Long-term performance monitoring for a permeable reactive barrier at the US Coast Guard Support Center, Elizabeth City, North Carolina

被引:166
作者
Puls, RW [1 ]
Blowes, DW
Gillham, RW
机构
[1] US EPA, Natl Risk Management Res Lab, Subsurface Protect & Remediat Div, Ada, OK USA
[2] Univ Waterloo, Waterloo, ON N2L 3G1, Canada
关键词
permeable reactive barrier; cis-dichloroethylene; trichloroethylenc; chromium;
D O I
10.1016/S0304-3894(99)00034-5
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
A continuous hanging iron wall was installed in June, 1996, at the U.S. Coast Guard (USCG) Support Center near Elizabeth City, NC, United States, to treat overlapping plumes of chromate and chlorinated solvent compounds. The wall was emplaced using a continuous trenching machine whereby native soil and aquifer sediment was removed and the iron simultaneously emplaced in one continuous excavation and fill operation. To date, there have been seven rounds (November 1996, March 1997, June 1997, September 1997, December 1997, March 1998, and June 1998) of performance monitoring of the wall. At this time, this is the only full-scale continuous 'hanging' wall installed as a permeable reactive barrier to remediate both chlorinated solvent compounds and chromate in groundwater. Performance monitoring entails the following: sampling of 10-5 cm PVC compliance wells and 15 multi-level samplers for the following constituents: TCE, cis-dichloroethylene (c-DCE), vinyl chloride, ethane, ethene, acetylene, methane, major anions, metals, Cr(VI), Fe(II), total sulfides, dissolved H(2), Eh, pH, dissolved oxygen, specific conductance, alkalinity, and turbidity. Electrical conductivity profiles have been conducted using a Geoprobe(TM) to verify emplacement of the continuous wall as designed and to locate upgradient and downgradient wall interfaces for coring purposes. Goring has been conducted in November, 1996, in June and September, 1997, and March, 1998, to evaluate the rate of corrosion on the iron surfaces, precipitate buildup (particularly at the upgradient interface), and permeability changes due to wall emplacement. In addition to several continuous vertical cores, angled cores through the 0.6-m thick wall have been collected to capture upgradient and downgradient wall interfaces along approximate horizontal flow paths for mineralogic analyses. (C) 1999 Elsevier Science B.V. All rights reserved.
引用
收藏
页码:109 / 124
页数:16
相关论文
共 10 条
[1]  
Blowes DW, 1995, GEOTECH SP, P1588
[2]  
CHAPELLE FH, ENV SCI TECHNOL, V30, P3585
[3]   ENHANCED DEGRADATION OF HALOGENATED ALIPHATICS BY ZERO-VALENT IRON [J].
GILLHAM, RW ;
OHANNESIN, SF .
GROUND WATER, 1994, 32 (06) :958-967
[4]   COUPLED IRON CORROSION AND CHROMATE REDUCTION - MECHANISMS FOR SUBSURFACE REMEDIATION [J].
POWELL, RM ;
PULS, RW ;
HIGHTOWER, SK ;
SABATINI, DA .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1995, 29 (08) :1913-1922
[5]  
Puls R. W., 1994, Journal of Soil Contamination, V3, P203, DOI 10.1080/15320389409383463
[6]  
PULS RW, 1995, EPA540S95504
[7]  
PULS RW, 1995, AM CHEM SOC ANN M EX, P788
[8]   Reductive elimination of chlorinated ethylenes by zero valent metals [J].
Roberts, AL ;
Totten, LA ;
Arnold, WA ;
Burris, DR ;
Campbell, TJ .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1996, 30 (08) :2654-2659
[9]  
Sabatini D.A., 1997, EPA600S97005
[10]  
USEPA, 1997, EPA600F97008