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Appendix F -Detailed Description of Alternative 3: DOEAR1,2001-11<br />

I Entombment with Internal Waste Disposal Rev. p l Draft 0<br />

Rcdlinc/Slrikcout<br />

I contamination present in the pipe. After the connecting pipes to cell 10 are sealed, grout would be<br />

2 pumped in from both ends of the cell drain header. Because the cell drain header flows<br />

3 downward from the building ends toward cell 10, a liquid-consistency grout would flow through<br />

4 the header and require very little pumping pressure. Drainage openings in each process cell<br />

5 would act as air vents, and the pressure would be regulated so that the grout would be visible in<br />

6 the process cell drains, but would not rise in the cells. After this operation, any liquid within the<br />

7 canyon would not automatically flow to cell 10.<br />

9 Waste placement is not planned for the ventilation tunnel due to limited accessibility of this area.<br />

10 Therefore, the ventilation tunnel would be grouted to eliminate voids in the building structure.<br />

I 1 Holes would be angle drilled through to canyon's exterior wall to allow access to the ventilation<br />

12 tunnel for grouting. Free-flowing grout would be pumped through these holes to 6ll the<br />

13 ventilation tunnel. The grouting would be completed in lifts to allow time for heat dissipation<br />

14 during grout curing. The tunnel is planned to be filled with grout to the maximum extent<br />

15 possible. It is estimated that the ventilation tunnel would require approximately 2,300 m3<br />

16 (3,000 ydP) of grout. During final design, the decision to fill the tunnel should be revisited.<br />

17 Preliminary structural calculations (Smyth 2001) show that the exterior wall of the tunnel may<br />

18 have sufficient strength to withstand later external pressures from fill heights associated with<br />

19 burying the canyon building and, therefore, not require grouting.<br />

20<br />

('_^'21 Facility modification would also involve removing and disposing of interfering structures,<br />

22 equipment, and material. During this phase of the work scopc, equipment and material removal<br />

23 would be limited to "clean" areas of the 271-U Office Building, the 221-U Facility galleries, and<br />

24 associated storage spaces. This activity would include the removal of the following:<br />

25<br />

26 • Installed and fixed equipment<br />

27 • All unattached equipment and components<br />

28 • Abandoned supplies<br />

29 • Materials<br />

30 • Debris.<br />

31<br />

32 These Items would be sorted for reusc, recycle, or disposal.<br />

33<br />

34 F.13.2 Disposal or Contaminated Equipment In 221-U. It is estimated that there+sare<br />

35 approximately 5,400 m3 (7,000 yd3) of contaminated equipment and components (gross loose<br />

36 volume before size reduction) currently steredon the canyon deck and in the process cells. For<br />

37 Alternative 3, those process cells with legacy equipment having dose rates >100 mrem/hr would<br />

38 be opened only to place size-reduced legacy equipment from the operating deck and erout into<br />

39 them. All of the equipment would be reduced in size and volume and then disposed into the<br />

40 process cells meeting the dose rate criteria (except for cell 3, which would be left unfilled for<br />

41 later equipment or waste placement). Size and volume reduction would be necessary so that all<br />

/-^42 of the contaminated equipment would fit into the process cells. Minimizing the amount of size<br />

1 43 and volume reduction to just the effort required to allow the contaminated equipment to fit into<br />

44 the process cells would be desirable because it would limit worker exposure. After size -<br />

F(nal^Feas(6tfity<br />

Study jor the Canyon Ditposition hdtiatlve (22l •U Facifity)<br />

Ju n e<br />

F-10

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