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Partitioning and Transmutation Studies at JAEA Toshinobu Sasa J-PARC Center Japan Atomic Energy Agency

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Page 1: Partitioning and Transmutation Studies at JAEArecycle/HP2008 KOBE WS/Session1_Dr.Sasa.pdfWastes from P-T cycle - Difference of waste form - waste volume per 32,000 HMt of 4-year cooled

Partitioning and Transmutation Studies at JAEA

Toshinobu Sasa

J-PARC CenterJapan Atomic Energy Agency

Page 2: Partitioning and Transmutation Studies at JAEArecycle/HP2008 KOBE WS/Session1_Dr.Sasa.pdfWastes from P-T cycle - Difference of waste form - waste volume per 32,000 HMt of 4-year cooled

International Workshop for Asian Nuclear Prospect Page 2

Fuel Cycle with Minor Actinides- Homogeneous / Heterogeneous / Double Strata -

Management of High Level Waste- Key for sustainable energy production

- Target: Np/Am/Cm & Specific FPsLWR/FRFuelFabrication

U,Pu,(Np)

Final disposal

FP

Reprocessing

(Np), Am, Cm

Second Stratum Cycle

Partitioning

Transmutor

FP

Reprocessing Fuel Fab.

(Np), Am, Cm

MA management by power reactor- Homogeneous recycle to all FR- Heterogeneous recycle to selected FR

Double-strata cycle- Dedicated cycle for transmutation - Independent to upper cycle uncertainty

- Demands of electricity- Transition from LWR to FR- Construction schedule

- Separate desired target materials- Optimized transmutation system

Page 3: Partitioning and Transmutation Studies at JAEArecycle/HP2008 KOBE WS/Session1_Dr.Sasa.pdfWastes from P-T cycle - Difference of waste form - waste volume per 32,000 HMt of 4-year cooled

International Workshop for Asian Nuclear Prospect Page 3

Wastes from P-T cycle- Difference of waste form -

waste volume per 32,000 HMt of 4-year cooled 45GWd/HMt LWR spent fuel (=40 years operation of 40GWe generation)

Cycle without P-TCycle with P-T

Spent fuel

glass5,500m3

reprocessing

HLW

NPP(LWR/FR)

=heat-generating waste=cold waste=LLW

Sr-Cs metals &rare earths

Tc &PGM

utilized16m3

Spent fuel

NPP(LWR/FR)

calcined700m3

glass1,200m3

washing liquid

& used solvent

LLW11,000m3

reprocessing & partitioning

×11

MA

ADS transmutor

solubleFP

metallicFP ZrN hull

sodalite70m3

Alloy60m3

80m3 480m3

dry reprocessing・fuel fabrication

Addition by ADS

Page 4: Partitioning and Transmutation Studies at JAEArecycle/HP2008 KOBE WS/Session1_Dr.Sasa.pdfWastes from P-T cycle - Difference of waste form - waste volume per 32,000 HMt of 4-year cooled

International Workshop for Asian Nuclear Prospect Page 4

Disposition of P-T cycle waste- (1) Reduction of waste forms amount -

Metals & REs are vitrified into highly waste-included (30%) glass form

Sr-Cs are stabilized into the calcined waste form- Sr and Cs are separated by hydrous

titanium oxide and zeolite with recovering rate over 99.6%.

- Temperature of waste doesn’t exceed sintering temperature (1200°C) and limitation of non P-T glass waste is applicable.

- The leach rate of Sr-Cs is about 10-5

g/m2/day and is 100 times lower than that of glass form.

0.0

0.5

1.0

1.5

2.0

2.5

3.0

3.5

4.0

non-PT PT

Num

ber

of w

aste

for

ms

(/TW

h)

ZrN and hullssodalite and alloyhigh-waste-loading glassSr-Csglass (non-PT)

42%

ADS wastes

Sr-Cs

Metals & REs

Page 5: Partitioning and Transmutation Studies at JAEArecycle/HP2008 KOBE WS/Session1_Dr.Sasa.pdfWastes from P-T cycle - Difference of waste form - waste volume per 32,000 HMt of 4-year cooled

International Workshop for Asian Nuclear Prospect Page 5

Disposition of P-T cycle waste- (2) Heat generation and storage periods -

Standard grass waste requires 50 years storage for conventional repository (~44.4m2/form). Since heat generation retains due to 241Am (T1/2=432.2 yr), glass waste can’t be disposed of in the compact manner.

Sr-Cs waste requires 130 years and 320 years storage for conventional and compact repository, respectively.

Metals & REs waste can be disposed of in very compact configuration (~0.95m2/form) after 45 years storage.

1

10

100

1000

10000

0 100 200 300 400Time after production (yr)

Heat

genera

tion (W

/fo

rm)

glass (non-PT)Sr-Cs (PT)Metals & REs (PT)

350 W/form, limitation of the conventional repository130 yr

4 W/form, limitation of the compact repository

50 yr5 yr

45 yr 320 yr

Am-241 decay heat

9.3

Waste form

OverpackDispos

al tun

nel

Buffer

Disposalpit

Buffer

Conventional repository

1.2

1.6

1.2

4 Waste formsw/o overpack

Cement

Wastepackage

4.44

Tunnel spacing:10

5

5

Compact repository

Page 6: Partitioning and Transmutation Studies at JAEArecycle/HP2008 KOBE WS/Session1_Dr.Sasa.pdfWastes from P-T cycle - Difference of waste form - waste volume per 32,000 HMt of 4-year cooled

International Workshop for Asian Nuclear Prospect Page 6

Disposition of P-T cycle waste- (3) Reduction of repository area -

Repository area for unit power generation can be reduced to 15% or 1% than those of glass waste, if 130 or 320 years storage can be acceptable for Sr-Cs waste.

The reduction of waste leads to prolong lifetime of the repository.

Facility scale of hundred-years storage for Sr-Cs waste is smaller than that of repository for the conventional glass waste* (about 20% of repository).

0

20

40

60

80

100

120

140

160

non-PT PT(Sr-Cs130yr)

PT(Sr-Cs320yr)

Em

plac

ement

are

a (m

2/T

Wh)

ADS wastes

High-waste-loading glass

Sr-Cs

Glass

1.6

15%1%

* K. Nishihara, et al., “Impact on Partitioning and Transmutation on LWR High-Level Waste Disposal,” J. Nucl. Scie. Technol., 45, 1-14 (2008).

Page 7: Partitioning and Transmutation Studies at JAEArecycle/HP2008 KOBE WS/Session1_Dr.Sasa.pdfWastes from P-T cycle - Difference of waste form - waste volume per 32,000 HMt of 4-year cooled

International Workshop for Asian Nuclear Prospect Page 7

Activities for Partitioning in JAEA- FaCT program and Basic Studies -

・Novel inorganic adsorbent (cation exchanger)・Extraction chromatography

-Sr-Csseparation

・Ion exchange (Tertiary Pyridine Resin-HNO3-MeOH)-Am/Cmseparation

・SETFICS (Solvent extraction by CMPO with DTPA)・TALSPEAK (Solvent extraction by DIDPA with DTPA)・Solvent extraction (TPEN, TPA, PDA, BTP etc.)・Extraction chromatography (PDA) ・Ion exchange (Tertiary Pyridine Resin-HCl-MeOH)

Extraction chromatography(BTP, HDEHP)An(III)/RE

separation

・TRUEX (Solvent extraction by CMPO)・Solvent extraction by DGA-extractants・Solvent extraction by DIDPA

Extraction chromatography(CMPO, TODGA)

An(III)+REseparation

・Solvent extraction N,N-dialkylamideCo-extraction by TBP

U-Np-Puco-recovery

・Precipitation by pyrrolidone・Solvent extraction by TBP (modified PUREX)・Solvent extraction by N,N-dialkylamide

CrystallizationU selectiveseparation

The other methods & technologiesNEXT Process*

*Fast reactor cycle technology development (FaCT) projectDissolution

U selectiveseparation

U-Np-Puco-recovery

An(III)+REseparation

An(III)/REseparation

Am/Cmseparation

Sr-Csseparation

Sr-Cs FP Am Cm

U, Pu, Np

U

RE

Page 8: Partitioning and Transmutation Studies at JAEArecycle/HP2008 KOBE WS/Session1_Dr.Sasa.pdfWastes from P-T cycle - Difference of waste form - waste volume per 32,000 HMt of 4-year cooled

International Workshop for Asian Nuclear Prospect Page 8

Transmutation by ADS- LBE Target/Cooled Concept -

RF RF RF RF RF RFLiquid He

70keV 2MeV 10MeV 100MeV 1GeVRFQ DTL Superconducting Cavity

Function of ADS•Effective acceleration of high intensity proton by superconducting LINAC•Protons are injected into spallation target through beam duct & window•Pb-Bi acts both spallation target and subcritical core coolant•Fuel mainly composed of MAs•Proton generates many neutrons by spallation reaction with Pb-Bi•MA-loaded subcritical core is driven by spallation neutrons•Fission neutron also transmute MA by trailing fission reactions

•Neutrons are multiplied 20 times by fission chain reaction•Generate electricity from fission reaction to operate own accelerator

Function of ADS•Effective acceleration of high intensity proton by superconducting LINAC•Protons are injected into spallation target through beam duct & window•Pb-Bi acts both spallation target and subcritical core coolant•Fuel mainly composed of MAs•Proton generates many neutrons by spallation reaction with Pb-Bi•MA-loaded subcritical core is driven by spallation neutrons•Fission neutron also transmute MA by trailing fission reactions

•Neutrons are multiplied 20 times by fission chain reaction•Generate electricity from fission reaction to operate own accelerator

Advantages of ADS•Chain reaction immediately stop by aborting accelerator•Wide margin for selection of safety parameter (Doppler coefficient, temperature coefficient etc.) than that of critical reactor•Pb-Bi is chemically stable

Advantages of ADS•Chain reaction immediately stop by aborting accelerator•Wide margin for selection of safety parameter (Doppler coefficient, temperature coefficient etc.) than that of critical reactor•Pb-Bi is chemically stable

Superconducting LINAC

Page 9: Partitioning and Transmutation Studies at JAEArecycle/HP2008 KOBE WS/Session1_Dr.Sasa.pdfWastes from P-T cycle - Difference of waste form - waste volume per 32,000 HMt of 4-year cooled

International Workshop for Asian Nuclear Prospect Page 9

Transmutation by ADS- Liquid Fuelled Concept -

Molten-salt fuel to avoid fuel incompatibility and heat release limitation of Am/CmDesigned as modular target and core unit with small cyclotronPossible to return converted Pu to power reactor cycle for effective fuel usage- Lower influence of heat/neutron release than those of homogeneous MA recycling- Complicated reprocessing process to isolate Pu than dedicated MA transmutation with dry

reprocessing is required Liquid Fuel

Liqu

id F

uel W

ater

Wat

er Target Radius/Height [cm] 12.0/60.0

Target Material/Coolant W / Water

Fuel Zone Radius/Height [cm] 18-38/~120

Fuel Density [g/cm3] 3.80

MA Fraction (Am:Cm) 88:12

Fuel Fraction(MACl3:NaCl) 30:70

Proton Energy [MeV] 600

Proton Beam Power [MW] 5

Reactor Power [MWth] 320

Initial k-effective ~0.98

Page 10: Partitioning and Transmutation Studies at JAEArecycle/HP2008 KOBE WS/Session1_Dr.Sasa.pdfWastes from P-T cycle - Difference of waste form - waste volume per 32,000 HMt of 4-year cooled

International Workshop for Asian Nuclear Prospect Page 10

Current Status of J-PARC

Jan. 28, 2008

50 GeV Synchrotron

LINAC

Neutrino

Site for Transmutation Experimental Facility

Material and LifeScience Facility

Hadron Facility

3 GeV Ring

Control Bldg.

Page 11: Partitioning and Transmutation Studies at JAEArecycle/HP2008 KOBE WS/Session1_Dr.Sasa.pdfWastes from P-T cycle - Difference of waste form - waste volume per 32,000 HMt of 4-year cooled

International Workshop for Asian Nuclear Prospect Page 11

Transmutation Experimental Facility

ADS Target Test Facility (TEF-T)Constructed in 2nd phase with Super-Conducting LINACPrepare material irradiation database to design future ADSMain Device: 600MeV-200kW Pb-Bi Target Unit

Critical Assembly

Pb-Bi Target200kW

10W

Proton Beam

Transmutation Physics Experimental Facility (TEF-P)Constructed at 1st Phase with 30kW Beam DumpStudy critical/subcritical core neutronics using MA-bearing fuelMain Device: Critical Assembly, Remote Systems for MA fuelPower: 500Wby fission with 600MeV-10W proton beam

Page 12: Partitioning and Transmutation Studies at JAEArecycle/HP2008 KOBE WS/Session1_Dr.Sasa.pdfWastes from P-T cycle - Difference of waste form - waste volume per 32,000 HMt of 4-year cooled

International Workshop for Asian Nuclear Prospect Page 12

Critical Assembly in TEF-P

Designed referring FCA facility located at JAEA Tokai-site- Effective use of existing fuels and experimental experiences (data, knowledge, equipment, …)

Simulate both Na-cooled core (FBR) and Pb-Bi cooled core (ADS)1012n/s of neutron source strength is available by 600MeV-10W (25Hz) proton beamBy replacing central 5 x 5 matrix tubes with pin-type assembly, MA fuel can be used with extra cooling circuits and remote handling.

Proton beam

Fixed half assembly

Movable half assembly

Fuel loading machineMovable shield

Core

Safety/control rod drive mechanism

5.5cm

Coolant simulator (Pb, Na, etc.)Stainless steel matrix

Plate-type fuel

Fuel drawer

Pin-type fuel

5.5cm

Proton beam

Beam duct

Spallation target

Page 13: Partitioning and Transmutation Studies at JAEArecycle/HP2008 KOBE WS/Session1_Dr.Sasa.pdfWastes from P-T cycle - Difference of waste form - waste volume per 32,000 HMt of 4-year cooled

International Workshop for Asian Nuclear Prospect Page 13

Preliminary Letter of Intent for TEF

Overseas- EUROTRANS- PSI(Swiss)

- CIAE(China)

- Seoul Univ.(Korea)

- MINT(Malaysia)

- NTI(Serbia)

Univ.:30

JAEA, KEK:26

Company:1

Abroads:56

Researchers113

(Except EUROTRANS)

Universities- Hokkaido Univ.- Tokyo Tech.- Nagoya Univ.- Kyoto Univ.- Kyushu Univ.

JAEA- Quantum Beam Sci. Dir.- Nucl. Sci. and Eng. Dir.- Advanced Nucl. System R&D Dir.- J-PARC Center

Company- Engineering Development inc.

Research Field and Items of Proposals (Total: 38 at 2008.10)1. ADS (Accelerator coupling,Multi-region core,Subcriticality measurements, etc.) 112. Innovative Reactors (MA Neutronics,Heavy Metal Reactor,FP Transmutation) 103. Nuclear Data Measurements (TOF Threshold Reaction) 64. Shielding, Safety 55. Particle Physics (Ultra Cold Neutron, Neutrino) 36. Pb-Bi Target Development (Irradiation) 27. Medical Application (Boron Neutron Capture Therapy) 1

Research Field and Items of Proposals (Total: 38 at 2008.10)1. ADS (Accelerator coupling,Multi-region core,Subcriticality measurements, etc.) 112. Innovative Reactors (MA Neutronics,Heavy Metal Reactor,FP Transmutation) 103. Nuclear Data Measurements (TOF Threshold Reaction) 64. Shielding, Safety 55. Particle Physics (Ultra Cold Neutron, Neutrino) 36. Pb-Bi Target Development (Irradiation) 27. Medical Application (Boron Neutron Capture Therapy) 1

- Tohoku Univ.- Niigata Univ.- Osaka Univ.- Kinki Univ.

Page 14: Partitioning and Transmutation Studies at JAEArecycle/HP2008 KOBE WS/Session1_Dr.Sasa.pdfWastes from P-T cycle - Difference of waste form - waste volume per 32,000 HMt of 4-year cooled

International Workshop for Asian Nuclear Prospect Page 14

Asia ADS Network Initiative

Started from 2003 and held meetings annually

Exchange R&D information for national programs, accelerator, neutronics, nuclear data, material issues

From 2007, topics extended to innovative systems including HLM system

2nd : Daejeon

3rd : Beijing

4th : Osaka

5th : Seoul1st :Tokyo

6th : Xian

Next MeetingXian, China

Dec. 3 - 5, 2008

Page 15: Partitioning and Transmutation Studies at JAEArecycle/HP2008 KOBE WS/Session1_Dr.Sasa.pdfWastes from P-T cycle - Difference of waste form - waste volume per 32,000 HMt of 4-year cooled

International Workshop for Asian Nuclear Prospect Page 15

Summary

Impact of P-T technology introductionWaste and waste repository can be reduced by P-T Technology

Prolong lifetime of waste repository 5 to 8 times or more

Partitioning and Transmutation system studies at JAEA

Various partitioning methods for U, Np/Pu, Am, Cm, Sr, Cs, etc. are studied

Design of dedicated ADS optimized for minor actinide transmutation is underway

R&D needs and experimental equipments to satisfy the requirements are discussed under research committee organized by Atomic Energy Society of Japan

Progress of last 8 years is reviewed by Atomic Energy Commission of Japan

International collaboration in Asian region

Asia ADS Network Initiative was established since 2003

Keep contact with extended research fields

Page 16: Partitioning and Transmutation Studies at JAEArecycle/HP2008 KOBE WS/Session1_Dr.Sasa.pdfWastes from P-T cycle - Difference of waste form - waste volume per 32,000 HMt of 4-year cooled

International Workshop for Asian Nuclear Prospect Page 16

Effect of Partitioning-Transmutation- Reduction of Radiotoxicity -

Long-term radiotoxicity can be reduced by two orders, if 99.5% of transmutation efficiency is achieved

The time period to reduce the radio-toxicity below the level of natural uranium used as raw material:- 50000 years by current national scenario

- 500 years by the case with P-T