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Transcript of Neptunium behaviour in PUREX and GANEX · PDF fileNeptunium behaviour in PUREX and GANEX...
Neptunium behaviour in PUREX and GANEX processes
C. Gregson, M. Carrott, D. Woodhead, R. Taylor
SNEC 2014, Manchester
Challenges in Np separations chemistry
•Background
•Neptunium extraction in an Advanced PUREX process
•Neptunium extraction in a GANEX process
Options for future fuel cycles
Homogeneous
Recycling
FR R
U, Pu, MA
FR R
MA
U, Pu
FP
Heterogeneous
Recycling
Advanced PUREX +
DIAMEX-SANEX or EXAm
GANEX
R: Recycle plant
FR: Transmutation reactor
V: Vitrification
V
FP
V
Requirements for advanced reprocessing
Optimise recycling processes so the option to close the fuel
cycle by ~2050 is competitive with other spent fuel
management options
• Reduced costs
• Reduced wastes
• Reduced environmental impact
• Enhanced process safety
• Enhanced proliferation resistance / safeguards
• Enhanced public acceptability
• Flexibility to process wider range of fuel types
• Integrated with fuel fabrication and waste management
PROCESS SIMPLIFICATION / INTENSIFICATION / INNOVATION
Np in the fuel cycle
•Current closed fuel cycles Np in HLW glass
• 237Np radiotoxicity in environment
• Past use for 238Pu production
• Future fuel cycles can burn Np in Pu/TRU fuels
•Current reprocessing by PUREX process Np is split across several streams
•Requires extra SX cycle to decontaminate
•Advanced reprocessing direct Np to single stream
• Reduced costs, wastes
• Enhance proliferation ‘resistance’
Np redox chemistry in HNO3
OHHNONpO
HNONpO
2222
32
2
1
2
1...
...2
3
2
1
NpO2+
NpO22+
Np4+
HNO3 / HNO2
HNO3 / HNO2
Disproportionation
OHNpONp
HNpO
222
4
2
2
42
3 easily inter-convertible oxidation states in HNO3
Np(V) oxidation vs. Np(VI) reduction in HNO3
0
0.2
0.4
0.6
0.8
1
0 5 10 15 20 25 30 35 40
time (min.)
Np(V
) R
el. A
bs.
Np(VI) with 1 mM NaNO2 Np(V) with 1mM NaNO2
Np(V) zero nitrite Np(VI) zero nitrite
Addition of 1 mM NaNO2
Reduction of Np(VI) and oxidation of Np(V) in 5 M HNO3 at 50oC with and without NaNO2
No HNO2 to catalyse the redox reaction
No HNO2 to catalyse the redox reaction
HNO2 added catalyses Np(V) oxidation
HNO2 added reduces Np(VI)
Np(V)/Np(VI) equilibrium position
defined by HNO3/HNO2
Np extraction in PUREX
D(NpVI) > D(NpIV) > D(NpV)
Need to stabilise the middle oxidation state
aqueous
organic
NpNp
NpD
][
][
Np(VI) = very extractable
Np(IV) = extractable
Np(V) = not extractable
Conventional PUREX process
~30 % Np
HA Feed
~70 % Np
How can we achieve 100 % extraction in future SX processes? -pulsed columns -centrifugal contactors
Condition U Finishing
Diluent washCondition
HAF
HAR 30% TBP
HA35C
HS50C
HNO3
30% TBP
20% TBP
UIV/N2H4
UIV/N2H4
HNO3
1BX35C
1BS
1BXX 35C 1C 50C
UP1 25C
25C UP2 50C
UP3 40C
PP1S45C
PP1E45C
PP2
HAN
HNO3
30% TBP
Diluent washCondition
Concentrate Finishing
HAN
HNO3
UIV/N
2 H4
HAN
20% TBP
Condition U Finishing
Diluent washCondition
HAF
HAR 30% TBP
HA35C
HS50C
HNO3
30% TBP
20% TBP
UIV/N2H4
UIV/N2H4
HNO3
1BX35C
1BS
1BXX 35C 1C 50C
UP1 25C
25C UP2 50C
UP3 40C
PP1S45C
PP1E45C
PP2
HAN
HNO3
30% TBP
Diluent washCondition
Concentrate Finishing
HAN
HNO3
UIV/N
2 H4
HAN
20% TBP
Advanced PUREX process
Simplified PUREX process •Single cycle SX flowsheet
•Np control
•In a single stream
•With Pu-U product
•With U then separated
Minor actinide (Am,Cm) separations require additional SX cycles on HLW
Extract/scrub
U/Pu separation Np barrier
A1: Pu,Np
A2:Pu,U,Np
B: Np
HLW
(Am,Cm,FPs)
Dissolved SNF
Np follows U,Pu
Option A. Np follows Pu Option B. Np follows U
U backwash
U
GANEX Process
Dissolved
SNF
U
extraction
U
GANEX 1st cycle
An + Ln
extraction
FPs
An stripping Ln stripping
Ln
GANEX 2nd cycle
Pu, Np, Am, Cm
Co-separation of all TRU actinides
PUREX vs. GANEX processes
• SX from nitric acid into an organic kerosene phase
• Different extracting ligands
N
O
C2H
4
N
O
C8H
17
CH3
CH3
C8H
17
O
C6H
13
OP
O
O
O
TODGA DMDOHEMA
TBP
ON
O
N
O
C8H17
C8H17C8H17
C8H17
ON
O
N
O
C8H17
C8H17C8H17
C8H17
U Pu Np
U Pu Np Am Cm
PUREX
EURO-GANEX
Np extraction depends on
• HNO3
• HNO2
• Extraction of HNO2 and Np(VI) into solvent
• U saturation of the solvent
• Chemical kinetics in aqueous and organic phases
• Temperature
• Any other redox active species
• Residence time in contactor
• Mixer-settlers > pulsed columns > centrifugal contactors
Common problem to Advanced PUREX & GANEX processes
Np extraction in Advanced PUREX
• Experiments increasing in complexity
• Single phase, 2-phase, single centrifugal contactor stage
• Flowsheet trial
• Modelling
• …See talk by Hongyan Chen!
• The Np(V) oxidation reaction is promoted by
• Conditions in aqueous solution
• High [HNO3], [HNO2]/[Np](aq) ~ 2, T = 50C
• U loading reduces D(HNO2)
• Within a flowsheet need to consider:
• Sufficient [HNO2] in regions of low [U] during extraction
• Increase [HNO3] across the extract section
• Elevated temperature around the extract and scrub section
NNL Np extraction flowsheet test
1 HS1 4 5 HA1 8 9 HA2 12 13 HA3 14
HEATER HEATER
HA
F1 F2
SP1
A2
FC1
AR1
S1
A1
1 HS1 4 5 HA1 8 9 HA2 12 13 HA3 14
HEATER HEATER
HAF
F1 F2
SP1
A2
FC1
AR1
S1
A1
1 HS1 4 5 HA1 8 9 HA2 12 13 HA3 14
HEATER HEATER
HA
F1 F2
SP1
A2
FC1
AR1
S1
A1
1 HS1 4 5 HA1 8 9 HA2 12 13 HA3 14
HEATER HEATER
HAF
F1 F2
SP1
A2
FC1
AR1
S1
A1
Miniature centrifugal contactors
Simulant feed U+Np
No hot test yet
CEA Np extraction test
HAF
HAR <0.11 % Np
30% TBP
E1
E2
HNO2
HNO3
30% TBP
X
S HNO3
SP U,Np,Pu
AR <0.25 % Np
•Spent fuel test
•LWR UOx fuel
•Pulsed columns
Dinh, B., et al. in Solvent
extraction: fundamentals to
industrial applications.
Proceedings ISEC 2008
International Solvent
Extraction conference
pp.581-586 (2008).
Key results – 2 successful tests
NNL
• >99 % Np extracted
• U/Np test
• HNO2 added
• No radiation field
• HM ~ 250 g/L
• Centrifugal contactors
• Lab scale
• Heated to 50 C (stages 1-8)
• 4.5 mol/L HNO3 feed
CEA
• >99.6 % Np extracted
• Spent fuel test
• No HNO2 feed required
• Radiolytically generated HNO2
• HM ~250 g/L
• Pulsed columns
• Pilot scale
• Ambient temperature
• 4.5 mol/L HNO3 feed
Np extraction in GANEX
1.E-01
1.E+00
1.E+01
1.E+02
1.E+03
0.1 1 10
[HNO3]aq,ini (M)
DN
p
Np(IV) 0.2M TODGA
Np(VI) 0.2M TODGA
Np(IV) 0.5M DMDOHEMA
Np(VI) 0.5M DMDOHEMA
1.E-02
1.E-01
1.E+00
1.E+01
1.E+02
1.E+03
1.E+04
0.1 1 10
[HNO3]aq,ini (M)
DN
p
Np(IV)
Np(VI)
Np(V)
GANEX: Np(IV)>>Np(VI)>>Np(V) Np(IV): TODGA>DMDOHEMA Np(VI): DMDOHEMA>TODGA Np(V) more extractable than PUREX
Optimising Np extraction
-0.05
0
0.05
0.1
0.15
0.2
0.25
0.3
600 700 800 900 1000 1100 1200 1300
Wavelength (nm)
Ab
so
rba
nc
e
10 minutes following extraction
17 hours following extraction at RT
Np(IV) Np(V)+(IV)
Np(IV)+(VI) Np(VI) in DMODHEMA
Initial aq. = 5 M HNO3
Stability Np(IV)>Np(VI)>>Np(V)
Promote extraction by promoting Np(V) disproportionation in flowsheet
Np(V) disproportionation
• Redox reaction residence time dependent
• Faster in organic phase than aqueous phase
• Faster in GANEX solvent than PUREX solvent
• Rate increases with increased nitric acid concentration and temperature
• Kinetic equation derived in 30 % TBP
• Products Np(IV,VI) are both extractable
• Promoting disproportionation should promote extraction
“EURO-GANEX” process tests
13 Scrub 16
32 Ln Strip 29
Solvent Feed
0.5M HNO3 Active feed 5.9 M HNO3 + 0.055 M CDTA SF solution (10 g/L Pu)
FPs
0.01M HNO3
Actinides Lanthanides
Lanthanides
Pu, Np, Am, Cm
Extract
Solvent Feed
Solvent Raffinate
0.5M HNO3 1M AHA 0.055M BTP
1 12
An Strip 28 17
23 22
Loaded Solvent Feed
Flowsheet results
Glovebox test (NNL)
Hot cell test
(ITU)
Contactors Centrifugals Centrifugals
Feed Surrogate Fast reactor spent fuel
Pu content in feed (g/L) 10 10
Pu recovery in E/S (%) > 99.9995 100.0
Am recovery in E/S (%) > 99.99 100.0
Np recovery in E/S (%) ~71 99.93
Np in HAR (%) ~ 29
Np in TRU product (%) ~69 99.9
Conclusions & outlook
• Np control is one of main chemistry challenges for advanced
reprocessing
• Affects plant layout, economics, waste management, proliferation
resistance, corrosion
• Complex chemistry in nitric acid and organic phases
• Extraction is residence time dependent
• Now demonstrated that complete extraction is achievable by
adjustment of acidity and temperature
• In advanced PUREX flowsheets
• In EURO-GANEX flowsheet
• & with short residence time centrifugal contactors
• Enhanced extraction under HA conditions (with SNF)
• Predictive & mechanistic based models now required…
Acknowledgments
NNL Signature Research programme in Spent Fuel and Nuclear Materials
EU Framework VII project “ACSEPT”
Sellafield Ltd.
UK Nuclear Decommissioning Authority
Chris Maher, Chris Mason, Katie Bell, Jamie Brown, Mark Sarsfield, Zara
Hodgson (NNL), Helen Steele (NNL/CEA)
Danny Fox, Cécile Roube, Gill Crooks, Chris Jones, Eddie Birkett (ex-NNL)
ACSEPT project – Andreas Geist (KIT), Rikard Malmbeck (ITU), Giuseppe
Modolo, Andreas Wilden (FZJ), Xavier Hères, Stéphane Bourg, Manuel
Miguirditchian (CEA)
Colin Boxall, Scott Edwards (Lancaster University)
Megan Jobson, Hongyan Chen, Andrew Masters (University of Manchester)
Key references 1. M. J. Carrott, et al. Neptunium extraction and stability in the GANEX solvent (0.2 M TODGA / 0.5 M DMDOHEMA /
kerosene), Solv. Extr. Ion Exch. 31, 463-482 (2013).
2. R. J. Taylor et al. Progress towards the full recovery of neptunium in an Advanced PUREX process, Solv. Extr. Ion
Exch. 31(4) 442-462 (2013).
3. C. Gregson et al. Neptunium (V) oxidation by nitrous acid in nitric acid, Procedia Chemistry, 7, 2012, 398-403