Link to the study - European Parliament - Europa
Link to the study - European Parliament - Europa Link to the study - European Parliament - Europa
Policy Department D: Budgetary Affairs ____________________________________________________________________________________________ 3. IDENTIFICATION AND DESCRIPTION OF BEST PRACTICES IN DECOMMISSIONING This chapter describes project practices and experiences made in decommissioning in several western European countries. The aim is to identify current best practices in such projects. The identified best practices shall, in later chapters, be used to compare the projects in Bulgaria, Lithuania and Slovakia with these, to identify differences that can or have caused delays and cost-overruns and to identify factors that have the potential to cause disadvantageous developments in respect to costs and risks. They shall also be used to draw recommendations for improving those projects and to avoid those drawbacks in the future. Chapter 3.1: Discusses criteria for identifying best practices in Europe and also names exclusion criteria; Selects the depth and extent to which the selected examples have to be described and evaluated, and lists aspects to be looked at in detail. The examples from France are described and evaluated in chapter 3.2. Selected aspects from a large decommissioning project in the UK are further described and evaluated in chapter 3.3. Chapter 3.4 describes and evaluates the case of Energiewerke Nord (EWN) in Germany in detail. The overall results of the best practice examples are summarized in chapter 3.5. 3.1. SELECTION CRITERIA FOR COMPARISON The following criteria for the selection of examples are seen as relevant to ensure an as-close-aspossible comparability with the projects in Bulgaria, Lithuania and Slovakia: 1. Reactor size and type The size of reactor(s) to be decommissioned shall be in the range above 100 MWel in order that the complete project framework is comparable to the three countries in terms of its complexity, its management and coordination requirements, its regulatory requirements, etc.. Reactors smaller than 100 MWel - such as the pilot plant Versuchsatomkraftwerk Kahl (VAK)/Germany, even though one of the few projects that has been completely decommissioned - are substantially different in this regard and need not to be taken into account. 2. Operational phase duration Contamination levels, technological complexity, regulatory requirements and waste management issues are only comparable with nuclear power plants operated over periods of at least several years. Shorter term operated plants, such as Niederaichbach/Germany or Heißdampfreaktor Großwelsheim/Germany, even though decommissioning to the 'Green Field' status has been totally completed, do not yield a comparable scale due to significantly lower levels of contamination. 52
Nuclear Decommissioning: Management of Costs and Risks ____________________________________________________________________________________________ 3. Owner type and organisation The basic distinction here is between private operator organisations such as private energy producing companies, and public owners on the federal or state level. As all of the three eastern European projects are public organisations, this type of organisations is better comparable. It would be scientifically interesting to discuss whether project organisation and management as well as experiences differ significantly under a private setting, but that comparison does not contribute much to the central task of this study. 4. Decommissioning stage and level The selected examples shall be in an advanced stage of physical decommissioning so that advantages and lessons learned from that project are already identifiable. Projects in an early stage are less usable to derive experiences from because all work is only in a preliminary stage. Aspects to be looked at and evaluated As all decommissioning projects in question are individually planned and implemented projects with a: Specific technical design and condition; Specific operational history, determining the type and extent of contamination in the facility; Specific organisational setting and owner condition; Specific national and regulatory framework condition it makes no sense to compare the projects in any technical detail, with regard to specific timeframes and cost figures. The projects are rather described and evaluated with regard to the following aspects: 5. How is the decision-making and the control over the organisation’s strategic decisions organised (external oversight, management control)? 6. How is the responsible organisation’s internal structure designed (management, project organisation, risk management, personnel management, etc.)? 7. How is national and international funding organised? Selecting examples For selecting examples that fit the selection criteria described above the following criteria were applied: As Figure 1 (on page 32) shows that only France, Germany and the UK are among the countries having more than four reactors in shutdown mode. So coverage of the situation in these three countries yields a representative picture. Figure 2 (on page 33) and Figure 3 (on page 34) summarise the size distribution and the operating time of reactors in the EU that are currently under shutdown and in different phases of 53
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Policy Department D: Budgetary Affairs<br />
____________________________________________________________________________________________<br />
3. IDENTIFICATION AND DESCRIPTION OF BEST PRACTICES IN<br />
DECOMMISSIONING<br />
This chapter describes project practices and experiences made in decommissioning in several<br />
western <strong>European</strong> countries. The aim is <strong>to</strong> identify current best practices in such projects. The<br />
identified best practices shall, in later chapters, be used <strong>to</strong> compare <strong>the</strong> projects in Bulgaria, Lithuania<br />
and Slovakia with <strong>the</strong>se, <strong>to</strong> identify differences that can or have caused delays and cost-overruns and<br />
<strong>to</strong> identify fac<strong>to</strong>rs that have <strong>the</strong> potential <strong>to</strong> cause disadvantageous developments in respect <strong>to</strong> costs<br />
and risks. They shall also be used <strong>to</strong> draw recommendations for improving those projects and <strong>to</strong><br />
avoid those drawbacks in <strong>the</strong> future.<br />
Chapter 3.1:<br />
Discusses criteria for identifying best practices in Europe and also names exclusion criteria;<br />
Selects <strong>the</strong> depth and extent <strong>to</strong> which <strong>the</strong> selected examples have <strong>to</strong> be described and<br />
evaluated, and lists aspects <strong>to</strong> be looked at in detail.<br />
The examples from France are described and evaluated in chapter 3.2.<br />
Selected aspects from a large decommissioning project in <strong>the</strong> UK are fur<strong>the</strong>r described and evaluated<br />
in chapter 3.3.<br />
Chapter 3.4 describes and evaluates <strong>the</strong> case of Energiewerke Nord (EWN) in Germany in detail.<br />
The overall results of <strong>the</strong> best practice examples are summarized in chapter 3.5.<br />
3.1. SELECTION CRITERIA FOR COMPARISON<br />
The following criteria for <strong>the</strong> selection of examples are seen as relevant <strong>to</strong> ensure an as-close-aspossible<br />
comparability with <strong>the</strong> projects in Bulgaria, Lithuania and Slovakia:<br />
1. Reac<strong>to</strong>r size and type<br />
The size of reac<strong>to</strong>r(s) <strong>to</strong> be decommissioned shall be in <strong>the</strong> range above 100 MWel in order that<br />
<strong>the</strong> complete project framework is comparable <strong>to</strong> <strong>the</strong> three countries in terms of its complexity,<br />
its management and coordination requirements, its regula<strong>to</strong>ry requirements, etc.. Reac<strong>to</strong>rs<br />
smaller than 100 MWel - such as <strong>the</strong> pilot plant Versuchsa<strong>to</strong>mkraftwerk Kahl (VAK)/Germany,<br />
even though one of <strong>the</strong> few projects that has been completely decommissioned - are<br />
substantially different in this regard and need not <strong>to</strong> be taken in<strong>to</strong> account.<br />
2. Operational phase duration<br />
Contamination levels, technological complexity, regula<strong>to</strong>ry requirements and waste<br />
management issues are only comparable with nuclear power plants operated over periods of at<br />
least several years. Shorter term operated plants, such as Niederaichbach/Germany or<br />
Heißdampfreak<strong>to</strong>r Großwelsheim/Germany, even though decommissioning <strong>to</strong> <strong>the</strong> 'Green Field'<br />
status has been <strong>to</strong>tally completed, do not yield a comparable scale due <strong>to</strong> significantly lower<br />
levels of contamination.<br />
52