Select Committee on European Scrutiny First Report


CLASSIFICATION SYSTEM FOR RADIOACTIVE WASTE


(20532)
11156/99
SEC(99) 1302

Commission Recommendation on a classification system for solid radioactive waste.
Legal base:
Document originated: 15 September 1999
Forwarded to the Council: 16 September 1999
Deposited in Parliament: 21 October 1999
Department: Environment, Transport and the Regions
Basis of consideration: EM of 4 November 1999
Previous Committee Report: None
Discussed in Council: Already adopted
Committee's assessment: Politically important
Committee's decision: Cleared; but further information requested

Background

  11.1  There are many sources of radioactive wastes, ranging from items such as protective clothing used in laboratories to material arising from reprocessing nuclear fuel or decommissioning nuclear reactors. Such wastes also have a number of different characteristics, of which the most obvious is, of course, the level of radioactivity (measured by alpha, beta and gamma activity[45]). However, other considerations — such as the potential damage to human tissue or the environment, the rate at which the radioactive isotopes (radionuclides) decay, and the extent to which emissions can be reduced by appropriate shielding — are also important so far as waste handling and disposal are concerned.

  11.2  Within the UK, waste is classified into the following four bands, according to its level of radioactivity:

  • very low level waste: this can essentially be treated as normal non- radioactive waste, and sent to conventional landfill sites without special treatment;

  • low level waste: this requires no shielding, and is currently compacted in drums and buried in a shallow engineered site;

  • intermediate level waste: this generally requires shielding and special handling; and

  • high level waste: this is so highly radioactive that the decay processes generate significant excess heat; it therefore has to be vitrified from a liquid form and stored (currently at Sellafield), pending a decision on the final disposal option.

Of the three categories listed above and requiring some kind of treatment, about two-thirds is low level waste. Less than 0.5% is classed as high level waste.

  11.3  However, the method of classification varies as between different countries, including those within the Community, often depending on whether or not a country relies on nuclear power generation. As a result, the Community Action Plan in the Field of Radioactive Waste[46] called for "concerted action on the safe management of radioactive waste", so as to make it possible to "approximate national practices and regulations in the field of safety disposal, with particular reference to waste categories".

The current document

  11.4  The Commission is now seeking to address this perceived need by recommending the adoption by Member States of a common classification, based on the International Atomic Energy Agency's system, but with some changes "to take into account the views and practical experience of European national experts". Under this proposal, waste would be categorised as follows:

  • transition radioactive: which would be waste (mainly of medical origin) which will decay within the period of temporary storage, and may then be suitable for management outside the regulatory control system;

  • low and intermediate level: for waste in this category, the concentration of radionuclides would be such that generation of thermal power during its disposal is sufficiently low, and it would be divided into two further sub-categories:

  short lived: waste with a half-life of no more than around 30 years, with a restricted alpha long lived radionuclide concentration;

  long lived: waste with long lived radionuclides and alpha emitters whose concentration exceeds the limits for short lived waste; and

  high level: waste with such a concentration of radionuclides that generation of thermal powers "shall be considered" during its disposal and storage.

  11.5  In putting forward this proposal, the Commission makes it clear that the classification would apply only for national and international communication purposes, and to facilitate information management in this field. In particular, it stresses that the intention is not to replace the technical criteria already used by Member State regulatory authorities for the management of radioactive waste disposal (which are said to require more detailed information than a Community-wide classification system can provide). The Commission also suggests that the classification proposed for international communication could be used initially in parallel with national systems until 1 January 2002.

The Government's view

  11.6  In his Explanatory Memorandum of 4 November 1999, the Parliamentary Under-Secretary of State at the Department of the Environment, Transport and the Regions (Mr Mullin) says that, since no changes to Member States' existing systems for regulatory purposes are proposed, the Recommendation — which he stresses is not legally binding — is likely to have "marginal" implications for UK waste management policy. He adds that there will, however, be a small cost incurred by Government, the regulators and the nuclear industry in examining its impact on the 1000 or so different waste streams whose classification would need to be established.

Conclusion

  11.7  Since this document is a non-binding Recommendation which has already been adopted by the Commission, and which we understand is not be discussed by the Council, we see no reason to withhold clearance. It does, however, give rise to three questions on which we would welcome the Government's comments.

  11.8  First, the underlying aim is apparently to achieve a common classification between different Member States in order to enable meaningful international comparisons to be drawn. It therefore seems curious that the Commission should have chosen a Recommendation, since, if Member States chose not to observe its terms, that objective would clearly be thwarted. In view of this, would not an alternative approach involving a Regulation have been more appropriate in this case?

  11.9  Secondly, we note the Minister's comment that the proposal would have only marginal implications for UK waste management policy. On the other hand, it seems to us that to have two separate classifications systems, albeit for different purposes, does run the risk of creating confusion in an area where this is obviously best avoided, given the unease which many members of the public feel about the whole subject of radioactive waste disposal. We hope the Minister will be able to assure us that our concerns are unfounded.

  11.10  Thirdly, we would like to know whether the proposed classification system would apply only to material originating within the EU, or whether it will apply also to material imported into the EU, for example, from the Central and Eastern European countries. If the classification would apply to waste originating from third countries, who would be responsible for deciding the appropriate category for each batch of waste?

  11.11  We would be grateful if the Minister could respond by 10 December so that we could consider this again before Christmas.


45   The activity of wastes is the number of radioactive disintegrations per second in a kilogramme of material. Alpha decay is the emission of a helium nucleus; beta decay the emission of an electron; and gamma decay the emission of high energy X-rays from an atom. Back

46   OJ No. C 158/2, 25.6.92. Back


 
previous page contents next page

House of Commons home page Parliament home page House of Lords home page search page enquiries

© Parliamentary copyright 1999
Prepared 7 December 1999