, J. Guo. Talanta, 2012,
 and the lower limits of quantitation for BPA and BPA-G in mouse   analysis of BPA (retention time 1.52 min) and BPA-G   94, 353-355.
 serum were 0.5 ng/mL and 0.2 ng/mL, respectively. Although   (retention time 1.04 min) in mouse serum after receiving   13.  R.R. Gerona, T.J. Woodruff, C.A. Dickenson, J. Pan, J.M.
 these LLOQ values for BPA and BPA-G in serum are not the lowest   dose of vegetable oil vehicle as a control (top) or in mouse   Schwartz, S. Sen, M. Friesen, V.Y. Fujimoto, P.A. Hunt
 in the literature, the serum sample size used in our experiments   serum after administration of oil containing 10 µg/kg BPA   Environ. Sci. Technol. DOI: 10.1021/es402764d 13 Aug 2013.
 (25 µL) was at least 10-fold smaller than previous methods. For   (bottom).  14.  P.V. Karalius, J.E. Harbison, R.B. van Breemen, G. Li, K. Huang,
 13
 example, using UHPLC-MS-MS Gerano et al . reported  an LLOQ      N. Mora, L.R. Dugas, L. Vail, N.C. Tuchman, T. Forrester, J.
 of 0.1 for both BPA and BPA-G in serum using a sample size of    Plange-Rhule, A. Luke. Environ. Health Insights, in press.
 250 µL serum. Therefore, on a sample size basis, our method is as
 sensitive as any in the literature.
 The method for measuring BPA in water was applied to the
 analysis of drinking water and surface water samples from the
 Chicago area, Jamaica and Ghana. BPA in water in these samples
 ranged from none detected to up to 0.186 ng/mL. These data are


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