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International Atomic Energy Agency
Modular Design of Processing and Storage Facilities
for Small Volumes of L & IL Radioactive Waste and
Disused Sealed Radioactive Sources
S.K.Samanta
Waste Technology Section (WTS)
Division of Nuclear Fuel Cycle and Waste Technology
TM on Practical Applications of Safety Assessment Methodologies for Predisposal
Management of Radioactive Waste, 9-13 May, 2011
International Atomic Energy Agency
Radioactive waste in generated in Member States from:
• Nuclear power plants
• Nuclear Fuel cycle facilities
• Research reactors
• Nuclear applications, including DSRS
• Installations & equipment to be decommissioned
International Atomic Energy Agency
Waste management steps
Pre
-Dis
posa
l Waste
Pre-Treatment
Storage
Treatment
Conditioning
Disposal
•Collection
•Characterization
•Segregation
•Chemical/physical adjustment
•Decontamination
•Volume reduction
•Radionuclide removal
•Change of composition
•Immobilization
•Packaging
•Over-packing
•Placement in licensed facility
•Monitoring
•Retrieval
•Placement in licensed facility
•No intention of retrieval
International Atomic Energy Agency
Existing reference designs to address the needs
of developing MSs with low volumes of RW and
DSRS
• Reference design for a centralized waste
processing and storage facility (CWPSF)
IAEA-TECDOC-776 (1994)
• Reference design for a centralized spent sealed
sources facility (CSSSF)
IAEA-TECDOC-806 (1995)
International Atomic Energy Agency
Reference design for a CWPSF (1/3)
• Targeted at MSs producing small but significant quantities liquid and solid wastes
• Design basis: • Aqueous waste: 100 m3/y
• Solid waste: 90 m3/y
• Processing facility: • Chemical precipitation for aqueous waste
• Low force in-drum compaction for solid waste
• In-drum cementation in 200 L steel drums
• Storage facility: • 3000 drums total @300 drums/y
International Atomic Energy Agency
Reference design for a CWPSF (2/3)
• Two separate buildings (5 m high) • Process & support functions – 29 m x 28 m
• Storage – 39 m x 26 m
• 3-Volume reference design package prepared by AEA Technology (UK) • Process flow diagram
• Engineering line diagrams for ventilation
• Building layouts and architectural drawings
• Equipment, specifications with performance data, etc
• Cost data
• The reference design package itself was not published
International Atomic Energy Agency
Reference design for a CWPSF (3/3)
International Atomic Energy Agency
Reference design for a CSSSF (1/2)
• Targeted at MSs with small amounts of DSRS and other solid waste from nuclear applications
• Design basis: • Sources with activity < 10 TBq (270 Ci) in their
housing or suitable shielding
• No handling of unshielded, high activity sources
• Conditioning: • In-drum cementation in 200 L steel drums
• Storage: • 110 drums total
International Atomic Energy Agency
Reference design for a CSSSF (2/2)
• Two buildings • Main building (conditioning & support functions) – 18 m x 14 m
• Storage building – 7 m x 11 m
• 2-Volume reference design package prepared by AEA Technology (UK) • Layout and construction details
• Safety assessment
• Operating procedures
• Quality assurance
• Treatment of leaking or contaminated sources
• Cost data
• The reference design package itself was not published
International Atomic Energy Agency
Present work on modular design
• Targeted at MSs with very small quantities of solid and liquid waste from nuclear applications and research
• Design basis (based on MSs input during TM in 2006):
• ~10 m3/y aqueous waste
• ~25 m3/y solid waste
• ~1 m3/y wet solids
• ~20 each of DSRS-SL and -LL
• Modular concept is chosen to provide maximum flexibility
• Processing: • A variety of modules depending on type and quantity of waste
• Storage: • A variety modules depending on number of packages, duration and
conditions of storage, etc
• Entire design package to be published
International Atomic Energy Agency
Processing
International Atomic Energy Agency
Key features of modular design
• Processing facility designs based on a set of modules for different functions
• Each module constructed independently
• Modules can be skid mounted
Simplifies installation and future re-location
Allows modules to be built and tested in factory
Only final connection of services (e.g. power, water) required by end-user
• Combination of modules to meet the required functions (waste streams, pre-disposal steps)
• Interfaces defined
• Advantages:
Flexibility in addressing RWM needs
Economical optimisation
International Atomic Energy Agency
IAEA Design Engineering Package for Processing Modules
• Waste streams
• Waste processing modules
• Waste management decision flowcharts
• Module specifications
• Process module integration guidance
• Example technical specifications for procurement
International Atomic Energy Agency
Waste streams considered
1. Low volume aqueous waste
2. High volume aqueous waste
3. Organic liquid
4. Compactable solid
5. Non-Compactable solid
6. Ion exchange resin
7. Sludge
8. DSRS-SL
9. DSRS-LL
10. Biological
11. SHARS
International Atomic Energy Agency
Process modules
1. Module A6 – Solidification
2. Module B1 – Chemical treatment
3. Module B2 – Ion Exchange
4. Module B3 – Reverse Osmosis
5. Module B4 – Cross-flow Filtration
6. Module B5 – Filtration
7. Module B6 – Solidification
8. Module D2 – Low-force Compaction
9. Module D3 – Unshielded booth
10. Module E1 – Encapsulation
11. Module L1 – Hot Cell (SHARS)
International Atomic Energy Agency
Process Module
Liquid and Wet Solid Waste Solid Waste
Ref
# Waste stream
Chemical
Treatment
Ion
Exch RO
Cross-
flow
filtrat’n
Filtrat’n Solidificat’n Encapsulat’n Low Force
Compaction
Unshielded
Booth
Mobile
Hot
Cell
A Low Vol Aq Liq A6
B High Vol Aq Liq B1 B2 B3 B4 B5 B6
C Organic Liq Same
as B4
Same
as B5
Same as
A6
D Compactable
Solid D2 D3
E
Non-
Compactable
Solid
E1 Same as
D3
F Ion Exch Resins Same as
A6
G Sludge Same as
A6
H
Disused Sealed
Source - Short
Lived Same as E1
Same as
D3
J
Disused Sealed
Source - Long
Lived Same as E1
Same as
D3
K Biological
(Carcasses) Same as E1
L High Activity
Sealed Source L1
Waste stream–Process module matrix
International Atomic Energy Agency
Waste Management Decision Flowcharts
1. Radioactive waste management strategy
2. Radioactive waste categorization
3. Sources waste management
4. Solid waste management
5. Low volume liquid waste management
6. High volume liquid waste management
7. Organic liquid waste management
International Atomic Energy Agency
Waste Generation
Is there an existing
national regulatory
strategy?
Is there an existing
national radwaste
strategy?
Are there existing
standards, guidelines etc?
Consult
responsible
national ministry
Approach IAEA for
support
Review constraints/ limits:
Aqueous discharges
Gaseous discharges
Activity levels
Dose rates
Contamination levles
Clearance levels
Confirm as waste for
treatment
Review existing waste
management infrastructure e.g.:
Incineration
Storage
Special Landfills
Repository
Drains
Repatriation of sources
Taking account of the above constraints and limits and any
existing waste management facilities, is it possible to dispose of
the waste via a conventional disposal route or via an existing
available waste management arrangement rather than needing to
manage a new radioactive waste stream?
Use conventional /
available disposal
routes
No
Yes
No
Yes
No
YesNo
A
Is waste adequately
characterised?
Preliminary characterization:
Radionuclide inventory
Dose monitoring
Historical data review,
Physical and chemical parameters
Other hazardous materials (pyrophoric,
pathogens, toxic)
Homogeneity
No
Yes
Radioactive Waste
for treatment
Is waste adequately
characterised?
Further characterization:
Radionuclide inventory
Dose monitoring
Historical data review,
Physical and chemical parameters
Other hazardous materials (pyrophoric,
pathogens, toxic)
Homogeneity
Is waste compliant with
WPSF WAC?
Does waste require
shielding?
Hot cell facility
Repackage waste
in shielded
container
Does waste require
sorting/segregation
and/or repackaging?
Sort/segregate or
repackage
No
Yes
No Yes
Yes No
NoYes
A
Solid Waste:
Compressible/compactable
Non-compactable
Sealed source, half-life <35 years
Sealed source, half-life >35 years
Biological
Low volume aqueous liquid High volume aqueous liquid
Classify waste
Organic liquid
B C D E
Unshielded booth
module
Interim storage at
source
Review options
Can source be
decay stored (half life
<1 year)?
Interim decay
store prior to
disposal
Yes
Long term store
Store source in
suitable long term
storage container
Store source
within 200-litre
drum
Can sealed source fit into a
special 200-litre drum with
annular shielding?
Yes No
Long term store
Sealed source,
half-life <30 years
B
Radioactive sources:
Sealed source, half-life <30 years
Sealed source, half-life >30 years
Encapsulation
Module E1
Product for
storage and/or
disposal
Grout waste into
200-litre drum
Process source by
encapsulation into
200-litre drum
No
Sealed source,
half-life >30 years
Solid waste
Does waste contain
sealed sources?
Does waste contain
biological material?
Does waste have
half life >35 years?
Can source be
decay stored (half life
<1 year)?
Does waste contain only soft
materials that can be compacted?
Low force in-drum
compaction
module
Product for
storage and/or
disposal
Encapsulation
module
Interim decay
store prior to
disposal
Product for
storage and/or
disposal
No Yes
No Yes
No
Yes
No
Yes
No
Yes
B
Long term store
Place sealed
source into
suitable long term
storage container
Grout waste into
200-litre drum
Compact waste
into 200-litre drum
Place waste into
200-litre drum
Place waste into
200-litre drum
Place sealed
source into centre
of special 200-litre
drum
Can sealed source fit into a
special 200-litre drum with
annular shielding?
Yes No
Encapsulation
module
Prepare grout cap
for waste package
Pre-treatment
Small scale
solidification
module
Buffer store facility
Is there sufficient
volume or mass to process
immediately:
Low Volume
Liquid Waste
Management
Product for
storage and/or
disposal
No
Yes
C
Solidification
module
Yes
Yes
Buffer store facility
Chemical
treatment module
Ion-exchange
module
Membrane
filtration module
Filtration module
Yes
Liquid residueSludge residue Liquid residue Spent IX media Liquid residueRetentate
Liquid residue Spent filters
No
Is there sufficient
volume or mass to process
immediately:
Is a liquid
discharge route with
defined CFA
available?
Spent membranes
Does liquid
residue require any
further treatment before
discharge?
No
Product for
storage and/or
disposal
Solid waste
management
Discharge to
approved route
High Volume
Liquid Waste
Management
No
D
B
Can the aqueous liquid waste be
decontaminated sufficiently by treatment
to allow it to meet the discharge CFA?
i.e. is the required DF< 100?
Does the liquid waste
contain trace oils or
solvents
Is the activity content
mainly insoluble?
Do the soluble
radionuclides have
insoluble hydroxides?
Does the liquid waste
have a high dissolved
salts content?
Does the liquid waste
have a low pH (pH<6)?
No
No
No
No
Pre-treat in
chemical
treatment module
to remove oils or
solvents
Yes
Filter liquid waste
by cartridge filter
No
Is the particulate size
<2 microns?
Filter liquid waste
by membrane filter
Yes
No
Yes
Treat in chemical
treatment module
to precipitate
radionuclides
Yes
Treat in chemical
treatment module
to adjust pH to
pH=7
Yes
Consider selective
ion exchange
media either in a
bed within an IX
module or loose
within a
membrane
filtration module
Solidify sludge
waste in 200-litre
drums
Yes
Solidify the liquid
waste (adjust pH
to >7 if
necessary).
No
Solidify the liquid
waste (adjust pH
to >7 if necessary.
No
Lab scale
solidification
module
Yes
Yes
Buffer store facility
Lab scale
distillation module
Membrane
filtration moduleFiltration module
Organic distllateOrganic residue
Organic liquid
permeate
Organic liquid
retentate
Organic liquid
filtrateSpent filters
No
Is there sufficient
volume or mass to process
immediately:
Is an organic liquid
discharge or disposal route
with defined CFA available?
Spent membranes
Does the organic liquid
require any further treatment
before discharge?
Product for
storage and/or
disposal
Solid waste
management
Discharge to
approved route
Organic Liquid
Waste
Management
No
E
B
Can the organic liquid waste be
decontaminated sufficiently by treatment
to allow it to meet the discharge CFA?
Is the activity content
mainly insoluble?
No
Filter liquid waste
by cartridge filter
Is the particulate size
<2 microns?
Filter liquid waste
by membrane filter
Yes
No
Yes
Treat in lab scale
distillation module
to volume reduce
active organic
Absorb the
organic residue on
to a solid e.g clay
granules and
solidify in 10-litre
containers
Yes
Absorb the
organic liquid on
to a solid e.g clay
granules and
solidify in 10-litre
containers
No
Absorb the
organic liquid on
to a solid e.g clay
granules and
solidify in 10-litre
containers
No
Yes
Absorb the
organic liquid on
to a solid e.g clay
granules and
solidify in 10-litre
containers
International Atomic Energy Agency
Example of flowchart questions
High Volume Liquid Waste Management
• Is there sufficient volume to process immediately?
• Is a liquid waste discharge route with defined CFA available?
• Can the liquid be decontaminated sufficiently by treatment to allow
it to meet the discharge CFA?
• Does the liquid contain trace oils and solvents?
• Is the activity mainly insoluble?
• Dose the liquid waste have a very complex chemical and
radionuclide composition?
• Do the soluble radionuclides have insoluble hydroxides?
• Does the liquid waste have a high dissolved salt content?
• Does the liquid waste have a low pH?
International Atomic Energy Agency
Module specifications
• General
To define the functional requirements, key features, design life, etc
• Basis of design
To identify the key parameters and assumptions used in determining the design of the process module
• Process Flow Diagram (PFD)
To illustrate the process module
• Equipment lists
To identify the main equipment items, valves, piping and instrumentation
• Equipment description
To provide further details on the major equipment items
International Atomic Energy Agency
Module specifications (contd.)
• Photographs of similar process modules or module equipment or simple models
To illustrate a possible arrangement of the module
• Facility requirements
To identify the requirements that need to be taken into account in incorporating the process module into a facility
• Process description and operation
To provide further details on how the module will be operated including pre-requisites prior to start of operation
• Interface requirements
To define the need for services (power, water, air), lighting, drains, HVAC, communications
Integration with other process modules – downstream or upstream
International Atomic Energy Agency
An example of process module design
Chemical treatment
International Atomic Energy Agency
Chemical Treatment Module
• Treat aqueous waste in batches
• Produce a small volume of sludge containing
the radionuclides
• Discharge of bulk volume of the aqueous
waste either immediately, or after further
"polishing”
Key functions:
International Atomic Energy Agency
Chemical Treatment (Module B1) – Basis of Design
Liquid Waste Characteristics
Total liquid vol. 0.5 – 10 m3 per year
Timing Arrives periodically in batches of about 50 litres.
Peak treatment
rates
100 litres for each batch
Feed activity Low level
Physical form Liquid, mainly aqueous but could have small quantities of oils or other immiscible species.
Solids content Could contain particulates
Chemical content No significant chemical content except potential for presence of small quantities of complexing agents.
Discharge requirements
Discharge activity Decontamination factor between 10 and 100 assumed.
pH pH 6-9 assumed
Other
constituents
Sludge separated from aqueous stream.
Services Availability
Services The designs shall identify options for connections to existing services or the need for dedicated services.
Water Required
Power Required
Building heating Required if temperatures likely to fall below 5°C.
HVAC Not required.
Chemical
reagents
Required
Drainage None. Any leaks or spillages that do occur to be captured in a drip tray and returned to a waste container
using a small pump e.g. the module transfer pump.
International Atomic Energy Agency
Chemical Treatment Module – Model picture
International Atomic Energy Agency
Chemical Treatment Module – PFD
B1-E-03
Chemical treatment tank
with variable speed impeller
B1-L-04
B1-E-10
Waste transfer pump
B1-L-02
B1-E-01
Dosing chemical container
B1-E-09
Chemical dosing pump
B1-L-01
B1-L-03
B1-L-05
B1-E-11
Funnel
B1-L-06
B1-E-12
Treated effluent
transfer pump
B1-L-07
B1-L-10B1-L-11
B1-L-12
B1-E-06
Sample point
B1-E-08
Drip tray
B1-E-07
Drip tray
B1-E-02
40-50 litre carboy
containing waste effluent
B1-E-05
40-50 litre carboy
containing treated effluent
B1-L-09
B1-L-08
B1-V-04
B1-V-02 B1-V-03
Dip pipe
B1-V-01
Module B1 - Chemical Treatment of High Volume Aqueous Liquid Waste
B1-E-04
40-50 litre carboy
containing waste sludge
B1-L-11
International Atomic Energy Agency
100 m3/batch
100 L/batch
Chemical Treatment – Large and Small facilities
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Other examples of processing modules
Cross flow filtration
Solidification
Ion exchange Filtration Reverse Osmosis
Unshielded booth
International Atomic Energy Agency
Process module integration
Integration can involve physical co-location and sequential
operation of the process modules with the benefits of:
• Minimising double-handling of waste and hence
reduced dose uptake by the operators.
• More efficient and effective use of staff and resources
as wastes can be processed in short campaigns.
• Reduced interim storage of un-conditioned or
incompletely treated waste because waste streams are
processed from their raw form to final conditioned form
in one campaign
International Atomic Energy Agency
Examples of module integration
•Chemical treatment
•Filtration
•Ion exchange
•Solid waste sorting
•Encapsulation
International Atomic Energy Agency
Example of module integration
• Chemical
treatment
• Cross-flow
filtration
• Ion exchange
• Solidification of
sludge and IX
media
International Atomic Energy Agency
Storage
International Atomic Energy Agency
Waste package types
• The majority are based on 200-litre waste drums
• Typical dimensions: 610 mm (OD) x 880 mm (high).
• Drum weight typically between 50kg (in-drum compacted
soft waste) and 400 kg for encapsulated and solidified
wastes.
• In good condition, with a protective coating
• Low radiation dose rates to allow contact handling
• Drums are clean i.e. sealed and free of external
contamination
• Drum handling by manual or electric lift trucks
International Atomic Energy Agency
Standard drums for storage
Typical mild steel drum with clamp
lid.
Mild steel drum with bolted lid. Stainless Steel Drum.
International Atomic Energy Agency
Number of Waste Packages
51 m3 when encapsulated
Typically less than 5 m3, for
the reference case 1 m3
should be used
Non-
Compactable
51 m3 after compaction
Typically less than 20 m3, for
the reference case 5 m3
should be used
Compactable
51 m3 if directly solidified.
Typically less than 0.3 m3, for
the reference case 0.1 m3
should be used
Organic Liquid
3 to 50
10 m3 if directly solidified.
If bulk volume is treated
and discharged then 500
litres of conditioned
residue.
Typically in the range 0.5 -10
m3, for the reference case 5
m3 should be used
High Volume
Aqueous Liquid
1200-litres
Typically up to 0.5 m3, for the
reference design, 0.1 m3
should be used
Low Volume
Aqueous Liquid
Equivalent
Number of
200-litre
Drums per
Annum
Estimated Annual
Conditioned Waste
Volume for Reference
Design
Annual Quantity to be
ProcessedWaste Stream
51 m3 when encapsulated
Typically less than 5 m3, for
the reference case 1 m3
should be used
Non-
Compactable
51 m3 after compaction
Typically less than 20 m3, for
the reference case 5 m3
should be used
Compactable
51 m3 if directly solidified.
Typically less than 0.3 m3, for
the reference case 0.1 m3
should be used
Organic Liquid
3 to 50
10 m3 if directly solidified.
If bulk volume is treated
and discharged then 500
litres of conditioned
residue.
Typically in the range 0.5 -10
m3, for the reference case 5
m3 should be used
High Volume
Aqueous Liquid
1200-litres
Typically up to 0.5 m3, for the
reference design, 0.1 m3
should be used
Low Volume
Aqueous Liquid
Equivalent
Number of
200-litre
Drums per
Annum
Estimated Annual
Conditioned Waste
Volume for Reference
Design
Annual Quantity to be
ProcessedWaste Stream
International Atomic Energy Agency
1 for solid waste
1 for liquid waste
1 for sealed
sources
Interim decay storageTypically less than 0.5 m3 of solid
and liquid waste and less than 10
disused sources, for the reference
case 0.2 m3 of solid and liquid
waste and 5 disused sources
should be used
Waste and Disused
Sources Suitable
for Decay Storage
2Assumed 400-litres when
encapsulated
Typically up to 0.5 m3, for the
reference case 0.1 m3 should be
used
Biological
(Carcasses)
5 to 20Depends on physical size of
source in shielded container.
Assumed 1 to 4 m3 when
encapsulated
Large variation of number of
sources, for the reference case 20
should be used
Disused Sealed
Source - Long
Lived Isotope
5 to 20Depends on physical size of
source in shielded container.
Assumed 1 to 4 m3 when
encapsulated
Large variation of number of
sources, for the reference case 20
should be used
Disused Sealed
Source - Short
Lived Isotope (<30
Years)
1200-litres when
encapsulated
Typically less than 0.5 m3, for the
reference case 0.1 m3 should be
used
Sludge
1 to 2250-litres when
encapsulated
Typically less than 0.5 m3, for the
reference case 0.1 m3 should be
used
Ion Exchange
Resins
Equivalent
Number of 200-
litre Drums per
Annum
Estimated Annual
Conditioned Waste
Volume for Reference
Design
Annual Quantity to be
Processed
Waste Stream
1 for solid waste
1 for liquid waste
1 for sealed
sources
Interim decay storageTypically less than 0.5 m3 of solid
and liquid waste and less than 10
disused sources, for the reference
case 0.2 m3 of solid and liquid
waste and 5 disused sources
should be used
Waste and Disused
Sources Suitable
for Decay Storage
2Assumed 400-litres when
encapsulated
Typically up to 0.5 m3, for the
reference case 0.1 m3 should be
used
Biological
(Carcasses)
5 to 20Depends on physical size of
source in shielded container.
Assumed 1 to 4 m3 when
encapsulated
Large variation of number of
sources, for the reference case 20
should be used
Disused Sealed
Source - Long
Lived Isotope
5 to 20Depends on physical size of
source in shielded container.
Assumed 1 to 4 m3 when
encapsulated
Large variation of number of
sources, for the reference case 20
should be used
Disused Sealed
Source - Short
Lived Isotope (<30
Years)
1200-litres when
encapsulated
Typically less than 0.5 m3, for the
reference case 0.1 m3 should be
used
Sludge
1 to 2250-litres when
encapsulated
Typically less than 0.5 m3, for the
reference case 0.1 m3 should be
used
Ion Exchange
Resins
Equivalent
Number of 200-
litre Drums per
Annum
Estimated Annual
Conditioned Waste
Volume for Reference
Design
Annual Quantity to be
Processed
Waste Stream
International Atomic Energy Agency
Key functions of store
To provide safe and secure storage of conditioned
radioactive waste packages pending disposal to a suitable
repository. Safety includes the operators who will access
the store for operational duties and the public.
To provide an environment such that the waste packages
do not degrade during the period of storage so that they are
safe to retrieve and transfer to the final repository
To provide security to prevent inadvertent or malicious
entry to the store
International Atomic Energy Agency
Available options for storage
• Shielded cabinet
• Concrete container
• ISO Freight container
• Dedicated room
• Below ground vault
• Purpose built industrial building
• Existing building
International Atomic Energy Agency
Some examples of store design options
• Ideal for storage of
small waste packages
in small quantities
• Can be located within
an existing facility
• Can be locked to
provide security
Shielded cabinet
International Atomic Energy Agency
• Widely used as transport, storage
and disposal containers.
• Particularly suitable for higher
dose rate waste packages as the
box provides shielding
• Most, if not all designs have a
removable lid for loading waste
packages.
• Requires a crane and grab for
handling waste packages and
removal of the lid.
• Adds complexity and cost to drum
handling.
Concrete container
International Atomic Energy Agency
• Widely available throughout the world
• Container Safety Convention certification.
• In wind and water tight condition.
• Fitted with a steel floor (or steel cladding of the existing wooden floor, sealed to the walls) to provide a decontaminable surface.
• Finished with a good paint finish outside and inside.
• Fitted with lock boxes on the doors to improve security.
ISO freight container
International Atomic Energy Agency
Purpose designed storage building (1)
In situ reinforced concrete framed building with walls and flat roof
also made of concrete (Warm, arid climate)
International Atomic Energy Agency
Purpose designed storage building (2)
In situ reinforced concrete framed building with concrete walls and
pitched roof to improve water run-off (Warm, humid climate).
International Atomic Energy Agency
Purpose designed storage building (3)
Steel framed, metal clad and thermally insulated building with
pitched roof (Cold climate).
International Atomic Energy Agency
Selection of Technical Options for Storage
Decision Flowcharts:
• Storage Strategy
• Store type selection
• Ventilation requirements
• Shielding requirements
• Mechanical handling requirements
• Implementation of storage facility project
International Atomic Energy Agency
Store type selection
• Is the total waste inventory and classification known for storage in a new facility?
• Are high activity radiation sources to be stored?
• Are the waste packages small and few in number?
• Is the total anticipated inventory of waste packages < 20 drums?
• Is the typical annual volume of waste received > 50 drums/year?
• Is anticipated period of storage > 10 years?
• Are the waste packages to be retrieved and/or inspected periodically?
International Atomic Energy Agency
Ventilation Requirements
• Do local environmental conditions involve extended periods
of high relative humidity?
• Can waste be packaged within stainless steel drums?
• Are volatile nuclides or hazardous gases likely to be
released?
• Is ventilation required to reduce the exposure?
• Can the necessary ventilation be achieved by natural
means?
International Atomic Energy Agency
Shielding requirements
• Are waste package surface dose rates acceptable for contact handling?
• Are dose rates from operating the store within regulatory requirements?
• Are dose rates from operating the store ALARA?
International Atomic Energy Agency
Mechanical Handling Requirements
• Can the waste package be safely handled manually?
• Does the size and quantity of waste packages require
powered handling facilities?
• Is electrical power available to support powered
handling equipment?
International Atomic Energy Agency
Store specifications
• Overall Functional Requirement
• Scope
• Location of the Storage Building
• Wastes Description Size/weight of packages
Radiological characteristics
Number of Packages
Period of Storage
• Operational Requirements (Normal and Abnormal Conditions)
• Information and Records
International Atomic Energy Agency
Store specifications (contd.)
• Building Functional Requirements Overall construction
Ground Conditions
Building Base Slab/Floor
Building Structure
Finishes
Shielding
Access
Modular construction
Waste Drum/Package Stacking
Fire protection
International Atomic Energy Agency
Some shielding options
International Atomic Energy Agency
Store specifications (contd.)
• Mechanical Handling Requirements
• Mechanical Equipment Requirements
• Electrical Equipment Requirements
• Environmental Control
• Environmental Conditions
• Seismicity
• HVAC Requirements
• Radiation Safety Requirements
• Industrial Safety Requirements
• Physical Protection / Security Requirements
• Maintenance and Inspection Requirements
• Reliability
• Standards
• Quality Assurance
• Training
International Atomic Energy Agency
Training courses & workshops on Modular WPSF
• Moldova, March 2009
• Armenia, July 2009
• Columbia, Jan 2010
• South Africa, August 2010
International Atomic Energy Agency
• Enable Operator to
select technical options for processing and storage - available
prepare technical specifications for procurement- available
develop safety case and safety assessment- future work with WES
develop operating procedures- future work in WTS
prepare a licensing application for design, construction and operation- existing document to be integrated
• Enable Regulator to
define the requirements for operating license - future work with WES
scrutinize and evaluate licensing application prior to granting of license - future work with WES
Integrated modular WPSF package for MSs with low volumes of RW and DSRS
International Atomic Energy Agency
Thank you
for your attention