Technology Status Report: In Situ Flushing - CLU-IN
Technology Status Report: In Situ Flushing - CLU-IN
Technology Status Report: In Situ Flushing - CLU-IN
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<strong>In</strong> <strong>Situ</strong> <strong>Flushing</strong> Project Summaries<br />
GWRTAC Case Study Database<br />
GWRTAC ID: FLSH0030<br />
Project Name: Montana Pole & Treating, Butte, MT<br />
City: Butte State/Province: MT<br />
Primary GWRTAC Personal<br />
Communication Source<br />
(Name/Organization):<br />
Project Summary:<br />
Neil Marsh<br />
Montana DEQ<br />
<strong>Report</strong>(s)/Publication(s) (GWRTAC Source):<br />
U.S. EPA, Nov. 1996: <strong>In</strong>novative Treatment Technologies: Annual <strong>Status</strong> <strong>Report</strong> (Eighth Edition),<br />
EPA 542-R-96-010, Number 8, U.S. EPA OSWER (5102G) TIO, Washington, DC<br />
<strong>In</strong>ternet URL http://www.epa.gov.superfund.htm<br />
The following text is from notes from a July 1998 conversation with the Montana DEQ RPM:<br />
The site has 10-15 acres of pentachlorophenol (PCP)-contaminated area bisected by an interstate<br />
highway. The ROD calls for accessible soils to be excavated and treated aboveground via<br />
landfarming and aerated biopiles. To date, soil excavation has taken place on the north side of the<br />
interstate, and excavation on the south side of the interstate will begin in 1999.<br />
A total of about 200,000 cubic yards of contaminated soils will be excavated and treated ex situ.<br />
However, approximately 50,000 cubic yards of contaminated soil lies beneath the interstate<br />
highway, and will be remediated via in situ flushing, although ozone injection is also under<br />
consideration for these soils <strong>In</strong> situ flushing will also be used to remediate groundwater. Much<br />
LNAPL at the site (comprised of diesel fuel and 5% PCP), was removed at the time of soil<br />
excavation, however remaining LNAPL will also be targeted with in situ flushing. The remediation<br />
goals for PCP for the site are 34 ppm in soil and 1 ppb in groundwater.<br />
The geologic material of the subsurface area targeted for in situ flushing is comprised of sandy<br />
alluvial material. The water table is present at approximately 5 to 8 feet below the ground surface.<br />
At the time of soil excavation north of the interstate, the excavations were extended to about two<br />
feet below the water table. The excavations were backfilled with clean soil, and recharge basins<br />
were constructed to allow current recharge of treated groundwater for flushing. (<strong>In</strong> the future after<br />
soils treated aboveground are replaced, the current recharge basin system will be replaced with a<br />
subsurface manifold system to deliver the treated groundwater to the subsurface).<br />
Two interception trenches (approximately 30 feet deep) have been installed north of the interstate.<br />
The downgradient trench is designed to prevent contaminated groundwater from leaving the site.<br />
Approximately 150 gpm groundwater is extracted from this trench and treated via carbon<br />
absorption with discharge to surface water or recharge to groundwater through the<br />
aeration/infiltration basins. The upgradient trench is designed to intercept both contaminated<br />
groundwater and LNAPL before it reaches the north site excavated area. About 150 gpm<br />
groundwater is exrracted, treated, and discharged. LNAPL is intercepted by a physical plastic<br />
Ground-Water Remediation Technologies Analysis Center<br />
Operated by Concurrent Technologies Corporation<br />
Appendix - Page 65 of 164<br />
Copyright GWRTAC 1998<br />
Revision 1<br />
Tuesday, November 17, 1998