Reverse Osmosis Shifts Chloramine Speciation Causing Re-Formation of NDMA during Potable Reuse of Wastewater

被引:68
作者
McCurry, Daniel L. [1 ,5 ]
Ishida, Kenneth P. [2 ]
Oelker, Gregg L. [3 ]
Mitch, William A. [1 ,4 ]
机构
[1] Stanford Univ, Dept Civil & Environm Engn, Stanford, CA 94305 USA
[2] Orange Cty Water Dist, Fountain Valley, CA 92708 USA
[3] Edward C Little Reclamat Facil, Suez, El Segundo, CA 90245 USA
[4] Re Inventing Nations Urban Water Infrastruct ReNU, Natl Sci Fdn, Engn Res Ctr, 473 Via Ortega, Stanford, CA 94305 USA
[5] Univ So Calif, Astani Dept Civil & Environm Engn, Los Angeles, CA 90089 USA
基金
美国国家科学基金会;
关键词
N-NITROSODIMETHYLAMINE FORMATION; DISINFECTION BY-PRODUCTS; TREATMENT PLANTS; NITROSAMINE PRECURSORS; RELATIVE IMPORTANCE; ULTRAVIOLET-LIGHT; TREATMENT TRAINS; DRINKING-WATER; SURFACE WATERS; FATE;
D O I
10.1021/acs.est.7b01641
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
UV-based advanced oxidation processes (AOPs) effectively degrade N-nitrosodimethylamine (NDMA) passing through reverse osmosis (RO) units within advanced treatment trains for the potable reuse of municipal wastewater. However, certain utilities have observed the re-formation of NDMA after the AOP from reactions between residual chloramines and NDMA precursors in the AOP product water. Using kinetic modeling and bench-scale RO experiments, we demonstrate that the low pH in the RO permeate (similar to 5.5) coupled with the effective rejection of NH4+ promotes conversion of the residual monochloramine (NH2Cl) in the permeate to dichloramine (NHCl2) via the reaction: 2 NH2Cl + H+ <-> NHCl2 + NH4+. Dichloramine is the chloramine species known to react with NDMA precursors to form NDMA. After UV/AOP, utilities generally use lime or other techniques to increase the pH of the finished water to prevent distribution system corrosion. Modeling indicated that, while the increase in pH halts dichloramine formation, it converts amine-based NDMA precursors to their more reactive, neutral forms. With modeling, and experiments at both bench-scale and field-scale, we demonstrate that reducing the time interval between RO treatment and final pH adjustment can significantly reduce NDMA re-formation by minimizing the amount of dichloramine formed prior to reaching the final target pH.
引用
收藏
页码:8589 / 8596
页数:8
相关论文
共 35 条
[1]  
[Anonymous], 1998, STANDARD METHODS EXA
[2]  
[Anonymous], 1993, Integrated risk information system
[3]  
[Anonymous], ANN PREL REG DET CON
[4]  
California Department of Public Health, 2013, NDMA OTH NITR DRINK
[6]   Fate of N-nitrosodimethylamine, trihalomethane and haloacetic acid precursors in tertiary treatment including biofiltration [J].
Farre, Maria Jose ;
Reungoat, Julien ;
Argaud, Francois Xavier ;
Rattier, Maxime ;
Keller, Juerg ;
Gernjak, Wolfgang .
WATER RESEARCH, 2011, 45 (17) :5695-5704
[7]  
Feng YG, 2007, J ENVIRON ENG SCI, V6, P277, DOI 10.1139/s06-052
[8]   Nitrosamines in pilot-scale and full-scale wastewater treatment plants with ozonation [J].
Gerrity, Daniel ;
Pisarenko, Aleksey N. ;
Marti, Erica ;
Trenholm, Rebecca A. ;
Gerringer, Fred ;
Reungoat, Julien ;
Dickenson, Eric .
WATER RESEARCH, 2015, 72 :251-261
[9]   Potable reuse treatment trains throughout the world [J].
Gerrity, Daniel ;
Pecson, Brian ;
Trussell, R. Shane ;
Trussell, R. Rhodes .
JOURNAL OF WATER SUPPLY RESEARCH AND TECHNOLOGY-AQUA, 2013, 62 (06) :321-338
[10]   Methadone Contributes to N-Nitrosodimethylamine Formation in Surface Waters and Wastewaters during Chloramination [J].
Hanigan, David ;
Thurman, E. Michael ;
Ferrer, Imma ;
Zhao, Yang ;
Andrews, Susan ;
Zhang, Jinwei ;
Herckes, Pierre ;
Westerhoff, Paul .
ENVIRONMENTAL SCIENCE & TECHNOLOGY LETTERS, 2015, 2 (06) :151-157