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SITING PROCESS FOR HLW REPOSITORY IN JAPAN
SITING PROCESS FOR HLW REPOSITORY IN JAPAN
In the year 2000, the geological disposal program for high-level radioactive waste in Japan moved from the phase of generic research and development (R&D) into the phase of implementation. Following legislation entitled the “Specified Radioactive Waste Final Disposal Act”, the Nuclear Waste Management Organization of Japan (NUMO) was established as the implementing organization.
Long Term Governance for Radioactive Waste Management WP4
Long Term Governance for Radioactive Waste Management WP4
The purpose of COWAM2 Work Package 4 (WP4) on "e;long term governance"e; was to identify, discuss and analyse the institutional, ethical, economic and legal considerations raised by long term radioactive waste storage or disposal on the three interrelated issues of: (i) responsibility and ownership of radioactive waste over long term, (ii) continuity of local dialogue between stakeholders and monitoring of radioactive waste management facilities, and (iii) compensation and sustainable development.
Guidance on the Selection of PTA Tools: For Stakeholders involved in Radioactive Waste Governance WP1
Guidance on the Selection of PTA Tools: For Stakeholders involved in Radioactive Waste Governance WP1
This research on "e;Guidance on the selection of PTA tools for stakeholders involved in radioactive waste governance"e; was performed under the umbrella of COWAM2-'Work Package 1' (WP1). Through a dialogue on enhancing involvement at a local level, WP1 allows local stakeholders to examine the issues they face in building a democratic local governance process. WP1 also tests how Participatory Technology Assessment (PTA) methods can offer a consensual framework and a platform for deliberative co-decision among scientific and societal actors at the local level.
Recommendation Group 1
Recommendation Group 1
European-level Guidelines for the Inclusive Governance of Radioactive Waste Management
European-level Guidelines for the Inclusive Governance of Radioactive Waste Management
CIP (Community Waste Management In Practice) is a research action gathering a wide spectrum of stakeholders from five European countries, interested in how society should manage the radioactive wastes that result from nuclear power production and/or from medical, military or industrial applications.
WP 2 Appendix 4 Estudio Sociológico Sobre La A.M.A.C. Y El Hecho Nuclear En España
WP 2 Appendix 4 Estudio Sociológico Sobre La A.M.A.C. Y El Hecho Nuclear En España
LONG TERM GOVERNANCE FOR RADIOACTIVE WASTE MANAGEMENT ANNEX OF THE FINAL REPORT OF COWAM2 - WORK PACKAGE 4
LONG TERM GOVERNANCE FOR RADIOACTIVE WASTE MANAGEMENT ANNEX OF THE FINAL REPORT OF COWAM2 - WORK PACKAGE 4
The purpose of COWAM2 Work Package 4 (WP4) on "e;long term governance"e; was to identify, discuss and analyse the institutional, ethical, economic and legal considerations raised by long term radioactive waste storage or disposal on the three interrelated issues of: (i) responsibility and ownership of radioactive waste over long term, (ii) continuity of local dialogue between stakeholders and monitoring of radioactive waste management facilities, and (iii) compensation and sustainable development.
Tools for Local Stakeholders in Radioactive Waste Governance: Challenges and Benefits of Selected PTA Techniques WP1
Tools for Local Stakeholders in Radioactive Waste Governance: Challenges and Benefits of Selected PTA Techniques WP1
The investigation consists of three parts and shall provide an input to the – empirical – PTA-2 study to be undertaken by SCK•CEN (called “lens”):<br>A. Compilation of – selected – existing PTA methods and procedures identifying requisites, practices, benefits, and challenges to answer the key questions in the context of WP1 about a PTA “toolbox”: “What can you apply, when can you apply, and what is needed to apply?” The multi-dimensional context of a possible “PTA situation” is analysed; suitable and nonsuitable methods, techniques and procedures are discussed.<br>B.
Recommendation Group 5
Recommendation Group 5
Final Report: Influence of Local Actors on National Decision-making Processes WP2
Final Report: Influence of Local Actors on National Decision-making Processes WP2
Work Package 2 (WP2) focused on the ways in which local stakeholders can influence national decision-making processes on radioactive waste management (RWM). The participants in WP2 were particularly interested in examining how local stakeholders could contribute to national debates. Their interest stemmed from the fact that participants from France, Spain and the United Kingdom — who made up the majority of the WP2 group — were engaged, as stakeholders, in the decision-making processes that were under way in each of those countries.
Recommendation Group 2
Recommendation Group 2
LEARNING AND ADAPTING TO SOCIETAL REQUIREMENTS
LEARNING AND ADAPTING TO SOCIETAL REQUIREMENTS
Reflections on Siting Approaches for Radioactive Waste Facilities: Synthesising Principles Based on International Learning
10-year Record of Learning Factual List of Activities and Investigated Topics, and of People Who Contributed to Them
The Partnership Approach to Siting and Developing Radioactive Waste Management Facilities
The Partnership Approach to Siting and Developing Radioactive Waste Management Facilities
History shows that the search for sites for radioactive waste management facilities has been marred by conflicts and delays. Affected communities have often objected that their concerns and interests were not addressed. In response, institutions have progressively turned away from the traditional “decide, announce and defend” model, and are learning to “engage, interact and co-operate”. This shift has fostered the emergence of partnerships between the proponent of the facility and the potential host community, as shown in a recent NEA study.
From Information and Consultation to Citizen Influence and Power: 10-year Evolution in Public Involvement in Radioactive Waste Management
Recommendation Group 6
Recommendation Group 6
REFLECTIONS ON THE INFLUENCE OF THE LOCAL ACTORS ON THE NATIONAL NUCLEAR WASTE MANAGEMENT FRAMEWORK
Locating a radioactive waste repository in the ring of fire
Locating a radioactive waste repository in the ring of fire
The scientific, technical, and sociopolitical challenges of finding a secure site for a geological repository for radioactive wastes have created a long and stony path for many countries. Japan carried out many years of research and development before taking its first steps in site selection.
H12: Project to Establish the Scientific and Technical Basis for HLW Disposal in Japan Project Overview Report
H12: Project to Establish the Scientific and Technical Basis for HLW Disposal in Japan Project Overview Report
As outlined in the overall program for high-level waste (HLW) management in Japan, defined by the Atomic Energy Commission (AEC), HWL separated from spent nuclear fuel during reprocessing will be immobilized in a glass matrix and stored for a period of 30 to 50 years to allow cooling; it will then be disposed of in a stable deep geological formation.
Evaluating Site Suitability for a HLW Repository
Evaluating Site Suitability for a HLW Repository
The primary objective of government policy, and of NUMO in implementing this policy, is to
ensure that a repository for Japan’s high-level radioactive waste is located so as to provide
secure isolation of the waste and adequate safety for present and future generations. This
means that the site has to be chosen carefully, taking full account of all its characteristics. In
order to address these characteristics in an orderly and structured manner, we have established
Joint Convention on the Safety of Spent Fuel Management and on the Safety of Radioactive Waste Management, National Report of Japan for the Third Review Meeting
Joint Convention on the Safety of Spent Fuel Management and on the Safety of Radioactive Waste Management, National Report of Japan for the Third Review Meeting
Nuclear facilities in Japan are as listed in the following table, the details of which are described in Section D.
H12: Project to Establish the Scientific and Technical Basis for HLW Disposal in Japan Supplementary Report Background of Geologic Disposal
H12: Project to Establish the Scientific and Technical Basis for HLW Disposal in Japan Supplementary Report Background of Geologic Disposal
Radioactive waste is produced from a wide range of human activities. The wastes arising from the nuclear fuel cycle occur as a wide range of materials and in many different physical and chemical forms, contaminated with varying activities of radionuclides. Their common feature is the potential hazard associated with their radioactivity and the need to manage them in such a way as to protect the human environment. The safe disposal of radioactive waste is a key reequirement of the nuclear industry worldwide.
The NUMO Structured Approach to HLW Disposal in Japan
The NUMO Structured Approach to HLW Disposal in Japan
The constraints set by the Japanese HLW disposal programme – particularly associated with
the decision to initiate siting by an open call for volunteers to host a geological repository –
pose particular challenges for repository project management. In order to maintain the
flexibility required to respond to the conditions found at volunteer sites, NUMO has not
published reference designs or site characterisation plans, as is normal for programmes
progressing by site nomination. Instead, we have developed a methodology – the NUMO
Joint Convention on the Safety of Spent Fuel Management and on the Safety of Radioactive Waste Management, National Report of Japan for the Fourth Review Meeting
Joint Convention on the Safety of Spent Fuel Management and on the Safety of Radioactive Waste Management, National Report of Japan for the Fourth Review Meeting
Nuclear facilities in Japan are listed in Table A1-1, the details of which are described in Section D.<br/>The overview of spent fuel management and radioactive waste management and the current<br/>status of the preparation of radioactive waste disposal regulation system are shown in Table<br/>A1-2 and Table A1-3 respectively.