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Behaviour of Carbon-14 Released from Activated Steel in Repository - - PowerPoint PPT Presentation
Behaviour of Carbon-14 Released from Activated Steel in Repository - - PowerPoint PPT Presentation
Behaviour of Carbon-14 Released from Activated Steel in Repository Conditions a Key Issue in the Long-term Safety of Decommissioning Waste NKS Seminar on Decommissioning of nuclear facilities, Studsvik, Nykping, Sweden, September 2010 1
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Contents of the presentation
- origin and activity of C-14 in activated metal components
- final disposal of activated components in Loviisa NPP
- corrosion as the release mechanism
- chemical speciation of the released carbon
- some comments on the conducted experimental work
- approach chosen for the safety assessment of Loviisa NPP
decommissioning plan
- possible mechanisms to affect the speciation
- ideas for further experimental work - and related problems
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Origin and activity of C-14 in activated metal components
- Neutron activation, three
reactions:
– N-14 (n,p) C-14 – C-13 (n,g) C-14 – O-17 (n,a) C-14
- In an LWR, in stainless
steel the reaction from N-14 dominates
Induced activity in the decommissioning waste
1E+2 1E+3 1E+4 1E+5 1E+6 1E+7 1E+8 1E+9 1 10 100 1000 10000 100000 1000000
time, yrs activity, GBq
TOTAL C-14 Ca-45 Mn-54 Fe-55 Co-60 Ni-59 Ni-63 Eu-152 H-3
Induced activity in the decommissioning waste of the Loviisa NPP
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Final disposal of activated components; case: Loviisa NPP, reactor pressure vessel with internals
- One-piece removal of large
components
- Reactor internals are packed in
the RPV
- The nozzles are sealed.
- Surrounding concrete silo
structure
- Low corrosion rate
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Release from steel and chemical speciation of carbon
- Carbon is assumed to be released from steel, as the steel corrodes.
- In anaerobic conditions in cementitious environment the corrosion rate is
low (~0.1 µm/a).
- Diffusion from steel is believed to be low compared to corrosion.
- Chemical speciation in the activated steel (carbide?; what happens if C-
14 is formed from N-14 as nitride? High neutron energy involved.)
- Chemical speciation after being released from the activated steel?
– carbonate? => low solubility and large amount stable carbonate in the cementitious repository conditions => OK – soluble organic form? => possibly very mobile – gaseous organic form? => solubility, mobility
- According to Pourbaix diagram the organic forms should not be stable in
the alkaline and reducing repository conditions; still there are indications
- f their existence.
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Possible migration routes for C-14 from the repository to the biosphere
C-14 ORGANIC INORGANIC DISSOLVED CARBONATE
- NEGLIGIBLE
RETAINED IN CARBONATE FORM RETAINED IN REPOSITORY WELL GAS LIQUID WELL TRANSPORTATION IN GAS PHASE DISSOLVED GAS METABOLISM - PLANT UPTAKE ATMOSPHERIC RELEASE ATMOSPHERIC RELEASE ATMOSPHERIC RELEASE
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Some comments on the available literature and the conducted experimental work
- Only few relevant articles on experimental results are available.
- Experimental works by Deng et al. (1997) and Kaneko et al. (2003) are often
cited
– open questions regarding coverage, representativeness and relevance for the repository issue
- phenomenology to some extent unclear
- redox conditions may not be representative
- Both gaseous and soluble organic compounds were detected
- No straightforward quantitative conclusions can be drawn.
- A master’s thesis (Kuitunen 2007) was financed by Fortum for the safety
assessment of Loviisa NPP
– Literature survey – …even though the formation of organic species has not been confirmed, their existence cannot be denied and this should be taken into account in the future safety assessments.
- Research is going on…
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Approach chosen for the safety assessment of Loviisa NPP decommissioning plan
- Release from the metal according to the corrosion rate
- Soluble and mobile chemical form assumed
- Sensitivity analysis: gaseous chemical form
- => C-14 is the dominant nuclide
1.0E+03 1.0E+04 1.0E+05 1.0E+06 1.0E+07 1.0E+08 1.0E+09 1.0E+10 1.0E+11 1.0E+03 1.0E+04 1.0E+05 1.0E+06 Time (a) Release rate (Bq/a) C-14 Ni-59 Tc-99 Nb-94
Release rates as 1000 years’ averages compared to regulatory constraints (dashed lines)
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Possible phenomena/mechanisms to tackle the problem
- chemical reactions between organic forms and carbonate; kinetics?
- some catalysts to enhance the reactions
- isotopic exchange
- radiolysis to decompose the organic molecules
- microorganisms
- …
- behavior of the organic species: sorption, diffusion?
- => Need for further experimental work
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Questions and ideas for further experimental work - and related problems
- A long phenomenological chain from the steel to the biosphere; which
phenomena are to be investigated?
- Is C-14 chemically similar to C-12 in steel => research work with radioactive
substances.
- Accelerated corrosion is probably needed in the experiments, but how not to
disturb the speciation of carbon?
- The reported experiments should be repeated with additional measurements.
- All the chemical species should be measured.
- If assumed to be organic => possible reactions and their kinetics (possible to
experiment with inactive substances).
- Long timescales characterize the repository conditions => how to accelerate the
experiments.
- Research within NKS?
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Conclusions
- C-14 in activated steel components may be one of the major dose
contributors in the decommissioning waste.
- Chemical speciation of C-14 in repository conditions is not completely
clear.
- Organic species may be significantly more mobile than inorganic ones.
- The problem is characterized by a long phenomenological chain from the
steel to the biosphere.
- Further research is necessary to reveal the main chemical reactions and
their kinetics.
- A more detailed – and possible less conservative – modelling can be
applied only if the phenomenology is sufficiently well known.
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