Fe(0) nanoparticles for nitrate reduction: Stability, reactivity, and transformation

被引:244
作者
Sohn, Kyounghee
Kang, Sung Wook
Ahn, Samyoung [1 ]
Woo, Myungwu
Yang, Seong-Koo
机构
[1] Sunchon Natl Univ, Dept Environm Educ, Sunchon 540742, Jeonnam, South Korea
[2] Sunchon Natl Univ, Dept Chem Engn, Sunchon 540742, Jeonnam, South Korea
[3] Kyungnam Univ, Ctr Instrumental Anal, Masan 631701, South Korea
关键词
D O I
10.1021/es0525758
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The pyrophoric character of zerovalent iron nanoparticles and cumbersome handling of this material has been a drawback in practical applications, despite the expectation of an enhanced reactivity. We have been interested in how the iron nanoparticles can gain stability in air without significantly sacrificing reactivity. The freshly synthesized iron nanoparticles ignited spontaneously upon exposure to air. However, when exposed slowly to air, an similar to 5nm coating of iron oxide was formed on the surface of particles. The oxide shell did not thicken for at least two months, indicating no sign of further corrosion of iron particles. The reactivity studies on nitrate reduction showed that the freshly synthesized iron reacted at the fastest rate. After formation of the oxide shell the rate constants decreased by ca. 50% of that of fresh iron, but were still higher than that of commercial grade micro- or milli-sized iron powder. Nitrate (50 ppm/350 mL) can be recharged 6 times into a bottle containing 0.5 g of iron nanoparticles. The reduction rate of the second cycle was the fastest among the six cycles, which can be attributed to the increase of surface area and the fresh iron surfaces that were bared by the dissolution of oxidized iron species on the surface. The oxidized iron was transformed to crystalline magnetite (Fe3O4) in solution.
引用
收藏
页码:5514 / 5519
页数:6
相关论文
共 28 条
[1]  
Ahn S. Y., 2001, J KOREAN CHEM SOC, V45, P395
[2]   Kinetics of nitrate, nitrite, and Cr(VI) reduction by iron metal [J].
Alowitz, MJ ;
Scherer, MM .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2002, 36 (03) :299-306
[3]   Passivated iron as core-shell nanoparticles [J].
Carpenter, EE ;
Calvin, S ;
Stroud, RM ;
Harris, VG .
CHEMISTRY OF MATERIALS, 2003, 15 (17) :3245-3246
[4]   Kinetics of reductive denitrification by nanoscale zero-valent iron [J].
Choe, S ;
Chang, YY ;
Hwang, KY ;
Khim, J .
CHEMOSPHERE, 2000, 41 (08) :1307-1311
[5]  
Clesceri L.S., 1998, STANDARD METHODS EXA, P4, DOI DOI 10.1016/J.AQUACULTURE.2003.12.024
[6]  
Cornell R.M., 1996, IRON OXIDES, P314
[7]  
CORNELL RM, 1996, IRON OXIDES, P166
[8]   The effects of electron donor and granular iron on nitrate transformation rates in sediments from a municipal water supply aquifer [J].
Devlin, JF ;
Eedy, R ;
Butler, BJ .
JOURNAL OF CONTAMINANT HYDROLOGY, 2000, 46 (1-2) :81-97
[9]   Dechlorination of the chloroacetanilide herbicides alachlor and metolachlor by iron metal [J].
Eykholt, GR ;
Davenport, DT .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1998, 32 (10) :1482-1487
[10]   Investigation of the long-term performance of zero-valent iron for reductive dechlorination of trichloroethylene [J].
Farrell, J ;
Kason, M ;
Melitas, N ;
Li, T .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2000, 34 (03) :514-521