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Published online 20 November 2007
Published in Vadose Zone J 6:971-984 (2007)
DOI: 10.2136/vzj2006.0166
© 2007 Soil Science Society of America
677 S. Segoe Rd., Madison, WI 53711 USA
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Carbon Tetrachloride Flow and Transport in the Subsurface of the 216-Z-9 Trench at the Hanford Site

M. Oostroma,*, M. L. Rockholda, P. D. Thornea, M. J. Truexa, G. V. Lasta and V. J. Rohayb

a Environmental Technology Division, Pacific Northwest National Lab., P.O. Box 999, MS K9-33, Richland, WA 99352
b Fluor Hanford, Inc., Richland, WA 99352


Figure 1
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FIG. 1. Outline of regional and 216-Z-9 trench geologic model domains at the Hanford Site near Richland, WA.

 

Figure 2
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FIG. 2. Current conceptual model of subsurface carbon tetrachloride behavior at the Hanford Site (after USDOE, 2004).

 

Figure 3
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FIG. 3. Three-dimensional geologic domain with a cut-out below the 216-Z-9 trench. The stratigraphic units in the legend denote Backfill, Hanford 1a (h1a), Hanford 1 (h1), Hanford 2 (h2), Lower Gravel (low_grvl), Lower Sand (low_sand), Cold Creek unit silt (pplz), Cold Creek unit carbonate (pplc), Upper Ringold (up_ring), Ringold E (ring_e), Ringold Lower Mud (low_rmud), Ringold A (ring_a), and Basalt.

 

Figure 4
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FIG. 4. Plan view of the STOMP computational domain with model grid and locations of soil vapor extraction wells. The domain is 440 m in the west–east direction and 540 m in the south–north direction. Well 299-W15-223 is a slant-borehole.

 

Figure 5
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FIG. 5. Dense nonaqueous phase liquid saturations in 1993 for the base case simulation. The stratigraphic units in the legend denote Backfill, Hanford 1a (h1a), Hanford 1 (h1), Hanford 2 (h2), Lower Gravel (low_grvl), Lower Sand (low_sand), Cold Creek unit silt (pplz), Cold Creek unit carbonate (pplc), Upper Ringold (up_ring), Ringold E (ring_e), Ringold Lower Mud (low_rmud), Ringold A (ring_a), and Basalt.

 

Figure 6
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FIG. 6. Carbon tetrachloride gas concentrations (g L–1) in 1993 for the base case simulation. The stratigraphic units in the legend denote Backfill, Hanford 1a (h1a), Hanford 1 (h1), Hanford 2 (h2), Lower Gravel (low_grvl), Lower Sand (low_sand), Cold Creek unit silt (pplz), Cold Creek unit carbonate (pplc), Upper Ringold (up_ring), Ringold E (ring_e), Ringold Lower Mud (low_rmud), Ringold A (ring_a), and Basalt.

 

Figure 7
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FIG. 7. Carbon tetrachloride mass (kg) distribution in the dense nonaqueous phase liquid (DNAPL), aqueous, and gaseous phases, and sorbed to the solid phase for the base case simulation. (VOC, volatile organic compound.)

 

Figure 8
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FIG. 8. Dense nonaqueous phase liquid (DNAPL) mass (kg) distribution among the hydrostratigraphic units for the base case simulation.

 

Figure 9
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FIG. 9. Cumulative transported dense nonaqueous phase liquid (DNAPL) and dissolved mass for the base case simulation.

 

Figure 10
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FIG. 10. Updated carbon tetrachloride subsurface flow and transport conceptual model for the Hanford Site.

 

Figure 11
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FIG. 11. Conceptual distribution of carbon tetrachloride from waste disposed at the 216-Z-9 site for (a) 1966, (b) 1974, (c) 1993, and (d) 2005. These figures are based on the results of the base case simulations. Note that some sensitivity simulations show significantly different results. The figure for the year 2005 shows the conceptual impact of soil vapor extraction remediation operations.

 





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