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首页> 外文期刊>Chemical engineering journal >Role of ammonia on haloacetonitriles and halonitromethanes formation during Ultraviolet irradiation followed by chlorination/chloramination
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Role of ammonia on haloacetonitriles and halonitromethanes formation during Ultraviolet irradiation followed by chlorination/chloramination

机译:氨在紫外线照射期间卤乙腈和卤代苯乙烷形成的作用,然后进行氯化/氯

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Combination of ultraviolet (UV) disinfection and chlorination became a common multi-barrier approach taken by water utilities against microbial pathogens in drinking water disinfection. Halogenated disinfection by-products (DBPs) have been monitored and regulated in drinking water under various jurisdictions around the world for decades. More recently, several nitrogenous DBPs (N-DBPs), like haloacetonitriles (HANs) and halo-nitromethanes (HNMs), have been identified in chlorinated drinking waters, whose precursors are N-containing organic compounds of various origins and structures. Rising concerns over the N-DBPs formation due to their more potent genotoxic and cytotoxic activity than the regulated carbonaceous-DBPs have prompted extensive research on drinking water disinfection processes. To examine the effect of ammonia nitrogen (NH3-N) on N-DBPs formation during UV disinfection of drinking water followed by chlorination/chloramination, as a first attempt, synthetic waters prepared by humic acid with different NH3-N concentrations were exposed to UV dose up to 300 mJ/cm(2) from either low pressure (LP) or medium pressure (MP) lamps, followed by chlorination/chloramination. To investigate trends, the study employed synthetic waters with elevated precursor concentrations and disinfectant exposures to generate significant byproduct formation possible. LP UV treatment had no obvious effect on N-DBP formation, whereas MP UV irradiation produced more dichloroacetonitrile (DCAN). The existence of ammonia (= 1 mg/L-N) increased DCAN concentration in high organics synthetic waters under varying MP UV doses, respectively. In high organics synthetic water samples exposed to a MP UV dose of 300 mJ/cm(2) DCAN reached a maximum yield of 13.7 mu g/L in the presence of 0.5 mg/L NH3-N, whereas lower yields were observed at NH3-N = 2 mg/L, i.e. 2.9 mu g/L and 1.8 mu g/L at 2 and 10 mg/L NH3-N, respectively.
机译:紫外线(UV)消毒和氯化的组合成为水实用程序对饮用水消毒中微生物病原体采取的常见多屏障方法。几十年来,已经监测并监测卤化消毒副产品(DBPS)并监测在世界各地的各种司法管辖区内的饮用水中。最近,已经在氯化饮用水中鉴定了几种含氮dbps(n-dbps),如卤代乙腈(Hans)和卤硝甲烷(HNMS),其前体是各种起源和结构的N含N个有机化合物。由于其更有效的遗传毒性和细胞毒性活性,对N-DBPS形成的担忧而不是受管制的碳酸碳酸盐毒性,促使对饮用水消毒过程进行广泛的研究。为了检查氨氮(NH3-N)在饮用水的UV消毒过程中对N-DBPS形成的影响,然后进行氯化/氯化,作为第一次尝试,用不同NH 3-N浓度的腐殖酸制备的合成水将暴露于UV从低压(LP)或中压(MP)灯,高达300mJ / cm(2),然后用氯化/氯聚酰胺。为了探讨趋势,该研究采用了前体浓度升高的合成水分和消毒曝光,以产生显着的副产品形成。 LP UV处理对N-DBP形成没有明显的影响,而MP UV照射产生更多的二氯乙腈(DCAN)。氨(& = 1mg / L-n)的存在分别在不同的MP UV剂量下分别增加了高有机合成水中的DCAN浓度。在暴露于300mJ / cm(2)的MP UV剂量下暴露于300mJ / cm(2)的合成水样品中,DCAN在0.5mg / L NH3-N存在下达到13.7μg/ L的最大收率,而在NH 3下观察到较低的收率-N& = 2mg / L,即2.9μg/ L和1.8μg/ L分别为2和10mg / L NH3-n。

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