CN108975367A - A kind of efficient method using high alumina coal gangue - Google Patents

A kind of efficient method using high alumina coal gangue Download PDF

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CN108975367A
CN108975367A CN201810822655.5A CN201810822655A CN108975367A CN 108975367 A CN108975367 A CN 108975367A CN 201810822655 A CN201810822655 A CN 201810822655A CN 108975367 A CN108975367 A CN 108975367A
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coal gangue
high alumina
acid
alumina coal
gangue
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CN108975367B (en
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夏举佩
辜芳
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Kunming University of Science and Technology
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    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F7/00Compounds of aluminium
    • C01F7/02Aluminium oxide; Aluminium hydroxide; Aluminates
    • C01F7/20Preparation of aluminium oxide or hydroxide from aluminous ores using acids or salts
    • C01F7/26Preparation of aluminium oxide or hydroxide from aluminous ores using acids or salts with sulfuric acids or sulfates
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B33/00Silicon; Compounds thereof
    • C01B33/113Silicon oxides; Hydrates thereof
    • C01B33/12Silica; Hydrates thereof, e.g. lepidoic silicic acid
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F7/00Compounds of aluminium
    • C01F7/02Aluminium oxide; Aluminium hydroxide; Aluminates
    • C01F7/44Dehydration of aluminium oxide or hydroxide, i.e. all conversions of one form into another involving a loss of water
    • C01F7/441Dehydration of aluminium oxide or hydroxide, i.e. all conversions of one form into another involving a loss of water by calcination
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    • C01INORGANIC CHEMISTRY
    • C01GCOMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
    • C01G49/00Compounds of iron
    • C01G49/009Compounds containing, besides iron, two or more other elements, with the exception of oxygen or hydrogen
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    • C01INORGANIC CHEMISTRY
    • C01PINDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
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    • C01P2006/12Surface area
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01PINDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
    • C01P2006/00Physical properties of inorganic compounds
    • C01P2006/19Oil-absorption capacity, e.g. DBP values
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01PINDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
    • C01P2006/00Physical properties of inorganic compounds
    • C01P2006/80Compositional purity

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  • Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
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Abstract

The invention discloses a kind of methods that high alumina coal gangue efficiently utilizes, and belong to industrial solid castoff application technology as the second resource field;This method is will to solidify after gangue or slag acid adding, it is acidified again, dissolve out, be filtered, washed obtain sulfur acid aluminium based on sulfate liquor and Silicon-rich removal of impurities acid sludge, sulfate liquor is used to prepare aluminium hydroxide or aluminium oxide, polyaluminium sulfate iron product, and acid sludge produces white carbon black through calcining;This method utilization of resources is reasonable, and without new solid waste discharge, product market constant is big, and a kind of practicable method can be provided for the resource utilization of high alumina coal gangue.

Description

A kind of efficient method using high alumina coal gangue
Technical field
The present invention discloses a kind of method for efficiently utilizing high alumina coal gangue, belong to industrial solid castoff resource utilization and Technical field of resource comprehensive utilization.
Background technique
Currently, gangue is a kind of black rock in coalification course with coal seam association, it is to choose and exploit in coal The waste generated in the process.The yield of the annual gangue in China reaches the 15%-20% of coal mining total amount, reaches national industry Waste generates the 40% of total amount, but total utilization rate is not high, and by 2015, the utilization rate of gangue just reached 70%, from The target that utilization of coal gangue utilization rate reaches 80% is far apart, and pressure is very huge.A large amount of Piling of Gangue is together not A large amount of soil can be only occupied, the ecological environment on periphery can be also polluted, also will cause the waste of resource.It is asked to solve these Topic, will not only reinforce the innovation and popularization of traditional technology, it is necessary to explore that other utilizations of resources are reasonable, environmentally friendly technique skill Art, by all kinds of means, multipath reinforce utilization of coal gangue utilize.
Extracting valuable element from gangue and producing related chemical products is a hot spot for efficiently utilizing gangue at present; The gangue in China is in the majority with clay class, mostly contains aluminium element more, therefore extracting aluminium oxide from pelite gangue is in recent years The research hotspot come.The method for extracting aluminium oxide from gangue at present mainly has acid system, alkaline process, sintering process, and alkaline process is due to alkali Dosage is big, and aluminium recovery is low, level of residue it is big there are secondary pollution and the utilization of resources it is unreasonable, and sintering process energy consumption is high, is country Provide the technical matters that should not be used, therefore the proper method of gangue synthetical recovery valuable element is acid system.
A kind of method that CN201310315648.3 has invented high efficiency extraction iron aluminium titanium from gangue, gangue is done It is dry, crush after for neutralizing dry method acidleach, the acid sludge that pickle liquor is obtained by filtration is dry, and then acid adding mixes, through acidleach, molten It solves, be filtered, washed, dry, and repeat above step, improve the dissolution rate of Iron in Coal Gangue aluminium titanium;The advantage of the invention is that Most of carbonate, purifying mass in raw material, which are eliminated, using acid-soluble material improves the utilization rate of acid;Dissolution rate after acidleach Height is conducive to the later use of acid sludge.
CN201610545655.6 proposes a kind of method for improving the leaching rate of aluminium in gangue, is existed with NaOH aqueous alkali Efficient-decomposition gangue under atmospheric low-temperature improves the leaching rate of aluminium element;Advantages of the present invention: this method does not need high temperature dehydration Roasting, reaction temperature is low, and the reaction time is short;Compared with traditional handicraft, operation of the present invention mild condition greatly reduces reaction temperature Degree and reaction pressure, easy to operate and green high-efficient, low energy consumption, and environmental pollution is small, the dissolution rate of aluminium element can reach 60% with On.
CN200510048215.1 is related to a kind of method for producing aluminium oxide using coal gangue as raw material, by smashed coal Spoil is leached after high-temperature roasting with sodium hydroxide solution, filters residue, and filtrate is passed through CO2Gas makes Al (OH)3Precipitating, vacuum Filtering, high temperature dehydration obtain Al2O3Product.Advantage of the invention is that reacting item using roasting salt-leaching combination method production technology Part is mild, and production process is easy to control, and the waste water that technique generates can be recycled, and the waste residue generated after extraction can be used as rubber The filler of product, environmentally protective, the recovery rate of aluminium oxide is also very high.
CN201010266645.1 is related to the side that a kind of coal gangue combustion lime-ash extracts aluminium oxide, silica and iron oxide Method, gangue according to calorific value situation coal blending, realizes activating coal gangue while calcining power generation after pretreatment, generated Electric power and steam are used for system;Lime-ash acidity extraction aluminium oxide, alkalinity extraction silica, and the comprehensive benefit for passing through by-product With extraction iron oxide;Acid required for each process procedure, alkali, lime, extractant, CO2It is recycled in system.Bastard coal of the invention The energy and chemical group Chengdu in stone are fully used, and drastically reduce the discharge amount of greenhouse gases and waste residue, improve The economic benefit of system is that a kind of novel gangue greenization and high value added utilization technology, competitive advantage are obvious.
CN201310315648.3 discloses a kind of method of high efficiency extraction ferro-aluminum titanium in gangue, belongs to coal solid Waste resource utilization technology field, gangue, for neutralizing the lysate of dry method acidleach clinker, neutralize after drying, grinding Terminal acid concentration or pH value dissolve titanium oxide content in object out according to acidleach and determine;The filtered neutralization filtrate of neutralization reaction is used for Aluminium, iron or aluminium, iron, titanium are separated, filter residue is neutralized and does not have to washing, directly acid adding mixing, carries out acid in chamber type electric resistance furnace after drying Leaching reaction, is dissolved after reaction, is filtered, washed, filtrate is neutralized with fresh gangue, circulating repetition aforesaid operations, this hair Bright method utilization rate is high, and the dissolution rates such as aluminium, iron, titanium are high, is aluminium, iron, titanium products open new raw material resources, it can be achieved that bastard coal Stone high value added utilization.
Cheng Fangqin etc. has studied the influence factor that aluminium oxide is extracted from gangue, the results showed that, leaching time is to oxidation The dissolution of aluminium influences maximum.The optimal conditions of dissolution be leaching time 3h, 650 DEG C of calcination temperature, hydrochloric acid acid amount 225mL(according to Aluminium oxide and the molar ratio of hydrochloric acid reaction are 1:6 meter in gangue), solid-to-liquid ratio 1:3.
In conclusion researcher has done many work in terms of the efficient dissolution of gangue, especially in gangue In terms of the high efficiency extraction of aluminium element and in terms of the preparation of related chemical products;But by reasonable process optimization and product design, The method of polymeric aluminum sulfate iron, aluminium hydroxide (or further calcining production aluminium oxide) and white carbon black is produced also not using gangue Appear in the newspapers announcement.
Summary of the invention
The purpose of the present invention is to provide a kind of method for efficiently utilizing high alumina coal gangue, this method is original with high alumina spoil Material adds according to its own calorific value directly using or by remake extraction valuable element raw material after recirculating fluidized bed recycling heat 98% industrial sulphuric acid of mass concentration is first solidified, then according to chemical composition supplement residual acid, then it is acidified reaction, dissolved out Journey extracts acid-soluble material aluminium, iron etc., and acid sludge roasting direct produces white carbon black;Acid-soluble material prepares polymeric aluminum sulfate iron and aluminium hydroxide (or aluminium oxide) product, calcining acid-soluble material tail gas recycle sulfuric acid be recycled, calcined material using Bayer process production aluminium hydroxide or Aluminium oxide, alkaline residue are then used for polyaluminium sulfate pH adjuster;This method is high alumina coal gangue efficiently using providing one kind New approaches, new technology, each element rate of recovery is high in gangue, and process is generated without new solid waste, will become the following high alumina bastard coal Maximally efficient one of the approach of stone resource utilization.
For the high alumina coal gangue in terms of ash content quality, each quality accounting that forms is Al2O3> 30%, Fe2O3< 15%, CaO < 2%, MgO < 2%.
The above method of the present invention has achieved the purpose that efficient to utilize high alumina coal gangue, the specific steps are as follows:
(1) gangue met the requirements is taken, as its low heat valve >=800cal/kg, then using recirculating fluidized bed recycling heat Amount obtains slag;If its low heat valve calorific value < 800cal/kg, then be used directly, properties of powder performace then with heat recovery with No determination, when recycling heat, properties of powder performace was 80 mesh screen over-size < 10%, when not recycling heat, crossed 120 mesh screen over-sizes < 5%;
(2) in the mass ratio of the industrial sulphuric acid of mass concentration 98% and raw material be 1.1~1.2 ratio, high alumina coal gangue or its Industrial sulphuric acid is added in slag, is reacted at room temperature~50 DEG C, is transferred to after its solidification in vertical acidification kiln, is pressed again simultaneously The ratio that the mass ratio of industrial sulphuric acid and raw material is 0.1~0.2 adds 98% industrial sulphuric acid, 2~3h of acidification reaction time, acidification Kiln entrance heat source temperature is 180~190 DEG C;
(3) after being acidified, acidulants is transferred in the reactive tank with stirring, are 1 by acidulants quality and lysate mass ratio: 2~3 ratio adds lysate, and 1~1.5h of stirring and dissolving at 60~80 DEG C obtains sulfate liquor through filtering, and filter residue is washed It washs to washing lotion pH > 3 and obtains acid sludge;
(4) the part of sulfuric acid salting liquid of step (3) is spray-dried, calcines acquisition aluminium oxide first product, and tail gas recycle sulfuric acid is used for System circulation uses, and aluminium oxide first product further calcines production aluminium oxide using Bayer process production aluminium hydroxide or aluminium hydroxide, It is used after the alkali of recycling is concentrated for system circulation, alkaline residue is then used as the pH regulator of production polymeric aluminum sulfate iron, uses simultaneously In supplement source of iron;Residual sulfuric acid salting liquid is aoxidized, and pH value is adjusted, and produces polymeric aluminum sulfate iron;
(5) acid sludge is calcined through 900~1000 DEG C, must reach the white carbon black product of HG/T3068-2008 standard E class requirement.
Lysate is the first time washing lotion that clear water or step (1) wash filter residue in the step (3).
Sulfate calcination temperature after the step (4) spray drying is 900~1000 DEG C, 2~3h when calcining;Aluminum sulfate Iron polymeric reaction temperature is 60~80 DEG C, and polymerization time is 4~6h, is conventional fabrication process.
The principle of the present invention:
In order to make in gangue acid is molten to dissolve out as far as possible, the removal of impurities of acid sludge Silicon-rich, the quality of gangue or slag and sulfuric acid are realized Than generally requiring to be 1.2~1.4, but it is added at one time sulfuric acid, then will lead to subsequent acidification reaction material transfer difficulty, be acidified kiln Poor air permeability, therefore, the present invention use at room temperature~50 DEG C, pass through reactant such as carbonate, reactivity easy in gangue High part kaolin or unformed aluminium oxide and sulfuric acid reaction generate sulfate, and sulfate band under solidification temperature is recycled to crystallize The characteristics of water, realizes that mixture facilitates material in acidification kiln internal mobility and gas permeability from slurry to solid-state in for 24 hours;In order to mention The dissolution rate of acid-soluble material in high gangue, only solidification is unable to satisfy requirement with acid, and therefore, the present invention takes solidfied material transfer process The mode of middle spray acid supplements residual sulfuric acid, to guarantee that the dosage of acid meets technique requirement.Acidification reaction itself is exothermic reaction, only The progress of reaction can be maintained by suitably supplementing certain heat source, measured, properly increased to control final dissolution acidulants middle reaches from acid Entrance heat source temperature, again in cold conditions solidfied material surface condensation, will then participate in reaction, improve acid after free acid carburation by evaporation Utilization rate.Acidification realizes conversion of the acid-soluble material to sulfate in gangue, and wherein aoxidizes silicic acid obtained by pasc reaction finally Dehydration forms unformed oxidation, can separate in subsequent process in leaching with sulfate, while being acid sludge baked for producing white carbon black It creates conditions.Part acid-soluble material is spray-dried to obtain the mixture based on anhydrous slufuric acid aluminium, and oxygen can be able to after calcining To change the unformed product based on aluminium, sodium metaaluminate is converted into after alkali soluble, i.e., available traditional handicraft kind point-score prepares aluminium hydroxide, Aluminium hydroxide again through calcining can produce aluminium oxide, the insoluble matter during alkali soluble be mainly iron, calcium, magnesium etc. oxide or Alkali is used for the pH adjuster preparation polymeric aluminum sulfate iron of acid-soluble material solution, passes through polymeric aluminum sulfate iron and aluminium hydroxide Or the reasonable arrangement of alumina product yield, the new solid waste generated during utilization of coal gangue utilizes on the one hand can be eliminated, separately On the one hand the iron content in polymeric aluminum sulfate iron also can be improved;Unformed silica (no ash base) content is 96% in acid sludge More than, pass through roasting removal residual carbon and bright lost article, as white carbon black product.
The invention has the following advantages over the prior art:
(1) by gangue curing mode, transfer and acidification reaction operational issue of the peracid cash than lower material are solved;
(2) Valuable Elements From Coal Gangue extracts product setting rationally, and added value is high, and process is generated without new solid waste;
(3) by way of secondary supplement acid, it ensure that acid amount needed for acid-soluble material reaction in gangue, by controlling entrance heat source Temperature reduces acidulants free acid amount;
(4) alkaline residue is used for the pH adjuster of polymeric aluminum sulfate iron preparation, the ingredient in alkaline residue is not only taken full advantage of, also disappears In addition to the problem of environmental pollution of alkaline residue;
(5) gangue valuable element extraction process is simple, technology maturation.
Detailed description of the invention
Fig. 1 is process flow diagram of the invention.
Specific embodiment
Below by embodiment, invention is further described in detail, but protection scope of the present invention be not limited to it is described Content.
Embodiment 1
(1) as shown in Figure 1, coal shale in brick making and ash content analysis the results are shown in Table 1.1, as seen from table, this gangue has more high-incidence Heat will should carry out again the utilization of slag after its heat recovery;
1.1 coal shale in brick making of table and ash content analysis
(2) by gangue crushed after being dried, being ground to 80 mesh screen over-sizes is 9.98%, recycles heat using recirculating fluidized bed Obtain slag;
(3) by the gangue slag of step (2) in the industrial sulphur of the ratio addition mass concentration 98% of sour cash mass ratio 1:1.2 Acid solidifies at 50 DEG C;
(4) ratio for being 0.2 in industrial sulphuric acid and the mass ratio of slag, with spray after the gangue solidifying substance of step (3) is taken out Mist form adds 98% industrial sulphuric acid, is transferred in vertical acidification kiln and carries out acidification reaction, and vertical acidification kiln entrance heating temperature is 180 DEG C, residence time 2.5h;
(5) after being acidified, acidification material is transferred in the reactive tank with stirring, is by acidulants quality and lysate mass ratio The ratio of 1:2 adds clear water, stirs 1.5h at 60 DEG C, and dissolved matter is filtered to obtain sulfate liquor, filter residue with clear water wash to PH > 3, first time washing lotion are used for the lysate of acidulants in next technique, and second of washing lotion is used for one of filter residue in next technique Washing lotion, third time washing lotion then make two washing lotions of filter residue in next technique, and so on, last time washing is clear water;Table 1.2 is Acid sludge chemical component;
The constituent analysis (wt%) of 1.2 acid sludge of table
(6) at the beginning of obtaining aluminium oxide after step (5) part of sulfuric acid salting liquid Direct spraying is dry, calcining (900 DEG C of calcining when 3h) Product, aluminium oxide first product alkali soluble obtain sodium metaaluminate, prepare aluminium hydroxide or aluminium hydroxide through kind of a point-score and further calcine production oxidation Aluminium, alkaline residue are then used as the pH regulator of production polymeric aluminum sulfate iron;Residual sulfuric acid salting liquid is adjusted through hydrogen peroxide oxidation with alkaline residue PH value is 3, and polymeric aluminum sulfate iron is made according to a conventional method under the conditions of 60 DEG C of reaction 6h;
(7) step (5) acid sludge is calcined into obtain white carbon black product, through analyzing, SiO at 900 DEG C2For 97.48wt%, oil factor is 2.5, specific surface area 83m2/g。
Embodiment 2
(1) coal shale in brick making and ash content analysis the results are shown in Table 2.1, and as seen from table, this gangue low heat valve is 820cla/ Kg meets heat recovery requirement, and the utilization of slag will should be carried out again after its heat recovery;
2.1 coal shale in brick making of table and ash content analysis
(2) by gangue crushed after being dried, being ground to 80 mesh screen over-sizes is 6.23%, recycles heat using recirculating fluidized bed Obtain slag;
(3) by the gangue slag of step (2) in the industrial sulphur of the ratio addition mass concentration 98% of sour cash mass ratio 1:1.1 Acid solidifies at normal temperature;
(4) ratio for being 0.1 in industrial sulphuric acid and the mass ratio of slag, with spray after the gangue solidifying substance of step (3) is taken out Mist form adds 98% industrial sulphuric acid, is transferred in vertical acidification kiln and carries out acidification reaction, and vertical acidification kiln entrance heating temperature is 190 DEG C, residence time 3h;
(5) after being acidified, acidification material is transferred in the reactive tank with stirring, is by acidulants quality and lysate mass ratio The first time washing lotion of the ratio addition embodiment 1 of 1:2.5, stirs 1h at 80 DEG C, dissolved matter is filtered to obtain sulfate liquor, filter Slag circulation washing (successively use second of washing lotion of 1 step of embodiment (5) as a washing lotion, third time washing lotion as two washing lotions, clearly Water), washing to pH > 3, first time washing lotion is used for the lysate of acidulants in next technique, and second of washing lotion is used for next technique One washing lotion of middle filter residue, and clear water washing lotion then makees two washing lotions of filter residue in next technique;Table 2.2 is acid sludge chemical component;
The constituent analysis (wt%) of 2.2 acid sludge of table
(6) at the beginning of obtaining aluminium oxide after step (5) part of sulfuric acid salting liquid Direct spraying is dry, calcining (1000 DEG C of calcining when 2h) Product, aluminium oxide first product alkali soluble obtain sodium metaaluminate, prepare aluminium hydroxide or aluminium hydroxide through kind of a point-score and further calcine production oxidation Aluminium, alkaline residue are then used as the pH regulator of production polymeric aluminum sulfate iron;Residual sulfuric acid salting liquid is adjusted through hydrogen peroxide oxidation with alkaline residue PH value is 4, and polymeric aluminum sulfate iron is made according to a conventional method under the conditions of 70 DEG C of reaction 5h;
(7) step (5) acid sludge is calcined into obtain white carbon black product, through analyzing, SiO at 1000 DEG C2For 96.09wt%, oil factor is 2.3, specific surface area 81m2/g。
Embodiment 3
(1) coal shale in brick making and ash content analysis the results are shown in Table 3.1, and as seen from table, this gangue low heat valve is 452cla/ Kg does not have heat recovery requirement, and gangue is dry, broken, grinding directly uses;
3.1 coal shale in brick making of table and ash content analysis
(2) being ground to step (1) gangue and sieving with 100 mesh sieve screen over-size is 4.56%;
(3) by the gangue slag of step (2) in the industrial sulphur of the ratio addition mass concentration 98% of sour cash mass ratio 1:1.2 Acid solidifies at 35 DEG C;
(4) ratio for being 0.15 in industrial sulphuric acid and the mass ratio of slag, after the gangue solidifying substance of step (3) is taken out with Sprayable adds 98% industrial sulphuric acid, is transferred in vertical acidification kiln and carries out acidification reaction, and vertical acidification kiln entrance heating temperature is 185 DEG C, residence time 2.5h;
(5) after being acidified, acidification material is transferred in the reactive tank with stirring, is by acidulants quality and lysate mass ratio The first time washing lotion of the ratio addition embodiment 2 of 1:3, stirs 1.2h at 70 DEG C, dissolved matter is filtered to obtain sulfate liquor, filter Slag circulation washing (successively use (5) second of washing lotion of 2 step of embodiment as a washing lotion, third time washing lotion as two washing lotions, clearly Water), washing to pH > 3, first time washing lotion is used for the lysate of acidulants in next technique, and second of washing lotion is used for next technique One washing lotion of middle filter residue, and clear water washing lotion then makees two washing lotions of filter residue in next technique;Table 3.2 is acid sludge chemical component;
The constituent analysis (wt%) of 3.2 acid sludge of table
(6) aluminium oxide first product is obtained after step (5) part of sulfuric acid salting liquid Direct spraying is dry, calcining (950 DEG C of calcining when 2h), Aluminium oxide first product alkali soluble obtains sodium metaaluminate, prepares aluminium hydroxide or aluminium hydroxide through kind of a point-score and further calcines production aluminium oxide, Alkaline residue is then used as the pH regulator of production polymeric aluminum sulfate iron;Residual sulfuric acid salting liquid adjusts pH through hydrogen peroxide oxidation, with alkaline residue Value is 3, and polymeric aluminum sulfate iron is made according to a conventional method under the conditions of 80 DEG C of reaction 4h;
(7) 1000 DEG C of acid sludge of step (5) are calcined into obtain white carbon black product, through analyzing, SiO2For 97.02wt%, oil factor 2.0, Specific surface area is 75m2/g。
Embodiment 4
(1) coal shale in brick making and ash content analysis the results are shown in Table 4.1, and as seen from table, this gangue low heat valve is 639cla/ Kg does not have heat recovery requirement, and gangue is dry, broken, grinding directly uses;
4.1 coal shale in brick making of table and ash content analysis
(2) being ground to step (1) gangue and sieving with 100 mesh sieve screen over-size is 5.27%;
(3) by the gangue slag of step (2) in the industrial sulphur of the ratio addition mass concentration 98% of sour cash mass ratio 1:1.1 Acid solidifies at 40 DEG C;
(4) ratio for being 0.2 in industrial sulphuric acid and the mass ratio of slag, with spray after the gangue solidifying substance of step (3) is taken out Mist form adds 98% industrial sulphuric acid, is transferred in vertical acidification kiln and carries out acidification reaction, and vertical acidification kiln entrance heating temperature is 180 DEG C, residence time 3h;
(5) after being acidified, acidification material is transferred in the reactive tank with stirring, is by acidulants quality and lysate mass ratio The first time washing lotion of the ratio addition embodiment 3 of 1:2.5, stirs 1h at 75 DEG C, dissolved matter is filtered to obtain sulfate liquor, filter The washing of slag circulation (successively use second of washing lotion in 3 step of embodiment (5) as a washing lotion, third time washing lotion as two washing lotions, Clear water), washing to pH > 3, first time washing lotion is used for the lysate of acidulants in next technique, and second of washing lotion is used for next work A washing lotion of filter residue in skill, and clear water washing lotion then makees two washing lotions of filter residue in next technique;Table 4.2 is acid sludge chemical component;
The constituent analysis (wt%) of 4.2 acid sludge of table
(6) at the beginning of obtaining aluminium oxide after step (5) part of sulfuric acid salting liquid Direct spraying is dry, calcining (1000 DEG C of calcining when 2h) Product, aluminium oxide first product alkali soluble obtain sodium metaaluminate, prepare aluminium hydroxide or aluminium hydroxide through kind of a point-score and further calcine production oxidation Aluminium, alkaline residue are then used as the pH regulator of production polymeric aluminum sulfate iron;Residual sulfuric acid salting liquid is adjusted through hydrogen peroxide oxidation with alkaline residue PH value is 4, and polymeric aluminum sulfate iron is made according to a conventional method under the conditions of 65 DEG C of reaction 5h;
(7) step (5) acid sludge is calcined into obtain white carbon black product, through analyzing, SiO at 900 DEG C2For 97.42wt%, oil factor is 2.4, specific surface area is 81 m2/g。

Claims (8)

1. a kind of method for efficiently utilizing high alumina coal gangue, it is characterised in that: add quality in high alumina coal gangue or its slag The industrial concentrated sulfuric acid of concentration 98% is first solidified, then it is acidified, dissolve out, be filtered, washed, obtain sulfate liquor and acid sludge;Portion Point sulfate liquor is spray-dried, calcining, and aluminium hydroxide is made in Bayer process or aluminium hydroxide further calcine preparation and aoxidized Aluminium, remainder sulfate liquor is for producing polymeric aluminum sulfate iron;Acid sludge produces white carbon black after calcining.
2. the efficient method using high alumina coal gangue according to claim 1, which is characterized in that specific step is as follows:
(1) in the mass ratio of the industrial sulphuric acid of mass concentration 98% and raw material be 1.1~1.2 ratio, high alumina coal gangue or its Industrial sulphuric acid is added in slag, is reacted at room temperature~50 DEG C, is transferred to after its solidification in vertical acidification kiln, is pressed again simultaneously The ratio that the mass ratio of industrial sulphuric acid and raw material is 0.1~0.2 adds 98% industrial sulphuric acid, 2~3h of acidification reaction time, acidification Kiln entrance heat source temperature is 180~190 DEG C;After acidification, acidulants are transferred in the reactive tank with stirring, by acidifying substance Amount adds lysate with the ratio that lysate mass ratio is 1:2~3, and 1~1.5h of stirring and dissolving at 60~80 DEG C is obtained through filtering Sulfate liquor is obtained, residue washing to washing lotion pH > 3 obtains acid sludge;
(2) part of sulfuric acid salting liquid is spray-dried, calcines acquisition aluminium oxide first product, and tail gas recycle Sulphuric acid makes for recycling With aluminium oxide first product further calcines production aluminium oxide using Bayer process production aluminium hydroxide or aluminium hydroxide;Residual sulfuric acid salt Solution is aoxidized, and adjustment pH value is 3-4, produces polymeric aluminum sulfate iron;
(3) acid sludge produces white carbon black after calcining.
3. the efficient method using high alumina coal gangue according to claim 1 or 2, it is characterised in that: work as high alumina coal gangue Low heat valve < 800cal/kg when, do not recycle heat and directly use;When high alumina coal gangue low heat valve >= When 800cal/kg, then slag is obtained using recirculating fluidized bed recycling heat.
4. the efficient method using high alumina coal gangue according to claim 3, it is characterised in that: high alumina coal gangue does not recycle When heat, properties of powder performace was 120 mesh screen over-size < 5%, and properties of powder performace was 80 mesh screen over-size < 10% when recycling heat.
5. the efficient method using high alumina coal gangue according to claim 2, it is characterised in that: lysate in step (1) The first time washing lotion of filter residue is washed for clear water or step (1).
6. the efficient method using high alumina coal gangue according to claim 2, it is characterised in that: step (2) spray drying Sulfate calcination temperature afterwards is 900~1000 DEG C, 2~3h when calcining;Aluminium iron sulfate polymeric reaction temperature is 60~80 DEG C, is gathered The conjunction time is 4~6h.
7. the efficient method using high alumina coal gangue according to claim 1 or 2, it is characterised in that: Bayer process produces hydrogen Alkaline residue in alumina technology is used as the pH regulator of production polymeric aluminum sulfate iron, while for supplementing source of iron.
8. the efficient method using high alumina coal gangue according to claim 1 or 2, it is characterised in that: acid sludge through 900~ 1000 DEG C are calcined to obtain product white carbon black.
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Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109824074A (en) * 2019-02-19 2019-05-31 昆明理工大学 A kind of production method of aluminium oxide
CN109835930A (en) * 2019-02-19 2019-06-04 昆明理工大学 A kind of production method of aluminium oxide
CN112607742A (en) * 2020-12-24 2021-04-06 神华准能资源综合开发有限公司 Method for preparing white carbon black by using high-silicon tailings
CN112915990A (en) * 2021-01-26 2021-06-08 中国矿业大学(北京) Coal gangue in-situ carbon activation material and preparation method and application thereof
CN113336253A (en) * 2021-05-24 2021-09-03 昆明理工大学 Method for extracting aluminum oxide from high-aluminum coal gangue by using high-concentration SO2
CN113413741A (en) * 2021-05-28 2021-09-21 昆明理工大学 Method for applying coal gangue and activated slag thereof to tail gas desulfurization
CN115340424A (en) * 2022-08-15 2022-11-15 昌晖自动化科技(济南)有限公司 Coal gangue magnetized soil conditioner and preparation method thereof
CN116253343A (en) * 2023-05-12 2023-06-13 中科镁基(北京)科技有限公司 Utilization method of black talcum

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1107807A (en) * 1994-12-29 1995-09-06 重庆大学 Process for preparing aluminium hydroxide from coal gangue
CN102515279A (en) * 2011-12-12 2012-06-27 昆明理工大学 Comprehensive extraction method of ferro-silico-aluminum in gangue
CN106477606A (en) * 2016-10-12 2017-03-08 北京矿冶研究总院 Method for extracting aluminum oxide from fly ash based on sulfuric acid curing
CN107021552A (en) * 2016-09-23 2017-08-08 宁夏师范学院 A kind of method that gangue prepares high-performance polysilicate ferric aluminum sulfate

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1107807A (en) * 1994-12-29 1995-09-06 重庆大学 Process for preparing aluminium hydroxide from coal gangue
CN102515279A (en) * 2011-12-12 2012-06-27 昆明理工大学 Comprehensive extraction method of ferro-silico-aluminum in gangue
CN107021552A (en) * 2016-09-23 2017-08-08 宁夏师范学院 A kind of method that gangue prepares high-performance polysilicate ferric aluminum sulfate
CN106477606A (en) * 2016-10-12 2017-03-08 北京矿冶研究总院 Method for extracting aluminum oxide from fly ash based on sulfuric acid curing

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
刘成龙: "煤矸石酸浸提取工艺与机理研究", 《中国优秀硕士学位论文全文数据库 工程科技Ⅰ辑》 *
李来时等: "硫酸浸出法提取氧化铝的热力学讨论", 《轻金属》 *

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109824074A (en) * 2019-02-19 2019-05-31 昆明理工大学 A kind of production method of aluminium oxide
CN109835930A (en) * 2019-02-19 2019-06-04 昆明理工大学 A kind of production method of aluminium oxide
CN112607742A (en) * 2020-12-24 2021-04-06 神华准能资源综合开发有限公司 Method for preparing white carbon black by using high-silicon tailings
CN112915990A (en) * 2021-01-26 2021-06-08 中国矿业大学(北京) Coal gangue in-situ carbon activation material and preparation method and application thereof
CN112915990B (en) * 2021-01-26 2022-02-15 中国矿业大学(北京) Coal gangue in-situ carbon activation material and preparation method and application thereof
CN113336253A (en) * 2021-05-24 2021-09-03 昆明理工大学 Method for extracting aluminum oxide from high-aluminum coal gangue by using high-concentration SO2
CN113413741A (en) * 2021-05-28 2021-09-21 昆明理工大学 Method for applying coal gangue and activated slag thereof to tail gas desulfurization
CN115340424A (en) * 2022-08-15 2022-11-15 昌晖自动化科技(济南)有限公司 Coal gangue magnetized soil conditioner and preparation method thereof
CN116253343A (en) * 2023-05-12 2023-06-13 中科镁基(北京)科技有限公司 Utilization method of black talcum

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