CN105948499A - Method for preparing barium-based glass frit with barium slag - Google Patents

Method for preparing barium-based glass frit with barium slag Download PDF

Info

Publication number
CN105948499A
CN105948499A CN201610278068.5A CN201610278068A CN105948499A CN 105948499 A CN105948499 A CN 105948499A CN 201610278068 A CN201610278068 A CN 201610278068A CN 105948499 A CN105948499 A CN 105948499A
Authority
CN
China
Prior art keywords
barium
barium slag
glass frit
bario
solid
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
CN201610278068.5A
Other languages
Chinese (zh)
Other versions
CN105948499B (en
Inventor
刘湘玉
严家铎
蒋友良
杨星
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Guizhou Red Star Development Big Dragon Meng Ye Co Ltd
Original Assignee
Guizhou Red Star Development Big Dragon Meng Ye Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Guizhou Red Star Development Big Dragon Meng Ye Co Ltd filed Critical Guizhou Red Star Development Big Dragon Meng Ye Co Ltd
Priority to CN201610278068.5A priority Critical patent/CN105948499B/en
Publication of CN105948499A publication Critical patent/CN105948499A/en
Application granted granted Critical
Publication of CN105948499B publication Critical patent/CN105948499B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C03GLASS; MINERAL OR SLAG WOOL
    • C03CCHEMICAL COMPOSITION OF GLASSES, GLAZES OR VITREOUS ENAMELS; SURFACE TREATMENT OF GLASS; SURFACE TREATMENT OF FIBRES OR FILAMENTS MADE FROM GLASS, MINERALS OR SLAGS; JOINING GLASS TO GLASS OR OTHER MATERIALS
    • C03C8/00Enamels; Glazes; Fusion seal compositions being frit compositions having non-frit additions
    • C03C8/02Frit compositions, i.e. in a powdered or comminuted form
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B17/00Sulfur; Compounds thereof
    • C01B17/22Alkali metal sulfides or polysulfides
    • CCHEMISTRY; METALLURGY
    • 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
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
    • C02F1/5245Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents using basic salts, e.g. of aluminium and iron
    • CCHEMISTRY; METALLURGY
    • C03GLASS; MINERAL OR SLAG WOOL
    • C03CCHEMICAL COMPOSITION OF GLASSES, GLAZES OR VITREOUS ENAMELS; SURFACE TREATMENT OF GLASS; SURFACE TREATMENT OF FIBRES OR FILAMENTS MADE FROM GLASS, MINERALS OR SLAGS; JOINING GLASS TO GLASS OR OTHER MATERIALS
    • C03C1/00Ingredients generally applicable to manufacture of glasses, glazes, or vitreous enamels
    • C03C1/002Use of waste materials, e.g. slags

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • General Chemical & Material Sciences (AREA)
  • Materials Engineering (AREA)
  • Geochemistry & Mineralogy (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Hydrology & Water Resources (AREA)
  • Water Supply & Treatment (AREA)
  • Environmental & Geological Engineering (AREA)
  • Glass Compositions (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention provided a method for preparing barium-based glass frit with barium slag. The method comprises the following steps: barium slag is ground, and a barium slag slurry is prepared; the barium slag slurry is subjected to pipeline sulfuric acid leaching; hydrogen sulfide gas produced in the product is absorbed with sodium alkali, such that sodium sulfide is obtained; solid-liquid separation is carried out, and an iron aluminum sulfate water purifying agent is obtained; the solid is washed and dried; the dried solid is added into a glass frit furnace, and is molten in an oxidation atmosphere; the molten glass is subjected to water extraction, such that the barium-based glass frit is obtained. With the method provided by the invention, barium slag utilization rate is improved, and a high-barium glass frit (ceramic glaze material) is obtained. A glass material prepared with the high-barium frit has the advantages of less bubbles, high transparency and bright color, and has functions that cannot be found in common glass.

Description

Utilize the method that barium slag produces bario glass frit
Technical field
The invention belongs to industrial residue administer and field of comprehensive utilization, in particular it relates to utilize barium slag The method producing bario glass frit.
Background technology
Barium slag is the residual solid during barium salt produces, and belongs to the waste residue of industrial discharge, and its chemical composition mainly has two Silicon oxide, ferrum oxide, aluminium oxide, calcium oxide, potassium oxide and the barium compound salt such as barium sulfate and brium carbonate Class.Barium slag muck puts pollution environment, damages health, the water solublity barium in appropriation of land, particularly barium slag, Easily infiltrate into subsoil water, make barium in subsoil water exceed standard, affect the healthy of people.
The current utilization to barium slag is mainly by barium slag brickmaking, this Land use systems value to resource The lowest, and the problem of solubility barium do not obtains basic solution.
Industry Waste barium slag raw material need not expense, but, exist when Industry Waste barium slag is utilized at present Subject matter be the rational problem of feasibility and economic investment of technology.Specifically, the most such as Lower problem:
How technical feasibility sex chromosome mosaicism, such as, will do, use which type of technical matters, the production technology to be No reliably etc..
The terminal of environmental issue, i.e. production process does not produce new three wastes problem.
The sale of the product question of market, i.e. product and price, and the saturation in market.
The reasonability of investment and problem payoff period of investment.
Energy problem, namely production cost problem, this is the core of whole production technology, and only ladder utilizes The energy could reduce cost.
All in all, during barium slag is administered and utilized, the problems referred to above the most do not obtain very well Solution.
Barium can be used for glass fining agent in glass and ceramic product, reduces glass blister, improves glass transparent degree, Make glass color and luster more bright-coloured, and there is the function that simple glass does not has: X-ray-preventing, UV resistance Line, is the requisite resource of safety check, medical examination, nuclear industry and electron trade.In glass ceramics industry In mostly use brium carbonate or barium sulfate, barium hydroxide, barium chloride, the barium salt waited.Due to brium carbonate and essence The barium salt price of Sulphuric acid barium etc. is high, and the production cost made is high.So barium consumption mostly adds in glass production Consumption is little.Glass, ceramic industry no matter select that barium salt but under the conditions of high-temperature fusion formed silicon Hydrochlorate is all to be combined into barium silicate glass body with barytic form and silico-calcium.Its acid group is with the shape of gas Formula is got rid of.How many barium glass and bario glaze determine the price of product with the content of barium.Barium slag due to iron content, Aluminum height can not utilize.Barium slag is a kind of industrial residue.Remove ferrum, the barium slag after aluminum.Become extraordinary glass The raw material of glass ceramic glaze.
Summary of the invention
The technical problem to be solved is for deficiency of the prior art, it is provided that barium slag is entered by one The method that row effectively utilizes, specifically provides a kind of method utilizing barium slag to produce bario glass frit, the party Method comprises the following steps:
(1) grind barium slag, prepare barium slag ore pulp;
(2) barium slag ore pulp prepared by step (1) is carried out pipeline sulfuric acid leaching;
(3) the gas cure hydrogen retrieval in product step (2) obtained utilizes, then solid-liquid separation;
(4) step (3) solid-liquid separation is obtained solid through washing, dry that to obtain solid barium silico-calcium glass former Material;
(5) solid barium silico-calcium frit step (4) obtained is melted in oxidizing atmosphere Glass melts, melted glass melts through water extraction obtain bario glass frit.
The aforesaid method utilizing barium slag to produce bario glass frit, in step (1), is ground to barium slag 100-400 mesh (preferably 200-300 mesh).
The aforesaid method utilizing barium slag to produce bario glass frit, in step (1), consolidating of barium slag ore pulp Liquid mass ratio is 1:1-1:2.5 (preferably 1:1-1:1.25).
The aforesaid method utilizing barium slag to produce bario glass frit, the sulphuric acid used in step (2) Mass concentration is 90%-105%.
The aforesaid method utilizing barium slag to produce bario glass frit, in step (2), barium slag ore pulp is carried out The pH value of pipeline sulfuric acid leaching reaction is 1-4.5 (preferable ph is 2-3).
The aforesaid method utilizing barium slag to produce bario glass frit, in step (2), in leaching process, Pressure limit is 16-0.5kg/cm2, preferably 10-8kg/cm2
The aforesaid method utilizing barium slag to produce bario glass frit, in step (2), barium slag ore pulp is carried out The response time of pipeline sulfuric acid leaching is 5-60 minute (preferably 10-20 minute, more preferably 10 minutes).
The aforesaid method utilizing barium slag to produce bario glass frit, uses the gas of alkali liquor absorption step (2) Body hydrogen sulfide obtains product sodium sulfide.
The aforesaid method utilizing barium slag to produce bario glass frit, makes step (3) solid-liquid separation obtain Liquid carries out purifying hydrolytic-polymeric reaction and obtains bodied ferric sulfate aluminium water purifying agent.
The aforesaid method utilizing barium slag to produce bario glass frit, obtains step (3) solid-liquid separation Water lotion return step (1) after solid is washed is used for modulating barium slag ore pulp.
The aforesaid method utilizing barium slag to produce bario glass frit, the solid barium silico-calcium that step (4) obtains The mass content of the ferrum in frit is less than 0.1%.
The aforesaid method utilizing barium slag to produce bario glass frit, in step (5), melted temperature is 800-1650 DEG C (preferably 800-1200 DEG C).
Compared with prior art, the present invention at least has the advantages that and can improve barium slag utilization rate, Be conducive to making full use of solid waste resource;Make full use of resource, it is achieved recycling economy;By the process to barium slag, Can more effectively utilize resource and protection environment, with the least resource consumption and Environmental costs, it is thus achieved that The biggest economic benefit and social benefit, reach economic development and coordinate mutually with resource, environmental conservation;Become Waste be changed into values, improves ambient level, preserves the ecological environment, it is achieved recycling economy.It addition, the method for the present invention Can obtain high barium silico-calcium glass ceramics raw material, the glass bubble that it is prepared is few, and transparency is high, color and luster Bright-coloured, and there is the function that simple glass does not has, such as X-ray-preventing and anti-ultraviolet, thus It is safety check, medical examination, nuclear industry, electron trade, requisite resource.
Accompanying drawing explanation
Fig. 1 is the process chart of the inventive method.
Detailed description of the invention
In order to be fully understood by the purpose of the present invention, feature and effect, by following detailed description of the invention, to this Invention elaborates.The process of the present invention is in addition to the description below, and remaining all uses the routine of this area Method or apparatus.
Barium slag is the residual solid during barium salt produces, and belongs to the waste residue of industrial discharge, and its chemical composition mainly has two The barium compound salts such as silicon oxide, ferrum oxide, aluminium oxide, calcium oxide, potassium oxide, barium sulfate, brium carbonate. Due to containing free acid, so there being the strongest corrosivity.To soil vegetative cover, water body has the biggest pollution.Deposit Not even a blade of grass grows to put ground.It is difficult to administer to underground water pollution.This industrial residue cannot be administered for a long time, becomes barium The a great problem of salt industry.As long as it is true that within the ferrum in barium slag is reduced to 0.4%, this waste residue I.e. may utilize and become a kind of resource, glass ceramics raw material can be produced or produce barium glass.If ferrum is less than 0.1% Just adapt to and various glass and ceramic products.Glass industry absorption of market is the biggest, except the barium silico-calcium after ferrum The glass bubble done is few, and transparency is high, bright in colour, and has the merit that simple glass does not has Can, X-ray-preventing, the function of anti-ultraviolet, is safety check, medical examination, nuclear industry, electron trade, Requisite resource.Inventor is according to the main component of barium slag, in conjunction with the demand in market, with production process, Terminal does not produce new waste residue and pollutes for standard, it is proposed that solve the economically viable technology of this polluter Scheme.
Below in conjunction with Fig. 1, the method for the present invention is described in detail.
The first step, grinds barium slag.Barium slag is ground to 100-400 mesh (British Standard), it is contemplated that technique Needs and cost, preferably 200-300 mesh.Carry out classification after grinding barium slag, meet above-mentioned granularity requirements Fine slag pass through, thick slag return regrind until meeting above-mentioned granularity requirements.Barium slag after grinding is made into barium slag Ore pulp, in the incipient stage produced, can prepare barium slag ore pulp with water, in process of production, and can be with Water lotion in subsequent step prepares barium slag ore pulp, such that it is able to reduce discharge of wastewater cost-effective, its In, solid-liquid mass ratio 1:1-1:2.5 in ore pulp, preferably 1:1-1:1.25.
Second step, carries out pipeline sulfuric acid leaching to barium slag ore pulp.Barium slag ore pulp flow in pipesization is leached and sets In Bei, and implantation quality concentration is the sulphuric acid of 90%-105%, and in leaching process, pressure limit is 16-0.5 kg/cm2, preferably 10-8kg/cm2, i.e. initial pressure 16kg/cm2, terminal pressure 0.5kg/cm2, preferably Ground, initial pressure 10kg/cm2, terminal pressure 8kg/cm2.Reaction is controlled by ore slurry pump and sulfuric acid pump Pressure.The pH value of reaction liquid is made to control at 1-4.5 by controlling the ratio of barium slag ore pulp and sulphuric acid, It is preferably controlled in 2-3.Response time is 5-60 minute, preferably 10-20 minute, more preferably 10 minutes.
Whole leaching system need not external energy heating, and the reaction of the heat of dilution of sulphuric acid and material generates heat can Meeting technological requirement, so that production cost is the lowest, production efficiency is high.It addition, have employed the height of advanced person Effect pipeline extract technology makes unit ton cost the lowest, and automaticity is high, and yield is big, can be unmanned On duty, reduce evaporating, emitting, dripping or leaking of liquid or gas trouble point, working environment is good.
Sulfuric acid leaching can be converted into soluble barium sulfate solubility barium, and the ferrum oxide in barium slag is anti-with sulphuric acid Should be converted into iron sulfate, partial oxidation aluminum generates aluminum sulfate with sulfuric acid reaction, silicon not with sulfuric acid reaction, calcium with Sulfuric acid reaction generates not capacitive calcium sulfate, such that it is able to obtain aluminum sulfate, ferrous solution, it is achieved ferrum aluminum and barium silicon Calcium extracts the purpose separated.This step relates generally to following chemical reaction:
BaS+H2SO4→BaSO4↓+H2S↑
Fe2O3+3H2SO4→Fe2(SO4)3+3H2O
AI2O3+3H2SO4→AI2(SO4)3+3H2O
CaO+H2SO4→Ca SO4↓+H2O
3rd step, gas-liquid separation.After the reaction of pipeline sulfuric acid leaching terminates, the hydrogen sulfide gas produced is used Soda absorbs and obtains sodium sulfide, and to product solid-liquid separation.
Specifically, after the reaction of pipeline sulfuric acid leaching terminates, first pass through gas-liquid separation surge tank, isolate sulfur Change hydrogen, absorb with sodium hydroxide and obtain sodium sulfide;Slurry fluid enters subsider, subsider top Overflow clear liquid enters hydrolytic-polymeric reaction tank to prepare bodied ferric sulfate aluminium water purifying agent after filtration, purification { Al (OH) nSO4}m{Fe2 (OH) nSO4}m (n≤5, m≤10).
Bodied ferric sulfate aluminium water purifying agent is a high efficiency sewage treating agent the most ripe.Solid barium slag per ton can be given birth to Product meets National Standard of the People's Republic of China " water purification agent bodied ferric sulfate " (GB14591-2006) and gathers Close ferric aluminium sulfate water purification agent 0.5-0.6 ton.
In this step, the produced gas of pipeline sulfuric acid leaching reaction and liquid are obtained for effective profit With, it is achieved thereby that the zero-emission of gas, liquid and solid.
4th step, the solid bottom subsider is washed through drainage and is dried thus obtains solid height barium silico-calcium glass Raw material, the mass content of ferrum therein is less than 0.1%, and water lotion returns the first step and is used for preparing barium slag ore deposit Slurry, such that it is able to realize water circulation use.
5th step, by high barium silico-calcium frit in glass frit stove, melted, preferably in oxidizing atmosphere Melt temperature is 800-1650 DEG C, more preferably 800-1200 DEG C;Carry out water extraction afterwards thus obtain bario glass Glass frit.This bario glass frit can be used for various high-grade glass ceramic glaze.
The method of the present invention relates generally to following equipment:
Pipeline leaching equipment: complete the setting of purpose leached with anticorrosion heat resisting and pressure resisting pipeline surrogate response tank Standby.Using retort to carry out leaching is discontinuous operation, and treating capacity is little, many with workman, and trouble point is many, yield Few, its efficiency is far below pipeline leaching equipment.
Gas-liquid separation surge tank: the mixing mud entrance gas-liquid separation surge tank after pipelineization has leached completes The equipment that gas separates with liquid.
Subsider: complete the liquid-solid mixing mud after gas-liquid separation and enter liquid and solid natural separation equipment, Top is to be that the solid that concentration is high enters filter plant bottom clear liquid.The effect of subsider is to reduce filter plant Workload, clear fluid product can be obtained again.
Hydrolytic polymerization tank: complete through the extracted liquid of filtration, purification be hydrolyzed polymerization equipment, equipment itself Band stirs, can control temperature, anticorrosion, compression resistance.
Glass frit stove: formed by refractory material laying.
Every equipment that disclosure satisfy that above-mentioned functions is used equally in the present invention.
Bario glass frit prepared by the method for the present invention easily stores, and easily packs, and cost of transportation is low, user Use and in producing, there is no the harmful gas erosion to resistance to material, furnace service life long production low cost, good product quality, Constant product quality.
Further illustrate the present invention below by the mode of embodiment, but the most therefore limit the present invention to institute Among the scope of embodiments stated.The experimental technique of unreceipted actual conditions in the following example, according to routine side Method and condition, or select according to catalogue.
Embodiment
Barium slag raw material used in following embodiment is from Beijing Wankun Jiahong Science and Technology Development Co., Ltd., and it is main Composition and weight/mass percentage composition are as follows:
SiO2 Fe2O3 Al2O3 CaO BaSO4
32%-46% 2%-4% 7%-8% 5%-8% 20%-40%
Embodiment 1
(1) use ball mill grinding barium slag to 100 mesh, with water furnishing barium slag ore pulp, wherein, in ore pulp Solid-liquid mass ratio 1:2.5.
(2) input of barium slag ore pulp is leached in pipeline by ore slurry pump, simultaneously sulfuric acid pump by 105% sulfuric acid pump Enter in pipeline, initial pressure 16kg/cm2, terminal pressure 0.5kg/cm2, control the pH value of reaction liquid It is 1,5 minutes response time.After reaction terminates, material enters gas-liquid separation surge tank and carries out gas-liquid separation.
(3) gas separated enters in absorption tower, uses sodium hydroxide to carry out absorbing to prepare sodium sulfide. Mud enters subsider, and the overflow clear liquid on subsider top enters hydrolysis tank with preparation after filtration, purification Bodied ferric sulfate aluminium water purifying agent.
(4) washing the solid bottom subsider through drainage, solid is dried thus is obtained high barium silico-calcium glass Raw material, measures iron content therein afterwards, and water lotion returns step (1) and is used for preparing barium slag ore pulp.
(5) high barium silico-calcium frit enters glass frit stove, melted under oxidizing atmosphere, melt temperature Being 800 DEG C-1200 DEG C, melted glass melts water extracts thus obtains bario glass frit.
Embodiment 2
(1) use ball mill grinding barium slag to 200 mesh, with water furnishing barium slag ore pulp, wherein, in ore pulp Solid-liquid mass ratio 1:1.25.
(2) input of barium slag ore pulp is leached in pipeline by ore slurry pump, and the sulphuric acid of 98% is pumped into by sulfuric acid pump simultaneously In pipeline, initial pressure 10kg/cm2, terminal pressure 8kg/cm2, the pH value controlling reaction liquid is 2, 10 minutes response time.After reaction terminates, material enters gas-liquid separation surge tank and carries out gas-liquid separation.
(3) gas separated enters in absorption tower, uses sodium hydroxide to carry out absorbing to prepare sodium sulfide. Mud enters subsider, and the overflow clear liquid on subsider top enters hydrolysis tank with preparation after filtration, purification Bodied ferric sulfate aluminium water purifying agent.
(4) washing the solid bottom subsider through drainage, solid is dried thus is obtained high barium silico-calcium glass Raw material, measures iron content therein afterwards, and water lotion returns step (1) and is used for preparing barium slag ore pulp.
(5) high barium silico-calcium frit enters glass frit stove, melted under oxidizing atmosphere, melt temperature Being 1200 DEG C-1400 DEG C, melted glass melts water extracts thus obtains bario glass frit.
Embodiment 3
(1) use ball mill grinding barium slag to 300 mesh, with water furnishing barium slag ore pulp, wherein, in ore pulp Solid-liquid mass ratio 1:1.25.
(2) input of barium slag ore pulp is leached in pipeline by ore slurry pump, and the sulphuric acid of 93% is pumped into by sulfuric acid pump simultaneously In pipeline, initial pressure 10kg/cm2, terminal pressure 2kg/cm2, the pH value controlling reaction liquid is 3, 20 minutes response time.After reaction terminates, material enters gas-liquid separation surge tank and carries out gas-liquid separation.
(3) gas separated enters in absorption tower, uses sodium hydroxide to carry out absorbing to prepare sodium sulfide. Mud enters subsider, and the overflow clear liquid on subsider top enters hydrolysis tank with preparation after filtration, purification Bodied ferric sulfate aluminium water purifying agent.
(4) washing the solid bottom subsider through drainage, solid is dried thus is obtained high barium silico-calcium glass Raw material, measures iron content therein afterwards, and water lotion returns step (1) and is used for preparing barium slag ore pulp.
(5) high barium silico-calcium frit enters glass frit stove, melted under oxidizing atmosphere, melt temperature Being 1200 DEG C-1400 DEG C, melted glass melts water extracts thus obtains bario glass frit.
Embodiment 4
(1) use ball mill grinding barium slag to 400 mesh, with water furnishing barium slag ore pulp, wherein, in ore pulp Solid-liquid mass ratio 1:1.
(2) input of barium slag ore pulp is leached in pipeline by ore slurry pump, and the sulphuric acid of 93% is pumped into by sulfuric acid pump simultaneously In pipeline, initial pressure 16kg/cm2, terminal pressure 8kg/cm2, the pH value controlling reaction liquid is 4.5,60 minutes response time.After reaction terminates, material enters gas-liquid separation surge tank and carries out gas-liquid separation.
(3) gas separated enters in absorption tower, uses sodium hydroxide to carry out absorbing to prepare sodium sulfide. Mud enters subsider, and the overflow clear liquid on subsider top enters hydrolysis tank with preparation after filtration, purification Bodied ferric sulfate aluminium water purifying agent.
(4) washing the solid bottom subsider through drainage, solid is dried thus is obtained high barium silico-calcium glass Raw material, measures iron content therein afterwards, and water lotion returns step (1) and is used for preparing barium slag ore pulp.
(5) high barium silico-calcium frit enters glass frit stove, melted under oxidizing atmosphere, melt temperature Being 1500 DEG C-1650 DEG C, melted glass melts water extracts thus obtains bario glass frit.
High barium silico-calcium frit weight of iron assay result is as follows:
Embodiment 1 Embodiment 2 Embodiment 3 Embodiment 4
Less than 0.1% Less than 0.1% Less than 0.1% Less than 0.1%

Claims (12)

1. one kind utilizes the method that barium slag produces bario glass frit, it is characterised in that the method include with Lower step:
(1) grind barium slag, prepare barium slag ore pulp;
(2) barium slag ore pulp prepared by step (1) is carried out pipeline sulfuric acid leaching;
(3) the gas cure hydrogen retrieval in product step (2) obtained utilizes, then solid-liquid separation;
(4) step (3) solid-liquid separation is obtained solid through washing, dry that to obtain solid barium silico-calcium glass former Material;
(5) solid barium silico-calcium frit step (4) obtained is melted in oxidizing atmosphere Glass melts, melted glass melts through water extraction obtain bario glass frit.
The method utilizing barium slag to produce bario glass frit the most according to claim 1, its feature exists In, in step (1), barium slag is ground to 100-400 mesh (preferably 200-300 mesh).
The method utilizing barium slag to produce bario glass frit the most according to claim 1 and 2, it is special Levying and be, in step (1), the solid-liquid mass ratio of barium slag ore pulp is 1:1-1:2.5 (preferably 1:1-1:1.25).
4. according to utilizing, described in any one of claim 1-3, the method that barium slag produces bario glass frit, It is characterized in that, the mass concentration of the sulphuric acid used in step (2) is 90%-105%.
5. according to utilizing, described in any one of claim 1-4, the method that barium slag produces bario glass frit, It is characterized in that, in step (2), it is 1-4.5 that barium slag ore pulp carries out the pH value of pipeline sulfuric acid leaching reaction (preferable ph is 2-3).
6. according to utilizing, described in any one of claim 1-5, the method that barium slag produces bario glass frit, It is characterized in that, in step (2), in leaching process, pressure limit is 16-0.5kg/cm2, preferably 10-8kg/cm2
7. according to utilizing, described in any one of claim 1-6, the method that barium slag produces bario glass frit, It is characterized in that, in step (2), it is 5-60 that barium slag ore pulp carries out the response time of pipeline sulfuric acid leaching Minute (preferably 10-20 minute, more preferably 10 minutes).
8. according to utilizing, described in any one of claim 1-7, the method that barium slag produces bario glass frit, It is characterized in that, use the gas cure hydrogen of alkali liquor absorption step (2) to obtain product sodium sulfide.
9. according to utilizing, described in any one of claim 1-8, the method that barium slag produces bario glass frit, It is characterized in that, the liquid making step (3) solid-liquid separation obtain carries out purifying hydrolytic-polymeric reaction and is gathered Close ferric aluminium sulfate water purification agent.
10. according to utilizing, described in any one of claim 1-9, the method that barium slag produces bario glass frit, It is characterized in that, the water lotion after the solid obtaining step (3) solid-liquid separation is washed returns step (1) it is used for modulating barium slag ore pulp.
11. according to utilizing, described in any one of claim 1-10, the method that barium slag produces bario glass frit, It is characterized in that, the mass content of the ferrum in the solid barium silico-calcium frit that step (4) obtains is less than 0.1%.
12. according to utilizing, described in any one of claim 1-11, the method that barium slag produces bario glass frit, It is characterized in that, in step (5), melted temperature is 800-1650 DEG C (preferably 800-1200 DEG C).
CN201610278068.5A 2016-04-29 2016-04-29 The method that barium base glass frit is produced using barium slag Active CN105948499B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610278068.5A CN105948499B (en) 2016-04-29 2016-04-29 The method that barium base glass frit is produced using barium slag

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610278068.5A CN105948499B (en) 2016-04-29 2016-04-29 The method that barium base glass frit is produced using barium slag

Publications (2)

Publication Number Publication Date
CN105948499A true CN105948499A (en) 2016-09-21
CN105948499B CN105948499B (en) 2018-05-18

Family

ID=56916325

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610278068.5A Active CN105948499B (en) 2016-04-29 2016-04-29 The method that barium base glass frit is produced using barium slag

Country Status (1)

Country Link
CN (1) CN105948499B (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108176700A (en) * 2017-11-08 2018-06-19 贵州昊华工程技术有限公司 A kind of method for innocent treatment of barium slag
CN109265005A (en) * 2018-10-26 2019-01-25 广东能强陶瓷有限公司 A kind of environmental protection sheen Ceramic Tiles and preparation method
CN109650727A (en) * 2018-09-13 2019-04-19 西南科技大学 A kind of method that vulcanized sodium slag prepares cellular glass

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN86108699A (en) * 1986-12-27 1988-04-13 王连弟 The treatment process that contains cyanogen, barium industrial residue
CN102115130A (en) * 2010-12-31 2011-07-06 马艳荣 Method for preparing industrial barium chloride from barium slag
CN105032890A (en) * 2015-07-07 2015-11-11 义马环保电力有限公司 Barium slag processing system and method
CN105329931A (en) * 2015-11-20 2016-02-17 金川集团股份有限公司 Method for treating barium-containing waste residues in nickel chloride production process

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN86108699A (en) * 1986-12-27 1988-04-13 王连弟 The treatment process that contains cyanogen, barium industrial residue
CN102115130A (en) * 2010-12-31 2011-07-06 马艳荣 Method for preparing industrial barium chloride from barium slag
CN105032890A (en) * 2015-07-07 2015-11-11 义马环保电力有限公司 Barium slag processing system and method
CN105329931A (en) * 2015-11-20 2016-02-17 金川集团股份有限公司 Method for treating barium-containing waste residues in nickel chloride production process

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108176700A (en) * 2017-11-08 2018-06-19 贵州昊华工程技术有限公司 A kind of method for innocent treatment of barium slag
CN109650727A (en) * 2018-09-13 2019-04-19 西南科技大学 A kind of method that vulcanized sodium slag prepares cellular glass
CN109650727B (en) * 2018-09-13 2021-09-17 西南科技大学 Method for preparing porous glass from sodium sulfide slag
CN109265005A (en) * 2018-10-26 2019-01-25 广东能强陶瓷有限公司 A kind of environmental protection sheen Ceramic Tiles and preparation method

Also Published As

Publication number Publication date
CN105948499B (en) 2018-05-18

Similar Documents

Publication Publication Date Title
CN102051486B (en) Method for preparing low-phosphorus vanadium liquid by using wastewater subjected to vanadium precipitation
CN101306926B (en) Process for abstracting floating air ball from fly ash or slag
CN110127725B (en) Dealkalization method of Bayer process red mud
CN103663511B (en) HCl treatment coal ash for manufacturing is for the method for aluminum oxide
CN108689671A (en) Manganese in electrolytic manganese residues and ammonium sulfate handle recovery method
CN105948499A (en) Method for preparing barium-based glass frit with barium slag
CN108913907A (en) A method of zinc being recycled from ferrous acid zinc resource using calcification baking-ammonia leaching process
CN104261473B (en) A kind of preparation method of Vanadium Pentoxide in FLAKES
CN106335981B (en) A kind of method of nickel slag and red mud comprehensive utilization
CN109207736A (en) A method of utilizing chromium-contained aluminum mud and red mud production ferrochrome and aluminium oxide
CN104058539B (en) A kind of half fine treatment process based on wastewater from viscose fiber producing
CN109809540B (en) Polysilicate aluminum ferric flocculant and preparation method thereof
CN106629803A (en) Method for producing calcium chloride and polymeric aluminum chloride by utilizing high-calcium fly ash
CN109055737A (en) A kind of method of sulfuric acid leaching lepidolite ore
CN106185953B (en) A kind of large-scale quartz sand pickling impurity removal whitening process
CN104692440A (en) De-silicication purifying method for fluorite for pre-melted slag
CN104711428B (en) Method for preparing and recovering metal in pickling sludge
CN103693830A (en) Process for treating free alkali in red mud by microorganisms
CN104404277A (en) Method for strengthened leaching of rhenium in rhenium-rich slag and rhenium leaching solution
CN204039189U (en) Micro-etched waste liquid and low copper waste water copper recovery system
CN207672103U (en) A kind of device preparing red mud Ti-enriched slag
CN108383142B (en) Method for producing alumina by recycling regenerated aluminum ash
CN105668597B (en) The method of flyash soda acid combined extracting aluminium base product and silica-based products
CN109943715A (en) A kind of lepidolite dump leaching leaching method
CN102241409A (en) Preparation method of cesium carbonate

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant