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Shot-clay MX-80 bentonite: An assessment of the hydro-mechanical behaviour A. Ferrari a, , A. Seiphoori a , J. Rüedi b , L. Laloui a,c a Ecole Polytechnique Fédérale de Lausanne (EPFL), School of Architecture, Civil and Environmental Engineering (ENAC), Laboratory for Soil Mechanics (LMS), EPFL-ENAC-LMS, Station 18, CH-1015 Lausanne, Switzerland b NAGRA, Hardstrasse 73, 5430 Wettingen, Switzerland c King Abdulaziz University, Jeddah, Saudi Arabia abstract article info Article history: Received 12 September 2013 Received in revised form 22 January 2014 Accepted 31 January 2014 Available online 12 February 2014 Keywords: Shot-clay MX-80 bentonite Controlled-suction testing Swelling potential Hydro-mechanical behaviour Water retention behaviour This study presents the results of an experimental study conducted to characterise the hydro-mechanical behav- iour of shot-clay MX-80 bentonite. In the shot-clay process, granular bentonite was mixed continuously with water and shot on the walls of a tunnel section at the Grimsel Underground Research Laboratory (URL), in Switzerland. The shot-clay was placed to create a layer of bentonite in direct contact with the host rock to avoid preferential water and/or gas ow along the tunnel wall. Samples for an experimental programme were collected during the shooting. The index properties, microstructural features, swelling potential and water reten- tion properties of the shot-clay were analysed. An experiment was then conducted under controlled total suction to analyse the hydro-mechanical behaviour of the material along a predened stress path involving suction and conning stress variations. Based on the results of this test, the expected behaviour of the shot-clay bentonite when subjected to the environmental conditions in the repository was determined. The test results were compared with data on the observed behaviour of compacted MX-80 granular bentonite to assess the effects of the shot-clay emplacement technique on the behaviour of the MX-80 bentonite. The results highlight the role of the emplacement dry density on the behaviour of bentonite. © 2014 Elsevier B.V. All rights reserved. 1. Introduction Engineered gas transport systems (EGTS) are used to limit gas over- pressures in the backlled underground structures of nuclear waste re- positories to acceptable levels without compromising the radionuclide retention capacity of the engineered barrier system (EBS) (Nagra, 2008). The main design elements of an EGTS are (i) specially designed backll materials for the emplacement caverns, characterised by high porosity and high compressive strength, and (ii) gas-permeable tunnel seals consisting of sand/bentonite (S/B) mixtures with bentonite con- tents of 20% to 30%. The Gas-Permeable Seal Test (GAST) was initiated in 2010 and conducted at the Grimsel Test Site (GTS, Switzerland) in 2011 and 2012. An S/B seal with a length of 8 m and a diameter of 3 m was emplaced to demonstrate the effective functioning of gas-permeable seals at realistic scales and under realistic hydraulic boundary condi- tions (proof of concept). Technological gaps may generate preferential ow paths within the swollen S/B mixture (Wang et al., 2013). To avoid preferential water and/or gas ow along the tunnel wall, a bentonite ring with a target hydraulic conductivity of at least 1E 12 m/s, corresponding to a dry density of the bentonite of approximately 1.4 Mg/m 3 , had to be emplaced around the S/B seal. The rst emplacement option assessed was shot-claying, which involved mixing MX-80 granular bentonite with water (at a volumetric water-to-bentonite ratio of 3 to 11.7), feeding the mixture into a hydraulic pump and shooting the mixture onto the tunnel wall (Fig. 1). A shot-clay test was performed at the Grimsel URL as part of the pre-testing for the nal experiment setup (Teodori et al., 2012). Dixon et al. (2011) presented a comprehensive summary of granular and bentonite pellet installations to ll technological gaps in high-level nuclear waste repositories. This summary highlighted the difculties related to the low angle of repose of dry pellets when poured and pellet damage that occurs when the material is blown in dry conditions. The summary by Dixon et al. (2011) also reported on wet-blowing in- stallations, highlighting the ability of wet-blown bentonite to be placed on near-vertical surfaces and the lack of information on the hydro- mechanical behaviour of the emplaced material. In the experiment discussed in the present study, after the layer of emplacing the bentonite on a tunnel wall, the layer was subjected to several hydro-mechanical processes, some of which resulted from the experimental emplacement and others of which were tested in the lab to assess their potential to optimise the nal dry density of the Engineering Geology 173 (2014) 1018 Corresponding author. Tel.: +41 21 693 23 24; fax: +41 21 693 41 53. E-mail address: alessio.ferrari@ep.ch (A. Ferrari). http://dx.doi.org/10.1016/j.enggeo.2014.01.009 0013-7952/© 2014 Elsevier B.V. All rights reserved. Contents lists available at ScienceDirect Engineering Geology journal homepage: www.elsevier.com/locate/enggeo

Transcript of Shot-clay MX-80 bentonite: An assessment of the hydro ... page files/Publicatio… · Shot-clay...

Page 1: Shot-clay MX-80 bentonite: An assessment of the hydro ... page files/Publicatio… · Shot-clay MX-80 bentonite: An assessment of the hydro-mechanical behaviour A. Ferraria,⁎,A.Seiphooria,J.Rüedib,

Engineering Geology 173 (2014) 10–18

Contents lists available at ScienceDirect

Engineering Geology

j ourna l homepage: www.e lsev ie r .com/ locate /enggeo

Shot-clay MX-80 bentonite: An assessment of thehydro-mechanical behaviour

A. Ferrari a,⁎, A. Seiphoori a, J. Rüedi b, L. Laloui a,c

a Ecole Polytechnique Fédérale de Lausanne (EPFL), School of Architecture, Civil and Environmental Engineering (ENAC), Laboratory for Soil Mechanics (LMS), EPFL-ENAC-LMS, Station 18,CH-1015 Lausanne, Switzerlandb NAGRA, Hardstrasse 73, 5430 Wettingen, Switzerlandc King Abdulaziz University, Jeddah, Saudi Arabia

⁎ Corresponding author. Tel.: +41 21 693 23 24; fax: +E-mail address: [email protected] (A. Ferrari).

http://dx.doi.org/10.1016/j.enggeo.2014.01.0090013-7952/© 2014 Elsevier B.V. All rights reserved.

a b s t r a c t

a r t i c l e i n f o

Article history:Received 12 September 2013Received in revised form 22 January 2014Accepted 31 January 2014Available online 12 February 2014

Keywords:Shot-clayMX-80 bentoniteControlled-suction testingSwelling potentialHydro-mechanical behaviourWater retention behaviour

This study presents the results of an experimental study conducted to characterise the hydro-mechanical behav-iour of shot-clay MX-80 bentonite. In the shot-clay process, granular bentonite was mixed continuously withwater and shot on the walls of a tunnel section at the Grimsel Underground Research Laboratory (URL), inSwitzerland. The shot-clay was placed to create a layer of bentonite in direct contact with the host rock toavoid preferential water and/or gas flow along the tunnel wall. Samples for an experimental programme werecollected during the shooting. The index properties, microstructural features, swelling potential andwater reten-tion properties of the shot-claywere analysed. An experimentwas then conducted under controlled total suctionto analyse the hydro-mechanical behaviour of the material along a predefined stress path involving suction andconfining stress variations. Based on the results of this test, the expected behaviour of the shot-clay bentonitewhen subjected to the environmental conditions in the repository was determined. The test results werecompared with data on the observed behaviour of compacted MX-80 granular bentonite to assess the effectsof the shot-clay emplacement technique on the behaviour of the MX-80 bentonite. The results highlight therole of the emplacement dry density on the behaviour of bentonite.

© 2014 Elsevier B.V. All rights reserved.

1. Introduction

Engineered gas transport systems (EGTS) are used to limit gas over-pressures in the backfilled underground structures of nuclear waste re-positories to acceptable levels without compromising the radionuclideretention capacity of the engineered barrier system (EBS) (Nagra,2008). The main design elements of an EGTS are (i) specially designedbackfill materials for the emplacement caverns, characterised by highporosity and high compressive strength, and (ii) gas-permeable tunnelseals consisting of sand/bentonite (S/B) mixtures with bentonite con-tents of 20% to 30%.

The Gas-Permeable Seal Test (GAST) was initiated in 2010 andconducted at the Grimsel Test Site (GTS, Switzerland) in 2011 and2012. An S/B seal with a length of 8 m and a diameter of 3 m wasemplaced to demonstrate the effective functioning of gas-permeableseals at realistic scales and under realistic hydraulic boundary condi-tions (‘proof of concept’).

Technological gaps may generate preferential flow paths within theswollen S/B mixture (Wang et al., 2013). To avoid preferential waterand/or gas flow along the tunnel wall, a bentonite ring with a target

41 21 693 41 53.

hydraulic conductivity of at least 1E−12 m/s, corresponding to a drydensity of the bentonite of approximately 1.4 Mg/m3, had to beemplaced around the S/B seal. The first emplacement option assessedwas “shot-claying”, which involved mixing MX-80 granular bentonitewith water (at a volumetric water-to-bentonite ratio of 3 to 11.7),feeding the mixture into a hydraulic pump and shooting the mixtureonto the tunnel wall (Fig. 1). A shot-clay test was performed at theGrimsel URL as part of the pre-testing for the final experiment setup(Teodori et al., 2012).

Dixon et al. (2011) presented a comprehensive summary of granularand bentonite pellet installations to fill technological gaps in high-levelnuclear waste repositories. This summary highlighted the difficultiesrelated to the low angle of repose of dry pellets when poured and pelletdamage that occurs when the material is blown in dry conditions.The summary by Dixon et al. (2011) also reported on wet-blowing in-stallations, highlighting the ability of wet-blown bentonite to be placedon near-vertical surfaces and the lack of information on the hydro-mechanical behaviour of the emplaced material.

In the experiment discussed in the present study, after the layer ofemplacing the bentonite on a tunnel wall, the layer was subjected toseveral hydro-mechanical processes, some of which resulted fromthe experimental emplacement and others of which were tested inthe lab to assess their potential to optimise the final dry density of the

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Fig. 1. Shot-clay experiment carried out at theGrimsel URL.MX-80 granular bentonitewasmixed with water, pumped and shot on the wall of the tunnel.

10-3 10-2 10-1 100 101 102 103

Pore size diameter, d [μm]

0

0.1

0.2

0.3

0.4

PS

D [-

]

MX-80 shot clay

0

0.2

0.4

0.6

0.8

1

Cum

ulat

ive

void

rat

io [-

]

a

b

Fig. 3. Results of the MIP test on a sample of MX-80 shot-clay bentonite: cumulative voidratio (a), and pore size density function (PSD) vs. pore size diameter (b).

11A. Ferrari et al. / Engineering Geology 173 (2014) 10–18

bentonite ring after full saturation. The laboratory tests primarilyassessed the impact of a ventilation phase immediately followingshot-claying and the compaction due to the emplacement of the S/Bseal inside the bentonite ring. The sampling procedure at GTS isdescribed in the next section. The material was characterised in termsof its index properties, microstructural features, swelling potential andwater retention capacity. A comprehensive stress path was designed,and a controlled-suction test was carried out to assess the probablehydro-mechanical response of thematerial during the various expectedphases of environmental conditions in the repository. The results of theexperiments were compared with other data on the behaviour ofcompacted MX-80 granular bentonite to assess the effects of the shot-clay emplacement technique on the behaviour of MX-80 bentonite.

2. Tested material

2.1. Sampling procedure

Laboratory tests were carried out on material samples collected onsite during the emplacement of the shot-clay. After the emplacementof the first bentonite layer, the shooting was suspended to allow theinstallation of several cylindrical steel tubes (with diameters of 9.5 cmand heights of 12 cm), that were pushed approximately 1 cm into thebentonite layer (Fig. 2.a).

The mixture of bentonite and water was then shot directly into thesampling tubes (Fig. 2.b), and eventually, the cylinders were extracted,trimmed (Fig. 2.c), sealed and transported to the laboratory. Visual in-spection of the shot-clay front on the tunnel surface suggested thatgood homogenisation of water and bentonite was obtained during theshooting. Examination of the trimmed core (Fig. 2.c) suggested thatthe bentonite grains were dry in their interiors and that water wasabsorbed by the finer particles and on the surfaces of the grains only.

Fig. 2. Sampling of the shot-clay MX-80 bentonite: a) installation of the steel sampling tubec) extracted tube containing the sample.

2.2. Index properties

MX-80 bentonite was used for the shot-clay experiment. It contains85% Na-smectite clay, which confers the well-known high swelling ca-pacity, and has a specific area of 523 m2/g (Plötze and Weber, 2007).The index properties of the shot-clay MX-80 bentonite were deter-mined in the laboratory. A specific gravity Gs = 2.74 was measuredwith a pycnometer, using Kerdane rather than water because its non-polarity prevents the development of diffuse double layers. A liquidlimitwl=4.30 wasmeasured using the fall cone penetration technique(Wood, 1985; BSI, 1990). A plastic limit wp = 0.65 was determined inaccordance with ASTM D4318. The average water content was 0.39 forthe samples that were extracted immediately from the shot layer andsealed and 0.32 for the samples thatwere exposed to the site conditionsfor approximately 30 min before the tubes were sealed. Determinationof the grain size distribution of the granular bentonite (apparent grainsize distribution) was performed by sieving the bentonite grains attheir hygroscopic water content; the analysis revealed a sand-sizedfraction of 60% and a gravel-sized fraction of 30%.

s on the tunnel wall; b) shooting of the mixture of water and bentonite into the tubes;

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Table 1Initial characteristics of the tested shot-clay specimens in the experimental activities.

Test Watercontent

Voidratio

Degree ofsaturation

Constrained swelling 0.380 1.38 0.75Free swelling 0.319 1.38 0.63Water retention 0.390 1.43 0.75Controlled-suction hydro-mechanical test 0.320 1.38 0.63

12 A. Ferrari et al. / Engineering Geology 173 (2014) 10–18

The bulk density and the dry density were in the ranges of1.58–1.63 Mg/m3 and 1.14–1.17 Mg/m3, respectively. The averagevoid ratio was 1.4. Complementary density measurements were per-formed on samples cored out from the bentonite layer after the shot-clay was completed. The density values of these samples were in thesame range of those obtained for the samples collected in the tubesinstalled before the shooting.

The initial total suction was measured using a chilled-mirror dew-point psychrometer (WP4C, Decagon Device Inc.) (Leong et al., 2003;Cardoso et al., 2007). The device measures the total suction using thepsychrometric law, which relates the water potential of the materialto the relative humidity established in the measuring chamber inwhich the specimen is placed. Initial total suction values of 4 MPa and6 MPa were measured for the samples at water contents of 0.38 and0.32, respectively.

2.3. Microstructural features

Mercury intrusion porosimetry (MIP) was used to determine thepore size density (PSD) function of the shot-clay. A cubic specimenapproximately 5 mm in size was trimmed from one of the collectedsamples and freeze-dried to remove the pore water. The porosimetrytest was carried out using a Thermo Electron Corporation porosimeter.The maximum applied intrusion pressure was 400 MPa (correspondingto an entrance pore size diameter of approximately 4 nm). The pressurewas changed incrementally, and the intruded volume was measuredcontinuously. The compressibility of the various components of theequipment was considered in the analysis.

Fig. 3 shows the cumulative intrusion void ratio (eHG) and the poresize density function (PSD = −ΔeHG / Δ(log d)) versus the entrancepore diameter (d). The difference between the cumulative void ratio

precision balance

Salt solution

desiccator

peristalticpump

123.20 g

coarse po

vapordistributionpanel

Fig. 4. Schematic layout of the experimental setu

and the void ratio measured on the samples (0.45) is associated withthe inter-lamellar bentonite porosity that cannot be accessed by themercury and with the largest pores on the sample surface being filledby the mercury before the intrusion process starts. A multimodal poresize density function was obtained and is shown in Fig. 3.b. A peakwith a modal value of approximately 20 nm is observed. This peak iscommonly observed in compacted granular bentonites and is associatedwith the intra-aggregate porosity, i.e. the pores between the bentoniteparticles within the aggregates (e.g., Romero et al., 2011). Pore sizes inthe range of 4 × 10−2 to 10 μm correspond to the swollen intra-aggre-gates pores in assemblages that were hydrated during the shot-clayprocess. Pore sizes larger than 10 μm correspond to inter-bentonite-assemblage pores and represent the macro-pores in the shot-claybentonite.

3. Experimental programme

The behaviour of the shot-clay MX-80 bentonite was assessedthrough an intense laboratory campaign. The aim of the tests was toanalyse the response of the material to the environmental conditionsexpected in the repository from emplacement through full saturation.The material's swelling potential, water retention behaviour andvolumetric response under hydro-mechanical loading were analysed.All of the tests were performed on specimens cored out from the tubesamples collected on site. The initial characteristics of the tested speci-mens in the various experiments are listed in Table 1. Distilled waterwas used in all of the experiments. All of the tests were run in atemperature-controlled laboratory (22 ± 0.5 °C). Details of the testingprocedures are given in the following sections.

3.1. Swelling behaviour

To evaluate the swelling potential of the shot-clay MX-80 bentonite,constrained and free swelling tests were performed on specimens 1.88 cmin height and 7.53 cm in diameter. Each specimen was placed in arigid-walled steel cell, resting on a porous disc connected to a waterinlet. The upper part of the specimenwas in contactwith a coarse porousstone, and a flushing line was connected to the upper part of the cell.

The swelling pressure wasmeasured by inserting the cell containingthe specimen into a rigid frame to ensure constant-volume conditions.To capture any swelling associated with the homogenisation of the

loading frame

Specimen

rous disks

LVDT

p for the controlled hydro-mechanical test.

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Vertical stress, σv [kPa]

Tot

alsu

ctio

n, ψ

[MP

a]

A. initialstabilization

A-B. initialcompaction

C-D. further compaction

D-E & E-F. wetting in constantvolume condition

B-C. drying

A B6

87C D

E

F

67 249 495 1240

37

Fig. 5. Stress path implemented for the investigation of the hydro-mechanical behaviour ofthe shot-clay MX-80 bentonite.

13A. Ferrari et al. / Engineering Geology 173 (2014) 10–18

water content in the material after the shooting, the specimen wastaken to the laboratory and placed in the test apparatus as soon as pos-sible (approximately 2.5 h after the shooting time). In this phase, no ac-cess to water was provided. A load cell (with an accuracy of 10 kPa withrespect to the area of the specimen) was placed between the top capand the frame to measure the swelling pressure. An initial total verticalstress of 80 kPa was applied to ensure good contact of the various partsof the apparatus. The specimenwas then inundatedwithwater, and theswelling pressure was continuously monitored until it stabilised.

A free swelling test was carried out by saturating the specimen andmeasuring the vertical heave with an LVDT system. A constant porewater pressure of 10 kPawas applied to the lower base of the specimen,and the flushing line on the top was opened periodically. This configu-ration ensured the evacuation of air from the top of the cell during therising of the wetting front.

3.2. Water retention behaviour

The water retention curve for the main drying path was analysedusing a controlled air drying process in which the total suction wasmeasured with a chilled-mirror dew-point psychrometer. Several spec-imens were cored from one sample using a special holder that could bepositioned directly in the device for the suctionmeasurement. After theinitial water content and total suction of the sample were determined, a

1 10 100Time [h]

0

200

400

600

800

1000

1200

Sw

ellin

gpr

essu

re, σ

p [k

Pa]

a b

Fig. 6. Results of the swelling tests: swelling pressure evolution vs. time under constant voconditions (b).

drying path was initiated in each specimen by controlled air drying atthe ambient laboratory conditions (T = 22 °C, RH = 40%). The evolu-tion of the water content wasmonitored for each specimen by continu-ously weighing the sample holder. The air-drying process was stoppedonce each specimen reached its target water content value. The sampleholder was then sealed, and the sample was cured for 2 days to ensuregood distribution of the water within the specimen. The total suction ofthe specimenwas thenmeasured using theWP4C device. After the suc-tion wasmeasured, the volume of the specimen was measured, and thewater content was determined by oven-drying.

3.3. Controlled-suction hydro-mechanical test

A controlled-suction hydro-mechanical test was carried out to mea-sure the volume change and water content variation in the materialover the range of environmental conditions expected in the repository.A schematic diagram of the experimental arrangement is shown inFig. 4. The cell holds a sample with a diameter of 7.53 cm and a heightof 1.88 cm. The vertical load is controlled by a level arm system. The ap-plied vertical stress is assumed to be representative of the radial stressof the shot-clay layer in the tunnel. The vertical displacement is mea-sured by an LVDT installed on the top the cell. The computed verticalstrains in the cell are equivalent to the radial strains of the shot-clay inthe tunnel. The total suction is controlled using the vapour equilibriumtechnique. The pore water potential of the material is represented bythe migration of water molecules through the vapour phase, relativeto a reference system of a known water potential, until equilibrium isachieved (Romero, 2001). At the end of the equalisation phase, thepore water and the vapour phase have the same potential. Throughthis equality and by assuming that the water vapour obeys the idealgas law, it is possible to express the total suction of the material as afunction of the relative humidity of the closed system inwhich the spec-imen is placed, according to the psychrometric law. The relative humid-ity (RH) and the absolute temperature (T) are related to the total suction(ψ) through the following expression (Fredlund and Rahardjo, 1993):

ψ ¼ −ρwRTMw

ln RHð Þ

where R is the universal gas constant and ρw andMw are the density andthe molecular mass of water, respectively.

Variably saturated NaCl solutions and a saturated Mg(NO3) solutionwere used to control the relative humidity and hence the total suction ofthe reference system. Romero (2001) and Witteveen et al. (2013)provided the relationship between the solution concentration and theapplied suction. A pump was used to force a humid air flow throughthe pores of the specimen to reduce the time required to reach equilib-rium (Pintado et al., 2009).

0.01 0.1 1 10 100

Time [h]

0

50

100

150

200

250

300

350

400

Wat

erco

nten

t,w

and

Axi

alst

rain

, εa

[%]

lume conditions (a); swelling heave and water content evolution under free swelling

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0

0.1

0.2

0.3

0.4

Wat

erco

nten

t,w

100101

Total suction, ψ [MPa]

0

0.2

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0.8

1

Deg

ree

of s

atur

atio

n, S

r

c

0.4

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1

1.2

1.4

1.6

1.8

Voi

dra

tio,e

a

b

sample atinitial condition

sample atinitial condition

sample atinitial condition

Fig. 7. Void ratio vs. suction for drying path in shot-clay MX-80 bentonite material (a);water retention behaviour of shot-clay MX-80 bentonite in terms of water content (b),and degree of saturation (c).

14 A. Ferrari et al. / Engineering Geology 173 (2014) 10–18

The applied stress path was based on the range of environmentalconditions that the shot-clay material is expected to experience in theevolution of the repository. The following steps were applied and aredepicted in Fig. 5:

1) In the initial state (point A), the specimen was placed in the cell andequalised to a total suction of 6MPa using a 1.3MNaCl solution. Thissuctionwas the valuemeasured in the sample immediately followingthe shooting (Section 2.2). A vertical stress of 8 kPa was applied toensure good contact between the specimen and the loading system.

2) The vertical load was increased to 67 kPa to simulate an initial com-paction of thematerial (path A–B) to reproduce the emplacement ofthe buffer material (such as bentonite blocks) in the repository.

3) A drying path (B–C) was applied to reflect the ventilation phase ofthe repository, during which the material will be exposed to the rel-ative humidity of the tunnel. A suction of 87MPawas applied using asaturatedMg(NO3) solution, corresponding to a relative humidity of50% at the laboratory temperature, which was the average relativehumidity at the Grimsel URL.

4) A loading path (C–D) was then applied increasing the vertical stressto 249 kPa at a constant total suction of 87 MPa. This phase isintended to reproduce the development of the swelling pressure inthe buffer material when it is wetted through the vapour phase.This adsorption is justifiedwhen considering that the buffermaterialis usually emplaced at its hygroscopic water content (e.g. 5% for thegranularMX-80bentonite at RH=34%, corresponding to a total suc-tion of 148MPa) and exposed to the relative humidity in the tunnel.

5) The path D–E reflected the wetting of the material upon watervapour uptake from the surrounding host rock. The wetting wasperformed using a saturated NaCl solution, resulting in a totalsuction of 37 MPa (corresponding to a relative humidity of 75%).During this phase, the volume was kept constant to reflect thepresence of the buffer material. The axial strain was limited to therange of ±0.25% by increasing the vertical stress in small steps, toprevent swelling of the material. This process was repeated untilthe specimen did not exhibit any further tendency to swell.

6) Lastly, the specimen was flooded with distilled water (path E–F) tomeasure the maximum swelling potential associated with the fullsaturation of the material. To accomplish this operation, the cellwas removed from the loading system and installed in a highlyrigid frame equipped with a load cell. An initial vertical stressequal to the swelling pressure obtained at the end of path D–E wasapplied.

To better observe the material behaviour during the application ofthe stress path described above, the cell was opened for visual observa-tion at the ends of steps B–C, D–E and E–F. This operation wasperformed quickly to minimise disturbance of the test. After eachinspection, the conditions of suction and vertical stress at the end ofthe imposed step were re-stabilised before the following step was ap-plied. No vertical strain or water content change was observed duringthis equalisation phase, confirming that the opening of the cell did notcause disturbance of the test procedure.

4. Test results

4.1. Swelling potential of the as-shot material

The results of the constrained swelling test are shown in Fig. 6.a, inwhich the measured swelling pressure is plotted with respect to time.The initial homogenisation of the water content after the shooting didnot produce any appreciable swelling pressure. A maximum swellingpressure of 990 kPa was observed 10 days after the cell was floodedunder constant-volume conditions.

The result of the free swelling test, in terms of the axial strain andwater content evolution over time, is shown in Fig. 6.b. A final swellingstrain of 324% and a final water content of 280% (corresponding to a

calculateddegree of saturation of 99%)were reached after approximate-ly 64 days.

4.2. Water retention behaviour

Thewater retention behaviour of shot-clayMX-80 bentonite along adrying path is depicted in Fig. 7 in terms of the void ratio, water content

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time [h]

A

A

B

B

B

B

C

C

C

C

D

D

D

F

FD

0.1

0.15

0.2

0.25

0.3

0.35

0.4

0.45W

ater

cont

ent,

w

0.01 0.1 1 10 0.01 0.1 1 10 100 1000 0.01 0.1 1 10 100 1000 0.01 0.1 1 10 100 10000.01 0.1 1 10 1000.15

0.1

0.05

0

-0.05

-0.1

-0.15

Axi

als

tra

in, ε

ab c d e

A

Initial equilibrium Initial compaction Drying Compaction Wetting

a

start

start

Fig. 8. Variation of the water content and axial strain of the specimen during the different steps of the applied stress path shown in Fig. 5.

15A. Ferrari et al. / Engineering Geology 173 (2014) 10–18

and degree of saturation versus the total suction. The initial conditionsmeasured on the whole sample from which the specimens were ex-tracted are also reported. The measured void ratio of the specimenswas initially higher than the sample void ratio. This difference is attrib-utable to the rebound of the material during the specimen extraction.This observation seems to be confirmed by the change in slope inFig. 7.a once the void ratio of the sample was reached during the drying

0.1

1

10

100

Tot

alsu

ctio

n, ψ

[MP

a]

A B

C D

E

F

0 0.5 1 1.5

Vertical stress, σv [MPa]

0.12

0.08

0.04

0

-0.04

Axi

alst

rain

, εa

A

c

a

A

B

C

D E FWetting

Wetting

Drying

Drying

Fig. 9. Results of the controlled-su

process. A residual degree of saturation of approximately 40% wasobtained.

4.3. Controlled suction hydro-mechanical behaviour

The initial characteristics of the tested specimen are reported inTable 1. The evolution of the water content and axial strain over time

A

B

C, D

0.12 0.16 0.2 0.24 0.28 0.32 0.36

Water content, w

d

bE

F

FED

C

B

A

Wetting

Wetting

Drying

Drying

ction hydro-mechanical test.

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Fig. 10. Observation of the specimen after opening of the cell at the end of different steps: drying due to step B–C (a), wetting due to step D–E (b), and full saturation due to step E–F (c).

16 A. Ferrari et al. / Engineering Geology 173 (2014) 10–18

for the different steps of the imposed stress path are shown in Fig. 8.Fig. 9 depicts the equilibrium states in the planes of total suction vs. ver-tical stress, axial strain vs. vertical stress, total suction vs. water contentand axial strain vs. water content. During the initial equalisation phase(A), no significant deformation of the specimen was recorded, andonly limited wetting was observed. This wetting is attributed to initialdrying of the specimen during the cell installation. The water contentreached (34%) is consistent with the water retention curve shown inFig. 7.b. The loading path (A–B) at constant total suction caused anaxial strain of approximately 1% without any expulsion of water. Thefollowing drying step (B–C) took 33 days to reach equilibrium and re-sulted in significant shrinkage of the material (9%) and a reduction ofthe water content to 14.2%, consistent with the water retention curveshown in Fig. 7.b. At this stage, the cell was opened to assess the lossof lateral contact with the oedometric ring and the formation of dryingcracks. Lateral shrinkage of approximately 4% in radial strain was calcu-lated by analysing the collected images (Fig. 10.a). Interestingly, thecreation of drying cracks was also observed on site, three to four daysafter the shooting. A loading pathwas applied by increasing the verticalstress to 249 kPa (C–D) while maintaining constant total suction. As aresult, the axial strain increased up to 11% while the water contentincreased slightly. The wetting path D–E, which was applied using anunsaturated NaCl solution in the vapour phase, resulted in an increaseof the water content to approximately 0.20, while the variation in theaxial strain wasmaintained in the range of ±0.25%. A swelling pressureof 495 kPa was measured during that intermediate saturation step(Fig. 11.a). The cell was also opened for visual observation after thispath. As Fig. 10.b shows, the specimen swelled due to water vapour up-take, reversing the lateral shrinkage around the perimeter that occurredduring the drying procedure along path B–C. The cracks observed earlier

Sw

elli

ng

pre

ssu

re, σ

P [

MP

a]

200

400

600

800

1000

1200

1400

0 400 800

Time [h]1200

a

Fig. 11. Swelling pressure development during the wet

in the centre of the sample were only partially healed and were stillclearly observed.

The flooding of the specimen (path E–F) at constant volume led tothe development of a final swelling pressure of 1250 kPa after approxi-mately 6 days (Fig. 11.b). The cell was finally dismantled and the fullhomogenisation of the specimen was observed due to saturation(Fig. 10.c). A final water content of 0.41 (corresponding to a computedfinal degree of saturation of 99%) was measured.

5. Discussion of test results

Some conclusions concerning the effects of the emplacement tech-nique on the material behaviour can be drawn from the experimentalresults obtained. The experimental results were compared with the re-sults of complementary tests performed on compacted samples of gran-ular MX-80 bentonite with a similar apparent grain size distribution,prepared at various dry densities (Seiphoori, 2014).

The dry density achieved by the shot-claying procedure (approx.1.15 Mg/m3) was similar to the density that would be obtained if gran-ular bentonite were simply poured on the ground (approximately1.2Mg/m3) but lower than the one thatwould be obtained using a gran-ular material optimised to a Fuller distribution (1.4–1.5 Mg/m3), as isforeseen for the use of granular bentonite as a buffer material, inaccordance with the Swiss concept of high-level nuclear waste disposal(Plötze and Weber, 2007). The lower dry density achieved by the shot-claying procedure is attributed to the fast swelling of the bentonitegrains during mixing with water in the pump system, and it is stronglydependent on the initial properties of the material and the amount ofwater added during shot-claying.

0 40 80Time [h]

120 160

b

ting phase: step D–E (a) and step E–F (b) in Fig. 5.

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0.35

1 1.2 1.4 1.6 1.8

Initial dry density, ρd (Mg/m3)

0

2

4

6

8

10

12

Sw

ellin

gpre

ssur

e, σ

P [M

Pa]

Compacted

Shot-clay

3.85ρ d

2

0.011

= 0.99

e

R

σp =

Fig. 13. Swelling pressure versus initial dry density under constant volume conditions forcompacted and shot-clay MX-80 bentonite samples.

17A. Ferrari et al. / Engineering Geology 173 (2014) 10–18

To compare themicro-structural features associated with the differ-ent emplacement techniques, the results of anMIP test (in terms of poresize distribution) on a poured granular bentonite sample (with a drydensity of 1.5Mg/m3)was compared to the PSD of the as-shot bentonite(Fig. 12). The comparison confirmed that the bentonite grains swellduring mixing with water. This swelling resulted in the creation oflarger void spaces particularly in the pore size range attributed tointer-bentonite-grain pores. This structure also resulted in a lower drydensity for the shot-clay. Evolution with time of the microstructuralfeatures of the shot-clay bentonitemay be expected as a result of ageingeffects (Delage et al., 2006).

The initial low dry density and high water content after shootingwere also responsible for the reduced swelling pressure of the bentoniteof approximately 1 MPa. In Fig. 13, the swelling pressure measured inthis study is compared with the results of swelling pressure testscarried out on granular bentonite compacted at various dry densities(Seiphoori, 2014). Interestingly, the swelling pressure for the shot-claybentonite fits the general exponential trend for the compacted materialwell. The results of this comparison suggest that the result of the em-placement technique on the behaviour of thematerial could be assesseddirectly by considering the dry density achieved in the shooting.

This tendency also seems to be confirmed by the results of theanalysis of thewater retention properties of thematerials. Thewater re-tention behaviour of the shot-clay and the compactedMX-80 bentoniteat different initial dry densities along drying paths are compared inFig. 14. The water retention behaviour observed in the controlled-suction oedometric test (point C) is also represented in this plot. Thewater retention properties of the samples prepared by differentemplacement techniques follow a unique trend for a wide range oftotal suction values, despite their different initial dry densities. Thisunique trend between the total suction and the water content is validfor the domain governed by the adsorptive storage mechanism, accord-ing to which water is retained in the intra-aggregate pores (Salageret al., 2013). The effect of the emplacement technique can be observedin the reduced air entry value for the shot-clay bentonite. This is a directconsequence of the lower initial dry density.

The controlled-suction test provided information on the hydro-mechanical behaviour of thematerial under various loading conditions.The most severe changes in strain and water content were associatedwith drying during the ventilation phase. The test also highlighted thetendency of the material to crack during the drying step at a relativehumidity of 50%, which is typical for GTS in the winter. The shot-claybentonite showed, however, good self-sealing properties once fullsaturation was attained. The formation of drying cracks at the imposedrelative humidity could be a consequence of the low emplacement drydensity (Kleppe and Olson, 1985; Péron et al., 2009).

10-3 10-2 10-1 100 101 102 103

Pore size diameter, d [μm]

0

0.1

0.2

0.3

0.4

PS

D[-

]

Shot-clay samplePoured sample

Fig. 12. Comparison between the results of the MIP test on a sample of shot-clay MX-80bentonite and a sample of compacted granular MX-80 bentonite.

6. Conclusions

Based on the above discussion, it can be concluded that the shot-clayemplacement technique does not change the overall behaviour of thegranular MX-80 bentonite, except that the low initial dry density leadsto reduced swelling capacity and a reduced air entry value and an in-creasing tendency to form drying cracks, compared to the compactedMX-80 bentonite. The dry density achieved with the shot-clay tech-nique was lower than the target value. In order to reach a higher drydensity, themethod could be improved by optimising the original gran-ular bentonitematerial and reducing the amount of water added duringshot-claying (Koch, 2002; Teodori et al., 2012). The shot-clay emplace-ment technique was capable of providing a homogeneous layer of ben-tonite along the entire section of the tunnel; such layer would not berealizable by simply pouring the granular bentonite. The laboratorytest results show that the final density (after full saturation underconstrained conditions) can be improved considerably by ventilatingthe tunnel at 50% RH, but the results also show that post-compactionof the material has little impact on the final density.

1 10 100

Total suction, ψ [MPa]

0.1

0.15

0.2

0.25

0.3

Wat

er c

onte

nt,w

Fig. 14. Comparison of thewater retention behaviour of shot-clay and the compactedMX-80 bentonite compacted at different initial dry densities. Point C recorded during thehydro-mechanical stress path is also shown (ρd,i is the initial dry density).

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18 A. Ferrari et al. / Engineering Geology 173 (2014) 10–18

Overall, the shot-clay technique has high potential to achieve thefinal dry density of 1.4 Mg/m3 in MX-80 bentonite, which was the tar-get density in this experiment. However, the shot-clay application ofthe bentonite on the tunnel surface, which permits free swelling,may bemore limited than the application into a closed volume, as per-formed by Dixon et al. (2011), because in that case, the early swellingof thematerial is limited by the confined volume of the backfilled voidspace.

Acknowledgments

The authors would like to thank the National Cooperative forNuclear Waste Storage of Switzerland (NAGRA) for its support.The helpful discussions with Mr Sven-Peter Teodori (NAGRA) areacknowledged.

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