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Published online 20 November 2007
Published in Vadose Zone J 6:935-945 (2007)
DOI: 10.2136/vzj2006.0176
© 2007 Soil Science Society of America
677 S. Segoe Rd., Madison, WI 53711 USA
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SPECIAL SECTION: HANFORD SITE

Impact Assessment of Existing Vadose Zone Contamination at the Hanford Site SX Tank Farm

Raziuddin Khaleela,*, Mark D. Whiteb, Martinus Oostromb, Marcus I. Woodc, Frederick M. Mannd and John G. Kristofzskid

a Fluor Government Group, P.O. Box 1050, Richland, WA 99352
b Pacific Northwest National Lab., P.O. Box 999, Richland, WA 99352
c Fluor Hanford, Inc., P.O. Box 1000, Richland, WA 99352
d CH2M HILL Hanford Group, Inc., P.O. Box 1500, Richland, WA 99352

* Corresponding author (raziuddin_khaleel{at}rl.gov).

Received 11 December 2006.

The USDOE has initiated an impact assessment of existing vadose zone contamination at the Hanford Site SX tank farm in southeastern Washington State. The assessment followed the Resource Conservation and Recovery Act (RCRA) Corrective Action process to address the impacts of past tank waste releases to the vadose zone at the single-shell tank farm. Numerical models were developed that consider the extent of contamination presently within the vadose zone and predict contaminant movement through the vadose zone to groundwater. The transport of representative mobile (technetium-99) and immobile (cesium-137) constituents was evaluated in modeling. The model considered the accelerated movement of moisture around and beneath single-shell tanks that is attributed to bare, gravel surfaces resulting from the construction of the underground storage tanks. Infiltration, possibly nearing 100 mm yr–1, is further amplified in the tank farm because of the umbrella effect created by percolating moisture being diverted by the impermeable, sloping surface of the large, 24-m-diameter, buried tank domes. For both the base case (no-action alternative) simulation and a simulation that considered placement of an interim surface barrier to minimize infiltration, predicted groundwater concentrations for technetium-99 at the SX tank farm boundary were exceedingly high, on the order of 106 pCi L–1. The predicted concentrations are, however, somewhat conservative because of our use of two-dimensional modeling for a three-dimensional problem. A series of simulations were performed, using recharge rates of 50, 30, and 10 mm yr–1, and compared to the base case (100 mm yr–1) results. As expected, lowering meteoric recharge delayed peak arrival times and reduced peak concentrations at the tank farm boundary.

Abbreviations: bgs, below ground surface • BTC, breakthrough curve • RCRA, Resource Conservation and Recovery Act




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