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Article

Estimation of the Soil–Water Characteristic Curve from Index Properties for Sandy Soil in China

1
Gansu Electric Power Corporation, State Grid Corporation of China, Lanzhou 730050, China
2
School of Civil Engineering, Southeast University, Nanjing 210096, China
*
Author to whom correspondence should be addressed.
Water 2024, 16(14), 2044; https://doi.org/10.3390/w16142044
Submission received: 2 July 2024 / Revised: 12 July 2024 / Accepted: 18 July 2024 / Published: 19 July 2024
(This article belongs to the Special Issue Soil Dynamics and Water Resource Management)

Abstract

:
The soil–water characteristic curve (SWCC) is an important parameter of unsaturated soil, and almost all the engineering characteristics of unsaturated soil are more or less related to the SWCC. The SWCC contains important information for geotechnical engineering, water engineering, hydrogeology modelling and climate modelling. It is noted that the experimental measurement of SWCC is costly and time consuming, which limits the implementation of principles of unsaturated soil mechanics in practical engineering. The indirect method, which estimates the SWCC from the index properties of soil, can provide the SWCC with the errors which are within tolerance in practical engineering. In addition, the indirect method can determine SWCC very fast and almost with no cost. In this paper, the domestic sandy soils are selected and the index properties of those sands are used to correlate the SWCC fitting parameters. Consequently, mathematical equations are proposed to estimate SWCC from index properties of domestic sands. The proposed models are trained from 44 sets of experimental data and verified with another independent 8 sets of experimental data from published literature. It is observed that the results from the proposed model agree well with the experimental data from literature.

1. Introduction

In conventional geotechnical engineering, engineers only consider the engineering properties of soil. When the problem relates to unsaturated soil, the coupled analysis of geo-environments and unsaturated properties is commonly conducted. In this sustainable coupled analysis, the soil–water characteristic curve (SWCC) is the critical parameter which is commonly adopted as the input information. The SWCC defines the relationship between the water content of soil (expressed as volumetric water content, saturation or gravity water content) and soil suction. Many researchers [1,2,3,4,5,6,7,8,9,10,11,12,13] have shown that engineering properties such as pore structure, water retention and its hysteresis, coefficient of permeability and shear strength, tensile strength and modulus could be closely related to the SWCC. On the other hand, the SWCC is also used for the evaluation of water infiltration, slope stability and wetting-induced collapse of loess [14,15,16,17]. In practical engineering, different continuous mathematical models have been proposed for the representation of the engineering characteristics of soil. Leong and Rahardjo [18] compared and analyzed various models and experimental results from different types of soil and concluded that Fredlund and Xing’s [19] (FX) model had the best performance in the representation of the SWCC for a wide range of soils.
To obtain the SWCC for the whole suction range, a few discrete experimental data points were collected from the laboratory measurements. Subsequently, a continuous mathematical equation was used to best fit with those discrete experimental data and the SWCC curve could be defined by the fitting parameters of the SWCC models. It is noted that the indoor direct measurement is commonly time consuming and costly, while the indirect method (i.e., estimation from the index properties of soil) is fast and also free. Fredlund and Fredlund [20] revealed that the error associated with the indirect method for the determination of SWCC could satisfy the tolerance requirement in practical engineering. Fredlund et al. [21] categorized the indirect method for the determination of SWCC into four groups: (1) statistical correlation of the water content corresponding to the specific matric suction values; (2) regression model for the fitting parameters of the SWCC model; (3) semi-empirical or physical–empirical model. Recently, the artificial intelligence (AI) technique has provided an alternative method for the estimation of the SWCC [22]. The regression model assumed there was a certain correlation between the fitting parameters of the SWCC model and the index properties of the soil. Liu et al. [23] adopted the effective particle size d10, non-uniformity coefficient Cu, porosity e and other parameters of granular soil to correlate the equivalent capillary height and the fitting parameters a, m and n in the FX model. Luo et al. [24] showed that the fitting parameters a and n in the FX model increased while the parameters n and m decreased with an increase in vertical stress and dry density. Chai and Khaimook [25] observed that the fitting parameter a in the FX model was related to permeability and parameter n was related to particle size distribution, while parameter m was related to plasticity index and the content of the fine particles. Both Zapata et al. [26] and Hosseini et al. [27] proposed empirical equations for the estimation of the fitting parameters a, n and m in the FX model from the weighted plasticity index. Wang et al. [28] proposed a simple equation to estimate the fitting parameter from the dry density. It seems that it is widely recognized that the fitting parameters of the SWCC model can be estimated from the index properties of soil.
As the FX model is commonly considered to be one of the most popular mathematical models for the representation of the SWCC for different types of soil, the fitting parameters in the FX model were estimated from the index properties of the sandy soil in China. Initially, a total of 52 sets of the SWCC experimental data for the sandy soil were collected. Subsequently, the collected data were divided into two groups, one (a total of 44 sets) was used for the training and the other one (a total of 8 sets) was used for the verification. Consequently, new equations were proposed for the estimation of the SWCC for the sandy soil in China from the index properties of soil.

2. Methodology

2.1. Soil Index Properties Selection

In the FX model, which is illustrated in Equation (1), there was a total of three fitting parameters and one input parameter.
θ θ s = 1 ln 1 + ψ C r ln 1 + 10 6 C r 1 ln e + ψ a n m ,
where a, n and m are the fitting parameters, Cr is the input parameter, which is a rough estimation of the residual suction (Fredlund and Xing [19] recommended that Cr be equal to 1500 kPa in most cases), ψ is the matric suction and θs is the saturated volumetric water content.
Vanapalli [29] indicated that those fitting parameters can be correlated to the stress history, mineral composition and pore structure. Luo et al. [30] observed that the particle size distribution had a great influence on the SWCC in the low suction region. Aubertin et al. [31] adopted a total of five parameters, such as the effective particle size (d10), median particle size (d30), limited particle size (d60), coefficient of nonuniformity (Cu) and the coefficient of the curvature (Cc) for the estimation of the SWCC for the sandy soil. Liu and Wen [32] pointed out that parameter a increased with an increase in the dry density of soil. With the same particle size distribution data (GSD), lower dry density results in the steeper slope of SWCC in the transition curve. As a result, the parameters such as specific gravity GS, dry density γd, d10, d30, d50 and d60, which were initially used as the input information for the estimation of the fitting parameters of the FX model for the sandy soil in China, were collected. The backward method was adopted to refine the regression equations.

2.2. Data Collection

A total of 52 sets of test data covering 19 different sandy soils in China were collected for this paper. Among those sets of data, 44 sets of data, which were randomly selected, were used for the linear regression analysis. The other 8 sets of data were used to verify the reliability of the proposed equation. The index properties of those 52 sets of soil were illustrated in Table 1.

2.3. Data Processing

The fitting parameters (a, n and m) in the FX model were determined by best fitting the FX model with the collected experimental data. To avoid invalid samples in the regression, the input parameter Cr was set at 1500 kPa, and the ranges of the fitting parameters were defined as follows: 0.01 ≤ a ≤ 1000, 0.1 ≤ n ≤ 20, 0.1 ≤ m ≤ 4 [25]. The determined fitting parameters in the FX model for those 44 sets of sandy soil in China are illustrated in Table 2.

2.4. Statistical Analysis

The multiple linear regression method was used for the mathematical statistical analysis to correlate the fitting parameters in the FX model and the index properties of the soil. In the process of analysis, the backward method was adopted for the refinement of the regression equation. The weakly correlated parameters were discarded based on a significance test. The procedures of the statistical analyses were illustrated as follows:
  • Construct an x-element regression equation using all x variables.
  • Calculate the significance test p-value of these x independent variables, respectively, and record the maximum value as p j x = max p 1 x , p 2 x , , p x x .
  • For a given significance level (0.05), it is considered that this variable can be removed from the regression equation if p j x 0.05 .
  • Reconstruct the regression equation using the remaining x − 1 variables.
  • Conduct false significance tests for the remaining x − 1 variables, respectively, and mark the maximum value as p j x 1 = max p 1 x , p 2 x , , p x 1 x 1 .
  • If p j x 1 0.05 , it is considered that the variable can be removed from the regression equation.
  • This cycle ends when the significance p-value of all independent variables in the regression equation is less than 0.05.
The adjusted coefficient of determination, R2, which is defined in Equation (2), was adopted for the evaluation of the performance of the proposed equation.
a d j u s t e d   R 2 = 1 1 R 2 n 1 n x 1 ,
where x is the number of independent variables and n is the sample size, R is the coefficient of the determination.
The results of the multiple linear regression analyses for the correlation of parameters a, m and n with the index properties of soil were illustrated in Table 3, respectively.
Table 3 illustrates that the adjusted R2 for model three was highest (i.e., 0.271), while that of model one was only 0.226. The p-value of the significance test of each variable in model three was less than 0.05. As a result, model three was selected for the estimation of the fitting parameter a in the FX model. On the other hand, Table 4 and Table 5 show that models six and two give the highest adjusted R2 for the parameter m and n, respectively. Therefore, model six, as illustrated in Table 4, was adopted for the estimation of the parameter m, while model two in Table 5 was adopted for the estimation of the parameter n. Consequently, Equations (3)–(5) were proposed for the estimation of the fitting parameters (a, n and m) in the FX model for the sandy soil in China from the index properties as follows:
a = 98.38 + 4.287 d 10 + 14.049 γ d 2.285 d 50 43.285 G S ,
n = 6.001 13.27 d 60 3.038 γ d + 15.109 d 30 + 18.748 d 50 16.111 d 10 ,
m = 0.373 + 3.728 d 10

3. Results and Discussion

The fitting parameters (a, n and m) of the remaining eight sets of sandy soil were determined by using Equations (3)–(5) and illustrated in Table 6. The measured experimental data of those remaining eight sets of sandy soil were used to compare with the estimated SWCC by using the fitting parameters in Table 4. The comparisons between the estimated SWCC and measured experimental data were illustrated in Figure 1.
Figure 1 shows that the predicted results are basically consistent with the experimental data, with R2 mostly greater than 80%. In general, the mathematical model proposed in this paper predicted the SWCC of sandy soil in China well. As indicated in Figure 1, the estimated SWCC can map the first bending point better than it can the second bending point. The work of Fredlund and Xing [19] indicated that the location of the first bending point was related to the air-entry value, which was related to the large pores in the soil, while the second bending point was related to the residual suction and residual volumetric water content, influenced by the micropores and adsorption action of the soil particles. In this regression analysis, the regression model was proposed for the prediction of the SWCC for sandy soil. In this proposed model, only grain size distribution data (GSD), dry density and specific gravity were adopted as the variables. The effect of the fine contents on the prediction of the SWCC was not considered in the proposed model. Therefore, it seems that more variables such as the percentage of fine contents and the plastic index should be adopted as the variables for the prediction of SWCC for the soil with high fine contents.

4. Conclusions and Recommendations

  • The linear regression analyses were conducted to investigate the correlations between the fitting parameters in the FX model and the index properties of sandy soil in China. A total of 52 sets of experimental data were collected in this paper, 42 sets of data were used to train the correlation equations, while the other 8 sets of data were used for the verification of the proposed equation. It was observed that the proposed equation could predict the SWCC of sandy soil in China well.
  • As only limited data for both the drying and the wetting SWCCs can be collected from the literature, only the dry SWCC data are used for the regression analyses. The hysteresis of the SWCC was not considered in this paper. More research is required on the estimation of the wetting SWCC.
  • It is known that the SWCC of the coarse-grained soil is mainly affected by the grain size distribution data (GSD) and packing density. In the proposed model, only GSD, dry density and specific gravity were used as variables to train the prediction model, and the effects of the fine contents and the plastic index on the SWCC were not considered. Therefore, it was observed that the proposed equation can perform well for soil with low fine contents, and perform less accurately for soil with high fine contents.

Author Contributions

Conceptualization, S.W.; methodology, S.W.; formal analysis, X.G.; investigation, F.Y.; data curation, Y.C. and Z.Z.; writing—original draft preparation, S.W., Y.C., Q.Z. and T.S.; writing—review and editing, T.S. and F.Y.; supervision, Q.Z. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Data Availability Statement

Data are contained within the article.

Conflicts of Interest

The authors declare no conflicts of interest.

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Figure 1. Comparison between the predicted and measured SWCCs of the sandy soil in China. (a) Clay gravel; (b) riddled sand sand II; (c) medium sand; (d) fine sand; (e) sandy soil; (f) sandy soil; (g) Hunan sandy soil; (h) coarse sand.
Figure 1. Comparison between the predicted and measured SWCCs of the sandy soil in China. (a) Clay gravel; (b) riddled sand sand II; (c) medium sand; (d) fine sand; (e) sandy soil; (f) sandy soil; (g) Hunan sandy soil; (h) coarse sand.
Water 16 02044 g001
Table 1. Index properties of the sandy soil in China.
Table 1. Index properties of the sandy soil in China.
SNSoilDry Density/
Mg·m−3
Specific Gravity/
Gs
d60/
mm
d30/
mm
d50/
mm
d10/
mm
References
1Clay gravel1.8972.713.5470.05820.045Luo et al. [24]
2Clay gravel2.0652.713.5470.05820.045
3Clay gravel2.1872.713.5470.05820.045
4Clay gravel2.2162.713.5470.05820.045
5Red sandstone soil1.72.70.70.10.50.05Song [33]
6Red sandstone soil1.772.70.70.10.50.05
7Red sandstone soil1.832.70.70.10.50.05
8Red sandstone soil1.782.70.70.10.50.05
9Red sandstone soil1.782.70.70.10.50.05
10Red sandstone soil1.782.70.70.10.50.05
11Mu Wu sand1.42.70.280.2310.2620.188Zhang [34]
12Chanhe sand1.42.70.5130.3250.4350.238
13Riddled sand sand I1.42.70.3080.250.2890.22
14Riddled sand sand II1.42.70.6190.5020.5750.443
15Medium sand1.752.660.4470.30.3970.075Liu and Wen [32]
16Medium sand1.752.660.4470.30.3970.075
17Medium sand1.82.660.4470.30.3970.075
18Fine sand1.72.670.3490.2280.320.061
19Fine sand1.752.670.3490.2280.320.061
20Fine sand1.82.670.3490.2280.320.061
21Silt1.72.680.1120.050.0930.03
22Silt1.752.680.1120.050.0930.03
23Silt1.82.680.1120.050.0930.03
24Sandy soil1.42.70.1090.0460.0870.003He [35]
25Sandy soil1.52.690.1090.0460.0870.003
26Sandy soil1.5792.71.3880.5320.8950.086Yang et al. [36]
27Sandy soil1.382.6850.140.0960.1550.076Tian and Kong [37]
28Sandy soil1.382.690.1360.0910.1490.038
29Sandy soil1.382.6940.1310.0860.1420.030
30Sandy soil1.382.6950.1270.080.1350.026
31Sandy soil1.382.6830.1480.1020.160.082
32Sandy soil1.382.7030.1060.0380.1050.013
33Hunan sandy soil1.32.70.0540.0310.0470.012Zhu [38]
34Hunan sandy soil1.352.70.0540.0310.0470.012
35Hunan sandy soil1.42.70.0540.0310.0470.012
36Hunan sandy soil1.452.70.0540.0310.0470.012
37Hunan sandy soil1.52.70.0540.0310.0470.012
38Hunan sandy soil1.62.70.0540.0310.0470.012
39Hunan sandy soil1.62.70.0540.0310.0470.012
40Sandy soil1.7542.550.3750.2880.3250.238Zhang [39]
41Sandy soil1.8882.550.3650.2730.3150.223
42Sandy soil1.9422.550.350.2540.3000.204
43Sandy soil2.0392.550.3220.230.2720.180
44Sandy soil1.9962.560.280.2350.2400.185
45Sandy soil1.9352.580.320.260.2700.210
46Sandy soil1.812.590.340.280.2900.230
47Sandy soil1.6832.550.3860.3040.3360.254
48Sandy soil1.262.690.1360.0980.10.079Tang [40]
49Sandy soil1.42.530.2040.1670.1930.134Hou [41]
50Fine sand1.42.550.2960.1480.2370.075Lou [42]
51Coarse sand1.42.550.6690.340.5610.141
52Medium sand1.42.550.3830.1960.3190.104
Table 2. The determined fitting parameters in the FX model for the sandy soils.
Table 2. The determined fitting parameters in the FX model for the sandy soils.
No.SoilFX Model ParameterR2
A (kPa)mn
1Clay gravel8.8350.3691.36899.88
2Clay gravel27.340.2821.66399.97
3Clay gravel27.40.112.89799.7
5Red sandstone soil39.880.5151.78199.8
6Red sandstone soil64.230.71.33499.89
7Red sandstone soil72.880.671.61499.8
8Red sandstone soil61.510.482.31999.53
9Red sandstone soil47.880.7681.26798.17
10Red sandstone soil155.80.531.4999.59
11Mu Wu sand20.8581.71
12Chanhe sand20.81087.32
13Riddled sand sand I2.2881.7513.66299.39
16Medium sand8.5790.488.64199.78
17Medium sand9.8520.4337.36898.73
18Fine sand9.5380.7084.28199.63
19Fine sand10.0620.5356.40599.92
21Silt17.9970.7715.18999.85
22Silt20.1380.6654.75499.73
23Silt20.1650.5954.38299.67
24Sandy soil3.7920.6451.51199.35
26Sandy soil2.6000.8664.27599.86
27Sandy soil2.4250.8654.33299.55
28Sandy soil3.0450.7265.16999.35
29Sandy soil2.3050.8682.50899.84
30Sandy soil2.4050.6672.71699.86
32Sandy soil2.6221.4832.55599.59
33Hunan sandy soil0.7340.4271.53099.87
34Hunan sandy soil0.6840.3901.41599.67
35Hunan sandy soil0.8130.3991.19099.51
36Hunan sandy soil0.9710.3591.39799.64
37Hunan sandy soil2.1670.2941.92099.49
39Hunan sandy soil3.6200.2581.83499.76
40Sandy soil2.1190.69815.42099.56
41Sandy soil2.7630.6996.16499.38
42Sandy soil13.5191.1951.49499.51
43Sandy soil13.5191.1951.49499.59
44Sandy soil287.4833.1551.02999.52
45Sandy soil75.9851.5141.21699.67
46Sandy soil46.4521.0051.41299.94
47Sandy soil7.8520.7245.57699.12
48Sandy soil0.51296.53
49Sandy soil102194.66
50Fine sand8.6860.7596.69799.58
52Medium sand7.2460.8825.88899.66
Table 3. The results of multiple linear regression analyses for the parameter a.
Table 3. The results of multiple linear regression analyses for the parameter a.
ModelVariablesCoefficientSignificance Test p-ValueRR2Adjusted R2
1(constant)−26.2520.970.6130.3760.226
dry density94.4070.081
specific gravity−37.9740.382
d60214.4640.306
d30−253.1460.103
d50−224.2520.469
d10394.0340.14
2(constant)−89.2830.8980.6020.3620.239
dry density97.4380.068
specific gravity−18.7730.194
d5067.7410.173
d30−236.2170.219
d10311.4390.189
3(constant)98.380.7280.60.3550.271
dry density14.0490.043
specific gravity−43.2850.202
d50−2.2850.039
d104.2870.027
4(constant)−136.2250.0270.490.240.18
dry density95.6180.02
d50179.2210.114
d10−20.4780.258
Notes: 1. Predictive variables: (constant), d10, d60, dry density, specific gravity, d30, d50; 2. predictive variables: (constant), d10, dry density, specific gravity, d30, d50; 3. predictive variables: (constant), d10, d50, dry density, specific gravity; 4. predictive variables: (constant), d10, d50, dry density.
Table 4. The results of multiple linear regression analyses for the parameter m.
Table 4. The results of multiple linear regression analyses for the parameter m.
ModelVariablesCoefficientSignificance Test p-ValueRR2Adjusted R2
1(constant)5.3450.3450.7710.5940.497
d105.2090.018
dry density−0.2380.568
specific gravity−1.7050.403
d600.0220.989
d30−0.4440.712
d500.1580.949
2(constant)5.330.3280.7710.5940.516
d105.1960.007
dry density−0.2370.555
Specific Gravity−1.7010.388
d30−0.4390.696
d500.190.738
3(constant)4.8360.3470.770.5920.532
d105.1410.006
dry density−0.180.614
specific gravity−1.5410.412
d30−0.2080.811
4(constant)4.9790.3210.7690.5920.548
d104.9510.003
dry density−0.2020.551
specific gravity−1.5870.387
5(constant)4.6520.3450.7660.5860.558
d104.7150.003
specific gravity−1.5780.385
6(constant)0.3730.0010.7580.5750.561
d103.7280
Notes: 1. Predictive variables: (constant), d50, specific gravity, dry density, d30, d10, d60; 2. predictive variables: (constant), d50, specific gravity, dry density, d30, d10; 3. predictive variables: (constant), specific gravity, dry density, d30, d10; 4. predictive variables: (constant), specific gravity, dry density, d10; 5. predictive variables: (constant), specific gravity, d10; 6. predictive variables: (constant), d10.
Table 5. The results of multiple linear regression analyses for the parameter n.
Table 5. The results of multiple linear regression analyses for the parameter n.
ModelVariablesCoefficientSignificance Test p-ValueRR2Adjusted R2
1(constant)12.5040.4030.7270.5280.419
dry density−3.2850.02
specific gravity−2.2880.659
d60−12.8420.025
d3014.910.001
d5018.3960.03
d10−16.5520.004
2(constant)6.0010.0020.7240.5250.437
dry density−3.0380.016
d60−13.270.017
d3015.1090.001
d5018.7480.024
d10−16.1110.004
3(constant)3.3650.1420.5780.3350.263
dry density−0.5150.732
d60−0.1680.653
d3012.7370
d10−15.280.005
Notes: 1. Predictive variables: (constant), d10, d60, dry density, specific gravity, d30, d50; 2. predictive variables: (constant), d10, d60, dry density, d30, d50; 3. predictive variables: (constant), d10, d60, dry density, d30.
Table 6. The estimated fitting parameters (a, n and m) in the FX model for the sandy soil in China by using the proposed equation in this paper.
Table 6. The estimated fitting parameters (a, n and m) in the FX model for the sandy soil in China by using the proposed equation in this paper.
No.SoilLinear Regression Model
a (kPa)mn
4Clay gravel7.8330.5410.1
14Riddled sand sand II1.7642.0254.761
15Medium sand6.5400.6535.672
20Fine sand7.6280.6004.363
25Sandy soil2.8310.3842.277
31Sandy soil1.6200.6793.064
38Hunan sandy soil5.3390.4181.268
51Coarse sand6.9940.8996.253
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MDPI and ACS Style

Wang, S.; Guo, X.; You, F.; Zhang, Z.; Shen, T.; Chen, Y.; Zhai, Q. Estimation of the Soil–Water Characteristic Curve from Index Properties for Sandy Soil in China. Water 2024, 16, 2044. https://doi.org/10.3390/w16142044

AMA Style

Wang S, Guo X, You F, Zhang Z, Shen T, Chen Y, Zhai Q. Estimation of the Soil–Water Characteristic Curve from Index Properties for Sandy Soil in China. Water. 2024; 16(14):2044. https://doi.org/10.3390/w16142044

Chicago/Turabian Style

Wang, Shijun, Xing Guo, Feng You, Zhong Zhang, Tianlun Shen, Yuhui Chen, and Qian Zhai. 2024. "Estimation of the Soil–Water Characteristic Curve from Index Properties for Sandy Soil in China" Water 16, no. 14: 2044. https://doi.org/10.3390/w16142044

APA Style

Wang, S., Guo, X., You, F., Zhang, Z., Shen, T., Chen, Y., & Zhai, Q. (2024). Estimation of the Soil–Water Characteristic Curve from Index Properties for Sandy Soil in China. Water, 16(14), 2044. https://doi.org/10.3390/w16142044

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