Reduction of N-nitrosodimethylamine with granular iron and nickel enhanced iron.: 1.: Pathways and kinetics

被引:118
作者
Gui, L [1 ]
Gillham, RW [1 ]
Odziemkowski, MS [1 ]
机构
[1] Univ Waterloo, Dept Earth Sci, Waterloo, ON N2L 3G1, Canada
关键词
D O I
10.1021/es9909778
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Laboratory batch and column tests were conducted to examine the reduction pathways and kinetics of N-nitrosodimethylamine (NDMA) by iron (Fe) and nickel-enhanced iron (Ni/Fe). A decrease in NDMA concentration and increases in dimethylamine (DMA) and ammonium were observed in both Fe and Ni/Fe columns. In the Fe column, the transformation process of NDMA appeared to follow pseudo-first-order kinetics with respect to NDMA, with an average half-life of 13+/-2 h. A small amount of nickel (0.25%) plated onto the iron greatly enhanced NDMA transformation rates. At early time the NDMA half-life in the Ni/Fe column was 2 min but as time progressed the half-life increased to 4 min, and departures from first-order kinetics were observed. The mass balances of carbon in DMA and nitrogen in DMA and ammonium improved over time and reached 100% and 90%, respectively, after NDMA had passed through the column for more than 50 pore volumes (PV). No 1,1-dimethylhydrazine, nitrous oxide, or methane were detected. Based on the electrochemical properties of NDMA, the transformation mechanism of NDMA with Fe and Ni/Fe is postulated to be catalytic hydrogenation, resulting in N-N bond breakdown to form DMA and ammonium as final products. Nickel, being a much stronger catalyst than Fe for catalytic hydrogenation, resulted in a much faster reduction rate of NDMA. Of several methods tested, flushing the Ni/Fe column with 0.01 N sulfuric acid proved to be the most effective in restoring the Ni/Fe activity. The rapid transformation rate on Ni/Fe and the formation of nontoxic products indicate that this material may be applicable for treating NDMA contaminated water, both in-situ and above ground.
引用
收藏
页码:3489 / 3494
页数:6
相关论文
共 39 条
[1]  
Budavari S., 1996, MERCK INDEX, V12th
[2]  
CHENG IF, 1997, 213 NAT M AM CHEM SO, P165
[3]   Hydrocarbon formation in metallic iron/water systems [J].
Deng, BL ;
Campbell, TJ ;
Burris, DR .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1997, 31 (04) :1185-1190
[4]   METAL-ASSISTED REACTIONS .2. RAPID REDUCTION OF N-NITROSOAMINES TO N,N-DISUBSTITUTED HYDRAZINES - THE UTILITY OF SOME LOW-VALENT TITANIUM REAGENTS [J].
ENTWISTLE, ID ;
WILBY, AH ;
JOHNSTONE, RAW .
TETRAHEDRON, 1982, 38 (03) :419-423
[5]   Understanding the mechanism of uranium removal from groundwater by zero-valent iron using X-ray photoelectron spectroscopy [J].
Fiedor, JN ;
Bostick, WD ;
Jarabek, RJ ;
Farrell, J .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1998, 32 (10) :1466-1473
[6]   Removal of N-nitrosodimethylamine from waters using physical-chemical techniques [J].
Fleming, EC ;
Pennington, JC ;
Wachob, BG ;
Howe, RA ;
Hill, DO .
JOURNAL OF HAZARDOUS MATERIALS, 1996, 51 (1-3) :151-164
[7]  
FREIFELDER M, 1978, CATALYTIC HYDROGENAT, P26
[8]   ENHANCED DEGRADATION OF HALOGENATED ALIPHATICS BY ZERO-VALENT IRON [J].
GILLHAM, RW ;
OHANNESIN, SF .
GROUND WATER, 1994, 32 (06) :958-967
[9]   The electrocatalytic reduction of NO3- on Pt, Pd and Pt+Pd electrodes activated with Ge [J].
Gootzen, JFE ;
Peeters, PGJM ;
Dukers, JMB ;
Lefferts, L ;
Visscher, W ;
vanVeen, JAR .
JOURNAL OF ELECTROANALYTICAL CHEMISTRY, 1997, 434 (1-2) :171-183
[10]   Reductive precipitation of uranium(VI) by zero-valent iron [J].
Gu, B ;
Liang, L ;
Dickey, MJ ;
Yin, X ;
Dai, S .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1998, 32 (21) :3366-3373