Assessment of degradation byproducts and NDMA formation potential during UV and UV/H2O2 treatment of doxylamine in the presence of monochloramine.

UV-C radiation is the U.S. EPA recommended technology to remove N-nitrosodimethylamine (NDMA) during drinking and recycled water production. Frequently, H(2)O(2) is added to the treatment to remove other recalcitrant compounds and to prevent NDMA reformation. However, the transformation of NDMA precursors during the UV and UV/H(2)O(2) process and the consequences for NDMA formation potential are currently not well understood, in particular in the presence of monochloramine. In this study, doxylamine has been chosen as a model compound to elucidate its degradation byproducts in the UV and UV/H(2)O(2) process and correlate those with changes to the NDMA formation potential. This study shows that during UV treatment in the presence and absence of monochloramine, NDMA formation potential can be halved. However, an increase of more than 30% was observed when hydrogen peroxide was added. Ultrafast liquid chromatography coupled to quadrupole-linear ion trap mass spectrometer was used for screening and structural elucidation of degradation byproducts identifying 21 chemical structures from the original parent compound. This work shows that further oxidation of NDMA precursors does not necessarily lead to a decrease in NDMA formation potential. Degradation byproducts with increased electron density in the vicinity of the dimethylamino moiety, for example induced by hydroxylation, may have a higher yield of nucleophilic substitution and subsequent NDMA formation compared to the parent compound during chloramination. This work demonstrates the need to consider the formation of oxidation byproducts and associated implications for the control and management of NDMA formation in downstream processes and distribution when integrating oxidative treatments into a treatment train generating either drinking water or recycled water for potable reuse.

[1]  W. Gernjak,et al.  Effect of UV and UV/H2O2 in the presence of chloramines on NDMA formation potential of tramadol. , 2012, Environmental science & technology.

[2]  A. Fernández-Alba,et al.  Photolytic and photocatalytic degradation of quinclorac in ultrapure and paddy field water: identification of transformation products and pathways. , 2012, Chemosphere.

[3]  P. K. Sinha,et al.  Degradation of 1,4-dioxane using advanced oxidation processes , 2012, Environmental Science and Pollution Research.

[4]  J. Keller,et al.  Fate of N-nitrosodimethylamine, trihalomethane and haloacetic acid precursors in tertiary treatment including biofiltration. , 2011, Water research.

[5]  S. Andrews,et al.  NDMA formation kinetics from three pharmaceuticals in four water matrices. , 2011, Water research.

[6]  Chia-Yang Chen,et al.  Performance evaluation of the UV/H2O2 process on selected nitrogenous organic compounds: reductions of organic contents vs. corresponding C-, N-DBPs formations. , 2011, Chemosphere.

[7]  J. Nawrocki,et al.  Nitrosamines and water. , 2011, Journal of hazardous materials.

[8]  K. Rabaey,et al.  Electrochemical degradation of the β-blocker metoprolol by Ti/Ru 0.7 Ir 0.3 O 2 and Ti/SnO 2-Sb electrodes. , 2011, Water research.

[9]  E. Robotti,et al.  HPLC-DAD-MSn to investigate the photodegradation pathway of nicosulfuron in aqueous solution , 2011, Analytical and bioanalytical chemistry.

[10]  J. Keller,et al.  Occurrence of N-nitrosodimethylamine precursors in wastewater treatment plant effluent and their fate during ultrafiltration-reverse osmosis membrane treatment. , 2011, Water science and technology : a journal of the International Association on Water Pollution Research.

[11]  J. Keller,et al.  Understanding the operational parameters affecting NDMA formation at Advanced Water Treatment Plants. , 2011, Journal of hazardous materials.

[12]  D. Barceló,et al.  Characterization of intermediate products of solar photocatalytic degradation of ranitidine at pilot-scale. , 2010, Chemosphere.

[13]  Jennifer Zhang,et al.  Investigation of collision-induced dissociations involving odd-electron ion formation under positive electrospray ionization conditions using accurate mass. , 2010, Rapid communications in mass spectrometry : RCM.

[14]  J. Nawrocki,et al.  N-nitrosodimethylamine formation during treatment with strong oxidants of dimethylamine containing water. , 2007, Water science and technology : a journal of the International Association on Water Pollution Research.

[15]  T. Clevenger,et al.  Prediction of N-nitrosodimethylamine (NDMA) formation as a disinfection by-product. , 2007, Journal of hazardous materials.

[16]  Jeyong Yoon,et al.  Oxidation of N-nitrosodimethylamine (NDMA) precursors with ozone and chlorine dioxide: kinetics and effect on NDMA formation potential. , 2007, Environmental science & technology.

[17]  W. Mitch,et al.  Nitrosamine formation pathway revisited: the importance of chloramine speciation and dissolved oxygen. , 2006, Environmental science & technology.

[18]  K. Linden,et al.  Polychromatic UV Fluence Measurement Using Chemical Actinometry, Biodosimetry, and Mathematical Techniques , 2006 .

[19]  Elisabeth L. Hawley,et al.  Minimization of NDMA Formation during Chlorine Disinfection of Municipal Wastewater by Application of Pre-Formed Chloramines , 2005 .

[20]  W. Mitch,et al.  Influence of the order of reagent addition on NDMA formation during chloramination. , 2005, Environmental science & technology.

[21]  David L Sedlak,et al.  Characterization and fate of N-nitrosodimethylamine precursors in municipal wastewater treatment plants. , 2004, Environmental science & technology.

[22]  David L Sedlak,et al.  A N-Nitrosodimethylamine (NDMA) precursor analysis for chlorination of water and wastewater. , 2003, Water research.

[23]  A. Catalfo,et al.  Photochemical properties of ofloxacin involved in oxidative DNA damage: a comparison with rufloxacin. , 2003, Chemical research in toxicology.

[24]  G. De Guidi,et al.  Photoinduced N-Demethylation of Rufloxacin and its Methyl Ester Under Aerobic Conditions¶ , 2002, Photochemistry and photobiology.

[25]  J. Bolton,et al.  UV direct photolysis of N-nitrosodimethylamine (NDMA): Kinetic and product study , 2002 .

[26]  J. Broekaert,et al.  Degradation of short-chain alkyl- and alkanolamines by TiO2- and Pt/TiO2-assisted photocatalysis. , 2000, Chemosphere.

[27]  André M. Braun,et al.  Photochemical processes for water treatment , 1993 .

[28]  C. Yao,et al.  Rate constants for reaction of hydroxyl radicals with several drinking water contaminants , 1992 .

[29]  R. L. Valentine,et al.  A spectrophotometric study of the formation of an unidentified monochloramine decomposition product , 1986 .

[30]  J. D. Lee,et al.  Interpretation of mass spectra. , 1973, Talanta.

[31]  Susan A Andrews,et al.  Demonstration of 20 pharmaceuticals and personal care products (PPCPs) as nitrosamine precursors during chloramine disinfection. , 2011, Water research.

[32]  E. R. Blatchley,et al.  UV photodegradation of inorganic chloramines. , 2009, Environmental science & technology.

[33]  DRAFT For Review Only Public Health Goal for N-Nitrosodimethylamine in Drinking Water , 2006 .

[34]  R. Al-awar,et al.  Pyridines and their Benzo Derivatives: Reactivity at the Ring , 1996 .

[35]  R. Zepp,et al.  Reactive Oxygen Species in Natural Waters , 1995 .