CN114472462A - Underground-aboveground linkage coal gangue disposal system and disposal method - Google Patents

Underground-aboveground linkage coal gangue disposal system and disposal method Download PDF

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CN114472462A
CN114472462A CN202111640225.XA CN202111640225A CN114472462A CN 114472462 A CN114472462 A CN 114472462A CN 202111640225 A CN202111640225 A CN 202111640225A CN 114472462 A CN114472462 A CN 114472462A
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coal gangue
underground
disposal
coal
grouting
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CN114472462B (en
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王晓东
朱世彬
武博强
王海
许刚刚
冯龙飞
韩乐
韩琳
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Xian Research Institute Co Ltd of CCTEG
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B5/00Operations not covered by a single other subclass or by a single other group in this subclass
    • EFIXED CONSTRUCTIONS
    • E21EARTH OR ROCK DRILLING; MINING
    • E21FSAFETY DEVICES, TRANSPORT, FILLING-UP, RESCUE, VENTILATION, OR DRAINING IN OR OF MINES OR TUNNELS
    • E21F15/00Methods or devices for placing filling-up materials in underground workings
    • E21F15/005Methods or devices for placing filling-up materials in underground workings characterised by the kind or composition of the backfilling material
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P40/00Technologies relating to the processing of minerals
    • Y02P40/10Production of cement, e.g. improving or optimising the production methods; Cement grinding
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/91Use of waste materials as fillers for mortars or concrete

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  • Environmental & Geological Engineering (AREA)
  • Mining & Mineral Resources (AREA)
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Abstract

The invention provides a system and a method for disposing underground-aboveground linkage coal gangue, which comprise an aboveground active coal gangue slurry preparation unit and an underground coal gangue underground disposal material preparation unit, wherein the aboveground active coal gangue slurry preparation unit is communicated with the underground coal gangue underground disposal material preparation unit, the aboveground active coal gangue slurry preparation unit is used for transporting prepared active coal gangue slurry to the underground coal gangue underground disposal material preparation unit, and the underground coal gangue underground disposal material preparation unit is used for preparing an underground coal gangue disposal material and filling and disposing a longwall goaf and/or a separation space. The invention can simultaneously dispose the coal gangue which is being produced from the coal gangue hill and the underground, and realizes the disposal of the gangue without lifting the well and the gangue on the surface.

Description

Underground-aboveground linkage coal gangue disposal system and disposal method
Technical Field
The invention belongs to the field of coal gangue solid waste disposal and resource utilization, and relates to a downhole-uphole linkage coal gangue disposal system and a disposal method.
Background
The coal gangue is rock with dry-basis ash content of more than 50% generated in the processes of coal mine well construction, development and excavation, coal mining and coal washing, and the discharge amount accounts for 10-20% of the coal yield. The coal gangue solid waste occupies a large amount of land resources, causes serious environmental damage, causes pollution to atmosphere, water sources, soil and the like in different degrees, and can cause geological disasters such as hillside landslide, collapse, debris flow and the like of a gangue dump. The 'underground filling of coal gangue and ground backfilling' are new directions for promoting the reduction of the coal gangue and the development of green mining industry, but how to achieve 'zero emission' of the coal gangue is a great problem to be solved urgently.
The existing coal gangue underground disposal technology comprises the following steps: directly throwing waste rock filling, water sand filling and cemented filling. The direct waste rock throwing filling method has potential safety hazard and coal resource waste problems and is forbidden to use; the disposal quantity of easy-to-collapse hole-blocking gangue in water sand filling is limited, and the gangue leachate enters an underground water environment to cause underground water pollution; the cementation filling method is characterized in that materials such as coal gangue, sand, broken stone, coal ash, loess, cement and the like are mixed to form cementation materials for filling underground spaces such as a goaf, a waste roadway, a separation layer and the like, the formed filling slurry contains a large amount of additional materials, the disposal amount of the coal gangue in unit filling amount is limited, the problems of capacity increase, labor hour increase, cost increase and the like exist, in the face of large-scale disposal of the coal gangue and limited underground spaces, the coal gangue cannot be disposed along with mining, the coal gangue after capacity increase cannot be disposed completely, namely, the coal gangue cannot be used up along with mining, and the coal gangue underground filling and ground backfilling cannot be realized at the same time. The coal gangue has activity, and the application of the coal gangue geopolymer prepared from the coal gangue as a filling cementing material in underground disposal of the coal gangue is not available, and the reason is as follows: 1) the coal gangue geopolymer gelling property needs to be excited, the excitation process is complex, and more factors need to be controlled; 2) the underground space of a mine is limited, and the coal gangue crushing and excitation difficulty is high.
Disclosure of Invention
Aiming at the defects in the prior art, the invention aims to provide a system and a method for disposing underground-aboveground linkage coal gangue.
In order to solve the technical problems, the invention adopts the following technical scheme:
the underground-aboveground linkage coal gangue disposal system comprises an aboveground active coal gangue slurry preparation unit and an underground coal gangue disposal material preparation unit, and is characterized in that the aboveground active coal gangue slurry preparation unit is communicated with the underground coal gangue disposal material preparation unit, the aboveground active coal gangue slurry preparation unit is used for transporting prepared active coal gangue slurry to the underground coal gangue disposal material preparation unit, and the underground coal gangue disposal material preparation unit is used for preparing underground coal gangue disposal materials and filling and disposing long-wall goafs and/or separation layer spaces;
the aboveground active coal gangue slurry preparation unit comprises an aboveground crushing device, a calcining device, a particle grinding device, an aboveground pulping device and a conveying pipeline which are connected; the aboveground crushing equipment is used for crushing ground coal gangue to obtain coal gangue fine materials; the calcining equipment is used for calcining the coal gangue fine materials and conveying the calcined coal gangue fine materials to the particle grinding equipment; the particle grinding equipment is used for decarbonizing and activating to form activated coal gangue powder, and the aboveground pulping equipment is used for mixing the activated coal gangue powder with water to obtain activated coal gangue slurry; the conveying pipeline is used for conveying the active coal gangue slurry to a preparation unit of underground coal gangue disposal materials in a well;
the underground coal gangue underground disposal material preparation unit comprises an underground coal gangue continuous conveying device, coal gangue underground sorting equipment, underground crushing equipment, underground pulping equipment and a cementing material preparation station which are connected;
the underground coal gangue continuous conveying device is used for conveying coal gangue generated on an underground coal mining working face to the underground coal gangue sorting equipment for sorting; the underground crushing equipment is used for crushing the coal gangue which is sorted by the underground sorting equipment and is used as solid waste to obtain coal gangue aggregate; the cementing material preparation station is communicated with the conveying pipeline through a conveying pipeline in an underground roadway; the cementing material preparation station is used for mixing water glass and an alkaline excitation material, cooling the mixture to prepare an excitation solution, and mixing the active coal gangue slurry conveyed by a conveying pipeline in the underground roadway with the excitation solution to form a coal gangue-based geopolymer cementing material; the underground pulping equipment is used for mixing the coal gangue-based geopolymer cementing material and the coal gangue aggregate to prepare a coal gangue underground disposal material.
The coal gangue underground treatment material filling system comprises an underground drill site and an equipment room, wherein the underground drill site and the equipment room are connected with the underground pulping equipment through a slurry conveying pipeline, and the coal gangue underground treatment material is filled into a longwall goaf and/or a separation space;
the particle grinding equipment is a ball mill; the underground crushing equipment is internally provided with a crushing system, a screening system and a coarse material reworking system.
The invention discloses an underground disposal method of all coal gangue, which adopts an underground-aboveground linkage coal gangue disposal system to carry out underground disposal of all coal gangue and comprises the following steps:
determining the coal gangue disposal amount of the longwall goaf according to the total void fracture space amount of the longwall goaf, selecting a grouting hole of the longwall goaf, and filling the coal gangue underground disposal material into the longwall goaf through the grouting hole of the longwall goaf according to the coal gangue disposal amount of the longwall goaf;
and/or selecting a grouting layer position of a separation space, determining the coal gangue disposal amount of the separation space according to the maximum limit injection-production ratio of the separation space, and sequentially filling the coal gangue disposal materials into the grouting layer position of the separation space according to the coal gangue disposal amount of the separation space according to a grouting sequence;
and the filling speed of filling the coal gangue underground disposal material is greater than or equal to the coal gangue generation speed.
Further, the total amount of void fracture space in the longwall gob is determined by the following formula:
V=λ×2L×lt×hm
wherein V is the total amount of the space of the gap and the crack of the longwall goaf, and the unit is m3(ii) a L is the limit collapse distance, and the unit is m; h ismThe unit is m for the mining height of the coal bed; ltAdvancing length for coal mining in units of m; lambda is a time factor, and 0.95 is taken when the coal is just mined; within 1 year of mining time, taking 0.9-0.4; mining for 1 to 3 years, and taking 0.4 to 0.3; mining for more than 3 years, and taking 0.3-0.25;
the limit collapse distance L is determined by the following formula:
L=3×min{Lt,Ls,Ly}
wherein L istThe limit span is formed under the action of bending moment when the old top beam is broken, and the unit is m; l issThe limit span is formed under the action of shear stress when the old top beam is broken, and the unit is m; l isyIs the actual monitored cycle step size in m.
Furthermore, the limit span L formed under the action of bending moment when the old top beam is brokentCalculated by the following formula:
Figure BDA0003443670620000031
the limit span L formed under the action of shear stress when the old top beam is brokensCalculated by the following formula:
Figure BDA0003443670620000032
wherein σtIs the basic roof rock tensile strength in kPa; sigmasIs the basic roof rock shear strength in kPa; h is the base top thickness in m; q is a radicalThe upper part of the top is uniformly distributed with load, and the unit is kPa;
the substantially top uniform load q is calculated by:
Figure BDA0003443670620000033
wherein, γiIs the weight of each stratum at the top of the base layer and has the unit of N/m3;hiIs the thickness of each layer of rock formation substantially on top, in m;
Figure BDA0003443670620000034
is the average weight of the basic top overburden rock layer and has the unit of N/m3;hcIs the thickness of the basic roof overburden in m; the value range of i is a positive integer from 1 to n.
Further, the grouting holes of the selected longwall goaf comprise directional construction grouting holes with the goaf, which is formed in longwall mining and is 1-2 m away from the end of the isolation coal pillar, as a target point;
the coal gangue disposal amount of the longwall goaf comprises the coal gangue disposal amount of the longwall goaf determined according to the coal gangue proportion in the filled coal gangue underground disposal material and the total amount of the void fracture space of the longwall goaf.
Further, the selection of the grouting horizon of the separation space comprises the following steps:
step 1, judging the rock stratum rigidity according to a drilling histogram, preliminarily judging a strong bearing rock stratum, and determining a plurality of key layers in the rock stratum;
step 2, calculating the breaking distance of each key layer in the plurality of key layers;
step 3, selecting a layer with a final hole layer position located above the comprehensive height top boundary of the water flowing fractured zone and larger than 20m and a limit mining width corresponding to the breaking distance of the key layer and larger than the width of the grouting filling working face from the plurality of key layers as a grouting layer position;
if the selected grouting layer position is one, grouting in the grouting layer position; and if the selected grouting positions are multiple, sequentially grouting the multiple grouting positions according to the sequence of the breaking distance value of each key layer from small to large.
Further, the breaking distance L of the key layerxCalculated from the following formula:
Figure BDA0003443670620000041
wherein: h isxThe thickness of the key layer of the x layer is m; sigmatxThe tensile strength of the key layer of the x layer is expressed in kPa; q. q.sxThe unit of the load borne by the key layer of the x layer is kPa; the value range of x is a positive integer from 1 to n;
the limit mining width corresponding to the breaking distance of the key layer is calculated by the following formula:
Figure BDA0003443670620000042
wherein s is the limit mining width corresponding to the breaking distance of the key layer and the unit is m; l isxThe breaking distance of the key layer is m; h is the distance between the key layer and the mining coal bed and the unit is m; and delta is the fracture angle of the overlying strata of the coal bed and has the unit of.
Further, the maximum limit injection-production ratio of the separation space is calculated by the following formula:
Figure BDA0003443670620000043
in the formula: alpha is the maximum limit injection-production ratio of the separation space; s is the limit mining width corresponding to the breaking distance of the key layer, and the unit is m; hzThe distance between the grouting filling section and the coal seam is m; h ismThe unit is m for the mining height of the coal bed; phi is a full mining angle, and the unit is DEG; hcThe height of the caving zone is m; k'pThe residual crushing and swelling coefficient of the goaf is 1.03-1.05; xi is the cause of grouting filling system, filling and mining matchingAnd the limiting coefficient is in a value range of 0.6-0.8.
Further, activated coal gangue powder rich in aluminosilico minerals in the coal gangue underground disposal material and the coal gangue aggregate are mixed according to the mass ratio of 1 (1-4);
the coal gangue-based geopolymer cementing material comprises the following components in percentage by mass: 200-300 parts of activated coal gangue powder rich in silica-alumina minerals, 20-40 parts of water glass, 5-10 parts of alkaline excitation materials and 120-900 parts of water;
the activated coal gangue powder rich in the silicon-aluminum mineral is prepared by crushing coal gangue through crushing equipment to ensure that the particle size of the coal gangue is less than 5mm, and adding Na into coal gangue particles with the particle size of less than 5mm2CO3After the powder is stirred, the powder is calcined for 0.5 to 4 hours at a high temperature of 500 to 850 ℃ for decarburization activation, and then ball milling is carried out by a ball mill to obtain the powder with an average particle size of less than 40 mu m and a specific surface area of 3500 to 5000cm2Activated coal gangue powder per gram, wherein the activated coal gangue powder with the particle size of less than 10 mu m accounts for 30-50 percent;
the Na is2CO3The mixing amount of the powder is 3 per mill of the mass of coal gangue particles smaller than 5 mm;
the modulus of the water glass is 1.0-1.3;
the alkali excitation material comprises one or more of sodium hydroxide, potassium hydroxide or quicklime;
the coal gangue aggregate is coal gangue with the maximum particle size of 5-20 mm after the coal gangue is crushed.
Compared with the prior art, the invention has the following technical effects:
the method (1) can simultaneously treat the coal gangue hill on the ground and the coal gangue being extracted underground, thereby realizing the purposes of no lifting of the gangue and treatment of the gangue on the ground surface; (2) the self-activity of the coal gangue is effectively excited by utilizing the self-characteristics of the coal gangue to prepare the cementing material, the in-situ crushed coal gangue aggregate can be wrapped and cured to form aggregate slurry, so that underground water pollution caused by infiltration of pollutants caused by the coal gangue in a high ground stress environment for a long time can be prevented, the coal gangue can be substituted for the doping of cement to promote the maximum disposal of the coal gangue, and the method has a huge popularization and application prospect; (3) the coal gangue underground disposal material is filled into the goaf, so that the broken rock mass in the goaf can be solidified, a top plate is supported, and the problem that the ecological environment is damaged due to surface subsidence caused by overlying strata settlement of the goaf is solved; (4) filling coal gangue underground disposal materials into the separation space can prevent the main key layer from being broken and can also prevent the ecological environment problem caused by surface subsidence.
Drawings
FIG. 1 is a schematic flow diagram of a downhole-uphole linkage coal gangue disposal system according to the present invention;
FIG. 2 is a schematic view of a downhole-uphole linkage coal gangue disposal system and disposal according to the present invention;
FIG. 3 is a schematic diagram of a delamination space disposal in a downhole-uphole linkage coal gangue disposal according to the present invention;
FIG. 4 is a schematic view of disposing a gob in a coal gangue disposing device in a downhole-uphole linkage manner according to the present invention;
FIG. 5 is a schematic view of a grouting pipe for underground disposal materials with preset coal gangue in a goaf according to the present invention;
the reference numbers are as follows:
1. a coal gangue dump; 2. an uphole crushing device; 3. a calcination apparatus; 4. a particulate grinding device; 5. aboveground pulping equipment; 6. A directional hole; 7. a delivery conduit; 8. conveying pipelines in the underground tunnel; 9. a coal gangue continuous conveying device under the well; 10. coal gangue sorting equipment; 11. a downhole crushing device; 12. a downhole pulping device; 13. a cementitious material preparation station; 14. a slurry delivery pipe; 15. a grouting pipe; 16. a gob; 17. isolating the coal pillars; 18. a roadway; 19. underground drill sites and equipment rooms; 20. A ground surface; 21. an earth formation; 22. a coal seam floor; 23. a top soil layer; 24. a primary key layer; 25. a weak rock formation; 26. a second sub-critical layer; 27 sub-critical layer one; 28, a coal seam roof; 29. a separation space; 1-1, presetting a grouting pipe; 1-2, automatic control valve.
The present invention will be explained in further detail with reference to examples.
Detailed Description
The following embodiments of the present invention are provided, and it should be noted that the present invention is not limited to the following embodiments, and all equivalent changes based on the technical solutions of the present invention are within the protection scope of the present invention.
When grouting is performed in the longwall goaf or the separation space, the two are sequentially grouted. Normally, when a working face is filled along with mining, a goaf is filled firstly, because the goaf is formed firstly, when the working face is pushed to a nearly middle position, a separation space appears, the separation space is filled, and then after the separation space is filled, the goaf can be filled at the pushing mining end section of the working face. And grouting can be performed to the corresponding crack space through directional drilling according to the operation near the working surface at the time of the crack space.
The following is an explanation of technical terms to which the present invention relates:
the injection-production ratio is the percentage of the volume of the compacted ash filled in the overlying rock to the volume of the produced rock.
A delamination space refers to the space between layers that results from unsynchronized subsidence between different strata of the roof.
The grouting holes of the longwall goaf are directional construction grouting holes taking the goaf at a position 1-2 m away from the end of the isolation coal pillar during longwall mining as a target point; after mining, the middle part of the goaf is compacted, the closer to the isolation coal pillar, the larger the goaf injectable space is, so that the goaf in the goaf formed by longwall mining, which is 1-2 m away from the end of the isolation coal pillar, serves as a target point directional construction grouting hole, and the grouting position is determined by selecting the grouting hole. The "end parts" refer to two ends of a horizontal plane, and as shown in fig. 4, the distance between the grouting pipe 15 located at the left end of the isolation coal pillar 17 and the goaf 16 is 1-2 m.
The related parameters in the scheme are explained as follows:
Figure BDA0003443670620000061
Figure BDA0003443670620000071
example 1
According to the technical scheme, with reference to fig. 1, the embodiment provides a downhole-uphole linkage coal gangue disposal system, which includes an uphole active coal gangue slurry preparation unit and a downhole coal gangue underground disposal material preparation unit, wherein the uphole active coal gangue slurry preparation unit is communicated with the downhole coal gangue underground disposal material preparation unit, the uphole active coal gangue slurry preparation unit is used for transporting the prepared active coal gangue slurry to the downhole coal gangue underground disposal material preparation unit, and the downhole coal gangue underground disposal material preparation unit is used for preparing a coal gangue underground disposal material and filling and disposing a longwall goaf and/or a separation space;
the aboveground active coal gangue slurry preparation unit comprises an aboveground crushing device 2, a calcining device 3, a particle grinding device 4, an aboveground pulping device 5 and a conveying pipeline 7 which are connected; the underground crushing equipment 2 is used for crushing ground coal gangue to obtain coal gangue fine materials; the calcining equipment 3 is used for calcining the coal gangue fine materials and conveying the calcined coal gangue fine materials to the particle grinding equipment 4; the particle grinding equipment 4 carries out decarburization and activation to form activated coal gangue powder, and the aboveground pulping equipment 5 is used for mixing the activated coal gangue powder with water to obtain activated coal gangue slurry; the conveying pipeline 7 is used for conveying the active coal gangue slurry to a preparation unit of underground coal gangue disposal materials;
specifically, the conveying mode among the aboveground crushing equipment 2, the calcining equipment 3, the particle grinding equipment 4 and the aboveground pulping equipment 5 is a continuous conveying mode, the continuous conveying mode comprises a belt conveying mode and the like, and the whole process is closed, so that dust pollution is prevented;
the method comprises the following steps: conveying the coal gangue collected from a ground 20 coal gangue dump 1 to an aboveground crushing device 2 for crushing in a continuous conveying mode, crushing the coal gangue until the particle size is less than 5mm, and adding Na into the coal gangue particles with the particle size less than 5mm2CO3After the powder is evenly stirred, the crushed coal gangue fine materials are conveyed to a calcining device 3 in a continuous conveying mode to be calcined and then conveyed to a particle grinding device 4 to be decarburized and activated to form activated coal gangue powder, and the activated coal gangue powder is conveyed to an aboveground pulping device 5 to be uniformly mixed with waterAnd (3) uniformly mixing, preparing active coal gangue slurry, drilling from the ground to the underground, installing a slurry conveying pipeline 7 in the directional hole 6, and conveying the active coal gangue slurry to an underground coal gangue underground disposal material preparation unit by utilizing the conveying pipeline 7.
The temperature of the calcining equipment 3 is adjustable and controllable, and the temperature range meets the calcining requirement of 500-850 ℃; the internal part of the cabin of the calcining equipment 3 is constantly stirred in a rolling way, so that the fine coal gangue materials can be rapidly and uniformly calcined, the calcining time is determined according to the physical and mechanical properties of required slurry and the leaching toxicity result of the original coal gangue produced by underground coal mining, and the fine coal gangue materials are continuously fed and discharged, so that the supply of the calcined fine coal gangue materials is ensured;
furthermore, the particle grinding equipment 4 is a ball mill and the like, which can ensure that the average particle diameter of the activated coal gangue micro powder is less than 40 mu m, the particle diameter of less than 10 mu m accounts for 30-50 percent, and the specific surface area is 3500cm2/g~5000cm2/g。
In another embodiment of this embodiment, the preparation unit for underground coal gangue disposal material includes an underground coal gangue continuous conveying device 9, an underground coal gangue sorting device 10, an underground crushing device 11, an underground pulping device 12 and a cementing material preparation station 13, which are connected to each other, where the underground coal gangue continuous conveying device 9 is configured to convey coal gangue produced in an underground coal mining working face into the underground coal gangue sorting device 10 for sorting; the underground coal gangue continuous conveying device 9 can be a gangue conveying belt. The underground crushing equipment 11 is used for crushing the sorted coal gangue serving as solid waste to obtain coal gangue aggregate; the gelled material preparation station 13 is communicated with a conveying pipeline 8 in an underground roadway; the cementing material preparation station 13 is used for mixing water glass and an alkaline excitation material, cooling the mixture to prepare an excitation solution, and mixing the active coal gangue slurry conveyed by the conveying pipeline 8 in the underground roadway with the excitation solution to form a coal gangue-based geopolymer cementing material; the underground pulping equipment 12 is used for mixing the coal gangue-based geopolymer cementing material and coal gangue aggregate to prepare the coal gangue underground disposal material.
The underground drilling site and the equipment room 19 are connected with the underground pulping equipment 12 through a slurry conveying pipeline 14, and coal gangue underground disposal materials are filled into the longwall goaf and/or the separation space;
in this embodiment, the downhole crushing plant 11 has built-in crushing, screening and coarse rework systems. According to the filling requirement, the parameters of the crushing system are adjusted, the coal gangue is crushed, the gangue aggregate meeting the particle size requirement is screened out by using the screening system, and the gangue not meeting the particle size requirement reaches the crushing system again through the coarse material reworking system for secondary crushing. The coal gangue underground sorting equipment 10, the underground crushing equipment 11, the underground pulping equipment 12 and the cementing material preparation station 13 are all suitable for underground narrow spaces, and the input and output of all materials are continuous processes. Meanwhile, the underground coal gangue continuous conveying device is in a sealed environment, so that underground dust is prevented.
Example 2
The embodiment discloses an all-coal gangue underground disposal method on the basis of the embodiment 1, and the underground-aboveground linkage coal gangue disposal system in the embodiment 1 is adopted to perform all-coal gangue underground disposal, and the method comprises the following steps:
determining the coal gangue disposal amount of the longwall goaf according to the total void fracture space amount of the longwall goaf, selecting a grouting hole of the longwall goaf, and filling the coal gangue underground disposal material into the longwall goaf through the grouting hole of the longwall goaf according to the coal gangue disposal amount of the longwall goaf;
and/or selecting a grouting layer position of a separation space, determining the coal gangue disposal amount of the separation space according to the maximum limit injection-production ratio of the separation space, and sequentially filling the coal gangue underground disposal materials into the grouting layer position of the separation space according to the coal gangue disposal amount of the separation space according to a grouting sequence;
and the filling speed of filling the coal gangue underground disposal material is greater than or equal to the coal gangue generation speed. The above-mentioned filling is performed in particular from the underground drill site and the equipment room 19 through the grout pipe 15.
In a preferred embodiment of this embodiment, specifically, the total amount of the void fracture space of the longwall gob is determined by the following formula:
V=λ×2L×lt×hm
wherein V is the total amount of the space of the gap and the crack of the longwall goaf, and the unit is m3(ii) a L is the limit collapse distance, and the unit is m; h ismThe unit is m for the mining height of the coal bed; ltAdvancing length for coal mining in units of m; lambda is a time factor, and 0.95 is taken when the coal is just mined; within 1 year of mining time, taking 0.9-0.4; mining for 1 to 3 years, and taking 0.4 to 0.3; mining for more than 3 years, and taking 0.3-0.25;
specifically, the limit collapse distance L is determined by the following formula:
L=3×min{Lt,Ls,Ly}
wherein L istThe limit span is formed under the action of bending moment when the old top beam is broken, and the unit is m; l issThe limit span is formed under the action of shear stress when the old top beam is broken, and the unit is m; l isyIs the actual monitored cycle step size in m. The specific calculation is Lt,Ls,LyThe minimum value of the three values is taken and then multiplied by 3, namely the limit collapse distance.
The limit span L formed under the action of bending moment when the old top beam is brokentCalculated by the following formula:
Figure BDA0003443670620000101
the limit span L formed under the action of shear stress when the old top beam is brokensCalculated by the following formula:
Figure BDA0003443670620000102
wherein σtIs the basic roof rock tensile strength in kPa; sigmasIs the basic roof rock shear strength in kPa; h is the base top thickness in m; q is the load uniformly distributed on the top of the basic part, and the unit is kPa;
the substantially top uniform load q is calculated by:
Figure BDA0003443670620000103
wherein, γiIs the weight of each stratum at the top of the base layer and has the unit of N/m3;hiIs the thickness of each layer of rock formation substantially on top, in m;
Figure BDA0003443670620000104
is the average weight of the basic top overburden rock layer and has the unit of N/m3;hcIs the base top overburden thickness in m.
Further, the grouting holes of the selected longwall goaf comprise directional construction grouting holes with the goaf, which is formed in longwall mining and is 1-2 m away from the end of the isolation coal pillar, as a target point;
the coal gangue disposal amount of the longwall goaf comprises the coal gangue disposal amount of the longwall goaf determined according to the coal gangue proportion in the filled coal gangue underground disposal material and the total amount of the void fracture space of the longwall goaf.
In a preferred embodiment of this embodiment, specifically, selecting a grouting level of the delamination space includes the following steps:
step 1, judging the rock stratum rigidity according to a drilling histogram, preliminarily judging a strong bearing rock stratum, and determining a plurality of key layers in the rock stratum; the key layers include a main key layer and a sub-key layer. Referring to fig. 3-4, there is one main critical layer 24 and two sub-critical layers, sub-critical layer two 26 and sub-critical layer one 27.
Step 2, calculating the breaking distance of each key layer in the plurality of key layers;
step 3, selecting a layer with a final hole layer position located above the comprehensive height top boundary of the water flowing fractured zone and larger than 20m and a limit mining width corresponding to the breaking distance of the key layer and larger than the width of the grouting filling working face from the plurality of key layers as a grouting layer position;
if the selected grouting layer position is one, grouting in the grouting layer position; and if the selected grouting positions are multiple, sequentially grouting the multiple grouting positions according to the sequence of the breaking distance value of each key layer from small to large.
By comparing the breaking distance values of the key layers, the smaller the breaking distance value of the key layer is, the rock stratum can be broken first, and the broken key layer does not generate a separation space, so that grouting is performed first.
Breaking distance L of the key layerxCalculated from the following formula:
Figure BDA0003443670620000111
wherein: h isxThe thickness of the key layer of the x layer is m; sigmatxThe tensile strength of the key layer of the x layer is expressed in kPa; q. q.sxThe unit of the load borne by the key layer of the x layer is kPa;
the limit mining width corresponding to the breaking distance of the key layer is calculated by the following formula:
Figure BDA0003443670620000112
wherein s is the limit mining width corresponding to the breaking distance of the key layer and the unit is m; l isxThe breaking distance of the key layer is m; h is the distance between the key layer and the mining coal bed and the unit is m; delta is the fracture angle of the overlying strata of the coal seam, and the unit is DEG;
and the width w of the grouting filling working face of the separation space is smaller than the limit mining width s corresponding to the breaking distance of the key layer.
The comprehensive height of the water-flowing fractured zone is comprehensively determined according to the height of a theoretical water-flowing fractured zone and the height of an actual water-flowing fractured zone, the height of the theoretical water-flowing fractured zone is calculated and determined according to a related formula of a procedure (a coal pillar setting and coal pressing mining procedure of buildings, water bodies, railways and main headings), and the height of the actual water-flowing fractured zone is determined according to the leakage amount of a drilling flushing fluid on site and a drilling television peeking method.
Further, the maximum limit injection-production ratio of the separation space is calculated by the following formula:
Figure BDA0003443670620000113
in the formula: alpha is the maximum limit injection-production ratio of the separation space; s is the limit mining width corresponding to the breaking distance of the key layer, and the unit is m; hzThe distance between the grouting filling section and the coal seam is m; h ismThe unit is m for the mining height of the coal bed; phi is a full mining angle, and the unit is DEG; hcThe height of the caving zone is m; k'pThe residual crushing and swelling coefficient of the goaf is 1.03-1.05; xi is a limiting coefficient of a grouting filling system, filling and mining matching and the like, and the value range is 0.6-0.8.
The actual value of the width w of the grouting filling working face is smaller than the limit mining width s corresponding to the breaking distance of the key layer, so that the actual injection-production ratio is smaller than the calculated maximum limit injection-production ratio.
The actual injection-production ratio of the separation space is calculated by the following formula:
Figure BDA0003443670620000114
αsand w is the actual injection-production ratio of the separation space, the width of a grouting filling working face is w < s, and the unit is m.
Determining the coal gangue disposal amount of the separation space according to the maximum limit injection-production ratio of the separation space, namely finally determining the coal gangue disposal amount according to the actual injection-production ratio alphasAnd the coal mining volume (known quantity) in the working face to obtain the volume of the compacted ash body filled in the overlying rock, wherein the volume of the compacted ash body filled in the overlying rock is equal to the groutable space of the separation space, namely the volume of the coal gangue underground disposal material of the separation space. Determining the density of the coal gangue underground disposal material by using a test method, and then combining the coal gangue with the coal gangue underground disposal materialThe mass ratio of the materials can obtain the disposal quantity of the coal gangue in the separation space.
In the embodiment, the coal gangue underground disposal material is conveyed to the underground gap fracture space in a pumping mode through an underground conveying pipeline, so that the coal gangue underground disposal material and a loose accumulation body in a goaf form cementation, on one hand, the coal gangue in the mining process is disposed in real time, the coal gangue is prevented from being soaked in underground water in a high ground stress environment for a long time, and then the coal gangue pollutant is prevented from being percolated to cause underground water pollution, and on the other hand, a cementation and solidification supporting top plate is formed in the goaf to prevent surface subsidence.
Further, as shown in fig. 5, a coal gangue underground disposal material grouting pipe 1-1 can be preset before the underground coal mining working face is pushed, the end of the grouting pipe is sealed, an automatic control valve 1-2 is arranged in the pipeline at a certain distance, the grouting amount is calculated according to the size of the working face, the coal seam mining height and the collapse and expansion coefficient, the real grouting amount is calculated by using the diameter of the grouting pipeline and the grouting time, and the control valves are opened from far to near in sequence to gradually fill the gap and crack space of the goaf.
Furthermore, a directional drilling method can be selected to construct a directional grouting hole, and the coal gangue underground disposal material is conveyed to the gap fracture space by using the directional grouting hole to dispose the coal gangue being mined.
The method for underground disposal of the full coal gangue obtains the coal gangue yield 1728m according to the coal mining advancing speed of 6 m/day, the working face width of 240m, the coal seam mining height of 6m and the coal gangue proportion of 20 percent in the coal mining process3The day is. Selecting proper underground coal gangue sorting and crushing equipment, matching corresponding coal gangue underground disposal material slurry conveying pipelines, and reasonably selecting the number of grouting holes and grouting flow rate by combining determined coal gangue disposal amount, coal mining propulsion speed, underground coal gangue sorting and crushing capacity and coal gangue underground disposal material slurry pipeline conveying capacity, wherein the filling speed when filling the coal gangue underground disposal material is more than or equal to coal gangue generation speed, temporary accumulation of underground coal gangue is reduced, and coal gangue lift-up is avoided.
In the embodiment, the activated coal gangue powder rich in the aluminosilico mineral in the coal gangue underground disposal material and the coal gangue aggregate are mixed according to the mass ratio of 1 (1-4);
the coal gangue-based geopolymer cementing material comprises the following components in percentage by mass: 200-300 parts of activated coal gangue powder rich in silica-alumina minerals, 20-40 parts of water glass, 5-10 parts of alkaline excitation materials and 120-900 parts of water;
the activated coal gangue powder rich in the silicon-aluminum mineral is prepared by crushing coal gangue through crushing equipment to make the particle size of the coal gangue smaller than 5mm, and adding Na into the coal gangue particles with the particle size smaller than 5mm2CO3After the powder is stirred, calcining the powder for 0.5 to 4 hours by high-temperature equipment at 500 to 850 ℃ for decarburization and activation, and then ball milling the powder by a ball mill to obtain the powder with the average particle size of less than 40 mu m and the specific surface area of 3500 to 5000cm2Activated coal gangue powder per gram, wherein the activated coal gangue powder with the particle size of less than 10 mu m accounts for 30-50 percent;
Na2CO3the mixing amount of the powder is 3 per mill of the mass of coal gangue particles smaller than 5 mm;
the modulus of the water glass is 1.0-1.3;
the alkali excitation material comprises one or more of sodium hydroxide, potassium hydroxide or quicklime;
the coal gangue aggregate is coal gangue with the maximum particle size of 5-20 mm after coal gangue crushing.
This example presents a preferred solution: the width of a working face of a certain mine is 240m, and the coal mining advancing length lt3000m, the coal seam mining height is 6m, the main key layer is sandy mudstone, the layer thickness is 49m, the overlying load borne by the main key layer is 2.0MPa, and the tensile strength of the main key layer is 2.37 MPa.
In this example, the total amount of void fracture space in the longwall gob is calculated as follows:
according to the measured data, the tensile strength of the basic roof rock is 4.03MPa, the shear strength is 6.2MPa, the basic roof thickness h is 15m, and the average density of the overlying strata is 2400kg/m3And the thickness of the top cover rock layer is 296.3 m.
Calculated limit span L formed under the action of bending momentt=13.03m;
Limit span L formed under shear stresss=17.44m
Periodic pressure L in coal mining processyIs 15 m.
And (3) synthesizing the ultimate span and period pressure results under the action of bending moment and shearing stress, and determining that the ultimate collapse distance L is 39 m. The minimum value of the three is multiplied by 3 to 13 multiplied by 3 to 39 m.
Calculating the void fracture space V of the longwall gob to be 0.95 multiplied by 2 multiplied by 39 multiplied by 6 multiplied by 3000 to be 1333800m3
The usage amount of the coal gangue underground disposal material is determined according to the total amount of the void fracture space of the longwall goaf, and the coal gangue disposal amount of the longwall goaf is determined according to the coal gangue proportion and the coal gangue underground disposal material density in the filled coal gangue underground disposal material. The method comprises the following specific steps:
the total space amount of the gap and the crack of the longwall goaf is 1333800m3The dosage of the coal gangue underground disposal material is 1333800m3The mass ratio of the coal gangue to the coal gangue underground disposal material is 62.5-66.7%; the density of the coal gangue underground disposal material is known to be 1750-2350 kg/m3(ii) a The disposal amount of the coal gangue is 1458843.75-2090664.81 t.
The coal gangue output of the working face is known to be 864000 m3The average density of the coal gangue is about 1700 to 1800kg/m3The output quality of the coal gangue on the working face is 1468800-1555200 t, and the amount of the coal gangue in the gap fracture space formed by the working face is equal to or less than the amount of the coal gangue in the gap fracture space formed by the working face, which indicates that sufficient goaf gap fracture space carries out underground cooperative treatment on the coal gangue produced by mining on the working face, the coal gangue can be filled along with mining on the same working face, and the coal gangue in the adjacent working face can be treated by using the residual fracture space.
In this embodiment, in step 2 of selecting a grouting position of the separation space, the maximum value of the breaking distance of the key layer is selected for filling by calculating the breaking distances of the plurality of key layers. Calculating the breaking distance L of the maximum key layerx=75.4m;
Meanwhile, the distance H between the key layer and the mining coal layer is 163m, the fracture angle delta of the overlying strata of the coal layer is 62 degrees, therefore, the limit mining width s corresponding to the fracture distance of the maximum key layer is calculated by a formula to be s-248.8 m, and the width w of the grouting filling working face of the off-bed space is smaller than the limit mining width s corresponding to the fracture distance of the key layer.
In the step 3, knowing that the total thickness of the coal seam is 6m, the overlying strata is a medium-hard top plate, the height of a theoretical water flowing fractured zone is 39.8-51.0 m, and the corresponding fracturing-mining ratio is 6.6-8.5. Obtaining the comprehensive result according to the leakage amount of the flushing liquid for drilling on site and the drilling television: the height of an actual water flowing fractured zone is 106-121 m, and the fracturing-mining ratio is 17.7-20.2.
Therefore, the comprehensive height of the water-flowing fractured zone is comprehensively determined to be below 121m according to the height of the theoretical water-flowing fractured zone and the height of the actual water-flowing fractured zone.
In order to prevent the separation zone from being communicated with the water flowing fractured zone during grouting, a safety distance of more than 20m, namely more than 141m, is reserved between the grouting layer and the top boundary of the water flowing fractured zone, and the key layer is located 163m above the coal bed, meets the requirements and can be used as the grouting layer.
Obtaining the comprehensive result according to the leakage amount of the flushing liquid for drilling on site and the drilling television: height H of caving zonec19.13m, coal seam mining height hm6.0m, the width w of the grouting filling working face is 240m, and the distance H between the main grouting filling section and the coal seamzIs 163m, the full mining angle phi is 53 degrees, and the residual crushing and expanding coefficient K of the goaf'pTaking 1.03, taking 0.75 as the limiting coefficient xi of the reasons of the grouting filling system, filling and mining matching and the like, substituting the limiting coefficient xi into a formula to calculate the actual injection-mining ratio alpha of the separation spaces=33.1%。
The coal gangue emission amount is known to be about 10% -20% of the coal yield, and the injection-production ratio is calculated to be 33.1% and is far more than 20%. The coal gangue is filled into the separation space, so that the coal gangue can be filled along with mining.
Actual injection-production ratio alphas(33.1%) is less than the calculated maximum limiting voidage replacement ratio alpha (34.34%). According to the actual injection-production ratio alphasAnd the coal extraction volume in the working face to obtain the volume of the compacted ash body, namely the volume of the coal gangue underground disposal material. Benefit toDetermining the density of the coal gangue underground disposal material by using a test method, and combining the mass ratio of the coal gangue to the coal gangue underground disposal material to obtain the coal gangue disposal amount of a separation space. The method comprises the following specific steps:
the volume of the coal gangue underground disposal material is 33.1 percent multiplied by 240 multiplied by 6 multiplied by 3000 as 1429920m3
The mass ratio of the coal gangue to the coal gangue underground disposal material is 62.5-66.7%;
the density of the coal gangue underground disposal material is 1750-2350 kg/m3
The disposal amount of coal gangue in the separation space is 1563975-2241328.1 t.
The output quality of the coal gangue on the working face is 1468800-1555200 t, and the coal gangue disposal quantity is smaller than the coal gangue disposal quantity of the separation space, so that the sufficient separation space is used for underground cooperative disposal of the coal gangue produced by mining the working face, the coal gangue can be mined and filled along with the same working face, and the coal gangue in the adjacent working face can be disposed by using the residual crack space.
Example 3
In this example, on the basis of example 2, the specific mixture ratio of the coal gangue underground disposal material and the performance data thereof are given.
Proportioning 1: the activated coal gangue powder rich in aluminosilico minerals in the coal gangue underground disposal material and the coal gangue aggregate are in a mass ratio of 1 (1-4), wherein the coal gangue-based geopolymer cementing material comprises the following components in percentage by mass: 200 parts of activated coal gangue powder rich in silicon-aluminum minerals, 1.0 and 28 parts of water glass modulus, 5 parts of NaOH and 210 parts of water. 200 parts of coal gangue aggregate.
Further, calcining for 0.5h at 600 ℃ in a high-temperature device for decarburization and activation. The water is common tap water or mine water after treatment, has good water quality, does not contain heavy metal and harmful components, meets the national underground water standard, and does not pollute underground water.
The difference between the mixture ratio 2 and the mixture ratio 1 is as follows: the coal gangue-based geopolymer cementing material comprises the following components in percentage by mass: 250 parts of activated coal gangue powder rich in silicon-aluminum minerals, 1.1 parts of water glass modulus, 32 parts of NaOH 8 parts of water and 380 parts of water. 500 parts of coal gangue aggregate.
The difference between the mixture ratio 3 and the mixture ratio 1 is as follows: the coal gangue-based geopolymer cementing material comprises the following components in percentage by mass: 300 parts of activated coal gangue powder rich in silicon-aluminum minerals, 1.3 parts of water glass modulus, 20 parts of NaOH 10 parts and 750 parts of water. 1200 parts of coal gangue aggregate.
The difference between the mixture ratio 4 and the mixture ratio 1 is as follows: the coal gangue-based geopolymer cementing material comprises the following components in percentage by mass: 200 parts of activated coal gangue powder rich in silica-alumina minerals, 1.0 part of water glass modulus, 30 parts of water glass modulus, 7 parts of KOH and 350 parts of water. 450 parts of coal gangue aggregate.
The ratio 5 is different from the ratio 1 in that: the coal gangue based geopolymer cementing material comprises the following components in percentage by mass: 250 parts of activated coal gangue powder rich in silicon-aluminum minerals, 1.1 and 28 parts of water glass modulus, 8 parts of KOH and 500 parts of water. 750 parts of coal gangue aggregate.
The mixture ratio 6 is different from the mixture ratio 1 in that: the coal gangue-based geopolymer cementing material comprises the following components in percentage by mass: 300 parts of activated coal gangue powder rich in silicon-aluminum minerals, 1.2 parts of water glass modulus, 25 parts of KOH 9 parts and 650 parts of water. 900 parts of coal gangue aggregate.
The difference between the mixture ratio 7 and the mixture ratio 1 is as follows: the coal gangue-based geopolymer cementing material comprises the following components in percentage by mass: 200 parts of activated coal gangue powder rich in silicon-aluminum minerals, 1.0 part of water glass modulus, 30 parts of CaO 5 parts of water and 220 parts of water. 200 parts of coal gangue aggregate.
The difference between the mixture ratio 8 and the mixture ratio 1 is as follows: the coal gangue based geopolymer cementing material comprises the following components in percentage by mass: 250 parts of activated coal gangue powder rich in silicon-aluminum minerals, 1.0 part of water glass modulus, 30 parts of CaO 8 parts of water and 380 parts of water. 500 parts of coal gangue aggregate.
The properties of the all-coal gangue underground disposal material obtained by different mass parts are shown in the table below, and the material injected into the gap fracture space has cementation property, generates certain strength and prevents the overlying rock stratum from being suddenly broken.
TABLE 1 properties of coal gangue underground disposal materials obtained by different mass portion ratios
Figure BDA0003443670620000151
Figure BDA0003443670620000161
The invention has the advantages that: (1) the coal gangue produced in the ground and the coal gangue produced underground can be treated simultaneously, so that the gangue is not lifted in the well and the surface gangue is treated; (2) the self-activity of the coal gangue is effectively excited by utilizing the self-characteristics of the coal gangue to prepare the cementing material, the in-situ crushed coal gangue aggregate can be wrapped and cured to form aggregate slurry, so that underground water pollution caused by infiltration of pollutants caused by the coal gangue in a high ground stress environment for a long time can be prevented, the advantage of maximally utilizing the disposal of the coal gangue by replacing the doping of cement can be realized, and the method has a huge popularization and application prospect; (3) the coal gangue underground disposal material is filled into the goaf, so that the broken rock mass in the goaf can be solidified, a top plate is supported, and the problem that the ecological environment is damaged due to surface subsidence caused by overlying strata settlement of the goaf is solved. (4) The coal gangue underground disposal material is filled into the separation space, so that the main key layer can be prevented from being broken, and the ecological environment problem caused by surface subsidence can also be prevented.

Claims (10)

1. The underground-aboveground linkage coal gangue disposal system comprises an aboveground active coal gangue slurry preparation unit and an underground coal gangue disposal material preparation unit, and is characterized in that the aboveground active coal gangue slurry preparation unit is communicated with the underground coal gangue disposal material preparation unit, the aboveground active coal gangue slurry preparation unit is used for transporting prepared active coal gangue slurry to the underground coal gangue disposal material preparation unit, and the underground coal gangue disposal material preparation unit is used for preparing underground coal gangue disposal materials and filling and disposing long-wall goafs and/or separation layer spaces;
the aboveground active coal gangue slurry preparation unit comprises an aboveground crushing device (2), a calcining device (3), a particle grinding device (4), an aboveground pulping device (5) and a conveying pipeline (7) which are connected with one another; the aboveground crushing equipment (2) is used for crushing ground coal gangue to obtain coal gangue fine materials; the calcining equipment (3) is used for calcining the coal gangue fine materials and conveying the calcined coal gangue fine materials to the particle grinding equipment (4); the particle grinding equipment (4) performs decarburization activation to form activated coal gangue powder, and the aboveground pulping equipment (5) is used for mixing the activated coal gangue powder with water to obtain activated coal gangue slurry; the conveying pipeline (7) is used for conveying the active coal gangue slurry to a preparation unit of underground coal gangue disposal materials;
the underground coal gangue underground disposal material preparation unit comprises an underground coal gangue continuous conveying device (9), an underground coal gangue sorting device (10), an underground crushing device (11), an underground pulping device (12) and a cementing material preparation station (13) which are connected;
the underground coal gangue continuous conveying device (9) is used for conveying coal gangue generated on an underground coal mining working face to the coal gangue underground sorting equipment (10) for sorting; the underground crushing equipment (11) is used for crushing the coal gangue which is separated by the underground sorting equipment (10) and is used as solid waste to obtain coal gangue aggregate; the cementing material preparation station (13) is communicated with the conveying pipeline (7) through a conveying pipeline (8) in an underground roadway; the cementing material preparation station (13) is used for mixing water glass and an alkaline excitation material, cooling the mixture to prepare an excitation solution, and mixing the active coal gangue slurry conveyed by the conveying pipeline (8) in the underground roadway with the excitation solution to form a coal gangue-based geopolymer cementing material; the underground pulping equipment (12) is used for mixing the coal gangue-based geopolymer cementing material and the coal gangue aggregate to prepare a coal gangue underground disposal material.
2. The system for disposing the coal gangue linkage underground-aboveground according to the claim 1, further comprising an underground drill site and an equipment room (19), wherein the underground drill site and the equipment room (19) are connected with the underground pulping equipment (12) through a slurry conveying pipeline (14), and the underground disposal material of the coal gangue is filled into a longwall goaf and/or a separation space;
the particle grinding equipment (4) is a ball mill; the underground crushing equipment (11) is internally provided with a crushing system, a screening system and a coarse material reworking system.
3. An underground all-coal gangue disposal method is characterized in that the underground all-coal gangue disposal system of any one of claims 1 to 2 is adopted to carry out underground all-coal gangue disposal, and the method comprises the following steps:
determining the coal gangue disposal amount of the longwall goaf according to the total void fracture space amount of the longwall goaf, selecting a grouting hole of the longwall goaf, and filling the coal gangue underground disposal material into the longwall goaf through the grouting hole of the longwall goaf according to the coal gangue disposal amount of the longwall goaf;
and/or selecting a grouting layer position of a separation space, determining the coal gangue disposal amount of the separation space according to the maximum limit injection-production ratio of the separation space, and sequentially filling the coal gangue disposal materials into the grouting layer position of the separation space according to the coal gangue disposal amount of the separation space according to a grouting sequence;
and the filling speed of filling the coal gangue underground disposal material is greater than or equal to the coal gangue generation speed.
4. The underground disposal method of full coal gangue as claimed in claim 3, wherein the total amount of void fracture space of the longwall gob is determined by the following formula:
V=λ×2L×lt×hm
wherein V is the total amount of the space of the gap and the crack of the longwall goaf, and the unit is m3(ii) a L is the limit collapse distance, and the unit is m; h ismThe unit is m for the mining height of the coal bed; ltAdvancing length for coal mining in units of m; lambda is a time factor, and 0.95 is taken when the coal is just mined; within 1 year of mining time, taking 0.9-0.4; mining for 1 to 3 years, and taking 0.4 to 0.3; mining for more than 3 years, and taking 0.3-0.25;
the limit collapse distance L is determined by the following formula:
L=3×min{Lt,Ls,Ly}
wherein L istThe limit span is formed under the action of bending moment when the old top beam is broken, and the unit is m; l is a radical of an alcoholsThe limit span is formed under the action of shear stress when the old top beam is broken, and the unit is m; l isyIs the actual monitored cycle step size in m.
5. The underground disposal method for all-coal gangue according to claim 4, wherein the limit span L formed under the action of bending moment when the old roof beam breaks is formedtCalculated by the following formula:
Figure FDA0003443670610000021
the limit span L formed under the action of shear stress when the old top beam is brokensCalculated by the following formula:
Figure FDA0003443670610000022
wherein σtIs the basic roof rock tensile strength in kPa; sigmasIs the basic roof rock shear strength in kPa; h is the base top thickness in m; q is the load uniformly distributed on the top of the basic part, and the unit is kPa;
the substantially top uniform load q is calculated by:
Figure FDA0003443670610000023
wherein, gamma isiIs the weight of each stratum at the top of the base layer and has the unit of N/m3;hiIs the thickness of each layer of rock formation substantially on top, in m;
Figure FDA0003443670610000031
is the average weight of the basic top overburden rock layer and has the unit of N/m3;hcIs the thickness of the basic roof overburden in m; the value range of i is a positive integer from 1 to n.
6. The underground disposal method for the full coal gangue as claimed in claim 3, wherein the selecting of the grouting holes of the longwall goaf comprises directional construction of the grouting holes by taking the goaf which is 1-2 m away from the end of the isolation coal pillar in the goaf formed in longwall mining as a target point;
the coal gangue disposal amount of the longwall goaf comprises the coal gangue disposal amount of the longwall goaf determined according to the coal gangue proportion in the filled coal gangue underground disposal material and the total amount of the void fracture space of the longwall goaf.
7. The underground disposal method of all-coal gangue as claimed in claim 3, wherein the selection of the grouting horizon of the separation space comprises the following steps:
step 1, judging the rock stratum rigidity according to a drilling histogram, preliminarily judging a strong bearing rock stratum, and determining a plurality of key layers in the rock stratum;
step 2, calculating the breaking distance of each key layer in the plurality of key layers;
step 3, selecting a layer with a final hole layer position located above the comprehensive height top boundary of the water flowing fractured zone and larger than 20m and a limit mining width corresponding to the breaking distance of the key layer and larger than the width of the grouting filling working face from the plurality of key layers as a grouting layer position;
if the selected grouting layer position is one, grouting in the grouting layer position; and if the selected grouting positions are multiple, sequentially grouting the multiple grouting positions according to the sequence of the breaking distance value of each key layer from small to large.
8. The underground disposal method for all-coal gangue according to claim 3, wherein the breaking distance L of the key layerxCalculated from the following formula:
Figure FDA0003443670610000032
wherein: h isxThe thickness of the key layer of the x layer is m; sigmatxThe tensile strength of the key layer of the x layer is expressed in kPa; q. q.sxThe unit of the load borne by the key layer of the x layer is kPa; the value range of x is a positive integer from 1 to n;
the limit mining width corresponding to the breaking distance of the key layer is calculated by the following formula:
Figure FDA0003443670610000033
wherein s is the limit mining width corresponding to the breaking distance of the key layer and the unit is m; l isxThe breaking distance of the key layer is m; h is the distance between the key layer and the mining coal bed and the unit is m; and delta is the fracture angle of the overlying strata of the coal bed and has the unit of.
9. The underground disposal method of full coal gangue as claimed in claim 4, wherein the maximum limit injection-production ratio of said separation space is calculated by the following formula:
Figure FDA0003443670610000041
in the formula: alpha is the maximum limit injection-production ratio of the separation space; s is the limit mining width corresponding to the breaking distance of the key layer, and the unit is m; hzThe distance between the grouting filling section and the coal seam is m; h ismThe unit is m for the mining height of the coal bed; phi is a full mining angle, and the unit is DEG; hcThe height of the caving zone is m; k'pThe residual crushing and swelling coefficient of the goaf is 1.03-1.05; xi is a limiting coefficient of a grouting filling system, filling and mining matching and the like, and the value range is 0.6-0.8.
10. The underground disposal method of all-coal gangue according to claim 3, wherein activated coal gangue powder rich in aluminosilico minerals in the underground disposal material of coal gangue and the aggregate of coal gangue are mixed according to a mass ratio of 1 (1-4);
the coal gangue-based geopolymer cementing material comprises the following components in percentage by mass: 200-300 parts of activated coal gangue powder rich in silica-alumina minerals, 20-40 parts of water glass, 5-10 parts of alkaline excitation materials and 120-900 parts of water;
the activated coal gangue powder rich in the silicon-aluminum mineral is prepared by crushing coal gangue through crushing equipment to ensure that the particle size of the coal gangue is less than 5mm, and adding Na into coal gangue particles with the particle size of less than 5mm2CO3After the powder is stirred, the powder is calcined for 0.5 to 4 hours at a high temperature of 500 to 850 ℃ for decarburization activation, and then ball milling is carried out by a ball mill to obtain the powder with an average particle size of less than 40 mu m and a specific surface area of 3500 to 5000cm2Activated coal gangue powder per gram, wherein the activated coal gangue powder with the particle size of less than 10 mu m accounts for 30-50 percent;
the Na is2CO3The mixing amount of the powder is 3 per mill of the mass of coal gangue particles smaller than 5 mm;
the modulus of the water glass is 1.0-1.3;
the alkali excitation material comprises one or more of sodium hydroxide, potassium hydroxide or quicklime;
the coal gangue aggregate is coal gangue with the maximum particle size of 5-20 mm after the coal gangue is crushed.
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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114776370A (en) * 2022-05-18 2022-07-22 中煤地生态环境科技有限公司 Method for treating coal gangue
CN115199326A (en) * 2022-07-25 2022-10-18 中国矿业大学 Method for dynamic disaster of space gangue grouting filling weakening overlying rock after coal mining
CN115203852A (en) * 2022-07-25 2022-10-18 中国矿业大学 Method for determining grouting time of coal mining subsequent space gangue

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20160311625A1 (en) * 2014-06-25 2016-10-27 China University Of Mining And Technology Solid filling coal mining feeding and conveying monitoring system
CN107246279A (en) * 2017-07-11 2017-10-13 太原理工大学 Underground selecting and purchasing sieve, which is mixed, fills the cementing construction filling system of integrated spoil and method
CN210343417U (en) * 2019-03-29 2020-04-17 新汶矿业集团有限责任公司 Realize closely knit filling system that full roof was met in collecting space area filling tunnel in pit
CN112343651A (en) * 2020-06-24 2021-02-09 山东恒驰矿业装备科技有限公司 Process and equipment for filling mining by using coal gangue
CN213928441U (en) * 2021-05-08 2021-08-10 兰州资源环境职业技术学院 Complete equipment for backfilling from top to bottom of well suitable for promoting ecological management in mine area waste rock treatment
CN113565510A (en) * 2021-07-05 2021-10-29 太原理工大学 Ultra-thick coal seam fully mechanized caving filling mining method based on underground gangue pile
CN113716917A (en) * 2021-09-08 2021-11-30 河北建筑工程学院 Preparation method of coal gangue coarse aggregate concrete

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20160311625A1 (en) * 2014-06-25 2016-10-27 China University Of Mining And Technology Solid filling coal mining feeding and conveying monitoring system
CN107246279A (en) * 2017-07-11 2017-10-13 太原理工大学 Underground selecting and purchasing sieve, which is mixed, fills the cementing construction filling system of integrated spoil and method
CN210343417U (en) * 2019-03-29 2020-04-17 新汶矿业集团有限责任公司 Realize closely knit filling system that full roof was met in collecting space area filling tunnel in pit
CN112343651A (en) * 2020-06-24 2021-02-09 山东恒驰矿业装备科技有限公司 Process and equipment for filling mining by using coal gangue
CN213928441U (en) * 2021-05-08 2021-08-10 兰州资源环境职业技术学院 Complete equipment for backfilling from top to bottom of well suitable for promoting ecological management in mine area waste rock treatment
CN113565510A (en) * 2021-07-05 2021-10-29 太原理工大学 Ultra-thick coal seam fully mechanized caving filling mining method based on underground gangue pile
CN113716917A (en) * 2021-09-08 2021-11-30 河北建筑工程学院 Preparation method of coal gangue coarse aggregate concrete

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114776370A (en) * 2022-05-18 2022-07-22 中煤地生态环境科技有限公司 Method for treating coal gangue
CN114776370B (en) * 2022-05-18 2024-04-16 中煤地生态环境科技有限公司 Method for treating coal gangue
CN115199326A (en) * 2022-07-25 2022-10-18 中国矿业大学 Method for dynamic disaster of space gangue grouting filling weakening overlying rock after coal mining
CN115203852A (en) * 2022-07-25 2022-10-18 中国矿业大学 Method for determining grouting time of coal mining subsequent space gangue
CN115199326B (en) * 2022-07-25 2024-04-09 中国矿业大学 Dynamic disaster method for weakening overburden rock by grouting, filling and weakening space gangue after mining of coal mine
CN115203852B (en) * 2022-07-25 2024-05-14 中国矿业大学 Method for determining grouting time of space gangue after coal mining

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