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18 pages, 8503 KiB  
Article
Characterization of Gas Seepage in the Mining Goaf Area for Sustainable Development: A Numerical Simulation Study
by Bing Li, Hao Li, Yuchen Tian, Helong Zhang, Qingfa Liao, Shiheng Chen, Yinghai Liu, Yanzhi Liu, Shiqi Liu, Shuxun Sang and Sijian Zheng
Sustainability 2024, 16(20), 8978; https://doi.org/10.3390/su16208978 (registering DOI) - 17 Oct 2024
Abstract
An in-depth understanding of gas (oxygen and methane) seepage characteristics in coal mine goafs is essential for the safe production of mines and for advancing sustainable development practices within the mining industry. However, the gas distribution and its flow processes still remain ambiguous. [...] Read more.
An in-depth understanding of gas (oxygen and methane) seepage characteristics in coal mine goafs is essential for the safe production of mines and for advancing sustainable development practices within the mining industry. However, the gas distribution and its flow processes still remain ambiguous. In this article, we developed a three-dimensional porous media mining goaf mathematical model (considering the heterogeneity) to analyze the methane and oxygen flow features. Firstly, based on the variation laws of the “three zones”—the free caving zone, fracture zone, and subsidence zone—porosity changes in the vertical direction were set. A three-dimensional physical model of a fully mechanized caving mining area with a “U”-shaped ventilation system was established as the basis, and a COMSOL Multiphysics multi-field coupled model was built. Secondly, based on the established model, the characteristics of porosity distribution, mixed gas pressure changes, and the volume fraction of oxygen in the goaf were analyzed. The results show that as the distance from the working face increases, the compaction intensity in the mined-out area gradually rises, resulting in a decreasing porosity trend. The porosity distribution characteristics significantly impact the mechanical behavior and gas flow. The gas pressure inside the mined-out area is much higher than the surroundings, decreasing with depth. The upper and middle parts have the highest-pressure concentrations, requiring focused assessment and targeted monitoring measures based on the pressure characteristics of different regions. The oxygen concentration gradually decreases with depth due to poor ventilation, leading to potential explosive gas mixtures, necessitating ventilation system optimization, enhanced monitoring, and emergency preparedness. The gas exhibits vertical stratification, with higher concentrations in the upper and deep regions. Targeted drainage and ventilation methods can effectively control the gas concentration and ensure production safety. Full article
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Figure 1

Figure 1
<p>Distribution of mining rights in the Huainan mining area (Figure a shows the location of the study area within Anhui Province).</p>
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<p>Schematic diagram of the distribution of abandoned mining goafs in the Huainan mining area.</p>
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<p>Three-dimensional physical model of the mined-out area.</p>
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<p>Porosity distribution cloud map along the X direction of the caved area.</p>
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<p>Porosity distribution cloud map along the Z direction of the caved area.</p>
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<p>Donut-shaped porosity distribution characteristics at the bottom of the caved area.</p>
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<p>Pressure distribution cloud map in the Z-direction of the mined-out area.</p>
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<p>Pressure distribution contour map (Z = 1 m).</p>
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<p>Oxygen volume fraction distribution map in the mined-out area (Z= 1 m).</p>
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<p>Three-dimensional gas volume fraction distribution cloud map in the mined-out area.</p>
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<p>Gas volume fraction distribution cloud map in the Z-direction of the mined-out area (Z = 1 m).</p>
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13 pages, 2645 KiB  
Article
Assessing the Effectiveness of Turf Transplantation and Artificial Replanting in Restoring Abandoned Mining Areas
by Amannisa Kuerban, Guankui Gao, Abdul Waheed, Hailiang Xu, Shuyu Wang and Zewen Tong
Sustainability 2024, 16(20), 8977; https://doi.org/10.3390/su16208977 (registering DOI) - 17 Oct 2024
Abstract
Long-term and extensive mineral mining in the Kuermutu mine section of the Two Rivers Nature Reserve in the Altai region has disrupted the ecological balance between soil and vegetation. To assess the effectiveness of various restoration measures in this abandoned mine area, we [...] Read more.
Long-term and extensive mineral mining in the Kuermutu mine section of the Two Rivers Nature Reserve in the Altai region has disrupted the ecological balance between soil and vegetation. To assess the effectiveness of various restoration measures in this abandoned mine area, we compared two restoration approaches—natural turf transplantation (NTT) and replanted economic crop grassland (ARGC)—against an unaltered control (original grassland). We employed 11 evaluation indices to conduct soil and vegetation surveys. We developed a comprehensive evaluation model using the Analytic Hierarchy Process (AHP) to assess restoration outcomes for each grassland type. Our findings indicate that both NTT and ARGC significantly improved ecological conditions, such as reducing soil fine particulate matter loss and restoring vegetation cover. This brought these areas closer to their original grassland state. The species composition and community structure of the NTT and ARGC vegetation communities improved relative to the original grassland. This was due to a noticeable increase in dominant species’ importance value. Vegetation cover averaged higher scores in NTT, while the average height was greater in ARGC. The soil water content and soil organic carbon (SOC) varied significantly with depth (p < 0.05), following a general ‘V’ pattern. NTT positively impacted soil moisture content (SMC) at the surface, whereas ARGC influenced SMC in deeper layers, with the 40–50 cm soil layer achieving 48.13% of the original grassland’s SMC. SOC levels were highest in the control (original grassland), followed by ARGC and NTT, with ARGC showing the greatest organic carbon content at 20–30 cm depths. A comprehensive AHP ecological-economic evaluation revealed that restoration effectiveness scores were 0.594 for NTT and 0.669 for ARGC, translating to 59.4% and 66.9%, respectively. ARGC restoration was found to be more effective than NTT. These results provide valuable insights into ecological restoration practices for abandoned mines in Xinjiang and can guide future effectiveness evaluations. Full article
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Figure 1

Figure 1
<p>Study area.</p>
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<p>Vegetation coverage (<b>a</b>) and mean height (<b>b</b>) of different types of grasslands. Note: Different lowercase letters indicate significant differences between different types of grasslands at the 0.05 level. NG, natural grassland; NTT, natural turf transplantation; ARCG, artificial replanting of cash crop grassland; this is applicable for the following figures as well.</p>
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<p>Changes in diversity indices of vegetation communities in different grassland types (<b>a</b>–<b>d</b>). “NS” indicated that the grassland type diversity indices of the restored NTT and ARCG were not significantly different from those of the original grassland, illustrating that the restoration was effective.</p>
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<p>Effect of restoration of natural turf-transplanted grassland and replanted cash crop blackcurrant grassland.</p>
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6 pages, 204 KiB  
Proceeding Paper
Optimization and Forecasting Modelling to Analyse India’s Pursuit of the Sustainable Development Goals in Agenda 2030
by Anas Melethil, Nabil Ahmed Khan, Mohd Azeem, Golam Kabir and Irfan Ali
Eng. Proc. 2024, 76(1), 16; https://doi.org/10.3390/engproc2024076016 (registering DOI) - 17 Oct 2024
Abstract
The Sustainable Development Goals (SDGs), set in Agenda 2030, are examined in this study, along with India’s progress towards attaining them, and creative solutions based on forecasting and optimization modelling are presented. We investigate the complex alternatives between economic development, mainly focusing on [...] Read more.
The Sustainable Development Goals (SDGs), set in Agenda 2030, are examined in this study, along with India’s progress towards attaining them, and creative solutions based on forecasting and optimization modelling are presented. We investigate the complex alternatives between economic development, mainly focusing on GDP, sustainability—environmental concerns—and employment—a problem at the core of India’s sustainable development. We examine India’s development across several sectors like agriculture, mining, trades, construction, and so on, using a lexicographic goal programming framework, developing a hierarchical structure with four different levels and prioritizing the most important goal. Decisions are made from the highest priority level to the lowest priority level. Research goes beyond assessment by providing practical solutions to problems. A numerical study highlight the applicability of our strategy. By emphasizing the relevance of coordinating progress across decision-making levels for a more equal, prosperous, and sustainable future by 2030, this research delivers customized, context-aware solutions to accelerate India’s achievement of the SDG goals. Full article
22 pages, 3894 KiB  
Article
Comparative Analysis of Domestic Production and Import of Hard Coal in Poland: Conclusions for Energy Policy and Competitiveness
by Izabela Jonek-Kowalska and Wieslaw Grebski
Energies 2024, 17(20), 5157; https://doi.org/10.3390/en17205157 - 16 Oct 2024
Abstract
In many energy policies, including Poland’s, environmental priorities clash with the issue of energy security. With these contradictions in mind, the main objective of the article is a comparative analysis of domestic production and imports of hard coal in Poland and the formulation [...] Read more.
In many energy policies, including Poland’s, environmental priorities clash with the issue of energy security. With these contradictions in mind, the main objective of the article is a comparative analysis of domestic production and imports of hard coal in Poland and the formulation of conclusions for energy policy and competitiveness. The analysis covers the years 2018–2023 and concerns three issues: the volume and directions of coal imports to Poland, the qualitative and price competitiveness of coal, and the possibility of substituting imported coal with domestic coal. The research used statistical analysis. Indicators of structure and dynamics as well as comparative analysis were also used. The analysis shows that the structure of coal importers to Poland is quite diverse and includes many geographic directions. However, until 2021, it was dominated by Russia, followed by Colombia, indicating a fairly homogeneous supply market and a continuing tendency to depend on a single importer. Analysis of qualitative competitiveness confirms the existence of balance and industrial resources whose quality parameters (sulfur content, ash content, and calorific value) are comparable to and better than those of imported coal. Polish hard coal can also compete with imported coal in terms of price. From 2021 to 2023, it was clearly cheaper than foreign coal. In the above circumstances, it is quite difficult to unequivocally assess the reasons for importing coal to Poland and to justify dependence on external suppliers. This is especially relevant since domestic mining in 2020–2023 remains stable (periodically even increasing), which does not indicate a decisive shift away from coal as an energy resource. Full article
(This article belongs to the Special Issue Circular Economy, Environmental and Energy Management)
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Figure 1

Figure 1
<p>Hard coal consumption in Poland in 2018–2023 [in million tonnes].</p>
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<p>Employment in Polish hard coal mining in 2008–2024 [in thousands]. Source: [<a href="https://polskirynekwegla.pl/raport-dynamiczny/stan-zatrudnienia" target="_blank">https://polskirynekwegla.pl/raport-dynamiczny/stan-zatrudnienia</a>]. [accessed on 1 July 2024].</p>
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<p>Determinants of energy resource imports: summary of the review.</p>
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<p>The size of hard coal import to Poland in 2018–2023 [in million tons]. Source: own work based on [<a href="#B83-energies-17-05157" class="html-bibr">83</a>,<a href="#B84-energies-17-05157" class="html-bibr">84</a>,<a href="#B85-energies-17-05157" class="html-bibr">85</a>,<a href="#B86-energies-17-05157" class="html-bibr">86</a>,<a href="#B87-energies-17-05157" class="html-bibr">87</a>,<a href="#B88-energies-17-05157" class="html-bibr">88</a>].</p>
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<p>Geographic structure of hard coal imports in Poland in 2018 [in %]. Source: own work based on [<a href="#B83-energies-17-05157" class="html-bibr">83</a>,<a href="#B84-energies-17-05157" class="html-bibr">84</a>,<a href="#B85-energies-17-05157" class="html-bibr">85</a>,<a href="#B86-energies-17-05157" class="html-bibr">86</a>,<a href="#B87-energies-17-05157" class="html-bibr">87</a>,<a href="#B88-energies-17-05157" class="html-bibr">88</a>].</p>
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<p>Geographic structure of hard coal imports in Poland in 2019 [in %]. Source: own work based on [<a href="#B83-energies-17-05157" class="html-bibr">83</a>,<a href="#B84-energies-17-05157" class="html-bibr">84</a>,<a href="#B85-energies-17-05157" class="html-bibr">85</a>,<a href="#B86-energies-17-05157" class="html-bibr">86</a>,<a href="#B87-energies-17-05157" class="html-bibr">87</a>,<a href="#B88-energies-17-05157" class="html-bibr">88</a>].</p>
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<p>Geographic structure of hard coal imports in Poland in 2020 [in %]. Source: own work based on [<a href="#B83-energies-17-05157" class="html-bibr">83</a>,<a href="#B84-energies-17-05157" class="html-bibr">84</a>,<a href="#B85-energies-17-05157" class="html-bibr">85</a>,<a href="#B86-energies-17-05157" class="html-bibr">86</a>,<a href="#B87-energies-17-05157" class="html-bibr">87</a>,<a href="#B88-energies-17-05157" class="html-bibr">88</a>].</p>
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<p>Geographic structure of hard coal imports in Poland in 2021 [in %]. Source: own work based on [<a href="#B83-energies-17-05157" class="html-bibr">83</a>,<a href="#B84-energies-17-05157" class="html-bibr">84</a>,<a href="#B85-energies-17-05157" class="html-bibr">85</a>,<a href="#B86-energies-17-05157" class="html-bibr">86</a>,<a href="#B87-energies-17-05157" class="html-bibr">87</a>,<a href="#B88-energies-17-05157" class="html-bibr">88</a>].</p>
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<p>Geographic structure of hard coal imports in Poland in 2022 [in %]. Source: own work based on [<a href="#B83-energies-17-05157" class="html-bibr">83</a>,<a href="#B84-energies-17-05157" class="html-bibr">84</a>,<a href="#B85-energies-17-05157" class="html-bibr">85</a>,<a href="#B86-energies-17-05157" class="html-bibr">86</a>,<a href="#B87-energies-17-05157" class="html-bibr">87</a>,<a href="#B88-energies-17-05157" class="html-bibr">88</a>].</p>
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<p>Geographic structure of hard coal imports in Poland in 2023 [in %]. Source: own work based on [<a href="#B83-energies-17-05157" class="html-bibr">83</a>,<a href="#B84-energies-17-05157" class="html-bibr">84</a>,<a href="#B85-energies-17-05157" class="html-bibr">85</a>,<a href="#B86-energies-17-05157" class="html-bibr">86</a>,<a href="#B87-energies-17-05157" class="html-bibr">87</a>,<a href="#B88-energies-17-05157" class="html-bibr">88</a>].</p>
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<p>Ash content of imported coal and the size of the balance coal reserves with ash content below 10% in Poland in 2020–2023 Source: own work based on data [<a href="#B82-energies-17-05157" class="html-bibr">82</a>,<a href="#B89-energies-17-05157" class="html-bibr">89</a>,<a href="#B90-energies-17-05157" class="html-bibr">90</a>,<a href="#B91-energies-17-05157" class="html-bibr">91</a>,<a href="#B92-energies-17-05157" class="html-bibr">92</a>].</p>
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<p>Sulfur content of imported coal and the size of the balance coal reserves with sulfur content below 0.6% in Poland in 2020–2023 Source: own work based on data [<a href="#B82-energies-17-05157" class="html-bibr">82</a>,<a href="#B89-energies-17-05157" class="html-bibr">89</a>,<a href="#B90-energies-17-05157" class="html-bibr">90</a>,<a href="#B91-energies-17-05157" class="html-bibr">91</a>,<a href="#B92-energies-17-05157" class="html-bibr">92</a>].</p>
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<p>Calorific value of imported coal and size of balance coal reserves with calorific value above 25,000 kJ/kg in Poland in 2020–2023. Source: own work based on data [<a href="#B82-energies-17-05157" class="html-bibr">82</a>,<a href="#B89-energies-17-05157" class="html-bibr">89</a>,<a href="#B90-energies-17-05157" class="html-bibr">90</a>,<a href="#B91-energies-17-05157" class="html-bibr">91</a>,<a href="#B92-energies-17-05157" class="html-bibr">92</a>].</p>
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<p>Price of imported (free-at-frontier) and domestically produced (ex-mine) hard coal in 2020–2023 [PLN/ton] Source: own work based on data [<a href="#B82-energies-17-05157" class="html-bibr">82</a>,<a href="#B89-energies-17-05157" class="html-bibr">89</a>,<a href="#B90-energies-17-05157" class="html-bibr">90</a>,<a href="#B91-energies-17-05157" class="html-bibr">91</a>,<a href="#B92-energies-17-05157" class="html-bibr">92</a>].</p>
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22 pages, 9243 KiB  
Article
Physical and Numerical Modeling of a Flow Control Layer Made with a Sludge and Slag Mixture for Use in Waste Rock Pile Reclamation
by Nelcy Carolina Otalora Vasquez, Abdelkabir Maqsoud and Tikou Belem
Mining 2024, 4(4), 841-862; https://doi.org/10.3390/mining4040047 (registering DOI) - 16 Oct 2024
Abstract
The reclamation of waste rock piles (WRPs) is complex, requiring adaptation of existing mine site reclamation techniques. An alternative approach has been developed for waste rock piles reclamation which involves installing finer materials on the top of waste rock piles. These finer layers [...] Read more.
The reclamation of waste rock piles (WRPs) is complex, requiring adaptation of existing mine site reclamation techniques. An alternative approach has been developed for waste rock piles reclamation which involves installing finer materials on the top of waste rock piles. These finer layers (flow control layers—FCLs) redirect water flowing inside the pile toward its slope and limits water infiltration into reactive waste rocks. In the context of sustainable development, a mixture material made with sludge and slag can be used as an FCL in the reclamation of a waste rock pile. To assess the effectiveness of this material, a physical model was used and instrumented with sensors for monitoring volumetric water content and suction and equipped with the following components: (1) a rain simulator; and (2) drains that allow the recovery of water that infiltrates through the system. The physical model was tested with various cover layer thicknesses, inclinations, and precipitation rates. Investigation results showed that the water infiltration across the system was very low, leading to the conclusion that the sludge and slug mixture performed well as a flow control layer in the reclamation of waste rock piles. Full article
(This article belongs to the Topic Mining Innovation)
Show Figures

Figure 1

Figure 1
<p>Quémont 2 mine site location (<a href="https://mapamundi.online" target="_blank">https://mapamundi.online</a> maps images, accessed on 11 July 2024).</p>
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<p>Particle size distribution of materials.</p>
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<p>Measured and fitted water retention curves of the sludge and slag mixture.</p>
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<p>Experimental setup: (<b>a</b>) laboratory physical model; (<b>b</b>) locations of different devices used for volumetric water content (θ), suction (ψ) measurements, and drains used to recover infiltration and runoff.</p>
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<p>Numerical model and location of simulated sensors in SEEP/W.</p>
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<p>Volumetric water content of the gravel and the sludge–slag materials.</p>
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<p>Permeability function of the gravel and the sludge–slag materials.</p>
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<p>Infiltration and runoff rates for different drains and for different slope and thickness scenarios: (<b>a</b>) thickness of 25 cm; (<b>b</b>) thickness of 50 cm; and (<b>c</b>) thickness of 75 cm.</p>
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<p>Infiltration and runoff rates for different slope and thickness scenarios.</p>
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<p>Saturation profiles for the scenario with an FCL thickness of 25 cm and a slope of 2.5°.</p>
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<p>Suction profiles for the scenario with an FCL thickness of 25 cm and slope 2.5.</p>
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<p>Saturation profiles for the scenario with an FCL thickness of 50 cm and a slope of 5°.</p>
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<p>Suction profiles for the scenario with an FCL thickness of 50 cm and a slope of 5°.</p>
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<p>Volumetric water content results for a precipitation of 46.8 mm/h, a slope of 2.5°, a layer thickness of 25 cm, and a period of 720 h (30 days).</p>
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<p>Volumetric water content results at a precipitation rate of 46.8 mm/h, a slope of 2.5°, a layer thickness of 25 cm, and a period of 5 h.</p>
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<p>Volumetric water content results for a precipitation of 46.8 mm/h, a slope of 5°, a layer thickness of 25 cm, and a period of 720 h (30 days).</p>
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<p>Volumetric water content results for a precipitation of 46.8 mm/h, a slope of 5°, a layer thickness of 25 cm, and a period of 5 h.</p>
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<p>Volumetric water content results for a precipitation of 46.8 mm/h, a slope of 2.5°, a layer thickness of 50 cm, and a period of 720 h (30 days).</p>
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<p>Volumetric water content results for a precipitation of 46.8 mm/h, a slope of 2.5°, a layer thickness of 50 cm, and a period of 5 h.</p>
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<p>Volumetric water content results for a precipitation of 46.8 mm/h, a slope of 5°, a layer thickness of 50 cm, and a period of 720 h (30 days).</p>
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<p>Volumetric water content results for a precipitation of 46.8 mm/h, a slope of 5°, a layer thickness of 50 cm, and a period of 5 h.</p>
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<p>Volumetric water content results for a precipitation of 46.8 mm/h, a slope of 2.5°, a layer thickness of 75 cm, and a period of 720 h (30 days).</p>
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<p>Volumetric water content results for a precipitation of 46.8 mm/h, a slope of 2.5°, a layer thickness of 75 cm, and a period of 5 h.</p>
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<p>Volumetric water content results for a precipitation of 46.8 mm/h, a slope of 5°, a layer thickness of 75 cm, and a period of 720 h (30 days).</p>
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<p>Volumetric water content results for a precipitation of 46.8 mm/h, a slope of 5°, a layer thickness of 75 cm, and a period of 5 h.</p>
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<p>Photos showing FCLs at 2.5° and 5° slopes which were not affected by superficial erosion.</p>
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<p>Visible superficial erosion for an FCL with a 10° slope.</p>
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17 pages, 1008 KiB  
Article
Active Disturbance Rejection Control of Engine Speed in Series Hydraulic Hybrid Power System
by Zhiqiang Guo, Junlin Luo and Yuwei Liu
Machines 2024, 12(10), 733; https://doi.org/10.3390/machines12100733 - 16 Oct 2024
Abstract
Abstract: In this paper, a novel series hydraulic hybrid powertrain is proposed for a three-axis all-terrain vehicle. The engine drives two variable displacement pumps responsible for driving and steering, respectively. A variable displacement motor is connected to the ring gear of the planetary [...] Read more.
Abstract: In this paper, a novel series hydraulic hybrid powertrain is proposed for a three-axis all-terrain vehicle. The engine drives two variable displacement pumps responsible for driving and steering, respectively. A variable displacement motor is connected to the ring gear of the planetary coupling mechanism to drive the vehicle and a fixed-displacement motor is connected to the sun gear to steer the vehicle. The active disturbance rejection control with feedforward control is employed to control the engine speed. The engine speed is controlled in a close-looped manner by adjusting the engine throttle. The controller parameters are decided by analyzing the influence of each parameter on the controller performance by means of the control variable method. The simulation results indicate that the proposed control strategy enables the vehicle to obtain better engine speed following and anti-disturbance performance. An all-terrain prototype is established and field tests are carried out to verify the effectiveness of the design and control strategy of the series hydraulic hybrid powertrain for the all-terrain vehicle. Full article
(This article belongs to the Section Vehicle Engineering)
14 pages, 1082 KiB  
Article
Acid Mine Drainage Neutralization by Ultrabasic Rocks: A Chromite Mining Tailings Evaluation Case Study
by Evgenios Kokkinos, Vasiliki Kotsali, Evangelos Tzamos and Anastasios Zouboulis
Sustainability 2024, 16(20), 8967; https://doi.org/10.3390/su16208967 - 16 Oct 2024
Abstract
Chromite is formed in nature in ophiolitic layers and ultrabasic rocks through fractional crystallization. The corresponding mining technologies separate the ore from these ultrabasic rocks, which are considered to be tailings for the process but may be valorized in other applications. The need [...] Read more.
Chromite is formed in nature in ophiolitic layers and ultrabasic rocks through fractional crystallization. The corresponding mining technologies separate the ore from these ultrabasic rocks, which are considered to be tailings for the process but may be valorized in other applications. The need to utilize this material is due to the large quantities of its production and the special management required to avoid possible secondary pollution. In the present work, the ultrabasic rocks of chromite mining were applied to acid mine drainage (AMD) neutralization. The aim was to increase the technological maturity of the method and promote circular economy principles and sustainability in the mining sector. Ultrabasic rocks were obtained from a chromite mining facility as reference material. Furthermore, an artificial AMD solution was synthesized and applied, aiming to simulate field conditions. According to the results, the sample was successfully utilized in AMD neutralization (pH 7), achieving rapid rates in the first 30 min and maximum efficiency (liquid to solid ratio equal to 8.3) at 24 h. However, the method presented a drawback since Mg was leached, even though the concentration of other typical metals contained in an AMD solution decreased. Full article
(This article belongs to the Special Issue Sustainable Mining and Circular Economy)
25 pages, 21419 KiB  
Article
A Coal Mine Excavation Tunnels Modeling Method Based on Point Clouds
by Haoyuan Zhang, Shanjun Mao and Mei Li
Appl. Sci. 2024, 14(20), 9454; https://doi.org/10.3390/app14209454 (registering DOI) - 16 Oct 2024
Abstract
The excavation tunnel model is an important reference for mine equipment control and tunnel deformation monitoring. Currently, tunnel models are mainly created manually, and point cloud reconstruction algorithms are difficult to directly apply to tunnel point clouds. To address these issues, this paper [...] Read more.
The excavation tunnel model is an important reference for mine equipment control and tunnel deformation monitoring. Currently, tunnel models are mainly created manually, and point cloud reconstruction algorithms are difficult to directly apply to tunnel point clouds. To address these issues, this paper proposes a point cloud-based excavation tunnel modeling method. First, preprocessing algorithms such as point cloud coordinate transformation, tunnel point cloud extraction, and tunnel point cloud completion are used to filter out equipment point clouds inside the tunnel and repair occluded holes. Then, the tunnel centerline is extracted, and consistency optimization is performed on the point cloud normal vectors. Finally, a tunnel model is established based on the Poisson modeling algorithm, enabling high-precision tunnel modeling. The proposed algorithm’s accuracy and effectiveness are demonstrated through experiments on four different coal mine tunnels. Full article
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<p>The difficulties of coal mine tunnel modeling. (<b>a</b>) Tunneling errors. (<b>b</b>) Equipment occlusion.</p>
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<p>The framework of tunnel modeling.</p>
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<p>Pipeline of coordinate transformation.</p>
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<p>Coordinate transformation of tunnels.</p>
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<p>Y-axis view of tunnel. (<b>a</b>) Roll angle of tunnel. (<b>b</b>) Minimum bounding rectangle of tunnel. (<b>c</b>) Tunnel after rotation.</p>
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<p>Point cloud density distribution curve along the X-axis.</p>
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<p>Completion based on the left-right symmetry.</p>
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<p>Completion based on the up-bottom symmetry.</p>
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<p>Method of calculating the centerline of the tunnel. (<b>a</b>) Centroid of slices forms the initial centerline. (<b>b</b>) Difference between centroid and geometric mean.</p>
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<p>Tunnel centerline polynomial fitting. (<b>a</b>) X-Y fitting. (<b>b</b>) Z-Y fitting.</p>
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<p>Point cloud normal optimization: (<b>a</b>) Before optimization. (<b>b</b>) After optimization.</p>
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<p>The three-dimensional laser scanner used in this study.</p>
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<p>Original point clouds from four different mines. (<b>a</b>) Tunnel a. (<b>b</b>) Tunnel b. (<b>c</b>) Tunnel c. (<b>d</b>) Tunnel d.</p>
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<p>Tunnel extraction results. (<b>a</b>) Tunnel a. (<b>b</b>) Tunnel b. (<b>c</b>) Tunnel c. (<b>d</b>) Tunnel d.</p>
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<p>Tunnel completion results. (<b>a</b>) Tunnel a. (<b>b</b>) Tunnel b. (<b>c</b>) Tunnel c. (<b>d</b>) Tunnel d.</p>
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<p>Tunnel completion results. (<b>a</b>) Tunnel a. (<b>b</b>) Tunnel b. (<b>c</b>) Tunnel c. (<b>d</b>) Tunnel d.</p>
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<p>Centerline of Tunnel d. (<b>a</b>) Top view. (<b>b</b>) Perspective view.</p>
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<p>Comparison between the proposed algorithm with other methods and ground truth. (<b>a</b>) X-axis. (<b>b</b>) Z-axis.</p>
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<p>Point clouds from four different mines. (<b>a</b>) Tunnel a. (<b>b</b>) Tunnel b. (<b>c</b>) Tunnel c. (<b>d</b>) Tunnel d.</p>
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<p>Comparison between surface reconstruction algorithms. (<b>a</b>) Ball-pivoting. (<b>b</b>) VCG. (<b>c</b>) NKSR. (<b>d</b>) Poisson.</p>
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<p>Comparison between surface reconstruction algorithms. (<b>a</b>) Ball-pivoting. (<b>b</b>) VCG. (<b>c</b>) NKSR. (<b>d</b>) Poisson.</p>
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<p>Modeling results with different steps: (<b>a</b>) Do not use any point cloud processing steps. (<b>b</b>) Only perform point cloud extraction. (<b>c</b>) Perform point cloud extraction and completion. (<b>d</b>) Use all point cloud processing steps.</p>
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<p>Modeling results with different steps: (<b>a</b>) Do not use any point cloud processing steps. (<b>b</b>) Only perform point cloud extraction. (<b>c</b>) Perform point cloud extraction and completion. (<b>d</b>) Use all point cloud processing steps.</p>
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<p>Mesh model of Tunnel a. Left shows the inside of the tunnel, while right shows the outside of the tunnel on each row. From top to bottom, the models progress from coarse to fine.</p>
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<p>Instantiated model based on Unreal Engine. (<b>a</b>) Tunnel model with anchor nets. (<b>b</b>) Tunnel model with equipment.</p>
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<p>Centerline of Tunnel a.</p>
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<p>Centerline of Tunnel b.</p>
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<p>Centerline of Tunnel c.</p>
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22 pages, 1654 KiB  
Article
A New Scene Sensing Model Based on Multi-Source Data from Smartphones
by Zhenke Ding, Zhongliang Deng, Enwen Hu, Bingxun Liu, Zhichao Zhang and Mingyang Ma
Sensors 2024, 24(20), 6669; https://doi.org/10.3390/s24206669 - 16 Oct 2024
Abstract
Smartphones with integrated sensors play an important role in people’s lives, and in advanced multi-sensor fusion navigation systems, the use of individual sensor information is crucial. Because of the different environments, the weights of the sensors will be different, which will also affect [...] Read more.
Smartphones with integrated sensors play an important role in people’s lives, and in advanced multi-sensor fusion navigation systems, the use of individual sensor information is crucial. Because of the different environments, the weights of the sensors will be different, which will also affect the method and results of multi-source fusion positioning. Based on the multi-source data from smartphone sensors, this study explores five types of information—Global Navigation Satellite System (GNSS), Inertial Measurement Units (IMUs), cellular networks, optical sensors, and Wi-Fi sensors—characterizing the temporal, spatial, and mathematical statistical features of the data, and it constructs a multi-scale, multi-window, and context-connected scene sensing model to accurately detect the environmental scene in indoor, semi-indoor, outdoor, and semi-outdoor spaces, thus providing a good basis for multi-sensor positioning in a multi-sensor navigation system. Detecting environmental scenes provides an environmental positioning basis for multi-sensor fusion localization. This model is divided into four main parts: multi-sensor-based data mining, a multi-scale convolutional neural network (CNN), a bidirectional long short-term memory (BiLSTM) network combined with contextual information, and a meta-heuristic optimization algorithm. Full article
(This article belongs to the Special Issue Smart Sensor Systems for Positioning and Navigation)
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<p>Four scene classifications: (<b>a</b>) outdoor, (<b>b</b>) semi-outdoor, (<b>c</b>) semi-indoor, and (<b>d</b>) indoor.</p>
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<p>Satellite zenith view: (<b>a</b>) west indoor neighboring window, (<b>b</b>) south indoor neighbouring window, (<b>c</b>) indoor, and (<b>d</b>) open outdoor neighboring window.</p>
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<p>DOP change graph: (<b>a</b>) outdoor DOP change graph, and (<b>b</b>) indoor DOP change graph.</p>
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<p>Visible satellite map: (<b>a</b>) variation in the number of visible satellites. (<b>b</b>) Variation in the rate of change of visible satellites in different windows.</p>
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<p>Satellite signal quality map: (<b>a</b>) CNR variation and (<b>b</b>) DCNR variation.</p>
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<p>State of motion versus acceleration.</p>
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<p>Wi-Fi channel spectrum scan: (<b>a</b>) indoor, (<b>b</b>) outdoor.</p>
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<p>Visible AP distribution of Wi-Fi: (<b>a</b>) number distribution, (<b>b</b>) signal strength distribution.</p>
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<p>Variation of light sensors and cellular network sensors: (<b>a</b>) variation of indoor and outdoor light intensity over 24 h, (<b>b</b>) variation of the number of base stations receiving signals.</p>
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<p>An algorithmic model for the classification of complex indoor and outdoor scenes based on spatio-temporal features.</p>
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<p>Pearson correlation feature map.</p>
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<p>Schematic of a two-scale convolutional neural network.</p>
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<p>BiLSTM network structure diagram.</p>
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<p>Structure of the ablation experiment.</p>
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<p>Confusion matrix: (<b>a</b>) confusion matrix before WOA optimization. (<b>b</b>) confusion matrix after WOA optimisation.</p>
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<p>Comparison of the accuracy of different models.</p>
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<p>Comparison of accuracy in different scenarios.</p>
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16 pages, 6046 KiB  
Article
Numerical Study on the Explosion Reaction Mechanism of Multicomponent Combustible Gas in Coal Mines
by Dong Ma, Leilin Zhang, Guangyuan Han and Tingfeng Zhu
Fire 2024, 7(10), 368; https://doi.org/10.3390/fire7100368 (registering DOI) - 16 Oct 2024
Abstract
Combustible gases, such as CO, CH4, and H2, are produced during spontaneous coal combustion in goaf, which may cause an explosion under the stimulation of an external fire source. It is of great significance to study the influence of [...] Read more.
Combustible gases, such as CO, CH4, and H2, are produced during spontaneous coal combustion in goaf, which may cause an explosion under the stimulation of an external fire source. It is of great significance to study the influence of combustible gases, such as CO and H2, on the characteristics of a gas explosion. In this study, CHEMKIN software (Version 17.0) and the GRI-Mech 3.0 reaction mechanism were used to study the influences of different concentration ratios between CO and H2 on the ignition delay time, free radical concentration, and key reaction step of a gas explosion. The results show that the increase in the initial CH4 and CO concentrations prolonged the ignition delay time, while the increase in the H2 concentration shortened the time and accelerated the explosion reaction. The addition of H2 promoted the generation of free radicals (H·, O·, ·OH) and accelerated the occurrence of the gas explosion. CO generated ·OH free radicals and dominated the methane consumption through the R119 and R156 reactions. As the concentrations of CO and H2 increased, the R38 reaction gradually became the main driving factor of the gas explosion. Full article
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<p>The technology roadmap of this study.</p>
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<p>Relationship between ignition delay time and concentration of added combustible gas.</p>
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<p>The influence of CO on H·, O·, and ·OH in the process of the 7% methane explosion.</p>
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<p>The influence of the concentration of CO and H<sub>2</sub> mixed gases on H·, O·, and ·OH in the 7% methane explosion process.</p>
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<p>The influence of CO or CO and H<sub>2</sub> on H·, O·, and ·OH during the methane explosion.</p>
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<p>Influence of CO on the reaction sensitivity of the 7% gas key elements.</p>
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<p>Effect of CO on the gas sensitivity of the 9.5% gas key element reaction.</p>
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<p>Effect of CO on gas sensitivity of 11% gas key elements.</p>
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<p>Influence of the CO and H<sub>2</sub> mixture on the sensitivity of 7% gas key elements.</p>
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<p>Influence of the CO and H<sub>2</sub> mixture on the reaction sensitivity of the 9.5% gas key elements.</p>
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<p>Influence of CO and H<sub>2</sub> mixture on the sensitivity of the 11% gas key elements.</p>
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36 pages, 3237 KiB  
Article
Spatial and Bioaccumulation of Heavy Metals in a Sheep-Based Food System: Implications for Human Health
by Florin-Ioan Fechete, Maria Popescu, Sorin-Marian Mârza, Loredana-Elena Olar, Ionel Papuc, Florin-Ioan Beteg, Robert-Cristian Purdoiu, Andrei Răzvan Codea, Caroline-Maria Lăcătuș, Ileana-Rodica Matei, Radu Lăcătuș, Adela Hoble, Ioan Valentin Petrescu-Mag and Florin-Dumitru Bora
Toxics 2024, 12(10), 752; https://doi.org/10.3390/toxics12100752 - 16 Oct 2024
Abstract
Heavy metal contamination in agricultural soils presents serious environmental and health risks. This study assessed the bioaccumulation and spatial distribution of nickel, cadmium, zinc, lead, and copper within a sheep-based food chain in the Baia Mare region, Romania, which includes soil, green grass, [...] Read more.
Heavy metal contamination in agricultural soils presents serious environmental and health risks. This study assessed the bioaccumulation and spatial distribution of nickel, cadmium, zinc, lead, and copper within a sheep-based food chain in the Baia Mare region, Romania, which includes soil, green grass, sheep serum, and dairy products. Using inductively coupled plasma mass spectrometry (ICP-MS), we analyzed the concentrations of these metals and calculated bioconcentration factors (BCFs) to evaluate their transfer through trophic levels. Spatial analysis revealed that copper (up to 2528.20 mg/kg) and zinc (up to 1821.40 mg/kg) exceeded permissible limits, particularly near former mining sites. Elevated lead (807.59 mg/kg) and cadmium (2.94 mg/kg) were observed in industrial areas, while nickel and cobalt showed lower concentrations, but with localized peaks. Zinc was the most abundant metal in grass, while cadmium transferred efficiently to milk and cheese, raising potential health concerns. The results underscore the complex interplay between soil properties, contamination sources, and biological processes in heavy metal accumulation. These findings highlight the importance of continuous monitoring, risk assessment, and mitigation strategies to protect public health from potential exposure through contaminated dairy products. Full article
(This article belongs to the Section Agrochemicals and Food Toxicology)
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<p>The spatial distribution of detectable elements in sheep milk and cheese samples; comparing mean concentration across different collection areas.</p>
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<p>The spatial distribution of detectable elements in sheep serum samples; comparing mean concentration across different collection areas.</p>
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16 pages, 8302 KiB  
Article
Effects of Soil Nutrient Restoration Aging and Vegetation Recovery in Open Dumps of Cold and Arid Regions in Xinjiang, China
by Zhongming Wu, Weidong Zhu, Haijun Guo, Yong Zhang, Chaoji Shen, Jing Guo, Ming Liu, Tuanwei Zhao, Hu Teng, Wanli Zhu, Yongfu Kang, Gensheng Li and Weiming Guan
Land 2024, 13(10), 1690; https://doi.org/10.3390/land13101690 - 16 Oct 2024
Abstract
Open-pit coal mining inevitably damages the soil and vegetation in mining areas. Currently, the restoration of cold and arid open-pit mines in Xinjiang, China, is still in the initial exploratory stage, especially the changes in soil nutrients in spoil dumps over time. Dynamic [...] Read more.
Open-pit coal mining inevitably damages the soil and vegetation in mining areas. Currently, the restoration of cold and arid open-pit mines in Xinjiang, China, is still in the initial exploratory stage, especially the changes in soil nutrients in spoil dumps over time. Dynamic remote sensing monitoring of vegetation in mining areas and their correlation are relatively rare. Using the Heishan Open Pit in Xinjiang, China, as a case, soil samples were collected during different discharge periods to analyze the changes in soil nutrients and uncover the restoration mechanisms. Based on four Landsat images from 2018 to 2023, the remote sensing ecological index (RSEI) and fractional vegetation cover (FVC) were obtained to evaluate the effect of mine restoration. Additionally, the correlation between vegetation changes and soil nutrients was analyzed. The results indicated that (i) the contents of nitrogen (N), phosphorus (P), potassium (K), and organic matter (OM) in the soil increased with the duration of the restoration period. (ii) When the restoration time of the dump exceeds 5 years, N, P, K, and OM content is higher than that of the original surface-covered vegetation area. (iii) Notably, under the same restoration aging, the soil in the artificial mine restoration demonstration base had significantly higher contents of these nutrients compared to the soil naturally restored in the dump. (iv) Over the past five years, the RSEI and FVC in the Heishan Open Pit showed an overall upward trend. The slope remediation and mine restoration project significantly increased the RSEI and FVC values in the mining area. (v) Air humidity and surface temperature were identified as key natural factors affecting the RSEI and FVC in cold and arid open pit. The correlation coefficients between soil nutrient content and vegetation coverage were higher than 0.78, indicating a close and complementary relationship between the two. The above results can clarify the time–effect relationship between natural recovery and artificial restoration of spoil dumps in cold and arid mining areas in Xinjiang, further promoting the research and practice of mine restoration technology in cold and arid open pits. Full article
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<p>(<b>a</b>) The province map of the study area location; (<b>b</b>) the city map of study area location; (<b>c</b>) distribution map of specific terrain and sampling points of the mining area.</p>
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<p>(<b>a</b>) Drone aerial view of mining area; (<b>b</b>) mine dump; (<b>c</b>) dump section view; (<b>d</b>) vegetated area.</p>
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<p>The FVC distribution map of the study area in (<b>a</b>) 2018, (<b>b</b>) 2020, (<b>c</b>) 2022 and (<b>d</b>) 2023.</p>
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<p>FVC percentage of the study area.</p>
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<p>The distribution map of the RSEI in the study area.</p>
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<p>RSEI percentage of the study area.</p>
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<p>The distribution map of LST and WET by the RSEI in the study area.</p>
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<p>Soil nutrient data map at different sampling sites.</p>
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<p>Correlation analysis of soil nutrient content and vegetation coverage by (<b>a</b>) in situ restoration and (<b>b</b>) vegetation mine restoration.</p>
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22 pages, 23991 KiB  
Article
Conceptual and Applied Aspects of Water Retention Tests on Tailings Using Columns
by Fernando A. M. Marinho, Yuri Corrêa, Rosiane Soares, Inácio Diniz Carvalho and João Paulo de S. Silva
Geosciences 2024, 14(10), 273; https://doi.org/10.3390/geosciences14100273 - 16 Oct 2024
Abstract
The water retention capacity of porous materials is crucial in various geotechnical and environmental engineering applications such as slope stability analysis, landfill management, and mining operations. Filtered tailings stacks are considered an alternative to traditional tailings dams. Nevertheless, the mechanical behaviour and stability [...] Read more.
The water retention capacity of porous materials is crucial in various geotechnical and environmental engineering applications such as slope stability analysis, landfill management, and mining operations. Filtered tailings stacks are considered an alternative to traditional tailings dams. Nevertheless, the mechanical behaviour and stability of the material under different water content conditions are of concern because these stacks can reach considerable heights. The water behaviour in these structures is poorly understood, particularly the effects of the water content on the stability and potential for liquefaction of the stacks. This study aims to investigate the water retention and flow characteristics of compacted iron ore tailings in high columns to better understand their hydromechanical behaviour. The research used 5 m high columns filled with iron ore tailings from the Quadrilátero Ferrífero region in Minas Gerais, Brazil. The columns were prepared in layers, compacted, and instrumented with moisture content sensors and suction sensors to monitor the water movement during various stages of saturation, drainage, infiltration, and evaporation. The sensors provided consistent data and revealed that the tailings exhibited high drainage capacity. The moisture content and suction profiles were effectively established over time and revealed the dynamic water retention behaviour. The comparison of the data with the theoretical soil water retention curve (SWRC) demonstrated a good correlation which indicates that there was no hysteresis in the material response. The study concludes that the column setup effectively captures the water retention and flow characteristics of compacted tailings and provides valuable insights for the hydromechanical analysis of filtered tailings stacks. These findings can significantly help improve numerical models, calibrate material parameters, and contribute to the safer and more efficient management of tailings storage facilities. Full article
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<p>(<b>a</b>) Ore-pile draining and (<b>b</b>) water content variation along the pile.</p>
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<p>Relationship between the water content and the amount of fines.</p>
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<p>(<b>a</b>) Physical model of a soil column with a water table (<b>b</b>) Relationships between free energy and water content in a soil column with a fixed water table (<b>c</b>) Variation of water content with the height of the column (modified from Edlefesen and Anderson [<a href="#B7-geosciences-14-00273" class="html-bibr">7</a>]).</p>
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<p>Suction (<b>a</b>) and water content (<b>b</b>) profile in the field.</p>
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<p>(<b>a</b>) PVC column; (<b>b</b>) schematic drawing of the column; (<b>c</b>) suction equilibrium profile, and (<b>d</b>) water content profiles for three hypothetical materials [<a href="#B15-geosciences-14-00273" class="html-bibr">15</a>].</p>
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<p>Soil water retention curve of the material (data from Jesus et al. [<a href="#B22-geosciences-14-00273" class="html-bibr">22</a>]).</p>
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<p>Segments for the column assembly.</p>
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<p>Drainage segment. Placement of (<b>a</b>) gravel and (<b>b</b>) medium sand.</p>
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<p>Column compaction process: (<b>a</b>) Details of the compaction; (<b>b</b>) column at its 6th segment.</p>
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<p>First completed column: (<b>a</b>) Image of the completed column; (<b>b</b>) sensor positions.</p>
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<p>Time lag graphical analysis between sensors WC6 and TE6 during (<b>a</b>) saturation, (<b>b</b>) drainage, (<b>c</b>) infiltration, and (<b>d</b>) evaporation.</p>
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<p>Stages imposed in the columns.</p>
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<p>Profiles at the end of construction and before saturation: (<b>a</b>) Volumetric water content and (<b>b</b>) suction.</p>
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<p>Profiles during saturation: (<b>a</b>) Volumetric water content and (<b>b</b>) suction.</p>
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<p>Profiles during drainage: (<b>a</b>) Volumetric water content and (<b>b</b>) suction.</p>
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<p>Responses of the TE6 (<b>a</b>) and WC6 (<b>b</b>) sensors to the first infiltration and evaporation.</p>
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<p>Responses of the TE6 (<b>a</b>) and WC6 (<b>b</b>) sensors to the second infiltration and evaporation.</p>
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<p>Profiles during the first infiltration: (<b>a</b>) volumetric water content and (<b>b</b>) suction.</p>
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<p>Profiles during the first evaporation: (<b>a</b>) volumetric water content and (<b>b</b>) suction.</p>
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<p>Profiles during the second infiltration: (<b>a</b>) volumetric water content and (<b>b</b>) suction.</p>
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<p>Profiles during the second evaporation: (<b>a</b>) Volumetric water content and (<b>b</b>) suction.</p>
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<p>Measured water flux at the base of the column.</p>
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<p>A closer look at the sensor readings plotted with the retention curve.</p>
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<p>Water retention curve with the sensor readings.</p>
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<p>SWRC versus infiltration and evaporation data.</p>
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12 pages, 2579 KiB  
Article
Study on the Characteristics of Combustible Mixed Gas Production during Lignite Oxidation Process
by Dong Ma, Tingfeng Zhu, Puchun Yuan and Leilin Zhang
Fire 2024, 7(10), 367; https://doi.org/10.3390/fire7100367 - 16 Oct 2024
Abstract
CO, H2, and other combustible gases will be produced during coal oxidation in coal mines, which will increase the risk of explosion when mixed with methane. Therefore, it is very important to understand the production characteristics of combustible gas during coal [...] Read more.
CO, H2, and other combustible gases will be produced during coal oxidation in coal mines, which will increase the risk of explosion when mixed with methane. Therefore, it is very important to understand the production characteristics of combustible gas during coal oxidation. In this paper, a programmed temperature gas test system is built to study the impact of lignite on the production of gases at different particle sizes and temperatures, and the release characteristics of gases are also analyzed. The result shows that the production of combustible gas is influenced by the coal particle size significantly when the temperature is above 200 °C, and it decreases as the particle size increases. CO is the main gas during the early stage of coal spontaneous combustion, and the release of CH4 and H2 increases after 300 °C. The fitted equations of gas generation and temperature are consistent with the experimental results. The research results are helpful in understanding the hazards of coal spontaneous combustion and have a certain guiding significance for coal mine monitoring and prevention of coal spontaneous combustion. Full article
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<p>Coal spontaneous combustion programmed temperature gas test system.</p>
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<p>The concentration of gas with temperature during the heating process.</p>
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<p>The percentage of combustible gas during the heating process with different particle sizes.</p>
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<p>The percentage of combustible gas during the heating process with different particle sizes.</p>
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<p>Fitting results of combustible gas production in the oxidation process.</p>
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<p>Comparison of experimental data and calculated results of the total concentration of combustible gas generated from EMW lignite.</p>
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19 pages, 7484 KiB  
Article
Archaeogenetic Data Mining Supports a Uralic–Minoan Homeland in the Danube Basin
by Peter Z. Revesz
Information 2024, 15(10), 646; https://doi.org/10.3390/info15100646 - 16 Oct 2024
Abstract
Four types of archaeogenetic data mining are used to investigate the origin of the Minoans and the Uralic peoples: (1) six SNP mutations related to eye, hair, and skin phenotypes; (2) whole-genome admixture analysis using the G25 system; (3) an analysis of the [...] Read more.
Four types of archaeogenetic data mining are used to investigate the origin of the Minoans and the Uralic peoples: (1) six SNP mutations related to eye, hair, and skin phenotypes; (2) whole-genome admixture analysis using the G25 system; (3) an analysis of the history of the U5 mitochondrial DNA haplogroup; and (4) an analysis of the origin of each currently known Minoan mitochondrial and y-DNA haplotypes. The uniform result of these analyses is that the Minoans and the Uralic peoples had a common homeland in the lower and middle Danube Basin, as well as the Black Sea coastal regions. This new result helps to reconcile archaeogenetics with linguistics, which have shown that the Minoan language belongs to the Uralic language family. Full article
(This article belongs to the Special Issue International Database Engineered Applications)
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<p>A hypothetical dispersal of the Uralic languages from a Danube Basin homeland based on Krantz [<a href="#B7-information-15-00646" class="html-bibr">7</a>] with the Ugric to Minoan link added by Revesz [<a href="#B8-information-15-00646" class="html-bibr">8</a>].</p>
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<p>Locations of the archaeological samples listed in <a href="#information-15-00646-t003" class="html-table">Table 3</a>.</p>
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<p>The root means square error values between each pair of archaeological cultures. The lower values (red) indicate a stronger genotypic connection, while the higher values (blue) indicate a weaker genotypic connection.</p>
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<p>The sources (rows) for various Cycladic samples (columns 2–3) and Minoan samples (columns 4–12), as well as some averages (columns 13–15) according to the G25 admixture analysis system. The sources have been grouped into five regions (column 1).</p>
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<p>The Greek and Macedonian Neolithic cultures are the primary sources of the Cycladic and the Minoan Charalambos samples (red), while the Danube Basin Neolithic cultures are the primary sources of the Minoan Odigitria and Petras samples (blue) according to the G25 admixture analysis. The red and dark blue lines show hypothetical migrations.</p>
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<p>Principal component analysis of archaeogenetic samples, including Minoan samples from the Charalambos Cave on the Lassithi Plateau (green pentagon), Moni Odigitria (red triangle), and Mycenaean samples (purple quadrangle).</p>
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<p>Location of samples based on [<a href="#B35-information-15-00646" class="html-bibr">35</a>], accessed on 20 September 2024: (<b>top</b>) U5 before 15,000 BP (purple), 15,000–10,000 BP (dark blue), and 10,000–8000 BP (light blue); (<b>middle</b>) U5a1 before 10,000 BP (dark blue), and 10,000–6000 BP (light blue); and (<b>bottom</b>) U5a1d2b before 5500 BP.</p>
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<p>Location of the archaeological samples listed in <a href="#information-15-00646-t005" class="html-table">Table 5</a>.</p>
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