r pampin , r bestwick euratom/ukaea fusion association amec-nnc ltd

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Study on recycling of fusion Study on recycling of fusion activated materials: activated materials: Identify activation levels, Identify activation levels, characteristics and decay time characteristics and decay time requirements of irradiated material requirements of irradiated material (deliverable 3) (deliverable 3) R Pampin R Pampin , R Bestwick , R Bestwick EURATOM/UKAEA Fusion Association EURATOM/UKAEA Fusion Association AMEC-NNC Ltd AMEC-NNC Ltd TW5-TSW-001 monitoring meeting TW5-TSW-001 monitoring meeting CEN-SCK Mol, June 2006 CEN-SCK Mol, June 2006

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TW5-TSW-001 monitoring meeting CEN-SCK Mol, June 2006. Study on recycling of fusion activated materials: Identify activation levels, characteristics and decay time requirements of irradiated material (deliverable 3). R Pampin , R Bestwick EURATOM/UKAEA Fusion Association AMEC-NNC Ltd. - PowerPoint PPT Presentation

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Page 1: R Pampin , R Bestwick EURATOM/UKAEA Fusion Association AMEC-NNC Ltd

Study on recycling of fusion activated materials:Study on recycling of fusion activated materials:

Identify activation levels, characteristics and Identify activation levels, characteristics and decay time requirements of irradiated materialdecay time requirements of irradiated material

(deliverable 3)(deliverable 3)

R PampinR Pampin, R Bestwick, R Bestwick

EURATOM/UKAEA Fusion AssociationEURATOM/UKAEA Fusion Association

AMEC-NNC LtdAMEC-NNC Ltd

TW5-TSW-001 monitoring meeting TW5-TSW-001 monitoring meeting CEN-SCK Mol, June 2006CEN-SCK Mol, June 2006

Page 2: R Pampin , R Bestwick EURATOM/UKAEA Fusion Association AMEC-NNC Ltd

TW5-TSW-001 monitoring meeting, CEN-SCK Mol, Belgium, June 2006 2/13

BackgroundBackground

European Fusion Programme strategy for fusion irradiated waste:

Release from regulatory control of mildly activated material, usually lifetime, bulky, outer components: TFC, VV, LTS

Recycle within the nuclear industry (fission/fusion) the rest

PPCS radioactive waste results: all material cleared/recycled within 100 years, but:

Release criteria: out-of-date IAEA clearance levels (1996)

Lack of detail in the models (e.g. outer components)

Inadequate modelling of particular materials (e.g. LiPb)

Recycling criteria based on radiological parameters only, which were imprecise and over-conservative.

Page 3: R Pampin , R Bestwick EURATOM/UKAEA Fusion Association AMEC-NNC Ltd

TW5-TSW-001 monitoring meeting, CEN-SCK Mol, Belgium, June 2006 3/13

BackgroundBackground

PPCS recycling criteria: some sensible for certain waste streams following certain routes (e.g. re-melting of steels); “complex recycling” limit is crucial but:

(a) noticeably over-conservative and

(b) depends on route followed!!

waste categorisation criteria contact dose (mSv/h)

decay heat (W/m3)

CI

Permanent disposal (PDW) > 20 > 10

Complex recycling (CRM) 2 – 20 1 – 10

Simple recycling (SRM):

remote

hands-on

< 2

< 10-2

< 1

< 1

Clearance < 1

Page 4: R Pampin , R Bestwick EURATOM/UKAEA Fusion Association AMEC-NNC Ltd

TW5-TSW-001 monitoring meeting, CEN-SCK Mol, Belgium, June 2006 4/13

BackgroundBackground

IAEA 1996/2004 clearance levels: many changes affect fusion-relevant radionuclides (e.g. 30-fold decrease in Ni-63 level).

-5

-4

-3

-2

-1

0

1

2

3

0 50 100 150 200 250mass number (A)

log

(200

4/1

996

)

Page 5: R Pampin , R Bestwick EURATOM/UKAEA Fusion Association AMEC-NNC Ltd

TW5-TSW-001 monitoring meeting, CEN-SCK Mol, Belgium, June 2006 5/13

Scope and objectivesScope and objectives

To review and update PPCS work using:

Up-to-date international clearance regulations: IAEA 2004

Up-to-date nuclear data: EAF 2005.

Practical recycling criteria: findings of this task.

More accurate modelling methodology (e.g. LiPb flow) and increased level of detail (e.g. TFC materials).

With the aim of:

Determining more realistic amounts and description of waste according to actual processing routes.

Identifying interim decay times required before recycling.

Identifying potential for (a) reduction of waste, and (b) simplification of recycling processes.

Page 6: R Pampin , R Bestwick EURATOM/UKAEA Fusion Association AMEC-NNC Ltd

TW5-TSW-001 monitoring meeting, CEN-SCK Mol, Belgium, June 2006 6/13

Computational tools and modelsComputational tools and models

HERCULES code automates 2D geometry + material modelling of tokamak power plants, coupling:

MCNP neutron transport FISPACT transmutation + EAF libraries

W armour

vessel TF coil

breeder zone

manifold

LT shield

HT shield

Fusion Power Plant internal componentsFusion Power Plant internal components

PPCS-AB HERCULES model.

Page 7: R Pampin , R Bestwick EURATOM/UKAEA Fusion Association AMEC-NNC Ltd

TW5-TSW-001 monitoring meeting, CEN-SCK Mol, Belgium, June 2006 7/13

Computational tools and modelsComputational tools and models

187 165

143

209 121

231

99

253

275 77

297

319 55

341 33

11

vessel TF coilneutron penetration - outboard

100001000001E+061E+071E+081E+091E+101E+111E+121E+131E+141E+151E+161E+171E+181E+191E+20

0 1 2 3 4 5 6

radial distance from PF surface (m)

ne

utr

on

flu

x (n

/m2

s)

(a)(b)(c) (d) (e) (f)

(a) VV front casing 316ss

(b) VV radial plates 316ss

(c) VV rear casing 316ss

(d) TFC front casing 316ss

(e) TFC winding pack 316ss, SC cable, incoloy, epoxy

(f) TFC rear casing 316ss

a b c d e f

PPCS

PPCS

Page 8: R Pampin , R Bestwick EURATOM/UKAEA Fusion Association AMEC-NNC Ltd

TW5-TSW-001 monitoring meeting, CEN-SCK Mol, Belgium, June 2006 8/13

Preliminary resultsPreliminary results

New IAEA levels increased amounts of material to be recycled: OB VV and IB TFC.

Segregation alleviates this.

PM-AB clearance index - outboard

1.E-04

1.E-03

1.E-02

1.E-01

1.E+00

1.E+01

1.E+02

1.E+03

1.E+04

1.E+05

1.E+06

1.E+07

1.E+08

0.1 1 10 100 1000time (y)

clea

ranc

e in

dex

TFC 2004

TFC 1996

VV 2004

VV 1996

LTS 2004

LTS 1996

0

5000

10000

15000

20000

25000

30000

TFC OB TFC IB VV OB VV IB total

IAEA 1996

IAEA 2004

IAEA 2004 with segregation

PM-AB clearance index (2004) - inboard

1.E-02

1.E-01

1.E+00

1.E+01

1.E+02

1.E+03

1.E+04

1.E+05

1.E+06

0.1 1 10 100 1000time (y)

clea

ranc

e in

dex

TFC 316ss frontTFC 316ss midTFC 316ss backTFC cableTFC incoloyTFC epoxyaverage

Page 9: R Pampin , R Bestwick EURATOM/UKAEA Fusion Association AMEC-NNC Ltd

TW5-TSW-001 monitoring meeting, CEN-SCK Mol, Belgium, June 2006 9/13

Preliminary resultsPreliminary results

Cooling times of PPCS-AB and PPCS-B individual constituents and materials and average components; in preparation.

PPCS-AB IB TFC 2 mSv/h 0.01 mSv/h

rear case < 1y < 1y

rad plates < 1y 25y

front case 1y 45y

SC strand < 1y 10y

incoloy <1y 35y

epoxy-glass < 1y < 1y

average < 1y 30y

Page 10: R Pampin , R Bestwick EURATOM/UKAEA Fusion Association AMEC-NNC Ltd

TW5-TSW-001 monitoring meeting, CEN-SCK Mol, Belgium, June 2006 10/13

Preliminary resultsPreliminary results

PPCS-AB results (general):

Ex-vessel: most materials, individually or as TFC, VV and LTS, show contact dose rates < 2 mSv/h (earlier OB than IB).

Ex-vessel: many of these show < 0.01 mSv/h after suitable decay time (few years OB, several decades IB).

In-vessel: poloidal variation is negligible.

In-vessel: all Eurofer and LTS neutron shield (WC) show contact dose rates < 2 mSv/h after ~75 years.

In-vessel: LiPb breeder and W armour still exceed 2 mSv/h after 100 years:

Dominant nuclides arise from Pb and W isotopes, hence impurity control not very useful in this case! isotopic separation seems imperative reuse in fusion plant?

Page 11: R Pampin , R Bestwick EURATOM/UKAEA Fusion Association AMEC-NNC Ltd

TW5-TSW-001 monitoring meeting, CEN-SCK Mol, Belgium, June 2006 11/13

PM-AB contact dose rates - outboard

1.E-04

1.E-03

1.E-02

1.E-01

1.E+00

1.E+01

0 1 10 100 1000time (y)

cont

act

dose

rat

e (S

v/h)

1 cycle LiPb5 cycles LiPbpure Pb

Preliminary resultsPreliminary results

PPCS-AB results: W and LiPb PPCS specifications contain many impurities: (a) manufacturer limits, (b) detection limits.

PM-AB contact dose rates - outboard

1.E-04

1.E-03

1.E-02

1.E-01

1.E+00

1.E+01

0 1 10 100 1000time (y)

cont

act

dose

rat

e (S

v/h)

ppcs w 5 FPY

ppcs w 1 FPY

pure w 5 FPY

Co, Ni, Nb, Mo, Eu, Sm, Gd, Tb, Pt, Ir, Pb, U, Th, Bi, Ag, Cd, Ba, Tl, Co, Nb

Page 12: R Pampin , R Bestwick EURATOM/UKAEA Fusion Association AMEC-NNC Ltd

TW5-TSW-001 monitoring meeting, CEN-SCK Mol, Belgium, June 2006 12/13

Preliminary resultsPreliminary results

PPCS-B results (general):

In-vessel: again, all Eurofer and LTS neutron shield (ZrH) show < 2 mSv/h in ~75 years.

In-vessel: Li4SiO4, Be and W armour, however, do not meet this target Li4SiO4 and Be dose entirely due to impurities:

control of these would meet target

PMB contact dose rates - outboard

1.E-05

1.E-04

1.E-03

1.E-02

1.E-01

1.E+00

1.E+01

0 1 10 100 1000time (y)

cont

act

dose

rat

e (S

v/h)

ppcs li4sio4pure li4sio4ppcs bepure be

Co, Ni, Nb, Mo, Eu, Sm, Gd, Tb, Pt, Ir, Pb, U, Th, Bi, Ag,

Cd, Ba, Tl, Co, Nb

Page 13: R Pampin , R Bestwick EURATOM/UKAEA Fusion Association AMEC-NNC Ltd

TW5-TSW-001 monitoring meeting, CEN-SCK Mol, Belgium, June 2006 13/13

SummarySummary

Upgrading PPCS work on PPCS-AB and PPCS-B radioactive waste analysis using recent regulations, new nuclear data, improved modelling and realistic recycling scenarios.

Assess clearance/recycling potential and interim decay times.

Results:

new IAEA levels increase amount of material to recycle.

PPCS analyses over-conservative: most material suitable for “simple-recycling” after < 75y cooling time.

control of impurities crucial, not only in steels but also for e.g. Be and Li4SiO4: requirements being developed.

Further input: definition of “non-simple” recycling routes and radiological criteria.

Draft report & radiological data available shortly

[email protected]