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| 1 | Evaluation of disinfection byproducts for their ability to affect mitochondrial function显示文摘In the race to deliver clean water to communities through potable water reuse, disinfection and water quality assessment are and will continue to be fundamental factors. There are over 700 disinfection byproducts(DBPs) in water;evaluating each compound is practically impossible and very time consuming. A bioanalytical approach could be an answer to this challenge. In this work, the response of four major classes of DBPs toward mitochondrial membrane potential( Δψm) and cytoplasmic adenosine triphosphate(C-ATP) was investigated with human carcinoma(Hep G2) cells. Within 90 min of cell exposure, only the haloacetic acid(HAA) mixture caused a cytotoxic response as measured by C-ATP. All four groups(haloacetonitriles(HANs), trihalomethanes(THMs), nitrosamines(NOAs), and HAAs) responded well to Δψm, R 2 > 0.70. Based on the half-maximum concentration that evoked a 50% response in Δψm, the response gradient was HANs >> HAAs ~ THM > NOAs. The inhibition of the Δψm by HANs is driven by dibromoacetonitrile(DBAN), while dichloroacetonitrile(DCAN) did not cause a significant change in the Δψm at less than 2000 μM. A mixture of HANs exhibited an antagonistic behavior on the Δψm compared to individual compounds. If water samples are concentrated to increase HAN concentrations, especially DBAN, then Δψm could be used as a biomonitoring tool for DBP toxicity. | George William Kajjumba Rachael E.Bokota Matias Attene-Ramos Erica J.Marti | 2022 | Journal of Environmental Sciences2022，34，7： | 1 |
| 2 | Kinetics of hydrogen peroxide quenching following UV/H_(2)O_(2)advanced oxidation by thiosulfate,bisulfite,and chlorine in drinking water treatment显示文摘Residual H_(2)O_(2)from UV/H_(2)O_(2)treatment can be quenched by thiosulfate,bisulfite,and chlorine,but the kinetics of these reactions have not been reported under the full range of practical conditions.In this study,the rates of H_(2)O_(2)quenching by these compounds were compared in different water matrices,temperatures,pH,and when using different forms of bisulfite and chlorine.In general,it was confirmed that thiosulfate would be too slow to serve as a quenching agent in most practical scenarios.At pH 7-8.5,chlorine tends to quench H_(2)O_(2)more than 20 times faster than bisulfite in the various conditions tested.An important observation was that in lightly-buffered water(e.g.,alkalinity of 20 mg/L as CaCO_(3)),the form of chlorine can have a large impact on quenching rate,with gaseous chlorine slowing the reaction due to its lowering of the pH,and hypochlorite having the opposite effect.These impacts will become less significant when water buffer capacity(i.e.,alkalinity)increases(e.g.,to 80 mg/L as CaCO_(3)).In addition,water temperature should be considered as the time required to quench H_(2)O_(2)by chlorine at 4℃is up to 3 times longer than at 20℃. | Tianyi Chen Lizbeth Taylor-Edmonds Susan Andrews Ron Hofmann | 2023 | Frontiers of Environmental Science & Engineering2023，17，12： | 0 |
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