1 A Consultancy on management of large amounts of radioactive waste after an emergency situation ~ Experience on aftermath of Fukushima Daiichi NPS accident.

Slides:



Advertisements
Similar presentations
Proposed UK Strategy for the Management of Solid Radioactive Waste from the Non-Nuclear Industry Katherine Mondon – representing the Department of Energy.
Advertisements

Lesson 3 Responding to Emergency Events. For additional information or questions please contact Toledo-Lucas County Health Department APC:
Development of WM strategy and implementation 1. Clarification of dominant nuclides and important characteristics of waste ( Cs only? with long-lived nuclides?
1 KRB-A (Grundremmingen, Germany). 2 Type:Boiling Water Reactor Power: 250 MW(e) Started in 1966, shut down in 1977 First commercial power reactor in.
International Atomic Energy Agency IX.4.3. Waste management.
Chapter 24 Solid and Hazardous Wastes
Copyright [insert date set by system] by [CH2M HILL Entity] Company Confidential Update on Fukushima Daiichi NPP 1 – Preparations for Core Debris Removal.
Exemption, Clearance, Discharges
 Progress with the revision and consolidation of the European Basic Safety Standards Directive Stefan Mundigl European Commission DG Energy and Transport.
1 RADIOACTIVE WASTE MANAGEMENT (PART 1) A RAHMAN RWE NUKEM Ltd (UK)
MODULE “PROJECT MANAGEMENT AND CONTROL” EMERGENCY PLANNING SAFE DECOMMISSIONING OF NUCLEAR POWER PLANTS Project BG/04/B/F/PP , Programme “Leonardo.
Licensing of Nuclear Power Plants in Pakistan
School for drafting regulations Nuclear Safety Decommissioning Vienna, 2-7 December 2012 Tea Bilic Zabric.
IAEA International Atomic Energy Agency CS-81 to prepare a work plan and material for developing a guidance on management of large amounts of radioactive.
1 Risk Assessment Develop Objectives And Goals Develop and Screen Cleanup Alternatives Select Final Cleanup Alternative Communicate Decisions to the Public.
IAEA International Atomic Energy Agency Consultants’ Meeting to develop a guidance document on management of large amounts of radioactive waste after an.
SÄTEILYTURVAKESKUS STRÅLSÄKERHETSCENTRALEN RADIATION AND NUCLEAR SAFETY AUTHORITY Protection of the environment from ionising radiation - views of a regulator.
MODULE “STRATEGY DEVELOPMENT”
PART IX: EMERGENCY EXPOSURE SITUATIONS Module IX.1: Generic requirements for emergency exposure situations Lesson IX.1-2: General Requirements Lecture.
Bapetco NORM Control Case Study IDENTIFY ASSESS CONTROL & RECOVERY.
IAEA International Atomic Energy Agency International Workshop on the Safe Disposal of Low Level Radioactive Waste WG3 debriefing.
Technical Meeting on Evaluation Methodology for Nuclear Power Infrastructure Development December, 2008 Nuclear Safety in Infrastructure Building.
Update on progress with development of DS459
Authorization and Inspection of Cyclotron Facilities Authorization for the Decommissioning of the Facility.
IAEA International Atomic Energy Agency SAFETY REQUIREMENTS FOR PREDISPOSAL MANAGEMENT OF RADIOACTIVE WASTE Luc Baekelandt Safety.
IAEA International Atomic Energy Agency Roger Seitz Addressing Future Human Actions for Safety Assessment Summary from CSM on Human Action And Intrusion.
Handling of Future Human Actions in the safety assessment SR-Site Eva Andersson.
Disposal of Waste from Contaminated Areas around Fukushima RSLS meeting October 23,
School for Drafting Regulations on Radiation Safety Vienna, November 2012 Rules and responsibilities of the regulatory body Jiří Veselý, SONS, Czech republic.
MODULE “COST ESTIMATION, CALCULATION AND COST CONTROL” SAFE DECOMMISSIONING OF NUCLEAR POWER PLANTS Project BG/04/B/F/PP , Programme “Leonardo da.
1 Chapter 6: Material Management Helmut Steiner Ulrich Priesmeyer Kernkraftwerk Gundremmingen GmbH Priesmeyer, KRB A, 6. Material Management.
Michael Webster (Cameco Corporation) Tamara Yankovich (IAEA, Formerly Saskatchewan Research Council) Martin Klukas (Atomic Energy of Canada Limited) IAEA.
International Atomic Energy Agency IX.4.4. Pre-disposal waste management Safety Standards.
RER/9/111: Establishing a Sustainable National Regulatory Infrastructure for Nuclear and Radiation Safety TCEU School of Drafting Regulations November.
MODULE “PROJECT MANAGEMENT AND CONTROL” SAFETY ASSESSMENT DURING DECOMMISSIONING SAFE DECOMMISSIONING OF NUCLEAR POWER PLANTS Project BG/04/B/F/PP ,
Source Control Phases I-II: Source Control Phases I-II: Main findings  Facility: drinking water and sewage treatment utility in Apatity, Murmansk region,
IAEA International Atomic Energy Agency. IAEA Outline Learning Objectives Introduction IRRS review of regulations and guides Relevant safety standards.
MODULE “PREPARING AND MANAGEMENT OF DOCUMENTATION” SAFE DECOMMISSIONING OF NUCLEAR POWER PLANTS Project BG/04/B/F/PP , Programme “Leonardo da Vinci”
Regulatory Approach to Radioactive Waste Management and Remediation in Central Asia Tamara Zhunussova Vienna, IAEA, 6-8 November, 2012.
MODULE “PROJECT MANAGEMENT AND CONTROL” WASTE MANAGEMENT SAFE DECOMMISSIONING OF NUCLEAR POWER PLANTS Project BG/04/B/F/PP , Programme “Leonardo.
56th Regular Session of the IAEA General Conference
Intervention for Chronic and Emergency Exposure Situations Module IX Basic Concepts for Emergency preparedness and Response for a nuclear accident or.
【機密性2、機構内限り 】 Phase to start waste management Main RN OriginWaste typeWaste quantity Site/Operator/ Intention to carry out waste management Temporary Storage.
Area I Burn Pit Santa Susana Field Laboratory RCRA Facility Investigation Work Plan February 19, 2008 Laura Rainey, P.G. Senior Engineering Geologist California.
1 ESTABLISHMENT OF REQUIREMENTS Module “DECOMMISSIONING PROCESS” Project BG/04/B/F/PP , Program “Leonardo da Vinci”
IAEA International Atomic Energy Agency PGEC Part VI Planned Exposure Situations - Generic Requirements Module VI.3 Requirements for public exposure in.
Specific Safety Requirements on Safety Assessment and Safety Cases for Predisposal Management of Radioactive Waste – GSR Part 5.
International Atomic Energy Agency Regulatory Review of Safety Cases for Radioactive Waste Disposal Facilities David G Bennett 7 April 2014.
Waste treatment after a radiological accident Miliza Malmelin.
International Atomic Energy Agency School for Drafting Regulations on Radiation Safety RER/9/096 Vienna, 3 May, 2010 Adriana Nicic, Regulatory Activities.
Ukraine Petro Nakhaba All-Ukrainian Public Organization “ Chysta Khvylya ” Deputy Head Kyiv, Ukraine Contaminated Sites Management Joint UMOE-DEPA Project.
RER/9/111: Establishing a Sustainable National Regulatory Infrastructure for Nuclear and Radiation Safety TCEU School of Drafting Regulations November.
Milestones for Nuclear Power Infrastructure Development Establishment of A Regulatory Framework Gustavo Caruso, Section Head, Regulatory Activities Section.
IAEA International Atomic Energy Agency MANAGEMENT OF THE REVIEW PROCESS Luc Baekelandt Safety of radioactive waste management.
DECOMMISSIONING OF NUCLEAR POWER PLANTS IN THE CZECH REPUBLIC Peter Lietava Division of Radioactive Waste and Spent Fuel Management State Office for Nuclear.
International Atomic Energy Agency V. Nys Definition and practical application of demonstration of operational and long-term safety for predisposal RWM.
IAEA International Atomic Energy Agency IAEA Safety Standards and Public Exposure to Radon Trevor Boal Radiation Protection Unit - NSRW.
By Annick Carnino (former Director of IAEA Division of Nuclear Installations Safety) PIME, February , 2012.
PREDISPOSAL MANAGEMENT OPTIONS Daniela E. Alvarez, Ph. D
Module Planned exposure situations Public exposure (GSR Part 3)
-EL ABBARI Younes, FADIL Najib (CNESTEN) -SADIQ Younes (AMSSNuR)
RER/9/111: Establishing a Sustainable National Regulatory Infrastructure for Nuclear and Radiation Safety TCEU School of Drafting Regulations
IAEA Safety Guidance on Licensing and Oversight Activities
TOPICAL TRAINING SESSION TENORM
Consultants’ Meeting to develop a guidance document on management of large amounts of radioactive waste after an emergency situation 04, Feb. – 08, Feb.
Communication and Consultation with Interested Parties by the RB
AFPC Policy Protect its personnel, contractors,3rd parties and the environment against the hazards of exposure to ionizing radiation due to AFPC activities.
Noteworthy points of environmental remediation work in Fukushima
Addressing Future Human Actions for Safety Assessment
Safety requirements for predisposal management
Presentation transcript:

1 A Consultancy on management of large amounts of radioactive waste after an emergency situation ~ Experience on aftermath of Fukushima Daiichi NPS accident ~ 4-8 February 2013

Outline of waste management established by MOE 2 What to manage (Waste characterization) Where to manage/Who is operator?/ Objective of waste management Temporary StoragePredisposalDisposal Evacuation Area (=Restricte d Area + Deliberate Evacuation Area) 1.Combustible waste 2. Incombustible waste 3. Waste arising from decontamination work (Wood, Grass, etc.) Evacuation area (Countermeasure area) / National Gov./ Reduction of radiation dose to the decontamination workers and the public <=100,000Bq/kg Incineration facilities etc./Waste generators or local gov. /Reduction of the volumes of wastes <=100,000Bq/kg The places where national government has been proposed/ National Gov./Waste Removal >100,000Bq/kg The places where national government has been proposed/ National Gov./ Reduction of the volumes of wastes, Reduction of radiation dose to the decontamination workers and the public >100,000Bq/kg The places where national government has been proposed except for Fukushima Pref./ National Gov./Waste Removal, Reduction of radiation dose to the decontamination workers and the public Out of Evacuation Area > 8,000Bq/kg Designated waste (ex. Incineration ash, Wasted sludge (Domestic water), Wasted sludge (Industrial water), Sewage sludge, Agriculture and forestry waste, Waste arising form decontamination work) Out of Evacuation Area / Waste generators /Reduction of radiation dose to the decontamination workers and the public Incineration facilities /National gov./Reduction of the volumes of wastes, Reduction of radiation dose to the decontamination workers and the public The place where national government has been proposed or existing final disposal sites/National Gov./Waste Removal, Reduction of radiation dose to the decontamination workers and the public Note: 1. Management of contaminated soil arising from decontamination work is similar to waste management mentioned above. 2. Waste ( ≦ 8,000 Bq/kg of Cs-134, -137) was evaluated to be able to conduct processing and disposal in existing domestic/ industrial service facilities.

When to start waste management What to manage (Waste characterization) Where to manage/Who is operator?/ Objective of waste management Temporary StoragePredisposalDisposal NPS on-siteAn early phase of an emergency exposure situation 1.Debris 2.Rubbles (Concrete, Metals, Soil) 3.Treatment equipment for contaminated water (Cesium adsorption vessels, Sludge etc.) 4.PPE (Personal protective equipment) 5.Logged woods NPS Site/ TEPCO/ a. Reduction of radiation dose to the worker, b. Reduction of radiological impact outside the site, c. Trees had to be cut down in order to secure the space for new installation (e.g. contaminated water tank). NPS Site/ TEPCO/ a. Reduction of worker’s radiation, b. Reduction of radiological impact outside the site, c. Reduction of the volumes of wastes ?/?/To carry out decommissioning Areas where decontamina tion activities are needed A late phase of an emergency exposure situation [Wastes arising from decontamination activities] 1.Combustible wastes 2. Incombustible wastes 3.Others (Woods, Grass, etc.) Places where decontamination are being or has been conducted / -/ Reduction of radiation dose to the decontamination workers and the public The place where national government has been proposed/ -/ a. Reduction of radiation dose to the decontamination workers and the public, b. Reduction of the volumes of wastes The place where national government has been proposed/-/Waste Removal The period when those wastes are found out [ Wastes arising from non- decontamination activities] 1.Incineration ash 2.Wasted sludge (Domestic water) 3.Wasted sludge (Industrial water) 4.Sewage sludge 5.Agriculture waste (> 8,000Bq/kg) Spots where those wastes were generated /Waste generators /Reduction of radiation dose to the public Incineration facilities/-/a. Reduction of radiation dose to the public, b. Reduction of the volumes of wastes The place where national government has been proposed/-/Waste Removal Waste management related to Fukushima Daiichi NPS accident 3

4 1. Properties of wastes generated from NPS site and outside the site are different. Waste from NPS site are also generated from controlled area. Those waste contain many kinds of RNs such as Co-60, H-3 and Sr-90 etc., and may contain even spent fuel debris. Waste outside the site mainly contain Cs-134 and Radioactive waste management at NPS site will intend to achieve a different goal from those outside the site. As compared with NPS site where no residents exist, the waste management outside the site should be conducted primarily in accordance with the radiation protection of general public. Since the difference between the approaches for the management at NPS site and for that outside the site is too large and substantial, we propose to exclude the discussion on waste management at NPS site from the scope of this guidance.

What should be included in the guidance? 5 Areas where decontamination activities can be needed Emergency preparedness arrangementResponse for waste management after accident Wastes arising from decontamination activities Temporary storage Matters that have to be considered as legal and regulatory framework Definition of responsibilities for relevant organizations Method for temporary storage (each property of waste) Matters that have to be considered as legal and regulatory framework Definition of responsibilities for relevant organizations Predisposal Matters that have to be considered as legal and regulatory framework Definition of responsibilities for relevant organizations Waste characterization and waste acceptance criteria (WAC) Requirements of implementation in an emergency exposure situation and in an existing exposure situation Impact and consideration of properties of waste in terms of implementation Matters that have to be considered as legal and regulatory framework Definition of responsibilities for relevant organizations Licensing process in accordance with graded approach Development of safety case and safety assessment in accordance with graded approach Communication with interested parties Siting process Disposal Matters that have to be considered as legal and regulatory framework Availability of disposal facilities in an existing exposure situation

Emergency preparedness arrangementResponse for waste management after accident Wastes arising from non- decontaminati on activities Temporary storage Matters that have to be considered as legal and regulatory framework Definition of responsibilities for relevant organizations Identification of spots where those wastes may be generated from and waste characterization in accordance with graded approach Handling method of waste generated from identified spots (each property of waste) Matters that have to be considered as legal and regulatory framework Definition of responsibilities for relevant organizations Predisposal Matters that have to be considered as legal and regulatory framework Definition of responsibilities for relevant How to adopt use of existing facilities using for domestic and industrial waste (each property of waste/WAC) Recycle/ reuse of waste generated from identified spots Communication with interested parties Disposal Matters that have to be considered as legal and regulatory framework How to adopt use of existing facilities using for domestic and industrial waste (each property of waste/WAC) 6 Areas where decontamination activities can be needed What should be included in the guidance?

7 Discussion on development of safety case and safety assessment in accordance with graded approach The management of the wastes contaminated by accidentally generated radioactive materials should be carried out in accordance with graded approach, so that the methods for processing and storage will be commensurate with the hazard potential (such as radiological and chemical) of the wastes. In terms of interim storage facilities, requirement of implementation should be identified by properties of waste. Generation of flammable gas (e.g. Methane) should be considered Substances outside NPS site Radiation protection needed? Accidentally generated Radioactive materials [Evaluation criteria] We need radiation protection in those area in accordance with graded approach. Usable/disposable without radiation protection. Evaluation criteria Properties (substances, amounts, activities, RNs composition) and reasonable scenarios Stepwise approach (Remediation process) Reuse/RecycleProcessing Disposal YES NO