Photodegradation of N-nitrosodiethylamine in water with UV irradiation

Factors affecting ultraviolet irradiation/hydrogen peroxide (UV/H2O2) degradation of mixed N-nitrosamines in water

Disinfection by-products (DBPs) are a great challenge to our drinking water security. Particularly, nitrosamines (NAms), as emerging DBPs, are potently carcinogenic, mutagenic, and teratogenic, and have increasingly attained public attention. This study was to evaluate the performance of the NAms degradation by the ultraviolet (UV) irradiation (253.7 nm) in the presence of hydrogen peroxide (H(2)O(2)). In the UV/H(2)O(2) system, hydroxyl radicals (OH), a type of nonselective and powerful oxidant, was produced to attack the molecules of NAms. Factors affecting the treatment efficiency, including the H(2)O(2) dosage, initial NAms concentration, UV irradiation intensity, initial solution pH, and inorganic anions present in water, were evaluated. All the NAms degradation exhibited a pseudo-first-order kinetics pattern. Within 60 min, 0.1 mg/L of any NAms could be almost decomposed except NDPhA that required 120 min for complete removal, at 25 μmol/L H(2)O(2) and at initial pH 7. Results demonstrate that the UV/H(2)O(2) treatment is a viable option to control NAms in water.

Progress towards the characterisation of faecal compounds

Intestinal nitrosation produces ATNCs (Apparent Total N-nitroso Compounds) and these have been linked with an increased risk of colon cancer from eating red meat. Modern LC-MS instrumentation makes direct detection of ATNC components in faecal water a possibility. The difficulty is in determining which of the many compounds present are N-nitrosamines before embarking on efforts to characterise them. We have assumed that any in vivo nitrosation of alimentary tract contents will be non-specific and depend on the amount and basicity of amine present, with concentration of nitrosating agent being the limiting factor. By further nitrosating faecal waters (and ileostomy fluids) we can increase the amount of ATNC and readily access these compounds. The amount and the number of nitrosamines generated depend on the concentration of individual amines present. By derivatisation separately using both 14N and 15N labelled nitrite, we demonstrated that inspecting chromatograms in parallel for a unit mass difference provides a novel and practicable means for identifying unknown ATNC in faecal and ileostomy samples. MS procedures were linked with the traditional approaches of thermal energy analyser (TEA), preparative HPLC, visualisation of nitrosamines with Griess reagent and degradation of N-nitroso compounds by UV irradiation. We have demonstrated that this approach is repeatable and have used it to identify 30 putative N-nitroso compounds (as protonated parent masses [M + H]+ at: 242, 258, 312, 313, 333, 348, 365, 377, 382, 386, 392, 412, 414, 421, 434, 442, 466, 467, 483, 493, 572, 582, 625, 636, 637, 656, 662, 752, 808, and 870.