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Management of Commercially Generated Radioactive Waste - U.S. ...

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1.29<br />

For the proposed program, resource requirements for reprocessing are somewhat higher<br />

than for the once-through cycle in the case <strong>of</strong> steel, cement, electricity, and manpower; are<br />

about the same to somewhat higher for diesel fuel and gasoline; and are substantially higher<br />

for propane. The higher propane requirement results from incineration <strong>of</strong> combustible waste.<br />

Gasoline and diesel fuel are used primarily in transportation. These fuel requirements are<br />

based on present practice and can be expected to change as fuel use patterns change gener-<br />

ally. The propane requirements for the reprocessing cycle represent about 0.5% <strong>of</strong> the total<br />

U.S. consumption for the period to year 2050 assuming current consumption rates hold con-<br />

stant. The largest diesel fuel use amounts to about 1% <strong>of</strong> total U.S. consumption over the<br />

period.(a) Electricity consumption amounts to 0.02 to 0.05% to the total energy generated<br />

by the nuclear power system in this case.<br />

The resource commitments for the program alternatives using the once-through cycle<br />

increase as the size <strong>of</strong> the nuclear system served increases. With the exception <strong>of</strong> the pre-<br />

sent inventory case which changes only slightly, requirements for the alternative program<br />

compared to the proposed program tend to range up to 2 to 3 times higher for steel, cement,<br />

gasoline, propane, and manpower and modestly higher for diesel fuel and electricity.<br />

Requirements for the no-action alternative are zero in the present inventory case and are<br />

about the same as the alternative program for steel, cement, gasoline, propane, and manpower<br />

but diesel and electricity consumption are much lower.<br />

Resource commitments for the program alternatives in the reprocessing cycle tend to be<br />

about the same to somewhat higher than for the proposed program requirements.<br />

1.7.3 Systems Costs(b)<br />

Both total cost and levelized ( c ) unit costs (per kWh) were developed. These costs<br />

include all waste treatment, storage, transport and disposal cos-ts-for wastes resulting<br />

from nuclear power generation through the year 2040. The costs also include DOE's research<br />

and development and repository site qualification costs which are assumed to be recovered<br />

through fees charged to the utilities for storage and disposal. The cost ranges consider<br />

four different disposal media.<br />

In terms <strong>of</strong> total costs, the costs increase with increasing size <strong>of</strong> the nuclear system<br />

but are disproportionately high for the very low-growth cases. The estimated costs range<br />

from $5 to $12 billion for the present inventory case (Case 1), to $80 to $150 billion for<br />

the system that reaches 500 GWe installed capacity in the year 2040 (Case 5). Of these<br />

totals, the estimated R&D and multiple-site qualification costs range from $2.9 to $3.6<br />

billion at the low end <strong>of</strong> the proposed program to $9 to $10 billion at the high end <strong>of</strong> the<br />

(a) While a commitment <strong>of</strong> 1% <strong>of</strong> current U.S. consumption may appear small, some commenters<br />

on the draft Statement viewed such a quantity as excessively large in terms <strong>of</strong> commitment<br />

for a single industrial use. It should be noted that resource needs have been<br />

approximated for this final Statement. It is believed that optimizing, for instance in<br />

terms <strong>of</strong> shipping distances, could result in reduction <strong>of</strong> quantities <strong>of</strong> resource<br />

required.<br />

(b) All costs are cited in terms <strong>of</strong> 1978 dollars.<br />

(c) Levelized Unit Cost = Annualized Capital and Operating Costs<br />

Annualized Units Produced

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