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7.48<br />

TABLE 7.6.3. Comparison <strong>of</strong> Total <strong>Waste</strong> <strong>Management</strong> Costs for the Program Alternatives<br />

Using the Reprocessing Cycle,tal $ Billions<br />

Proposed Program Alternative Program<br />

Nuclear Power Growth (Geologic Disposal (Disposal Starting No-Action<br />

Case Assumption Starting 1990 - 2010) 2010 - 2030) Alternative<br />

1 Present Inventory Only NA(b) NA NA<br />

2 Present Capacity and<br />

Normal Life NA NA NA<br />

3 250 GWe System by<br />

Year 2000 and Normal<br />

Life 59 to 90 58 to 90 NA<br />

4 250 GWe System by<br />

Year 2000 and Steady<br />

State 87 to 108 89 to 104 NA<br />

5 500 GWe System by Year 2040 114 to 146 116 to 137 NA<br />

(a) Assumed reprocessing startup dates range from 1990 to 2010.<br />

(b) NA = not applicable.<br />

the alternative program than for the proposed or no-action alternatives. With the reproces-<br />

sing cycle, the cost ranges are about the same for both the proposed and alternative<br />

programs.<br />

Costs for the program alternative are compared on the basis <strong>of</strong> levelized unit costs in<br />

terms <strong>of</strong> mills/kWh at a 0% discount rate in Table 7.6.4 for the once-through cycle and<br />

Table 7.6.5 for the reprocessing cycle. On this basis, unit cost ranges for the present<br />

inventory case (Case 1) are much higher than the other cases because <strong>of</strong> the small quantity<br />

<strong>of</strong> kilowatt-hours generated in this case relative to the fixed costs. With the present cap-<br />

acity case (Case 2), the costs drop to about 1/3 <strong>of</strong> the Case 1 costs. For the once-through<br />

cycle, the alternative program unit costs range higher than the proposed program and the no-<br />

action alternative costs lie at the low end to mid-range <strong>of</strong> the proposed program cost<br />

range. Costs are higher for the proposed program using the reprocessing cycle than are the<br />

costs <strong>of</strong> the oncethrough cycle, but the cost range for the alternative program is almost<br />

identical to the proposed program range.<br />

When a discount rate larger than zero is used to calculate levelized costs, the differ-<br />

ences between the proposed program and the alternative program and differences between once-<br />

through and reprocessing cycles become less pronounced. This is shown in Tables 7.6.6 and<br />

7.6.7, which compare the costs for the once-through cycle and the reprocessing cycle on the<br />

basis <strong>of</strong> a 7% discount rate and in Tables 7.6.8 and 7.6.9, which compare the same cost<br />

ranges on the basis <strong>of</strong> a 10% discount rate.<br />

At a 7% discount rate, cost differences between the proposed program and the alterna-<br />

tive program are not significant for either the once-through cycle or the reprocessing<br />

cycle. Costs for the reprocessing cycle range mostly about 10% higher to as much as 30%<br />

higher than for the once-through cycle.<br />

At a 10% discount rate, as with a 7% rate, the cost differences between the proposed<br />

program and the alternative program are not significant. The costs for the reprocessing<br />

cycle range from slightly higher to as much as 15% higher than for the once-through cycle.

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