CN107899596A - A kind of desulfurization denitrification agent and preparation method thereof - Google Patents

A kind of desulfurization denitrification agent and preparation method thereof Download PDF

Info

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
Application number
CN201711033847.XA
Other languages
Chinese (zh)
Inventor
张冬冬
吴琼
宁平
张晋鸣
李石雷
李创
王思鼎
李凯
汤立红
孙鑫
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.)
Kunming University of Science and Technology
Original Assignee
Kunming University of Science and Technology
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 Kunming University of Science and Technology filed Critical Kunming University of Science and Technology
Priority to CN201711033847.XA priority Critical patent/CN107899596A/en
Publication of CN107899596A publication Critical patent/CN107899596A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J27/00Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
    • B01J27/14Phosphorus; Compounds thereof
    • B01J27/186Phosphorus; Compounds thereof with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J27/187Phosphorus; Compounds thereof with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium with manganese, technetium or rhenium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/8637Simultaneously removing sulfur oxides and nitrogen oxides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • B01D2258/0283Flue 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

A kind of desulfurization denitrification agent and preparation method thereof
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.
CN201711033847.XA 2017-10-30 2017-10-30 A kind of desulfurization denitrification agent and preparation method thereof Pending CN107899596A (en)

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)

* Cited by examiner, † Cited by third party
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)

* Cited by examiner, † Cited by third party
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

Patent Citations (8)

* Cited by examiner, † Cited by third party
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)

* Cited by examiner, † Cited by third party
Title
谌伦建 等: "《工业型煤技术》", 30 September 2012, 煤炭工业出版社 *

Cited By (18)

* Cited by examiner, † Cited by third party
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