Current Radioactive Waste Management Policy in the Netherlands

Author(s):  
Henk C. G. M. Brouwer
2022 ◽  
pp. 101-108
Author(s):  
E. A. Sharyapova ◽  
A. V. Shuvaev ◽  
I. O. Zhavoronkova

The topic of the article is relevant — the problem of radioactive waste management, since the task of increasing the level of security of organizations of the country’s nuclear power-industrial complexes is one of the priorities for ensuring state and public security in the National Security Strategy of the Russian Federation. The growth of radioactive waste is a hazard to human health and the environment. The state needs a unified regulation of the radioactive waste management policy and prevention of radioactive disasters.


2012 ◽  
Vol 1475 ◽  
Author(s):  
Pablo Zuloaga ◽  
Julio Astudillo

ABSTRACTSpanish Radioactive Waste Management policy is established by the Government and implemented by ENRESA. The General Plan (GRWP) covers the analysis of the actual and foreseen inventories of spent fuel and all categories of radioactive waste, their present situation, the management strategy and actions identified, as well as funding and financial provisions. Very Low (VLLW) and Low and Intermediate Level Waste (LILW) are disposed of at El Cabril facility, which has two separate disposal areas: one intended for VLLW, based on clay and polyethylene and started up in 2006; and one for LILW conditioned in retrievable concrete containers, commissioned in 1992. Spent fuel (SF) is being stored in pools and in two dry storage installations. The priority is the development of the SF and HLW centralized storage facility. In 2009, the Government launched a call for candidate municipalities, in a public, participative process. In September 2010 a report was sent to the Cabinet, proposing eight volunteer communities, four of them deemed preferred. In the 90’s a deep geological repository (DGR) site identification program was carried out. DGR basic designs and associated performance assessments were developed in three rock types. ENRESA has set a research program that includes research projects in order to strengthen the link between management and scientific basis and improve the performance assessment, directed to the behavior of barriers, fuel or waste forms in different storage and final disposal conditions, and characterization techniques. There is also a participation in connected fields or supporting decision-making, such as advanced separation and transmutation.


1982 ◽  
Vol 15 ◽  
Author(s):  
F S Feates ◽  
H J Richards

ABSTRACTIn the United Kingdom the responsibility for radioactive waste management policy lies with the environmental Ministers. The Department of the Environment is also responsible in England for authorisation of all radioactive waste disposal activities and has its own Radiochemical Inspectorate to ensure that government policy is implemented. An independent Radioactive Waste Management Advisory Committee reports directly to the Secretary of State for the Environment.Low-level wastes are currently disposed of by shallow burial or to the deep ocean. Sites for the disposal of intermediate-level wastes are being sought as a matter of urgency and heat-emitting, reprocessing wastes will be stored on the surface for at least fifty years. The rationale of this policy is explained.


Author(s):  
Hans Code´e ◽  
Ewoud Verhoef

Time will render radioactive waste harmless. How can we manage the time radioactive substances remain harmful? Just ‘wait and see’ or ‘marking time’ is not an option. We need to isolate the waste from our living environment and control it as long as necessary. For the situation in the Netherlands, it is obvious that a period of long term storage is needed. Both the small volume of waste and the limited financial possibilities are determining factors. Time is needed to let the volume of waste grow and to let the money, needed for disposal, grow in a capital growth fund. An organisation such as COVRA — the radioactive waste organisation in the Netherlands — can only function when it has good, open and transparent relationship with the public and particularly with the local population. If we tell people that we safely store radioactive waste for 100 years, they often ask: “That long?” How can we explain the long-term aspect of radioactive waste management in a way people can relate to? In this paper, an overview is given of the activities of COVRA on the communication of radioactive waste management.


Author(s):  
E. William Colglazier

A sustained and definitive radioactive waste management policy has been a elusive goal for our nation since the beginning of the nuclear age. An atmosphere of contentiousness and mistrust among the interested parties, fed by a long history of policy reversals, delays, false starts, legal and jurisdictional wrangles, and scientific overconfidence and played out against the background of public concern with nuclear power and weapons issues generally, has dogged society's attempts to come to grips with the radioactive waste-management issue. The policy conflicts have become so intense and intractable that Congress has been forced to deal with the issue periodically. The year 1982 was one watershed year for congressional action on high-level nuclear waste, and 1987 proved to be another. This chapter will examine ethical and value issues in radioactive waste management (RWM), with a special emphasis on disputes about scientific evidence. Controversies over evidence have been particularly important because of the many scientific uncertainties and problems inherent in trying to ensure that nuclear waste in a geological repository will harm neither people nor the environment for the thousands of years that the waste will remain hazardous. This requirement of guaranteeing adequate safety over millennia is an unprecedented undertaking for our regulatory and scientific institutions. The first section of the chapter will provide a brief historical overview of the national policy disputes in radioactive waste management, and the second section will discuss some of the key value issues that have been at the heart of the controversies. Our approach is to delineate key policy issues and to separate the value components of each into three categories: procedural, distributional, and evidential. Key stakeholders—Congress, federal agencies, the nuclear industry, utilities, environmental groups, state governments, Native American tribes, local communities—take particular policy positions justified in part on the basis of procedural, distributional, and evidential values. Procedural values refer to who should make what decision for whom and by what process. Distributional values concern what is a fair allocation of costs, benefits, and risks to the affected parties and to society as a whole. Evidential values refer to what counts as evidence, for example, what type and degree of scientific evidence is sufficient and admissible in making a particular societal decision, especially in the face of large scientific unknowns and significant social and scientific debate. Categories of "value concerns" thus include fairness and appropriateness of process, outcomes, and evidence.


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