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Chemical Durability of Vitreous Wasteforms ICTP ICTP ICTP ICTP- - -IAEA joint workshop on vitrification IAEA joint workshop on vitrification IAEA joint workshop on vitrification IAEA joint workshop on vitrification Stéphane GIN, CEA, Marcoule site, France Waste Treatment Department [email protected] November 8th, 2017 — Trieste, Italy

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Page 1: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

Chemical Durabilityof Vitreous Wasteforms

ICTPICTPICTPICTP----IAEA joint workshop on vitrificationIAEA joint workshop on vitrificationIAEA joint workshop on vitrificationIAEA joint workshop on vitrification

Stéphane GIN, CEA, Marcoule site, FranceWaste Treatment [email protected]

November 8th, 2017 — Trieste, Italy

Page 2: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

Glass durability?

Glass / NF materials interactions

Reactive surface area

Alteration rate

| PAGE 2

Disposal Concept Design

THMCRBoundary Conditions

Mechanistic Studies Parametric Studies

Mechanistic Modeling

Couplings Study

Lon

g-te

rm B

eha

vior

Sci

enc

e

Key Phenomena Ranking

Operational Model Design

Validation of mechanistic and Operational Models

Performance AssessmentSource Term Calculation

RN Migration Assessment

RN Impact on BiosphereAssessment

Acceptance Criteria

Glo

bal S

afe

ty A

sses

smen

t

ASTM Standard C1174-07Poinssot et al., JNM 2012

Page 3: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

Outline

1. Basic mechanisms of glass corrosion

2. Kinetic regimes

3. Ongoing studies to better understand how gel layer form and

passivate the glass surface

4. Remaining challenges

| PAGE 3

Page 4: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

Can thermodynamic equilibrium between glass surface and solution be achieved?

| PAGE 4

No, for thermodynamic & kinetic reasons

→ Keq (glass) >> Keq (crystal) due to structural disorder

→ Secondary phases with low solubility AND fast precipitation kinetics control the solution chemistry

Grambow, J. Nucl. Mater. 2001Frugier, J. Nucl. Mater. 2008Gin, Nature Com. 2015Glass → Hydrated Glass → Gels → Crystalline Phases

Ostwald rule of stages

Page 5: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

What are the key parameters to be considered?

| PAGE 5

Intrinsic Parameters

→ Glass composition

→ Glass structure (cooling rate, homogeneity)

→ Reactive surface area, surface roughness and residual stress

→ Self irradiation (in case of nuclear glasses)

Extrinsic Parameters

→ Temperature

→ Unsaturated (relative humidity) vs water saturated medium

→ pH, water composition (itself modified by the surrounding solids)

→ Flow rate

→ (Pressure, Eh, microbial activity)

Page 6: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

Basic mechanisms

| PAGE 6

• Hydration / Interdiffusion

• Hydrolysis of glass formers

• Condensation of some hydrolyzed species (Si, Al, Ca…)

• Precipitation of secondary phases

Page 7: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

KINETIC REGIMES

Massive precipitation of silicate mineralsGel formation

& affinity effect

Am

ount

of a

ltere

d gl

ass

TimeInterdiffusion

Initial rate r 0

Hydrolysis

Water diffusion &Secondary phases precipitation

I II IIIStagesR

ate

Ion exchange

Page 8: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

Pristine

glass

Hydrated

glassMacroporousalteration layer Crystalline

phases

2 µm

No free water in pores of 1 nm: e.g. Bourg, J. Phys. Chem. C 2012

Nanoporous material

Bulksolution

Reactioninterface

| PAGE 8

Page 9: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

A few orders of magnitude

Massive precipitation of silicate mineralsGel formation

& affinity effect

Am

ount

of a

ltere

d gl

ass

TimeInterdiffusion

Initial rate r 0

Hydrolysis

Water diffusion &Secondary phases precipitation

I II IIIStagesR

ate

r0 depends on glass composition, T, pH and to a lesser extent to the solution composition (Jollivet Chem. Geol. 2012)

PA relying on r0 ends up withglass lifetime of a few 103

years…

| PAGE 9

Some key figures @ 90°C for R7T7 type glass• Stage I : r0 ~ 0.5 µ.d-1 Dw in pristine glass ∼ 10-20 m2.s-1

• Stage II : r0 ~ 10-4 µ.d-1 Dw in stage II ∼ 10-23 m2.s-1

� What is behind these low apparent D?�What is the effect of glass composition?� How secondary phases disrupt passivating layers?

Page 10: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

Relation between short-term & residual rate

• Measuring initial rates does not help understand what could happen at long term

• Same conclusion for PCT 7d

R² = 0.0075

R² = 0.0429

1.E-06

1.E-05

1.E-04

1.E-03

1.E-02

0 2 4 6 8 10 12

Re

sid

ua

l ra

te 5

0°C

(g

.m-2

.d-1

)

Initial rate 100°C (g.m-2.d-1)

R7T7

AVM

Massive precipitation of silicate mineralsGel formation

& affinity effect

Am

ount

of a

ltere

d gl

ass

TimeInterdiffusion

Initial rate r 0

Hydrolysis

Water diffusion &Secondary phases precipitation

I II IIIStages

Rat

e

| PAGE 10

Page 11: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

Modeling glass alteration in an open and reactive environment

| PAGE 11

GRAAL has been developed to predict the rate of glass dissolution as a function of environmental conditions. GRAAL relies on the properties of a passivating layer called PRIEquations are implemented either in a reactive transport code (HYTEC)

Frugier et al. J. Nucl. Mater. (2008) 380; Minet et al., J. Nucl. Mater (2010) 404; Debure et al., J. Nucl. Mater. (2013) 443

Recent applications : evaluate the effect of COx ground water, the effect of flow rate, the effect of Mg bearing minerals, simulate the resumption of alteration

Under development: complete parameterization between RT and 90°C, 2 PRIs, construction of a simplified tool to assess the effect of corrosion products on glass durability

E(t) : Thickness of the dissolved PRIe(t) : Thickness of the PRI

−=

PRI

PRIdisso K

Qr

dt

dE1

dt

dE

D

re

r

dt

de

PRI

hydr

hydr −⋅+

=1

→→→→ Empirical parameter

→→→→ Macroscopic parameter

Page 12: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

Pre-sat solution makes the RD stage much shorter (Si affects the rate of Si-O-Si hydrolysis) but does not impact the RR regime.

Processes causing the drop of the rate1 : Effect of Si (affinity effect)

Grambow, MRS proc. 1985Mc Grail, J. Non-Cryst. Sol. 2001Neeway, J. Nucl. Mater. 2011Gin, Int. J. Appl. Glass Sci. 2013Icenhower, J.Nucl.Mater. 2013

| PAGE 12

Static tests, S/V 8,000 m-1, 90°C, 3yPre-saturated solution vs DIW

Page 13: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

8%

4%

3%

2%

1%

0%

6 hours

ZrO2 Forward rate of alterationWater Glass

H2O

Si

BZr

Condensed Si

Zr at.: immobilize increasing numbers of Si

-> prevents any reorganization

-> percolation pathways(leaching sol. - pristine glass surf.)

Porosity clogging: up to 4% of ZrO22.5 microns

Processes causing the drop of the rate2 : Formation of a diffusion barrier

500 nm 100 nm500 nm 100 nma b c500 nm 100 nm500 nm 100 nma b c

Cailleteau, Nature Materials 2008

| PAGE 13

Page 14: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

Why alteration does not stop in stage II?

Page 15: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

A rate never equal to zero: case of nuclear glass and basaltic glass

| PAGE 15

0

20

40

60

80

100

120

140

160

180

200

0 1000 2000 3000 4000 5000 6000 7000 8000

NL(

B)

(1

0-2

g.m

-2)

Time (days)

Nuclear glass (ISG - 6 oxides)

Basaltic glass

Alteration at 90°C, in deionized water, in static mode

rr∼ 80 nm/y

rr∼ 4 nm/y

Page 16: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

Why alteration does not stop in stage II?

Massive precipitation of silicate mineralsGel formation

& affinity effect

Am

ount

of a

ltere

d gl

ass

TimeInterdiffusion

Initial rate r 0

Hydrolysis

Water diffusion &Secondary phases precipitation

I II IIIStages

Rat

e

Hypothesis 1: because precipitation of secondary phases consumes elementsform the passivation layer.Yes for some cases but not necessarily! Most of simple glasses do not formsecondary phases between pH 5 and 10

Hypothesis 2: because IX continues beyond the saturation of the solution w.r.t. SiO2am (Grambow MRS proc. 1985 ; McGrail J. Non Cryst. Sol. 2001)

No, recent results show that Na and B profiles do not match a simple IX process

Gin, J. Non Cryst. Sol. 2012

Hypothesis 3: water accessibility to reactive sites ishampered the the low porous gel formed by in-situ reoganization of the silicate network after the departure of mobile speciesNeed to be confirmed by a better understanding of water speciation and dynamics within the alterationlayers (DOE - EFRC WastePD project) | PAGE 16

Page 17: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

Results @ pH 9 – APT Profiles

| PAGE 17

Gin et al. Geochim. Cosmochim. Acta, 2017

Page 18: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

Why glass dissolution can turn into stage III?

Page 19: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

Why dissolution can turn into stage III?Massive precipitation of

silicate mineralsGel formation & affinity effect

Am

ount

of a

ltere

d gl

ass

TimeInterdiffusion

Initial rate r 0

Hydrolysis

Water diffusion &Secondary phases precipitation

I II IIIStages

Rat

e

(Fournier, PhD thesis, 2015)

(Gin, Geochim. Cosmochim. Acta 2015♣, Ribet, J.Nucl.Mater. 2004, Fournier, J.Nucl.Mater. 2014)

At pH > 10.5, IX is not a active process and both Si and Al are highlysoluble.

A dense, rate limiting, amorphouslayer is supposed to precipitate

Zeolite crystals nucleate and grow, first consuming species available in the bulk solution until the solution isundersaturaed wrt the passivatinglayer

The glass surface is no longer protected, the rate increases by several O.M., controled by the growthrate of zeolites

AG

f

0

2

4

[Si]

(g.L

-1)

0

20

40

60

0 10 20 30 40 50 60 70 80

[Al]

(mg.

L-1 )

time (d)

seeded without seeding

| PAGE 19

Page 20: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

| PAGE 20

-4

-3

-2

-1

0

1

2

2 4 6 8 10 12

log

r(r

in g

·m-2·d

-1)

pH90°C

with seeds

r0

rr

Seeding: a new tool to investigate long-term glass stability

ISG glass, 90°C, seeds: Zeolite P2

(Fournier et al., npj-Materials Degradation, accepted)

Page 21: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

| PAGE 21

Ongoing studies at CEA on fundamentals in glass corrosion

29Si 28Si

Page 22: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

| PAGE 22

Experiments

� International Simple Glass (ISG)

� 3 exp run in controlled conditions – Launching Feb. 2013

� 16 glass coupons (with one face polished) 90°C - 380 mL

of solution initially saturated in 29Si02am (S/V= 0.6 cm-1)

1. pH90°C 7 (Nat. Com., 6, 2015)

2. pH90°C 9 (Geochim Cosmochim. Acta, 202, 2017)

3. pH90°C 9 for 209d then 11.5 (Geochim Cosmochim. Acta, 151, 2015)

� Coupon withdrawal: 7, 209, 363, 875, 1625… days

� Tracing experiments (room T – various probe molecules)

� Isotope sensitive analytical techniques: MC-ICP-MS and

ToF-SIMS, APT + TEM

SiO2 B203 Na20 Al 2O3 Ca0 ZrO2

56.2 17.3 12.2 6.1 5.0 3.3

ISG glass composition (wt%) (29Si/28Si)solution = 40

29Si/28Si = 0.05

Page 23: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

| PAGE 23

o r evolves similarly at 0.6 cm-1 and 500 cm-1

o r drops by 3 O.M. in ∼ 6 monthso r(pH 7) > r(pH 9)o r “immediately” increases when the the pH is

raised @ 11.5

First set of observations

1E-4

1E-3

1E-2

1E-1

1E+0

1E+1

1E-4

1E-3

1E-2

1E-1

1E+0

1E+1

0 100 200 300 400

Ra

te (

g.m

-2. d

-1)

Time (days)

M - pH7

M - pH9

P - pH9

M - pH9 -> 11.5

pH 9 – 209d

pH 7 – 209d

o A uniform, “isovolumetric” gel layer forms at pH 7 and 9 (best conditions for ToF-SIMS depth profiling)

o No secondary phases precipitate at pH 7 and 9

Page 24: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

| PAGE 24

Evidence of the formation of a passivating layer by in situ reorganization of the silicate network

Rate limiting mechanisms strongly depend

leaching conditionsMore discussion in Gin, Chem. Geol 2016

SiO2 B203 Na20 Al 2O3 Ca0 ZrO2

56.2 17.3 12.2 6.1 5.0 3.3

ISG glass composition (wt%)

ISG glass altered

@ 90°C, Si

saturated solution

and pH 7Gin et al. Nature

Comm. (2015)

Page 25: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

Evidence of the formation of a passivating layer by in situ reorganization of the silicate network

ISG glass altered @

90°C, Si saturated

solution and pH 7Gin, Nature Comm. 2015

Page 26: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

| PAGE 26

ISG glass

Alteration kinetics

Altered glass

Structural study of pristineand altered glass

Water speciation

Water dynamics

Experimental study

ICP-AES Experimental study : chemical composition,

ToF-SIMS, NMR

MD simulations in collabooration with J. Du

(NTU)

Experimental studyTGA, NMR, IR

Experimental study: isotopic tracing, ToF-

SIMS

MD simulations of nanoconfined water in

collaboration with I. Bourg (Princeton

University) et J. Du (NTU)

ISG glass altered at pH 7 90°C in SiO 2 saturation conditions

Collin et al., npj-Materials Degradation accepted

Page 27: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

| PAGE 27

Water dynamics in passivating layers

ISG glass coupon altered for 1 year @

90°C, pH 7, Sisat

H218O

ToF-SIMS

Quantitative analysis of 18O/16O profiles with the

passivating layer

In depth characterization of the passivating layer (water content, porosity,

pore size, speciation) • Mass balance• Flux of water reaching

the pristine glass surface

0

0.01

0.02

0.03

0.04

0.05

0.06

0.07

0.08

0.09

0.1

0

0.2

0.4

0.6

0.8

1

1.2

1.4

0 500 1000 1500 2000 2500 3000

18O

/16O

No

rma

lize

d B

/Si

Depth (nm)

24 h

B

18O/16O

Porosity ∼∼∼∼ 30%Pore size ∼∼∼∼ 1 nm

Oskeleton = 0.71, OSiOH = 0.13, OH20 = 0.16

25°C

Page 28: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

| PAGE 28

� Coupon of ISG altered @ 90°C, pH 7, SiO2 satsolution for 363 days

� 1.5 µm thickalteration layer

� Equilibriumwould beachieved in ∼1 s in case of an open highlyconnected pore network

Page 29: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

Conceptual model

18O-enriched

H2O

Pristine ISG

<r>

Large connected pores

Restricted dead-end pores

Diffusion in connected pores

1D diffusion along z with DcConstant source: C0 at z = 0zmax. = Lgel

z = 0

z = Lgel

x

z

Diffusion in dead-end pores

1D diffusion along x with DdConstant source: C0 at x = 0xmax. = <r>

Lgel = gel thickness

<r> = mean distance between connected pores

For 2% of H 20 Dquick ∼∼∼∼10-12 m2.s-1

For 98% of H 20 Dslow ∼∼∼∼ 10-20 – 10-24 m2.s-1

Page 30: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

Can MD explain the peculiar behavior of water molecules?(Φpore 1 nm, CLAYFF, rigid water, collab. with Ian Bourg @ Princeton Univ and Jincheng Du)

Deprotonation of silanols on the surface of a nanop orous silica bloc (potassium as charge compensator) :

| PAGE 30

0.0

0.5

1.0

1.5

2.0

2.5

3.0

3.5

0.0

0.5

1.0

1.5

2.0

2.5

-3 -2 -1 0 1 2 3 4 5 6

Ρ(K

)

Ρ(O

w, H

w)

d (Å)

Ow, Hw and K mean densities inside the porosity

Hw poreOw poreK2 pore

0.0

0.2

0.4

0.6

0.8

1.0

0 15 30 45 60 75

D (

10-9

m2 .

s-1 )

Number of deprotonation

Mean Diffusion coefficient inside the pore

0.0

0.4

0.8

1.2

1.6

-4 -3 -2 -1 0 1 2 3 4 5

D (

10-9

m2 .

s-1 )

d (Å)

Water diffusion coefficient as a function of the distance from the pore surface

Neutre 75°C

Deprotonation 65

Deprotonation 26

Deprotonation 10

24

105

0

Number of potassium inside the porosity

65 26 10 0

102 100 101

93

Number of water molecules inside the porosity

65 26 10 0Number of deprotonation: Number of deprotonation:

Radius

Page 31: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

| PAGE 31

How passivating layer forms (ISG, 90°C, pH 7)?

65% of the bridging O of the gel network have been

hydrolyzed and exchanged between day 3

and 7 and this figures becomes 79% at day 13.

The gel is a dynamicmaterial but in the studied

conditions Si is lowmobile. Water mobility isdramatically affected by

these H/C reactions

Page 32: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

BRIEF SUMMARY

� The initial dissolution rate is controlled by the hydrolysis of the silicate

network. It is the fastest rate for a given glass under given T and pH

conditions

� The rate drops because Ahydrolysis � and a passivating layer forms

� The mechanisms by which passivating layers and non passivating gels

(dissolution/precipitation vs in situ reorganization) form strongly depends on the pH

� The origin of passivation needs to be better understood. It seems that

reorganization of the silicate network following the release of mobile species

is a major process controling the properties of the passivating layer

� Precipitation of Si-phases plays a major role in stage II and III

| PAGE 32

Page 33: Stéphane GIN, CEA, Marcoule site, France Waste Treatment ...indico.ictp.it/event/8002/session/42/contribution/304/material/slides/0.pdfStructural study of pristine and altered glass

ACKNOWLEDGEMENTS

Collaborators:Joe Ryan, John Vienna, Sebastien Kerisit (PNNL)Jincheng Du (North Texas University)Seong H. Kim (Penn State)Ian Bourg (Princeton)Nathalie Wall (WSU)Abdesselam Abdelouas (Subatech)Damien Daval (Univ. Strasbourg)Patrick Jollivet, Maxime Fournier, Pierre Frugier, Frédéric Angeli, Jean-Marc Delaye, Christophe Jégou, Magaly Tribet (CEA)

Students:Marie Collin, Thomas Ducasse, Trilce de Echave, Amreen Jan

Funding support from:CEA, Areva, Andra, DOE EFRC

| PAGE 33