CN107899596A - A kind of desulfurization denitrification agent and preparation method thereof - Google Patents
A kind of desulfurization denitrification agent and preparation method thereof Download PDFInfo
- Publication number
- CN107899596A CN107899596A CN201711033847.XA CN201711033847A CN107899596A CN 107899596 A CN107899596 A CN 107899596A CN 201711033847 A CN201711033847 A CN 201711033847A CN 107899596 A CN107899596 A CN 107899596A
- Authority
- CN
- China
- Prior art keywords
- slag
- ore
- desulfurization denitrification
- denitrification agent
- phosphorus
- 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.)
- Pending
Links
- 238000006477 desulfuration reaction Methods 0.000 title claims abstract description 31
- 230000023556 desulfurization Effects 0.000 title claims abstract description 31
- 238000002360 preparation method Methods 0.000 title claims abstract description 8
- 239000002893 slag Substances 0.000 claims abstract description 42
- 239000003795 chemical substances by application Substances 0.000 claims abstract description 31
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 claims abstract description 25
- 239000011574 phosphorus Substances 0.000 claims abstract description 25
- 229910052698 phosphorus Inorganic materials 0.000 claims abstract description 25
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 claims abstract description 15
- 239000011701 zinc Substances 0.000 claims abstract description 15
- 229910052725 zinc Inorganic materials 0.000 claims abstract description 15
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims abstract description 14
- 229910052802 copper Inorganic materials 0.000 claims abstract description 14
- 239000010949 copper Substances 0.000 claims abstract description 14
- 229910052761 rare earth metal Inorganic materials 0.000 claims abstract description 14
- 150000002910 rare earth metals Chemical class 0.000 claims abstract description 14
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 claims abstract description 13
- LIKBJVNGSGBSGK-UHFFFAOYSA-N iron(3+);oxygen(2-) Chemical compound [O-2].[O-2].[O-2].[Fe+3].[Fe+3] LIKBJVNGSGBSGK-UHFFFAOYSA-N 0.000 claims abstract description 13
- 229910052748 manganese Inorganic materials 0.000 claims abstract description 13
- 239000011572 manganese Substances 0.000 claims abstract description 13
- 239000000843 powder Substances 0.000 claims abstract description 13
- 239000011148 porous material Substances 0.000 claims abstract description 6
- 238000002156 mixing Methods 0.000 claims description 6
- 239000002994 raw material Substances 0.000 claims description 6
- 239000003546 flue gas Substances 0.000 abstract description 12
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 abstract description 9
- 238000000034 method Methods 0.000 abstract description 8
- 230000008569 process Effects 0.000 abstract description 5
- 239000000779 smoke Substances 0.000 abstract description 5
- 238000004064 recycling Methods 0.000 abstract description 4
- 239000006227 byproduct Substances 0.000 abstract description 3
- 230000007613 environmental effect Effects 0.000 abstract description 3
- 239000007787 solid Substances 0.000 abstract description 3
- 238000004140 cleaning Methods 0.000 abstract 1
- PNEYBMLMFCGWSK-UHFFFAOYSA-N Alumina Chemical compound [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 25
- CPLXHLVBOLITMK-UHFFFAOYSA-N Magnesium oxide Chemical compound [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 description 16
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 12
- DQMUQFUTDWISTM-UHFFFAOYSA-N O.[O-2].[Fe+2].[Fe+2].[O-2] Chemical compound O.[O-2].[Fe+2].[Fe+2].[O-2] DQMUQFUTDWISTM-UHFFFAOYSA-N 0.000 description 11
- XLOMVQKBTHCTTD-UHFFFAOYSA-N Zinc monoxide Chemical compound [Zn]=O XLOMVQKBTHCTTD-UHFFFAOYSA-N 0.000 description 10
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 description 10
- 239000000292 calcium oxide Substances 0.000 description 10
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 10
- 238000005516 engineering process Methods 0.000 description 10
- 239000000395 magnesium oxide Substances 0.000 description 8
- 238000006243 chemical reaction Methods 0.000 description 7
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 description 6
- 230000008859 change Effects 0.000 description 6
- AMWRITDGCCNYAT-UHFFFAOYSA-L hydroxy(oxo)manganese;manganese Chemical compound [Mn].O[Mn]=O.O[Mn]=O AMWRITDGCCNYAT-UHFFFAOYSA-L 0.000 description 6
- 238000009616 inductively coupled plasma Methods 0.000 description 6
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 6
- 239000000377 silicon dioxide Substances 0.000 description 6
- 229910052593 corundum Inorganic materials 0.000 description 5
- 238000001514 detection method Methods 0.000 description 5
- 239000007789 gas Substances 0.000 description 5
- 229910001845 yogo sapphire Inorganic materials 0.000 description 5
- 239000011787 zinc oxide Substances 0.000 description 5
- QPLDLSVMHZLSFG-UHFFFAOYSA-N Copper oxide Chemical compound [Cu]=O QPLDLSVMHZLSFG-UHFFFAOYSA-N 0.000 description 4
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 4
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 4
- QVQLCTNNEUAWMS-UHFFFAOYSA-N barium oxide Inorganic materials [Ba]=O QVQLCTNNEUAWMS-UHFFFAOYSA-N 0.000 description 4
- CSSYLTMKCUORDA-UHFFFAOYSA-N barium(2+);oxygen(2-) Chemical compound [O-2].[Ba+2] CSSYLTMKCUORDA-UHFFFAOYSA-N 0.000 description 4
- NUJOXMJBOLGQSY-UHFFFAOYSA-N manganese dioxide Chemical compound O=[Mn]=O NUJOXMJBOLGQSY-UHFFFAOYSA-N 0.000 description 4
- 239000001301 oxygen Substances 0.000 description 4
- 229910052760 oxygen Inorganic materials 0.000 description 4
- 239000002002 slurry Substances 0.000 description 4
- 239000002910 solid waste Substances 0.000 description 4
- DLYUQMMRRRQYAE-UHFFFAOYSA-N tetraphosphorus decaoxide Chemical compound O1P(O2)(=O)OP3(=O)OP1(=O)OP2(=O)O3 DLYUQMMRRRQYAE-UHFFFAOYSA-N 0.000 description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 4
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 3
- 239000003245 coal Substances 0.000 description 3
- 239000012535 impurity Substances 0.000 description 3
- 239000011777 magnesium Substances 0.000 description 3
- 229910052749 magnesium Inorganic materials 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- 238000005245 sintering Methods 0.000 description 3
- 239000004408 titanium dioxide Substances 0.000 description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- CWYNVVGOOAEACU-UHFFFAOYSA-N Fe2+ Chemical compound [Fe+2] CWYNVVGOOAEACU-UHFFFAOYSA-N 0.000 description 2
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 2
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 2
- 239000003054 catalyst Substances 0.000 description 2
- 239000000919 ceramic Substances 0.000 description 2
- 229960004643 cupric oxide Drugs 0.000 description 2
- 230000003009 desulfurizing effect Effects 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 239000003517 fume Substances 0.000 description 2
- 229910052602 gypsum Inorganic materials 0.000 description 2
- 239000010440 gypsum Substances 0.000 description 2
- BHEPBYXIRTUNPN-UHFFFAOYSA-N hydridophosphorus(.) (triplet) Chemical compound [PH] BHEPBYXIRTUNPN-UHFFFAOYSA-N 0.000 description 2
- 230000006872 improvement Effects 0.000 description 2
- 229910052742 iron Inorganic materials 0.000 description 2
- WPBNNNQJVZRUHP-UHFFFAOYSA-L manganese(2+);methyl n-[[2-(methoxycarbonylcarbamothioylamino)phenyl]carbamothioyl]carbamate;n-[2-(sulfidocarbothioylamino)ethyl]carbamodithioate Chemical compound [Mn+2].[S-]C(=S)NCCNC([S-])=S.COC(=O)NC(=S)NC1=CC=CC=C1NC(=S)NC(=O)OC WPBNNNQJVZRUHP-UHFFFAOYSA-L 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 238000005272 metallurgy Methods 0.000 description 2
- 238000005065 mining Methods 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- FGIUAXJPYTZDNR-UHFFFAOYSA-N potassium nitrate Chemical compound [K+].[O-][N+]([O-])=O FGIUAXJPYTZDNR-UHFFFAOYSA-N 0.000 description 2
- CHWRSCGUEQEHOH-UHFFFAOYSA-N potassium oxide Chemical compound [O-2].[K+].[K+] CHWRSCGUEQEHOH-UHFFFAOYSA-N 0.000 description 2
- 229910001950 potassium oxide Inorganic materials 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- HJTAZXHBEBIQQX-UHFFFAOYSA-N 1,5-bis(chloromethyl)naphthalene Chemical compound C1=CC=C2C(CCl)=CC=CC2=C1CCl HJTAZXHBEBIQQX-UHFFFAOYSA-N 0.000 description 1
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 1
- 238000003916 acid precipitation Methods 0.000 description 1
- 239000004411 aluminium Substances 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- GOLCXWYRSKYTSP-UHFFFAOYSA-N arsenic trioxide Inorganic materials O1[As]2O[As]1O2 GOLCXWYRSKYTSP-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000010531 catalytic reduction reaction Methods 0.000 description 1
- 239000003638 chemical reducing agent Substances 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 238000002386 leaching Methods 0.000 description 1
- 229910000464 lead oxide Inorganic materials 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- JKQOBWVOAYFWKG-UHFFFAOYSA-N molybdenum trioxide Chemical compound O=[Mo](=O)=O JKQOBWVOAYFWKG-UHFFFAOYSA-N 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- YEXPOXQUZXUXJW-UHFFFAOYSA-N oxolead Chemical compound [Pb]=O YEXPOXQUZXUXJW-UHFFFAOYSA-N 0.000 description 1
- VDGJOQCBCPGFFD-UHFFFAOYSA-N oxygen(2-) silicon(4+) titanium(4+) Chemical compound [Si+4].[O-2].[O-2].[Ti+4] VDGJOQCBCPGFFD-UHFFFAOYSA-N 0.000 description 1
- 239000011591 potassium Substances 0.000 description 1
- 229910052700 potassium Inorganic materials 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 238000006722 reduction reaction Methods 0.000 description 1
- KKCBUQHMOMHUOY-UHFFFAOYSA-N sodium oxide Chemical compound [O-2].[Na+].[Na+] KKCBUQHMOMHUOY-UHFFFAOYSA-N 0.000 description 1
- 229910001948 sodium oxide Inorganic materials 0.000 description 1
- 238000003900 soil pollution Methods 0.000 description 1
- 239000004575 stone Substances 0.000 description 1
- 230000001360 synchronised effect Effects 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J27/00—Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
- B01J27/14—Phosphorus; Compounds thereof
- B01J27/186—Phosphorus; Compounds thereof with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
- B01J27/187—Phosphorus; Compounds thereof with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium with manganese, technetium or rhenium
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/8637—Simultaneously removing sulfur oxides and nitrogen oxides
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2258/00—Sources of waste gases
- B01D2258/02—Other waste gases
- B01D2258/0283—Flue gases
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Environmental & Geological Engineering (AREA)
- Health & Medical Sciences (AREA)
- Organic Chemistry (AREA)
- Materials Engineering (AREA)
- Biomedical Technology (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Catalysts (AREA)
- Treating Waste Gases (AREA)
Abstract
The present invention discloses a kind of desulfurization denitrification agent and preparation method thereof, belongs to Making Use of Tailings utilization and industrial smoke Treatment process field.Desulfurization denitrification agent of the present invention includes phosphorus ore or phosphorus tailing 5% 45%, Iron-ore Slag 5% 25%, manganese mud 5% 30%, zinc ore slag 5% 35%, Copper Slag 1% 10%, red mud 5% 15%, rare-earth tailing 10% 35%, gangue 1% 10%.The preparation method of desulfurization denitrification agent is that above-mentioned solid by-product is milled to about 200 300 mesh respectively, powder after will be broken is mixed in a certain ratio, 1 3h is calcined under the conditions of 800 DEG C 1200 DEG C be fabricated to porous material using Muffle furnace, it is broken into 80 100 mesh powders again afterwards, becomes new desulfurization denitrification agent.The method of the invention technique is simple, and denitrification efficiency is high, and while industrial flue gas cleaning, slag has also obtained recycling, has significant economic benefit and environmental benefit.
Description
Technical field
The present invention relates to a kind of desulfurization denitrification agent and preparation method thereof, specifically using phosphorous chemical industry, non-ferrous metal metallurgy and adopt
Solid by-product in coal production technology is prepared into desulfurizing industrial fume denitrfying agent, belongs to Making Use of Tailings utilization and industrial smoke
Treatment process field.
Background technology
Industrial smoke is the primary pollution source of atmosphere pollution, and flue gas contains a large amount of sulfide, nitrogen oxides, to human body and life
The toxic effect of state system, while the main reason for still produce acid rain, it is big to there is investment in existing desulphurization denitration technology, running cost
The problems such as with height, pipeline is perishable, and technological process is complicated, and operation operation is numerous and diverse, research desulphurization denitration technology control China big
Gas pollution is of great significance.Especially simultaneous SO_2 and NO removal technology, is more of practical significance.
Mineral Resources in China is enriched, huge number.But in the process of China's mining development, generate and be largely difficult to
The solid waste utilized, such as:Phosphorus ore(Or phosphorus tailing), Iron-ore Slag, manganese mud, zinc ore slag, Copper Slag, rare-earth tailing, bastard coal
Stone.These percentage of industrial solid waste that is comprehensively utilizeds are also relatively low at present, a large amount of to store up not only land occupation resource, also result in serious
Atmosphere pollution, soil pollution and water resource pollution, present environmental risks and human health.These solid waste but have mostly
Available value, is recycling resource.By it, simple processing is used in other pollution controls again, has both realized waste profit
With reduction pollution, also reduces the consumption of resource, the energy, be the important embodiment for implementing the strategy of sustainable development.
The widely used wet process of FGD of flue gas desulfurization and denitrification and selective catalytic reduction at this stage(SCR)It is combined skill
Art, i.e. SO2And NOxHandle respectively.Existing desulphurization denitration technology there are many problems, such as:The equipment of limestone-gypsum method
The problems such as investment is big, and desulphurization cost is high, and a large amount of gypsum of generation are difficult to handle;SCR technology there are catalyst investment is big, flue gas into
The problems such as dividing influences greatly, and operating cost is high, there are reaction temperature is high, reducing agent and flue gas mixability are poor, denitration for SNCR technologies
A series of problems, such as efficiency is low, ammonia escaped quantity is big.Therefore, there are fixed investment height, operation dimension for united desulphurization denitration technology
Protect the problems such as costly, operation is complicated.Using a kind of simultaneous SO_2 and NO removal agent, this technical matters is simple, and investment is less,
Realize SO2And NOXRemoving, and do not change existing industrial equipment, and operating cost is low, denitrification efficiency is high, clearly
Clean environmental protection.
The content of the invention
It is an object of the invention to provide a kind of desulfurization denitrification agent, utilizes phosphorous chemical industry, non-ferrous metal metallurgy(Iron, manganese, zinc,
Copper, aluminium, rare earth etc.)Desulfurizing industrial fume denitrfying agent is prepared into the solid by-product in coal mining production technology, desulfurization is improved and takes off
The efficiency of nitre.The desulfurization denitrification agent is prepared by following raw material, and each raw material and mass percent are:Phosphorus ore or phosphorus tailing
5%-45%, Iron-ore Slag 5%-25%, manganese mud 5%-30%, zinc ore slag 5%-35%, Copper Slag 1%-10%, red mud 5%-15%, rare earth tail
Ore deposit 10%-35%, the sum of gangue 1%-10%, the mass percent of all raw materials are 100%.
The preparation method of desulfurization denitrification agent of the present invention, it is characterised in that:By phosphorus ore or phosphorus tailing, Iron-ore Slag, manganese
Slag, zinc ore slag, Copper Slag, red mud, rare-earth tailing, gangue are milled to 200-300 mesh respectively, and all kinds of miberal powders after crushing are pressed
Certain proportion mixes, and the miberal powder after mixing calcines 1-3h under the conditions of 800 DEG C -1200 DEG C and is made for porous material, is crushed to 80
The mesh of mesh -100, you can obtain novel desulphurization denitrfying agent.
Phosphorus ore of the present invention(Or phosphorus tailing)Main component is:Phosphorus pentoxide 23%-31%, calcium oxide 35%-55%, oxygen
Change magnesium 0.5%-2.0%, di-iron trioxide 0.8%-2.0%, aluminium oxide 1.0%-3.0%, silica 1 2%-30%.
Iron-ore Slag main component of the present invention is:Silica 5.0%-15%, aluminium oxide 2.0%-5.0%, calcium oxide
30%-50%, magnesia 5.0%-12%, ferrous oxide and di-iron trioxide 5.0%-38%.
Manganese mud main component of the present invention is:Manganese dioxide 5.0%-15%, silica 35%-55%, aluminium oxide
8.0%-15%, di-iron trioxide 10%-25%, calcium oxide 5.0%-15%, titanium dioxide 0.8%-2%, magnesia 2.0%-6.0%, oxygen
Change potassium 0.3%-2.0%.
Zinc ore slag main component of the present invention is:Lead oxide 8.0%-20%, zinc oxide 40%-70%, arsenic trioxide
0.5%-1.2%, cupric oxide 0.1%-1.1%, di-iron trioxide 1.0%-5.0%.
Copper Slag main component of the present invention is:Cupric oxide 0.2%-1.0%, zinc oxide 1.0%-5.0%, di-iron trioxide
25%-40%, calcium oxide 1.0%-15%, magnesia 1.0%-10%, aluminium oxide 2.0%-15%, silica 25%-45%.
Red mud main component of the present invention is:Silica 3%-23%, calcium oxide 2%-49%, di-iron trioxide 7%-
60%th, alundum (Al2O3) 5%-20%, magnesia 0%-1.6%, sodium oxide molybdena 2%-10%, potassium oxide 0%-0.7%, titanium dioxide 2%-
7.7%。
Rare-earth tailing main component of the present invention is:Calcium oxide 22%-30%, di-iron trioxide 8.0%-15%, titanium dioxide
Silicon 7.0%-15%, magnesia 3.0%-10%, barium monoxide 3.0%-8.0%, manganese dioxide 1.0%-4.0%, aluminium oxide 1.0%-5.0%.
Gangue main component of the present invention is:Alundum (Al2O3) 20%-30%, di-iron trioxide 1.8%-3%, calcium oxide
0.1%-1.5%, magnesia 0.3%-1.2%, titanium dioxide 0.5%-1.0%, potassium oxide 2.0%-4.0%, silica 50%-55%.
Beneficial effects of the present invention:
(1)The utilization rate of industrial solid wastes is fully improved, realizes the recycling of resource, the present invention these raw materials mixing used
After sintering, certain change can occur for its structure, can produce the effect of similar catalyst, its desulfurization degree is 95%-98%, denitration rate
For 90%-93%, duration extension 20h-50h;It can meet requirement of the industry to desulphurization denitration, and desulphurization denitration rate at the same time
Height, duration length, meanwhile, the leaching rate of manganese, magnesium, zinc in ore pulp is high, is conducive to the recycling of resource.
(2)The SO in industrial smoke is removed at the same time2And nitrogen oxides, realize synchronized desulfuring and denitrifying, reduce atmosphere pollution.
(3)Preparation method is simple and practicable, and desulfurization off sulfide effect is good.
Embodiment
The present invention is illustrated in detail with reference to embodiment, embodiment is only the preferred real-time of this invention
Mode, is not the restriction of the present invention.
Embodiment 1
Desulfurization denitrification agent described in the present embodiment by phosphorus ore 30%, Iron-ore Slag 10%, manganese mud 20%, zinc ore slag 10%, Copper Slag 5%,
Red mud 5%, rare-earth tailing 15%, gangue 5% form;By ICP(Inductively-coupled plasma spectrometer)Detection obtains desulfurization and takes off
The main component of nitre agent is calcium oxide 29.65%, di-iron trioxide 12.28%, phosphorus pentoxide 13.45%, zinc oxide 7.32%, oxygen
Change magnesium 5.6%, barium monoxide 0.52%, manganese oxide 7.65%, alundum (Al2O3) 8.21%, other impurity components 15.32%.
Phosphorus ore or phosphorus tailing, Iron-ore Slag, manganese mud, zinc ore slag, Copper Slag, red mud, rare-earth tailing, gangue are ground respectively
To 200 mesh, all kinds of miberal powders after crushing mix by a certain percentage, and the miberal powder after mixing is calcined 2h under the conditions of 100 DEG C and is made
For porous material, 80 mesh are crushed to, you can obtain novel desulphurization denitrfying agent.
This embodiment uses coal-fired flue-gas as processing gas, wherein SO2Concentration is 3000mg/m3, NOxConcentration is
1000mg/m3, it is 1.5 that desulfurization denitrification agent powder, which is pressed with the mass ratio of water,:1 ratio is configured to slurries, controls its pH in 5-6
Left and right, and squeezed into slurry in reactor with centrifugal pump, industrial smoke is continuously passed through, air velocity control is left for 3.5L/min
The right side, the control of reactor interior reaction temperature is at 50 DEG C, successive reaction 5h;After being handled by desulphurization denitration, SO in exiting flue gas2It is dense
Degree is about 45mg/m3, desulfurization degree arrival 98.5%;NOxConcentration is 55mg/m3, denitration efficiency reaches 94.5%.
Embodiment 2
Desulfurization denitrification agent described in the present embodiment is by phosphorus tailing 23%, Iron-ore Slag 13%, manganese mud 13%, zinc ore slag 16%, Copper Slag
10%th, red mud 8%, rare-earth tailing 11%, gangue 6% form.Through ICP(Inductively-coupled plasma spectrometer)Detection detection obtains
The main component of the main component desulfurization denitrification agent of desulfurization denitrification agent is calcium oxide 31.65%, di-iron trioxide 10.73%, five oxygen
Change two phosphorus 8.84%, zinc oxide 6.32%, magnesia 4.3%, barium monoxide 0.98%, manganese oxide 9.33%, alundum (Al2O3) 4.21%, its
Its impurity component 23.64%.
Phosphorus ore or phosphorus tailing, Iron-ore Slag, manganese mud, zinc ore slag, Copper Slag, red mud, rare-earth tailing, gangue are ground respectively
To 300 mesh, all kinds of miberal powders after crushing mix by a certain percentage, and the miberal powder after mixing is calcined 3h under the conditions of 800 DEG C and is made
For porous material, 100 mesh are crushed to, you can obtain novel desulphurization denitrfying agent.
This embodiment uses iron making and sintering flue gas as processing gas, wherein SO2Concentration is 1200mg/m3, NOxConcentration is
600mg/m3;It is 1 that desulfurization denitrification agent particle, which is pressed with the mass ratio of water,:1 ratio is configured to slurries, controls its pH left in 5-6
The right side, and squeezed into ore pulp in reactor with centrifugal pump, sintering flue gas is continuously passed through, air velocity control is left for 3.0L/min
The right side, the control of reactor interior reaction temperature is at 45 DEG C, successive reaction 8h.After being handled by desulphurization denitration, SO in exiting flue gas2It is dense
Degree is about 50mg/m3, desulfurization degree arrival 95.8%;NOxConcentration is 40mg/m3, denitration efficiency reaches 93.3%.
Embodiment 3
Desulfurization denitrification agent described in the present embodiment by phosphorus ore 19%, Iron-ore Slag 14%, manganese mud 8%, zinc ore slag 14%, Copper Slag 9%,
Red mud 9%, rare-earth tailing 18%, gangue 9% form;Through ICP(Inductively-coupled plasma spectrometer)Detection detection obtains desulfurization
The main component of the main component desulfurization denitrification agent of denitrfying agent is calcium oxide 35.46%, the oxidation of di-iron trioxide 10.28%, five two
Phosphorus 5.54%, zinc oxide 8.46%, magnesia 5.7%, barium monoxide 1.88%, manganese oxide 12.03%, alundum (Al2O3) 9.97%, it is other
Impurity component 10.68%.
Phosphorus ore or phosphorus tailing, Iron-ore Slag, manganese mud, zinc ore slag, Copper Slag, red mud, rare-earth tailing, gangue are ground respectively
To 300 mesh, all kinds of miberal powders after crushing mix by a certain percentage, and the miberal powder after mixing is calcined 1h under the conditions of 1200 DEG C and is made
For porous material, 100 mesh are crushed to, you can obtain novel desulphurization denitrfying agent.
This embodiment uses ceramics factory's kiln to discharge flue gas as processing gas, wherein SO2Concentration is 800mg/m3, NOxIt is dense
Spend for 500mg/m3, it is 2.0 that desulfurization denitrification agent particle, which is pressed with the mass ratio of water,:1 ratio is configured to slurries, controls its pH to exist
5-6 or so, and squeezed into ore pulp in reactor with centrifugal pump, ceramics factory's kiln gas is continuously passed through, air velocity control is
4.0L/min or so, the control of reactor interior reaction temperature is at 55 DEG C, successive reaction 3h.After being handled by desulphurization denitration, outlet
SO in flue gas2Concentration is about 9mg/m3, desulfurization degree arrival 98.9%; NOxConcentration is 48mg/m3, denitration efficiency reaches 90.4%.
The above is the preferred embodiment of the present invention, for those of ordinary skill in the art, is not being taken off
On the premise of from principle of the present invention, it can also be made improvements according to actual conditions, these improvement also should be regarded as the present invention's
Protection domain.
Claims (2)
1. a kind of desulfurization denitrification agent, it is characterised in that the desulfurization denitrification agent is prepared by following raw material, each raw material and quality
Percentage is:Phosphorus ore or phosphorus tailing 5%-45%, Iron-ore Slag 5%-25%, manganese mud 5%-30%, zinc ore slag 5%-35%, Copper Slag 1%-
10%th, red mud 5%-15%, rare-earth tailing 10%-35%, gangue 1%-10%.
2. the preparation method of the desulfurization denitrification agent described in claim 1, it is characterised in that:By phosphorus ore or phosphorus tailing, Iron-ore Slag, manganese
Slag, zinc ore slag, Copper Slag, red mud, rare-earth tailing, gangue are milled to 200-300 mesh respectively, and all kinds of miberal powders after crushing are pressed
Certain proportion mixes, and the miberal powder after mixing calcines 1-3h under the conditions of 800 DEG C -1200 DEG C and is made for porous material, is crushed to 80
The mesh of mesh -100, you can obtain novel desulphurization denitrfying agent.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201711033847.XA CN107899596A (en) | 2017-10-30 | 2017-10-30 | A kind of desulfurization denitrification agent and preparation method thereof |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201711033847.XA CN107899596A (en) | 2017-10-30 | 2017-10-30 | A kind of desulfurization denitrification agent and preparation method thereof |
Publications (1)
Publication Number | Publication Date |
---|---|
CN107899596A true CN107899596A (en) | 2018-04-13 |
Family
ID=61842871
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201711033847.XA Pending CN107899596A (en) | 2017-10-30 | 2017-10-30 | A kind of desulfurization denitrification agent and preparation method thereof |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN107899596A (en) |
Cited By (16)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109012109A (en) * | 2018-06-26 | 2018-12-18 | 昆明理工大学 | It is a kind of while removing the SO in flue gas2With the method and device of NO |
CN109821412A (en) * | 2019-03-26 | 2019-05-31 | 安徽工业大学 | A kind of composite modified active carbon and preparation method thereof for flue gas desulfurization and denitrification |
CN109847701A (en) * | 2019-04-02 | 2019-06-07 | 安徽工业大学 | A kind of compound modified biomass active carbon and preparation method thereof for flue gas desulfurization and denitrification |
CN109876591A (en) * | 2019-03-26 | 2019-06-14 | 安徽工业大学 | A kind of compound solid waste based biomass active carbon and preparation method thereof for flue gas desulfurization and denitrification |
CN109966853A (en) * | 2019-04-04 | 2019-07-05 | 安徽工业大学 | A kind of compound solid waste matrix activated carbon and preparation method thereof for flue gas desulfurization and denitrification |
CN110975923A (en) * | 2019-11-21 | 2020-04-10 | 太原理工大学 | For catalytic oxidation of NO and SO2Preparation method of composite liquid-phase catalytic oxidant |
CN111454010A (en) * | 2020-04-07 | 2020-07-28 | 中海油天津化工研究设计院有限公司 | Calcium sulfate pyrolysis inhibitor and preparation method thereof |
CN111495164A (en) * | 2020-04-26 | 2020-08-07 | 昆明理工大学 | Method and device for desulfurization and denitrification of flue gas by combination of yellow phosphorus excitation and ozone production with ore pulp |
CN112337426A (en) * | 2020-06-05 | 2021-02-09 | 河南众仕联环境工程有限公司 | Adsorbent capable of being used for low-temperature dry desulfurization and denitrification in steel mill and preparation method thereof |
CN112495446A (en) * | 2020-12-17 | 2021-03-16 | 南京永能新材料有限公司 | Cement denitration catalyst and preparation method and application thereof |
CN113041838A (en) * | 2021-05-06 | 2021-06-29 | 昆明理工大学 | Method for cooperatively removing low-concentration sulfur dioxide and mercury in smelting flue gas |
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 |
CN114534467A (en) * | 2022-03-25 | 2022-05-27 | 昆明理工大学 | Flue gas treatment process and system for synergistic desulfurization, denitrification and demercuration |
CN116099351A (en) * | 2022-12-29 | 2023-05-12 | 杭州尚善若水环保科技有限公司 | Desulfurization agent and desulfurization method for garbage incineration flue gas treatment |
CN116272334A (en) * | 2022-12-26 | 2023-06-23 | 杭州尚善若水环保科技有限公司 | Coupling desulfurization and denitrification medicament, preparation method and use method thereof |
CN117205735A (en) * | 2023-11-09 | 2023-12-12 | 北京中科润宇环保科技股份有限公司 | Deacidifying agent for purifying waste incineration flue gas |
Citations (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1555906A (en) * | 2003-12-31 | 2004-12-22 | 卢伟林 | Composite desulfur agent and its manufacturing method and application |
CN1899668A (en) * | 2006-06-30 | 2007-01-24 | 昆明理工大学 | Phosphate rock slurry catalytically oxidaizing process for removing low concentration SO2 |
CN101279197A (en) * | 2008-05-23 | 2008-10-08 | 张宏 | Red mud-active carbon compound flue gas circulation and regeneration system for desulfuration and denitration |
CN103521164A (en) * | 2013-10-18 | 2014-01-22 | 东南大学 | Flue gas demercuration, desulfurization and denitration adsorbent and preparation method thereof |
CN105056747A (en) * | 2015-08-18 | 2015-11-18 | 昆明尔康科技有限公司 | Process and device for removing SO2 from exhaust gas generated by sulfuric acid production in phosphate chemical enterprise |
CN105289267A (en) * | 2015-11-23 | 2016-02-03 | 内蒙古科技大学 | Desulfurization denitration agent for fire coal and preparation method thereof |
CN106914125A (en) * | 2017-05-17 | 2017-07-04 | 莱芜市泰钢工程设计研究有限公司 | Flue gas passes through grinding slag dust-removal and desulfurizing method of denitration and system equipment |
CN107213774A (en) * | 2017-05-15 | 2017-09-29 | 昆明理工大学 | A kind of flue gas desulfurization and resource utilization method based on smelting mine tailings |
-
2017
- 2017-10-30 CN CN201711033847.XA patent/CN107899596A/en active Pending
Patent Citations (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1555906A (en) * | 2003-12-31 | 2004-12-22 | 卢伟林 | Composite desulfur agent and its manufacturing method and application |
CN1899668A (en) * | 2006-06-30 | 2007-01-24 | 昆明理工大学 | Phosphate rock slurry catalytically oxidaizing process for removing low concentration SO2 |
CN101279197A (en) * | 2008-05-23 | 2008-10-08 | 张宏 | Red mud-active carbon compound flue gas circulation and regeneration system for desulfuration and denitration |
CN103521164A (en) * | 2013-10-18 | 2014-01-22 | 东南大学 | Flue gas demercuration, desulfurization and denitration adsorbent and preparation method thereof |
CN105056747A (en) * | 2015-08-18 | 2015-11-18 | 昆明尔康科技有限公司 | Process and device for removing SO2 from exhaust gas generated by sulfuric acid production in phosphate chemical enterprise |
CN105289267A (en) * | 2015-11-23 | 2016-02-03 | 内蒙古科技大学 | Desulfurization denitration agent for fire coal and preparation method thereof |
CN107213774A (en) * | 2017-05-15 | 2017-09-29 | 昆明理工大学 | A kind of flue gas desulfurization and resource utilization method based on smelting mine tailings |
CN106914125A (en) * | 2017-05-17 | 2017-07-04 | 莱芜市泰钢工程设计研究有限公司 | Flue gas passes through grinding slag dust-removal and desulfurizing method of denitration and system equipment |
Non-Patent Citations (1)
Title |
---|
谌伦建 等: "《工业型煤技术》", 30 September 2012, 煤炭工业出版社 * |
Cited By (18)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109012109A (en) * | 2018-06-26 | 2018-12-18 | 昆明理工大学 | It is a kind of while removing the SO in flue gas2With the method and device of NO |
CN109821412A (en) * | 2019-03-26 | 2019-05-31 | 安徽工业大学 | A kind of composite modified active carbon and preparation method thereof for flue gas desulfurization and denitrification |
CN109876591A (en) * | 2019-03-26 | 2019-06-14 | 安徽工业大学 | A kind of compound solid waste based biomass active carbon and preparation method thereof for flue gas desulfurization and denitrification |
CN109847701A (en) * | 2019-04-02 | 2019-06-07 | 安徽工业大学 | A kind of compound modified biomass active carbon and preparation method thereof for flue gas desulfurization and denitrification |
CN109966853A (en) * | 2019-04-04 | 2019-07-05 | 安徽工业大学 | A kind of compound solid waste matrix activated carbon and preparation method thereof for flue gas desulfurization and denitrification |
CN110975923A (en) * | 2019-11-21 | 2020-04-10 | 太原理工大学 | For catalytic oxidation of NO and SO2Preparation method of composite liquid-phase catalytic oxidant |
CN111454010A (en) * | 2020-04-07 | 2020-07-28 | 中海油天津化工研究设计院有限公司 | Calcium sulfate pyrolysis inhibitor and preparation method thereof |
CN111495164A (en) * | 2020-04-26 | 2020-08-07 | 昆明理工大学 | Method and device for desulfurization and denitrification of flue gas by combination of yellow phosphorus excitation and ozone production with ore pulp |
CN112337426A (en) * | 2020-06-05 | 2021-02-09 | 河南众仕联环境工程有限公司 | Adsorbent capable of being used for low-temperature dry desulfurization and denitrification in steel mill and preparation method thereof |
CN112495446A (en) * | 2020-12-17 | 2021-03-16 | 南京永能新材料有限公司 | Cement denitration catalyst and preparation method and application thereof |
CN113041838A (en) * | 2021-05-06 | 2021-06-29 | 昆明理工大学 | Method for cooperatively removing low-concentration sulfur dioxide and mercury in smelting flue gas |
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 |
CN114534467A (en) * | 2022-03-25 | 2022-05-27 | 昆明理工大学 | Flue gas treatment process and system for synergistic desulfurization, denitrification and demercuration |
CN116272334A (en) * | 2022-12-26 | 2023-06-23 | 杭州尚善若水环保科技有限公司 | Coupling desulfurization and denitrification medicament, preparation method and use method thereof |
CN116272334B (en) * | 2022-12-26 | 2023-08-15 | 杭州尚善若水环保科技有限公司 | Coupling desulfurization and denitrification medicament, preparation method and use method thereof |
CN116099351A (en) * | 2022-12-29 | 2023-05-12 | 杭州尚善若水环保科技有限公司 | Desulfurization agent and desulfurization method for garbage incineration flue gas treatment |
CN117205735A (en) * | 2023-11-09 | 2023-12-12 | 北京中科润宇环保科技股份有限公司 | Deacidifying agent for purifying waste incineration flue gas |
CN117205735B (en) * | 2023-11-09 | 2024-03-05 | 北京中科润宇环保科技股份有限公司 | Deacidifying agent for purifying waste incineration flue gas |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN107899596A (en) | A kind of desulfurization denitrification agent and preparation method thereof | |
AU2016266463B2 (en) | Method for comprehensive recovery of smelting wastewater containing magnesium | |
CN107213774B (en) | Flue gas desulfurization and resource utilization method based on smelting tailing slag | |
CN102534187A (en) | Method for treating pyrite cinder by combining acidic leaching with alkaline dissolving | |
CN103408052B (en) | A kind of decomposition method of phosphogypsum | |
Sun et al. | Sulfur resource recovery based on electrolytic manganese residue calcination and manganese oxide ore desulfurization for the clean production of electrolytic manganese | |
CN106731629A (en) | A kind of method of utilization copper smelting plant mine tailing dreg slurry desulfurization dearsenification mercury | |
CN113337295B (en) | Method for producing soil conditioner by utilizing bulk industrial solid wastes and product | |
CN106756001A (en) | A kind of method of the production electrolytic manganese metal for comprehensively utilizing electrolytic manganese residues | |
CN109626339B (en) | Method for preparing sulfuric acid from gypsum | |
Wu et al. | Red gypsum utilization and acidic wastewater treatment based on metal self-enrichment process | |
CN103627893B (en) | Calcium method dry method and semi-dry process flue gas desulphurization ash is utilized to carry out the method for agglomerate | |
CN103588240A (en) | Green utilization method of waste acid | |
CN104826481A (en) | Combined desulfurization and denitrification method implemented by using metallurgical slags | |
CN110152467B (en) | Flue gas advanced treatment method for synchronous desulfurization and denitrification by absorption method | |
CN113041838A (en) | Method for cooperatively removing low-concentration sulfur dioxide and mercury in smelting flue gas | |
CN103725879A (en) | Method for producing tungsten and tin chemical products through chemical metallurgical separation of tungsten-tin paragenic ore | |
CN112403184B (en) | Method for recovering various sulfur resources by using sintering flue gas | |
CN107398171A (en) | A kind of method that acid gas in flue gas is removed using metal tailings | |
CN111039299B (en) | Method for efficiently recycling lead-zinc tailings | |
CN108939852A (en) | A kind of method that tin smelts the arsenic removal of arsenical fume washing, purifying | |
CN109206028A (en) | A kind of cement rotary kiln efficient sulfur-fixing agent and its application method | |
AU2021104221A4 (en) | Method for improving desulfurization efficiency of electrolytic manganese ore/slag slurry | |
CN108525513B (en) | Removing agent for simultaneous desulfurization and denitrification and preparation method thereof | |
CN103305692B (en) | Zinc sulfide concentrates leaching method |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20180413 |
|
RJ01 | Rejection of invention patent application after publication |