Skip to main content
ACS Omega logoLink to ACS Omega
. 2021 May 24;6(22):14309–14316. doi: 10.1021/acsomega.1c01092

Mesoscopic Seepage Simulation and Analysis of Unclassified Tailings Pores Based on 3D Reconstruction Technology

Baomeng Chang †,‡,*, Cuifeng Du †,‡,*, Mingkang Sun †,, Yifan Lin †,, Yuan Wang †,, Xiaofeng Chu §, Long Zhang §, Jiaqing He
PMCID: PMC8190888  PMID: 34124454

Abstract

graphic file with name ao1c01092_0009.jpg

Taking the unclassified tailings as the research object, the three-dimensional (3D) pore model was established using computed tomography (CT) scanning technology, image processing, and the 3D reconstruction method. The model was imported into Flac3D software for mesoscopic seepage simulation and analysis. Combined with the laboratory seepage experiment, the influence of tailings’ mesoscopic parameters on permeability was explored. The results show that there is a high correlation between the fractal dimension and fragmentation index of tailings pores and the mesoscopic seepage coefficient, with correlation coefficients of 0.987 and 0.973, respectively. When the porosity difference of the pore model is small, the permeability is mainly affected by pore connectivity. The mathematical model between the permeability coefficient and the fragmentation index of tailings is established. The average error between the permeability coefficient calculated by the model and the measured value is reduced to 4.98%, which proves that the mathematical model has guaranteed reliability.

1. Introduction

In addition to backfilling, most of the unclassified tailings are discharged to the tailings pond for storage.1 The tailings pond is a major hazard source, prone to destabilization and dam failure under extreme conditions such as heavy rainfall.2,3 Moreover, the tailings contain a large number of heavy metal elements, which also pose a potential pollution risk to the surrounding environment.46 It has been studied that the permeability of tailings affects the height of the seepage line of the tailings pond, which in turn affects the stability of the dam; seepage is also the main driving force for the migration of heavy metals within the tailings. Therefore, it is necessary to study the seepage process within the pores of the tailings and the change law of the permeability properties from the mesoscopic perspective.

Unclassified tailings are unclassified and discontinuous anisotropic bodies with different types and sizes of internal pores due to differences in their original structure, which affects the permeability.79 At present, the determination of the permeability of tailings mainly adopts constant-head or variable-head permeability test. The research on the mesoscopic structure also mainly focuses on the description of the mesoscopic morphology of tailings. However, the macroscopic permeability determination focuses more on the variation of the overall permeability of the tailings, while neglecting the influence of the differences on the morphology of the skeletal structure of the tailing particles and the pore connectivity. It is difficult to quantitatively analyze the pore microstructure in the study of the mesoscopic structure. In recent years, the widespread application of three-dimensional (3D) reconstruction technology in the fields of materials and chemistry has made it possible to solve the above problems.10,11

At present, foreign research in this area mainly focuses on the coupling analysis of porous media by different methods, such as 3D reconstruction and NMR, and the practice and innovation of 3D model construction principles and methods.1217 Izadi Hossein proposed a fast and reliable 3D reconstruction method, which helped to obtain more accurate models for different sandstones;18 Yang et al. performed a detailed calculation and analysis of the porosity, pore size distribution, and connectivity of the filling mineral grain based on the self-developed Matlab 3D image analysis program;19 Lee et al. performed 3D reconstruction and micromechanical response simulation of the porous media using the Montage continuous slicing technique.20 Domestic studies have focused on the quantitative characterization of the mesoscopic structure of tailings pores,2127 while the interrelationship between the mesoscopic structure and permeability has been less studied.

In the study, from the perspective of the mesoscopic view, with the computed tomography (CT) scanning technology, image processing, and the 3D reconstruction method, the 3D model of tailings and pores was established, and the mesoscopic parameters were analyzed. The 3D pore model was imported into Flac3D software to simulate the mesoscopic seepage process in the pore channel of tailings. Meanwhile, combined with the laboratory seepage experiment, the mathematical model between the permeability coefficient and the fragmentation index was established to reveal the influence law of pores on the permeability performance of tailings from the mesoscopic perspective, which had important theoretical significance and engineering application value for the seepage mechanism and stability analysis of tailings pond.

2. Results and Discussion

2.1. Pore Seepage Process Analysis

After importing five groups of pore models into Flac3D and setting the model length in mm, the original model was expanded by 1000 times to perform a mesoscopic seepage similarity simulation. The fixed pore water pressures at the nodes on the upper and lower surfaces of the model were p1 = 10 MPa and p2 = 0.1 MPa, respectively, as the inflow and outflow sources of the model. The flow rate Q of the inflow source pore unit on the upper surface of the model was recorded. It will approach a constant value when the seepage equilibrium is reached. The permeability coefficient k (m/s) of the pore model is calculated based on the dimensions of the model and the difference in the pore water pressure between the upper and lower surfaces of the model. The formula for the permeability coefficient k is28

2.1. 1

where Q is the flow rate of the pore unit on the model surface, m3/s; L is the height of the model, m; A is the cross-sectional area of the model, m2; p1 and p2 are the fixed pore pressures on the upper and lower surfaces, Pa.

The permeability coefficient k is a comprehensive coefficient reflecting the water permeability of the pore and a measure of the flow rate. According to the gravity similarity criterion, the ratio of the flow rate for different-size models is λk = λL0.5. Therefore, the ratio of the permeability coefficient for different-size models should be the same as λk = λL0.5. The size ratio between the mesoscopic pore model and the similar experimental pore model is 1:1000, i.e., λL = 1 × 103. Then, the permeability coefficient kλ of the mesoscopic model can be obtained by the following equation

2.1. 2

The seepage process of the five groups of pore models is similar; therefore, model 1 is taken as an example (the grouping of “tailings” is hidden in Figure 1). From Figure 2a, it can be seen that when the water pressure in the upper surface pore is fixed at 10 MPa, water starts to percolate downward. The contour line of the pore water pressure cloud is parallel to the edge line of the top surface, indicating that there is little difference in the seepage speed around the top of the pore. Figure 2b shows that when the water has percolated 1/3 of the depth, the pore water pressure cloud becomes an arc, which is distributed along the seepage pore channel in a large to small step from top to bottom, perpendicular to the direction of the seepage velocity. From Figure 2c, we can see that the seepage depth has reached 2/3, the isolated pore channels in the xz plane cannot be penetrated by water, and the pore water pressure remains at zero, while the water pressure in the other pore channels gradually increases as the seepage progresses. At the same height, the pore water pressure of impervious channels is higher than that of permeable channels due to head loss caused by percolation in the permeable channel, which is less than the pore pressure of the impervious passage of the same height. From Figure 2d, we can see that at this time, the flow rate of the inflow source at the top of the model is basically no longer changing, and almost all of the permeable channels are in the saturated state, which has reached a stable percolation state (Figure 1).

Figure 1.

Figure 1

Mesh model of five groups of random pores.

Figure 2.

Figure 2

Seepage process of model 1.

2.2. Influence of Mesoscopic Parameters on Seepage

The three-dimensional fractal dimension is a number greater than 2 and less than 3, reflecting the effectiveness of the space occupied by the complex form. It is a measure of the irregularity of the complex form,29,30 and in this case, it characterizes the degree of pore complexity. The fractal dimension d is calculated as follows

2.2. 3

where ε is the edge length of the cube and N(ε) is the number of times the cube is used to cover the measured

The fragmentation index is an index that calculates the relative convexity or concavity of a surface. When considering connectivity, concavity indicates a connected structure, while convexity indicates an isolated disconnected structure,31 where pore connectivity is characterized. The fragmentation index Ni can be calculated by the following equation

2.2. 4

where P and A are the perimeter and area of the object, respectively, and subscripts a and b indicate before and after image expansion.

After the software calculation, the porosity, fractal dimension, fragmentation index, and mesoscopic permeability coefficient kλ for each model are shown in Table 1. The model 3’s pore volume ratio of 62.5% is the maximum among the five groups of models, and its permeability coefficient of 7.336 × 10–6 cm/s is also the maximum. This is consistent with the general rule that the permeability coefficient increases with the increase of the porosity of the porous medium because a larger porosity makes it easier for water to flow through. However, when the difference in porosity is small, such as when comparing models 1 and 5 and models 2 and 4, the model with greater porosity has a lower permeability coefficient. The reason is that the pores do not all constitute seepage channels, e.g., the isolated pore in the xz plane in Figure 6d is not connected to other pores, so the region is less connected and less permeable.3234

Table 1. Mesoscopic Parameters and Permeability Coefficient of Each Pore Model.

model number pore volume ratio (%) fractal dimension fragmentation index flow (m3/s) permeability coefficient kλ (cm/s)
1 58.18 2.418 –0.0339 1.25 × 10–4 4.130 × 10–6
2 53.79 2.430 –0.0483 4.71 × 10–5 1.556 × 10–6
3 62.50 2.375 –0.0110 2.22 × 10–4 7.336 × 10–6
4 51.55 2.424 –0.0371 1.06 × 10–4 3.504 × 10–6
5 56.94 2.415 –0.0313 1.41 × 10–4 4.658 × 10–6

Figure 6.

Figure 6

Image preprocessing process.

The linear relationship between the fragmentation index and the permeability coefficient is evident from Table 2, and the fit with the linear regression equation (Formula 5) and the correlation coefficient R2 of 0.987 is shown in Figure 3a. The fractal dimension and the permeability coefficient of the parameters have an obvious negative correlation, and the fit with the regression equation (Formula 6) (the defined domain is a decreasing interval) and the correlation coefficient R2 of 0.973 is shown in Figure 3b. From Figure 3, we can see that the permeability of pores increases with pore connectivity and decreases with pore complexity. To a certain extent, the fractal dimension can reflect the pore connectivity, that is, the fragmentation index, and there is a clear correlation between them.

2.2. 5
2.2. 6

Table 2. Test Results of the Permeability Coefficient of Unclassified Tailings.

sample number measurement time (s) head (cm) water infiltration (cm3) 20 °C permeability coefficient (cm/s)
1 3000 75.4 16 1.016 × 10–5
2 2220 74.5 16 1.389 × 10–5
3 2549 74.6 16 1.206 × 10–5
4 2678 73.5 16 1.179 × 10–5
5 2798 74.2 16 1.118 × 10–5
6 2394 75.1 16 1.291 × 10–5
7 2863 73.2 16 1.107 × 10–5
8 2914 73.6 16 1.082 × 10–5
average value       1.174 × 10–5

Figure 3.

Figure 3

Fitting results of the mesoscopic parameters and the permeability coefficient of the model.

When there is a big difference in porosity, the permeability of the larger porosity model tends to be better because the larger pores are more likely to allow water to percolate. However, when the difference in porosity is small, porosity is no longer the dominant factor affecting the permeability, while the effect of pore connectivity on seepage is more pronounced.3538

2.3. Mathematical Modeling of the Permeability Coefficient

The permeability coefficient of unclassified tailings is tested using a TST-55 permeameter. According to Darcy’s law, the permeability coefficient at T (°C) can be expressed by the following equation

2.3. 7

where Q is the percolation volume, cm3; L is the percolation height, cm; Δh is the head loss, cm; A is the cross-flow cross-sectional area, cm2; and t is the percolation time, s.

As shown in Table 2, the mean value of the laboratory test of the tailings permeability coefficient at a water temperature of 20 °C is 1.204 × 10–5 cm/s.

From the comparison of Tables 1 and 2, we can see that the permeability coefficient calculated by the numerical simulation experiment is much smaller than the laboratory test value. This is because the permeability coefficient measured by the numerical simulation ignores the mechanical coupling of the seepage process to ensure that the structure of the tailings samples remains unchanged, which has errors with the actual situation.39

Dividing formula 1 and formula 5, we can get

2.3. 8

Substituting formula 2 into formula 8, we can get

2.3. 9

Since the permeability coefficient calculated by the numerical simulation experiment is quite different from that measured in the laboratory, the formula for calculating the permeability coefficient of the fine-scale model can be modified based on the laboratory test value. In other words, kT = 1.174 × 10–5 is substituted into formula 9 to obtain the modified permeability coefficient Kα (m/s). The calculation formula is as follows

2.3. 10

where Q is the flow rate of the model surface pore unit, m3/s; L is the height of the model, m; A is the cross-sectional area of the model, m2; p1 and p2 are the fixed pore pressures on the upper and lower surfaces, respectively, Pa; and Ni is the fragmentation index of the model.

The corrected permeability coefficient kα can be obtained by substituting the flow rate and fragmentation index of the five groups of models when they reach the stable permeability into equation 6, as shown in Table 3. The error between the corrected kα and the mean value of the laboratory test is between 0.08 and 10.71%, which is within a reasonable range. Therefore, the mathematical model can be used to express the relationship between the tailings pore fragmentation index and the actual permeability coefficient.

Table 3. Error Calculation between the Permeability Coefficient of the Mathematical Model and the Laboratory Test Value.

model number flow (m3/s) fragmentation index permeability coefficient kα (cm/s) mean lab test values (cm/s) error (%) average error (%)
1 1.25 × 10–4 –0.0339 1.210 × 10–5 1.174 × 10–5 3.07 4.98
2 4.71 × 10–5 –0.0483 1.020 × 10–5   13.12  
3 2.22 × 10–4 –0.0110 1.143 × 10–5   2.64  
4 1.06 × 10–4 –0.0371 1.170 × 10–5   0.34  
5 1.41 × 10–4 –0.0313 1.241 × 10–5   5.71  

3. Conclusions

Permeability is one of the important physical properties of tailings in the tailings pond. The stability of tailings pond, migration, and diffusion of heavy metals and other harmful pollutants in tailings are closely related to the permeability of tailings particles. In the paper, from the perspective of mesoscopic view, a combination of 3D reconstruction and numerical simulation is used to analyze the mesoscopic seepage process of tailings pores and the influence of mesoscopic parameters of tailings on permeability performance. The specific conclusions are as follows.

Using 3D reconstruction technology and a watershed algorithm to establish and partition the pore model of tailings with high precision, the pore volume percentage calculated by Avizo software is 48.32%, which shows a very small difference from the measured porosity of the tailings sample of 47.62%, proving that the 3D reconstruction model of tailings pores has high reliability.

Pore models with different spatial locations are imported into Flac3D for mesoscopic seepage simulation analysis. When the difference of porosity is large, the model with larger porosity has better permeability, which is consistent with the general rule that the permeability coefficient increases with the increase of porosity of porous media. When the difference of porosity is small, the model with larger porosity has a smaller permeability coefficient. The reason for this is that porosity is no longer the main factor affecting permeability. However, the influence of the pore connectivity on permeability is more significant. The fragmentation index characterizing the pore connectivity and the fractal dimension characterizing the pore complexity were calculated and analyzed for their correlation with the pores mesoscopic permeability coefficient as follows: the permeability coefficient of the pores models increased linearly with the increase of the fragmentation index and decreased significantly with the increase of the fractal dimension, and their correlation coefficients R2 were 0.987 and 0.973, respectively.

Based on the results of mesoscopic seepage simulation and laboratory permeability experiments, the mathematical model between the fragmentation index and the permeability coefficient was established, which reduced the calculation error of the permeability coefficient to within 11% and revealed the variation law of the permeability performance of the tailings from the mesoscopic perspective.

4. Materials and Methods

4.1. Sample Source and Basic Properties

The unclassified tailings sample was taken from Sanshandao Gold Mine in Shandong province, with a density of 2.73 g/cm3 and a porosity of 47.62% as measured by the laboratory. The composition of tailings was determined by X-ray fluorescence spectroscopy, and the content of each element is shown in Table 4, whose chemical composition mainly includes SiO2 and Al2O3, in addition to the presence of heavy metal elements such as Mn, Pb, Cd, and As. The particle size composition of the tailings was determined by a laser particle sizer, and its cumulative size distribution curve of the tailings is shown in Figure 4, d10 = 3.53 μm, d50 = 18.7 μm, and d60 = 37.93 μm, with an inhomogeneity coefficient of 10.75. The tailings are well graded.

Table 4. Main Chemical Composition and the Content of Unclassified Tailings.

analytical composition (* in units of 10–6, except * for %)
Au* Ag* S SiO2 Fe2O3 Al2O3 FeO CaO MgO P2O5 TiO2
0.03 0.95 1.12 58.30 3.05 13.45 1.09 3.10 1.07 0.05 0.26
K2O Na2O As Hg* Pb Zn Cd Cr* Mn Cu burning loss
5.36 0.17 0.008 0.11 0.006 0.015 0.004 4 0.09 0.005 4.17

Figure 4.

Figure 4

Grain size composition distribution curve of unclassified tailings.

4.2. CT Scan and 3D Reconstruction of Tailings

First, 30 g of dried unclassified tailings sample was put into a 10 mL centrifuge tube, and a gauze was inserted to compact the tailings to ensure that the tailings would not move during the test. The centrifuge tube was placed in a Zeiss MicroXCT-400 micro-CT test chamber as shown in Figure 5(Photograph courtesy of Gao Yuan, Institute of Physics, Chinese Academy of Sciences. Copyright 2021. Image is a free domain). And 990 grayscale images of different height sequences were obtained after tomographic scanning of selected areas of the tailings. The image resolution was 992 pixels × 1012 pixels, and the distance between pixels was 3.4 μm. The images were cut by Avizo, and the center 400 pixels × 400 pixels square area was taken. The original CT image has problems such as noise and the difference in the scanning intensity of different tomograms, which will increase the accuracy of particle and pore recognition, thereby increasing the data error. Therefore, a series of processing on the original CT image is required: filter noise reduction—threshold segmentation—recognition of particles and pores. The binary map of the pores could be obtained by selecting 400 segmenting CT images for image preprocessing as shown in Figure 6(40,41)

Figure 5.

Figure 5

Zeiss MicroXCT-400 micro-CT.

The watershed algorithm is a mathematical morphological segmentation method based on topological theory, which converts image grayscale values into gradient images and divides the image into different connected regions according to the gradient. It is widely used in the field of image processing.42,43 The three-dimensional model of the pores can be obtained by segmenting the binary pore map with high precision using the watershed algorithm. As shown in Figure 7, the model is a cube with a side length of 1360 μm, and the pore volume accounts for 48.32% by Avizo software analysis module, which differs very little from the measured porosity of 47.62% in the tailings sample, proving the high reliability of the three-dimensional reconstructed tailings pore model.

Figure 7.

Figure 7

3D reconstruction model of pores.

4.3. Simulation Modeling of Pore Seepage in Tailings

It is necessary to establish a mesoscopic pore model for the numerical simulation of pore seepage, and the specific steps are as follows: (1) In the pore 3D reconstruction model, five groups of pore models were randomly intercepted in different spatial locations, as shown in Figure 4, and the green intercept box was the pore model used for numerical simulation experiments. (2) The advanced surface generation and meshing function of Avizo were used to manipulate the pore model, whose length × width × height was 170 μm × 170 μm × 299 μm, and it was divided into the “pore” group and the “tails” group. The pore model was imported into Flac3D software as shown in Figure 5. (3) When using FLAC3D software for seepage analysis, tailings were set as impermeable cells, i.e., model fl_null, and pores were set as isotropic permeable cells, i.e., model fl_iso. In the simulation, mechanical coupling was not performed to ensure that the structure of the tailings skeleton remains unchanged under ideal conditions.

Acknowledgments

This study was supported by the Funds of National Key Research and Development Program of China (2018YFC0604605) and the Fundamental Research Fund for the Central Universities (FRF-TP-19-039A1).

The authors declare no competing financial interest.

References

  1. Wanzhong Y. Latest Progress of Tailings Stockpiling Technology. Met. Mine 2016, 7, 10–19. [Google Scholar]
  2. Armstrong M.; Langrené N.; Petter R.; Chen W.; Petter C. Accounting for tailings dam failures in the valuation of mining projects. Resour. Policy 2019, 63, 101461 10.1016/j.resourpol.2019.101461. [DOI] [Google Scholar]
  3. Owen J. R.; Kemp D.; Lèbre E.; Svobodova K. Catastrophic tailings dam failures and disaster risk disclosure. Int. J. Disaster Risk Reduct. 2019, 42, 101361 10.1016/j.ijdrr.2019.101361. [DOI] [Google Scholar]
  4. Glotov V. E.; Chlachula J.; Glotova L. P.; Little E. Causes and environmental impact of the gold-tailings dam failure at karamken. the russian far east. Eng. Geol. 2018, 245, 236–247. 10.1016/j.enggeo.2018.08.012. [DOI] [Google Scholar]
  5. Li C.; Wen Q.; Hong M.; Liang Z.; Zhuang Z.; Yu Y. Heavy metals leaching in bricks made from lead and zinc mine tailings with varied chemical components. Constr. Build. Mater. 2017, 134, 443–451. 10.1016/j.conbuildmat.2016.12.076. [DOI] [Google Scholar]
  6. Wang P.; Sun Z.; Hu Y.; Cheng H. Leaching of heavy metals from abandoned mine tailings brought by precipitation and the associated environmental impact. Sci. Total Environ. 2019, 695, 133893 10.1016/j.scitotenv.2019.133893. [DOI] [PubMed] [Google Scholar]
  7. Wu A.; Yang S.; Wang H. Present situation and trend of disposal technology of superfine unclassified paste. Min. Tech. 2011, 11, 4–8. [Google Scholar]
  8. Zhu L.; Lyu W.; Yang P.; Wang Z. Effect of ultrasound on the flocculation-sedimentation and thickening of unclassified tailings. Ultrason. Sonochem. 2020, 66, 104984 10.1016/j.ultsonch.2020.104984. [DOI] [PubMed] [Google Scholar]
  9. Li P.; Hou Y.; Cai M. Factors influencing the pumpability of unclassified tailings slurry and its interval division. Int. J. Miner., Metall. Mater. 2019, 26, 417–429. 10.1007/s12613-019-1750-8. [DOI] [Google Scholar]
  10. Jussiani E. I.; Reis P. J. D.; Appoloni C. R. Determining the chemical composition of materials through micro-CT images. Micron 2016, 89, 9–15. 10.1016/j.micron.2016.06.004. [DOI] [PubMed] [Google Scholar]
  11. Huang S.; Ji T.; Guo W. Biomechanical comparison of a 3D-printed sacrum prosthesis versus rod-screw systems for reconstruction after total sacrectomy: A finite element analysis. Clin. Biomech. 2019, 70, 203–208. 10.1016/j.clinbiomech.2019.10.019. [DOI] [PubMed] [Google Scholar]
  12. Derossi A.; Gerke K. M.; Karsanina M. V.; Nicolai B.; Verboven P.; Severini C. Mimicking 3D food microstructure using limited statistical information from a 2D cross-sectional image. J. Food Eng. 2019, 241, 116–126. 10.1016/j.jfoodeng.2018.08.012. [DOI] [Google Scholar]
  13. Liu X.; Wang J.; Ge L.; et al. Pore-scale characterization of tight sandstone in Yanchang Formation Ordos Basin China using micro-CT and SEM imaging from nm- to cm-scale. Fuel 2017, 209, 254–264. 10.1016/j.fuel.2017.07.068. [DOI] [Google Scholar]
  14. Lu S.; Landis E. N.; Keane D. T. X-ray microtomographic studies of pore structure and permeability in Portland cement concrete. Mater. Struct. 2007, 39, 611–620. 10.1617/s11527-006-9099-7. [DOI] [Google Scholar]
  15. He B.; He J.; Zou H.; Lao T.; Bi E. Pore-scale identification of residual morphology and genetic mechanisms of nano emulsified vegetable oil in porous media using 3D X-ray microtomography. Sci. Total Environ. 2021, 763, 143015 10.1016/j.scitotenv.2020.143015. [DOI] [PubMed] [Google Scholar]
  16. Ji L.; Lin M.; Jiang W.; Cao G. A hybrid method for reconstruction of three-dimensional heterogeneous porous media from two-dimensional images. J. Asian Earth Sci. 2019, 178, 193–203. 10.1016/j.jseaes.2018.04.026. [DOI] [Google Scholar]
  17. Bodla K. K.; Garimella S. V.; Murthy J. Y. 3D reconstruction and design of porous media from thin sections. Int. J. Heat Mass Transfer 2014, 73, 250–264. 10.1016/j.ijheatmasstransfer.2014.02.006. [DOI] [Google Scholar]
  18. Izadi H.; Baniassadi M.; Hasanabadi A.; et al. Application of a full set of two-point correlation functions from a pair of 2D cut sections for 3D porous media reconstruction. J. Pet. Sci. Eng. 2017, 149, 789–800. 10.1016/j.petrol.2016.10.065. [DOI] [Google Scholar]
  19. Yang B.; Wu A.; Miao X.; Liu J. 3D characterization and analysis of pore structure of packed ore particle beds based on computed tomography images. Trans. Nonferrous Met. Soc. China 2014, 24, 833–838. 10.1016/S1003-6326(14)63131-9. [DOI] [Google Scholar]
  20. Lee S. G.; Gokhale A. M.; Sreeranganathan A. Reconstruction and visualization of complex 3D pore morphologies in a high-pressure die-cast magnesium alloy. Mater. Sci. Eng., A 2006, 427, 92–98. 10.1016/j.msea.2006.04.095. [DOI] [Google Scholar]
  21. Xie C.; Zhang W.; Yao D.; Jian W.; Yuchen Z. Quantitative characterization of spatial pore network of soils based on the maximal-balls algorithm. J. Eng. Geol. 2020, 28, 60–68. 10.13544/j.cnki.jeg.2019-207. [DOI] [Google Scholar]
  22. Jiao H. Z.; Wang S. F.; Wu A. X.; Wang Y. M.; Yang Y. X. Shear evolution and connected mechanism of pore structure in thickening bed of paste. J. Cent. South Univ. 2019, 50, 1173–1180. [Google Scholar]
  23. Yu B. Y.; Chen Z. Q.; Feng M. M.; Wu J. Y.; Ding Q.-L. Microstructure evolution of saturated crushed limestone under lateral confined compression based on CT test. J. China Coal Soc. 2017, 42, 367–372. 10.13225/j.cnki.jccs.2016.6014. [DOI] [Google Scholar]
  24. Zhang W.; Liang X.; Tang X.; Shi B.; Xu Y.-D. Fine characterization of spatial pore structure of Nanjing silty sand using micro-CT. Chin. J. Geotech. Eng. 2017, 39, 683–689. 10.11779/CJGE201704013. [DOI] [Google Scholar]
  25. Ye Y.; Liu G. Porous seepage in calcirudite rock with 3-D stresses. J. Tianjin Univ. 2007, 3, 335–339. [Google Scholar]
  26. Mocanu A. C.; Miculescu F.; Miculescu M.; Ciocoiu R. C.; et al. Comprehensive analysis of compatible natural fiber as sacrificial porogen template for tailored ceramic 3D bioproducts destined for hard tissue reconstruction. Ceram. Int. 2021, 47, 5318–5334. 10.1016/j.ceramint.2020.10.113. [DOI] [Google Scholar]
  27. Zieliński T. G.; Venegas R.; Perrot C.; Chevillotte F.; Attenborough K. Benchmarks for microstructure-based modeling of sound-absorbing rigid-frame porous media. J. Sound Vib. 2020, 483, 115441 10.1016/j.jsv.2020.115441. [DOI] [Google Scholar]
  28. Yanlin Z.; Jinzhou T.; Ping C.; Wenhao M.; Shuqing L.; Weijun W. 3-dimensional reconstruction model of rock with random pore structure and microscopic seepage analysis. J. Cent. South Univ. 2017, 48, 168–176. [Google Scholar]
  29. Zhou Bo.; Ku Q.; Lv K. Three-Dimensional Characterization of Inner Pores in Calcareous Sand Particles. J. Tianjin Univ. 2019, 52, 41–48. [Google Scholar]
  30. Zuo X.; Tang X.; Zhou Y. Influence of sampling length on the estimated fractal dimension of surface profile. Chaos, Solitons Fractals 2020, 135, 109755 10.1016/j.chaos.2020.109755. [DOI] [Google Scholar]
  31. Bernardes E. E.; Carrasco E. V. M.; Vasconcelos W. L.; de Magalhães A. G. X-ray microtomography (μ-CT) to analyze the pore structure of a Portland cement composite based on the selection of different regions of interest. Constr. Build. Mater. 2015, 95, 703–709. 10.1016/j.conbuildmat.2015.07.128. [DOI] [Google Scholar]
  32. Zeng F.; Guo Z.; Wang L.; Gao Y.; Liu Z. Experimental investigation on macro-mesoscopic characteristics of seepage flow in transparent porous media. Appl. Ocean Res. 2020, 105, 102424 10.1016/j.apor.2020.102424. [DOI] [Google Scholar]
  33. Yang X.; Liang Y.; Chen W. A spatial fractional seepage model for the flow of non-Newtonian fluid in fractal porous medium. Commun. Nonlinear Sci. Numer. Simul. 2018, 65, 70–78. 10.1016/j.cnsns.2018.05.014. [DOI] [Google Scholar]
  34. Miao T.; Yu B.; Duan Y.; Fang Q. A fractal model for spherical seepage in porous media. Int. Commun. Heat Mass Transfer 2014, 58, 71–78. 10.1016/j.icheatmasstransfer.2014.08.023. [DOI] [Google Scholar]
  35. Cai J.; Zhang Z.; Wei W.; Guo D.; Li S.; Zhao P. The critical factors for permeability-formation factor relation in reservoir rocks: Pore-throat ratio, tortuosity, and connectivity. Energy 2019, 188, 116051 10.1016/j.energy.2019.116051. [DOI] [Google Scholar]
  36. He M.; Zhou Y.; Wu K.; Hu Y.; et al. Pore network modeling of thin water film and its influence on relative permeability curves in tight formations. Fuel 2021, 289, 119828 10.1016/j.fuel.2020.119828. [DOI] [Google Scholar]
  37. Koestel J.; Larsbo M.; Jarvis N. Scale and REV analyses for porosity and pore connectivity measures in undisturbed soil. Geoderma 2020, 366, 114206 10.1016/j.geoderma.2020.114206. [DOI] [Google Scholar]
  38. Ong G. P.; Jagadeesh A.; Su Y. M. Effect of pore network characteristics on non-Darcy permeability of pervious concrete mixture. Constr. Build. Mater. 2020, 259, 119859 10.1016/j.conbuildmat.2020.119859. [DOI] [Google Scholar]
  39. Amoozegar A. Examination of models for determining saturated hydraulic conductivity by the constant head well permeameter method. Soil Tillage Res. 2020, 200, 104572 10.1016/j.still.2020.104572. [DOI] [Google Scholar]
  40. Bao-hua Y.; Ai-xiang W.; Xiu-xiu M. 3D micropore structure evolution of ore particles based on image processing. Chin. J. Eng. 2016, 38, 328–334. [Google Scholar]
  41. Sun Y.; Tan W.; Chen T. A method to remove chattering alarms using median filters. ISA Trans. 2018, 73, 201–207. 10.1016/j.isatra.2017.12.012. [DOI] [PubMed] [Google Scholar]
  42. Roerdink J. B. T. M.; Meijster A. The Watershed Transform: Definitions, Algorithms and Parallelization Strategies. Fundam. Inf. 2000, 41, 187–228. 10.3233/FI-2000-411207. [DOI] [Google Scholar]
  43. Haag S.; Schwartz D.; Shakibajahromi B.; Campagna M.; Shokoufandeh A. A fast algorithm to delineate watershed boundaries for simple geometries. Environ. Modell. Software 2020, 134, 104842 10.1016/j.envsoft.2020.104842. [DOI] [Google Scholar]

Articles from ACS Omega are provided here courtesy of American Chemical Society

RESOURCES