A Numerical Investigation on the Effect of Gas Pressure on the Water Saturation of Compacted Bentonite-Sand Samples

Liu, Jiang-Feng; Song, Shuai-Bing; Liu, Jian; Huang, Bing-Xiang; Cao, Xu-Lou; Zhang, Kai; Skoczylas, Frédéric

doi:https://doi.org/10.1155/2017/9010572

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Fluid Dynamics in Geomaterials

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Research Article | Open Access

Volume 2017 | Article ID 9010572 | https://doi.org/10.1155/2017/9010572

A Numerical Investigation on the Effect of Gas Pressure on the Water Saturation of Compacted Bentonite-Sand Samples

Jiang-Feng Liu,^1,2Shuai-Bing Song,¹Jian Liu,³Bing-Xiang Huang,⁴Xu-Lou Cao,¹Kai Zhang,¹and Frédéric Skoczylas⁵

Academic Editor: Qinghui Jiang

Received08 Jun 2017

Revised19 Sept 2017

Accepted08 Oct 2017

Published27 Dec 2017

Abstract

In deep geological disposal for high-level radioactive waste, the generated gas can potentially affect the sealing ability of bentonite buffers. There is a competition between water and gas: the former provides sealing by swelling bentonite, and the latter attempts to desaturate the bentonite buffer. Thus, this study focused on numerically modelling the coupling effects of water and gas on the water saturation and sealing efficiency of compacted bentonite-sand samples. Different gas pressures were applied to the top surface of an upper sample, whereas the water pressure on the bottom side of the lower sample was maintained at 4 MPa. The results indicated that gas pressure did not significantly affect the saturation of the bentonite-sand sample until 2 MPa. At 2 MPa, the degree of water saturation of the upper sample was close to 1.0. As the gas pressure increased, this influence was more apparent. When the gas pressure was 6 MPa or higher, it was difficult for the upper sample to become fully saturated. Additionally, the lower sample was desaturated due to the high gas pressure. This indicated that gas pressure played an important role in the water saturation process and can affect the sealing efficiency of bentonite-based buffer materials.

1. Introduction

The management of high-level radioactive waste is an important issue for countries with nuclear power. Currently, deep geological disposal methods are used by most countries. In deep geological disposal systems, barriers include natural geological barriers and engineered barrier systems (EBSs). EBSs may comprise various subsystems or components, such as waste forms, canisters, buffers and backfills, seals, and plugs. Bentonite or bentonite-based materials (e.g., a bentonite/sand mixture was used in this study) have been used by several countries as buffer and backfill materials [1–7]. In most repository concepts, bentonite is only partially saturated. After the repository is closed, groundwater in the host formation will invade the bentonite barriers. Underground water seepage will cause bentonite swelling and consequently disposal pit sealing.

Nevertheless, in the long term, gases may be produced in the repository by several methods, such as metal corrosion, water radiolysis, and organic waste microbial degradation, which produce hydrogen, oxygen, methane, and carbon dioxide [8–10]. Over time, gas pressure will increase and build up if generation rates are high and transport is within the repository. This pressure may be sufficient to affect the repository structure and properties, particularly those of bentonite/sand mixtures. Water is favourable for the saturation of bentonite, whereas gas has the opposite effect. Therefore, the sealing provided by swollen bentonite competes with the effects of gas, which attempts to be desaturated and migrate through the buffer to the surrounding host rock and potentially the environment and simultaneously remove radionuclides [11].

In recent decades, researchers have tried to evaluate the sealing efficiency of engineered barriers. One approach is to measure the gas permeability of samples under different confining pressures [12–14]. Another approach is to measure the gas breakthrough pressure of samples under constant confining pressures [5, 6, 15–18]. Regarding these two approaches, one of the most important factors is the water saturation degree, which has a close relationship with the sealing ability of the samples. However, it is difficult to measure the degree of saturation of a sample during a traditional triaxial test because the sample cannot be removed from the triaxial cell during the test. Therefore, numerical modelling is a good method to evaluate the degree of saturation. Additionally, we can obtain the distribution of the degree of saturation in different potions of the sample.

At the time of writing, a few modelling studies have been performed to simulate gas/water transport in clayey materials. Fall et al. [19] utilized a coupled hydromechanical (HM) model to predict and analyse gas migration in sedimentary rock. This model considered elastic degradation due to microcracks or damage and mechanical damage-controlled gas flow. Xu et al. [20] simulated gas migration in water-saturated argillaceous rock with a two-phase flow and a mechanics-coupled numerical model (H²M). In this model, intrinsic permeability and mechanical and hydraulic conditions were varied during the gas migration process. Gonzalez-Blanco et al. [21] simulated gas migration in a Cenozoic clay with a fully coupled hydromechanical model, which incorporated an embedded fracture permeability model. Additionally, other researchers performed a series of numerical modelling assays to determine gas migration in clayey materials [16, 22–24].

In situ water pressure is approximately 4-5 MPa, whereas gas pressure increases gradually and decreases again when breakthrough occurs. This indicates that a coupling effect exists between a constant water pressure and an increasing gas pressure. However, many researchers overlooked this phenomenon. Thus, our modelling aimed to reproduce the competition between water and gas and their coupling effects on the water saturation of bentonite-based buffers. This study is a supplementary work in conjunction with our other FORGE (Fate of Repository Gases) experiments [6]. The overall project aims to investigate and quantify gas generation and migration in the underground disposal of radioactive wastes.

2. Theoretical Model

2.1. Governing Equation

Flow in unsaturated medium is commonly described by the Richards equation [26–28]:where is the hydraulic conductivity (Darcy law), is the hydraulic pressure, and is the vector of gravity (the value is −1 for the vertical direction, and the value is 0 for the horizontal direction). The effective water saturation can be expressed as follows:where is the volume water content, is the residual water content, and is the saturated water content (i.e., 1.0). With (2), we can rewrite (1) as where is the apparent porosity in water (in this case, the water content is defined by the ratio of the water volume to the sample volume), is the water permeability, is the relative water permeability, is the viscosity of water, is the density of water, is the acceleration of gravity, and is the water pressure. In the nonsaturated case, , where is the gas pressure and is the capillary pressure.

There are three unknown parameters in (3): , , and ( and are constant and directly determined by laboratory experiments, and is equal to 1.0 × 10⁻³ Pa·s). Therefore, (3) requires two additional equations to solve, which are presented as follows.

2.2. Kelvin-Laplace Equation

The Kelvin-Laplace equation describes the relationship between capillary pressure and relative humidity RH. The relative humidity of the air above the meniscus in a capillary pore is given by the Kelvin equation [29], as cited by Galvin [30]:where is the molar volume, is the universal gas constant, is the temperature, is the surface tension, is the radius of the droplet, and is the contact angle. Indeed, for a porous medium, this equation is assumed to describe the relationship between the inside relative humidity and the maximum radius of the pores, which are filled with water. With the Young-Laplace equation [31, 32]the relationship between the capillary pressure and the relative humidity RH is

2.3. Retention and Relative Permeability Models

The relationship between water saturation and the capillary pressure is defined by the Van Genuchten (VG) model [33]:where and are two parameters that are related to the pore size distribution of the porous medium.

The sorption isotherm, which reflects the relationship between the water saturation and the relative humidity, can be determined by the Van Genuchten model and the Young-Laplace equation. Using laboratory experimental results, parameters and can be determined by the least-squares method.

The relative permeability is given by the Mualem model [34]:Based on the Van Genuchten model, (5) and (6) can be rewritten as follows:For all tests, the temperature was maintained at 20°C; therefore, the temperature effect was neglected in our numerical simulations. The effect of water gravity was also assumed to be negligible.

3. Geometric Model and Boundary Conditions

3.1. Modelling Scheme Design

In situ experiments require several years to several decades. Therefore, laboratory experiments are used to provide useful data for the design and construction of in situ geological repositories and essential parameters for numerical modelling. For the in situ model, as shown in Figure 1, a significant water saturation gradient is observed between the core and the periphery of the buffer because of underground water seepage [25]. The partially saturated core is gradually saturated with water because the saturated peripheral samples are in direct contact with underground water from the surrounding host rock. To reproduce this phenomenon, an original laboratory experiment and a numerical model were established.

Figure 2 shows two samples in a triaxial cell: a fully saturated sample and a partially saturated sample (just after compaction) placed above the fully saturated sample [6]. In a first stage, water and gas were simultaneously injected from the top and bottom sides. The upper sample was supplied with water by the lower sample to realistically simulate an in situ case. In a second stage, the lower sample was removed and replaced by an empty tube. Gas was injected from the bottom side, and the gas pressure was increased from 1 MPa with a step of 1 MPa until a continuous flow was detected. First, when a discontinuous gas flow was detected at the downstream side, the corresponding upstream gas injection pressure was defined as a discontinuous gas breakthrough pressure. Then, the gas pressure was continuously increased. When a continuous gas flow was detected, the corresponding upstream gas injection pressure was defined as the continuous gas breakthrough pressure. More details regarding the definition of discontinuous/continuous gas breakthrough pressures can be found in Liu et al. [5, 6].

Numerical modelling was performed using essential parameters and proper boundary conditions measured during the experimental tests. In this study, we only simulated the first stage of the experiment (see Table 1).

3.2. Model Setup

Simulations were performed with the finite element software “Code_Aster” (Code of Structural Analysis and Thermomechanics For Studies and Research, EDF, France). This code is a general code for thermomechanical calculations and includes a series of analytical methods and nonlinear multiphysical modelling. The finite element method (FEM) was implemented for discretization. The “THM” module of “Code_Aster” was used to treat the continuum mechanics equations using the theory of unsaturated porous media and assuming completely coupled mechanical, thermal, and hydraulic phenomena. In our study, the “AXIS_HH2D” model was selected from the “THM” module. “AXIS” indicates axisymmetry, “HH2” indicates hydraulic modelling with two unknown pressures and two components, and “D” indicates that the points of integration are taken at the tops of the elements. This treatment enables one to diagonalize data matrices to avoid hydraulic oscillation problems.

The boundary and initial conditions of the tests enabled an axisymmetric analysis (see Figure 3). The mesh consisted of quadratic and quadrangular elements (QUAD8). As shown in Figure 3, a two-dimensional 50 mm (height) × 21.5 mm (radius) axisymmetric finite element model was established which was identical to the sample size in the laboratory experiment. There were 1387 nodes and 451 elements in the model. Monitoring points along the axial and radial directions were selected to record the evolution of the saturation degree versus time (see Figure 4).

3.3. Initial Condition

The “AXIS_HH2D” model cannot directly define the initial saturation by . Therefore, we used the capillary pressure to express the initial water saturation. For the lower sample, a water saturation corresponded to a capillary pressure . Theoretically, the capillary pressure must be infinite to define a saturation level of 0, which is impossible in numerical simulations. Therefore, a large capillary pressure was applied to ensure that . For the upper sample, the bentonite-sand mixture received an atmosphere at a controlled relative humidity (RH = 85%) before compacting. Thus, the relevant capillary pressure was (see Figure 5).

The values of the main parameters used for the numerical modelling are shown in Table 2. The parameters , , , , , and were kept constant in all simulations. and were measured by the laboratory experiments. To obtain the parameters and , a series of water retention tests was performed to obtain the relationship between water saturation and relative humidity RH (Figure 6). Then, the least-squares method was used to calculate and .

3.4. Boundary Conditions

For the axisymmetric model, there are three types of boundary conditions: a bottom boundary, a top boundary, and a lateral boundary (Figure 3). Mechanical boundary conditions require zero displacement in the vertical direction at the bottom and the top of the sample and zero radial displacement on the lateral side of the sample. The flow boundary conditions contained water and gas flows. Specifically, the bottom boundary was defined to be in direct contact with water (), the top boundary in direct contact with gas (, and 8 MPa), and the lateral boundary in contact with water and gas (Figure 2). The distributions of gas pressure and water pressure along the height direction were linear (after the hydraulic cut-off), which has been shown by laboratory experiments [6]. For simplicity, the gas and water pressures should decrease systematically along the height direction (Figure 7).

4. Results and Discussion

4.1. Water Saturation of the Bentonite-Sand Sample without Gas: MPa; MPa

The overall evolution of the water saturation degree of the sample is presented in Figure 8(a) as a function of time. A fully water-saturated state was clearly obtained on the 29th day, which was consistent with the experimental results (see Figure 8(b)); that is, the swelling pressure of the upper bentonite-sand sample became stable after the 28th day. In the laboratory experiment, we were unable to judge the evolution of the water saturation degree because the sample could not be removed during the experiment. Therefore, the evolution of the swelling pressure was the only indicator to determine the water saturation degree before the gas breakthrough test.

(a)

(b)

As shown in Figure 8(a), water invasion gradually occurred from the periphery to the centre of the sample. In the experiment, as soon as a water pressure of 4 MPa was applied to the lower sample, the water flow permeated into the upper sample from the top surface of the lower sample and the lateral (right side) and top surfaces of the upper sample. This was due to an initial clearance between the sample and the tube inner surface (Figure 9). In the numerical simulation, this phenomenon was realized by applying water pressure around the boundaries (see Figure 7). Therefore, a significant water saturation gradient was present among the lateral and top surfaces and core. This phenomenon was also observed by the FBEX in situ test [25]. A significant water saturation gradient was observed due to water invasion from the host rock; the water content increased from the axis of the gallery towards the gallery wall (see Figure 1).

Figures 10(a) and 10(b) show the evolution of the water saturation degree of monitoring points at different parts of the sample: from the external surface to the centre of the sample. The water saturation profile changed with time because of the redistribution of moisture. The increasing speed of the water saturation degree was clearly dependent on the distance to the water source, that is, the top surface of the lower sample and the top and lateral surfaces of the upper sample. As shown in Figures 10(a) and 10(b), 17 days were required for moisture to arrive at point A3, whereas 4 days and 9 days were required for water to reach point A2 and point B3, respectively. However, all monitoring points were completely water-saturated after 29 days, which was close to the stabilization time of the swelling pressure of the bentonite sample (see Figure 8(b)).

(a)

(b)

4.2. Water Saturation of the Bentonite-Sand Sample with MPa and MPa

Figure 11 shows the overall evolution of the water saturation degree of the sample versus time at MPa and MPa. No significant differences were observed with or without 2 MPa of gas. However, more time was required for the upper sample to become fully water-saturated, that is, 29 days versus 78 days. The top and upper right surfaces of the sample were not fully but close to fully water-saturated (Figures 11 and 12, point A1) because of the low applied gas pressure. This result was also likely due to coupling effects between the water and gas pressures. In this case, water pressure played a predominant role in the water saturation process.

(a)

(b)

Figures 12(a) and 12(b) show the saturation kinetics of the monitoring points as a function of time. The trends found in series S-1 were confirmed. The water saturation speeds near the water source were higher than those at other sample positions. Additionally, the water saturation gradient appeared in both the axial and radial directions. Because of the applied gas pressure, the water saturation degrees of monitoring points A_1 and C_3 in the external surface were not at full saturation but were close to 1.0 (0.945). This indicated that 2 MPa gas pressure had a limited effect on the water saturation of the upper sample. We can conclude that 2 MPa gas pressure delayed the water saturation process of the upper sample.

4.3. Water Saturation of the Bentonite-Sand Sample with MPa and MPa

The simulation results for the bentonite-sand sample under 4 MPa, 6 MPa, and 8 MPa gas pressure and 4 MPa water pressure are shown in Figure 13. Compared with previous results, the results were notably different when a high gas pressure was applied. First, the upper bentonite-sand sample was only partially water-saturated even after 150 days; second, water did not permeate into the core of the upper sample because of the high-applied gas pressure; finally, more time was required for water to enter the pore network of the sample. Similar phenomena were found in the laboratory experiments: the top surface of the upper sample was only partially water-saturated at the end of the first stage ( MPa and MPa, see Figure 14(a)). Additionally, more time was required for the swelling pressure of the upper sample to become stabilized (Figure 14(b)). Similarly, gas breakthrough tests showed that gas could pass through the sample at low gas pressure when compared with the case when only water pressure was applied during the swelling test (E-1; see Figure 14(c)). Thus, the bentonite-sand sample lost its sealing ability to gas at this stage due to partial water saturation. Thus, the sealing ability of the bentonite-sand sample was very sensitive to the water saturation degree, which had a close relationship with the water and gas around the sample.

(a)

(b)

(c)

In fact, when gas and water were simultaneously applied, a coupling effect was observed. This coupling effect had an apparent effect on the water saturation of the bentonite-sand sample, particularly when the gas pressure was equal to or higher than 4 MPa. For series S-4 and S-5, the lower sample was slightly desaturated when the gas pressure was at least 6 MPa. As a result, a competitive effect was observed between water pressure and gas pressure: the water saturated the sample, whereas the gas had an opposite effect. The water saturation degree of the lower sample gradually decreased with time, which implied that the higher gas pressure had a stronger effect than the water permeation.

More results can be found at the monitoring points (Figures 15(a) and 15(b)). First, the water saturation degrees of the monitoring points (A_2 and A _4) continued increasing even after 150 days. The water saturation developed more rapidly near the top surface of the lower sample, that is, A_2 versus A_4. Figure 13 shows that it was difficult for water to permeate into the centre of the sample, as shown by the profile of curve A_3 (Figures 14(a) and 14(b)). The water saturation degree of A_3 was stable at 0.5, which implied that the sample core was not disturbed by either gas or water. However, this was not the case for the periphery area. For example, the water saturation degrees of the monitoring point C3 were 0.85 (S-3), 0.78 (S-4), and 0.74 (S-5). This indicated that the influences of gas and water on the water saturation of the bentonite-sand buffer were largely dependent on the position and the distance to the gas/water source.

(a)

(b)

4.4. Effect of Gas Pressure on the Water Saturation of the Bentonite-Sand Sample

Regarding the effect of the gas pressure on the water saturation degree of the sample, we analysed points A1 and A3; S-1 ( and MPa) was used as a reference. We calculated the differences of the water saturation degrees between S-2, S-3, S-4, and S-5 (, and 8 MPa) and the reference S-1. As shown in Figure 16(a), gas pressure had a limited effect on the water saturation at 2 MPa or lower. As the gas pressure increased, the effect of gas pressure became increasingly apparent. At MPa, the water saturation degree of point A1 was only 0.76, which indicated that gas pressure had a significant influence on the water saturation at point A1.

(a)

(b)

For point A3, gas pressure had no effects on the evolution of the water saturation degree when the gas pressure was 2 MPa or lower. As shown in Figures 10(a) and 10(b), the water saturation degree of point A3 was 1.0 for S-1 and S-2. However, the water saturation degrees of point A3 remained constant when 4, 6, and 8 MPa gas pressures were applied. This point became fully saturated when 2 MPa or no gas was applied. This indicated that high gas pressure prevented water from transporting into the pores at this point.

Overall, water and gas are two important factors that affect the water saturation and sealing efficiency of the artificial barrier of a radioactive waste repository. In the initial stage, the gas flow rate was notably low, and water can access the pore network of the buffer material. As a result, progressive water saturation and sealing were obtained over time. As the gas pressure increased, the bentonite-sand buffer progressively desaturated, and the sealing ability of the bentonite-sand buffer gradually diminished. When gas release occurred through a part of the bentonite buffer, the gas pressure decreased. Progressive water saturation and sealing were again obtained. This process continued, and the bentonite-sand buffer was saturated and desaturated due to the competition between the water and gas pressures.

5. Conclusions

Both laboratory and in situ experiments require long durations and significant funding. Therefore, numerical simulations are essential tools for understanding gas and water flow processes through partially water-saturated bentonite-sand buffer. Regarding the two important factors of water and gas, this study examined their coupling effect, particularly on the water saturation of bentonite-sand samples. Our investigation was performed with five cases; that is, the water saturation of the bentonite-sand sample was tested with different gas pressures and at a constant water pressure. First, a significant water saturation gradient was observed between the core and the surface of the sample during the saturation process. This gradient disappeared after the entire sample was fully saturated (only for series S-1). When a gas pressure was applied, a coupling effect between the water and gas pressures was observed. Water saturated the sample, whereas gas had the opposite effect. The predominant role was determined by the gas or water pressure acting on the pore structure of the bentonite-sand sample. Even for the same sample, the water saturation distribution was not uniform because of boundary condition variations. When the gas pressure was at least 4 MPa (during the swelling process), it was difficult for water to permeate into the pore network of the sample. Hence, high gas pressures had strong effects on the desaturation of the bentonite-sand sample. The water saturation degrees of the upper and lower samples decreased with time when the gas pressure was at least 6 MPa. This phenomenon is particularly important. In situ, the voids between the canister and the buffer and between the host rock and the buffer are potential places for gas accumulation. If the gas pressure is sufficiently high, both the buffer and host rock near the buffer are affected. As a result, the sealing efficiency of the entire barrier is affected and should not be overlooked.

Conflicts of Interest

The authors declare that they have no conflicts of interest.

Acknowledgments

The authors are grateful for the support provided by the Natural Science Foundation of Jiangsu Province of China (BK20160249) and the Fundamental Research Funds for the Central Universities (China University of Mining and Technology) (2014YC03).

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Copyright © 2017 Jiang-Feng Liu et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

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