In 2001, two potential disinfection by-products (DBPs) were tentatively identified as 1-aminoxy-1-chlorobutan-2-ol (DBP-A) and its bromo analogue (DBP-B) (Taguchi 2001). Subsequently it became clear, by consulting an updated version of the NIST database, that their mass spectra are close to those of the halohydrins 4-chloro-2-methylbutan-2-ol and 3-bromo-2-methylbutan-2-ol. To establish the structures of these DBPs, additional mass spectrometric experiments, including Fourier transform ion cyclotron resonance (FTICR), were performed on treated drinking water samples and authentic halohydrin standards. It appears that DBP-A is 3-chloro-2-methylbutan-2-ol and that DBP-B is its bromo analogue. DBP-B has been detected in ozonated waters containing bromide. Our study also shows that these DBPs can be laboratory artefacts, generated by the reaction of residual chlorine in the sample with 2-methyl-2-butene, the stabilizer in the CH2Cl2 used for extraction. This was shown by experiments using CH2Cl2 stabilized with deuterium labelled 2-methyl-2-butene. Quenching any residual chlorine in the drinking water sample with sodium thiosulfate minimizes the formation of these artefacts. 1. Introduction Since its inception in the late 19th century, drinking water disinfection has been one of the most important advancements for public health. While disinfectants such as chlorine, ozone, chloramines, and chlorine dioxide are used to kill harmful microorganisms, an unintended consequence is the formation of the so-called disinfection by-products (DBPs), which arise from the degradation of natural organic matter by the disinfectants [1, 2]. It is now widely known that DBPs, such as the two most common classes of DBPs, the trihalomethanes (THMs) and the haloacetic acids (HAAs), are associated with long-term health risks [3, 4]. The Ontario Ministry of the Environment (MOE) has been monitoring raw and treated drinking water as part of the Drinking Water Surveillance Program (DWSP) since 1986. Target compound analyses include THMs and HAAs. To complement these target compound analyses, gas chromatography-mass spectrometry (GC-MS) is routinely used to characterize a broad range of organic compounds, including DBPs, which may also be present in drinking water but whose identity has not yet been established. More than ten years ago, two unexpected disinfection by-products, a chloro compound labelled DBP-A, and a bromo analogue DBP-B, were being detected. Their electron ionization (EI) mass spectra were not available in the NIST98 database. On the basis of various mass
References
[1]
S. D. Richardson, “Disinfection by-products and other emerging contaminants in drinking water,” Trends in Analytical Chemistry, vol. 22, no. 10, pp. 666–684, 2003.
[2]
C. Zwiener and S. D. Richardson, “Analysis of disinfection by-products in drinking water by LC-MS and related MS techniques,” Trends in Analytical Chemistry, vol. 24, no. 7, pp. 613–621, 2005.
[3]
S. D. Richardson, “New disinfection by-product issues: emerging DBPs and alternative routes of exposure,” Global Nest Journal, vol. 7, no. 1, pp. 43–60, 2005.
[4]
S. D. Richardson, “Water analysis: emerging contaminants and current issues,” Analytical Chemistry, vol. 81, no. 12, pp. 4645–4677, 2009.
[5]
V. Y. Taguchi, “Structural elucidation of disinfection by-products in treated drinking water,” Rapid Communications in Mass Spectrometry, vol. 15, no. 7, pp. 455–461, 2001.
[6]
F. W. McLafferty and F. Turecek, Interpretation of Mass Spectra, chapter 9, University Science Books, South Orange, NJ, USA, 4th edition, 1993.
[7]
K. J. Jobst, P. J. A. Ruttink, and J. K. Terlouw, “The remarkable dissociation chemistry of 2-aminoxyethanol ions NH2OCH2CH2OH+ studied by experiment and theory,” International Journal of Mass Spectrometry, vol. 269, no. 3, pp. 165–176, 2008.
[8]
K. J. Jobst, S. Jogee, R. D. Bowen, and J. K. Terlouw, “A mechanistic study of the prominent loss of H2O from ionized 2-hydroxyaminoethanol,” International Journal of Mass Spectrometry, vol. 306, no. 2-3, pp. 138–149, 2011.
[9]
T. W. Collette, S. D. Richardson, and A. D. Thruston Jr., “Identification of bromohydrins in ozonated waters,” Applied Spectroscopy, vol. 48, no. 10, pp. 1181–1192, 1994.
[10]
J. E. Cavanagh, H. S. Weinberg, A. Gold et al., “Ozonation byproducts: identification of bromohydrins from the ozonation of natural waters with enhanced bromide levels,” Environmental Science and Technology, vol. 26, no. 8, pp. 1658–1662, 1992.
[11]
G. M. Bennett and W. G. Philip, “CCLIII.—the influence of structure on the solubilities of ethers. Part II. Some cyclic ethers,” Journal of the Chemical Society, pp. 1937–1942, 1928.
[12]
H. F. van Garderen, P. J. A. Ruttink, P. C. Burgers, G. A. McGibbon, and J. K. Terlouw, “Aspects of the CH5N2 potential energy surface: ions CH3NHNH+, CH3NNH2?+ and CH2NHNH2?+ and radicals CH2NHNH2 studied by theory and experiment,” International Journal of Mass Spectrometry and Ion Processes, vol. 121, no. 3, pp. 159–182, 1992.
[13]
F. C. Whitmore, C.S. Rowland, S. N. Wrenn, and G. W. Kilmer, “The dehydration of alcohols. XIX. t-Amyl alcohol and the related dimethylneopentylcarbinol,” Journal of the American Chemical Society, vol. 64, no. 12, pp. 2970–2972, 1942.
[14]
J. B. Westmore and M. M. Alauddin, “Ammonia chemical ionization mass spectrometry,” Mass Spectrometry Reviews, vol. 5, pp. 381–465, 1986.
[15]
J. L. Holmes, C. Aubry, and P. M. Mayer, Assigning Structures to Ions in Mass Spectrometry, CRC Press, Boca Raton, Fla, USA, 2007.
[16]
Y. Xie and D. A. Reckhow, “Formation of halogenated artifacts in brominated, chloraminated, and chlorinated solvents,” Environmental Science and Technology, vol. 16, no. 7, pp. 1357–1360, 1994.