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DOE 2000. - Waste Isolation Pilot Plant - U.S. Department of Energy

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WIPP RH PSAR <strong>DOE</strong>/WIPP-03-3174 CHAPTER 4<br />

Option B represents the preferred option for panels that will be closed for more than 20 years prior to<br />

final facility closure, and whose entries are reasonably intact at time <strong>of</strong> closure. These will likely be<br />

Panels 2 through 5. Option C may be desirable for panels whose entries require DRZ removal, and<br />

whose closure precedes final facility closure by less than 20 years. This is the likely configuration <strong>of</strong> the<br />

closure for Panels 9 and 10. Finally, Option D may be appropriate for panels whose entries require<br />

significant removal <strong>of</strong> the DRZ, and whose closure will precede final facility closure by more than 20<br />

years. Panel 1 is the most likely candidate for this type <strong>of</strong> closure.<br />

The 20-year limit in the design selection process is based on what the <strong>DOE</strong> believes to be conservative<br />

analytical results that indicate methane, being generated by waste degradation at the rate <strong>of</strong> 0.1 mole per<br />

drum per year, will not reach flammable concentrations for at least 20 years. As part <strong>of</strong> the decision<br />

making process on design selection, an investigation <strong>of</strong> the DRZ would precede the selection <strong>of</strong> the<br />

concrete component and the specification <strong>of</strong> the amount <strong>of</strong> excavation that is needed. The investigation<br />

could be done using geophysical methods (such as ground penetrating radar) or drill holes. Drill holes<br />

can be investigated using video cameras or "scratchers." The <strong>DOE</strong> considers the 20-year criterion is still<br />

appropriate, since the design report shows that it takes 25 years to reach explosive limits. A ten percent<br />

reduction in this time is still beyond 20 years. Furthermore, the chances that methane will be generated<br />

initially are minimized by the fact that the closed panels will be initially oxic and may remain so for a<br />

long time after facility closure.<br />

The <strong>DOE</strong> believes that design Options A through D will function adequately as panel closures, given the<br />

current state <strong>of</strong> knowledge about gas generation, the understanding <strong>of</strong> the DRZ, the expected<br />

characteristics <strong>of</strong> the waste, and the inability <strong>of</strong> monitoring techniques to accurately detect extremely<br />

small concentrations <strong>of</strong> VOCs. However, in the event sufficient information is collected that allows the<br />

<strong>DOE</strong> to make less conservative assumptions regarding these items, designs A through D may provide<br />

significantly more protection than is actually needed. Consequently, the <strong>DOE</strong> has retained as a design<br />

concept, Option E, which is simply the explosion wall portion <strong>of</strong> Options B and D. Option E represents<br />

a significantly simpler panel closure system that the <strong>DOE</strong> would use if either <strong>of</strong> the following criteria are<br />

met:<br />

Ç<br />

Gas generation rates are smaller. Current (unreported) work being performed by Sandia National<br />

Laboratories indicates that microbial gas generation rates under humid conditions are close to zero,<br />

and/or<br />

Ç<br />

The average headspace concentrations are less than the averages used in the calculations. As new<br />

wastes are generated, the use <strong>of</strong> organic solvents is expected to drastically be reduced.<br />

Condition 1 <strong>of</strong> the Certification Decision Final Rule 4 requires that the <strong>DOE</strong> implement the Option D<br />

panel closure system at the WIPP.<br />

4.2-29 January 28, 2003

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