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Interaction of Eu-isotopes with saponite as a component of the engineered barrier

Abstract

Bentonite is accepted as the best clay material in the engineered barrier of deep geological repositories (DGRs) for radioactive waste disposal. In recent years, the interactions between a wide range of rare-earth (REE) cations and smectites have been studied. A combined study of stable europium and radioactive isotopes is reported here. Saponite was subjected to hydrothermal reactions with stable and radioactive (152Eu) europium ions under subcritical conditions. The structural changes of saponite were evaluated by XRD and SEM. The effect of temperature and reaction time on the changes was quantified by measuring 152Eu through gamma spectrometry. The reaction between europium and saponite was a first-order reaction. The presence of Eu in the precipitate in an amount much higher than the cation exchange capacity of saponite confirmed participation of chemical reactions or surface adsorption in the europium immobilization, even at temperatures as low as 150°C. The reaction rate constant indicated that an 8- to 9-month period was needed for the completion, without significant changes, of the europium/saponite chemical reaction under the subcritical conditions of 200°C and 350°C.

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Interaction of Eu-isotopes with saponite as a component of the engineered barrier

Author: Alba Carranza, María Dolores; Castro Arroyo, Miguel Ángel; Chaín, P.; Hurtado, Santiago; Orta Cuevas, María del Mar; Pazos, Mariana Carolina; Villa Alfageme, María
Publisher: Elsevier
Year: 2011
DOI: 10.1016/j.clay.2011.02.027
Source: https://idus.us.es/bitstreams/e60c5c24-9354-411f-baf9-5b4518eaf7de/download
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In e ac ion o Eu-iso opes wi h saponi e as a componen o he enginee ed ba ie
Ma ía D. Alba (a), Miguel A. Cas o (a), P. Chaín (a), San iago Hu ado (b), M. Ma O a (a),
M. Ca olina Pazos (a), Ma ía Villa (b)
a Ins i u o Ciencia de los Ma e iales de Se illa, CSIC-US, A da. Ame ico Vespucio, 49, 41092
Se illa, Spain
b Cen o de In es igación, Tecnología e Inno ación de la Uni e sidad de Se illa, CITIUS, A da.
Reina Me cedes, 4, 41012 Se illa, Spain
Abs ac
Ben oni e is accep ed as he bes clay ma e ial in he enginee ed ba ie o deep geological
eposi o ies (DGRs) o adioac i e was e disposal. In ecen yea s, he in e ac ions be ween a
wide ange o a e-ea h (REE) ca ions and smec i es ha e been s udied. A combined s udy o
s able eu opium and adioac i e iso opes is epo ed he e. Saponi e was subjec ed o
hyd o he mal eac ions wi h s able and adioac i e (152Eu) eu opium ions unde subc i ical
condi ions. The s uc u al changes o saponi e we e e alua ed by XRD and SEM. The e ec o
empe a u e and eac ion ime on he changes was quan i ied by measu ing 152Eu h ough
gamma spec ome y. The eac ion be ween eu opium and saponi e was a i s -o de eac ion.
The p esence o Eu in he p ecipi a e in an amoun much highe han he ca ion exchange
capaci y o saponi e con i med pa icipa ion o chemical eac ions o su ace adso p ion in he
eu opium immobiliza ion, e en a empe a u es as low as 150 °C. The eac ion a e cons an
indica ed ha an 8- o 9-mon h pe iod was needed o he comple ion, wi hou signi ican
changes, o he eu opium/saponi e chemical eac ion unde he subc i ical condi ions o 200
°C and 350 °C.
Keywo ds
Enginee ing ba ie ; Radionuclide; Ben oni e
1. In oduc ion
The managemen o adioac i e was e con aining ac inides is cu en ly a key en i onmen al
p oblem due o he need o i s long- e m, sa e and e icien s o age. The deep geological
eposi o y (DGR) concep in ol es he placemen o long-li ing high-ac i i y adioac i e was e
(HARW) in ooms exca a ed deep wi hin a s able, low-pe meabili y bed ock. In many
coun ies, he DGRs a e based on a passi e mul i-ba ie sys em app oach ha combines
was e packages, enginee ed seals, and bed ock whe eby he majo esponsibili y o sa e y
alls on he enginee ed ba ie sys em (EBS). Nowadays, ben oni e is accep ed as he bes clay
ma e ial o he enginee ed ba ie o DGRs (Bailey, 1980). In almos all eposi o ies o his
ype i is assumed ha he geosphe e su ounding he EBS is sa u a ed wi h wa e since
2
g oundwa e g adually seeps back in o he unnel and could be in con ac wi h he EBS. Unde
sa u a ion condi ions, ben oni e, due o i s high con en o smec i e, swells and seals he
unnel, es ic ing almos all low o wa e inside he EBS (Bailey, 1980).
The in e ac ion o 4 elemen s, such as La, Lu, Nd and Sm, wi h na u al and syn he ic clay
mine als du ing he mal and hyd o he mal eac ions was s udied in a sys ema ic and
undamen al way (Alba and Chain, 2005, Alba and Chain, 2007, Alba e al., 2009a and Alba e
al., 2009b). A ne e s udied eac ion mechanism, based on he in e ac ion be ween he
lan hanide ca ions and he clay mine al, was iden i ied (T illo e al., 1994). Unde subc i ical
empe a u e and p essu e condi ions (374.3 °C, 218 a m), an in e ac ion be ween smec i es
and a e-ea h elemen s (REE) was ound o exis (Chapman and Smellie, 1986) and an
insoluble disilica e, REE2Si2O7, was gene a ed (Bece o e al., 2003). The eac ion ex ends o
he whole se o smec i es, al hough hei eac i i y di e s, wi h saponi e as he mos eac i e
(Alba e al., 2001). These esul s implied an e icien mechanism o he enginee ed ba ie
(ben oni e ba ie ) o highly ac i e adioac i e was e (HARW) managemen when he
p ope ies o ben oni es (ca ion exchange and swelling capaci y), ha a e esponsible o he
physical e en ion, ail his e en ion.
These sys ema ic s udies we e pe o med by using lan hanide ions as he HARW chemical
analogous. I u anium (95% o he spen uel) we e dis ega ded, an a e age composi ion o he
spen - uel pelle s o e e ence would be app ox. 18 mass% o plu onium and 2 mass% o
equally dis ibu ed nep unium and ame icium, wi h he emaining ac inides as mino elemen s
(As udillo, 2001). The e o e, he easibili y o he chemical-in e ac ion immobiliza ion
mechanism o he main HARW p esen in he nuclea was e emains o be es ed.
Thus, in o de o unde s and he abo e-men ioned hyd o he mal eac ion, a combined s udy
was pe o med: On one hand, he s uc u al changes o saponi e by he s able iso opes should
be conside ed. On he o he hand, oge he wi h a s able iso ope, a adioiso ope can be added
in ul a- ace concen a ions, which makes i possible o quan i a i ely de e mine he
dis ibu ion o he REE ca ions be ween he solid and he liquid pa s o he eac ion.
Many s udies in he li e a u e a e dedica ed o he adso p ion o he s able eu opium ions by
clay mine als. The ca ion exchange p ocess is he main adso p ion mechanism a 25 °C–150 °C
and a a mosphe ic p essu e (Sánchez e al., 2006 and Te e e al., 2006). The s udy o he
beha io o adioiso opes in a ious ma ices is widesp ead, o example adso p ion and
deso p ion p ope ies in con amina ed soils ha e been s udied in Liu e al. (2003) and in
Spalding (2001), while soil- o-plan ans e p ope ies ha e been in es iga ed by Rigol e al.
(2008). S udies o he adso p ion o adioiso opes on clay mine als include hose by De i ie e
al. (2004) o 125I, Vejsada e al. (2005) o 134Cs, and Rabung e al. (2005) o ace
concen a ions o cu ium. The beha io o eu opium ions in clay mine als has been widely
s udied, o example, adso p ion s udies ha e been ca ied ou by Rabung e al. (2005), and in
Fan e al. (2009), whe eas Rahman e al. (2007) ocused on leaching s udies.
Depending on he empe a u e, REE2Si2O7 is o med, unde hyd o he mal condi ions a 300
°C, om a wide se o REE3+ ca ions, such as Sc3+, Y3+, La3+, Nd3+, Sm3+ and Lu3+, (Alba e
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al., 2009a). In o de o e alua e he applicabili y o he long immobiliza ion p ocess in eal
eposi o ies, i is necessa y o explo e he easibili y o he eac ion below 200 °C. The s udy o
s uc u al changes below his empe a u e, howe e , is no always achie able (Allen and
Wood, 1988, Ma he e al., 1982 and Sa age and Chapman, 1982), and he e o e highe
empe a u es a e aken as app op ia e condi ions o he simula ion o deep geological
disposal condi ions and o an inc ease o he eac ion a es.
The use o s able iso opes enables an analysis o be ca ied ou o he s uc u al changes o he
ben oni e a e he hyd o he mal eac ion wi h REE. The use o adioac i e iso opes enables o
ob ain u he da a: a) he immobiliza ion capaci y can be quan i a i ely de e mined; b) he
kine ics o he p ocess can be analyzed; c) he p oposed eac ion mechanism can be es ed in a
wide ange o empe a u es, e en when he ex en o he eac ion is insu icien o enable
de ec ion o s uc u al changes; and d) an app op ia e me hodology can be es ablished o
ex end he s udy o ins able adionuclides.
Eu3+ seems o be he mos sui able REE ca ion o his s udy since i s physical p ope ies
(ca ion size, hyd oliza ion cons an , and oxida ion s a e) a e compa able wi h hose o Am3+
and Cm3+ (B adbu y e al., 2005 and Fan e al., 2009). I is a ailable as s able iso opes, 151Eu,
153Eu, and he adioac i e iso ope, 152Eu (T1/2 = 13.5 yea s). The e o e, in his expe imen al
s udy we add ess he a e and mechanism o Eu3+ ion as a model sys em, unde condi ions
simila o hose p edic ed o he nuclea was e s o age assessmen . In geochemical p ocesses
o was e deg ada ion and was e/ ock in e ac ion, he expec ed empe a u es each up o
app ox. 200 °C (Sa age and Chapman, 1982). Howe e , many s udies de o ed o simula ing
deep geological disposal condi ions used empe a u es o up o 350 °C o inc ease he eac ion
a es, (Allen and Wood, 1988, Ma he e al., 1982 and Sa age and Chapman, 1982).
2. Expe imen al
2.1. Saponi e
Saponi e was ob ained om he Sou ce Clay Mine als Reposi o y Uni e si y o Missou i
(Columbia) and had he ollowing chemical o mula: Na0.61K0.02Ca0.09 (Si7.2Al0.8)IV(Mg5.79
Fe2+0.15)VIO20(OH)4 (Alba e al., 2001). The in e laye ca ion concen a ion and he wa e
con en we e es ima ed o be 103.0 meq/100 g and 9.2 mass% (Chain, 2007).
2.2. Eu3+ solu ion
Two se s o s a ing solu ions o 7.9 · 10− 2 M Eu(NO3)3 (151Eu and 153Eu, wi h 52.2% 153Eu)
we e p epa ed: i) The i s solu ion con ained pu ely s able Eu iso opes and ii) he second
solu ion was en iched wi h he adioiso ope 152Eu. A olume o 1 ml om a dilu ed s anda d
solu ion (9.8 Bq/ml) up o a o al ac i i y o 9.8 Bq was added o 35 ml o he o me solu ion,
i.e. a comp omise be ween low adioac i i y concen a ions o sa e handling and high
coun ing a es o ge as measu emen s. Due o i s sho hal -li e (13.5 yea s) 10− 14 mol o
152Eu we e added.
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The pH o bo h solu ions was adjus ed o pH = 6.0–6.5, by slowly adding 0.05 M ammonia
solu ion unde s i ing.
2.3. Hyd o he mal eac ions
300 mg o he powde ed samples we e dispe sed in 40 ml o he Eu3+ solu ions and we e
hea ed in a s ainless s eel eac o , (Pe digón, 2002), a he empe a u es and imes
summa ized in Table 1. The cells ma ked wi h e ical line co espond o he ea men wi h a
s a ing solu ion o 7.9 · 10− 2 M Eu(NO3)3, he g ay colo cells wi h a s a ing solu ion o 7.9 ·
10− 2 M Eu(NO3)3 en iched wi h he 152Eu iso ope. The eac ion p oduc s we e collec ed by
il e ing, washed wi h dis illed wa e , and d ied in ai a 60 °C. The eac ion solu ion and he
washing liquid we e kep o he quan i a i e analysis o eu opium by gamma spec oscopy.
Fo he e alua ion o possible a i ac s such as adso p ion on o he wall o he eac o , he
eac o essel wi h 40 ml o Eu(NO3)3 7.9 · 10− 2 M was hea ed a 350 °C o 4.5 days. The
152Eu con en o he emnan solu ion showed ha he Eu adso p ion on o he con aine was
negligible unde hese eac ion condi ions.
2.4. Cha ac e iza ion me hods
X- ay powde di ac ion (XRD) pa e ns we e ob ained wi h a B uke D8I ins umen , a he
CITIUS, Uni e si y o Se ille (Spain) (a Ni- il e ed Cu Kα adia ion, 40 kV, 40 mA, scan s eps o
0.05° 2θ, wi h a coun ing ime o 3 s). The c ys alline phases we e iden i ied by using he
compu e p og am X'Pe HighSco e (Philips Analy ical B.V. Almelo, The Ne he lands).
Scanning elec on mic oscopy (SEM) was used o obse e he ma e ials o which no
app eciable c ys alline phases we e obse ed by XRD. The mo phology and chemical
composi ions o he samples we e analyzed, a he Mic oscopy Se ice o CITIUS, Uni e si y o
Se ille (Spain), in a scanning elec on mic oscope (JEOL 6460LV) equipped wi h EDX.
The adioac i e eu opium, 152Eu, was measu ed wi h an HPGe coaxial gamma de ec o , a he
CITIUS, Uni e si y o Se ille (Spain). To calib a e he coun ing e iciency, 152Eu- ee, solid
samples ob ained a e he hyd o he mal eac ion we e spiked wi h a known amoun o
152Eu. The ac i i y concen a ion o 152Eu was measu ed in he liquid and solid phases.
3. Resul s and discussion
3.1. S uc u al s udies
The XRD pa e ns o he saponi e and hose a e eac ion wi h 7.9 · 10− 2 M Eu(NO3)3 a 350
°C, 200 °C and 150 °C, a e displayed in Fig. 1. The pa e n o he o iginal saponi e (Fig. 1a)
showed he gene al and basal e lec ions. The hk bands we e composed o asymme ical
e lec ions wi h he cha ac e is ic “saw- oo h” shape o he wo-dimensional e lec ions
(Wa en, 1941). The basal e lec ions we e symme ical. The 12.30 Å d001 alue o un eac ed
saponi e co esponded o he monolaye hyd a e o Na-saponi e ( Alba e al., 2001, G im,
1968, Ra ina and Low, 1977 and Wa en, 1941).
A e he hyd o he mal eac ion a 150 °C o 47 days, (Fig. 1b) he basal spacing o saponi e
was inc eased o 14.30 Å, in ag eemen wi h da a epo ed o smec i es sa u a ed wi h
5
mul i alen ca ions (Ra ina and Low, 1977). Also, he posi ion o he 060 e lec ion, in he
ange o he ioc ahed al smec i es (G im, 1968), was sligh ly shi ed o d060 = 1.526 Å.
Addi ionally, small e lec ions in he 25–30° 2θ ange we e obse ed and co esponded o F-
Eu2Si2O7 (PDF 87–2475, ma ked wi h F) and Eu(OH)3 (PDF 83–2305, ma ked wi h h). The XRD
pa e n was noisy and showed a p ominen backg ound which indica ed he pa ial dis up ion
o he saponi e amewo k.
The hyd o he mal eac ion a 350 °C yielded simila XRD pa e ns (Fig. 1c and d) which we e
domina ed by e lec ions o F-Eu2Si2O7 (PDF 87–2475, ma ked wi h F), c ys alline Eu(OH)3
(PDF 83–2305, ma ked wi h h), Eu2O3 (PDF 34–392, ma ked wi h o) and EuONO3 (PDF 31–518,
ma ked wi h n). These phases coexis ed wi h he emnan clay mine al o a new mixed-laye ed
clay mine al which was cha ac e ized by a se o basal e lec ions wi h d002 = 14.6 Å and he
absence o he hk e lec ions. The only e ec o he eac ion ime was he be e c ys alliza ion
o he new phases (Fig. 1c and d). Thus, empe a u e played a g ea e ole han ime in he
o ma ion o he disilica e, as is expec ed due o he laws o he modynamics and kine ics.
The elec on mic og aphs and he EDX analysis o he saponi e eac ed wi h Eu3+ a 150 °C o
47 days (Fig. 2) showed lamella mo phology o he majo i y o he pa icles (Fig. 2a) wi h
some small b illian pa icles on hei su aces. The EDX spec um o his saponi e (Fig. 2c) was
cha ac e ized by he absence o Na+, low con en o Mg2+, and a ela i ely high amoun o
Eu3+ when compa ed o he o iginal saponi e (Fig. 2b). When saponi e was eac ed a 350 °C,
mos o he pa icles again showed he lamella mo phology (Fig. 3a and b). The EDX spec a
(Fig. 3d) we e cha ac e ized by he Kα1 lines o Si, Al and Mg and Mα, and Lα and Lβ lines o
Eu. The dec ease o he Mg con en and he absence o Na, in compa ison wi h he o iginal
saponi e (Fig. 3c), we e due o he leaching o Mg ions om he s uc u e and he exchange o
Na+ by Eu3+ in he in e laye space. This is in line wi h he XRD pa e ns ha showed a
mode a ely deg aded s a e o he laye s and an inc eased basal spacing (Fig. 1c and d). The
al e ed saponi e seemed o o m agg ega es and showed an inc easingly blocky mo phology
wi h inc easing eac ion ime. In addi ion o he lamella pa icles, some compac pa icles
wi h b illian appea ance unde he backsca e ing elec on beam we e also obse ed wi h a
chemical composi ion (Fig. 3d) compa ible wi h he eu opium c ys alline phases al eady
obse ed by XRD, e.g. Eu2Si2O7, Eu(OH)3, Eu2O3 o EuONO3. These b illian pa icles we e
mo e abundan a he longe eac ion imes (Fig. 3b).
Thus, in he ini ial s ep o he eac ion a 150 °C, he Na+ ions o he saponi e we e exchanged
by Eu3+. As he eac ion p og essed up o 350 °C, he saponi e s uc u e was decomposed
o ming c ys alline F-Eu2Si2O7. O he mino eu opium phases we e also obse ed a 150 °C
and 350 °C.
3.2. The ex en o he eac ion
The pa ame e s used o he quan i a i e e alua ion o he ex en o he eu opium and silica e
eac ion as a unc ion o ime and empe a u e a e summa ized in Table 2. The amoun o
eu opium bound by saponi e was calcula ed om he measu ed adioac i i y in he liquid
(non- eac ed) and he solid ( eac ed) phases a e he hyd o he mal eac ion. The con en o
silicon in ol ed in he chemical immobiliza ion mechanism indica ed he p og ess o Eu2Si2O7
o ma ion.

6
E en a he lowes empe a u e and eac ion ime, he amoun o bound eu opium ions was
mo e han h ee imes he ca ion exchange capaci y o saponi e (103.0 meq/100 g). This
clea ly indica ed ha in addi ion o he ion exchange, eu opium phases we e o med.
The amoun o bound eu opium ions a e he eac ion o 20 days changed almos linea ly
wi h he empe a u e (Fig. 4): 390 ± 20 meq/100 g a 150 °C, o 990 ± 40 meq/100 g a 200 °C,
and o 1170 ± 30 meq/100 g a 350 °C, whe e 390 and 990 a e he a e age alues ob ained
om wo measu emen s. The dependence on he eac ion ime could no be clea ly seen a
150 °C, since, a ha empe a u e, he eac ion imes we e oo sho .
The esul s we e i ed o an exponen ial unc ion whe e he exponen co esponded o he
eac ion a e cons an , k. I0 was in ag eemen wi h he a e age 152Eu eco e ed in he liquid
and in he solid. The i ing indica ed ha he eac ion be ween eu opium and saponi e was a
i s -o de eac ion.
Fo 350 °C and 200 °C, he bes i was exponen ial bu wi h a a e cons an ha sligh ly
dec eased be ween 350 °C and 200 °C (1.33 · 10− 2 s 1.19 · 10− 2). The eac ion was almos
h ee imes as e a 350 °C han a 200 °C. Using he calcula ed eac ion a es, i can be
in e ed ha he chemical immobiliza ion o Eu ion would be comple ed a e 8–9 mon hs o
eac ion unde subc i ical condi ions a 350 °C and a 200 °C. Since he eac ion imes a 150 °C
we e no long enough, i ing could no be ca ied ou a his empe a u e.
4. Conclusions
The amoun o Eu in he eac ed saponi e in much highe amoun s han co esponding o he
ca ion exchange capaci y o saponi e was he esul o he ca ion exchange and he
neo o ma ion o he eu opium phases, e en a empe a u es as low as 150 °C. The kine ic
pa ame e s o eu opium immobiliza ion we e e alua ed. Mo eo e , hese esul s may be used
o p edic he beha io o HARW ca ions (Am, Cm, Th, U, and Pu) wi hin he ben oni e ba ie s
when s uc u al analysis is un easible.
Acknowledgmen s
We g a e ully acknowledge inancial suppo om Minis e io del Medio Ambien e y Medio
Ru al y Ma ino p ojec no. 300/PC08/3-01.1 and DGICYT p ojec no. CTQ2010-14874. Finally,
we hank ENRESA o i s inancial suppo .
7
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Figu e 4