theramin technical training school...alignment of technologies and waste types ... incineration with...
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THERAMIN
Technical Training SchoolWhy use thermal treatment?
Benefits and challenges
Steve Wickham (Galson Sciences Ltd.)
12th June 2019
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Acknowledgements
THERAMIN – EC funding
Contributors to THERAMIN Work Package 2
Slimane Doudou, Emily Phipps, Adam Fuller, Liz Harvey,
Jenny Kent (Galson Sciences)
Christophe Girolde, Maxime Fournier (CEA)
Etienne Fourcy, Remy Lesachey (Orano)
All WP2 questionnaire respondents
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Outline
Waste management lifecycle
Conventional waste management routes
Thermal technologies and strategic drivers
Alignment of technologies and waste types
Benefits and challenges of thermal treatment
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Waste Management Lifecycle
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NDA Integrated
Waste
Management
Strategy, 2018
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Waste Management Lifecycle
Pre-treatment: operations prior to waste treatment (e.g., dismantling, size reduction)
Treatment: operations to improve safety, economics of waste management (e.g., volume reduction, change of physical or chemical state, concentration of activity)
Conditioning: operations to produce a waste package suitable for transport, storage or disposal (may involve immobilisation, encapsulation)
Storage: maintaining waste packages in safe confinement to ensure retrievability
Transport: movement of waste packages
Disposal: emplacement of waste packages without intention to retrieve
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Ojovan and Lee, 2014
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Radioactive Waste Treatment
Objectives of treatment respond to fundamental
principles of radioactive waste management
(IAEA, 1995)
Additional requirements of optimisation, BAT/BPM,
ALARP and the waste hierarchy
Typically the objectives of treatment are:
Volume reduction
Concentration / removal of radionuclides
Change of physical state and chemical composition
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Radioactive Waste Treatment
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Waste Type Treatment Examples
Aqueous
Liquid
Concentrate activity,
discharge remainderEvaporation, sorption, filtration
Organic
Liquid
Convert to solid,
oxidiseIncineration, absorbent polymers
Solid
Minimise volume Compaction / supercompaction
Oxidise / destroy
reactivity / convert to
inorganic form
Incineration / pyrolysis
Other thermal treatments (melting, glass
encapsulation, HIP)
Chemical /thermochemical decomposition
Remove activity Decontamination
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Immobilisation of Radioactive Wastes
Changes the form of the waste such that the resulting product can be safely handled, transported, stored and disposed of
A requirement for storage / transport / disposal
May consider as treatment or conditioning
May be applied to raw waste, as a treatment process itself, or as a conditioning/packaging step applied to the products of waste treatment
Main commercially available technologies are/have been:
Cement encapsulation (conditioning)
Bituminisation (conditioning)
Vitrification (treatment/conditioning)
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Cement Encapsulation
Main technology adopted for immobilisation of LLW and ILW
Benefits: Inexpensive and readily available
Simple, low-cost process
Cement matrix acts as a diffusion barrier and provides sorption
Can be used for sludges, liquors, dry solids
Wasteforms generally have good thermal/chemical stability
Reduces solubility of many radionuclides
Non-flammable, good compressive strength, not degraded by radiation
Many cement-encapsulated waste packages disposed (LLW/SL-ILW) or in storage pending disposal (ILW)
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Cement Encapsulation
Challenges:
Cement encapsulation leads to a ~3-fold volume
increase
− More packages, higher storage/disposal capacity requirements
→ higher cost
Some waste components interact with cement
− Reactive metals, organic ion exchange resins, and plutonium-
contaminated materials (PCM)
− Retard cement hydration reactions
− Long-term waste package degradation (gel formation, expansive
corrosion of reactive metals)
− Some legacy cemented wastes do not meet WAC /disposability
criteria
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Bituminisation
Used since the 1960s - >200,000 m3 currently
worldwide
Particularly suitable for water-soluble wastes
(e.g., bottom residues from evaporators) and
spent organic resins
Most water evaporated to produce homogeneous
bitumen compound with:
Higher waste loading than cement
Better radionuclide retention than cement
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Bituminisation
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Challenges:
Potential fire hazard
Reactive product – gas
generation, salts
Bituminised waste presents
challenges for operational and
long-term disposal safety
cases
Has become a legacy waste in
some countries, requiring
further treatment to destroy
organic component
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Vitrification Thermal treatment (vitrification) used for nuclear waste immobilisation for >50
years Belgium, France, Germany, Japan, Russia, UK, USA
Benefits: Immobilise a wide range of elements
Simple technology adapted from glass manufacturing
Small volume of resulting glassy waste form
High chemical durability of glassy wasteforms in contact with natural waters
High tolerance to radiation damage
Hazardous waste constituents immobilised by direct incorporation into the glass structure (dissolution in the melt) or by encapsulation Borosilicate glasses have been first choice for immobilisation of HLW and LLW/ILW
Typical temperature range 1100 - 1300ºC to prevent excessive volatilisation
Main application has been to HLW from reprocessing (>23,000 t worldwide by 2011)
Operating industrial facilities for LLW/ILW in South Korea, Switzerland, Russia, USA Several other facilities for LLW/ILW in development
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Thermal Technologies for Radioactive Waste Treatment
Definition of thermal technologies (IAEA TecDoc 1527) Use heat to break down organic components of the wastes,
producing inorganic, non-flammable, chemically inert and relatively homogeneous end products; or
Destroy organic components while melting inorganic components; or
Involve the assistance or application of heat at temperatures in excess of 600ºC
Three broad technology areas considered in THERAMIN for application to LLW/ILW Treatment for volume reduction and passivation (e.g.,
incineration, pyrolysis, gasification)
Treatment/conditioning by immobilisation in glass (e.g., vitrification)
Treatment/conditioning by immobilisation in ceramic or glass-ceramic (e.g., HIP)
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Thermal Technologies
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Treatment for volume
reduction and
passivation
Treatment /
conditioning by
immobilisation in glass
Treatment /
conditioning by
immobilisation in
ceramic or glass-
ceramic
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D2.3 Technologies
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High-level process Technology Facility Country
Treatment for volume reduction and
passivation
Incineration with burner and refractory
walls
JÜV 50/2 - Jülich JEN Germany
KTE incinerator Germany
EDF CENTRACO France
Rotary kiln incineration IRIS France
Pyrolysis Belgoprocess Belgium
Thermal gasification VTT gasification Finland
Calcination Widely used France, UK
Underwater plasma incineration ELIPSE France
Hydrothermal Oxidation (HTO) DELOS France
Induction metal melter
CARLA Germany
EDF CENTRACO France
Cyclife (formerly Studsvik) Sweden
Treatment / Conditioning by immobilisation
in glass
Joule-Heated In-Container
Vitrification
In-Can Melter and DEM & MELT
(metallic inner wall), CEAFrance
GeoMelt (ceramic inner wall), NNL UK
Joule-Heated Ceramic Melter (JHCM)VEK, PAMELA (both
decommissioned)
Germany,
Belgium
Cold crucible induction melter (CCIM)La Hague CCIM and Marcoule CCIM
pilotFrance
Advanced CCIM (A-CCIM) Marcoule A-CCIM pilot France
Indirect induction (metallic wall - hot
metal pot)
VICHR Slovakia
La Hague and Sellafield France, UK
Coupled cold wall direct metal
induction melting and plasma burnerPIVIC France
Coupled cold wall direct glass
induction melting and plasma burnerSHIVA France
Refractory wall plasma burning and
melting
Retech (ZWILAG) Switzerland
EUROPLASMA – Belgoprocess Bulgaria
Tetronics UK
Treatment / Conditioning by immobilisation
in ceramic or glass-ceramic HIP
NNL – Workington and University of
SheffieldUK
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Technical Drivers for Thermal Treatment
Stable, durable wasteform
Removal / decomposition / incorporation of reactive waste constituents
Volatiles driven off
Product has limited / no water content
Product has limited / no gas generation
Product has limited / no organics or complexants
More homogeneous wasteform with well-distributed radionuclides
Opportunity for better characterisation
For some technologies, consolidated (monolithic) wasteform with low voidage and low porosity
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Strategic Drivers for Thermal Treatment
Significant reduction in the number of waste packages / containers (c.f., cement encapsulation) Reduced storage capacity, transport movements and disposal
capacity
Reduced packaging, transport, storage and disposal cost
Increased passivity that could mitigate the need for package rework Greater confidence in long-term performance for certain waste groups
Provide national/international treatment services Bespoke solutions for problematic wastes (wastes without an obvious
management route)
Contingency for reworking degraded legacy waste packages Ensure compliance with the near-surface / geological disposal WAC
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Three Hypothetical Examples
1) Thermal treatment (vitrification) as an
alternative encapsulation approach
2) Thermal treatment to remove / destroy reactive
waste constituents
3) Thermal treatment to provide enhanced
containment / controlled release of radioactivity
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Vitrification as an alternative encapsulation approach
Principal motivations are the potential for: Reduced volume of conditioned waste
Reduced plant footprint
Reduced carbon footprint
Faster processing / packaging throughput
Additional benefits are possible (e.g. reduced reactivity / gas generation)
Key product characteristics Effective waste encapsulation
Low voidage wasteform
Particular relevance to ILW streams that are not easily mixed into cement slurries e.g. metals, decommissioning wastes
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Thermal treatment to remove / destroy reactive waste constituents
Principal motivations are the potential to: ‘Pre-react’ waste so that it is inert during storage and disposal –
avoid detrimental interactions with other wastes
Enhanced passive safety of wasteform improves operational safety case – in keeping with ALARP principles
Minimise potential requirement for repackaging
Various approaches could be applied Vitrification – may require pre-treatment step to break down
waste constituents
Incineration
Gasification / pyrolysis
Hydrothermal oxidation
Principally relevant for wastes with a high organic, liquid or reactive metal content, including oils, solvents,…
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Additional appeal if there are also strong drivers to minimise volume reduction
• Product does not contain any matrix formers
• But may require further treatment to be disposable
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Thermal treatment for enhanced containment
Not necessarily required for ILW, but potentially relevant for other inventory components, such as separated Pu Long-term safety case for disposal relies on minimising likelihood
and consequences of criticality
Principal motivations are the potential to: Limit the release of radionuclides such as Pu-239 for a long time
after disposal (and spread releases over time)
Control the accumulation of fissile material
Key product characteristics Durable wasteform – likely to be a ceramic / glass-ceramic
Homogeneity, with waste radionuclides well distributed
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Application of Thermal Treatment
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The Choice of Treatment Route is Important
Product characteristics vary considerably depending on the
raw waste characteristics and the thermal treatment route
employed
Waste may fully react and be incorporated in a glass or ceramic
matrix
Waste constituents may be encapsulated by the matrix
Some techniques (e.g. pyrolysis) cause thermal decomposition
but do not produce a consolidated solid product
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What Makes a Disposable Product?
Depends on waste acceptance criteria (WAC) at the relevant disposal facility
Geological disposal: may depend on generic disposability criteria – influences operation of treatment / conditioning facility
For near-surface disposal: meet WAC for relevant facility
Near-surface disposability
In UK, disposal routes to LLWR / VLLW facilities established for active products from Geomelt trials
Extension to larger volumes / more active waste uncertain
Key issues: concentration of activity; discrete items
− Implications for dose associated with human intrusion scenarios
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THErmal treatment for RAdioactive waste MINimisation and hazard reduction (THERAMIN)
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Alignment of Waste Characteristics and Treatment Route
Work has been
conducted under
THERAMIN WP2
to match waste
groups to thermal
treatment routes
Viability matrix
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Generic Waste Groups
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Waste Group Definition
Cement-conditioned solid wasteWastes which have been conditioned in a cementitious matrix. The nature of the original raw waste is
varied.
Bitumen-conditioned waste Wastes which have been conditioned in a bitumen matrix. The nature of the original raw waste is varied.
Polymer-conditioned waste Wastes which have been conditioned in a polymer matrix. The nature of the original raw waste is varied.
Metallic waste (pure or high content) Waste containing pure metal or metal mixed with other materials.
Alpha waste (including PCM)Material contaminated with alpha-emitting radionuclides (e.g. plutonium, uranium, etc.). This waste
includes PCM.
Miscellaneous contaminated solid
waste (including PVC)Other miscellaneous solid waste that is non-metallic, e.g. maintenance wastes, contaminated gravel,
concrete, etc.
Inorganic ion exchange materialIon exchange materials used for the removal of soluble radionuclides (e.g. caesium) from liquid waste
(e.g. irradiated fuel cooling pond water). Example inorganic resins include: zeolites, Ionsiv® and clays
Organic ion exchange materialIon exchange materials composed of high-molecular-weight polyelectrolytes. They are also used for the
removal of soluble radionuclides from solution.
Sludge and concentratesIncludes bulk sludge, residuals, and concentrates. Sludges arise in tanks, sumps and ponds, and
comprise a mixture of materials in particulate form.
Hazardous or Chemotoxic waste Wastes which have chemotoxic properties (e.g. Be, Cd, Hg) or which are hazardous (e.g. asbestos)
FiltersFilters are used to remove radionuclides and particulates from contaminated air or other media. Example
filters include: HEPA, charcoal filters, and cartridge filters used to remove radionuclides and particulates
from active effluent.
GraphiteWaste graphite from decommissioning of reactors that used graphite as part of the reactor design. This
could include core graphite or graphite debris from the fuel assemblies.
Organic liquids and oils Contaminated liquid waste which contains organics such as oils or solvents
Other liquid waste (e.g. Chrompik) Contaminated aqueous liquids which do not contain organics
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Task 2.2 – Strategic Analysis and Database Report
Brief descriptions of national context, programme status, and waste classifications in each country
Data gathering approach and database development
Analysis of waste to identify benefits of thermal treatment, as well as risks and barriers
Benefits could include volume reduction, passivation / remove chemical reactivity, increase GDF acceptability, reduce packaging and storage requirements, reduce costs
Identify currently planned management route and strategic benefits that could result from thermal treatment
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Existing Wastes (excl. Ukraine)
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Future Wastes
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Benefits – generic waste group matrix: Example
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Metric
Conditioned Waste
Cement-conditioned wasteBitumen-conditioned
waste
Polymer-conditioned
waste
BEL FIN FRA DEU CHE GRB BEL FIN LTU CHE CHE
Be
nef
its
Increase in wasteformstability (plus storage/disposal compatibility)
() ()
Waste volumereduction
Commercialapplication of thermal treatment technologies
Provision of (alternative) treatment routes
Cost savings
Useful for learning from experience to apply to other waste streams
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Challenges – generic waste group matrix: Example
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Metric
Conditioned wastes
Cement-conditioned wasteBitumen-conditioned
waste
Polymer-conditioned
waste
BEL FIN FRA DEU CHE GRB BEL FIN LTU CHE CHE
Ris
ks a
nd
bar
rie
rs
Lack of characterisation data
Requirement to stop ASR
Large numbers of packages needing treatment
Delays to national waste management programmes
Waste segregation
α-contamination
Increased costs/timescales
ALARP issues re waste handling
Physical and/or chemical properties of wastes
Regulatory issues
Transport restrictions
Final disposal requirements for residues following treatment unclear
Waste recovery issues
Fissile content/criticality risks
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Benefits of Thermal Treatment (1/2)
An overall increase in wasteform stability, leading to increased disposability
Elimination of organics
Chemical passivation by destroying or transforming reactive constituents
Elimination of gels formed by cement degradation
Immobilisation of corrosive / mobile species (e.g., chloride)
Volume reduction of wastes
More significant for raw (unconditioned) wastes that still require packaging for ongoing storage/disposal
Savings on storage/disposal space, transport requirements and container purchasing costs
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Benefits of Thermal Treatment (2/2)
Provision of (alternative) management routes
Potential solution for problematic wastes
Alternative to existing technologies
Can potentially accept a wide range of waste inputs - offers advantages over less flexible options
− Contingency for degrading legacy waste packages
Cooperation with other countries with similar challenges could provide a mutually beneficial solution
Cost savings
Realised throughout the waste treatment and disposal lifecycle
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Challenges – Some Pre-Treatment Issues
Lack of characterisation data
Demonstration of compliance with some key operational safety criteria may be hard to accomplish, particularly for legacy conditioned wastes
Some wastes may require segregation prior to treatment
Will increase the complexity of the treatment processing route
May have implications for keeping doses to workers ALARP
Some waste streams may be difficult to transport to a treatment facility
Difficulty of waste retrieval
Advantage of wastes that can be pumped (liquids, sludges, slurries)
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Challenges – Some Treatment Issues
Radiological risks and/or doses during treatment Ease of making relevant safety cases for thermal
Wastes containing high levels of certain radionuclides (e.g., alpha-contamination) may be more difficult to deal with More stringent off gas mitigation needs and criticality concerns
May add to operational complexity of thermal process
Waste composition and heterogeneity May need to include additives within the waste stream
before/during treatment in order to achieve a satisfactory final product
May limit the efficiency / practicability of a thermal process
Scale of process Large volume waste streams would require a different scale of
treatment process to smaller waste streams
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Challenges – Some Post-Treatment Issues
What post-treatment work is needed to ensure
disposability?
Particularly relevant to incineration / pyrolysis /
gasification
Radiological risks and/or dose issues may arise
Treatment may concentrate activity and produce a more
active waste product
Is a final disposal route currently available for all
wasteforms?
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Challenges – Some Strategic Issues
Implementing a thermal treatment option may increase costs and/or timescales, at least temporarily, over the baseline management option
Existing cementation plants may be able to process wastes quicker and more cheaply than would be achieved by building a new thermal treatment facility
The desired properties of the final wasteform and overall cost implications may help to make the case for thermal
Industrial application of thermal treatment technologies
Long lead times
Potentially high upfront investment costs
Making an acceptable safety case at any stage of the process
− E.g., where feed wastes are highly heterogeneous and/or poorly characterised
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Case for Thermal Treatment of LLW/ILW
High durability product with good disposability Little if any risk of requiring any rework prior to disposal
Reactive components destroyed
Reduces operational and long term storage, transport and disposal risks
Potentially significant volume reduction and higher waste loading compared with conventional technologies Benefit for the organic and inorganic, solid and wet wastes
Relatively generic technology - can be applied to a wide range of waste streams Economies of scale
Opportunities to treat problematic wastes, legacy wastes
Alternative to existing technologies
Cost savings for storage, packaging, disposal
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Any Questions?
THERAMIN WP2 Lead
Steve Wickham
+44 (1572) 770 649
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