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Green Low-Carbon Technology for Metalliferous Minerals

A special issue of Metals (ISSN 2075-4701).

Deadline for manuscript submissions: closed (31 August 2022) | Viewed by 50699

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Guest Editor
1. Department of Mining Engineering, Beijing General Research Institute of Mining and Metallurgy (BGRIMM), Beijing 100160, China
2. National Centre for International Research on Green Metal Mining (CIRGM), Beijing 102628, China
Interests: fundamental and applied research of green low-carbon mining; mine waste management; paste backfill; mechanics of mine backfills; mineral processing; environmental geomechanics
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Special Issue Information

Dear Colleagues,

Metalliferous minerals play a central role in the global economy. They will continue to provide the raw materials we need for industrial processes. Significant challenges will likely emerge if the climate-driven green and low-carbon development transition of metalliferous minerals exploitation is not managed responsibly and sustainably.

Prof. Guo of BGRIMM was the first to propose a new development concept for green low-carbon mining. Green low-carbon technology is vital to promote the development of metalliferous mineral resources shifting from extensive destructive mining to clean and energy-saving mining in future decades. Global mining scientists and engineers have conducted a lot of research in related fields such as green mining, ecological mining, energy-saving mining, and mining solid waste recycling and have achieved many innovative progress and achievements.

This Special Issue intends to collect the latest developments in the green low-carbon mining field, written by well-known researchers who have contributed to the innovation of new technologies, process optimization methods, or energy-saving techniques in metalliferous minerals development.

Topics addressed in this Special Issue may include but are not limited to:

  • Green low-carbon technologies and systems
  • Green low-carbon mining optimization method
  • Fronters in mining with backfill
  • Mine waste and heat management
  • Geomechanical behavior of mine backfill
  • Energy-saving techniques in mining
  • Alternative by product materials for green mining
  • Green low-carbon development criteria of mining
  • Case studies of green low-carbon mining

Prof. Dr. Lijie Guo
Guest Editor

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Keywords

  • Metalliferous minerals
  • Green mining
  • Low-carbon mining
  • Energy-saving mining
  • Mine backfill
  • Mine waste management
  • Geomechanical behavior
  • Alternative materials

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Published Papers (18 papers)

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Editorial

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4 pages, 175 KiB  
Editorial
Green Low-Carbon Technology for Metalliferous Minerals
by Lijie Guo
Metals 2022, 12(10), 1719; https://doi.org/10.3390/met12101719 - 14 Oct 2022
Viewed by 1168
Abstract
Metalliferous minerals play a central role in the global economy [...] Full article
(This article belongs to the Special Issue Green Low-Carbon Technology for Metalliferous Minerals)

Research

Jump to: Editorial

20 pages, 6336 KiB  
Article
Experimental Study on Strength Development and Engineering Performance of Coal-Based Solid Waste Paste Filling Material
by Jiqiang Zhang, Ke Yang, Xiang He, Zhen Wei, Xinyuan Zhao and Juejing Fang
Metals 2022, 12(7), 1155; https://doi.org/10.3390/met12071155 - 6 Jul 2022
Cited by 27 | Viewed by 2283
Abstract
To explore the strength development characteristics and engineering performance of different coal-based solid waste filling materials cemented into filling body, coal gangue was used as coarse material, fly ash, desulfurization gypsum, gasification slag, and furnace bottom slag as fine material, and cement as [...] Read more.
To explore the strength development characteristics and engineering performance of different coal-based solid waste filling materials cemented into filling body, coal gangue was used as coarse material, fly ash, desulfurization gypsum, gasification slag, and furnace bottom slag as fine material, and cement as a gelling agent. The uniaxial compressive strength (UCS) and bleeding rate of coal-based solid waste cemented backfill (CBSWCB) were tested by an orthogonal experiment, and the influencing factors of mechanical properties and strength development were analyzed. The multiple generalized linear model of strength and bleeding rate was established, and the optimal filling material ratio was determined. The engineering performance index of CBSWCB with the optimal ratio was tested. The results show the following points: (1) the concentration and content of desulfurization gypsum had a great influence on the early compressive strength of CBSWCB, while fly ash, gasification slag, and furnace bottom slag had little influence on the early compressive strength. (2) High concentration, high content of fly ash and furnace bottom slag, low content of desulfurization gypsum, and gasification slag can significantly improve the early strength. High concentration and high content of fly ash, low content of gasification slag, furnace bottom slag, and desulfurization gypsum are beneficial to the later strength increase. (3) Under the optimal ratio scheme, the bleeding rate of CBSWCB was 1.6%, the slump was 16.6 cm, the cohesion was general, the segregation resistance was good, the initial setting time was 5.42 h, the final setting time was 7 h, and the early strength after curing for 8 h reached 0.24 MPa. Full article
(This article belongs to the Special Issue Green Low-Carbon Technology for Metalliferous Minerals)
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<p>Ecological and environmental problems caused by large-scale mining of coal resources.</p>
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<p>Application of coal-based solid waste in paste filling.</p>
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<p>Analysis of main components of coal-based solid waste filling materials.</p>
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<p>X-ray diffraction (XRD) of coal-based solid waste filling material.</p>
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<p>SEM microstructure of coal-based solid waste filling material, with (<b>a</b>) coal gangue, (<b>b</b>) fly ash, (<b>c</b>) gasification slag, (<b>d</b>) furnace bottom slag, (<b>e</b>) desulfurization gypsum, and (<b>f</b>) cement in the figure.</p>
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<p>The geographical location of the mining area and sources of coal-based solid waste materials.</p>
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<p>Particle size distribution diagram of coal-based solid waste materials, including (<b>a</b>) fly ash, (<b>b</b>) gasification slag, (<b>c</b>) bottom slag, (<b>d</b>) desulfurized gypsum.</p>
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<p>Partial specimen of CBSWCB.</p>
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<p>Test system.</p>
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<p>Influence of concentration and ash/gangue ratio on strength development.</p>
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<p>Influence of gasification slag, bottom slag and desulfurized gypsum on strength development.</p>
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<p>Effect of coal-based solid waste filling material on bleeding rate. (<b>a</b>) Factors of B and C; (<b>b</b>) factors of C and E; (<b>c</b>) factors of B and E; (<b>d</b>) factors of A and E; (<b>e</b>) factors of A and B; (<b>f</b>) factors of A and C; (<b>g</b>) factors of A and D; (<b>h</b>) factors of B and D; (<b>i</b>) factors of C and D.</p>
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<p>Influence of C and D factors on compressive strength of different curing ages. (<b>a</b>) 3 d UCS; (<b>b</b>) 7 d UCS; (<b>c</b>) 28 d UCS.</p>
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<p>Engineering performance inspection of coal-based solid waste filling body. (<b>a</b>) Slump test; (<b>b</b>) cohesion test; (<b>c</b>) water retention test; (<b>d</b>) initial setting time test; (<b>e</b>) final setting time test.</p>
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14 pages, 6749 KiB  
Article
The Characteristics of Spiral Pipe Increasing Resistance and Reducing Pressure and the Amendment Equation of Stowing Gradient
by Weixiang Wang, Hongwei Mu, Guodong Mei, Lijie Guo, Xinqi Lu, Anhu Wang and Ran Sun
Metals 2022, 12(7), 1105; https://doi.org/10.3390/met12071105 - 28 Jun 2022
Cited by 3 | Viewed by 2276
Abstract
To solve the high slurry pressure and severe wear at some sections in backfilling pipelines, this study investigates the solution of using an auxiliary pipe to increase the resistance and reduce the pressure of the mine backfilling pipeline. Using computational fluid dynamics, three [...] Read more.
To solve the high slurry pressure and severe wear at some sections in backfilling pipelines, this study investigates the solution of using an auxiliary pipe to increase the resistance and reduce the pressure of the mine backfilling pipeline. Using computational fluid dynamics, three auxiliary pipe models, a Z-shaped pipe, a S-shaped pipe and a spiral pipe were constructed and the velocity and pressure distribution characteristics of the filling slurry in the auxiliary pipes were analyzed. The function of friction loss in spiral pipes with different pitches and spiral diameters was established, and the amendment equation for calculating the effective stowing gradient was studied when using spiral pipes to increase resistance and reduce pressure. The results show that, compared with the Z-shaped pipe and the S-shaped pipe, the velocity and pressure in the spiral pipe change continuously and steadily, and there is no obvious sudden change in the local velocity and pressure. Therefore, it is difficult to burst the pipe. When the velocity is 2.5 m/s and the vertical height of the pipe is 2.5 m, the friction loss of the filling slurry in the spiral pipe can reach 3.87~21.26 times that in the vertical pipe, indicating that the spiral pipe can effectively play the role of increasing resistance and reducing pressure. The relationship between the friction loss and spiral diameter is a linear function, and the relationship between the friction loss and pitch is a quadratic function. The three are binary quadratic function relationships. The equation for calculating the effective stowing gradient is obtained, which provides a convenient method for engineering applications and industrial design. Full article
(This article belongs to the Special Issue Green Low-Carbon Technology for Metalliferous Minerals)
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<p>Increasing resistance and reducing pressure schematic of auxiliary pipe (illustration by authors). 1—Program-controlled electric valve, 2—auxiliary pipe, 3—pressure change of vertical pipe of L-shaped pipe, 4—pressure change of vertical pipe after using auxiliary pipe.</p>
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<p>Models of the Z-shaped pipe (<b>a</b>), the S-shaped pipe (<b>b</b>) and the spiral pipe (<b>c</b>).</p>
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<p>Models of the L-shaped pipe (<b>a</b>,<b>b</b>) elbow of the L-shaped pipe.</p>
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<p>Preparation process of the filling slurry sample. (<b>a</b>) Weigh tailings of a certain mass, (<b>b</b>) weigh cementitious materials of a certain mass, (<b>c</b>) weigh some water, (<b>d</b>) pour the tailings, curing material and water into the hopper of the mixer successively and mix for 10 min at 60 r/min to evenly distribute the components.</p>
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<p>Slurry under test (<b>a</b>), Brookfield R/S Plus rheometer (<b>b</b>) and rheological curve of filling slurry (<b>c</b>).</p>
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<p>Velocity field (<b>a</b>) and pressure field (<b>b</b>) of the filling slurry in the Z-shaped pipe.</p>
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<p>Velocity field (<b>a</b>) and pressure field (<b>b</b>) of the filling slurry in the S-shaped pipe.</p>
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<p>Velocity field (<b>a</b>) and pressure field (<b>b</b>) of the filling slurry in the spiral pipe.</p>
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<p>Spiral pipe models with the same height, spiral diameter <span class="html-italic">W</span> and different pitch <span class="html-italic">Q</span>. (<b>a</b>) <span class="html-italic">Q</span> = 0.25, <span class="html-italic">W</span> = 0.75, (<b>b</b>) <span class="html-italic">Q</span> = 0.50, <span class="html-italic">W</span> = 0.75, (<b>c</b>) <span class="html-italic">Q</span> = 0.75, <span class="html-italic">W</span> = 0.75, (<b>d</b>) <span class="html-italic">Q</span> = 1.00, <span class="html-italic">W</span> = 0.75, (<b>e</b>) <span class="html-italic">Q</span> = 1.25, <span class="html-italic">W</span> = 0.75.</p>
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<p>∆<span class="html-italic">P</span> vs. <span class="html-italic">Q</span> at different <span class="html-italic">W</span>.</p>
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<p>∆<span class="html-italic">P</span> vs. <span class="html-italic">W</span> at different <span class="html-italic">Q</span>.</p>
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<p>Three-dimensional coordinate diagram of ω with <span class="html-italic">Q</span> and <span class="html-italic">W</span>.</p>
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19 pages, 7527 KiB  
Article
Regional Distribution and Causes of Global Mine Tailings Dam Failures
by Shui-Quan Lin, Guang-Jin Wang, Wen-Lian Liu, Bing Zhao, Ying-Ming Shen, Meng-Lai Wang and Xiao-Shuan Li
Metals 2022, 12(6), 905; https://doi.org/10.3390/met12060905 - 26 May 2022
Cited by 42 | Viewed by 6320
Abstract
Tailings ponds are one of the three major production facilities in metal mines. The volume of tailings increases year by year, but the storage capacity of existing tailings ponds is limited. Therefore, tailings dams must become more fine-grained and larger. The potential hazard [...] Read more.
Tailings ponds are one of the three major production facilities in metal mines. The volume of tailings increases year by year, but the storage capacity of existing tailings ponds is limited. Therefore, tailings dams must become more fine-grained and larger. The potential hazard they represent should not be underestimated. This paper reveals the causes and regional distribution patterns of 342 tailings dam failures globally from 1915 to 2021 through statistical analysis. It was found that tailings pond failures occur almost every year, with an average of 4.4 accidents/year (1947–2021). The frequency has been gradually increasing in recent years, and most tailings pond failures are directly related to heavy rainfall or earthquakes. The frequency of tailings pond failures was significantly higher in Asia (21.3%) and the Americas (57.9%), especially in China (n = 43) and the United States (n = 107). Causes of tailings pond failures differed among regions. Most tailings pond failures in Asia and Europe were related to hydroclimate, while those in South America were mainly triggered by earthquakes. This study will provide theoretical data for the pre-design as well as the safe and stable operation of global tailings ponds, which will help to prevent global tailings pond failures. Full article
(This article belongs to the Special Issue Green Low-Carbon Technology for Metalliferous Minerals)
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Figure 1
<p>Feijío tailings pond dam failure, Brazil, 2019. (<b>a</b>) Before dam-failure; (<b>b</b>) Dam-failure 5.5s; (<b>c</b>) Dam-failure 6.7s; (<b>d</b>) Dam-failure 11s; (<b>e</b>) Dam-failure 18s; (<b>f</b>) Dam-failure completed.</p>
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<p>Feijío tailings pond dam failure, Brazil, 2019. (<b>a</b>) Before dam-failure; (<b>b</b>) Dam-failure 5.5s; (<b>c</b>) Dam-failure 6.7s; (<b>d</b>) Dam-failure 11s; (<b>e</b>) Dam-failure 18s; (<b>f</b>) Dam-failure completed.</p>
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<p>Temporal distribution of tailings pond failures (TSF—Tailings Storage Facility).</p>
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<p>Three-dimensional distribution of tailings pond failures.</p>
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<p>Magnitude of tailings pond failures over time.</p>
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<p>Three-dimensional diagram of the relationship between dam construction method and dam failure causes.</p>
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<p>Global distribution of tailings dam events.</p>
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<p>Causes in regions with a high frequency of tailings dam failures.</p>
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<p>Causes of tailings pond failures in different mines.</p>
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<p>Dam height distributions of tailings dam failures for different mines.</p>
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<p>Linear regression analysis of dam height.</p>
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<p>Relationship between the proportion of released tailings and the dam construction method after dam failure.</p>
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<p>Relationship between the proportion of released tailings and the hazard level after dam failure.</p>
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<p>Relationship between tailings storage volume and release volume. (<b>a</b>) Before logarithmic transformation; (<b>b</b>) after logarithmic transformation.</p>
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<p>Global geographic distribution of tailings pond dam failures.</p>
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<p>Distribution of global mines in seismic zones.</p>
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<p>Global climate and seismic zone distribution.</p>
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<p>Global average rainfall distribution.</p>
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11 pages, 1790 KiB  
Article
A Particle Size Distribution Model for Tailings in Mine Backfill
by Zongnan Li, Lijie Guo, Yue Zhao, Xiaopeng Peng and Khavalbolot Kyegyenbai
Metals 2022, 12(4), 594; https://doi.org/10.3390/met12040594 - 30 Mar 2022
Cited by 11 | Viewed by 3536
Abstract
With the increasing awareness of sustainable mining, the cement tailings backfill (CTB) method has been developed rapidly over the past decades. In the CTB technique, the two main mechanical properties engineers were concerned with are the rheological properties of CTB slurry and the [...] Read more.
With the increasing awareness of sustainable mining, the cement tailings backfill (CTB) method has been developed rapidly over the past decades. In the CTB technique, the two main mechanical properties engineers were concerned with are the rheological properties of CTB slurry and the resulting CTB strength after curing. Particle size distribution (PSD) of tailings material or PSD of the slurry is a significant factor that highly influences the rheological of CTB slurry and the strength performance of CTB. However, the concentrically partial size distribution curve and existing mathematical model could not represent the PSD of tailings material. In this study, a mathematical model for the particle size distribution of mine tailings was established using three model coefficients A B and K, which mainly reflect the characteristics of particles from three aspects respectively, the average size of particles, the proportion of the coarse or the fine parts of particles, and the distribution width of particles; meanwhile, an optimal coefficient solution method based on error analysis is given. Twelve tailing materials sourced from metal mines around China were used for the model establishment and validation. The determination coefficient of error analysis (R2) for all twelve modeled PSD lognormal curves was more significant than 0.99, and the modeled PSD lognormal curves are highly consistent with the determined particle size distribution curve. Full article
(This article belongs to the Special Issue Green Low-Carbon Technology for Metalliferous Minerals)
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<p>The particle size distribution of twelve different tailings.</p>
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<p>Loop iteration calculation method chart (Main loop idea: Set the circulation step of <span class="html-italic">K</span> value as 1.0, and calculate the <span class="html-italic">A</span> and <span class="html-italic">B</span> values according to the measured points. If the fitting coefficient <span class="html-italic">R</span><sup>2</sup> of the model is greater than 0.99, it is regarded as the potential solution, and the potential solution appears three times in a row is the optimal solution, otherwise the output failures.).</p>
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<p>Model curve under different coefficient <span class="html-italic">A</span>.</p>
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<p>Model curve under different coefficient <span class="html-italic">B</span>.</p>
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<p>Model curve under different Coefficient <span class="html-italic">K</span>.</p>
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<p>Model curve of tailings samples.</p>
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<p>Comparison between modeled PSD curve and measured PSD curve.</p>
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14 pages, 9195 KiB  
Article
Numerical Modelling of Blasting Dust Concentration and Particle Size Distribution during Tunnel Construction by Drilling and Blasting
by Jianjun Shi, Wei Zhang, Shucheng Guo and Huaming An
Metals 2022, 12(4), 547; https://doi.org/10.3390/met12040547 - 23 Mar 2022
Cited by 18 | Viewed by 3173
Abstract
In order to reduce the blasting dust concentration in the tunnel during the drilling and blasting, accelerate the tunnel excavation process, and improve the working environment for the construction workers, a three-dimensional geometric model of dust transport was established based on the gas-solid [...] Read more.
In order to reduce the blasting dust concentration in the tunnel during the drilling and blasting, accelerate the tunnel excavation process, and improve the working environment for the construction workers, a three-dimensional geometric model of dust transport was established based on the gas-solid two-phase flow model using the DesginModeler software, and the discrete phase model (DPM) in the FLUENT software was used to simulate the variation of dust concentration and the distribution of dust particle size at different locations along the tunnel route within 1200 s after tunnel blasting. The results showed that the concentration of blasting dust gradually decreased over time, with the fastest decrease in the range of 2 s to 120 s, and after 900 s, the dust concentration stabilized. The overall spatial distribution of the dust concentration showed a trend of decreasing from the palm face to the tunnel entrance and from the bottom plate to the upper part. The distribution pattern of dust with different particle sizes was not the same along the length of the tunnel. The large particles settled in the area of 25 m from the palm face under the action of gravity. With the increases of distance, the mass flow rate decreased, and the dust particle size became smaller, but the proportion of small particles gradually increased, while the R-R distribution index increased. The results in this study were confirmed to be reliable by comparing the measured data to provide guidance for the dust reduction technology in tunnel blasting, so as to quickly remove the dust generated during the blasting process and improve the engineering construction efficiency. Full article
(This article belongs to the Special Issue Green Low-Carbon Technology for Metalliferous Minerals)
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<p>Tunnel geometry model and meshing.</p>
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<p>Distribution of airflow streamlines in the tunnel.</p>
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<p>Wind speed body of the tunnel space.</p>
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<p>Distribution of blasting dust concentration at a 1.5 m height.</p>
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<p>Dust concentration cloud map with time at three height levels.</p>
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<p>Curves of the blasting dust concentration with time at three height levels.</p>
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<p>Trajectory of blasting dust over time.</p>
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<p>Trajectory of blasting dust over time.</p>
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<p>Distribution of the dust particle size at different locations along the tunnel.</p>
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<p>Distribution of the dust particle size at different locations along the tunnel.</p>
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<p>Comparison between the simulated and measured values of the dust concentration.</p>
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19 pages, 10889 KiB  
Article
A Numerical Model for the Compressive Behavior of Granular Backfill Based on Experimental Data and Application in Surface Subsidence
by Zhi-Hua Le, Qing-Lei Yu, Jiang-Yong Pu, Yong-Sheng Cao and Kai Liu
Metals 2022, 12(2), 202; https://doi.org/10.3390/met12020202 - 21 Jan 2022
Cited by 8 | Viewed by 3394
Abstract
Granular backfill is generally confined in stopes to bear underground pressure in metal mines. Its mechanical behavior under lateral confinement is vital for controlling stope wall behavior and estimating surface subsidence in backfill mining operations. In this paper, an experimental apparatus has been [...] Read more.
Granular backfill is generally confined in stopes to bear underground pressure in metal mines. Its mechanical behavior under lateral confinement is vital for controlling stope wall behavior and estimating surface subsidence in backfill mining operations. In this paper, an experimental apparatus has been developed to explore the bearing process of granular material. Pebbles were selected to model granular backfill. A series of compression experiments of pebble aggregation were performed under lateral confinement condition using the experimental apparatus. The bearing characteristics of the pebble aggregation with seven gradations were analyzed. Based on the experimental data, a constitutive model that takes the real physical characteristics of granular material into account was proposed with variable deformation modulus. The constitutive model was implemented into the FLAC3D software and verified basically by comparison with experimental results. The surface subsidence in backfilling mines was studied using the proposed model. The effects of the particle size of the granular backfill and the height and buried depth of mined-out stopes on surface subsidence have been clarified. The research results are of great significance for guiding backfill mining and evaluating surface subsidence and movement. Full article
(This article belongs to the Special Issue Green Low-Carbon Technology for Metalliferous Minerals)
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<p>Testing system.</p>
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<p>Seven gradations of pebbles and 3D scan image of particles.</p>
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<p>Stress–strain curves of pebbles with seven gradations.</p>
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<p>Deformation modulus (<math display="inline"><semantics> <mrow> <msub> <mi>E</mi> <mi>t</mi> </msub> </mrow> </semantics></math>) and AE energy of the pebbles in response to the axial strain: (<b>a</b>) 4.75–9.5 mm; (<b>b</b>) 16–20 mm; (<b>c</b>) 31.5–37.5 mm.</p>
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<p>Relationship between <math display="inline"><semantics> <mrow> <msub> <mi>E</mi> <mi>t</mi> </msub> </mrow> </semantics></math> and <math display="inline"><semantics> <mrow> <msub> <mi>ε</mi> <mi>v</mi> </msub> </mrow> </semantics></math>. (<b>a</b>) 4.75–9.5 mm; (<b>b</b>) 16–20 mm; (<b>c</b>) 31.5–37.5 mm.</p>
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<p>Numerical modeling procedure for granular material.</p>
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<p>Comparison of the axial stress-axial strain curves obtained by experiment and simulation.</p>
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<p>Numerical model in FLAC<sup>3D</sup>.</p>
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<p>Comparison of the surface subsidence and horizontal movement obtained by the proposed model and the double-yield model: (<b>a</b>) Surface subsidence; (<b>b</b>) Surface horizontal movement.</p>
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<p>Stress nephogram along the length: (<b>a</b>) Mined-out stope unfilled; (<b>b</b>) Mined-out stope filled with pebbles of 4.75–9.5 mm.</p>
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<p>Subsidence of overlying strata: (<b>a</b>) Mined-out stope unfilled; (<b>b</b>) Mined-out stope filled with pebbles of 4.75–9.5 mm.</p>
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<p>Surface subsidence and horizontal movement with different particle sizes: (<b>a</b>) Subsidence; (<b>b</b>) Horizontal movement.</p>
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<p>Characteristics of surface subsidence and movement with different particle sizes: (<b>a</b>) Inclination deformation; (<b>b</b>) Curvature deformation; (<b>c</b>) Horizontal deformation.</p>
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<p>Relationship between maximal surface subsidence and deformation modulus of the granular backfill.</p>
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<p>Surface subsidence basins for the granular backfill with various particle sizes: (<b>a</b>) 4.75–9.5 mm, (<b>b</b>) 9.5–13.2 mm, (<b>c</b>) 13.2–16 mm, (<b>d</b>) 16–20 mm, (<b>e</b>) 20–26.5 mm, (<b>f</b>) 26.5–31.5 mm, (<b>g</b>) 31.5–37.5 mm.</p>
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<p>Surface subsidence basins for the granular backfill with various particle sizes: (<b>a</b>) 4.75–9.5 mm, (<b>b</b>) 9.5–13.2 mm, (<b>c</b>) 13.2–16 mm, (<b>d</b>) 16–20 mm, (<b>e</b>) 20–26.5 mm, (<b>f</b>) 26.5–31.5 mm, (<b>g</b>) 31.5–37.5 mm.</p>
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<p>Maximal value of surface subsidence and movement in the backfilling cases (height of the stope) with different particle sizes: (<b>a</b>) Surface subsidence; (<b>b</b>) Horizontal movement; (<b>c</b>) Inclination deformation; (<b>d</b>) Curvature deformation; (<b>e</b>) Horizontal deformation.</p>
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<p>Maximal value of surface subsidence and movement in the backfilling cases (depth of the stope) with different particle sizes: (<b>a</b>) Surface subsidence; (<b>b</b>) Horizontal movement; (<b>c</b>) Inclination deformation; (<b>d</b>) Curvature deformation; (<b>e</b>) Horizontal deformation.</p>
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12 pages, 1824 KiB  
Article
Copper and Zinc Recovery from Sulfide Concentrate by Novel Artificial Microbial Community
by Xinglan Cui, Xuetao Yuan, Hongxia Li, Xiaokui Che, Juan Zhong, Lei Wang, Ying Liu, Xuewu Hu, Qidong Zhang, Rongzhen Jin and Qi Zheng
Metals 2022, 12(1), 45; https://doi.org/10.3390/met12010045 - 25 Dec 2021
Cited by 2 | Viewed by 2891
Abstract
Exploring efficient methods to enhance leaching efficiency is critical for bioleaching technology to deal with sulfide concentrate. In our study, a novel artificial microbial community was established to augment the bioleaching efficiency and recovery of copper (Cu) and zinc (Zn). The optimum parameters [...] Read more.
Exploring efficient methods to enhance leaching efficiency is critical for bioleaching technology to deal with sulfide concentrate. In our study, a novel artificial microbial community was established to augment the bioleaching efficiency and recovery of copper (Cu) and zinc (Zn). The optimum parameters in bioleaching experiments were explored according to compare a series of conditions from gradient experiments: the pH value was 1.2, temperature was 45 °C, and rotation speed was 160 r/min, which were different with pure microorganism growth conditions. Under optimal conditions, the result of recovery for Cu and Zn indicated that the average leaching rate reached to 80% and 100% respectively, which almost increased 1.8 times and 1.2 times more than control (aseptic condition) group. Therefore, this method of Cu and Zn recovery using a new-type artificial microbial community is expected to be an environmentally-friendly and efficient bioleaching technology solution, which has the potential of large-field engineering application in the future. Full article
(This article belongs to the Special Issue Green Low-Carbon Technology for Metalliferous Minerals)
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<p>Powder XRD pattern for sulfide concentrate.</p>
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<p>(<b>a</b>) Sieve size distribution for different minerals in sulfide concentrate; (<b>b</b>) liberation classes results for sulfide concentrate.</p>
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<p>Culture condition results of (<b>a</b>) pH, (<b>b</b>) temperature, and revolving speed for artificial microbial community.</p>
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<p>Leaching efficiency for Cu and Zn under (<b>a</b>) different pH and (<b>b</b>) different temperature conditions by the artificial microbial community.</p>
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<p>Leaching efficiency curves determined by ore pulp density and inoculation quantity.</p>
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<p>Copper and zinc recovery by the novel artificial microbial community.</p>
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14 pages, 3419 KiB  
Article
Experimental Study on Factors Influencing the Strength Distribution of In Situ Cemented Tailings Backfill
by Xiaopeng Peng, Lijie Guo, Guangsheng Liu, Xiaocong Yang and Xinzheng Chen
Metals 2021, 11(12), 2059; https://doi.org/10.3390/met11122059 - 20 Dec 2021
Cited by 11 | Viewed by 2913
Abstract
Previous studies have found that the strength of in situ cemented tailings backfill usually presents an S-shaped distribution, which decreases first, then increases, and decreases thereafter along the direction of slurry flow. In this study, to explore the factors determining the distribution, a [...] Read more.
Previous studies have found that the strength of in situ cemented tailings backfill usually presents an S-shaped distribution, which decreases first, then increases, and decreases thereafter along the direction of slurry flow. In this study, to explore the factors determining the distribution, a similar model test of cemented tailings backfill was carried out. The distribution law of grain size composition and the cement content of backfill materials along the flow direction were experimentally studied, and the comprehensive factor influencing the strength distribution was analyzed. The results show that, firstly, near the feeding point, there are more coarse particles, whereas the content of fine particles is higher farther away. The measured maximum median particle size can be more than three times the minimum value. Secondly, the cement content increases gradually along the flow direction and reaches the peak at the end of the model, which can be more than twice the minimum value, indicating that the degree of segregation is significant. Thirdly, the strength distribution of cemented backfills is comprehensively determined by both the particle size distribution (PSD) and the cement content. The maximum value appears neither at the point with peak median particle size, nor at the point with the highest cement content. Lastly, there is a strong linear correlation between the strength of cemented backfills and the strength factor (SF), which is defined as the product of the uniformity coefficient and cement content of filling materials, indicating that the SF can be used to quantitatively reflect the comprehensive effects of PSD and cement content on the strength. As SF is a comprehensive quantitative index reflecting the distribution of strength, it will be further studied in later research to acquire more experimental results of the relationship between sample strength and SF, which will be meaningful for the quality evaluation of in situ cemented backfills, and the optimization of backfill system. Full article
(This article belongs to the Special Issue Green Low-Carbon Technology for Metalliferous Minerals)
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<p>Diagram of the flume model test system. (<b>a</b>) Picture of the flume model; (<b>b</b>) the components of the test system.</p>
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<p>Particle size distribution (PSD) of the tailings used in the study.</p>
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<p>Illustration of sampling scheme of model test from top view.</p>
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<p>The final profile of backfill slurries after flowing in the test model.</p>
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<p>The cemented tailings backfill (CTB) specimens drilled from different areas after the flume test. (<b>a</b>) The specimens obtained; (<b>b</b>) the uniaxial compressive strength (UCS) testing process; (<b>c</b>) the specimen after failure.</p>
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<p>The strength distribution of backfill samples along the flowing direction.</p>
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<p>Verification chart of the cement contents of sampling cores in different rows.</p>
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<p>Comparison chart of the cement contents and UCS of samples in row 2 along the flowing direction.</p>
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<p>Comparison chart of the median particle sizes and UCS of samples in row 2 along the flowing direction.</p>
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<p>Comparison chart of the strength factor (SF) values and UCS of samples in row 2.</p>
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15 pages, 87158 KiB  
Article
Response of Floc Networks in Cemented Paste Backfill to a Pumping Agent
by Jiaqi Zhu, Shunchuan Wu, Haiyong Cheng, Xiaojie Geng and Jin Liu
Metals 2021, 11(12), 1906; https://doi.org/10.3390/met11121906 - 26 Nov 2021
Cited by 4 | Viewed by 1856
Abstract
Cemented paste backfill is critical for the development of green mines, the safe exploitation of mineral resources deep underground, and the efficient disposal of solid wastes produced by mining. In this paper, the mechanism underpinning how the pumping agent works was studied. The [...] Read more.
Cemented paste backfill is critical for the development of green mines, the safe exploitation of mineral resources deep underground, and the efficient disposal of solid wastes produced by mining. In this paper, the mechanism underpinning how the pumping agent works was studied. The number, area, and fractal dimension of pores in the microstructure of fresh paste were quantitatively analyzed using scanning electron microscopy (SEM), image processing, and fractal theory, and the response of flocs was investigated. The results show that floc networks disintegrated and the liquid network became the dominant structure under the action of the pumping agent, which enhanced the lubrication and promotion of multi-scale particles. In addition, the force chains became fragile and scattered, diminishing the yield stress of the paste. The pores had a more homogenized dimension and the porosity was 15.52% higher. The increase in the fractal dimension of the pores indicated that there was a higher self-similarity, in terms of microstructure, with a strengthened liquid network. The migration of floc structures contributed to the enhancement of the fluidity and rheology of the paste. This study provides insights into the effects of floc and liquid networks on the performance of paste, and it is of engineering significance in terms of realizing safe and efficient CPB operations. Full article
(This article belongs to the Special Issue Green Low-Carbon Technology for Metalliferous Minerals)
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<p>Location map of mining area.</p>
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<p>Particle size distribution of unclassified tailings.</p>
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<p>Schematic of slump tests: (<b>a</b>) size of the slump cone and (<b>b</b>) measurement of slump and divergence.</p>
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<p>The test program.</p>
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<p>Amount of slump and expansion degree with different pumping agents added.</p>
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<p>Yield stress curve for different pumping agent dosages.</p>
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<p>SEM image at magnification of 5000: (<b>a</b>) no pumping agent added; (<b>b</b>) pumping agent added.</p>
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<p>The floc structure: (<b>a</b>) SEM image; (<b>b</b>) schematic diagram.</p>
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<p>The concave structure formed after the breakage of flocs: (<b>a</b>) SEM image; (<b>b</b>) schematic diagram.</p>
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<p>Particle diameter measurement: (<b>a</b>) diameter of typical floc structure without pumping agent; (<b>b</b>) particle diameter after the addition of pumping agent.</p>
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<p>SEM pictures at a magnification of 1000 denoting the destructive effect of pumping agent on flocs: (<b>a</b>) CPB without pumping agent; (<b>b</b>) CPB with pumping agent.</p>
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<p>Binary analysis of a microscopic image of the paste without pumping agent and the extraction process of the force chain: (<b>a</b>) SEM image at a magnification of 5000; (<b>b</b>) binary image; (<b>c</b>) idealized sketch of force chain.</p>
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<p>Binary analysis of a microscopic image of paste with pumping agent and the extraction process of the force chain: (<b>a</b>) SEM image at a magnification of 5000; (<b>b</b>) binary image; (<b>c</b>) idealized sketch of force chain.</p>
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<p>Quantitative analysis of boundaries between particles and pores: (<b>a</b>) no pumping agent added; (<b>b</b>) pumping agent added.</p>
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<p>SEM images at 2000 magnification and binary pictures: (<b>a</b>) SEM without pumping agent; (<b>b</b>) SEM with pumping agent; (<b>c</b>) binary picture without pumping agent; (<b>d</b>) binary picture with pumping agent.</p>
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<p>Distribution of pores: (<b>a</b>) no pumping agent added; (<b>b</b>) pumping agent added.</p>
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<p>Calculation of fractal dimension: (<b>a</b>) Without pumping agent; (<b>b</b>) with pumping agent.</p>
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12 pages, 18109 KiB  
Article
Tailings Settlement Velocity Identification Based on Unsupervised Learning
by Jincheng Xie, Dengpan Qiao, Runsheng Han and Jun Wang
Metals 2021, 11(12), 1903; https://doi.org/10.3390/met11121903 - 26 Nov 2021
Cited by 2 | Viewed by 1449
Abstract
In order to reasonably and accurately acquire the settlement interface and velocity of tailings, an identification model of tailing settlement velocity, based on gray images of the settlement process and unsupervised learning, is constructed. Unsupervised learning is used to classify stabilized tailing mortar, [...] Read more.
In order to reasonably and accurately acquire the settlement interface and velocity of tailings, an identification model of tailing settlement velocity, based on gray images of the settlement process and unsupervised learning, is constructed. Unsupervised learning is used to classify stabilized tailing mortar, and the gray value range of overflow water is determined. Through the identification of overflow water in the settlement process, the interface can be determined, and the settlement velocity of tailings can be calculated. Taking the tailings from a copper mine as an example, the identification of tailings settling velocity was determined. The results show that the identification model of tailing settlement speed based on unsupervised learning can identify the settlement interface, which cannot be manually determined in the initial stage of settlement, effectively avoiding the subjectivity and randomness of manual identification, and provide a more scientific and accurate judgment. For interfaces that can be manually recognized, the model has high recognition accuracy, has a rapid and efficient recognition process, and the relative error can be controlled within 3%. It can be used as a new technology for measuring the settling velocity of tailings. Full article
(This article belongs to the Special Issue Green Low-Carbon Technology for Metalliferous Minerals)
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<p>Schematic diagram of the settlement process.</p>
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<p>Principle of unsupervised learning to identify settling velocity of tailings.</p>
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<p>Schematic diagram of experiment device.</p>
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<p>Settlement experiment: (<b>left</b>) mass concentration 15%, (<b>right</b>) mass concentration 20%.</p>
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<p>Determination of gray scale range of overflow water. (<b>a</b>) original image; (<b>b</b>) gray statistical chart; (<b>c</b>) visualization of classification results.</p>
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<p>Unsupervised learning recognition result of interface settlement.</p>
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<p>Comparison between the unsupervised learning recognition results and the manual recognition results.</p>
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21 pages, 1733 KiB  
Article
Dispatch Optimization Model for Haulage Equipment between Stopes Based on Mine Short-Term Resource Planning
by Ning Li, Shuzhao Feng, Haiwang Ye, Qizhou Wang, Mingtao Jia, Liguan Wang, Shugang Zhao and Dongfang Chen
Metals 2021, 11(11), 1848; https://doi.org/10.3390/met11111848 - 17 Nov 2021
Cited by 6 | Viewed by 2530
Abstract
The working environment of underground mines is complicated, making it difficult to construct an underground mine production plan. In response to the requirements for the preparation of a short-term production plan for underground mines, an optimization model for short-term resource planning was constructed, [...] Read more.
The working environment of underground mines is complicated, making it difficult to construct an underground mine production plan. In response to the requirements for the preparation of a short-term production plan for underground mines, an optimization model for short-term resource planning was constructed, with the goal of maximizing the total revenue during the planning period. The artificial bee colony optimization algorithm is used to solve the model using MATLAB. According to the basic requirements of underground mine ore haulage and ore hoisting, a haulage equipment inter-stopes dispatch plan model was constructed, with the primary goal of minimizing the haulage equipment wait time. A non-dominated sorting genetic algorithm is used to solve the optimization model. An underground mine is examined using the two models, and the optimization results are compared and verified with the scheme obtained by using traditional optimization algorithms. Results show that based on the improved optimization algorithm, the use of short-term production planning schemes to guide mine production operations can increase the haulage equipment utilization rate, thereby increasing mine production revenue. Full article
(This article belongs to the Special Issue Green Low-Carbon Technology for Metalliferous Minerals)
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<p>Location map.</p>
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<p>Mine layout.</p>
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<p>Horizontal direction mining rule.</p>
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<p>Simple dispatching model.</p>
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<p>Simple spatial model of ore blocks.</p>
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<p>Change curve of the target optimization value with evolutionary generation.</p>
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<p>Change curve of the target value with evolutionary generation.</p>
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<p>Operation route of the #1 scraper during a certain period of time.</p>
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23 pages, 5360 KiB  
Article
Propagation Laws of Reclamation Risk in Tailings Ponds Using Complex Network Theory
by Zhixin Zhen, Ying Zhang and Mengrong Hu
Metals 2021, 11(11), 1789; https://doi.org/10.3390/met11111789 - 6 Nov 2021
Cited by 7 | Viewed by 2062
Abstract
Accidents have occurred periodically in the tailings ponds where mine solid waste is stored in recent years, and thus their safety has become one of the constraints restricting the sustainable development of the mining industry. Reclamation is an important way to treat tailings [...] Read more.
Accidents have occurred periodically in the tailings ponds where mine solid waste is stored in recent years, and thus their safety has become one of the constraints restricting the sustainable development of the mining industry. Reclamation is an important way to treat tailings ponds, but improper reclamation methods and measures not only cannot reduce the accident risk of tailings ponds, but will further increase the pollution to the surrounding environment. The influencing factors of reclamation accidents in tailings ponds are complex, and the existing models cannot characterize them. In order to study the propagation process of tailings pond reclamation risk, this paper proposes a three-dimensional identification framework for accident hazards based on evidence (TDIFAHE) to identify all potential hazards that may occur during the reclamation stage, and obtain a list of hazards. Based on the complex network theory, this paper uses identified hazards as network nodes and the correlation between hazards as the edges of the network. Based on the identified hazard data, the evolution network of reclamation risk in tailings ponds (ENRRTP) is constructed. By analyzing the statistical characteristics of ENRRTP, it can be found that ENRRTP has small world and scale-free characteristics. The above characteristics show that the reclamation risk of tailings ponds is coupled with multiple factors and the disaster path is short. Giving priority to those hub hazards that have a dominant impact on the reclamation risk can significantly reduce the reclamation risk of the tailings pond. Full article
(This article belongs to the Special Issue Green Low-Carbon Technology for Metalliferous Minerals)
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<p>A flow chart of research methods and results.</p>
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<p>A three-dimensional identification framework for accident hazards based on evidence.</p>
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<p>Propagation process of reclamation risk in the tailings ponds.</p>
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<p>Node degree in the ENRRTP.</p>
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<p>Cumulative degree distribution of the ENRRTP.</p>
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<p>Clustering coefficient of the nodes in the ENRRTP.</p>
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<p>The equal-sized random network of the ENRRTP.</p>
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<p>Betweenness centrality of nodes in the ENRRTP.</p>
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<p>Mode of the PNRRGTP.</p>
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17 pages, 30490 KiB  
Article
Study and Analysis on the Influence Degree of Particle Settlement Factors in Pipe Transportation of Backfill Slurry
by Chonghao Wang and Deqing Gan
Metals 2021, 11(11), 1780; https://doi.org/10.3390/met11111780 - 5 Nov 2021
Cited by 12 | Viewed by 2579
Abstract
In this study, we developed a pipeline transport model to investigate the influence of particle sedimentation factors on slurry transportation through pipelines. The particle tracking module of the software was used to simulate the transport process, and the influences on the sedimentation rate [...] Read more.
In this study, we developed a pipeline transport model to investigate the influence of particle sedimentation factors on slurry transportation through pipelines. The particle tracking module of the software was used to simulate the transport process, and the influences on the sedimentation rate were analyzed considering the slurry concentration, particle size, and flow velocity. The established model exhibited small calculation errors. In addition, the results revealed that the proposed model is reliable for calculating the degree of influence of various factors on particle sedimentation. The effect of the particle sedimentation rate on the pipeline slurry was explored considering the particle size, slurry concentration, and flow velocity. The sedimentation rate was positively related to particle size and adversely related to the slurry concentration and flow velocity. Indeed, study on the sedimentation rate requires considering a reasonable range of particle sizes, preparing a slurry with an appropriate concentration, and adjusting an appropriate flow velocity. Numerical simulations were performed using the filling data as the background for a sample mining area. The experimental results showed optimal slurry concentration and particle size of 60% and 25.25 µm, respectively. Full article
(This article belongs to the Special Issue Green Low-Carbon Technology for Metalliferous Minerals)
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<p>(<b>a</b>) Volume of the particle size; (<b>b</b>) cumulative proportions of the particle size.</p>
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<p>Geometric simulation.</p>
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<p>Meshing pattern.</p>
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<p>A contour of the flow pattern of particle deposition.</p>
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<p>Pressure result.</p>
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<p>Experimental platform.</p>
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<p>Three-dimensional direct view.</p>
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<p>Relationship between the particle size and sedimentation velocity.</p>
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<p>Relationship between the concentration and sedimentation velocity.</p>
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<p>Relationship between the flow velocity and sedimentation velocity.</p>
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<p>Diagram of the mine filling system.</p>
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<p>Results of simulation experiment.</p>
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16 pages, 14528 KiB  
Article
Monitoring and Analysis of Dynamic Response for Open-Pit Mine with Inside Inclined Shafts under Train Loading
by Yong Wang, Song-Tao Ni, Fa-Wu Yang, Zhong-Xin Wang, Hong Zhang, Ke Ma and Xiao-Jun Li
Metals 2021, 11(11), 1681; https://doi.org/10.3390/met11111681 - 22 Oct 2021
Cited by 2 | Viewed by 2224
Abstract
The stability of open-pit mining is a hot issue in geotechnical engineering. A mining railroad is in operation on the slope where the east exhaust inclined shaft and the east sand injection inclined shaft on the Laohutai Mine are located, and it was [...] Read more.
The stability of open-pit mining is a hot issue in geotechnical engineering. A mining railroad is in operation on the slope where the east exhaust inclined shaft and the east sand injection inclined shaft on the Laohutai Mine are located, and it was necessary to determine whether railroad vibration would have an impact on the safety of the inclined shafts. With this project as the background, the dynamic response of the slope with inside two inclined shafts was conducted under train loading. A three-dimensional numerical model by using PLAXIS 3D was established to analyze the stability of the slope. The results show that the dynamic reaction caused by the full-loaded train is significantly greater than the no-load train. The safety factor of the slope under the dynamic load is 1.201, and the maximum displacement of the slope which occurred in the gravel layer directly beneath the train track is about 5 mm. The acceleration responses of the two inclined shafts are almost consistent. The maximum horizontal and vertical acceleration occur at the epidote weak layer. The acceleration directly below the load increases significantly. Therefore, it can be considered that the slopes are stable under the action of train vibration, and the influence on the two inclined shafts is small and negligible. Full article
(This article belongs to the Special Issue Green Low-Carbon Technology for Metalliferous Minerals)
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<p>Site picture of Laohutai Mine. (<b>a</b>) Schematic outline of the mine site; (<b>b</b>) road and railroad diagram of the mining area.</p>
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<p>Monitoring location diagram. (<b>a</b>) Schematic diagram of the measuring point layout. (<b>b</b>) Cross-sectional view of monitoring location.</p>
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<p>Monitoring instruments. (<b>a</b>) CF5920N dynamic signal test analyzer; (<b>b</b>) 173A500 Acceleration Sensor.</p>
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<p>Field monitoring situation. (<b>a</b>) Location of the railway tracks; (<b>b</b>) monitoring site.</p>
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<p>Calculation model diagram.</p>
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<p>Schematic diagram of dynamic load and inclined shaft position.</p>
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<p>Time range curve of train dynamic load.</p>
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<p>Schematic layout of measurement points. (<b>a</b>) East exhaust inclined shaft measurement point; (<b>b</b>) east sand injection inclined shaft measurement point.</p>
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<p>Ground vertical acceleration time. (<b>a</b>) Ground vertical acceleration time range curve at 1.5 m from the track; (<b>b</b>) ground horizontal acceleration time range curve at 1.5 m from the track.</p>
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<p>Acceleration change curve of each measuring point of the no-load train. (<b>a</b>) Horizontal acceleration change curve of each measuring point of the no-load train; (<b>b</b>) vertical acceleration change curve of each measuring point of the no-load train.</p>
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<p>Acceleration change curve of each measuring point of the fully load train. (<b>a</b>) Horizontal acceleration change curve of each measuring point of the fully load train; (<b>b</b>) vertical acceleration change curve of each measuring point of the fully load train.</p>
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<p>Comparison of acceleration simulation of measuring points above the injection shaft and measured results. (<b>a</b>) Comparison of horizontal acceleration simulation of measuring points above the injection shaft and measured results; (<b>b</b>) comparison of vertical acceleration simulation of measuring points above the injection shaft and measured results.</p>
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<p>Simulation results of acceleration of east exhaust inclined shaft. (<b>a</b>) Simulation results of horizontal acceleration of east exhaust inclined shaft; (<b>b</b>) simulation results of vertical acceleration of east exhaust inclined shaft.</p>
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<p>The displacement of slope. (<b>a</b>) Overall slope displacement; (<b>b</b>) mixed fill layer displacement; (<b>c</b>) gravelly soil displacement; (<b>d</b>) upper displacement of the epidote; (<b>e</b>) epidote weak layer displacement; and (<b>f</b>) sandstone displacement under the epidote.</p>
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<p>The displacement of slope. (<b>a</b>) Overall slope displacement; (<b>b</b>) mixed fill layer displacement; (<b>c</b>) gravelly soil displacement; (<b>d</b>) upper displacement of the epidote; (<b>e</b>) epidote weak layer displacement; and (<b>f</b>) sandstone displacement under the epidote.</p>
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<p>Slope safety factor.</p>
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<p>Displacement of east exhaust inclined shaft. (<b>a</b>) Horizontal displacement of east exhaust inclined shaft; (<b>b</b>) vertical displacement of east exhaust inclined shaft.</p>
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<p>Schematic diagram of relation between acceleration and inclined shaft length of east exhaust inclined shaft. (<b>a</b>) Schematic diagram of relation between horizontal acceleration and inclined shaft length of east exhaust inclined shaft; (<b>b</b>) schematic diagram of relation between vertical acceleration and inclined shaft length of east exhaust inclined shaft.</p>
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<p>Displacement of east injection inclined shaft. (<b>a</b>) Horizontal displacement of east injection inclined shaft; (<b>b</b>) vertical displacement of east injection inclined shaft.</p>
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<p>Schematic diagram of relation between acceleration and inclined shaft length of east injection inclined shaft. (<b>a</b>) Schematic diagram of relation between horizontal acceleration and inclined shaft length of east injection inclined shaft; (<b>b</b>) schematic diagram of relation between vertical acceleration and inclined shaft length of east injection inclined shaft.</p>
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14 pages, 3147 KiB  
Article
Experimental SHPB Study of Limestone Damage under Confining Pressures after Exposure to Elevated Temperatures
by Lei Liu, Rui Li, Hao Qin and Wei Sun
Metals 2021, 11(10), 1663; https://doi.org/10.3390/met11101663 - 19 Oct 2021
Cited by 9 | Viewed by 2377
Abstract
Studying the dynamic performance of rocks affected by high temperatures is a crucial theoretical foundation of mining engineering design and the construction of deep metallic mineral resources. More importantly, such studies can provide technical support for the green and low-carbon mining of these [...] Read more.
Studying the dynamic performance of rocks affected by high temperatures is a crucial theoretical foundation of mining engineering design and the construction of deep metallic mineral resources. More importantly, such studies can provide technical support for the green and low-carbon mining of these resources. However, systematic studies on the dynamic mechanical properties of rocks affected by both confining pressure and temperature during the mining of deep metallic mineral resources are lacking. Therefore, systematic research was conducted on the dynamic mechanical properties of limestone under confining pressure after high-temperature treatment, and a corresponding constitutive model was established. In this study, limestones were heated to 200 °C, 400 °C, 600 °C, and 800 °C, and the Split Hopkinson Pressure Bar impact test was conducted with confining pressures of 0.0 MPa, 0.5 MPa, 1.5 MPa, and 2.5 MPa. The test results show that the temperature has a significant effect on the dynamic compressive strength of limestone, and as the temperature rises, the strength tends to first increase and then decrease, reaching the turning point at a temperature of 400 °C. The dynamic compressive strength increases as the confining pressure increases. The constitutive equation of the dynamic damage to limestone under confining pressure after high-temperature treatment is consistent with the test results. Therefore, the established constitutive model can represent the dynamic behavior of limestone, providing a reference for evaluating the dynamic performance of this material, and serving as a theoretical basis for the green and low-carbon mining of deep metallic mineral resources. Full article
(This article belongs to the Special Issue Green Low-Carbon Technology for Metalliferous Minerals)
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<p>SHPB test system.</p>
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<p>Confining pressure device.</p>
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<p>Typical test curve for stress equalization.</p>
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<p>Limestone specimen.</p>
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<p>Heating temperature control curve.</p>
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<p>Dynamic stress–strain curves at different temperatures. (<b>a</b>) Impact velocity = 5.3 m/s; (<b>b</b>) Impact velocity = 8.6 m/s.</p>
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<p>The relationship between uniaxial dynamic compressive strength and the temperature of limestone.</p>
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<p>Dynamic stress–strain curve for a confining pressure of 0.5 MPa. (<b>a</b>) Impact velocity = 5.3 m/s; (<b>b</b>) impact velocity = 8.6 m/s.</p>
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<p>Dynamic stress–strain curve for a confining pressure of 1.5 MPa. (<b>a</b>) Impact velocity = 5.3 m/s; (<b>b</b>) impact velocity = 8.6 m/s.</p>
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<p>Dynamic stress–strain curve for a confining pressure of 2.5 MPa. (<b>a</b>) Impact velocity = 5.3 m/s; (<b>b</b>) impact velocity = 8.6 m/s.</p>
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<p>Dynamic compressive strength of limestone under different confining pressures after high-temperature treatment. (<b>a</b>) Impact velocity = 5.3 m/s; (<b>b</b>) impact velocity = 8.6 m/s.</p>
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<p>Differential element model.</p>
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<p>Fitting of the dynamic damage constitutive model. (<b>a</b>) Confining pressure = 0 MPa; (<b>b</b>) confining pressure = 2.5 MPa.</p>
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16 pages, 4425 KiB  
Article
Structural Parameter Optimization for Large Spacing Sublevel Caving in Chengchao Iron Mine
by Yuye Tan, Mochuan Guo, Yimin Hao, Chi Zhang and Weidong Song
Metals 2021, 11(10), 1619; https://doi.org/10.3390/met11101619 - 12 Oct 2021
Cited by 8 | Viewed by 2239
Abstract
Non-pillar sublevel caving is beginning to use large structural parameters in China. Appropriate structural parameters can effectively control the loss and dilution of stope and improve ore drawing efficiency. In this study, taking Chengchao Iron Mine as the engineering background, a theoretical calculation, [...] Read more.
Non-pillar sublevel caving is beginning to use large structural parameters in China. Appropriate structural parameters can effectively control the loss and dilution of stope and improve ore drawing efficiency. In this study, taking Chengchao Iron Mine as the engineering background, a theoretical calculation, a numerical simulation, and physical similarity experiments were combined to optimize sublevel height, production drift spacing, and drawing space. The optimal structural parameter range, based on the ellipsoid ore drawing theory, was obtained as a theoretical reference for subsequent studies. A “two-step” strategy was used, in which PFC2D software (Itasca Consulting Group, Minneapolis, MN, USA) was used to numerically simulate 20 groups of different sublevel heights and production drift spacing parameters were used to determine the appropriate sublevel height and production drift spacing for the project. Subsequently, the optimization of the ore drawing space was studied using PFC3D (Itasca Consulting Group, Minneapolis, MN, USA) particle unit software, numerical simulation analysis, and similar physical experiments. The results showed that safe and efficient mining can be achieved when the structural parameters of the stope are 17.5 m sublevel height, 20 m production drift spacing, and 6 m drawing space. The findings of this study can further the goal of green and efficient mining, and provide a theoretical reference for the popularization and application of pillarless sublevel caving with large structural parameters at home and abroad. It is an effective measure for the green mining of caving mines. Full article
(This article belongs to the Special Issue Green Low-Carbon Technology for Metalliferous Minerals)
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<p>Arrangement of large space of discharged ellipsoid.</p>
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<p>The ellipsoid arrangement is released in the direction of the vertical access.</p>
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<p>Schematic of the model: (<b>a</b>) schematic of model size, m; (<b>b</b>) 2D numerical model diagram.</p>
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<p>Numerical simulation of ore drawing process: (<b>a</b>) subparagraph 1; (<b>b</b>) subparagraph 2; (<b>c</b>) subparagraph 3; (<b>d</b>) subparagraph 4.</p>
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<p>Relationship of the difference between recovery and dilution ratio Y and sublevel height H and production drift spacing B: (<b>a</b>) relationship curve of sublevel height H and the difference between recovery and dilution ratio Y; (<b>b</b>) relationship curve of production drift spacing B and the difference between recovery and dilution ratio Y.</p>
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<p>Relation curve of the difference between recovery and dilution ratio Y and sublevel height H and production drift spacing B.</p>
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<p>Top view of 3D visual model of No. II, III, and IV ore bodies from −500 m to −570 m.</p>
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<p>Single model design.</p>
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<p>Initial diagram of the single model: (<b>a</b>) front view; (<b>b</b>) side view.</p>
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<p>Schematic of the drawn-out ore body: (<b>a</b>) front view contrast of the drawn-out ore body; (<b>b</b>) side view contrast of the drawn-out ore body.</p>
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<p>Relationship between ore recovery ratio and caving step.</p>
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<p>Relationship between ore dilution ratio and caving step.</p>
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<p>Relationship of the difference between recovery and dilution ratio Y and caving step.</p>
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<p>Physical ore drawing model. (<b>a</b>) Ore and waste rock particles; (<b>b</b>) Physical drawing model framework.</p>
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<p>Drawing process diagram (<b>a</b>) before drawing, (<b>b</b>) at the initial drawing stage, (<b>c</b>) at the middle drawing stage, and (<b>d</b>) at the end of ore drawing.</p>
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<p>Curves of the recovery indexes of sublevel ore in each structural parameter scheme: (<b>a</b>) recovery ratio curve of sublevel ore; (<b>b</b>) rock mixing ratio curve of sublevel ore; (<b>c</b>) curve of the difference between recovery and dilution ratio of sublevel ore y.</p>
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<p>Relationship between recovery indexes and drawing space from an overall perspective.</p>
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13 pages, 5555 KiB  
Article
Enhancing Arsenic Solidification/Stabilisation Efficiency of Metallurgical Slag-Based Green Mining Fill and Its Structure Analysis
by Wei Gao, Zifu Li, Siqi Zhang, Yuying Zhang, Pingfeng Fu, Huifen Yang and Wen Ni
Metals 2021, 11(9), 1389; https://doi.org/10.3390/met11091389 - 1 Sep 2021
Cited by 6 | Viewed by 2069
Abstract
To dispose of arsenic-containing tailings with low carbon and high efficiency, sodium sulphate (Na2SO4), sodium hydroxide (NaOH), calcium nitrate Ca(NO3)2 and calcium hydroxide Ca(OH)2 were independently added to metallurgical slag-based binder (MSB) solidification/stabilisation (S/S)-treated tailings [...] Read more.
To dispose of arsenic-containing tailings with low carbon and high efficiency, sodium sulphate (Na2SO4), sodium hydroxide (NaOH), calcium nitrate Ca(NO3)2 and calcium hydroxide Ca(OH)2 were independently added to metallurgical slag-based binder (MSB) solidification/stabilisation (S/S)-treated tailings (MSTs) to enhance the MST arsenic S/S performance. Results showed that only Ca(OH)2 could increase the unconfined compressive strength of MST from 16.3 to 20.49 MPa and decrease the leachate As concentration from 31 ?g/L to below 10 ?g/L. Na3AsO4·12H2O and NaAsO2 were used to prepare pure MSB paste for mechanism analysis. The results of microstructure analyses showed the high specific surface area and amorphous properties of calcium–sodium aluminosilicate hydrate facilitated the adsorption or solid-solution formation of As(V) and As(III). As(V) formed an inner-sphere complex in ettringite, whereas As(III) formed an outer-sphere complex, and the relatively larger size and charge of As(V) compared with SO42? restrict substitution inside channels without affecting the ettringite structure under high loading of As(V). The added Ca(OH)2 promoted the hydration reaction of MSBs and facilitated the formation of a Ca–As(V) precipitate with low solubility, from Ca4(OH)2(AsO4)2·4H2O (Ksp = 10?27.49) to Ca5(AsO4)3(OH) (Ksp = 10?40.12). This work is beneficial for the application of cement-free MSB in the S/S process. Full article
(This article belongs to the Special Issue Green Low-Carbon Technology for Metalliferous Minerals)
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<p>(<b>a</b>) UCS of MST samples at 3, 7 and 28 day; (<b>b</b>) As leachability of 28 day MST samples.</p>
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<p>The XRD patterns of (<b>a</b>) B, B(III) and B(V) paste; (<b>b</b>) B-C3, B-C3(III) and B-C3(V) paste.</p>
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<p>FTIR spectra of (<b>a</b>) ① and ② B sample, ③ and ④ B(III) sample and ⑤ and ⑥ B(V) sample; (<b>b</b>) ① and ② B-C3 sample, ③ and ④ B-C3(III) sample and ⑤ and ⑥ B-C3(V) sample.</p>
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<p>SEM-EDS result for (<b>a</b>) B-3d; (<b>b</b>) B-28 d; (<b>c</b>) B(V)-3 d; (<b>d</b>) B(V)-28 d; (<b>e</b>) B(III)-3 d; (<b>f</b>) B(III)-28 d.</p>
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<p>SEM-EDS result for (<b>a</b>) B-C3-3 d; (<b>b</b>) B-C3-28 d; (<b>c</b>) B-C3(V)-3 d; (<b>d</b>) B-C3(V)-28 d; (<b>e</b>) B-C3(III)-3 d; (<b>f</b>) B-C3(III)-28 d.</p>
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