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

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3.14<br />

We do not yet have sufficient operating experience with nuclear plants to predict this<br />

life cycle with high confidence. These plants are generally assumed to have lifetimes in<br />

the range <strong>of</strong> 30 to 40 years. The upper end <strong>of</strong> this range was used here to be conservative<br />

in regard to the amount <strong>of</strong> radioactive waste to be managed for a specific system. The<br />

declining load factor as facilities age has not yet been observed in nuclear plants but is<br />

similar to the experience <strong>of</strong> large central-station fossil-fuel generating units.<br />

Using the year 2000 as a reference point, the impacts <strong>of</strong> other growth assumptions can<br />

be derived by comparison to this case. For example, a 500 GWe system in the year 2000 would<br />

produce approximately twice the impacts <strong>of</strong> Case 3 if allowed to run out its useful life, or<br />

a 125 GWe system in the year 2000 would produce approximately one-half as much impact.<br />

Case 4--250 GWe in Year 2000 and Constant--This case follows the same growth pattern<br />

as Case 3 up to the year 2000. Then, instead <strong>of</strong> phasing out capacity as plants are decom-<br />

missioned, new capacity is added to maintain the total capacity at 250 Gwe until the<br />

year 2040, beyond which time the case is not analyzed. A total <strong>of</strong> 316,000 MTHM <strong>of</strong> spent<br />

fuel is produced in this case.<br />

This case illustrates the rate at which continuous waste management requirements and<br />

impacts would occur in a constant or steady-state system. An approximate equilibrium is<br />

established.<br />

<strong>Waste</strong> management requirements and impacts at other constant capacity levels can be<br />

obtained by comparing capacities and impacts to this case.<br />

Case 5--250 GWe in Year 2000 and 500 GWe in 2040--This case also follows the same<br />

growth pattern as Case 3 up to the year 2000. After that, however, capacity additions con-<br />

tinue until a doubled capacity <strong>of</strong> 500 GWe is reached in the year 2040. Beyond the<br />

year 2040, the case is not analyzed. A total <strong>of</strong> 427,000 MTHM <strong>of</strong> spent fuel is produced in<br />

this case.<br />

No equilibrium is established in this case. It illustrates the waste management<br />

requirements and impacts for a continuously expanding system. Results can be extrapolated<br />

to other growth rates by comparing the differences between the year 2040 capacities in<br />

Cases 4 and 5 to the difference in impacts. For example, a capacity <strong>of</strong> 750 GWe in the<br />

year 2040 would have twice the additional impact over Case 4 that Case 5 has.<br />

3.2.3 Resource Commitment Assessment<br />

In most instances, data describing environmental impacts that are caused by commitments<br />

<strong>of</strong> resources are presented as land and water requirements, material requirements, energy<br />

consumption, and manpower requirements for construction, operation, and decommissioning <strong>of</strong><br />

the facilities. Resource commitments are combined by facilities on a single reference plant<br />

basis for analyzing predisposal activities in Section 4.7 and for geologic repositories in<br />

Section 5.4. Resource commitments are further aggregated by plant to systems <strong>of</strong> waste<br />

management and disposal within fuel cycle options in Chapter 7.

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