Simultaneous chlorine decay and disinfection byproduct (DBP) formation have been discussed extensively because of their regulatory and operational significance. This study further examines kinetic variability of the water quality changes responding to hydrodynamics in drinking water distribution. The variations of kinetic constant for overall chlorine decay (kE), trihalomethane (THM) formation were determined under a set of physiochemical and flow conditions using three devices of different wall demand and two types of natural organic matters (NOM) in water. The results from the comparative experiments and modeling analyses show the relative importance of wall demand (kw), DBP-forming chlorine decay (kD), and other bulk demand () for pipe flow Re=0–52500. It is found that chlorine reactivity of virgin NOM is the overriding factor. Secondly, for tap water NOM of lower reactivity, pipe flow properties (Re or u) can significantly affect, the THM yield (T), formation potential (Y), and the time to reach the maximum THM concentration (tmax) through their influence on kinetic ratio These observations, corroborating with turbidity variations, cannot be explained alone by chlorine dispersion to and from the pipe wall. Mass exchanges through deposition and scale detachment are most likely the other mechanism depending on the flow velocity and shear stress on pipe walls. Thus for the simultaneous occurrence of chlorine decay and DBP formation, model considerations of NOM reactivity, pipe types (wall demand), flow hydraulics, and their interactions are essential.
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机译:同时氯衰减和消毒副产物(DBP)形成已被广泛讨论,因为它们的监管和操作意义。这项研究进一步检查了响应于饮用水分配中水动力的水质变化的动力学变化。在一组理化和流动条件下,使用三种具有不同壁需求的设备和两种水中的天然有机物(NOM)来确定总氯衰减(kE),三卤甲烷(THM)形成的动力学常数变化。比较实验和模型分析的结果表明,墙面需求(kw),形成DBP的氯衰减(kD)和其他批量需求的相对重要性( k mi> b mi> '< / mo> msubsup> mrow> math>)用于管道流量Re = 0-52500。发现原始NOM的氯反应性是主要因素。其次,对于反应性较低的自来水NOM,管道流量特性(Re或u)会显着影响THM产量(T),地层势(Y)和通过其影响达到最大THM浓度(tmax)的时间。关于动能比<数学xmlns:mml =“ http://www.w3.org/1998/Math/MathML” display =“ inline” id =“ M2”溢出=“ scroll”> k mi> D mi> msub> / mo> ( mo> k mi > b mi> ' mo> msubsup> + mo> k mi> w mi> msub> mrow> ) mo> mrow> 。 mo> mrow> math>这些观察结果与浊度变化密切相关,不能单独用氯气分散到和从管壁。通过沉积和水垢分离的质量交换很可能是另一种机制,这取决于管壁上的流速和切应力。因此,对于同时发生的氯气衰减和DBP形成,必须考虑NOM反应性,管道类型(管壁需求),流动水力及其相互作用的模型考虑。
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