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

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6.2<br />

annual throughput or a common environment. As an example, the well injection concept section<br />

presents radiological impact information extracted from a reference which addresses the<br />

impacts <strong>of</strong> intermediate level waste disposal. This is done to provide the reader with<br />

related information that may be important to the understanding <strong>of</strong> the concept. In addi-<br />

tion, the space disposal and transmutation concepts require chemical processing <strong>of</strong> spent fuel<br />

to prepare waste for disposal or elimination. Accordingly, comparisons between these con-<br />

cepts and, for example, others not requiring processing would be difficult. For instance,<br />

transportation costs in the processing case could not be compared with those for disposal <strong>of</strong><br />

spent fuel.<br />

Four <strong>of</strong> the concepts (very deep hole, rock melt, space, and subseabed), however, were<br />

covered in a common reference and thus have a common basis. The other options are not nor-<br />

malized because, for example, while linear extrapolation to a higher or lower quantity <strong>of</strong><br />

waste handled may result in a more or less conservative estimate <strong>of</strong> impacts and costs for a<br />

particular option, it may also bias any comparative analysis for or against that concept.<br />

Also, the descriptions, impacts, and costs that have been reported for some <strong>of</strong> the alterna-<br />

tives are incomplete because <strong>of</strong> the early stage <strong>of</strong> the alternatives' technical development.<br />

In addition to being, in many cases, incomplete, the cost and impact data should be con-<br />

sidered speculative. For example, the costs projected for the development <strong>of</strong> an alternative<br />

are generally based on judgment regarding the current state <strong>of</strong> technical uncertainty for the<br />

alternative. In practice, many such cost estimates do not adequately anticipate the expanded<br />

scope <strong>of</strong> activities'that may result as additional uncertainties and issues are identified in<br />

attempts to resolve the original set <strong>of</strong> uncertainties. It was felt, therefore, that manipu-<br />

lating costs and impact information may indicate more significance than is warranted.<br />

The disposal methods along with rates used as a basis for defining each <strong>of</strong> the alterna-<br />

tives, including the mined geologic repository, are:<br />

Alternative Disposal Rate, MTHM/yr Reference<br />

Mined Geologic Repository 6,000 Chapter 3<br />

Very Deep Hole 5,000 Bechtel (1979a)<br />

Rock Melt 5,000 Bechtel (1979a)<br />

Island Disposal rates similar to mined<br />

geologic repository. Ocean<br />

transportation similar to subseabed<br />

concept, see section 6.1. Chapter 5, and Section 6.1.4<br />

Subseabed 5,000 Bechtel (1979a)<br />

Ice Sheet 3,000 MITRE (1979)<br />

Well Injection Unspecified ORNL TM 1533, DOE (1979)<br />

Transmutation 2,000 Blomeke et al. (1980)<br />

Space 5,000 Bechtel (1979a)<br />

Frequently, numbers taken from the various references are rounded to an appropriate<br />

number <strong>of</strong> significant digits in an effort to simplify this section <strong>of</strong> the document.<br />

The general approach to each <strong>of</strong> the topical discussions used to describe the alternatives<br />

is as follows.

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