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Overview of INPRO methodology
Presented by A. Korinny
IAEA/INPRO
INPRO Dialogue Forum on Roadmaps for a Transition to Globally Sustainable Nuclear Energy Systems
20 - 23 October 2015, Vienna, Austria
2
Outline of presentation
• History of INPRO methodology
• Structure of INPRO methodology
• Summary of INPRO methodology areas
• Users, types and benefits of Nuclear Energy System
Assessments (NESA)
• Experience with NESA
3
History of INPRO methodology
• 2000: Launching of the INPRO;
• 2001 – 2006: Development of the Methodology as a tool for Nuclear Energy System Assessment (NESA):
• Contribution by 150 experts (29 countries) and 50 IAEA staff.
• 2004 – 2008: Six national and one multinational NESA leading to several
collaborative projects;
• 2009 – 2011: NESA in Belarus (exemplary study);
• 2011 - : NESAs in Ukraine, Indonesia, Romania;
• 2012 - : INPRO methodology update project (two volumes are
published in 2014, one is expected in 4Q 2015);
• 2014 - : Limited scope NESA studies in China, India and Russia.
Scope of INPRO methodology
Nuclear power sustainability
issues (Brundtland report):
Nuclear accidents risks
Economics
Proliferation risks
Waste disposal
Health and environment
risks
Public acceptance
Sufficiency of national and
international institutions
INPRO assessment areas:
Safety of reactor
Safety of fuel cycle
Economics
Proliferation resistance
Waste management
Environment
Infrastructure
Physical Protection
4
Nuclear accidents risks
Economics
Proliferation risks
Waste disposal
Health and environment
risks
Public acceptance
Sufficiency of national and
international institutions
4
5
• Economics: competitiveness against alternatives available (in the
country);
• WM: managing waste so that humans and environment are protected and
undue burdens on future generations are avoided;
• Infrastructure: adequate infrastructure and effort to create / maintain it.
• PP: effective nuclear security regime;
• PR: unattractiveness for a nuclear weapon program by combination of
intrinsic features and extrinsic measures;
• Environment: impact of stressors must stay within performance envelope
of current NES. Resources sufficient to run NES until end of 21 century;
• Safety: superiority against safety of existing plants. Large off-site releases
should be prevented so that there is no need for evacuation*.
Main messages in areas of INPRO methodology
* - emergency preparedness and response remain a prudent
requirement
6
Structure of INPRO requirements
Criteria: assessor’s
tools to check whether
user requirement has
been met
BP
UR
1
CR
1.1
UR
2
UR
N
CR
1.2
CR
…
CR
2.1 CR
…
CR
N.1
CR
…
User Requirements: what should be
done to meet goal defined in basic
principle
Basic Principles: goals for development of
sustainable NES
INPRO methodology sustainability metrics
• Sustainability assessment – not analysis (except area of economics);
• Sustainability measured in a given time frame – within a century:
• Linked to the lifecycle period of modern NPP and difficulty to make
projections on the technologies available over a century:
– e.g. costs of available alternative energy supply options will be different, fuel cycle
technologies may be different etc
• Except waste management and decommissioning.
• Types of INPRO sustainability criteria:
• Comparative performance on a metric with respect to technology used for
similar purpose (e.g., coal, natural gas);
• Progress toward improved metric within a technology lineage;
• Forward-looking target value of a metric;
• Yes or no answers on certain requirements and good practices.
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Scope of INPRO area of economics
• Cost competitiveness of power production:
• Dominated by costs of reactor construction, maintenance and operation;
• Involves costs of services from fuel cycle facilities.
• Attractiveness for investment (internal rate of return, net present value
etc.);
• Risk of investment (maturity of design and sensitivity studies);
• Flexibility of design;
• Economics issues in other areas of INPRO methodology:
• Financing of infrastructure (not NPP);
• Analysis of benefit to society;
• Cost-benefit analysis for national industry;
• Cost of waste management including disposal (estimation of assets being
accumulated now to cover expenditures in the future)
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Scope of INPRO area of infrastructure
• Legal and institutional infrastructure:
• Nuclear law, regulatory body and regulations
• Industrial and economic infrastructure:
• Financing of infrastructure and spin-off benefits:
• benefit to society (e.g. security of supply, avoidance of cost fluctuations,
minimisation of emissions, conservation of fossil resources, higher paid
jobs);
• cost-benefit analysis for national industry (licensing agreements, quality
assurance, training staff, increase of production, increased
competitiveness, higher skilled jobs)
• Size of nuclear facilities, support infrastructure and siting
• Political support and public acceptance;
• Human resources;
• Minimization of infrastructure and regional/international arrangements
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Scope of INPRO area of waste management
• Waste minimisation;
• Waste characterisation and classification;
• End states for all classes of radioactive waste, i.e. VLLW, VSLW, LLW,
ILW, HLW and spent fuel (when SF is not planned to be reprocessed):
• End state technology (including waste forms, packages and specific sites);
• Safety of end state (safety case);
• Schedule for achieving end state;
• Resources (funding, space, capacity etc)
• Pre-disposal waste management:
• Process descriptions that encompass the entire waste life cycle;
• Predisposal waste management safety;
• Time for waste form production
11 Scope of INPRO areas of depletion of resources
and environmental stressors
• Depletion of resources:
• Consistency with resource availability:
• Sufficiency of fissile/ fertile materials, other non-renewable materials and power
supply to NES;
• Efficient use of fissile/ fertile materials and other non-renewable materials
• Adequate net energy output (energy output should match the total energy
input within acceptably short period)
• Environmental stressors:
• Controllability of stressors (limitation):
• Radiation exposure to public and non-human biota;
• Impact of chemicals and other non-radiation stressors
• Reduction of environmental impact of radiation (total radiotoxicity);
• Optimisation of measures reducing environmental impact
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Scope of INPRO area of reactor safety
• Robustness of design for normal operation: • quality of operation and occupational doses;
• capability to inspect and frequencies of failures and AOO;
• Detection and interception of failures and AOO: • I&C, inherent characteristics, grace period and inertia;
• Design basis accidents: • Frequencies of DBAs and grace period;
• Engineered safety features, barriers and sub-criticality margins;
• Accidents with major release into containment: • Frequency of release into containment and consequences (dose);
• Robustness of containment, accident management and frequency of release into
environment*
• Independence of DID levels, inherent safety characteristics and passive
safety systems;
• Human factors: • operator errors in design analysis, formal human response models, safety culture
• R&D for innovations
* - level 5 of DID (emergency preparedness and
response) considered in the INPRO area of infrastructure
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Scope of INPRO area of fuel cycle safety
• Fuel cycle steps (facilities) considered:
• Uranium/ thorium mining and milling;
• Uranium/ thorium refining and conversion;
• Uranium enrichment;
• Fuel fabrication and transportation including re-fabrication of nuclear fuel
using fissile material from reprocessing;
• Spent nuclear fuel storage and transportation;
• Spent nuclear fuel reprocessing;
• Scope of consideration for every fuel cycle step (facility):
• DID levels 1 to 4* taking into account graded approach (stringency of
requirements is commensurate with risks);
• Independence of DID levels and inherent safety characteristics;
• Human factors;
• R&D for innovations
* - level 5 of DID (emergency preparedness and response)
considered in the INPRO area of infrastructure
INPRO Requirements and Output of NESA
INPRO User Requirements are directed at:
• Designer or developer of nuclear facilities;
• State (government institutions);
• Operator of nuclear facilities;
• National industry (involved in nuclear power program).
NESA’s output:
• Confirmation of sustainability of NES, or identification of gaps*;
• Definition of follow up actions to close gaps*;
• Note: Even if “gaps” are found, NES may be a good interim solution, if
path to sustainable system has been defined.
* “Gap” = INPRO Methodology Criterion not met.
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Users and types of NESA
• Different types of users perform NESA studies:
• Developer/ designer of nuclear technology;
• User (experienced) of nuclear technology;
• Newcomer (first time nuclear technology user).
• Type of user influences type (and benefit) of NESA
• Different levels of depth and scope in a NESA:
• NESA as learning tool: Increase of awareness of long term nuclear
issues (newcomer);
• NESA with limited scope: Selected areas and/or selected
components of NES (developer);
• Full scope NESA: All areas of INPRO methodology, full depth of
assessment, complete NES Judgement on sustainability
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Benefits of NESA
• Developer:
• Identification of critical issues, i.e. gaps to be closed;
• Balanced design, i.e. avoidance of undesirable consequences in one
area caused by development in another area and assistance in
selection of preferred option;
• Experienced user:
• Identification of gaps and follow-up actions to move NES towards
sustainability at early stage of deployment of additional units;
• Identification of advantages of different NES options and better
transparency in decision making;
• Newcomer :
• Increase of awareness of all nuclear issues and development of cadre
of knowledgeable individuals, i.e. educational tool;
• Assistance in strategic planning and decision making process.
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Experience with NESA in 2004-2008
• 1 multinational assessment (“Joint Study”):
• Canada, China, France, India, Japan, Republic of Korea,
Russian Federation, and Ukraine
• Development of NES of sodium cooled Fast Reactor with
Closed NFC
• Result documented in IAEA-TECDOC-1639 rev.1
• 6 national assessments:
• Argentina, Brazil, India, Republic of Korea as technology
developer;
• Armenia, and Ukraine as technology user.
• Results documented in IAEA-TECDOC-1636
17
Experience with NESA:
NESA of Belarus (2009-2011)
• Full scope assessment of all INPRO methodology areas
published as IAEA-TECDOC -1716 (2013);
• Simplified NES consisting of power plant and waste
management facilities;
• Ca. 150 criteria and evaluation parameters assessed;
• 54% of criteria are met;
• 19% of criteria are met partly or conditionally (e.g. actions had
been planned and results were expected soon);
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• For 20% of criteria assessor could not
collect enough data to make a judgment
(recommendation was to collect necessary
input and to finalize assessment);
• 7% of criteria were not fulfilled (gaps
identified and follow-up actions defined).
Ongoing NESA studies
• Technology user’s NESAs on-going in Indonesia,
Ukraine and Romania;
• Technology developer’s NESAs:
• Limited scope NESA of 3 different SFR designs started in 2015:
• India: CFBR with MOX fuel;
• Russia: BN-1200 with nitride or MOX fuel;
• China: CFR-1000.
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Pictures taken from presentations: ‘Safety design criteria and design approach’ by Mr John Arul
(IGCAR, India); ‘Design features to enhance safety in CBR’ by Mr Raghupathy (IGCAR, India);
‘Introduction to safety characteristics of CFR1000’ by Mr Peng Yang (CIAE, China).
Conclusion
• INPRO methodology – the IAEA tool for sustainability assessment of
nuclear energy systems;
• Updated methodology will comprise 8 assessment areas and ca. 100
criteria;
• National trainings on the INPRO methodology application, examples of
INPRO assessments and other complementary materials are available
via NESA support package;
• Annual regional trainings organized by INPRO:
• 2014 – Latin America (Santiago, Chile);
• 2015 – Asia and Pacific (Kuala Lumpur, Malaysia);
• 2016 – Africa (planned in Rabat, Morocco).
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…Thank you for your attention