View Document Here - Hanford Site
View Document Here - Hanford Site
View Document Here - Hanford Site
Create successful ePaper yourself
Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.
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