Abstract
An unsaturated soil is a three-phase material that is ubiquitous on the earth’s surface. The fully saturated and completely dry states are just two limiting conditions of an unsaturated soil. The state and properties of unsaturated soils can change significantly with external loads, weather conditions and groundwater level. Proper modelling of the state-dependent behaviour of unsaturated soils is crucial for analysing the performance of almost all civil engineering structures. So far, there are many unsaturated soil models and several relevant review papers in the literature. None of the existing review papers, however, focused on the state dependency of unsaturated soil behaviour. Moreover, some aspects of soil behaviour have not been reviewed, including small strain stiffness, dilatancy and stress-dependence of water retention curve. In the current review paper, the state dependency of unsaturated soil behaviour is reviewed, with a particular attention to the three missing parts. The review is carried out in a unified and relatively simple constitutive framework, which adopts a three-by-three compliance matrix to link incremental volumetric strain, deviator strain and degree of saturation to incremental mean net stress, deviator stress and suction. All of the nine variables in the proposed three-by-three compliance matrix have clear physical meanings and can be measured through compression, shearing and water retention tests. Theoretical models based on other constitutive stress variables can be also converted to this framework by matrix transformation.
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1 Introduction
Soil is a porous medium in which the pores between solid grains play an important role in governing its mechanical and hydraulic behaviour. The pores can be filled up with liquid and/or gas. Many classical theories of soil mechanics have been developed based on the assumptions that the pores are filled up with either liquid (i.e. fully saturated) or gas (i.e. completely dry), e.g. Terzaghi’s theory of one-dimensional consolidation, Rankine’s theory of earth pressure, among others. However, fully saturated and completely dry states are only two limiting conditions of soils [57]. In many geotechnical engineering applications, the degree of saturation lies between zero and one. Many phenomena observed in unsaturated soils cannot be explained adequately by the classical theories of soil mechanics, leading to the emergence of unsaturated soil mechanics over the past few decades (e.g. [1, 11, 22, 29, 46, 57, 66, 68, 79, 84, 92, 97, 100, 104, 107]).
Since the pioneering work in the 1950s and 1960s to develop different laboratory techniques to control suction and to test unsaturated soils [8, 17, 35, 55, 67], the contributions of suction to the mechanical and hydraulic behaviour of unsaturated soils have been better understood. The theoretical development of constitutive models for unsaturated soils lags behind the corresponding laboratory studies. So far, several reviews on the constitutive models for unsaturated soils are available in the literature [19, 32, 80, 82, 91]. These reviews discussed some of the important aspects of constitutive modelling of unsaturated soils, such as constitutive variables, wetting-induced collapse, compressibility, yielding, shear strength, failure criteria, water retention behaviour and hydromechanical coupling. The different aspects of unsaturated soil behaviour were not reviewed and discussed in a unified theoretical framework. Moreover, some issues were relatively less discussed, including state-dependent small strain stiffness, dilation and stress-dependent water retention behaviour.
In this study, a unified and relatively simple constitutive framework is presented for unsaturated soils. This framework adopts a three-by-three compliance matrix to link volumetric strain, deviator strain and incremental degree of saturation to incremental mean net stress, deviator stress and suction. All of the nine variables in the compliance matrix have clear physical meanings, which are illustrated throughout by various unsaturated soil tests. Based on this constitutive framework, the modelling of state-dependent behaviour of unsaturated soils is reviewed in a systematic approach.
2 A unified and simple framework for the state-dependent behaviour of unsaturated soils
In the constitutive modelling of unsaturated soils, one of the key issues is the choice of proper constitutive variables. Many different constitutive stress variables have been proposed in the literature to model the mechanical behaviour of unsaturated soils (e.g. [21, 77, 92]). Gens et al. [32] reviewed the different variables adopted in existing elastoplastic models. They believed that “Different constitutive stresses stand on an equal footing and the matter of adopting one or the other must be decided using the criteria of convenience”. In the unified and simple framework of this current review, net stress and matric suction are used for simplicity. Net stress is defined as the difference between total stress (σ) and pore air pressure (ua). Matric suction is calculated as the difference between pore air pressure and pore water pressure (uw), and it is referred to as suction for simplicity in the following paragraphs.
By adopting net stress and suction, the constitutive formulations for an unsaturated soil can be expressed in a general incremental form as follows:
where dεv is the increment in volumetric strain; dεq is the increment in deviator strain; dSr is the increment in the degree of saturation; dp is the increment in the mean net stress; dq is the increment in the deviator stress; ds is the increment in suction; and Iij (i = 1, 2 and 3; j = 1, 2 and 3) are state-dependent variables for a given soil. According to Eq. (1), the variables I11, I21, and I31 in the compliance matrix describe the behaviour of unsaturated soils during compression, including the development of volumetric strain, deviator strain and the change in degree of saturation. Similarly, I12, I22, and I32 describe the hydromechanical behaviour during the shearing process, while I13, I23 and I33 capture the behaviour of soil subjected to drying/wetting. All nine variables can be calibrated through suction- and stress-controlled tests on unsaturated soils. These variables can be also determined by using constitutive formulations for the compression, shearing and water retention behaviour of unsaturated soils, as discussed later. Equation (1) is still valid when soil is saturated, which is considered as a special case of unsaturated soil with Sr = 100%. At this special condition, the net stress should be replaced by the Terzaghi’s effective stress and the values of I13, I23, I31, I32 and I33 become zero.
Some unsaturated soil models in the literature are based on other constitutive stress variables rather than net stress and suction. These models can be also converted to Eq. (1) by matrix transformation. In any constitutive model, the relationship between strain increment \(\left\{ {{\text{d}}{\hat{\boldsymbol{\upvarepsilon }}}} \right\}\) and stress increment \(\left\{ {{\text{d}}{\hat{\boldsymbol{\upsigma }}}^{*} } \right\}\) can be described using a general formulation:
where \(\left[ {{\mathbf{C}}^{*} } \right]\) is the compliance matrix; \(\left\{{\hat{\boldsymbol{\upsigma }}}^{*}\right\}\) and \(\left\{{\hat{\boldsymbol{\upvarepsilon }}}\right\}\) are the constitutive stress and strain variables, respectively. For the discussion here, the strain variables \(\left\{{\hat{\boldsymbol{\upvarepsilon }}}\right\}\) are defined as \(\left\{ {\varepsilon_{v} ,\varepsilon_{q} , S_{r} } \right\}\) in all models. To obtain the relationship between \(\left[ {{\mathbf{C}}^{\varvec{*}} } \right]\) and \(\left[ {\mathbf{C}} \right]\) [i.e. the compliance matrix defined in Eq. (1)], \(\left\{ {{\text{d}}{\hat{\boldsymbol{\upsigma }}}^{*} } \right\}\) can be expressed as [10]
where \(\left\{ {{\text{d}}{\hat{\boldsymbol{\upsigma }}}} \right\}\) is the incremental form of constitutive stress variables \(\left\{ {{\text{dp}},{\text{d}}q,{\text{d}}s} \right\}\) used in Eq. (1); \(\left[ {\mathbf{T}_{{\mathbf{a}}} } \right]\) and \(\left[ {\mathbf{T}_{{\mathbf{b}}} } \right]\) are two matrixes and their values depend on the constitutive stress variables in the constitutive model investigated. Substituting Eqs. (1) and (3) into Eq. (2), it is obtained that
where \(\left[ {\mathbf{I}} \right]\) is a unit matrix. It should be noted that Eqs. (2) and (4) are general equations. They can be used to convert any constitutive model to Eq. (1). When different models are used, however, \(\left[ {\mathbf{T}_{{\mathbf{a}}} } \right]\) and \(\left[ {\mathbf{T}_{{\mathbf{b}}} } \right]\) take different forms. For example, the model of Wheeler et al. [92] uses the following three constitutive stress variables: \(\left\{{\hat{\boldsymbol{\upsigma }}}^{*}\right\} = \left\{ {p^{*} ,q,s^{*} } \right\}\), where the Bishop’s stress \(p^{*}\) and modified suction \(s^{*}\) are defined as \(\left( {p + sS_{\text{r}} } \right)\) and \(\left( {ns} \right)\), respectively. From the incremental form of \(\left\{{\hat{\boldsymbol{\upsigma }}}^{*}\right\}\), it can be readily derived that:
Another example is the model of Khalili et al. [39], which adopts the following constitutive stress variables: \(\left\{{\hat{\boldsymbol{\upsigma }}}^{*}\right\} = \left\{ {p_{\text{k}}^{*} ,q,s} \right\}\). \(p_{\text{k}}^{*}\) is the mean effective stress proposed by Khalili and Khabbaz [40]: \(\left( {p + \chi s} \right)\), where \(\chi\) is defined as follow:
where \(s_{\text{e}}\) is the suction value marking the transition between saturated and unsaturated states. \(\left[ {{\mathbf{T}}_{{\mathbf{a}}} } \right]\) and \(\left[ {{\mathbf{T}}_{{\mathbf{b}}} } \right]\) are calculated using the following two equations:
Lu et al. [47] proposed a new effective stress formulation \(\left( {\sigma - \sigma^{s} } \right)\) based on the concept of suction stress \(\sigma^{s}\) [48]. For constitutive models based on this effective stress formulation, \(\left[ {{\mathbf{T}}_{{\mathbf{a}}} } \right]\) and \(\left[ {{\mathbf{T}}_{{\mathbf{b}}} } \right]\) are calculated using the following two equations:
where Srr is the residual degree of saturation. The above three examples clearly show that all constitutive models can be converted to Eq. (1) by matrix transformation. Within this unified framework [i.e. Eq. (1)], the constitutive formulations for unsaturated soil behaviour are reviewed in the following paragraphs.
2.1 Determination of the variable I11
The variable I11 in Eq. (1) can be determined using the following equation:
According to Eq. (12), the variable I11 is the ratio of incremental volumetric strain to incremental mean net stress when q and s are constant. The value of this variable corresponds to soil volumetric compressibility, which can be measured through compression tests at constant-q and s condition. For example, Ng and Yung [64] carried out a series of suction-controlled isotropic compression tests on a compacted completely decomposed tuff (CDT, a silt). Four suction levels, 0, 50, 100 and 200 kPa, were considered and applied. Figure 1 shows the measured relationship between volumetric strain and mean net stress. One of the key findings was that the measured compressibility decreased with increasing suction in the stress and suction ranges considered, due to the stiffening effects of water meniscus. This observation implies that the value of I11 is lower at a higher suction. In contrast, some other soils have been found to be more compressible at a higher suction (e.g. Wheeler and Sivakumar [93]), probably because drying a soil would result in more compressible macro-pores [26, 104]. These differing trends suggest that to obtain the value of I11 accurately, suction-controlled compression tests should be carried out.
To model the volume change behaviour of unsaturated soils during loading and unloading process, various formulations have been reported in the literature. They were compared and discussed by Sheng [80] in detail. To illustrate the relationship between volume change behaviour and Eq. (1), this current study adopts the following equation as an example:
where e is the void ratio; αp(s) is the compressibility. It should be noted that although Eq. (1) does not explicitly consider yield surface, the values of variables such as I11 are affected by it. For unloading/reloading inside the yield surface and loading on the yield surface, αp(s) are equal to κ(s) and λ(s), respectively. Equation (13) assumes that the compression behaviour of an unsaturated soil can be described by a straight line in the e-ln p plane. This equation has been widely used in elastoplastic models (e.g. Chiu and Ng [15]), mainly because it is simple but effective in modelling the volume change behaviour of unsaturated soils.
Based on Eqs. (12) and (13), the following equation can be derived:
Equation (14) clearly reveals that the value of I11 is affected by net stress, suction and the void ratio. Therefore, the state-dependent compressibility is considered by this equation and hence by Eq. (1).
2.2 Determination of the variable I12
According to Eq. (1), the variable I12 is described by
It is the ratio of incremental volumetric strain to incremental deviator stress when p and s are constant. Volumetric strain can be induced by dilation/contraction during the shearing process, which is irreversible (i.e. the elastic volumetric strain is equal to zero). Hence,
where G0 is the elastic shear modulus; and Dq is the dilatancy associated with the plastic mechanism of shearing. From Eqs. (15) and (16), the following equation can be derived:
where ∂εq/∂q is defined as I22. Equation (17) suggests that the value of I12 is governed by three variables, I22, G0 and Dq. The variable Dq is discussed here, whereas detailed discussion on I22 and G0 are given later.
Ng and Chiu [53, 54] carried out two series of triaxial tests on compacted decomposed volcanic (CDV, a silty clay) and compacted decomposed granitic (CDG, a sand silt) soils. Triaxial undrained and constant water content tests were conducted on saturated and unsaturated specimens, respectively. They found that a higher stress ratio is required to mobilise the same amount of dilatancy when the suction is higher. A similar behaviour was found for the CDG soil. Ng and Zhou [69] reported a series of suction-controlled direct shear tests on another coarse-grained CDG soil. For the five tested specimens, specimens subjected to suctions of 200 and 400 kPa exhibited brittle stress–strain behaviour, while the other three specimens at suctions of 0, 10 and 50 kPa exhibited ductile behaviour. All four unsaturated specimens exhibited a phase transformation from positive to negative dilatancy with increasing stress ratio. It was also observed that the stress ratio corresponding to a maximum negative dilatancy increased with suction. Besides, the maximum negative dilatancy decreased (i.e. the soil became more dilative) with increasing suction. Through microscopic analysis, Ng et al. [61] have illustrated that suction-induced dilatancy is not governed by a change in void ratio, but depends on suction effects on the micro and macro-pores. Based on the above experimental results, it is evident that the dilatancy of unsaturated soils depends on suction. As a consequence, the formulations developed for saturated soils should be modified for unsaturated soils.
Dilatancy equation (or plastic flow rule) is one of the essential components of a constitutive model for unsaturated soils. Alonso et al. [1] has presented one of the first elastoplastic models for unsaturated soils. This model is commonly referred to as the Barcelona basic model (BBM), which adopts the Modified Cam Clay model (MCCM) as the reference model at the saturated state. Hence, the yield curve is an ellipse at constant suction associated with a preconsolidation stress p0 (or yield stress), which increases with increasing suction. The relationship between p0 and suction is referred to as the loading-collapse (LC) curve in the BBM. It should be noted that the shape of LC curve depends on the isotropic compression lines at different values of suction. In the three-dimensional stress and suction space, the yield surface is a series of ellipse. As the associated flow rule is used in the MCCM, the plastic potential function is the same as the yield curve. However, the MCCM over-predicts the volumetric deformation at K0 condition [31]. Thus, a non-associated flow rule is adopted in the BBM [see Eq. (A1) in Table 1]. A parameter α is used such that no lateral strain is predicted from equation (A1) under K0 condition. ps is a parameter describing the contribution of suction on the tensile strength of unsaturated soil. In Eq. (A1) parameters p0 and ps are functions of suction. Thus, the contribution of suction on the dilatancy is taken into account by these two parameters. If the stress states of a soil lie on a yield curve corresponding to a suction s1 for a given stress ratio η, the same stress states of soil will lie inside a yield curve corresponding to a higher suction s2 (s2 > s1). In other words, the soil subjected to suction s2 is modelled as an overconsolidated soil in the BMM. The elasticity and Eq. (A1) are used to predict the shear-induced volume change when the stress states lie inside and on the current yield surface, respectively. Besides, a higher stress is required to reach the zero dilatancy at the critical state for soil subjected to a higher suction (i.e. a higher ps).
Due to the inherent shortcomings of the MCCM, the BBM and the other models derived from the MCCM also cannot predict satisfactorily the shear-induced volumetric behaviour of unsaturated granular and overconsolidated soils. Two different approaches can be identified to address this limitation. In the first approach, different dilatancy equations for saturated sand have been modified for unsaturated soils [2, 9, 15, 18]. In the second approach, new constitutive models have been developed based on the bounding surface plasticity [52] and sub-loading surface plasticity [49, 101] to model the dilatancy of unsaturated overconsolidated soil. Cui and Delage [18] used the Nova-Wood equation [see Eq. (A2) in Table 1], where ηr is the stress ratio at zero dilatancy. It should be noted that ηr corresponds to not only the stress ratio at the critical state, but also the stress ratio at the phase transformation state, i.e. it changes from contractive to dilative behavior for an overconsolidated soil. ηr is dependent on both suction and stress. Two of the key limitations of their equation are that: (1) a finite dilatancy (d = ηr/μ) is predicted for isotropic compression (η = 0); and (2) the effects of density on dilatancy are not considered.
To improve the modelling of unsaturated soil dilatancy, Chiu and Ng [15] extended the framework of state-dependent dilatancy [45] from saturated to unsaturated conditions. In their formulation [i.e. denoted as Eq. (A3) in Table 1], d1(s) is a model parameter that is a function of suction, and ψ is the state parameter defined as the difference between the current void ratio and the void ratio at the critical state for a given mean stress [6]. The state parameter describes the density and stress level of soils. Based on the experimental evidences [53, 54], Chiu and Ng [15] revealed that ψ is a function of density, mean net stress and suction for unsaturated soils. They illustrated that by using a single set of model parameters, Eq. (A3) can capture the shearing-induced volume changes of unsaturated CDV and CDG soils with different initial densities and confining pressures well. Russell and Khalili [77] also used ψ in the formulation of dilatancy for a boundary surface plasticity model as depicted in Eq. (A4). The model parameters kd may vary for different soils, which would be assumed as a material constant if high precision simulations are not required. When kd becomes zero, the dilatancy equation of Cam Clay is recovered. Chávez and Alonso [9] have also adopted a similar state-dependent dilatancy framework [90] in their constitutive model. The dilatancy angle φm is expressed as Eq. (A5) in Table 1, where ϕm = mobilised friction angle; ϕcr = friction angle at the critical state; e and ecr = current void ratio and void ratio at the critical state for a given mean stress and β = model parameter. In the equation, ϕcr and ecr both depend on suction. A major assumption of the three models proposed in Chiu and Ng [15], Russell and Khalili [77] and Chávez and Alonso [9] is that the tested materials can reach the critical state after large shear deformation for the range of suction studied. The triaxial test results of compacted DV and DG soils can support such hypothesis (Ng and Chiu [53, 54]). On the other hand, the experimental results of compacted shale and limestone gravels did not reach the critical state after shearing to large deformation [2, 9]. Thus, Alonso et al. [2] has proposed an alternative parameter, the plastic work input (Wp) to describe the dilatancy. It is found that Eq. (A6) in Table 1 gives a good fit to the measured dilatancy for the suction-controlled triaxial tests conducted on the compacted limestone gravel. In the equation, ηWp/p is a dimensionless parameter. The effect of confining pressure p on the constraint of dilatancy is considered in the parameter. Besides, η is added such that Eq. (A6) can predict an infinite value of dilatancy at the isotropic compression, i.e. η = 0. Parameters a and b are two fitting variables that are functions of total suction. In the second approach, some recent constitutive models still adopted the yield function and plastic potential of MCCM, but were developed based on the bounding surface plasticity [52] and sub-loading surface plasticity [101] to model the dilatancy of unsaturated overconsolidated soil. Morvan et al. [52] extended Bardet’s boundary surface model [5] for saturated soil to unsaturated soil. In this series of constitutive models, a limit state line (LSL) is defined which represents an upper bound for the admissible stress domain. The hardening modulus is formulated as a function of the stress ratio of LSL, which influences the amplitude of dilatancy and post-peak softening. Zhou and Sheng [101] adopted the framework of sub-loading surface plasticity to model the effect of initial density on the mechanical behaviour of unsaturated soil. In this model, an unified hardening (UH) parameter proposed by Yao et al. [98] was used to model the hardening of the yield surface. UH parameter depends on the similarity ratio (R) between the sub-loading surface and the reference yield surface. If the soil is normally consolidated and overconsolidated, R will be equal to 1 and less than 1, respectively. The magnitude of dilatancy and post-peak softening depend on R. Recently, Luo et al. [49] proposed a new function for the UH parameter including a state variable that describes the degree of overconsolidation under the current void ratio with reference to the anisotropic consolidation line. This state variable increases with increasing degree of overconsolidation, which controls the amount of strain softening and shear-induced dilatancy.
Figure 2 shows the measured and calculated values of dilatancy during shearing. The measurements were obtained from two triaxial tests on a gravelly sand at suctions of 0 and 40 kPa [53]. Two specimens were consolidated to the same confining pressure and similar void ratio but different suction before shearing. Theoretical results were calculated using Eqs. (A1)–(A3) and (A5) in Table 1. The value of model parameters is summarised in Table 2. It is clear that Eq. (A1) [1] overestimates the dilatancy of the gravelly sand, as expected. This is mainly because the model of Alonso et al. [1] was developed based on the modified Cam Clay model, which was originally proposed based on the test results of reconstituted clay. The theoretical results calculated using Eqs. (A2)–(A3) and (A5) are generally consistent with the trend of experimental data. All of these three equations were modified from the Rowe’s dilatancy equation. Equation (A2) cannot take into account of density effects. Thus, a new set of parameters have to be calibrated for different densities. Khalili et al. [39] also adopted Eq. (A2) in a coupled flow deformation model, but formulated in an effective stress using the χ parameter as presented in Eq. (7). The merit of using effective stress approach is the parameters are independent of suction. On the contrary, both Eqs. A3 [15] and A5 [9] consider the effects of density. For modelling the effect of state, (A3) and (A5) adopt the variables (e − ec) and (e/ec), respectively, where e and ec are the current void ratio and void ratio at critical state, respectively. It seems that Eq. (A3) gives better prediction of the experimental results, particularly in the range of stress ratio below 0.6. On the other hand, all these equations do not explicitly consider the influence of suction path. Some researchers found that at the same suction, the values of shearing-induced dilatancy are obliviously different along the drying and wetting paths [10, 12, 33]. Effects of suction path on soil dilatancy need more experimental and theoretical studies in the future.
One of the existing formulations for dilatancy can be used to determine I12. Taking Eq. (A3) as an example here, based on Eqs. (15) through (17), the following equation can be derived:
According to Eq. (18), the value of I12 is affected by suction. Therefore, the state-dependent dilatancy of unsaturated soils is considered by this equation and hence by Eq. (1).
2.3 Determination of the variable I13
The variable I13 in Eq. (1) can be calculated by
Equation (19) denotes that I13 is a ratio of incremental volumetric strain to incremental suction when p and q are constant. This variable can describe shrinkage and swelling of unsaturated soils subjected to drying and wetting. Figure 3 shows the experimental results of drying-induced shrinkage reported by Chiu and Ng [14]. The test soil was a compacted CDT, classified as a silt. Three different mean net stresses, 0, 40 and 80 kPa, were applied and maintained constant during the drying process. It is evident that the void ratio reduced nonlinearly with an increase in suction. More importantly, the reduction rate was affected by stress, suggesting that I13 is a function of stress.
To model the suction-induced volume changes of unsaturated soils, several formulations have been reported in the literature, as reviewed Sheng [80]. Among these formulations, the equation of Sheng et al. [81] consider of the influence of mean net stress on the shrinkage/swelling of unsaturated soils. It is used to show the interpretations of suction-induced volume change in the unified framework [i.e. Eq. (1)]:
where αs is the compressibility of unsaturated soils upon a change in suction. The value of αs strongly depends on the suction history, which governs the location of yield surface. Four different cases are considered: (1) When the soil is subjected to drying and the current suction is equal to the maximum suction in the suction history (i.e. on the yield surface), αs is equal to the shrinkage index λs; (2) when the soil is subjected to drying but the current suction is below the maximum suction in the suction history (i.e. within the yield surface), αs is equal to the swelling index κs; (3) when the soil is subjected to wetting and the soil is over-consolidated (i.e. soil state within the yield surface), αs is equal to the swelling index κs; and (4) when the soil is subjected to wetting and the soil is normally consolidated (i.e. soil state on the yield surface), wetting collapse occurs and αs is equal to the accumulation rate of plastic strain.
Based on Eqs. (19) and (20), the following equation can be derived:
A key feature of Eq. (20) is that the suction-induced volume changes of unsaturated soils are dependent on mean net stress. The coupling effects of hydromechanical behaviour are taken into account.
2.4 Determination of the variable I21
The variable I21 in Eq. (1) can be determined using the following equation:
According to Eq. (22), the variable I21 is the ratio of incremental deviator strain to incremental mean net stress when q and s are constant. Moreover, the incremental deviator strain can be calculated using
where Dp is the dilatancy associated with the plastic mechanism of compression. Dp of unsaturated soils has been studied previously through compression tests under constant ratio of suction to stress. Figure 4 shows the experimental results of Dp of a compacted silt at the suctions of 200, 400, 600 and 1500 kPa [18]. During the compression process, the stress ratio was maintained at 1. Dp was clearly affected by soil suction, particularly at mean net stresses below 300 kPa. To model the suction-dependent Dp, Chiu and Ng [15] proposed the following equation:
Based on Eqs. (22) through (24), the following equation can be derived:
It can be seen that the value of I21 is affected by suction. Therefore, the state-dependent dilatancy of unsaturated soils is considered by Eq. (25) and hence by Eq. (1).
2.5 Determination of the variable I22
The variable I22 in Eq. (1) can be determined using
According to Eq. (26), I22 is the ratio of incremental deviator strain to incremental deviator stress when p and s are constant. This variable is closely related to the tangent shear modulus G (i.e. I22 = 1/G), which has been studied by many researchers [3, 16]. It is well-recognised that G of soil depends one strain, as shown in Fig. 5. At very small strains below 0.001%, shear modulus is almost constant and it is denoted by G0. The value is widely used for different purposes, such as the calculation of ground movement under dynamic loads. At small strains between 0.001 to 0.01%, shear modulus reduces significantly with an increase in strain. At the working condition of many civil engineering structures in relatively medium and dense/stiff soils, typical strains encountered fall within the small strain range [4, 50, 65]. In this following section, the formulation of G0 and the strain dependence of shear modulus are discussed. A formulation for I22 is then derived.
2.5.1 Initial shear modulus G0 at very small strains
Through a series of resonant column tests on unsaturated sand, Wu et al. [96] found that as the degree of saturation increased, G0 first increased and then decreased. The maximum value occurred at a degree of saturation of about 20%. A similar relationship between G0 and the degree of saturation was observed by Qian et al. [74]. In these two studies, soil suction was not controlled/measured and soil specimens were compacted at different water contents, resulting in different soil microstructures and hence these specimens could not be qualified as ‘identical’ [57]. In more recent studies, soil specimens were generally prepared at the same water content and density to obtain the same microstructure. After preparation, the soil specimens were subjected to drying and wetting in suction-controlled apparatus prior to the determination of G0. Using a suction-controlled resonant column, Mancuso et al. [51] investigated G0 of a compacted silty sand subjected to isotropic compression at constant suction. They found that G0 increased with suction. Similar findings from different unsaturated soils have also been reported by many researchers [36, 64, 78, 89]. Apart from suction, the effects of suction history on anisotropic G0 were identified by Ng et al. [63], as shown in Fig. 6. They applied a drying and wetting cycle to unsaturated silt at constant net stress. It was found that at the same suction, G0 was higher along the wetting path than along the drying path. They revealed that apart from the current suction, the suction path also affected the stiffness of unsaturated soils. Their finding was confirmed by Khosravi and Mccartney [41] who tested another compacted silt.
Some semi-empirical equations have been reported in the literature to describe G0 of unsaturated soil. In this review, these equations are classified into four types based on their constitutive variables. The first type of G0 models, such as Eqs. (B1) through (B3) in Table 3, adopts net stress suction as constitutive variables. One example is Eq. (B1) proposed by Leong et al. [43]. This equation considered the influence of stress and suction, but it ignored the influence of stress path and suction path. As a consequence, effects of degree of saturation and density on G0 cannot be captured. More importantly, this equation is only applicable for isotropic condition, including isotropic soil fabric and isotropic stress state. Ng and Yung [64] proposed Eq. (B2) to describe the anisotropic G0 of unsaturated soil. According to Eq. (B2), the anisotropic G0 of unsaturated soils is affected by the soil fabric, void ratio, stress and suction. In addition, Sawangsuriya et al. [78] proposed Eq. (B3) for the G0 of unsaturated soil. Different from Eqs. (B1) and (B2), this equation uses multiplication rather than addition. Hence, suction-induced variation of G0 is independent of stress in Eq. (B3). In other words, the effects of stress and suction on G0 are assumed to be independent. On the other hand, it should be pointed out that the first type of G0 models predicts a unique relationship between G0 and suction when stress and void ratio are constant. Effects of suction history are not captured by the first type of G0 models. To improve these models, a possible approach is to incorporate degree of saturation or water content.
The second type of G0 models, such as Eqs. (B4) and (B5) in Table 3, is based on effective stress of unsaturated soil. In Equation (B4) proposed by Sawangsuriya et al. [78], the effective stress of unsaturated soil is taken as (σ − ua) + Sκr (ua − uw). The typical values of parameter κ were found to range from 1 to 3. At a given suction, the calculated G0 is therefore smaller along the wetting path than that along the drying path. This predicted tread is different from experimental results reported by many researchers (see Fig. 6). Recently, Pagano et al. [72] developed a microscale-based model [i.e. Eq. (B5)] for G0 in unsaturated granular geomaterials. In their formulation, σi is the intergranular stress of the unsaturated packing; σb i and σm i are the intergranular stresses in the regions of bulk water and meniscus water, respectively. It is conceptually good to differentiate intergranular stresses in bulk water and meniscus water, considering these two types water are very different in changing intergranular stresses [92]. This microscopic approach, however, leads to great difficulty in model calibration.
To properly consider the effects of suction history on G0, some recent models used two constitutive variables, at least one of which is a function of degree of saturation. Equations (B6) through (B9) in Table 3 all belong to this type of G0 model [7, 41, 95]. Equation (B6), which was proposed by Sawangsuriya et al. [78], has six model parameters (A, K, b, n, λ and κ). A lot of test results are required to calibrate all of these parameters. Similarly, Eq. (B7) [7] requires the information of NCLs to compute OCR of a soil, apart from five models parameters (A, n, m, a and b). Wong et al. [95] developed a semi-empirical equation based on the effective stress formulation of Khalili and Khabbaz [40]. Compared with the model of Biglari et al. [7], the model of Wong et al. [95] adopts a void ratio function to consider effects of stress history, instead of incorporating both OCR and void ratio. Consequently, less model parameters are required in the model of Wong et al. [95]. Wong et al. [95] applied the three above models to predict G0 of different soils along various stress paths. They found that along the drying and isotropic compression processes, the predictions using these three models are quite consistent with measured data. Furthermore, equations of Biglari et al. [7] and Wong et al. [95] are able to capture the variation of G0 along cycles of drying and wetting. Dong et al. [20] proposed the G0 model based on effective stress and effective degree of saturation. This model is qualitatively similar to that of Wong et al. [95].
The last type of G0 models includes Eqs. (B10) through (B12) in Table 3. These models use a reference G0 at a specific moisture condition (generally the fully saturated or completely dry condition), and calculate the variation of G0 with soil moisture. Hence, these models do not require an explicit consideration of stress state variables. Equation (B10), which was proposed by Wu et al. [96], used the function H(Sr) to calculate the variation of G0 with soil moisture condition. Mancuso et al. [51] proposed Eq. (B11), in which parameter β controls the increase rate of G0 with increasing suction; r is the ratio of shear modulus at a very high suction and (G0)s*. Han and Vanapalli [34] proposed Eq. (B12) to calculate the variation of G0 with increasing suction and degree of saturation. To improve the model prediction, two reference values of G0 are used, including the fully saturated state and an unsaturated state. This type of models is simple, but they may not be able to capture some important aspects of soil stiffness. For example, by using a scalar (water content/degree of saturation), suction effects on stiffness anisotropy (see Fig. 6) cannot be simulated. In addition, the hysteresis of stiffness during drying and wetting cannot be captured.
As discussed above, theoretical formulations for G0 in Table 3 may be classified into four types based on the constitutive stress variables. One equation from each type, including Eqs. (B2), (B4), (B9) and (B12), is selected to simulate the very small strain behaviour of an unsaturated silt. The very small strain moduli G0 of this soil were measured by Ng and Yung [64] and Ng et al. [63] along two different stress paths, including constant-s compression and constant-p drying and wetting. The measured and calculated results are compared in Fig. 7 and parameter values are shown in Table 4. To evaluate the performance of each equation, the coefficient of determination (R2) is calculated and shown in the figure. During the constant-s compression, Eq. (B2) [64] gives the best prediction of G0, with R2 values of 0.97. This is mainly because Eq. (B2) uses the two independent stress state variables. The increase rates of G0 with increasing suction and stress can be well-simulated using two independent terms:\(\left[ {\left( {\sigma_{\text{i}} - u_{\text{a}} } \right)/p_{\text{atm}} \cdot \left( {\sigma_{\text{j}} - u_{\text{a}} } \right)/p_{\text{atm}} } \right]^{n}\) and \(\left( {1 + s/p_{\text{atm}} } \right)^{n}\). When Eq. (B4) [78] is used, however, there is an obvious discrepancy between measured and calculated results with R2 of 0.62. This problem is mainly because Eq. (B4) is based on a single constitutive stress variable, which is not sufficient to capture the influence of net stress, suction and degree of saturation in a unified formulation. During the constant-p drying and wetting, Eq. (B9) [20] gives the best prediction of experimental results (R2 = 0.89). This is because this equation properly considers at least two different effects of suction path: (a) altering the suction stress and hence effective stress proposed [47]; (b) affecting suction hardening [38]. Equation (B12) [34] gives the lowest value of R2 (i.e. 0.65). This is because at a given suction, the model predicts a higher G0 along the drying path, while the experimental results reveal that G0 is larger along the wetting path. In addition, Eq. (B2) [64] is not able to well-capture the variation of G0 during drying and wetting (R2 = 0.67), because this equation does not include Sr. In addition, during the constant-p drying and wetting, the values of R2 are less than 0.9 for all equations. Further studies are therefore required to improve the modelling of suction path on G0.
2.5.2 Reduction in shear modulus with increasing strain
To determine the stiffness strain relationship of a Singapore residual soil (clayey sand), Leong et al. [43] carried out a series of undrained triaxial compression tests. Ten specimens with different suctions were sheared at constant water content and constant confining stress. They observed that the shear modulus increased consistently with initial suction and confining stress. It should be noted that suction was not controlled during the isotropic compression and shearing process, and the reported degradation of shear stiffness was a function of deviator strain as well as varying with suction during shearing. Ng and Xu [62] carried out a series of suction-controlled constant mean net stress shear tests to investigate the effects of suction on the small strain behaviour of an unsaturated CDT. Suction was controlled using the axis-translation technique. After the specimens were equalised under the target mean net stress and target suction, they were sheared under constant mean net stress and constant suction. As shown in Fig. 8, the initial shear stiffness and stiffness degradation are affected by suction.
On the other hand, various semi-empirical equations have been proposed to model the degradation of shear modulus with strain based on experimental studies of saturated soils (see for example [71, 88, 99]). One example is the following hyperbolic equation proposed by Vardanega and Bolton [88]:
where G is the secant shear modulus at any deviator strain; εq is deviator strain; α is a curvature parameter that controls the degradation rate of shear modulus with strain; and εqe is the elastic threshold strain beyond which shear modulus decreases with increasing deviator strain. εqref is a characteristic reference strain, defined as the deviator strain at which secant shear modulus is reduced to 0.5G0. Parameter α is mainly affected by the soil type, while εqe and εqref depends on not only the soil type but also the soil state (for example, the void ratio and stress level) [88]. Equation (27) was originally developed by Vardanega and Bolton [88] for saturated soils. Zhou [105] illustrated that it can be used for unsaturated soils with a minor modification. In unsaturated soil, meniscus water increases the inter-particle normal force, which would stabilise the soil skeleton. Hence, the elastic threshold strain (εqe) in Eq. (27) is expected to increase when soil becomes desaturated.
2.5.3 Formulation for I22
According to Eqs. (26) and (27), it can be shown that the value of I22 depends on the current deviator strain. When it is lower than the elastic threshold strain, shear modulus is constant. Hence,
When the current deviator strain is above the elastic threshold value, the strain dependence of shear modulus should be considered. I22 is calculated using the following equation:
There are four parameters in Eqs. (28) and (29): C, n, k and α. The first three parameters can be obtained from stress and suction-controlled bender element and resonant column tests, while the last one can be determined through a constant-p shear test.
2.6 Determination of the variable I23
According to Eq. (1), the variable I23 is equal to
Equation (30) suggests that I23 is the ratio of incremental/decremental deviator strain to incremental/decremental suction when p and q are constant. Hence, the value of I23 can be calibrated using stress-controlled drying/wetting tests. Figure 9 shows the development of deviator strain of a compacted gravelly sand subjected to wetting [54]. This study considered four mean net stresses of 0, 50, 100 and 200 kPa, and applied a stress ratio of 1.4 in all tests. During the wetting process, the deviator strain accumulated at an increasing rate, because yielding had occurred when the wetting path reached the yield surface. Assuming that the wetting-induced deviator strain is essentially plastic (i.e. elastic strain is zero), the slope of deviator strain-suction relation is equal to I23.
It should be pointed out that in most drying/wetting tests reported in the literature, only volumetric strain was measured under an assumption of isotropic soil behaviour. Hence, experimental results of suction-induced deviator strain are very limited. If suction-induced elastic deviator strain is small and can be ignored, Eq. (30) suggests
where Ds is the dilatancy during drying/wetting. Ds generally take the value of Dq and Dp [see Eqs. (A3) and (15)], when suction-induced yielding occurs for the plastic mechanisms of shearing and compression, respectively. Based on Eqs. (20) and (31), the following equation is derived:
Equation (32) implies that I23 is a function of I13, αs and Ds, which can be all determined based on experimental results, as introduced and discussed previously. Hence, the value of I23 can be readily calculated in this alternative approach. No extra tests are required for calibrating I23.
2.7 Determination of the variable I31
The variable I31 in Eq. (1) can be determined by
According to Eq. (33), the variable I31 is the ratio of the incremental degree of saturation to incremental mean net stress when q and s are constant. Hence, this variable is closely related to the stress-dependent SWRC of unsaturated soils. The following paragraphs first discuss the measurement and modelling of a SWRC. Then, a specific SWRC model is used as an example to derive a formulation for I31.
2.7.1 Stress-dependence of the SWRC
Various experimental technologies have been developed for determining the SWRC in soil science and agriculture-related disciplines, such as the Tempe pressure cell, the volumetric pressure plate extractor, the pressure membrane extractor and the osmotic desiccator [22]. However, these apparatuses do not take into account of the deformation and stress of soil as well as their influence on the SWRC. It is implicitly assumed that the SWRC of a given soil is unique. As a consequence, the value of I31 is assumed to be zero.
Different from soil science and agriculture-related disciplines, in geotechnical engineering the soil state including the density and stress is an important variable. This is because soil behaviour depends strongly on the soil state. Since about 20 years ago, the influence of soil density and deformation on SWRC has been recognised and actively investigated. Although the net stress of soil specimen was not controlled in their study, Vanapalli et al. [87] tested several specimens with different initial void ratios. With a reduction in the void ratio from 0.59 to 0.54, the water retention ability of soil was greatly improved, particularly at suctions lower than 100 MPa. A further reduction in the void ratio from 0.54 to 0.51 did not affect the water retention ability too much. The influence of the initial density on the SWRC has been reported by a large number of researchers [58, 85]. The observed effects of soil density on the SWRC are attributed to the fact that the average pore size of a soil specimen decreases as a result of deformation. The influence of pore size distribution on a SWRC cannot be known and modelled explicitly.
Ng and Pang [59] developed a new stress-controllable pressure plate apparatus, which can be used to determine the SWRC of unsaturated soils subjected to different stress states. Using the modified apparatus, the researchers measured the SWRC of unsaturated silt at vertical net stresses of 0, 40 and 80 kPa. The results are shown in Fig. 10. It is clear that the SWRC was greatly affected by stress. The water retention ability of the soil specimens increased with stress. Similar observation was reported by Lee et al. [42] and their results are shown in Fig. 11. The effects of stress on the SWRC were partially due to the average density-dependence of the SWRC. As reported by Vanapalli et al. [87], when stress increases, the density increases and so does the water retention ability. It should be pointed out that, however, stress effects are not equivalent to density effects. This is because the application of stress affects not only soil density (or void ratio) but also pore size distribution, as illustrated by the results of MIP tests shown in Fig. 12.
2.7.2 Modelling the stress-dependent SWRC
Many SWRC models have been reported in the literature, and they may be classified into three types. The major difference comes from their approaches for considering the influence of soil state on the SWRC. The first type of SWRC models adopts a unique relationship between suction and soil moisture. Examples include Eqs. (C1) through (C3) in Table 5 [23, 30, 86]. The SWRC calculated using these models is a curve in the Sr-s plane. Even though these models are widely used in practice for simplicity, they do not consider the coupling effects between the hydraulic and mechanical behaviour of unsaturated soils. Due to this limitation, I31 predicted by these equations is always regarded as zero.
The second type of SWRC models explicitly considers effects of soil density on the water retention behaviour of unsaturated soil, such as Eqs. (C4) and (C6) in Table 5. Among these models, Gallipoli et al. [27] employed a closed-form equation which was modified from the Van Genuchten [86] model by including the void ratio (e) in the formulation. Hence, Sr is a function of not only suction but also the void ratio. The calculated SWRC becomes as a surface in the Sr–s–e space. Tarantino [85] modified the model of Gallipoli et al. [27] by reducing one parameter based on extensive tests on both fine-grained and coarse-grained soils. Experimental results revealed that the product of Sr and e is almost independent of e at high suction. Based on this experimental evidence, it can be derived that the product of m1m2m4 should be equal to 1. Sheng and Zhou [83] proposed an incremental form. The influence of void ratio on the SWRC was taken into account. This type of models implicitly assumes that stress effects are equivalent to density effects on the SWRC.
The last type of SWRC model [denoted as Eq. (C7) in Table 5] was proposed by Zhou and Ng [106]. Equation (C7) was developed from the following equation.
where ξm is the ratio between the volume of micro-pores (VM) to the total volume of pores (VT) which characterises the pore size distribution (PSD), ξ0 is the initial value of ξm before applying any net stress; and m1, m2, m3, m4 and mm are model parameters. This model takes into account two different effects of net stress on the SWRC: stress-induced change in the average void ratio and stress effects on the pore size distribution. The first effect is described by the following equation:
Moreover, the following equation was derived for the theoretical relationship between PSD parameters and net mean stress:
Equation (36) determines the relationship between the proportion of macro-pores and net stress. Hence, the influence of stress on the pore size distribution is considered in a simplified manner. By considering the net stress effects on water retention ability, the new constitutive relation can overcome the limitations of previous studies based on soil science.
The performance of three SWRC models is evaluated here, including Eq. (C2) [86], Eq. (C5) [85] and Eq. (C7) [106]. Equation (C2) assumes a rigid soil and Eqs. (C5) and (C7) are derived from this equation by considering density effects and stress effects, respectively. These three equations are representative of most SWRC models in Table 5, as discussed above. They are used to simulate the experimental results of Ng and Pang [59] and Lee et al. [42]. Ng and Pang [59] carried out two series of tests to investigate the influence of density and vertical stress on the water retention behaviour of a clayey silt. In the first series of tests, three specimens with different initial void ratios of 0.86, 0.75 and 0.69 were dried at zero net stress. In the second series of tests, three specimens with the same initial void ratio (0.69) were dried at different vertical net stresses of 0, 40 and 80 kPa. Lee et al. [42] measured WRCs of a silty sand at various stresses, similar to the second series of tests in Ng and Pang [59]. The measured and calculated SWRCs are shown in Fig. 10 and Fig. 11. Parameter values are summarised in Table 6. It is revealed from the comparisons that:
(a). Among the three equations, Eq. (C7) show the best performance, with R2 above 0.97 in all cases (see Figs. 10e, f, 11c). This equation is able to well-capture density effects and stress effects observed in both studies. It should be noted that even though Eq. (C7) gives the best prediction of the above experimental results, it considers stress effects on pore structure in a simplified approach. The ratio of inter-aggregate pore volume to intra-aggregate pore volume is used to describe pore structure. This ratio does not account for some features of pore structure, such as the pore size distribution, pore orientation, pore connection and pore shape. Other stress-dependent SWRC models in the literature have similar simplifications [76]. More studies are required to better understand stress effects on the pore structure and hence SWRC of unsaturated soil.
(b). Equation (C5) gives the same prediction as Eq. (C7) for density effects (see Fig. 10c, e), because Eq. (C7) reduces to this equation when net stress is zero. Equation (C5), however, slightly underestimate stress effects on SWRC (R2 = 0.95 and 0.94 in Figs. 10d and 11b, respectively). This deficiency is caused by the limitation of Eq. (C5), which can only partially consider stress effects through the change in void ratio. In the past two decades, many SWRC models have been proposed with a consideration of soil deformation [28, 37, 73, 75, 85, 103], as summarised in Table 5. Even though they have been developed using different approaches, they all implicitly assume that stress effects are equivalent to density effects on the SWRC. Hence, they are expected to show similar performances as Eq. (C7). Their performance is lightly worse than Eq. (C7), but less parameters are required. This type of models may be used as an approximation if the stress change is not very significant.
(c). Equation (C2) only predicts a single SWRC for each soil at different test conditions (see Figs. 10a, b, 11a), as expected. Even though this model is widely used in practice for simplicity, density effects and stress effects cannot be captured. It does not consider the coupling effects between the hydraulic and mechanical behaviour of unsaturated soils. Due to this limitation, I31 predicted by the equation is always zero. Other similar equations, such as Eqs. (C1) through (C3) in Table 5 [23, 30, 86], have similar limitation. These models are expected to show similar performance as Eq. (C2).
Based on the discussion above, the SWRC model proposed by Zhou and Ng [106] shows a fundamental advantage in modelling stress-dependent the SWRC. Based on Eqs. (33)–(36), the following equation can be derived:
Then,
It should be noted that the first type of SWRC models [i.e. Eqs. (C1)–(C3) in Table 5] assume that I31 is equal to zero, while the second type of SWRC models (i.e. equations (C4)–(C6) simply consider the first term on the right-hand of Eq. (38).
2.8 Determination of the variable I32
The variable I32 in Eq. (1) can be determined using the following equation:
According to Eq. (39), the variable I32 is the ratio of the incremental/decremental degree of saturation to incremental/decremental deviator stress when p and s are constant. Ideally, I32 is determined from the relationship between Sr and q based on shear tests at constant-p and s condition. Such data is very limited in the literature because it is uncommon to carry out constant-p and s shear tests. Alternatively, it can be determined using data from SWRCs at various q conditions. Ng et al. [56] measured the SWRCs of a compacted silt. Three different values of the stress ratio q/p (0, 0.75 and 1.2), corresponding to different deviator stresses, were applied. They found that the influence of deviator stress on the SWRC was much smaller than the effects of mean net stress. Based on this observation, mean net stress is directly incorporated in the SWRC model, while the effects of deviator stress on SWRC are described using void ratio for simplicity. Hence, Eq. (39) can be derived as follows:
Based on Eqs. (16), (39) and (40), the following equation can be derived:
Equation (41) suggests that the value of I32 is affected by several factors, including density effects on the SWRC, Dq and I22. A lot of data is available in the literature for determining each of them, so I32 can be determined based on experimental results readily.
2.9 Determination of the variable I33
The variable I33 in Eq. (1) can be calculated using the following equation:
According to Eq. (42), the variable I33 is the ratio of the incremental degree of saturation to incremental suction when p and q are constant. This variable is related to desorption/adsorption rates of unsaturated soils. Based on Eqs. (34) and (42), the following equation can be derived:
It should be noted that the value of I33 is not constant, but dependent on suction and stress. Moreover, the influence of stress on I33 is related to change in the average void ratio and pore size distribution.
Apart from stress-dependence, hydraulic hysteresis also imposes great influence on the water retention behaviour of unsaturated soil. At a given suction, the equilibrium water content along the drying path is higher than or equal to that along the wetting path. So far, some theoretical models have been proposed for the hysteretic water retention behaviour of unsaturated soil. In each model with an assumption of rigid soil, two boundary curves are generally defined, including the main drying curve and main wetting curve. Any state in the Sr–s plane is bounded by these two curves. Similarly, a main drying surface and a main wetting surface are defined in the Sr–s–e space or Sr–s–p space, if density/stress effects on SWRC are considered in the model. When soil state is on the main drying and wetting curves/surfaces, Sr is simply calculated from s, e and p. When soil state is between the main drying and wetting curves/surfaces, Sr is affected by not only s and e but also suction path, due to the existence of hydraulic hysteresis. Different methods have been used in the theoretical model to simulate the scanning curves between the main drying and wetting curves/surfaces. Wheeler et al. [92] modelled the water retention behaviour in a classic elastoplastic framework. Two processes were defined, including the elastic and elastoplastic processes. During each process, a constant adsorption/desorption rate was assumed. Similar approaches were used in many unsaturated soil models [24, 70, 81, 94]. These approaches cannot predict a smooth transition between scanning curves and main curves/surfaces, since the adsorption/desorption rate during the elastoplastic process is much larger than that during the elastic process. To solve this problem, Li [44] applied the bounding surface theory to model the hysteretic water retention behaviour of unsaturated soil. Different from the model of Wheeler et al. [92], the adsorption/desorption rate is not constant when soil state is between the main drying and wetting curves. The adsorption/desorption rate is affected by suction history, the current suction and degree of saturation. The model of Li [44] assumes a rigid soil, so density and stress effects on SWRC cannot be captured. In recent years, some advanced water retention models have been proposed with a consideration of density effects and hysteresis effects [25, 104, 108]. Zhou et al. [108] developed a bounding surface model with a consideration of the influence of soil deformation on water retention behaviour. The main drying/wetting curves in the model of Li [44] was extended from Sr–s plane to Sr–s–e space. Gallipoli et al. [25] proposed a new term (i.e. scaled suction s*), which is a function of suction and void ratio. By adopting the scaled suction, the main drying/wetting surfaces in the Sr–s* plane become as two curves. It should be pointed out that all the above models do not explicitly consider the reasons for hydraulic hysteresis. These models are therefore semi-empirical. Hence, some researchers attempt to model the hysteretic water retention behaviour with an explicit consideration of specific reasons for hydraulic hysteresis. For instance, Zhou [102] applied different contact angles for advancing and receding water meniscus, leading to different water retention abilities during the drying and wetting processes. Cheng et al. [13] incorporated the influence of pore non-uniformity on the water retention behaviour. These models have clear physical meaning, but the calibration of soil parameters is not very straightforward. More studies at the micro- and macro-levels are needed in the future.
2.10 Discussion on the unified and simple framework
Based on the discussion above, it is illustrated that Iij (i = 1, 2 and 3; j = 1, 2 and 3) in Eq. (1) can be derived theoretically. More importantly, these nine variables can be calibrated from suction- and stress-controlled unsaturated soil tests. Hence, Eq. (1) provides a simple but effective framework for modelling the state-dependent behaviour of unsaturated soils.
It should be pointed out that Eq. (1) does not explicitly consider differentiate the elastic and elastoplastic processes. To consider these two processes in numerical analysis, the variables Iij (i = 1, 2 and 3; j = 1, 2 and 3) should take different values at different processes. For instance, in the formulation for I11 [i.e. Eq. (13)], αp(s) is equal to κ(s) and λ(s) for the elastic process and elastoplastic process, respectively.
The cross-terms in the compliance matrix of Eq. (1) are not independent. Firstly, I12 and I21 describe soil dilatancy during constant-p shearing and constant-q compression, respectively. Soil dilatancy during these two processes is modelled using a unified formulation in many constitutive models such as the Barcelona basic model (BBM) [1]. Secondly, I12 and I32 are closely related because shearing-induced volumetric strain (described by I12) would affect the water retention behaviour (described by I32) of unsaturated soil. Finally, I13 and I23 govern the volumetric and deviator strains induced by drying/wetting at a condition of constant-p and q. The ratio of I13 and I23 represents soil dilatancy.
3 Conclusions
In this paper, the state-dependent hydromechanical behaviour of unsaturated soil is reviewed based on a unified and relatively simple framework. This framework uses mean net stress, deviator stress and suction as the constitutive stress variables. Theoretical models based on other constitutive stress variables can be also converted to this framework by matrix transformation. The nine variables, which have clear physical meanings, in the proposed compliance matrix are derived. Moreover, the calibration methods for these nine variables are discussed and explained.
Small strain stiffness of unsaturated soil is greatly affected by many factors, including strain, suction and suction path. So far, extensive formulations for G0 at the very small strains (below 0.001%) can be found in the literature. Performance study of these formulations suggests that at least two constitutive stress variables are required to well-capture the variation of G0 along various stress paths, such as compression and drying/wetting. Moreover, most of the existing models cannot predict the hysteresis of stiffness during drying and wetting, because they have not incorporated effects of suction path properly. On the other hand, the modelling of stiffness degradation curve at small strains (between 0.001 and 1%) is relatively less studied. More unsaturated soil models for stiffness degradation are needed. Some other topics may also need further studies, including suction-induced anisotropy, effects of recent suction path.
Dilatancy of unsaturated soil is affected by not only stress ratio and density, but also some other factors such as suction and its path. With an increase in suction, soil dilatancy generally increases. It is therefore essential to model state-dependent dilatancy, which has not been incorporated in most of existing models. To model state-dependent dilatancy, the choice of void ratio function is not neutral. Based on test results analysed in this study, the use of (e–ec) seems better than e/ec, where e and ec are the current void ratio and void ratio at critical state, respectively. Furthermore, as far as the authors are aware, none of the existing model can capture the influence of drying and wetting cycles on the dilatancy of unsaturated soil. Effects of suction path on dilatancy need further experimental and theoretical studies.
Stress effects and density effects on SWRC are fundamentally different. This is because net stress not only reduces average void ratio, but more importantly, alters the pore structure of unsaturated soil. The use of average void ratio to describe stress effects on water retention capability is therefore not sufficient. Hence, SWRC models including stress effects on pore structures are desired. More studies are required to better understand stress effects on the pore structure and hence SWRC of unsaturated soil.
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Acknowledgements
The authors would like to thank the Research Grants Council (RGC) of the Hong Kong Special Administrative Region, China for providing financial support through the Grants 16204817 and AoE/E-603/18.
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Ng, C.W.W., Zhou, C. & Chiu, C.F. Constitutive modelling of state-dependent behaviour of unsaturated soils: an overview. Acta Geotech. 15, 2705–2725 (2020). https://doi.org/10.1007/s11440-020-01014-7
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DOI: https://doi.org/10.1007/s11440-020-01014-7