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Appendix CRF - Part 3 - Northamptonshire County Council

Appendix CRF - Part 3 - Northamptonshire County Council

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Radiological Assessment 0820-2<br />

Version 2<br />

3 Assessment Methodology<br />

This section describes the overall assessment methodology used to calculate potential<br />

doses from disposals of LLW at the ENRMF and to determine radiological capacities.<br />

Section 3.1 summarises the SNIFFER methodology, on which the assessment is<br />

based. Section 3.2 describes the changes made to the SNIFFER methodology to take<br />

account of specific features of the ENRMF and the proposed disposals.<br />

3.1 Summary of SNIFFER methodology<br />

3.1.1 Assessment framework<br />

The SNIFFER methodology was developed so as to provide the regulators, and other<br />

stakeholders, with a consistent approach to assessing the potential for landfill sites to<br />

accept the category of LLW known as Special Precautions Burial (SPB). The overall<br />

assessment approach is illustrated in Figure 3.1 (SNIFFER 2006a).<br />

It was originally envisaged that a screening stage would be useful if large numbers of<br />

sites were examined (SNIFFER 2006a). This might be done by site owners, seeking<br />

to put forward a few sites as potential disposal sites, or by planners, seeking to assess<br />

the overall availability of disposal capacity for LLW. The principal application of the<br />

methodology, however, would be for the assessment of particular sites and this<br />

screening stage would not be required.<br />

An important aim of the SNIFFER methodology was to provide regulators with a<br />

means of assessing radiological capacity for a landfill site and updating this capacity<br />

as more information becomes available and the available capacity is reduced though<br />

disposals. To ensure that the assessment is robust and fit for purpose, the approach<br />

developed by the IAEA and others of defining an assessment context forms an<br />

important part of the SNIFFER methodology. To provide as much consistency and<br />

flexibility as possible, the elements comprising the assessment context were<br />

incorporated as generic elements (providing consistency) or site-specific elements<br />

(providing flexibility) as considered most appropriate.<br />

Using the assessment terminology established by the IAEA, the generic aspects of the<br />

assessment context are the assessment purpose, endpoints, basis, and assumptions<br />

regarding future society. The site-specific aspects of the assessment context are the<br />

environmental system of interest, site context, nature of the wastes, and assessment<br />

timescales.<br />

The assessment endpoint and basis are established as generic factors so as to ensure as<br />

much consistency as possible between sites. The assessment end-point is dose, so that<br />

the results can be compared with an effective dose criterion. The SNIFFER<br />

methodology was based on a criterion of 20 Sv/year, representing the point at which<br />

doses arising from disposals can be regarded as being below regulatory concern<br />

(SNIFFER 2006a).<br />

Galson Sciences Limited 14 14 July 2009<br />

WS010001/ENRMF/CONSAPP<strong>CRF</strong> 564

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