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Application of electrochemical depassivation in PRB systems to recovery Fe0 reactivity |
Xin LU1,2,3,Miao LI1,Hao DENG2,3,Pengfei LIN4,Mark R. MATSUMOTO5,Xiang LIU1,*() |
1. School of Environment, Tsinghua University, Beijing 100084, China
2. CNPC Research Institute of Safety & Environmental Technology, Beijing 102206, China
3. State Key Laboratory of Petroleum and Petrochemical Pollution Control and Treatment, Beijing 102206, China
4. College of Chemical Engineering, China University of Petroleum (East China), Qingdao 266580, China
5. Department of Chemical and Environmental Engineering, University of California, Riverside, Riverside, CA 92521, USA |
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Abstract Utilizing electrochemical depassivation to recovery Fe0 activity was effective, and minerals were cleaned layer by layer, with no ions secondary contamination, and no transformation from Cr(III) to Cr(VI).
Electrochemical depassivation process under various electrolysis conditions was revealed.
Electro-PRB configuration for caisson excavation construction technique was designed.
Permeable reactive barriers (PRBs) show remarkable Cr(VI) removal performance. However, the diminished removal rate because of mineral fouling over time is the bottleneck for application of PRBs. The present study demonstrated that electrochemical depassivation was effective for recovering the Fe0 reactivity, and minerals can be cleaned layer by layer with no secondary ion contamination and no transformation from Cr(III) to Cr(VI). The removal recovery rate increased with increasing electrolysis voltage before reaching the optimal electrolysis voltage, and then decreased as the electrolysis voltage further increased. The recovery effect at electrolysis voltages of 5, 10, and 15 V show the same trend as a function of electrolysis time, where recovery rate first increased and then decreased after reaching the optimal electrolysis time. The Cr(VI) removal rate significantly decreased with increasing electrolysis distance. Furthermore, Fe0 brush meshes electrode, Fe0 fillings, and polyvinyl chloride (PVC) meshes separators were combined to create an Electro-PRB configuration for the caisson excavation construction technique, which lays the foundation for establishment of promising Electro-PRB systems to treat Cr(VI)-contaminated groundwater.
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Keywords
PRB
Cr(VI)
Fe
Passivation
Electrochemical depassivation
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Fund: |
Corresponding Author(s):
Xiang LIU
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Issue Date: 09 May 2016
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1 |
Xu B, Xu Q, Liang C, Li L, Jiang L. Occurrence and health risk assessment of trace heavy metals via groundwater in Shizhuyuan Polymetallic Mine in Chenzhou City, China. Frontiers of Environmental Science & Engineering, 2015, 9(3): 482–493
https://doi.org/10.1007/s11783-014-0675-8
|
2 |
Wei X, Guo S, Wu B, Li F, Li G. Effects of reducing agent and approaching anodes on chromium removal in electrokinetic soil remediation. Frontiers of Environmental Science & Engineering, 2016, 10(2): 253–261
https://doi.org/10.1007/s11783-015-0791-0
|
3 |
Lo I M C, Lam C S C, Lai K C K. Competitive effects of trichloroethylene on Cr(VI) removal by zero-valent iron. Journal of Environmental Engineering, 2005, 131(11): 1598–1606
https://doi.org/10.1061/(ASCE)0733-9372(2005)131:11(1598)
|
4 |
Manning B A, Kiser J R, Kwon H, Kanel S R. Spectroscopic investigation of Cr(III)- and Cr(VI)-treated nanoscale zerovalent iron. Environmental Science & Technology, 2007, 41(2): 586–592
https://doi.org/10.1021/es061721m
pmid: 17310726
|
5 |
Qafoku N P, Dresel P E, Mckinley J P, Liu C, Heald S M, Ainsworth C C, Phillips J L, Fruchter J S. Pathways of aqueous Cr(VI) attenuation in a slightly alkaline oxic subsurface. Environmental Science & Technology, 2009, 43(4): 1071–1077
https://doi.org/10.1021/es802658x
pmid: 19320160
|
6 |
Bourotte C, Bertolo R, Almodovar M, Hirata R. Natural occurrence of hexavalent chromium in a sedimentary aquifer in Urania, state of Sao Paulo, Brazil. Anais da Academia Brasileira de Ciencias, 2009, 81(2): 227–242
https://doi.org/10.1590/S0001-37652009000200009
|
7 |
Henderson A D, Demond A H. Long-term performance of zero-valent iron permeable reactive barriers: a critical review. Environmental Science & Technology, 2007, 24(4): 401–423
|
8 |
Blowes D W, Ptacek C J, Jambor J L. In-situ remediation of Cr(VI)-contaminated groundwater using permeable reactive walls: laboratory studies. Environmental Science & Technology, 1997, 31(12): 3348–3357
https://doi.org/10.1021/es960844b
|
9 |
Flury B, Eggenberger U, Maeder U. First results of operating and monitoring an innovative design of a permeable reactive barrier for the remediation of chromate contaminated groundwater. Applied Geochemistry, 2009, 24(4): 687–696
https://doi.org/10.1016/j.apgeochem.2008.12.020
|
10 |
Bang S, Korfiatis G P, Meng X. Removal of arsenic from water by zero-valent iron. Journal of Hazardous Materials, 2005, 121(1–3): 61–67
https://doi.org/10.1016/j.jhazmat.2005.01.030
pmid: 15885407
|
11 |
Kalinovich I, Rutter A, Poland J S, Cairns G, Rowe R K. Remediation of PCB contaminated soils in the Canadian Arctic: excavation and surface PRB technology. Science of the Total Environment, 2008, 407(1): 53–66
https://doi.org/10.1016/j.scitotenv.2008.08.006
pmid: 18838153
|
12 |
Simon F G, Segebade C, Hedrich M. Behaviour of uranium in iron-bearing permeable reactive barriers: investigation with 237U as a radioindicator. Science of the Total Environment, 2003, 307(1–3): 231–238
https://doi.org/10.1016/S0048-9697(02)00548-X
pmid: 12711437
|
13 |
Mishra D, Farrell J. Understanding nitrate reactions with zerovalent iron using tafel analysis and electrochemical impedance spectroscopy. Environmental Science & Technology, 2005, 39(2): 645–650
https://doi.org/10.1021/es049259y
pmid: 15707067
|
14 |
Liu T, Tsang D C W, Lo I M C. Chromium(VI) reduction kinetics by zero-valent iron in moderately hard water with humic acid: iron dissolution and humic acid adsorption. Environmental Science & Technology, 2008, 42(6): 2092–2098
https://doi.org/10.1021/es072059c
pmid: 18409642
|
15 |
Flury B, Frommer J, Eggenberger U, Mäder U, Nachtegaal M, Kretzschmar R. Assessment of long-term performance and chromate reduction mechanisms in a field scale permeable reactive barrier. Environmental Science & Technology, 2009, 43(17): 6786–6792
https://doi.org/10.1021/es803526g
pmid: 19764250
|
16 |
Lai K C K, Lo I M C. Removal of chromium (VI) by acid-washed zero-valent iron under various groundwater geochemistry conditions. Environmental Science & Technology, 2008, 42(4): 1238–1244
https://doi.org/10.1021/es071572n
pmid: 18351099
|
17 |
Lu X, Li M, Tang C, Feng C, Liu X. Electrochemical depassivation for recovering Fe0 reactivity by Cr(VI) removal with a permeable reactive barrier system. Journal of Hazardous Materials, 2012, 213– 214(7): 355–360
https://doi.org/10.1016/j.jhazmat.2012.02.007
pmid: 22386999
|
18 |
He W C, Shao H B, Chen Q Q, Wang J M, Mang J Q. Polarization characteristic of iron anode in concentrated NaOH solution. Acta Physico-Chimica Sinica, 2007, 23(10): 1525–1530
|
19 |
Melitas N, Chuffe-Moscoso O, Farrell J. Kinetics of soluble chromium removal from contaminated water by zerovalent iron media: corrosion inhibition and passive oxide effects. Environmental Science & Technology, 2001, 35(19): 3948–3953
https://doi.org/10.1021/es001923x
pmid: 11642457
|
20 |
Chen G H. Electrochemical technologies in wastewater treatment. Separation and Purification Technology, 2004, 38(1): 11–41
https://doi.org/10.1016/j.seppur.2003.10.006
|
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