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Permeable Reactive Wall Remediation of Chlorinated Hydrocarbons
in Groundwater |
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Objective:
This ESTCP project monitored and evaluated the performance
of a funnel-and-gate permeable reactive wall and its ability
to remediate groundwater contaminated with chlorinated solvents
including trichloroethylene (TCE), perchloroethylene (PCE),
and cis-1,2 dichloroethene (DCE). The reactive wall was installed
at the former NAS Moffett Field, California, by the U.S. Navy
Engineering Field Activity West in April 1996, and the Naval
Facilities Engineering Services Center (NFESC) subsequently
conducted the performance and cost evaluations. The permeable
reactive wall is an innovative in-situ technology in which
a reactive cell, typically composed of granulated iron, is
emplaced across the contaminated plume. As the contaminants
flow through the cell, an abiotic chemical reduction reaction
occurs between zero-valent iron and the chlorinated hydrocarbons,
which produces less toxic, readily biodegradable by-products,
including non-chlorinated hydrocarbons and chloride, iron,
and hydroxide ions.
Results:
The reactive cell has consistently reduced groundwater concentrations
of PCE (2,900 ug/L), TCE (26 ug/L) cis-1,2-DCE (280
ug/L), and vinyl chloride (4 ug/L) to well below their respective
drinking water maximum contaminant levels (MCLs) or to non-detect
within the first few feet of the iron cell, without contributing
significant levels of dissolved by-products . Although calcium
and iron compounds were observed to be precipitating in the
reactive cell, there was no apparent detrimental effect on
hydraulic performance during the 20-month demonstration period.
Water level measurements and bromide tracer tests showed that
flow patterns through the reactive cell were heterogeneous,
with more flow apparent through the deeper portions of the
cell. Linear velocities were lower than expected from previous
site characterization (pumping tests) and modeling, and equated
to a 3-12 day residence time (0.5 to 1.5 ft/day flow velocities).
Benefits:
The estimated capital cost for a full-scale system at Moffett
Field was $4.9 million, with an annual operating cost of $70K
(monitoring) and an assumed iron replacement cost of $270K
every 10 years. Although the initial capital investment is
higher, the overall costs would be less than the conventional
pump-and-treat option after about 6-8 years of operation,
with cost savings ranging from 29% to 64% for a 20- to 30-year
remediation period. Over 2,000 U.S. Department of Defense
(DoD) sites are contaminated with chlorinated compounds, and
implementation of reactive wall systems could potentially
save the DoD millions of dollars annually.
Implications:
Although the technology is ready for field use, permeable
reactive walls must be carefully designed on a case-by-case
basis for: (1) contaminant type and concentration; (2) size
of plume; (3) groundwater velocity; (4) aquifer geochemistry;
and (5) geotechnical considerations. Results from this demonstration
indicated that the targeted groundwater was being captured
and treated by the reactive barrier, although the iron cell
was over-designed to treat greater than expected linear flows
with a shorter residence time. Estimation of long-term maintenance
costs is uncertain because the longevity of field systems
and their hydraulic performance may be compromised by chemical
precipitation build-up. General maintenance techniques for
the replacement of the reactive cell have not yet been established. (Project Completed - 1999)
References:
- Battelle Memorial Institute, Columbus, OH. Report prepared
for the Naval Facilities Engineering Service Center. Field
Tracer Application to Evaluate the Hydraulic Performance
of the Pilot-Scale Permeable Barrier at Moffett Federal
Airfield. February 1998.
- Battelle Memorial Institute, Columbus, OH. Report prepared
for the Naval Facilities Engineering Service Center. Performance
Evaluation of a Pilot-Scale Permeable Reactive Barrier
at Former Naval Air Station Moffett Field, Mountain View,
CA. November 1998.
- ESTCP
Cost and Performance Report. July 1999 (PDF File Format)
- Gavaskar, A, N. Gupta, B. Sass, T. Fox, and R. Jonosy
(Battelle Memorial Institute, Columbus, OH). Design
Guidance for Application of Permeable Barriers to Remediate
Dissolved Chlorinated Solvents. February 1997. DTIC
ADA 326450.
- Interstate Technology and Regulatory Cooperation. Regulatory
Guidance for Permeable Reactive Barriers Designed to Remediate
Chlorinated Solvents. 2nd Edition. December 1999.
Web site www.itrcweb.org/pbw_1.pdf.
- Remediation Technologies Development Forum. Web site
www.rtdf.org/barriers.htm.
ESTCP
Point of Contact:
Program
Manager, Cleanup
ESTCP Program Office
901 North Stuart Street, Suite 303
Arlington, VA 22203
Telephone: (703) 696-2118
Fax: (703) 696-2114
E-mail: Cleanup@estcp.org
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