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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 />

was found to coincide with elevated surfactant concentration. Also, the tailing of surfactant<br />

recovery continues to enhance contaminant concentrations in the recovered groundwater. Average<br />

enhancements of contaminant concentrations in the recovered groundwater ranged from a factor of<br />

10 to 20. It should be noted that, to ensure hydraulic control, the recovered groundwater stream<br />

was being diluted within the well bores by factor of 4:1. Actual enhancement of contaminant<br />

concentration in the flushed zone is estimated to range from 40 to 100 times the normal aqueous<br />

contaminant concentration.<br />

The enhancement of contaminant recovery was not consistent for the BTEX compounds. The<br />

results indicate that the enhancement of benzene and toluene was consistently higher than that of<br />

xylenes. This may be due to the relative low concentrations of xylenes at this particular site or<br />

preferential solubilization.<br />

Air Stripper Results<br />

Three air strippers were utilized for contaminant removal, a packed column (PC) and two hollow<br />

fiber membranes (HF1 and HF2). These strippers were operated in a number of different<br />

configurations and using a wide range of operating parameters. All air strippers were operated<br />

effectively at surfactant concentrations well above the CMC. The packed column was operated at<br />

varying air to water ratios without foam production. Stripper required minmal adjustment and<br />

maintenance.<br />

As noted by the results the stripping effectiveness of the hollow fiber membrane HF2 surpassed<br />

that of HF1. It should be noted that HF2 was new, whereas HF1 was used and did not perform as<br />

well as HF2. Also, recovered surfactant concentrations fluctuate throughout the air stripping<br />

sensitivity analysis, and could introduce some small differences in TPH removal. Baseline<br />

removal was evaluated for each of the air strippers before surfactant was introduced into the<br />

system. These values were used to determine the extent that surfactants inhibit contaminant<br />

removal using these strippers. The baseline values were calculated by running the strippers in<br />

parallel and using the same operating parameters.<br />

Once the baseline had been established and surfactant had been introduced into the system at .5<br />

% by weight,the strippers were operated under similar conditions (air to water ratio of 5.2:1 instead<br />

of 4:1) and the removal efficiency calculated. Results from operating the P.C., HF1 and HF2 in<br />

parallel with water flow at .25 gpm and air flow at 1.3 cfm to each were given in tabular form. It<br />

can be seen that the surfactant inhibited contaminant removal by as much as 32% in HF1 (the<br />

used hollow fiber unit) and little as 17% in the packed column.<br />

The hollow fiber membranes were operated in series and parallel and under varying flow rate ratios<br />

of air to water. The results from operating HF1 and HF2 in series with a 4.5:1 air to water ratio<br />

were shown in a table. The average removal for HF1 and HF2 in series is the percentage removed<br />

from total TPH entering the system. That is, HF2 removed 61% of the TPH going into HF1, not<br />

61% of the TPH leaving HF1. Table 4 also shows the same units in parallel with a ratio of 5:1 air<br />

to water. Comparison of the two tables indicate that running the HF units in parallel is somewhat<br />

more efficient. <strong>In</strong> comparison with Table 5, not much improvement was realized from by<br />

increasing the ratio from 3:1 to 5:1. Another table provides results from operating the three units<br />

in parallel at an air to water ratio of 8:1. It was seen that some improvement was realized for the<br />

HF units but none for the Packed Column.<br />

Ground-Water Remediation Technologies Analysis Center<br />

Operated by Concurrent Technologies Corporation<br />

Appendix - Page 148 of 164<br />

Copyright GWRTAC 1998<br />

Revision 1<br />

Tuesday, November 17, 1998

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