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7.47<br />

1980). (This schedule actually leads to a first repository in 1997, so some <strong>of</strong> the expendi-<br />

tures occur a little earlier than would be the case for a year 2000 startup.) For the 1990<br />

repository opening, costs for activities that could not be completed by that time are<br />

deleted. Second and third repositories in 1995 and 2000 are assumed. For the 2010 repos-<br />

itory opening, it has been assumed that the delay is caused in half by political, regulatory<br />

or other reasons at no cost and in half by technical problems with siting, licensing or<br />

other factors. Second and third repositories in 2015 and 2020 are assumed. For the 2020<br />

and 2030 repository openings (dates within the alternative program envelope), it was assumed<br />

that expenditures continue at the 1981 level ($190 million/yr) with the program restruc-<br />

tured to give equal emphasis to two or three disposal technologies. At the year 2000 and<br />

2010, respectively, a preferred technology is selected and the expenditure rate is reduced<br />

by one-third. After the first repository opening (2020 and 2030, respectively), the expen-<br />

diture rate is halved and continues for another 10 years when R&D is assumed to be<br />

completed.<br />

For Cases 1 and 2, where only one repository is required, the R&D and multiple site<br />

qualification costs are reduced and phased out earlier. For the "no-action" alternative<br />

cases only the costs <strong>of</strong> R&D expended through 1980 plus the spent fuel storage R&D costs<br />

(Table A.9.5) are included, for a total <strong>of</strong> $614 million.<br />

The total waste management costs in billions <strong>of</strong> dollars are compared for the program<br />

alternatives when using the once-through cycle in Table 7.6.2 and in Table 7.6.3 when using<br />

the reprocessing cycle. The range <strong>of</strong> costs takes into account the variation <strong>of</strong> costs with<br />

disposal and reprocessing dates and the variation in costs with the four disposal media that<br />

were considered and include the estimated R&D multiple site qualification costs. The costs<br />

increase as one would expect with the higher nuclear growth assumptions. However, they are<br />

disproportionally high for the very low growth assumptions because <strong>of</strong> the fixed costs for fa-<br />

cilities and research and development costs. For the three cases where the no-action alter-<br />

native was evaluated, the costs are similar to the low end to mid-range <strong>of</strong> the range for the<br />

proposed program. With the once-through cycle, the cost ranges are significantly higher for<br />

TABLE 7.6.2. Comparison <strong>of</strong> Total <strong>Waste</strong> <strong>Management</strong> Costs for the Program Alternatives<br />

Using the Once-Through Cycle, $ 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 5.1 to 7.6 7.4 to 14 6.4<br />

2 Present Capacity<br />

and Normal Life 11 to 18 16 to 24 12<br />

3 250 GWe System by<br />

Year 2000 and Normal<br />

Life 39 to 68 60 to 82 49<br />

4 250 GWe System by<br />

Year 2000 and Steady<br />

State 61 to 72 87 to 98 NA(a)<br />

5 500 GWe System by Year 2040 78 to 93 116 to 131 NA<br />

(a) NA = not applicable.

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