N-nitrosodimethyl amine (NDMA) formation at an indirect potable reuse facility

被引:55
作者
Sgroi, Massimiliano [1 ,2 ]
Roccaro, Paolo [1 ,2 ]
Oelker, Gregg L. [3 ]
Snyder, Shane A. [2 ,4 ]
机构
[1] Univ Catania, Dept Civil Engn & Architecture, I-95125 Catania, Italy
[2] Univ Arizona, Dept Chem & Environm Engn, Tucson, AZ 85721 USA
[3] United Water, Edward C Little Water Reclamat Facil, El Segundo, CA 90245 USA
[4] Natl Univ Singapore, Environm Res Inst NERI, Singapore 117411, Singapore
基金
新加坡国家研究基金会;
关键词
Dimethylformamide; Hydrogen peroxide; UV; Ozone; Chloramination; Reverse osmosis; WASTE-WATER TREATMENT; REVERSE-OSMOSIS; NITROSAMINE FORMATION; BY-PRODUCTS; PRECURSORS; UV; UV/H2O2; OZONATION; REMOVAL; CHLORAMINATION;
D O I
10.1016/j.watres.2014.11.051
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Full-scale experiments to evaluate N-nitrosodimethylamine (NDMA) formation and attenuation were performed within an advanced indirect potable reuse (IPR) treatment system, which includes, sequentially: chloramination for membrane fouling control, microfiltration (MF), reverse osmosis (RO), ultraviolet irradiation with hydrogen peroxide (UV/H2O2), final chloramination, and pH stabilization. Results of the study demonstrate that while RO does effectively remove the vast majority of NDMA precursors, RO permeate can still contain significant concentrations of NDMA precursors resulting in additional NDMA formation during chloramination. Thus, it is possible for this advanced treatment system to produce water with NDMA levels higher than regional requirements for potable applications (10 ng/L). The presence of H2O2 during UV oxidation reduced NDMA photolysis efficiency and increased NDMA formation (similar to 22 ng/L) during the secondary chloramination and lime stabilization. This is likely due to formation of LTV/H2O2. degradation by-products with higher NDMA formation rate than the parent compounds. However, this effect was diminished with higher UV doses. Bench-scale experiments confirmed an enhanced NDMA formation during chloramination after UV/H2O2 treatment of dimethylformamide, a compound detected in RO permeate and used as model precursor in this study. The effect of pre-ozonation for membrane fouling control on NDMA formation was also evaluated at pilot- (ozone-MF-RO) and bench-scale. Relatively large NDMA formation (117-227 ng/L) occurred through ozone application that was dose dependent, whereas chloramination under typical dosages and contact times of IPR systems resulted in only a relatively small increase of NDMA (similar to 20 ng/L). Thus, this research shows that NDMA formation within a potable water reuse facility can be challenging and must be carefully evaluated and controlled. (C) 2014 Elsevier Ltd. All rights reserved.
引用
收藏
页码:174 / 183
页数:10
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