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I<br />

f^<br />

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DOE!RL-2001-29<br />

Ikaft D RedlinelStriketwt B<br />

Figure 6. Alternative 4- Cross Section of the Environmental Cap and Exterior Waste F'ilL<br />

Enplnwnd OartMr<br />

(dedUMd RCRA &bn0e C Sudxe Banier)<br />

^ ^'&oq tOm<br />

^'.<br />

... . .<br />

am<br />

^`ic=l;^f^::'7`•.^i^J^,:'<br />

7<br />

. .E. .. t' ..:i:: 1<br />

. ^'7Ext..wrw..ur:tn L<br />

2214 "^^^^DuN unerlNow weste Flll<br />

(Oaw,Na Ntuelun<br />

wlNwaNena)<br />

IsarrMr i^ ^^-Enplnsandfill^<br />

i^.s.<br />

C_k. .<br />

provide containment to both interior and exterior waste<br />

Gll (Figure 6). The disposal unit's exterior waste fill<br />

area will include as part of its design a RCRArnaapliant<br />

double Finer and leachate collection<br />

21 system to account for the potential to receive<br />

9 hazardous waste from CERCLA or RCRA past-<br />

10 practice aleanups at ffanford In this portion of the<br />

11 facility. With the addition of the external disposal<br />

12 area, approxhmtely 63,600 ms (82,700 yds) of waste<br />

13 could be disposed at the 221-U Facility under<br />

14 Alternative 4. Like Alternative 3, approximately<br />

IS 1.4 million m' (1.8 million yd') of borrow materials<br />

16 would be required to construct the environmental cap.<br />

17 The facility after placement of the environmental cap<br />

18 would be approximately 461 m(1312 h) in length by<br />

19 234 m(768 fl) in width by 24 in (80 ft) high at existing<br />

20 grade.<br />

21 Alterodive 6: Close In Place - Collapsed Strueture<br />

2<br />

2<br />

2<br />

2f{<br />

21<br />

2<br />

29<br />

31<br />

31<br />

32<br />

33<br />

34<br />

5<br />

31 3<br />

3<br />

3<br />

This allernaQve would require dispn.^ei-of-F000-tnr<br />

rki:ar,-^i approxinutely 3,400 m' (4,400 yd) of existing<br />

contaminated equipment from the canyon eperatingdock<br />

weadd-be size reduced and disposed to the pracess cells<br />

and erotncd (Figiae 7). The upper part of the 221-U<br />

Faeility would then be demolished to approximately the<br />

level of the canyon eperadng-dock. Demolition would<br />

involve cutting the upper part of the structtuo into large<br />

blocks. The eot>Retc debris from building demolition<br />

would be placed on the canyon deck and on the ground<br />

adjacent to the building, Cementitious grout would be<br />

placed around waste to minimize the potential for void<br />

spaces Unlike Aitem^vl^ves 3 and 4. Alternative 6 would<br />

ruy include dispnsal of impnned llanfttrd <strong>Site</strong><br />

mmediatinn waaes de cr unmd the outcide of the<br />

Ermbn Probeaon<br />

' `<br />

39 2^1-U Facititv. -A kxa<br />

40 m .,<br />

41 FxiiityandeN4kernntive{r.<br />

NaloscaVe<br />

ae,aw ,as<br />

42 The oaniallv demolished_ building and concrete debris<br />

43 would be covered with a modified RCRA Subtitle C.<br />

44 compliant environmental cap; however, the<br />

45 environmental cap would be smaller in dimension than<br />

46 In Alternatives 3 and 4 as a result of the decreased<br />

47 height of the structure. Approximately 460,000 ms<br />

48 (602.000 yd)) of borrow materials would be required<br />

49 under this alternative for environmental cap materials.<br />

50 The facility after placement of the environmental cap<br />

SI would be approximately 370 m(1,214 R) In length by<br />

52 159 m(522 ft) in width by 12 m(39 It) high.<br />

53 Post-closure cara, Institutional controls, and<br />

54 monitoring required as pan of this alternative would be<br />

55 similar to Alternatives 3 and 4.<br />

56 EVALUATION OF REMEDIAL<br />

37 ALTERNATIVES<br />

58 The following evaluation of remedial alternatives<br />

59 summarizes each alternative in rolation to the aine<br />

60 CERCLA criteria (see box - Explanation of CERCLA<br />

61 Evaluation Criteria). A comprehensive analysis of<br />

62 each alternative is contained In the 221-U Facility final<br />

63 feasibility study.<br />

64 The first two criteria. overall protection and<br />

65 compliance with ARARs. are defined under CERCLA<br />

66 as'tihreshold criteria." Threshold criteria ttwst be met<br />

67 by an alternative to be eligible for selection. The next<br />

68 five criteria are defined as "primary balancing<br />

69 criteria." These criteria are used to weigh major<br />

70 tradaoffs among alternatives. The Wst two criteria,<br />

71 stale and community acceptance, are defined as<br />

14

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