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Technology Status Report: In Situ Flushing - CLU-IN

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3.1 <strong>Flushing</strong> Solutions<br />

3.0 ANALYSIS OF <strong>IN</strong> SITU FLUSH<strong>IN</strong>G TECHNOLOGY<br />

Figure 9 is a pie chart illustrating the types of flushing solutions being used in the various case studies of<br />

all scales. For this chart, if more than one type of flushing solution was used in a project, or if a flushing<br />

solution contained more than one type of flushing additive, both were counted (i.e. a project where both<br />

surfactants and co-solvents were used was counted as both a surfactant and a co-solvent project). The<br />

“other” category for this figure encompasses several different potential flushing additives (such as<br />

polymers, electolytes, complexing sugars, etc.), as indicated by the note on the figure, whether or not<br />

these additives are in use alone or combined with surfactant or other solutions. As shown, surfactants,<br />

plain water, other, and then co-solvents (in descending frequency of occurrence) are the top four<br />

categories of the known flushing solutions which have been used. It should be noted that, of the 22 fullscale<br />

studies, where known, the flushing solution used in the majority of the studies was plain water (or<br />

water with addition of nutrients), usually treated site groundwater. Exceptions are six sites located in<br />

Quebec, Canada, and three sites located in the U.S. GWRTAC ID FLSH0011 is the Estrie Region<br />

Machine Shop site in Quebec, Canada, in which a surfactant flushing solution was utilized at a site<br />

contaminated with LNAPL. GWRTAC ID FLSH0037 is a site in Drummondville, Quebec, where<br />

surfactants are used to remediate soil contaminated with benzene, toluene, ethylbenzene, and xylene<br />

(BTEX) and mineral oil and grease (MOG). GWRTAC ID FLSH0042 is the Thouin Sand Quarry Site in<br />

Quebec, Canada, where additives including surfactant were used to remediate DNAPL. GWRTAC ID<br />

FLSH0066 is an aluminum processing facility in Quebec where surfactants were used in the remediation<br />

of polychlorinated biphenyls (PCBs) and MOG. GWRTAC IDs FLSH0067 and FLSH0068 are two<br />

separate projects in Quebec where surfactants were used to treat soils contaminated with BTEX and<br />

MOG at or near petroleum sites. One of the sites in the U.S. thought to be the first to use a flushing<br />

additive other than nutrients at full-scale, is FLSH0050, located in Florida, where an arsenic plume in<br />

groundwater is being remediated using proprietary chemicals in the flushing solution. The remaining two<br />

U.S. projects are in planning stages or are confidential in nature.<br />

Figure 10 is a bar chart depicting the flushing solution type used by project scale. As in Figure 9, more<br />

than one category of flushing solution per project may be included in this figure. As is apparent from this<br />

figure, while surfactants are used in many laboratory-scale studies and are being tested in the field at pilotscale,<br />

only a small number of full-scale applications have occurred to date, and these are outside the U.S.;<br />

six Canadian projects are identified above. However, plans are currently underway to remediate at least<br />

a portion of Operable Unit 2 (OU2) at Hill Air Force Base using a surfactant flood. This is thought to be<br />

the first full-scale (currently funding for 1/5 of the full project is earmarked) application of surfactant<br />

flushing planned in the U.S., and may be underway within the next two years. Still, at least 14 full-scale in<br />

situ flushing case studies have been identified by GWRTAC where water (treated or untreated site<br />

groundwater, or potable water) with no additives other than nutrients is used as the flushing solution.<br />

Considering the laboratory- and pilot-scale studies, which are included in Figure 10, the majority of the<br />

research and demonstration projects have examined the use of surfactants. Only eight of the pilot-scale<br />

projects used co-solvents, compared to 30 which used surfactants. At the laboratory scale, 17 projects<br />

examined surfactants and one examined co-solvents. As mentioned above, the majority of the pilot-scale<br />

projects would have had laboratory work completed prior to the project. Figure 10 shows only<br />

laboratory/bench scale cases in which the given research group is doing laboratory work independently of<br />

a pilot-scale demonstration.<br />

Ground-Water Remediation Technologies Analysis Center © GWRTAC<br />

Operated by Concurrent Technologies Corporation Page 5 Revision 1 11/17/98

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