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PNNL-13501 - Pacific Northwest National Laboratory

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encountered in the field. The contaminanted soil was then<br />

packed in columns. Ozone was passed through the<br />

columns at discrete time increments of 1, 2, 4, 8, and 16<br />

hours. Each time increment represents one experiment<br />

after which the column was dismantled and the<br />

concentrations of TNT in the soil were measured. A<br />

control column was also conducted by passing oxygen<br />

through the column for 16 hours. Figure 3 shows the<br />

results of these time series experiments.<br />

Concentration TNT (mg/Kg)<br />

60<br />

50<br />

40<br />

30<br />

20<br />

10<br />

0<br />

0 100 200 300 400 500 600 700 800 900 1000<br />

Elapsed Time (min)<br />

Figure 3. Degradation of TNT in ozone<br />

Results and Accomplishments<br />

Initial proof-of-principle data were obtained for treatment<br />

of TNT-contaminated sediment with ozone. In these<br />

tests, a silty sandy alluvium from White Sands was spiked<br />

to a concentration level of about 50 ppm TNT and then<br />

exposed to concentrated ozone gas (several percent in<br />

oxygen). After 2 hours of exposure, 50% of the TNT was<br />

decomposed, and after 16 hours the concentrations were<br />

reduced by 80%. This was not an exponential decline in<br />

concentrations and therefore not a first-order reaction. In<br />

a shorter, 4-hour test, a Hanford sandy loam sediment<br />

spiked to a concentration level of 10 ppm was tested for<br />

two time increments. After 1 hour of exposure, 30% of<br />

the TNT decomposed, and after 4 hours, 70%<br />

decomposed. In this 4-hour experiment, we determined<br />

that essentially all the TNT that was degraded was<br />

converted completely to nitrate and carbon dioxide,<br />

though trace levels of trinitrobenzene were observed.<br />

Summary and Conclusion<br />

Interaction of ozone with the sediment matrix was<br />

determined to be insignificant based on ozone<br />

breakthrough characteristics for a control column test<br />

conducted with uncontaminated sediment. Based on this<br />

limited testing, ozone appears to be capable of degrading<br />

TNT in unsaturated sediment. Additional testing will be<br />

required to determine the factors controlling the<br />

degradation rates in the soil.<br />

Bibliography<br />

Thornton EC, JT Giblin, TJ Gilmore, KB Olsen,<br />

JM Phelan, and RD Miller. 1999. In situ gaseous<br />

reduction pilot demonstration—Final Report. <strong>PNNL</strong>-<br />

12121. <strong>Pacific</strong> <strong>Northwest</strong> <strong>National</strong> <strong>Laboratory</strong>, Richland,<br />

Washington.<br />

Earth System Science 229

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