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Review

Underground Disposal of Coal Gangue Backfill in China

by
Weijian Song
1,2,
Jixiong Zhang
1,2,*,
Meng Li
1,2,*,
Hao Yan
1,2,
Nan Zhou
1,2,
Yinan Yao
1,2 and
Yaben Guo
1,2
1
State Key Laboratory of Coal Resources and Safe Mining, China University of Mining & Technology, Xuzhou 221116, China
2
School of Mines, China University of Mining & Technology, Xuzhou 221116, China
*
Authors to whom correspondence should be addressed.
Appl. Sci. 2022, 12(23), 12060; https://doi.org/10.3390/app122312060
Submission received: 19 October 2022 / Revised: 18 November 2022 / Accepted: 23 November 2022 / Published: 25 November 2022
(This article belongs to the Special Issue Advances and Challenges in Rock Mechanics and Rock Engineering)
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Abstract

:
China’s total coal production in 2021 exceeded 4.13 billion tons, 52% of the world’s total. Coal gangue, a solid waste of coal mining accounts for 15–20% of coal production, when directly discharged on the ground surface as waste heaps, it occupies large areas of land and cause environmental pollution. This paper summarizes the existing gangue backfilling methods, their working principles, efficiency, and application status. The methods that are meeting Middle and Western China’s mining demands are discussed in detail. The state-of-the-art technologies that can realize high-efficiency, centralized, and large-scale underground backfilling of coal gangue are analyzed. This paper shows that the industrial implementation of these technologies can increase the current maximum disposal capacity of coal gangue by three times, reaching five million tons per year. The equipment innovation and automation are analyzed, and the environmental effect of coal gangue backfilling is discussed. This review offers inspirations and guidelines for coal gangue disposal and the environmental hazard reduction of coal mining.

1. Introduction

According to the statistics released by the International Energy Agency (IEA), the world’s total coal production increased continuously from 2017 to 2019. However, due to the impact of COVID-19, the world’s coal production in 2020 dropped to 7.721 billion tons, a reduction of 4.8%. Except for China, the coal production in many countries, including Indonesia, Russia, Australia, Mongolia, and the United States declined. The top ten countries in terms of coal production were China, India, Indonesia, the United States of America, Australia, Russia, South Africa, Kazakhstan, Germany, and Poland [1]. The world’s total coal production rebounded in 2021, but is still not at pre-COVID-19 levels. China’s coal production in 2021 amounted to 4.13 billion tons [2], 52.4% of the world’s total. Offering robust support to the national economic and social stability of China, coal will remain its main energy source in the foreseeable future [3]. A large amount of coal gangue is generated during coal mining, accounting for 15–20% of the total coal production. The solid wastes discharged on the ground surface then form waste heaps. According to incomplete statistics, the accumulated coal gangue in China has exceeded six billion tons, with waste heaps numbering between 1500 and 1700 and occupying over 13,300 hectares. The annual increase of the coal gangue in China is 500 to 800 million tons (e.g., 795 million tons were produced in 2020) [4,5,6]. Coal gangue accumulated on the ground occupies large areas of land, causing severe air pollution and presenting other environmental hazards, including vegetation damage, water and soil loss, groundwater pollution, or even spontaneous combustion of waste heaps and landslides [7].
Given the environmental impact of coal gangue in the mining areas, many countries have elaborated their national gangue management regulations and strategies. Since the 1960s, developed countries, such as Germany and U.K., have issued plans to encourage the use of coal gangue to build materials in land reclamation, roads, and dams. Some western countries have established waste exchange systems, which makes waste exchange a resource [8]. In France, Germany, and the U.K., coal gangue was used as filling material for road embankments or the road base of arterial highways [9]. The use of coal gangue for power generation started early in developed countries. For example, Germany and Holland began to build coal power plants alongside coal preparation plants in the 1970s to recycle coal gangue for power generation. As some developed countries become less dependent on coal over time, the projects utilizing coal gangue for power generation have stalled in recent years [10]. Coal gangue combined with sulfate-reducing bacteria (SRB) could be used as a microbial organic fertilizer [11]. Land reclamation using coal gangue has been proven successful in Hungary, the former Soviet Union, the U.K., and the U.S. Coal gangue can also be used as cover material [12,13]. Although aboveground utilization of coal gangue in China has started only recently, an explosive development has occurred. Currently, about 140 million tons of coal gangue in China are annually used for power generation, which is equivalent to conserving approximately 38 million tons of standard coal [14]. Since the 1980s, China has consolidated the subgrade use of coal gangue as filling materials during road engineering [15].
Extensive theoretical and practical explorations of coal gangue recycling to prepare building materials and chemical raw materials have been conducted worldwide. Because of the high content of SiO2, Al2O3, and Fe2O3 [16], coal gangue has been used for manufacturing building materials, such as cement [17,18], bricks [19,20], lightweight aggregate concrete [21,22], and glass-ceramics [23]. Coal gangue, rich in Si, C, and Al, is also used to develop aluminum salt chemicals [24,25], silicon salt chemicals [26,27], carbon chemicals [28], and reinforcing materials [29]. Coal-producing countries keep developing and deepening the utilization of coal gangue on the ground, as shown in Figure 1.
Australia, Russia, Germany, Poland, the Ukraine, and other countries have also carried out backfill mining research on coal mining with pneumatic stowing [30], backfilling in highwall mining [31], partial backfilling [32], cemented paste backfilling [33,34,35,36] and other innovations in backfill mining [37,38,39,40].
The utilization rate of coal gangue in China has reached 73% [3]. Some major progress has been made in the industrialization of coal gangue recycling. However, due to the intrinsic features of coal gangue, technical limitations, and other external factors, the number of gangue recycling programs that can generate high economic yield and are practically feasible is limited [41]. More than 35% of coal gangue still exists in the form of waste heaps [42]. Given the huge annual production of coal gangue in China, the coal gangue recycling on the ground alone cannot meet the growing demands for gangue disposal. China encourages gangue backfill mining to control ground subsidence, farmland destruction, and coal gangue discharge on the ground. In particular, China has formulated favorable policies to push forward the disposal of coal gangue. According to the environmental protection tax law of China, the entities conducting coal gangue recycling in accordance with the national and local environmental protection standards are exempt from the environmental protection taxes (CNY 5 per ton of coal gangue). The resource tax will be cut by 50% for backfill mining. At present, the commonly used gangue backfilling technologies are mechanical backfilling, fully mechanized mining with solid backfilling [43], mixed workface using a gangue backfilling and caving method, longwall-roadway cemented backfilling, and paste backfilling [44,45]. These backfilling technologies are mainly intended for coal mining under buildings (structures), railways, and water bodies and are considered the key technologies for green coal mining [46]. The development of the underground disposal of coal gangue, especially gangue backfilling, is not only directly envisaged by the national policies, but meets the practical needs of backfill disposal.
The remaining part of this paper contains a review of existing gangue backfilling technologies. Their principles, advantages and deficiencies, efficiencies, and application conditions are discussed, and the latest progress in the high-efficiency, large-scale underground gangue backfilling technology is summarized. The key equipment for the underground gangue backfilling technology is also analyzed. This paper provides theoretical support for large-scale gangue backfilling in China.

2. The Current Status of Coal Gangue Discharge on the Ground in China

Coal gangue, as a solid waste generated during coal mining and washing, is a black-gray rock with low carbon content, low calorific value, and hard texture. Coal gangue is subdivided into the gangue generated during underground drifting and mining and the gangue generated during washing and dressing [47]. In addition to containing 20~30% carbon, coal gangue is generally dominated by oxides: SiO2 at 30~60%, Al2O3 at 15~40%, Fe2O3 at 2~10%, CaO, MgO, and K2O at 1~4%. There are also other trace elements such as boron and nickel. More coal gangue is generated in North and Northwest China than in South and Northeast China. The amount of coal gangue discharged in North China is close to 3.5 billion tons, which far exceeds that in other areas and accounts for about 50% of the total discharge [48]. As shown in Figure 2, the total amount of coal gangue generated in 25 coal-producing provinces of China from 2017 to 2021 was estimated as 2.80 billion tons. This estimate was made by conservatively assuming that gangue accounted for 15% of coal production. Besides, the coal gangue produced in these five years accounted for 40.0% of the total amount of coal gangue. The top ten provinces in terms of coal production generated 2.59 billion tons of coal gangue in the five years. As shown in Figure 3, darker areas on the map indicate greater coal gangue production. The coal gangue produced by the top ten provinces accounted for 92.6% of the total in the past five years, while that produced by Shanxi, Shaanxi, and Inner Mongolia accounted for 70% [3], which shows the characteristics of intensive coal gangue production.
As the intensification and the scale of China’s coal production have been rising, coal gangue production is increasing, and the centralized tendency of gangue production has become more pronounced. At present, most coal mines adopt two types of gangue disposal. The first one is to discharge the coal gangue aboveground and allow it to be utilized by other enterprises. However, the industrial and mining enterprises only utilize the coal gangue to a minimal degree due to the following factors: the high coal gangue discharge cost, scattered distribution of aboveground gangue disposal facilities, environmental protection policies applicable to gangue transportation, high gangue utilization costs, the complex process and technology of aboveground gangue disposal, and the high requirements for recycling due to the gangue composition [49,50]. The second one is to dump the gangue at a specified site in or near the mining area, thus forming waste heaps of varying sizes [51]. These waste heaps occupy valuable land resources, and the water leaching from the gangue pollutes the surrounding soil and groundwater [52]. Besides, the coal gangue contains combustible components, which may ignite spontaneously under proper conditions, leading to instability of the coal gangue [53,54]. Noxious gases generated by the spontaneous combustion, including sulfur dioxide, nitrogen oxides, carbon oxides, and smoke, can cause air and ecological pollution, which threatens local residents’ health [55].
The recycling of coal gangue on the ground can hardly meet the gangue disposal requirements. In contrast, underground gangue disposal technology has the benefits of high-efficiency, in-situ disposal, and the centralized distribution of disposal facilities. There is an urgent need to develop underground gangue backfilling technology, which meets the demand for centralized, high-yield, and large-scale gangue disposal.

3. Gangue Backfilling Technologies

Figure 4 shows the development process of gangue backfilling [44,45,56]. These technologies can accomplish the basic goals of backfilling, strata movement control, and safe production [57].

3.1. Mechanical Backfilling

Mechanical backfilling [58] is subdivided into roadway throwing-gangue mechanical backfilling (Figure 4a) and conventional mechanized mining with mechanical backfilling (Figure 4b). The key equipment in mechanical backfilling is the high-speed gangue throwing machine, mainly composed of an electric motor, driving roller, steering roller, carrier roller, gangue throwing belt, and the support [59]. The gangue throwing machine casts the gangue at a high speed into the goaf, thus using the gangue as backfill.

3.2. Fully Mechanized Mining with Solid Backfilling Technology

Fully mechanized mining with solid backfilling technology [60,61,62] (Figure 4c) is a suitable method for coal mining under buildings (structures), railways, and water bodies. The gangue produced by underground coal mining is initially crushed mechanically and then transported to the working face for in-situ backfilling. The filling materials in the goaf are compacted by the ramming mechanism [63,64]. The integrated underground mining-dressing-backfilling technology that combines solid backfilling mining and underground gangue dressing has appeared in response to China’s policies of green mine construction and to accommodate deep coal resources [65]. On this basis, the technical concept of “mining, dressing, backfilling + X” integrated green mining (Figure 4d) has been proposed. The “X” consists of active control for strata movement, gob-side entry retaining, gas extraction, disaster prevention and control, and water conservation mining [66,67,68].

3.3. Mixed Workface Using a Gangue Backfilling and Caving Method

A mixed workface using a gangue backfilling and caving method [69,70] (Figure 4e) refers to the use of a solid backfilling section, a conventional caving section, and a transition section in the same working face. The equipment for fully mechanized mining with solid backfilling technology and that of conventional fully mechanized mining are arranged in the same working face and work jointly to complete backfilling mining. In the working face of the backfilling section, backfilling shield and rear multihole-bottom-dump chain conveyor are arranged to backfill the gangue to the goaf for roof management. For the caving section’s working face, a conventional fully mechanized working is employed, and the conventional hydraulic supports are arranged. The goaf is managed by the caving method. Transition supports are installed in the transition segment [71].

3.4. Longwall-Roadway Cemented Backfilling

Longwall-roadway cemented backfilling [72] (Figure 4f) involves solid waste (such as coal gangue and fly ash) as the filling materials. The solid wastes are added with a cementing agent at a specific ratio to prepare a high-concentration paste by mixing without the additional need for dehydration [73]. The paste is delivered underground by a pipeline pumping system to backfill the goaf. In longwall-roadway cemented backfilling, the coal is broken using a bolter miner instead of a coal cutter via the longwall mining system. After the connection roadway has been excavated, the roadway is backfilled with cemented filling materials [74]. Another connection roadway is excavated simultaneously while the roadway is backfilled.

3.5. Paste Backfilling

Paste backfilling [75] (Figure 4g) uses paste transportation behind the hydraulic supports in the working face via the pipelines based on the original working face for fully mechanized mining. The backfilling, which is performed through the space dug out by the coal cutter, can proceed continuously along with the advancing working face. Fly ash, cement, and coal gangue are used as the primary filling materials for paste backfilling in fully mechanized mining. They are mixed at a specific ratio in the presence of additive material to prepare a paste without a critical flow rate or the need for dehydration. The main process consists of coal cutting, bag hanging, backfilling, and solidification. The key equipment used for paste backfilling behind the hydraulic support in fully mechanized mining is the backfilling shield, with a long rear top beam. The latter provides the roof support behind the working face, offers enough backfilling space, and prevents the roof caving or the paste entering into the working face [76].

3.6. Hybrid Gangue Backfilling Technology

Under the conditions of particular coal mines, two or more backfilling technologies may be used in combination, depending on ground control requirements. If there is a shortage of the fill materials, such as coal gangue, the above-mentioned backfilling technologies can be used concomitantly with superhigh water-filling materials. The combination of different backfilling technologies is common for aboveground gangue disposal while ensuring safe coal production [77].

4. Gangue Backfilling Technologies: Advantages and Deficiencies

Mechanical backfilling has a limited coal gangue disposal ability, and it is suitable only for a few roadways. This backfilling technology has been gradually abandoned [78].
Fully mechanized mining with solid backfilling technology has developed the key equipment, the backfilling shield and the multihole-bottom-dump chain conveyor, and formed a complete set of mature processes with a huge demand for underground coal gangue disposal. This technology reduces coal gangue discharge, alleviates the surface subsidence induced by mining, and improves the mining resource recovery rate [79,80]. However, this technology is associated with a high investment cost and high requirements for the working face. For example, the working face is required to be straight and the roof of the coal seam has to be intact.
The mixed workface using a gangue backfilling and caving method mainly applies to coal mines where there is a need to protect the aboveground structures, accompanied by a working face length above 220 m and the backfilling section’s maximum length of 150 m. This backfilling technology does not interfere with the mining operation and can protect the ground surface. In addition, its efficiency is 4–6 times that of the simple backfilling working face [81].
In longwall-roadway cemented backfilling, the working face can be arranged flexibly. This backfilling technology is more favored for residual mining area where the fully mechanized working face is difficult to arrange. It can be used for large-scale disposal of solid wastes such as coal gangue and fly ash. The paste is backfilled to the goaf via a pipeline pumping system from the surface backfilling stations, and the backfilled ratio can exceed 90%. This technology can effectively support the goaf, control the movement of the overlying strata, and protect the environment of the mining area [82].
Paste backfilling combines the advantages of cemented backfilling and fully mechanized mining with solid backfilling. The cemented filling materials are backfilled to the goaf of the fully mechanized working face via the pipeline. This technology has the benefits of the high degree of mechanization and high production capacity in the working face, its simple process, and its high system stability. It can effectively control the movement of overlying strata in the mining area and dispose of solid wastes such as coal gangue and fly ash on a large scale, hence protecting mines environment [83,84].
Some typical examples of applying underground gangue backfilling in coal mines in China are listed in Table 1. They are mainly concentrated in Shandong, Hebei, Shanxi, Henan, Anhui, and other provinces which have large populations and dense buildings. Coal gangue backfilling can reduce the impact of mining on the surface. Fully mechanized mining with solid backfilling technology is the most widely used among these applied technologies.

5. Problems and Proposed Solutions

5.1. Problems

At present, ground and aquifer control should be considered for most underground gangue backfilling technologies, which have to meet a specified backfilling ratio to ensure the stability of aboveground structures and aquifers [85,86]. For this reason, coal production and gangue disposal depend, to a certain degree, on the effect of backfilling. Backfilling may interfere with the mining operation, leading to a low gangue disposal efficiency. The backfilling efficiency is also influenced by the following factors: (i) a complex ramming mechanism in backfilling shields, (ii) the small transport capacity of the multihole-bottom-dump chain conveyor, and (iii) the insufficient automation degree, reliability, and/or efficiency of the key backfilling equipment. Due to these deficiencies, the current gangue backfilling technologies can hardly satisfy the demands of large-scale coal gangue disposal in China.

5.1.1. The Backfilling Process Effect on Gangue Backfilling Efficiency

Coal resources in Eastern China are being gradually exhausted, and their potential for coal production growth is limited. Considering that Eastern China is densely populated and built-up, its coal mining mostly occurs under buildings (structures), railways, and water bodies, which is becoming increasingly difficult. Large coal mines are mainly located in Middle and Western China, where coal production and the demand for coal gangue disposal has been growing [87,88,89,90,91]. For example, the annual amount of coal gangue at the Daliuta coal preparation plant of the Shandong Coal Group reached 5.10 million tons and at the Buertai Coal Mine it was approximately 3 million tons. At present, utilization and disposal technologies can hardly handle such a large amount of coal gangue efficiently.
For coal mines in Eastern China, backfilling materials need more strength to control the surface movement. However, for coal mines in Middle and Western China, the backfilling mining technologies no longer need to achieve a better backfilling effect, but aim to backfill efficiently under normal production. Backfill mining aimed at coal mining has been transferred from Eastern China to Middle and Western China. Therefore, the gangue backfilling technologies, adapted to coal mining under buildings (structures), railways, and water bodies, are no longer applicable to the large-scale coal gangue disposal in Middle and Western China.

5.1.2. The Effect of Equipment Performance on Gangue Backfilling Efficiency

Backfilling shields have undergone modification and innovation from a six-prop to four-prop configuration as the backfill mining technology has been improved over the years. Six generations of backfilling shields have been designed and optimized successively [92,93,94]. The backfilling shields can accommodate the change in mining height from 2.0 to 5.0 m. The support resistance offered by the shields has also increased from 4500 to 11,000 kN. These backfilling shields are mainly intended for coal mining under buildings (structures), railways, and water bodies. However, as the application scenarios change, the backfilling shields’ ramming mechanism has become a barrier to improving the backfilling efficiency. The purpose of the ramming is to compact the fill body and control ground movement. However, in Middle and Western China, there is no rigorous demand for surface protection and backfilling material strength, so the current ramming mechanism can no longer adapt to the new backfilling, which aims to dispose of coal gangue.
Several models of the multihole-bottom-dump chain conveyor have been designed, including SGBC630/150, SGBC764/250, SGBC764/300, and SGZC764/250 [95,96,97,98]. However, the existing multihole-bottom-dump chain conveyors generally have the deficiencies of low transport capacity, high accident rate, and low reliability. They generally fail in the task of disposing of a large amount of coal gangue. Multihole-bottom-dump chain conveyors have a low transport capacity, with a small dumping hole that is less optimized in shape, resulting in a limited dumping amount. They may bend, twist, or even rupture due to the hanging method and the multihole-bottom-dump chain conveyor may be clogged by coal gangue, leading to a rupture and a high accident rate. Therefore, the available multihole-bottom-dump chain conveyors can hardly satisfy the coal gangue requirements.

5.2. Prospects

The existing backfilling technologies and key equipment seem to impede the high-efficiency, large-scale backfilling of coal gangue. To satisfy the growing demands for gangue backfilling in the underground coal mines of Middle and Western China, innovative gangue backfilling technologies and more reliable key equipment are required. In addition, automation should be improved and the environmental effect of the coal gangue should be considered.

5.2.1. Innovative Gangue Disposal

(1)
Slurry backfilling in the goaf
The materials of slurry backfilling in the goaf consist of coal gangue from the coal preparation chamber and the water, which is prepared into a slurry with a certain concentration in the backfilling material preparation chamber. The rheological properties of slurry are excellent, stable, and convenient for pipeline transportation. The backfilling pump provides the power and transports the slurry to the roadway via the pipeline. Following this, the backfill slurry is placed into the adjacent or current goafs [99,100]. Its technical principles are illustrated in Figure 5. For adjacent goafs, slurry backfilling is undertaken at a certain distance ahead of the current working face. Through the section’s coal pillars between the two working faces, the slurry is injected from the roadway on the working face into the adjacent goaf. For the current goafs, pipeline laying and grouting are arranged at a triangular zone formed in the roadway after roof caving. As soon as the single-hole grouting is finished, the drill hole is sealed. The drill hole grouting is repeated at certain distances until slurry backfilling is completed for the entire goaf.
Slurry backfilling in the goaf has the benefits of being a simple process, having a high mechanization degree, large spaces of coal gangue backfilling, and a low investment cost. This technology is suitable for coal mining without ground protection, and due to having no ground structures, slurry materials don’t need great strength.
(2)
High-efficiency gangue backfilling in a super-long mining workface
High-efficiency gangue backfilling in a super-long mining workface is developed based on fully mechanized mining with solid backfilling technology for the purpose of the high-efficiency backfilling of a large amount of coal gangue. This technology mainly uses the coal gangue as the backfilling materials, which enters the goaf via the backfilling material vertical feeding hole system and the underground solid backfilling material transportation system. Its technical principle is shown in Figure 6.
The length of the working face in this backfilling technology usually exceeds 275 m. The maximum disposal capacity of coal gangue is more than five million tons per year, outperforming the previous gangue backfilling technologies by more than three times. This backfilling technology achieves high-efficiency disposal of a large-scale coal gangue without affecting the mine production capacity. Besides, it can reduce strata movement and protect the environment of the mining area. Because of these benefits, high-efficiency gangue backfilling in a super-long mining workface is particularly suitable for modern large coal mines in ecologically vulnerable regions of China, such as Shaanxi and Inner Mongolia.

5.2.2. Research and Development of New Equipment

(1)
Optimized design of the backfilling shield
The up-to-date high-efficiency backfilling mining should dispose of a large amount of coal gangue without affecting the coal mining. One significant change to the backfilling shield in response to this demand is removing the compactor. There has been a trend towards a compact structural design of backfilling shields to reduce the size, improve the space utilization rate, and support the efficiency of the shields. Specifically, the relative position between the four-bar linkage dimension, the linkage, and the post are optimized to achieve a compact spatial layout. The design of the working space under backfilling reduces the amount of ineffective space and achieves compact, safe, and effective goals. The length of the front and rear top beams is optimized so that the support better accommodates the roof deformation. The supporting line is moved backward to the tail of the top beam to accommodate roof caving and improve the coal mining and backfilling efficiency [101,102,103].
(2)
Research and development of a novel type of multihole-bottom-dump chain conveyor
The following aspects of the multihole-bottom-dump chain conveyor should be optimized to achieve the high-efficiency, fixed-point, and quantitative unloading of the filling materials, which includes: the gradation of coal gangue; the hanging method of the multihole-bottom-dump chain conveyor; the method of connection between the scrapers; strength of key components; and the position, size, and switch mode of the dumping hole [104,105].
As shown in Figure 7, a hydraulic cylinder can be used to hang the multihole-bottom-dump chain conveyor. By changing the original hanging method, one can avoid bending and compression of the multihole-bottom-dump chain conveyor and improve its reliability. The conveyor’s central double chain design is changed to a side double chain, increasing the dumping area of the dumping hole. The conventional rectangular shape of the dumping hole is changed to a shape consisting of a rectangle and a semicircle. An arched connection is adopted between the flashboard and scraper of the dumping hole to avoid height difference and prevent clogging by the coal gangue. The multihole-bottom-dump chain conveyor’s preferred transport capacity is 1000 t/h and above, as required by the high-efficiency large-scale gangue disposal technology.
(3)
Research and development of the gangue pipeline pumping system
Slurry backfilling in the goaf requires that the pipeline pumping system should have the desired transport performance for coal gangue and water over long distances without clogging. To meet this demand, one should further optimize the gangue-based slurry’s mix ratio for backfilling to ensure favorable rheological properties, a low bleeding rate, a uniform composition, and the convenience of pipeline transportation of slurry. During the transport, the pumping system’s capacity should be improved to accommodate a long distance by adding a smooth coating inside the transporting pipeline and by increasing the pumping power, to facilitate the continuous transport of coal gangue, and the backfilling of the goaf. Moreover, the stope’s spatial distribution can be accurately determined by numerical simulation or surveying to make preliminary decisions concerning the laying of the pipeline pumping system.

5.2.3. Automation

Australia, The United States, Canada, and other countries have carried out extensive research on the mechanization and automation of backfill mining, while in China, the current backfilling process primarily relies on the manual operation of machinery [106,107,108,109]. To increase the efficiency of coal gangue underground backfilling, the backfilling shield control program can be developed with the introduction of a digital electro-hydraulic control system, a displacement sensor, and an inclination sensor, which are essential for the automated control of support advancing and pushing. Meanwhile the automation of the pulling of the multihole-bottom-dump chain conveyor should be designed and implemented. These measures can achieve the goal of the automation of backfilling and support-advancing mining [110,111,112,113].
Dumping height ultrasonic sensors are used to detect the height and morphology of backfilling materials to achieve automatic control for opening or closing the dumping hole. The automation of the backfilling operation is realized by using signal acquisition with equipment such as ultrasound detectors, displacement sensors, and inclination sensors, and using the command control with the system controller [114,115,116].
After the backfilling operation is completed, the control system will receive signals and send automated commands about the support advancing and pushing; subsequently, signals will be sent back to the control system and trigger the automated control of the backfilling. Through the above process, a coordinated cyclic control system is established between the backfilling shield and the multihole-bottom-dump chain conveyor [117,118,119], achieving the automated control of the entire backfilling. The schematic diagram of an automated control system for backfilling is presented in Figure 8.
While not affecting the normal coal mining procedure and ensuring safe production, high-efficiency automated backfill mining accomplishes the efficient automatic backfilling of coal gangue, to achieve zero discharge of the mine waste and accommodate the demand for intensive, high-yield, and large-scale utilization of coal gangue in China. High-efficiency automated backfill mining offers a breakthrough solution to coal gangue disposal.

5.2.4. Attaching Importance to the Environmental Effects

In the process of coal gangue underground backfilling and disposal, in addition to environmental protection of the ground, we should pay special attention to the underground environmental benefits of the gangue-based filling body and the interactions between the coal gangue and the water environment [120,121,122]. However, few papers have considered the environmental benefits of coal gangue backfilling. Limited studies have shown that: (i) based on short-term data the coal gangue backfilling doesn’t damage the groundwater environment and may have minimal potential risks in the future [5], (ii)materials in the coal gangue filling can retard heavy metal accumulation [123], and (iii)some risk prevention and control methods have been established for groundwater environmental pollution by backfill mining [124]. These will minimize the ecological and environmental damage from mining [125], and achieve an environmentally friendly underground gangue backfilling and green sustainable development [126,127,128,129].

6. Conclusions

This paper summarizes the recycling of coal gangue on the ground, the existing coal gangue backfilling technology, and the latest progress of high-efficiency and large-scale coal gangue disposal technology; innovations of the key equipment and automation of the technology and some environmental benefits of coal gangue backfilling are also mentioned. The main conclusions are as follows:
(i)
The recycling of coal gangue on the ground is restricted by high cost and difficult technologies, which cannot meet the demand for coal gangue disposal;
(ii)
The existing underground gangue backfilling technologies include: mechanical backfilling, fully mechanized mining with solid backfilling technology, mixed workface using a gangue backfilling and caving method, longwall-roadway cemented backfilling, and paste backfilling. These technologies are mainly applied to coal mining under buildings (structures), railways, and water bodies in Eastern China. However, they have quite limited gangue disposal capacity due to inadequate equipment and low automation;
(iii)
Slurry backfilling in the goaf and high-efficiency gangue backfilling in a super-long mining workface have been innovatively developed, showing that the maximum disposal capacity of coal gangue can increase by three times, reaching five million tons per year;
(iv)
The key equipment and automation of the technology have been innovated, which can facilitate the intensive, high-yield, large-scale utilization of coal gangue. The environmental benefits of coal gangue are also mentioned. These will achieve green sustainable coal mining development.

Author Contributions

Conceptualization, W.S., J.Z. and M.L.; investigation, H.Y. and Y.Y.; data curation, W.S. and N.Z.; writing—original draft preparation, W.S. and Y.G.; writing—review and editing, W.S. and J.Z. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded the National Natural Science Foundation of China, grant number 52004271, the National Science Fund for Distinguished Young Scholars, grant number 51725403, the China Postdoctoral Science Foundation, grant number 2021M693417, the Jiangsu Postdoctoral Research Funding Program, grant number 2021K039A, and the Postgraduate Research & Practice Innovation Program of Jiangsu Province, grant number KYCX21_2359.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. The utilization of coal gangue on the ground.
Figure 1. The utilization of coal gangue on the ground.
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Figure 2. The annual coal gangue production in different provinces of China from 2017 to 2021.
Figure 2. The annual coal gangue production in different provinces of China from 2017 to 2021.
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Figure 3. The percentages of coal gangue production in different provinces of China from 2017 to 2021.
Figure 3. The percentages of coal gangue production in different provinces of China from 2017 to 2021.
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Figure 4. The history of the gangue backfilling technology development.
Figure 4. The history of the gangue backfilling technology development.
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Figure 5. Schematic diagram of slurry backfilling in the goaf.
Figure 5. Schematic diagram of slurry backfilling in the goaf.
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Figure 6. Schematic diagram of high-efficiency gangue backfilling technologies.
Figure 6. Schematic diagram of high-efficiency gangue backfilling technologies.
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Figure 7. Schematic diagram of a novel type of multihole-bottom-dump chain conveyor.
Figure 7. Schematic diagram of a novel type of multihole-bottom-dump chain conveyor.
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Figure 8. Schematic diagram of an automated control system for backfilling.
Figure 8. Schematic diagram of an automated control system for backfilling.
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Table
Table 1. The application of the gangue backfilling technologies in some coal mines of China.
Table 1. The application of the gangue backfilling technologies in some coal mines of China.
No.Coal MineProvince
Location		Applied
Technology		Backfilling
Materials		Disposal Capacity of Coal Gangue/(ton thousand t·a−1)
1Xingdong Coal MineHebeiRoadway throwing gangue mechanical backfillingGangue generated during roadway excavation (GRE)4.5
2Taiyuan Dongshan Coal MineShanxiGangue from the waste heap (GWH)15
3Shengquan Mining CompanyShandongConventional mechanized mining with mechanical backfillingGRE, GWH10
4E’zhuang Coal MineShandongGRE21.6
5Jisan Coal MineShandongFully mechanized mining with solid backfilling technologyGRE30
6Yangzhuang Coal MineAnhuiGRE30
7Huayuan Coal MineShandongGRE, GWH50
8Zhaizhen Coal MineShandongGWH, fly ash (FA)50
9Xinjulong Coal MineShandongGangue from underground washing and dressing (GWD)60
10Tangshan Coal MineHebeiGRE, GWH, GWD60
11Wugou Coal MineAnhuiGWH, FA70
12Taiyuan Coal MineInner
Mongolia		GWH, FA90
13Xingtai Coal MineHebeiGWH, FA45.5
14Tangkou Coal MineShandongGRE40
15Shi’er Coal MineHenanMixed workface using a gangue backfilling and caving methodGWH, GWD150
16Gongge Yingzi Coal MineInner
Mongolia		Longwall-roadway
cemented backfilling		GWH, FA45
17Xiaotun Coal MineHebeiPaste backfillingGWH, FA21
18Daizhuang Coal MineShandongGWH, FA23.2
19Xinyang Coal MineShanxiGWH, FA26.9
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Song, W.; Zhang, J.; Li, M.; Yan, H.; Zhou, N.; Yao, Y.; Guo, Y. Underground Disposal of Coal Gangue Backfill in China. Appl. Sci. 2022, 12, 12060. https://doi.org/10.3390/app122312060

AMA Style

Song W, Zhang J, Li M, Yan H, Zhou N, Yao Y, Guo Y. Underground Disposal of Coal Gangue Backfill in China. Applied Sciences. 2022; 12(23):12060. https://doi.org/10.3390/app122312060

Chicago/Turabian Style

Song, Weijian, Jixiong Zhang, Meng Li, Hao Yan, Nan Zhou, Yinan Yao, and Yaben Guo. 2022. "Underground Disposal of Coal Gangue Backfill in China" Applied Sciences 12, no. 23: 12060. https://doi.org/10.3390/app122312060

APA Style

Song, W., Zhang, J., Li, M., Yan, H., Zhou, N., Yao, Y., & Guo, Y. (2022). Underground Disposal of Coal Gangue Backfill in China. Applied Sciences, 12(23), 12060. https://doi.org/10.3390/app122312060

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