inpro dialogue forum on cooperative approaches to the back
TRANSCRIPT
INPRO Dialogue Forum on Cooperative Approaches to the Back End of
the Nuclear Fuel Cycle: drivers and legal, institutional and financial
impediments
26-29 May 2015 IAEA Headquarters, Vienna, Austria
Vienna International Centre (VIC)
Slide 2 of 58
UO2 Powder
Plant
Nuclear Research Institute
VVRS Reactor Cernavoda NPP
Heavy Water Plant
The Ministry of Economy, Commerce and Trade: management of the back
end of the nuclear fuel cycle, including remediation related activities; The Ministry of Energy: nuclear energy production sector, nuclear research &
engineering, nuclear fuel; The Ministry of the Environment: specific responsibilities in the licensing
and control of nuclear installations; CNCAN: the national authority competent in exercising regulation, licensing
and control in the nuclear field; Nuclear Agency for Radioactive Waste (ANDR):
National authority under the supervision of the Ministry of Economy;
responsible for: promotion, development and monitoring the nuclear activities exclusively for peaceful
purposes;
disposal of SNF and RW in Romania;
The waste producers:
Responsible for predisposal activities;
shall bear the expenses related to the collection, handling, transport,
treatment, conditioning, storage and disposal of the waste they have
produced
Main organisations
Romanian Nuclear Fuel Cycle Facilities
Mining
Uranium
Ore
Extraction
Feldioara
Conversion
Factory
Conversion
Pitesti Nuclear
Fuel Factory
Fuel
Fabrication
Drobeta Turnu-Severin
Heavy Water Factory
Heavy Water Production
Cernavoda NPP Units
1 and 2
Electricity Production
Spent Fuel Disposal
The solution is not yet
decided
Cernavoda
Dry Storage Facility
Spent Fuel Storage
The CANDU 6 power reactor was designed specifically for electricity production, unlike other major reactor types that evolved from other uses.
This focused development is one of the reasons that CANDU has such high fuel efficiency.
CANDU 6 is AECL's 700 MWe class nuclear power reactor. The first CANDU 6 plants went into service in the early 1980’s as leading-edge technology, and the design has continuously evolved since to maintain superior technology and performance.
The CANDU 6 power reactor uses nuclear fission process to produce the necessary energy.
The CANDU 6 power reactor
Nuclear Spent Fuel Storage
Cernavoda NPP Spent fuel bundle inventories on December 31, 2012:
Wet Storage:
- about 34,000 Irradiated Fuel Bundles in the Bays of Unit #1, and
- about 26,000 Irradiated Fuel Bundles in the Bays if Unit #2.
Dry Storage - IDSFS : 50,000 Irradiated Fuel Bundles.
Main Storage Bay filling rate (discharge tare): about 5,200 bundles/year/unit
1. Nuclear Power Plant (NPP)
SNN/CNE Cernavoda – U1, CANDU type, 720MWe, in operation from 1996;
SNN/CNE Cernavoda – U2, CANDU type, 720MWe , in operation from 2007;
SNN/CNE Cernavoda –U3&4, CANDU type: to be constructed by 2020;
2. Research reactors (RR)
RAAN/SCN Pitesti, TRIGA type, 14 MW, in operation from 1979
IFIN-HH Magurele, VVR-S type, shutdown in 1997, under decommissioning
3. Mining and milling (M&M)
CNU, various sites/uranium ores extraction mines
CNU/Feldioara, uranium ores processing plant
4. Nuclear Fuel Plant (NFP)
FCN Pitesti, CANDU type fuel fabrication plant
5. Institutional field
Medicine, Industry, Universities, Agricultural
Sources of RW
SNF from VVRS Research Reactor
An important step through the decommissioning of the VVRS RR from Magurele has been made by the repatriation of entire inventory of SF into the Russian Federation. First shipment of HEU SF has been finalised in 2009 under the GTRI programme, conducted by USDOE , NNSA, followed in 2012 by three shipments of LEU SF, fully implemented and financed by Romania.
ANDR main responsibilities (1/3)
• draws up and reviews, at least every 5 years, the National medium and long term strategy on the safe management of SNF and RW, which it forwards for approval to the Ministry of Economy, and monitors its implementation;
• is directly liable for the set up of the repositories for the disposal of RW; the repositories are in the patrimony and administration of ANDR;
• ensures, directly or by means of third parties, the design, construction, commissioning, operation, closing and post-closing monitoring of the repository of RW;
• ensures the set up and annual update of a national data base regarding the quantities, types of generated RW, including the ones resulting from the decommissioning of the nuclear and radiological facilities;
• approves the documentations and procedures drawn up by the holders of license, related to the stages of the safe management of SNF and of RW, in order to comply with the WAC for disposal;
• draws up the WAC for the disposal of RW and subjects them to the approval of CNCAN;
ANDR main responsibilities (2/3)
• ensures, directly or by means of third parties, for the disposal, the
execution of services of safe management of:
• the orphan sources of nuclear radiations;
• historical RW resulting from past practices;
• RW resulting from incidents and nuclear accidents;
• the SNF and RW from the economic operators which are
bankrupt or in official winding up;
• ensure, directly or by means of third parties, the physical protection of
the repositories of RW;
• performs audits at the main generators of radioactive waste in order
to ensure the compliance of the activities of safe management of RW
with WAC;
• monitors the radioactivity of the environment in the area of the
repositories in order to protect the population and the environment;
ANDR main responsibilities (3/3)
• periodically checks, for reporting purposes, according to the
regulations in force, the stage of accumulation of the financial
resources designated to the management of the SNF and RW and the
decommissioning of the nuclear and/or radiological facilities;
• draws up and updates, periodically, technical-economic studies
regarding the estimation of the costs related to the disposal of the SNF
and RW for the establishment of the amounts of the annual
contributions of the license holders;
• manages the financial resources designated to the management of
the SNF and RW and the decommissioning of the nuclear and/or
radiological facilities;
• informs and prepares the public of the area close to the repositories
for the acceptance of their location.
Basic principle
Basic principle of radioactive waste disposal in Romania:
• VLLW: less complex arrangement than LILW-SL;
• LILW-SL: near surface disposal facility;
• LILW-LL and SNF: geological repository;
• SNF is considered RW;
• Import of RW is forbidden.
LILW-SL
INTERIM
STORAGE
ON NPP SITE
SALIGNY
REPOSITORY
(2020)
NPP
TREATMENT
FACILITY
EXISTING PLANNED
RR
TREATMENT
FACILITIES
BAITA BIHOR
REPOSITORY
RR /
INSTITUTIONA
L
LILW-LL
NPP Mining
INTERIM
STORAGE
ON NPP SITE
NPP
TREATMENT
FACILITY
The National Strategy for Safe Management of Radioactive Waste
- LILW -
Milling
DISPOSAL IN
GEOLOGICAL
REPOSITORY
(2056)
STORAGE IN
TAILING
PONDS
CLOSURE
OF TAILING
PONDS
RR /
INSTITUTIONAL
INTERIM
STORAGE
ON RRs SITE
RR
TREATMENT
FACILITIES
NFP
DISPOSAL IN
SURFACE
TRENCHES
IN SITU
CAPPING /
RELOCATING
IN MINES
NPP
The National Strategy for Safe Management of Radioactive Waste
- SNF, NPP -
Dry storage (50 years)
Wet storage (6-7 years)
- The first dry storage module was commissioned in May 2003; - The site can accommodate 50 years operation spent fuel from two CANDU 6 units. - Possibility to extend the site to accommodate the spent fuel produced by 4 units from Cernavoda NPP.
Nuclear Spent Fuel Storage
Wet Storage
• Wet storage in the Main Storage Bay for minimum six years.
• Fuel bundles are placed on special designed trays (24 fuel bundles/tray) that are stacked one to each other up to 19 trays per stack.
• Stacks are inspected and sealed by IAEA inspectors.
Nuclear Spent Fuel Storage
Dry Storage
The Intermediate Dry Spent Fuel Storage for Cernavoda is the MACSTOR system.
The MACSTOR (Modular Air Cooled STORage) System is designed for storing fuel, which has been cooled for a period of six years.
MACSTOR - Design and
Safety Features
The MACSTOR module is primarily cooled by a natural convection from the storage cylinders surface.
It is designed:
- to withstand natural and man-made hazards.
- for zero release over the entire storage period.
The MACSTOR design ensures that the containment of fission products is maintained during all phases of the fuel handling operations.
MACSTOR - Design and
Safety Features
Specifically, the MACSTOR modules are qualified for:
– design basis tornado, wind loads and related tornado missiles;
– seismic events;
– floods;
– snow loads;
– heavy rain;
– extreme ambient air temperature and humidity;
– wind loads.
Fuel Storage
At the storage area, the transfer flask is lifted from the transporter by the gantry crane above the storage module.
The loading plug previously positioned over the
storage cylinder to be loaded is removed, the transfer
flask positioned over the cavity, and the fuel basket
lowered into the storage cylinder
Nuclear Fuel Cycle Facilities: Radioactive Waste Storage Facilities
– Operated by Cernavoda
NPP
– Capacity for 2 Units, 40
years of operation, solid
(solidified) waste;
– Consist of 3 Structures:
Concrete warehouse
Concrete cylindrical cells
Concrete cubes.
DIDR - The structure no. 1 – warehouse inside view
Cernavoda NPP RW Storage Facility
Assumptions: - 25 y operating period / unit followed by refurbishment
- 5300 SFB / year / unit;
- DICA: 12.000 SFB / module;
- wet storage period: 6-7 years;
- dry storage period: 50 years / module;
Projected inventory – Cernavoda NPP, scenario 1
2003 2056
Refurbishment (2 y per Unit)
Operation of dry storage module (DICA)
1996 2021 2022 2047
U1 Normal operation Normal operation Decommissioning
2007 2032 2033 2058
U2 Normal operation Normal operation Decommissioning
2056
Operation of deep geological repository
NOTE: Preliminary decommissioning plan for U1 and 2 is under approval
-525.000 SFB to be disposed of;
- RW / LL under estimation.
Transfer of SFB
Assumptions: - 25 y operating period / unit followed by refurbishment
- 5300 SFB / year / unit;
- DICA: 12.000 SFB / module;
- wet storage period: 6-7 years;
- dry storage period: 50 years / module;
Projected inventory – Cernavoda NPP, scenario 2
2003 2056
Refurbishment (2 y per Unit)
Operation of dry storage module (DICA)
1996 2021 2022 2047
U1 Normal operation Normal operation Decommissioning
2007 2032 2033 2058
U2 Normal operation Normal operation Decommissioning
2019 2044 2045 2070
U3 Normal operation Normal operation Decommissioning
2020 2045 2046 2071
U4 Normal operation Normal operation Decommissioning
2056
Operation of deep geological repository
NOTE: Preliminary decommissioning plan for U1 and 2 is under approval
-1.060.000 SFB to be disposed of;
- RW / LL under estimation.
Transfer of SFB
Cernavoda Units 1& 2 Preliminary
Decommissioning Plan, May 2013
HLW in the form of used fuel will be stored onsite until a geological repository or a suitable alternative storage or disposal facility is available.
WET STORAGE FOR
AT LEAST 6 YEARS
DRY STORAGE FOR
ABOUT 50 YEARS
GEOLOGICAL
REPOSITORY USED
FUEL
Existing facility
Planned facility
The DGR concept
• generic (for costing purposes)
and has not been based on
conditions at any particular site.
There is no host rock established
and no proposed site. It is
assumed a Generic Site;
• assumes the similarity of
Canadian Concept for a Deep
Geological Repository for CANDU
spent fuel;
• DGR facility will dispose both
spent fuel and long lived wastes
from 4 Cernavoda Units in
operation their decommissioning;
• DGR will be located for both
waste types at a depth between
500-1000 m.
Basic Principle 1 – Waste minimisation
IAEA-TECDOC-1575 Rev. 1 (INPRO Manual - WM)
Generation of RW associated with SF management is minimized through:
- the quality of fuel;
- online fuelling (this allows through the systems for detecting the failed fuel and immediate replacement);
- canning of the failed fuel;
- control of water parameters for wet storages;
- control of confinement and of the isolation air parameters for dry storage.
Basic Principle 2 – Protection of Human Health and the Environment
IAEA-TECDOC-1575 Rev. 1 (INPRO Manual - WM)
In the licensing process, the RB pays due attention to the effective protection of workers, public and environment. The dose estimate and monitoring are based on the analysis of the external effective doses and of the (internal) committed effective doses for members of critical groups for all radiation pathways.
These analysis are performed according to methods and procedures recommended in IAEA and in other western regulations.
The results of the analyses leads to derived emissions limits for the effluents, and the monitoring program of the environment shall demonstrate that the derived emissions limits are observed both in normal operation and during events with relative high probability of occurrence.
Basic Principle 3 – Burden on future generations
IAEA-TECDOC-1575 Rev. 1 (INPRO Manual - WM)
Romania authorities fully accept and promote this principle.
Based on the GO no.11/2003 were created the Funds earmarked for the management of radioactive waste and for decommissioning of nuclear installations.
Basic Principle 4 – Waste optimization
IAEA-TECDOC-1575 Rev. 1 (INPRO Manual - WM)
The classifications of the radioactive waste as well as the requirements for classification are established by RB in the Order 156/2005 approving the Regulation on the classification of radioactive waste. According to art. 6 in Order 156/2005 the general classification of radioactive waste refers strictly to the requirements regarding the isolation from the biosphere at final disposal radioactive waste.
According to the general classification the radioactive waste are: a) exempt waste; b) transition waste; c) very low level waste; d) short lived low and intermediate level waste; e) long lived low and intermediate level waste; f) high level waste.
Basic Principle 4 – Waste optimization
IAEA-TECDOC-1575 Rev. 1 (INPRO Manual - WM)
According to art. 9 of CNCAN Order 156/2005 the operational classification of radioactive waste shall be performed by the licensee. For establishing the operational classification the licensee shall take into account:
a) origin of managed waste such as: site, facility, the arising system, b) types of managed waste such as: used filters, worn-out components,
demolished structures, miscellaneous trash, spent sealed sources, radioisotopes handling residues;
c) nuclear and radiological properties such as: fissile content, heat generation, ambient dose rate, surface contamination, activity concentration, radionuclide composition and half-lives of dominant nuclides, radiolysis potential;
d) other properties such as: physico-chemical and biological properties/hazards corrosivity, content of free liquids, flammability, volatility, solubility, miscibility, dispersibility, organic content, complexing/chelating agents, reactivity, sorption of radionuclides, swelling potential, chemically or biologically hazardous substances, etc.;
e) management options such as: compressibility, combustibility, immobilization, segmentation, decontamination or melting.
• reviewing the National Strategy for safe management of Spent Nuclear
Fuel and Radioactive Waste according to the requirements of Council
Directive 2011/70/EURATOM of 19 July 2011 establishing a Community
framework for the responsible and safe management of spent fuel and
radioactive waste;
• to elaborate and implement a strategic programme for the initial stages
of repository development, including site selection, surface-based site
characterisation, development of a URL, development of the safety
case, etc.;
• reviewing the costs for geological disposal.
Next steps
• The SNF is safe managed according to best international practices;
• Geological disposal of SNF is considered the end-point to ensure
sustainable, safe and secure long-term management;
• Knowledge of the complex geological context of Romania exists
through mapping;
• A concept for DRG was elaborated;
• The DGR will be designed to receive the SNF and LILW/LL coming from
operation, dismantling and refurbishment of Romanian nuclear facilities;
• The programme for implementing geological disposal of SNF and
LILW/LL is in the initial stages (no host rock established and no
proposed site).
Conclusions