Exploring Environmentally Friendly Biopolymer Material Effect on Soil Tensile and Compressive Behavior
Abstract
:1. Introduction
2. Materials and Methods
2.1. Material
2.2. Uniaxial Compressive Test
2.3. Scanning Electron Microscope (SEM)
3. Numerical Investigation
- (1)
- Contact model. The rigid particles interact with each other at particle surface contacts. Contact modes are assigned at the contacts to develop internal forces for various contact mechanics. The SEM images in Figure 3 present the differences between the clean sand and xanthan gum biopolymer-treated sand. The clean sand has irregular and isolated particles (Figure 3a) while the biopolymer-treated sand is covered and connected by the biopolymer (Figure 3b). The formed hydrogen bonding between the sand particles and xanthan gum provides this bonding connection [27]. In the PFC component, the linear parallel bond exhibits elastic interactions between particles that transmit a normal force, shear force, and moment [17]. When particles are bonded together, they delivered resistance to the particle rotation and therefore exhibit linear elastic to present bond properties. When the bond is broken, it acts as a linear model that cannot resist rotation and tension. Details can be found in the research by Potyondy and Cundall [19]. Thus, the linear parallel bond model can simulate the bonded and unbonded state of the sample particles in the test.
- (2)
- Biopolymer bonding. In the SEM images, biopolymers were distributed in the soil and connected the soil particles. Figure 4 can reproduce this condition by adding a linear parallel contact bond between the sand particles. Contact parameters were embodied in all the particle contacts. Thus, all the particle contacts were set as linear parallel bonds. The different contents of the biopolymer were represented by the different contact parameters.
- (3)
- Sample generation. Previous studies have pointed out that particle sizes and numbers are important factors that affect the simulation time [28]. Considering the computational efficiency and realistic particle size distribution, the particle radius is scaled up 2 times. This is a common way to reduce simulation time with fewer particle balls [29]. The specimen was generated with dimensions of 50 mm × 50 mm in accordance with the experimental sample, as presented in Figure 4. After multiple cycling calculations, the balls reached the equilibrium state in the subsequent test.
- (4)
- Calibrate material behavior. The PFC parameter calibration is a process that reproduces the macro experimental behavior by selecting corresponding numerical parameters to match the experimental data. Due to the complicated interaction in realistic geo-mechanics and simplification in the simulation model, it is difficult to expect these parameters to be precisely recorded and matched with the real conditions. The parameters are given to the PFC components including the ball, wall and contact. As it is difficult to calculate the input parameters through the macroscopic response of the specimen, the most commonly used method of “trial and error” is adapted to calibrate the parameters [30]. Table 1 summarizes the biopolymer binding model parameters.
- (5)
- Remove floaters. When generating ball particles in PFC software, it is evident that there are no contacts around some particles. These floating particles called floaters are isolated and are not connected with the other particles from the initial point of the test. However, with the deformation of the samples during the test, these floaters may contact other particles and influence their properties. Thus, multiple cycles are set to remove the floaters.
- (6)
- Simulating the uniaxial compressive test. Frictionless walls were applied as confined caps at the top and bottom of the sample in the simulation model. The compressive rate was identical to the experimental test. To analyze the micro-behavior of the samples, the stress-strain, internal force, and crack images were tracked and captured during the simulation. The compressive strength was recorded as the average force value on the top and bottom walls during the test.
- (7)
- Simulating the direct tensile test. Unlike the uniaxial compressive test, loading walls were removed in the direct tensile test. A measurement circle was embedded in the specimen to record the axial tensile strength through the built-in FISH language. As the parameters were successfully calibrated to match the experimental test results for the uniaxial compressive test, the direct tensile tests were conducted by using identical parameters to those of the uniaxial compressive test. The particles were divided into an upper group (1~25 mm; 5~25 mm; 10~25 mm; 15~25 mm; 20~25 mm; 24~25 mm;) and a lower group (−1~−25 mm; −5~−25 mm; −10~−25 mm; −15~−25 mm; −20~−25 mm; −24~−25 mm;) according to their position. Then these two groups were given an opposite movement velocity to simulate the direct tensile test. The tensile tests were set for specimens a~f according to their different tensile positions. The schematic diagram is presented in Figure 5.
4. Results and Discussion
4.1. Comparison of Experimental and Numerical Uniaxial Compressive Test Results
4.2. Tensile Strength
4.3. Internal Force and Crack Propagation Patterns
4.4. Correlation of Compressive Verse Tensile Strength
5. Conclusions
- (1)
- The experimental and numerical results with different xanthan contents indicate that the calibrated material behavior and contact model can effectively simulate the geotechnical behavior of the samples. They all indicate that the uniaxial compression strength and tensile strength in the xanthan gum biopolymer-treated sand increase with a higher biopolymer content.
- (2)
- The bond tensile stress and cohesion value in the PFC numerical simulation model increased with increasing biopolymer content, illustrating that a higher biopolymer content can provide a stronger bond. This can also be confirmed by a decrease in the fracture number when the biopolymer content increases.
- (3)
- There was a second-degree polynomial function relationship between the tensile position and tensile strength.
- (4)
- According to the development of the contact force chain and crack propagation pattern in PFC, the behavior from biopolymer-treated sand under uniaxial compression can be classified into three stages: the compact stage, crack development stage, and failure stage, which can be regarded as the tensile stage and failure stage when the specimen is subjected to the tensile test.
- (5)
- Although biopolymer content had a substantial effect on the compressive strength (qu) and tensile strength (qt) of sand, the ratio of qt/qu remained constant at each tensile position, independent of other factors.
Author Contributions
Funding
Conflicts of Interest
References
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Parameter | Symbol | Biopolymer Content | ||||
---|---|---|---|---|---|---|
0.2% | 0.5% | 1% | 1.5% | 2% | ||
Value | ||||||
Sand particle density (kg/m3) | ρs | 2600 | 2600 | 2600 | 2600 | 2600 |
Bond tensile stress (Pa) | pb_ten | 1 × 105 | 5.8 × 105 | 6.1 × 105 | 7.4 × 105 | 8 × 105 |
Bond cohesion (Pa) | pb_coh | 5 × 104 | 2 × 105 | 3.5 × 105 | 4.6 × 105 | 6 × 105 |
Bond normal-to-shear stiffness ratio | kratio | 2 | 2 | 2 | 2 | 2 |
Friction coefficient | μ | 0.34 | 0.45 | 0.61 | 0.64 | 0.68 |
Bond effective modulus (Pa) | emod | 9.8 × 106 | 1 × 107 | 1.3 × 107 | 1.4 × 107 | 1.5 × 107 |
Biopolymer Content | qu (kPa) | Tensile Position | |||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1~25 mm −1~−25 mm | 5~25 mm −5~−25 mm | 10~25 mm −10~−25 mm | 15~25 mm −15~−25 mm | 20~25 mm −20~−25 mm | 24~25 mm −24~−25 mm | ||||||||
qt (kPa) | qt/qu | qt (kPa) | qt/qu | qt (kPa) | qt/qu | qt (kPa) | qt/qu | qt (kPa) | qt/qu | qt (kPa) | qt/qu | ||
0.2% | 131 | 27 | 0.206 | 30 | 0.229 | 31 | 0.237 | 31 | 0.237 | 22 | 0.168 | 7 | 0.053 |
0.5% | 548 | 108 | 0.197 | 120 | 0.219 | 126 | 0.230 | 122 | 0.223 | 87 | 0.159 | 28 | 0.051 |
1% | 920 | 182 | 0.198 | 202 | 0.220 | 216 | 0.235 | 217 | 0.236 | 152 | 0.165 | 48 | 0.052 |
1.5% | 1204 | 240 | 0.199 | 260 | 0.216 | 282 | 0.234 | 281 | 0.233 | 200 | 0.166 | 63 | 0.052 |
2% | 1412 | 316 | 0.224 | 344 | 0.244 | 364 | 0.258 | 360 | 0.255 | 262 | 0.186 | 82 | 0.058 |
Average value | - | - | 0.205 | - | 0.225 | - | 0.239 | - | 0.237 | - | 0.169 | - | 0.053 |
Standard deviation | - | - | 0.0100 | - | 0.0101 | - | 0.0098 | - | 0.0104 | - | 0.0090 | - | 0.0024 |
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Chen, C.; Peng, Z.; Gu, J.; Peng, Y.; Huang, X.; Wu, L. Exploring Environmentally Friendly Biopolymer Material Effect on Soil Tensile and Compressive Behavior. Int. J. Environ. Res. Public Health 2020, 17, 9032. https://doi.org/10.3390/ijerph17239032
Chen C, Peng Z, Gu J, Peng Y, Huang X, Wu L. Exploring Environmentally Friendly Biopolymer Material Effect on Soil Tensile and Compressive Behavior. International Journal of Environmental Research and Public Health. 2020; 17(23):9032. https://doi.org/10.3390/ijerph17239032
Chicago/Turabian StyleChen, Chunhui, Zesen Peng, JiaYu Gu, Yaxiong Peng, Xiaoyang Huang, and Li Wu. 2020. "Exploring Environmentally Friendly Biopolymer Material Effect on Soil Tensile and Compressive Behavior" International Journal of Environmental Research and Public Health 17, no. 23: 9032. https://doi.org/10.3390/ijerph17239032
APA StyleChen, C., Peng, Z., Gu, J., Peng, Y., Huang, X., & Wu, L. (2020). Exploring Environmentally Friendly Biopolymer Material Effect on Soil Tensile and Compressive Behavior. International Journal of Environmental Research and Public Health, 17(23), 9032. https://doi.org/10.3390/ijerph17239032