Abstract

Long-term stability and safety of the Bayer red mud (BRM) disposal field is very important for the local residents’ life, which necessitates the knowledge of its creep behavior. In order to investigate the creep behavior of BRM, a series of triaxial drained creep tests were conducted by using an improved triaxial creep apparatus. The results indicate that the creep behavior of BRM is significant with confining and deviatoric stresses being critical factors. The creep strain is in a nonlinear relationship with stress and time, and a larger deviator stress will lead to a larger creep strain. The main failure mechanism of BRM is plastic shear, accompanied by a significant compression and ductile dilatancy. Based on the test results, two well-established creep models, the Burgers creep model and Singh–Mitchell creep model, were used to comparatively analyze the creep behavior of the Bayer red mud under a certain stress level. Then, an improved Burgers creep damage constitutive model with the addition of a damage variable was proposed, whose parameters were also analyzed in detail. The comparison of the calculated values of the creep model and the experimental values shows that the proposed creep damage model can better describe the instant elastic deformation, attenuation creep, steady-state creep, and accelerated creep stages of the Bayer red mud.

1. Introduction

The Bayer red mud (BRM), also called as bauxite residue, is a hazardous solid waste generated during the Bayer alumina extraction from bauxite ore [1, 2]. It generally exists as a highly alkaline slurry (Ph 10–12.5) that is appropriately regarded as a hazardous material [3]. As there is a great deal of industrial alkali, fluoride, heavy metals, and other potential pollutants in red mud, long-term stockpiling would not only occupy scarce land resources but also easily lead to serious pollution of the surrounding soil, air, and groundwater [4]. In the past 50 years, the wet process was used to stockpile the Bayer red mud in Guizhou Aluminum Factory red mud disposal field, which led to much unconsolidated BRM in the disposal field. At present, the production technique has been upgraded to the sintering method, more and more dried red mud was stockpiled on the unconsolidated ones directly, which much exceed the original design storage capacity. Therefore, to make disposal field stable when renewing the dry red mud, we must evaluate the long-term stability of the original Bayer red mud.

Good mechanical performance and especially creep behavior of the BRM is essential for safe and stable operation of such disposal field. Many laboratory studies investigated the creep behavior of various soils [57]. Yu et al. [8] performed several creep tests (lasting more than one year) to study the delayed mechanical behavior of Boom clay under the hydromechanical coupling effect. Wen and Jiang [9] discussed creep behavior of natural clayey soil with gravel at the residual state through a series of creep shear tests. Liao et al. [10] conducted a series of triaxial creep on warm frozen silts extracted from Qinghai–Tibet Plateau at a temperature of −1.5°C under the confining pressures of 0.5, 1.0, and 2.0 MPa, respectively. Karimpour and Lade [5] performed triaxial compression tests on dense specimens of Virginia Beach sand at low and high confining pressures to study time effects that relate to grain crushing due to static fatigue or delayed fracture. The abovementioned experimental studies mostly investigated clay, sand, and frozen silts. However, concerning the study of creep mechanical behavior of the Bayer red mud, little experimental data have been reported. Therefore, studies focusing on the Bayer red mud are needed to further our understanding of its creep mechanical behavior.

Based on experimental investigations, various viscoelastic-plastic models [11, 12] taking into account soil and rock microstructure and damage have been proposed. These models can be classified into three categories: empirical models, rheological models, general stress-strain-time models [7, 13], and damage-involved models [14, 15]. The empirical models are mainly obtained by fitting the experimental results from creep tests; due to its relatively simple mathematical formulation and few parameters, the empirical models [1618] are widely used to simulate the creep behavior of various soils.Rheological models usually use differential representation, visualizing the material by the elementary mechanical models composed of elastic springs, plastic sliders, and viscous dashpots[13, 19, 20]. The general stress-strain-time models are often in the incremental form and usually implemented in numerical software [21], such as the overstress model proposed by Karstunen and Yin [22] and the further extended overstress model by Yin et al. [23]. Due to its clear physical meaning and numerical convenience in programming, the general stress-strain-time model is recommended for engineering practice [21].

To clarify the creep behavior of the Bayer red mud, a series of triaxial compression creep tests were conducted on the Bayer red mud samples under different confining pressures. Based on the results, two well-established creep models, the Burgers creep model and the Singh–Mitchell equation, were used to describe the creep behavior of the Bayer red mud under a certain stress level. And then, an improved Burgers creep damage model is built to describe the creep mechanical behavior and damage evolution process of the Bayer red mud under compression. The validity of the improved model is tested by comparing the numerical simulations and test results.

2. Test Conditions and Results

2.1. Materials and Sample Preparation

The Bayer red mud materials were obtained from the disposal field of Guizhou aluminum factory in southwest of China. Natural Bayer red mud is a bauxite residue generated from the Bayer process (a wet process) for alumina production, which presents the color of reddish brown. X-ray diffraction was used to determine the clay minerals [24]. According to the X-ray diffraction, the Bayer red mud is comprised of cancrinite, hydrogrossular, tilleyite, calcite, and xonotlite; the main chemical constituent was SiO2 (accounting for 22.35%), followed by 20.80% of Al2O3, 18.51% of CaO, 8.83% of Na2O, 7.73% of Fe2O3, and a small amount of mixture of K2O, MgO, TiO2, and SO3.

To avoid the nonuniformity of the undisturbed specimens, the remolded specimens were used in this study; that is, the specimens were formed into cylindrical shape, which has a height of 80 mm and diameter of 39.1 mm. The average values of the index properties along with the main characteristics of the tested material are mentioned in Table 1. The Bayer red mud can be classified, according to the Unified Soil Classification System [25], as high-plasticity clays (CH).

2.2. Experimental Apparatus and Procedures

An improved strain control triaxial apparatus of TSZ-6A was used to test the creep behavior of the samples (Figure 1). The improved apparatus changes the former axial strain-controlled loading system into a weight-controlled stress loading system [26]. It also retains the confining/back pressure, pore pressure, volume change, and displacement measurement systems of the former triaxial apparatus.

After the sample was saturated under both 140 kPa confining pressure and 110 kPa back pressure for at least 24 hours, the triaxial creep tests were performed at an ambient temperatures of (20 ± 2)°C. Based on the measured triaxial short-term compression strength, the axial deviatoric stress levels of multistep creep tests of the Bayer red mud samples were determined (Table 2), which are 16.67%, 33.33%, 50.00%, 66.67%, 83.33%, and 100% of the maximum short-term deviatoric stress value. Each deviatoric stress level was maintained for no less than 4500 minutes before the final failure.

2.3. Test Results and Discussions

To show the creep behavior that took place under each stress level clearly, the axial strain-time curve obtained for each stress level is plotted separately in Figure 2 (due to the limitation of the device, the volumetric creep responses of the BRM was not discussed). It is found that, under the low deviatoric stress level (less than maximum short-term deviatoric stress value), the creep curve of the Bayer red mud is composed of instant elastic deformation, attenuation creep, and steady-state creep stages. As shown in Figures 2(a)2(c), when the deviatoric stresses are less than 591 kPa, 684 kPa, and 849 kPa, respectively, only attenuation and steady creep appears in the test, while the creep phenomenon of the samples becomes significant with the increase of the deviatoric stress. It also can be obtained from Figure 2 that attenuation creep occurred for a very short time and was not obvious, indicating that internal damage could not continue to occur over time under a stable lower loading level.

When the deviatoric stress reaches a certain level (100% of the maximum short-term deviatoric stress value), the creep strain is much greater than that at previous stress levels; the accelerated creep stage appears, while instant elastic deformation and attenuation creep strain are unnoticeable. As shown in Figures 3 and 4, when the deviatoric stresses are 591 kPa, 684 kPa, and 849 kPa, respectively, the original structure of the soil sample begins to destruct while the displacement of the soil grains is produced that causes the creep strain of the samples to increase rapidly and fail eventually. Under the maximum deviatoric stress level, the process for each stress level lasts only for 110, 210, and 210 minutes. Figure 5 shows a schematic view of the red mud sample after failure under the deviatoric stress of 591 kPa and the confining pressure of 100 kPa; the main feature associated with the failure is the high axial plastic strain due to the accumulation of the former deviatoric stress level’s damage effects, and no brittle damage is observed in the samples. These results indicated that damage had begun to occur in weak local areas of the soil sample, causing increasing damage and time required for internal stress nonlinear adjustment to an equilibrium state with increased load.

3. Comparative Analysis of Two Creep Constitutive Models

The creep curves in Figure 2 show that the Bayer red mud sample experiences an attenuation creep stage and a steady creep stage when the stress level was less than a certain threshold and no obvious damage occurred over time.

According to the behavior shown by these curves, two well-established creep models, the Burgers creep model and the Singh–Mitchell equation, were used to describe the creep behavior of the Bayer red mud.

The Burgers creep model [27, 28] is made up of the Kelvin and Maxwell models in series as shown in Figure 6.

The creep equation of the Burgers creep model iswhere is the deviatoric stress; and are the elastic modulus and viscosity coefficient of the Maxwell body; and and are the elastic modulus and viscosity coefficient of the Kelvin body, respectively.

The Singh–Mitchell model is an empirical equation with three parameters [16]. The creep equation of the Singh–Mitchell model is given as [27]where is the slope of against at any fixed value of , is the slope of against , at any fixed time, and is the intercept of against at .

The data measured under multistep loading in the test are processed using the Boltzmann superposition [29]. Based on the quasi-Newton search method [30] by the software of Origin 8.5, the Burgers model and the Singh–Mitchell model are used to fit the creep data to obtain the creep parameters. The comparison among the Burgers model’s predictions of creep curves, the Singh–Mitchell model’s predictions of creep curves, and the experimental creep results under different confining pressures is shown in Figure 7. The relevant parameters of the Burgers creep model and the Singh–Mitchell model identified from the data processing are shown in Tables 3 and 4. It is observed that both the models can capture the creep behavior of the Bayer red mud, but the Burgers model results are consistent with the experimental data, and the model can better describe the typical creep behavior under the stress less than a certain threshold.

4. Damage Evolution Equation and Improved Burgers Creep Damage Model

4.1. Damage Evolution

According to the former test results, it can be obtained that if the applied load is much higher, the structure of the soil sample begins to destruct and the creep strain of the samples increases rapidly in the accelerated creep stage and fails eventually. Kachanov [31] suggested that this increase in the strain rate can be described by the introduction of a damage variable into the constitutive equation. The concept of an effective stress proposed by Kachanov [32] has been used to formulate constitutive equations for damaged materials [33]. From the test results, we assume that the damage evolution begins at the steady creep stage. So, the evolution equation of the damage variable can be expressed as [10]where and are creep strain and damage factor, respectively; while is the damage initial strain, which can be obtained at the starting point of the steady creep stage.

According to the whole creep curves (Figure 3), an exponential equation (4) was used to describe the strain of . The fitting test results are shown in Figure 8 when are 4.13%, 5.91%, and 6.28%, respectively. And the squares of the fitting correlation coefficient (R2) are 0.995, 0.983, and 0.946, respectively, indicating that the exponential equation (4) can well describe the steady creep and accelerated stages of the Bayer red mud samples.

By substituting (4) into (3), we can construct the soil damage evolution constitutive model:where and are the parameters controlling the damage evolution with time, which are related to the stress levels. is the creep time and is the unit time, which value is 1. The relationship between the damage evolution and creep time, obtained by fitting the test results, is shown in Figure 9; the parameters of the damage constitutive model are listed in Table 5.

4.2. Improved Burgers Creep Damage Model

The viscous coefficient will increase with the effect of low stress and decrease when the stress that exceeds the long-term ultimate strength [34]. According to the above test results, a new nonlinear viscoplasticity model was presented based on the creep damage model represented by (5). Also, in series with the Burgers creep model, a new improved Burgers creep damage model (Figure 10) was proposed, which can accurately describe the properties of the BRM during the instantaneous creep, decay creep, steady creep, and accelerating creep stages, to explain the evolution law of the damage characteristics over time.

If a series connection is made for each creep body in Figure 10, then

Based on (16), the creep equation of the improved Burgers damage model l under the effect of constant compression stress iswhere is the long-term strength which is the threshold of the damage and is the original viscosity coefficient.

Test data of artificially frozen soil that is reproduced from [35] was used to validate and analyze the applicability of the improved Burgers damage model, as shown in Figure 11. The creep parameters of this soil are shown in Table 6. It can be seen clearly that the creep experimental results of the Bayer red mud agree very well with the numerical prediction using the improved Burgers creep damage model, and square of the correlation coefficient (R2) is 0.996, indicating that the improved Burgers creep damage model has good applicability.

4.3. Parameter Identification of Improved Burgers Creep Model

In order to determine creep mechanical parameters of the improved Burgers creep model at different deviatoric stresses, an iteration procedure was used based on the quasi-Newton search method [30]. The relevant parameters of the improved Burgers creep damage model were identified from data processing, as shown in Table 7, and the calculated results of the creep curves and the tested ones are shown in Figure 12. From Figure 12, it is found that the calculated results of the proposed model are in good agreement with the tested results under these three deviatoric stress (591 kPa, 684 kPa, and 849 kPa). The correlation coefficient squares (R2) of the three curves are 0.995, 0.996, and 0.996, respectively, indicating that the prediction precision of the proposed model here is high in the simulating properties of the Bayer red mud.

5. Conclusions

The aim of this research is to lay a foundation for the evaluation and design processes in the Bayer red mud in the Guizhou Aluminum Factory red mud disposal field. A series of triaxial drained creep tests were conducted under different confining and deviatoric stresses. The test results indicate that the Bayer red mud has two creep stages under lower deviatoric stresses, namely, the attenuation creep stage and the steady creep stage; while in high deviatoric stress level, the accelerated creep stage with less instant elastic deformation and attenuation creep strain appears. The main failure mechanism of the Bayer red mud is plastic shear, accompanied by a significant compression and ductile dilatancy.

Based on the tested results, the creep parameters of the Burgers creep model and Singh–Mitchell creep model were determined through the curve fitting of the measured data. The results demonstrate a high precision of the Burgers creep model in prediction of the creep curve under certain deviatoric stress level, compared with the Singh–Mitchell creep model.

A new damage evolution constitutive equation of the Bayer red mud was constructed according to the creep strain of steady creep and accelerating creep stages and combined with the Burgers creep model, and a new improved Burgers creep damage model was proposed, which parameters were also analyzed in detail. The improved Burgers creep damage model which has been verified by the conformity of the result of the experiment illustrates that the model can accurately describe the properties of the BRM during the instant elastic strain, attenuation creep, steady creep, and accelerating creep stages.

Conflicts of Interest

The authors declare that there are no conflicts of interest regarding the publication of this paper.

Acknowledgments

This study was partially supported by the National Natural Science Foundation of China (Grant no. 41302223), Science and Technology Plan Projects of Chongqing Administration of Land, Resources and Housing (KJ-2015047), Chongqing No. 3 Colleges and Universities Youth Backbone Teachers Funding Plans and Chongqing Research Program of Basic Research and Frontier Technology (cstc2016jcyjA0074, cstc2016jcyjA0933, and cstc2015jcyjA90012), and Scientific and Technological Research Program of Chongqing Municipal Education Commission (KJ1713327 and KJ1600532). The authors also thank Professor Yang Mijia, Department of Civil and Environmental Engineering, North Dakota State University, for his valuable suggestions and English improvement of this manuscript.