- •Preface
- •Acronyms
- •Introduction
- •Background and objectives
- •Content, format and presentation
- •Radioactive waste management in context
- •Waste sources and classification
- •Introduction
- •Radioactive waste
- •Waste classification
- •Origins of radioactive waste
- •Nuclear fuel cycle
- •Mining
- •Fuel production
- •Reactor operation
- •Reprocessing
- •Reactor decommissioning
- •Medicine, industry and research
- •Medicine
- •Industry
- •Research
- •Military wastes
- •Conditioning of radioactive wastes
- •Treatment
- •Compaction
- •Incineration
- •Conditioning
- •Cementation
- •Bituminisation
- •Resin
- •Vitrification
- •Spent fuel
- •Process qualification/product quality
- •Volumes of waste
- •Inventories
- •Inventory types
- •Types of data recorded
- •Radiological data
- •Chemical data
- •Physical data
- •Secondary data
- •Radionuclides occurring in the nuclear fuel cycle
- •Simplifying the number of waste types
- •Radionuclide inventory priorities
- •Material priorities
- •Inventory evolution
- •Assumptions
- •Errors
- •Uncertainties
- •Conclusions
- •Acknowledgements
- •References
- •Development of geological disposal concepts
- •Introduction
- •Historical evolution of geological disposal concepts
- •Geological disposal
- •Definitions and comparison with near-surface disposal
- •Development of geological disposal concepts
- •Roles of the geosphere in disposal options
- •Physical stability
- •Hydrogeology
- •Geochemistry
- •Overview
- •Alternatives to geological disposal
- •Introduction
- •Politically blocked options: sub-seabed and Antarctic icecap disposal
- •Sea dumping and sub-seabed disposal
- •Antarctic icesheet disposal
- •Technically impractical options; partitioning and transmutation, space disposal and icesheet disposal
- •Partitioning and Transmutation
- •Space disposal
- •Icesheets and permafrost
- •Non-options; long-term surface storage
- •Alternatives to conventional repositories
- •Introduction
- •Alternative geological disposal concepts
- •Utilising existing underground facilities
- •Extended storage options (CARE)
- •Injection into deep aquifers and caverns
- •Deep boreholes
- •Rock melting
- •The international option: technical aspects
- •Alternative concepts: fitting the management option to future boundary conditions
- •Conclusions
- •References
- •Site selection and characterisation
- •Introduction
- •Prescriptive/geologically led
- •Sophisticated/advocacy led
- •Pragmatic/technically led
- •Centralised/geologically led
- •Conclusions to be drawn
- •Lessons to be learned (see Table 4.2)
- •Site characterisation
- •Can we define the natural environment sufficiently thoroughly?
- •Sedimentary environments
- •Hydrogeology
- •The regional hydrogeological model
- •More local hydrogeological model(s)
- •Crystalline rock environments
- •Lithology and structure
- •Hydrogeology
- •Hydrogeochemistry
- •Any geological environment
- •References
- •Repository design
- •Introduction: general framework of the design process
- •Identification of design requirements/constraints
- •Concept development
- •Major components of the disposal system and safety functions
- •A structured approach for concept development
- •Detailed design/specifications of subsystems
- •Near-field processes and design issues
- •Design approach and methodologies
- •Design confirmation and demonstration
- •Interaction with PA/SA
- •Demonstration and QA
- •Repository management
- •Future perspectives
- •References
- •Assessment of the safety and performance of a radioactive waste repository
- •Introduction
- •The role of SA and the safety case in decision-making
- •SA tasks
- •System description
- •Identification of scenarios and cases for analysis
- •Consequence analysis
- •Timescales for evaluation
- •Constructing and presenting a safety case
- •References
- •Repository implementation
- •Legal and regulatory framework; organisational structures
- •Waste management strategies
- •The need for a clear policy and strategy
- •Timetables vary widely
- •Activities in development of a geological repository
- •Concept development
- •Siting
- •Repository design
- •Licensing
- •Construction
- •Operation
- •Monitoring
- •Research and development
- •The staging process
- •Attributes of adaptive staging
- •The decision-making process
- •Status of geological disposal programmes
- •Overview
- •Status of geological disposal projects in selected countries
- •International repositories
- •Costs and financing
- •Cost estimates
- •Financing
- •Conclusions
- •Acknowledgements
- •References
- •Research and development infrastructure
- •Introduction: Management of research and development
- •Drivers for research and development
- •Organisation of R&D
- •R&D in specialised (nuclear) facilities
- •Introduction
- •Inventory
- •Release of radionuclides from waste forms
- •Solubility and sorption
- •Waste form dissolution
- •Colloids
- •Organic degradation products
- •Gas generation
- •Conventional R&D
- •Engineered barriers
- •Corrosion
- •Buffer and backfill materials
- •Container fabrication
- •Natural barriers
- •Geochemistry and groundwater flow
- •Gas transport and two-phase flow
- •Biosphere
- •Radionuclide concentration and dispersion in the biosphere
- •Climate change
- •Landscape change
- •Underground rock laboratories
- •URLs in sediments
- •Nature’s laboratories: studies of the natural environment
- •General
- •Corrosion
- •Cement
- •Clay materials
- •Degradation of organic materials
- •Glass corrosion
- •Radionuclide migration
- •Model and database development
- •Conclusions
- •References
- •Building confidence in the safe disposal of radioactive waste
- •Growing nuclear concerns
- •Communication systems in waste management programmes
- •The Swiss programme
- •The Japanese programme
- •Examples of communication styles in other countries
- •Finland
- •Sweden
- •France
- •United Kingdom
- •Comparisons between communication styles in Finland, France, Sweden and the United Kingdom
- •Lessons for the future
- •What is the way forward?
- •Acknowledgements
- •References
- •A look to the future
- •Introduction
- •Current trends in repository programmes
- •Priorities for future efforts
- •Waste characterisation
- •Operational safety
- •Emplacement technologies
- •Knowledge management
- •Alternative designs and optimisation processes
- •Materials technology
- •Novel construction/immobilisation materials: the example of low pH cement
- •Future SA code development
- •Implications for environmental protection: disposal of other wastes
- •Conclusions
- •References
- •Index
6 |
L.E. McKinley and W.R. Alexander |
(although this is more of a problem in some countries than others), stop talking in technological riddles and come forward and communicate plainly and clearly with all stakeholders – the public, politicians, other scientists and engineers – and, more importantly, listen to their concerns. Only with open dialogue – a two-way process – can the ethically correct solution be achieved, namely to establish facilities for the safe disposal of radioactive waste in our lifetime – and not that of our children or children’s children.
Chapter 10 notes that, despite the fact that the principles underlying the deep geological disposal of radwaste are relatively simple, actually constructing a repository is, in fact, a remarkably complex task. Potentially, the most arduous is the necessary integration of socio-political factors with the technical areas, a strand which runs throughout the book, even though the vast majority of the authors have a technical background (engineers, chemists, physicists, geologists, etc.).
Despite this, however, the main focus of the book remains technical and thus Chapter 10 attempts to put all the technical information presented in the book in context by examining trends in progress with implementation of repository programmes and highlighting areas where priorities for future efforts could lie. It considers the possible significance of technological developments and implications for environmental protection – and ends by asking why there remains any doubt that deep geological disposal of radwaste is the only practicable solution.
1.3. Radioactive waste management in context
Finally, it is worth providing some comments on the polarisation of the radioactive waste disposal issue and its coupling to nuclear power generation. It was noted that renewed interest in this topic is associated with the debate on the role of nuclear in reducing greenhouse gas emissions. As such, disposal projects have been violently opposed by those who are against nuclear power, rather than waste disposal per se. Indeed, some groups have offered to drop their opposition if this is coupled to a nuclear phase-out. Such a position is fundamentally dishonest – if there are no basic technical concerns associated with the waste disposal issue then this should be introduced as a highly favourable attribute of this option. Combining claims for the unacceptability of nuclear due to the unresolved waste disposal issue together with the assumption that everything can be solved as soon as a phase-out of nuclear is initiated involves true looking-glass logic.
Ethically, the generation benefiting from nuclear technology should implement projects to ensure its safe management. Higher activity radwastes suitable for geological disposal exist now and are stored at a wide variety of facilities around the world. Apart from a basic philosophical objection to the entire idea of geological disposal, arguments for delaying moving onwards are often based on the claim that new technology might bring better solutions. This may well be the case, but that is not a justification for doing nothing now. As will be seen in this book, geological disposal options already offer levels of safety far in advance of anything considered for any other industrial activity. It has to be assured that such projects are implemented properly, but this is completely feasible with existing technology. Indeed, the over-design of repositories, which is possible due to the large value of nuclear power relative to the small amount of waste produced, might be considered a rather profligate use of resources and further efforts to
Introduction |
7 |
reduce presently minimal risks goes against the general principle of sustainability. There are much better ways to improve total environmental safety – even if only the potential benefits of bringing treatment of chemotoxic wastes to a similar level is considered.
Ethical and technical arguments may cut little ice with those religiously opposed to ‘‘dumping’’ of radioactive waste but, recently, an emerging concern may help to improve the push towards implementing projects – concerns about the security of surface stores, particularly with regard to the potential consequences of terrorist attacks. It is true that the real hazard involved from this source is exaggerated and, in fact, radwaste stores are very hard targets compared to the wide range of soft options available to the determined terrorist. However, the very fact that this causes great concern indicates that such facilities could be targets, especially if the aims were more psychological than physical.
The authors of the chapters of this book may have very different opinions on the need for nuclear power and the timescales for repository implementation, but all would agree that any debate on these topics should be founded on sound science. We hope that the following chapters will help to build this foundation.
1.4. Reference
NRC (1957). The disposal of radioactive waste on land; National Research Council, National Academic Press, Washington DC, USA.