CN108744906A - A kind of phosphorus ore slurry wet desulfurization additive - Google Patents

A kind of phosphorus ore slurry wet desulfurization additive Download PDF

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Publication number
CN108744906A
CN108744906A CN201810612132.8A CN201810612132A CN108744906A CN 108744906 A CN108744906 A CN 108744906A CN 201810612132 A CN201810612132 A CN 201810612132A CN 108744906 A CN108744906 A CN 108744906A
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ore pulp
mass percent
nitrate
phosphate ore
phosphorus ore
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张冬冬
李创
宁平
王思鼎
吴琼
张慧芳
李鹏毅
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Kunming University of Science and Technology
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Kunming University of Science and Technology
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    • 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
    • B01D53/46Removing components of defined structure
    • B01D53/48Sulfur compounds
    • B01D53/50Sulfur oxides
    • B01D53/501Sulfur oxides by treating the gases with a solution or a suspension of an alkali or earth-alkali or ammonium compound
    • B01D53/502Sulfur oxides by treating the gases with a solution or a suspension of an alkali or earth-alkali or ammonium compound characterised by a specific solution or suspension
    • 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
    • B01D53/46Removing components of defined structure
    • B01D53/48Sulfur compounds
    • B01D53/50Sulfur oxides
    • B01D53/507Sulfur oxides by treating the gases with other liquids
    • 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
    • B01D53/80Semi-solid phase processes, i.e. by using slurries
    • 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
    • B01D53/8603Removing sulfur compounds
    • B01D53/8609Sulfur oxides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/40Alkaline earth metal or magnesium compounds
    • B01D2251/404Alkaline earth metal or magnesium compounds of calcium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/60Inorganic bases or salts
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/60Inorganic bases or salts
    • B01D2251/602Oxides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/70Organic acids
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/80Organic bases or salts
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/202Alkali metals
    • B01D2255/2027Sodium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/204Alkaline earth metals
    • B01D2255/2045Calcium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/207Transition metals
    • B01D2255/2073Manganese
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/207Transition metals
    • B01D2255/20738Iron
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/207Transition metals
    • B01D2255/20792Zinc
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/70Non-metallic catalysts, additives or dopants
    • B01D2255/707Additives or dopants
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • B01D2258/0283Flue gases

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  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Treating Waste Gases (AREA)

Abstract

The present invention discloses a kind of phosphorus ore slurry wet desulfurization additive, including nitrate, metal oxide, organic acid and salts substances.The pH value that the additive can slow down reaction system declines, and improves the utilization rate of phosphorus ore, increases the stability of desulphurization system, and then improve SO2Removal rate.Within a certain period of time, additive, which is added in reaction system, handles industrial smoke, and after reacting 120min, the desulfuration efficiency of phosphate ore pulp desulphurization system, to improve the utilization rate of phosphorus ore, achievees the purpose that recycling than improving 5-20% under the conditions of not doping.

Description

A kind of phosphorus ore slurry wet desulfurization additive
Technical field
The present invention relates to a kind of phosphorus ore slurry wet desulfurization additives, belong to prevention and control of air pollution and improvement, more particularly to phosphorus Chemical industry flue gases purification field.
Background technology
Phosphate rock resource is widely used in industry, agricultural, medicine and other fields, and social development be unable to do without phosphate rock resource.Therefore, Rational exploitation and utilization phosphate rock resource is of great significance to the sustainable development of phosphorous chemical industry enterprise.China's phosphate rock resource is abundant, phosphorus Contain a large amount of impurity in mine, mainly there is iron, aluminium, magnesium, calcium, silicon, also manganese, vanadium, iodine, potassium, strontium etc..Sulphur dioxide of phosphor chemical industry economy is imitated Benefit is good, but environmental pollution is very important, how effectively clean manufacturing and economic well-being of workers and staff to be combined together, and is phosphorous chemical industry enterprise The very severe problem faced.Currently, administered for sulphur dioxide of phosphor chemical industry flue gas desulfurization, wet process of FGD is and wet using more Method flue gas desulfurization mainly has limestone-gypsum method, sodium alkali, ammonia process, magnesium processes, Dual alkali, phosphorus ore slurry processes etc..In recent years, phosphatization There is relatively advanced enterprise's adaptation to local conditions in industrial and commercial bank's industry, using " the phosphate ore pulp catalytic oxidative desulfurization of the patent No. 200610011003.0 Method described in the method for low-concentration sulfur dioxide " creates or sulfuric acid tail gas purifier has been transformed, obtains good fortune Row effect.
And phosphorus ore slurry wet desulfurization is a kind of more emerging sulfur method, for phosphorous chemical industry enterprise, is had de- The features such as sulfur feedstock is easy to get, the byproduct of desulfurization can recycle, is easy to operate.But there is also some problems, such as phosphorus for this method Mine consumption is big, the not first-class factor of phosphorus ore grade causes desulfuration efficiency fluctuation larger so that desulphurization system is unable to stable operation, adds Some problems existing for acute desulphurization system itself.In recent years, " a kind of Gypsum Wet of the patent No. 201110182586.4 Sulfur-removing additives " prepare sulfur-removing additives using organic acid substance, metal oxide, salts substances etc., which is subtracting The significant effect of few fouling, raising desulfuration efficiency etc..A kind of " the Gypsum Wet of the patent No. 201410112266.5 Flue gas desulfurization additive " is composed of one or more of organic acid, acylate, inorganic metal salt etc., the additive The resistance to mass tranfer of desulfurization slurry solid-liquid interface, the pH value of stably desulphurizing slurries can be effectively reduced, and then improves desulfuration efficiency. The patent No. 201410072548.7 " a kind of Wet Fgd By Limestone With Additives and preparation method thereof ", using adipic acid, lemon Lemon acid sodium, magnesia etc. prepare a kind of sulfur-removing additives, which has significant desulfurization effect to high-sulfur flue-gas, and The utilization rate and desulfuration efficiency that desulfurization slurry can be effectively improved have many advantages, such as to reduce energy consumption, prevention desulphurization system fouling.
In existing phosphate ore pulp desulfurization technology, since the ingredient of phosphorus ore itself is more complex, its property of the phosphorus ore of different sources Also difference, this can cause desulphurization system performance unstable so that phosphorus ore is not fully utilized, and then leads to desulfurization effect It is undesirable.
Invention content
To overcome the shortcomings of the prior art, the present invention to provide one kind and need not be on a large scale transformed equipment, subtracted Few desulphurization reaction period, dosage is small and can improve the phosphorus ore slurry wet desulfurization additive of desulfuration efficiency the long period, to reach Desulfurization effect stablizes preferable purpose.
The technical scheme is that:
A kind of phosphorus ore slurry wet desulfurization additive, including nitrate, metal oxide and organic acid and salts substances, each component Dosage is:The mass percent of nitrate and phosphate ore pulp is 1 ~ 5%, the mass percent of metal oxide and phosphate ore pulp is 0.5 ~ 5%, organic acid and the mass percent of salts substances and phosphate ore pulp are 1 ~ 5%.
The nitrate is at least one of ferric nitrate, calcium nitrate, zinc nitrate.
The metal oxide is at least one of manganese dioxide, di-iron trioxide, zinc oxide.
The organic acid and salts substances are at least one of sodium citrate, citric acid, adipic acid.
Advantages of the present invention is:
(1)The prior art(Additive of the present invention is not added)When pH is below 4, desulfuration efficiency drastically declines, Bu Nengwei Keep steady fixed desulfurization performance, and the pH run in equipment using additive of the present invention is down to 4 and still had below preferable Desulfurization effect;
(2)Nitrate provides metal ion to desulfurization system in the present invention, is easy to the O being passed into an acidic solution2Oxidation, Metal ion again can be SO3 2-It is oxidized to SO4 2-.Metal ion plays good catalysed oxidn to phosphate ore pulp desulfurization, increases Add the stability of desulphurization system, promotes SO2Oxidation, and then improve desulfuration efficiency;
(3)Metal oxide to desulfurization system while providing transition metal ions in the present invention, additionally it is possible to reach very high Valence state from S4+In capture electronics, then generate active middle medium, middle medium promotes catalytic oxidation again, moreover it is possible to which buffering is anti- The pH value of system is answered to decline so that the utilization rate higher of phosphorus ore;
(4)Organic acid and salts substances in the present invention by synergistic effect can effectively reduce in phosphate ore pulp reaction system it is solid- The resistance to mass tranfer at liquid interface improves the reactivity of phosphate ore pulp, promotes the dissolving of phosphate ore pulp, greatly shortens industrial smoke and slurries Time of contact, within a certain period of time, desulfuration efficiency higher;In addition, when sodium citrate, citric acid, adipic acid are used in mixed way, Can form pH buffer systems, the fluctuation of stably desulphurizing system phosphate ore pulp pH value, they between each other can also by act synergistically into One step strengthens phosphate ore pulp desulfurization effect.
Specific implementation mode
In order to more fairly set out the technology contents of the present invention, illustrated herein in conjunction with specific example.But the present invention's Protection domain is without being limited thereto.
Embodiment 1
A kind of phosphorus ore slurry wet desulfurization additive, including ferric nitrate, zinc oxide, di-iron trioxide, sodium citrate and adipic acid, respectively The dosage of component is:The mass percent of ferric nitrate and phosphate ore pulp is 2%, and the mass percent of zinc oxide and phosphate ore pulp is 2%, three The mass percent for aoxidizing two iron and phosphate ore pulp is 2%, and the mass percent of sodium citrate and phosphate ore pulp is 2%, adipic acid and phosphorus The mass percent of ore pulp is 2%.It adds it in phosphate ore pulp and mixes, stir evenly.
Desulfurization system inlet flue gas SO2A concentration of 3000mg/m3, ore pulp solid-to-liquid ratio is 5%, and reaction temperature is 25 DEG C.Actual measurement 120min desulfuration efficiencies averagely improve about 13% up to 95% or more, than not doping desulfuration efficiency.
Embodiment 2
A kind of phosphorus ore slurry wet desulfurization additive, including zinc nitrate, manganese dioxide, di-iron trioxide, zinc oxide, sodium citrate and The dosage of citric acid, each component is:The mass percent of zinc nitrate and phosphate ore pulp is 1%, the quality hundred of manganese dioxide and phosphate ore pulp Divide than being 2%, the mass percent of di-iron trioxide and phosphate ore pulp is 2%, and the mass percent of zinc oxide and phosphate ore pulp is 1%, lemon The mass percent of lemon acid sodium and phosphate ore pulp is 2%, and the mass percent of citric acid and phosphate ore pulp is 1%.Add it to phosphorus ore It mixes, stirs evenly in slurry.
Desulfurization system inlet flue gas SO2A concentration of 3000mg/m3, ore pulp solid-to-liquid ratio is 5%, and reaction temperature is 25 DEG C.Actual measurement 120min desulfuration efficiencies averagely improve about 12% up to 94% or more, than not doping desulfuration efficiency.As pH=2.7, desulfurization effect Rate 78%;Under the conditions of same pH, not doping desulfuration efficiency is 62%.
Embodiment 3
A kind of phosphorus ore slurry wet desulfurization additive, including zinc nitrate, calcium nitrate, manganese dioxide, zinc oxide and sodium citrate, each group Point dosage be:The mass percent of zinc nitrate and phosphate ore pulp is 4%, and the mass percent of calcium nitrate and phosphate ore pulp is 1%, dioxy The mass percent for changing manganese and phosphate ore pulp is 0.5%, and the mass percent of zinc oxide and phosphate ore pulp is 0.5%, sodium citrate and phosphorus The mass percent of ore pulp is 3%.It adds it in phosphate ore pulp and mixes, stir evenly.
Desulfurization system inlet flue gas SO2A concentration of 3000mg/m3, ore pulp solid-to-liquid ratio is 5%, and reaction temperature is 25 DEG C.Actual measurement 120min desulfuration efficiencies averagely improve about 11% up to 92% or more, than not doping desulfuration efficiency.
Embodiment 4
A kind of phosphorus ore slurry wet desulfurization additive, including calcium nitrate, manganese dioxide, di-iron trioxide and adipic acid, each component Dosage is:The mass percent of calcium nitrate and phosphate ore pulp is 3%, and the mass percent of manganese dioxide and phosphate ore pulp is 2%, three oxidations The mass percent of two iron and phosphate ore pulp is 1%, and the mass percent of adipic acid and phosphate ore pulp is 1%.Add it to phosphate ore pulp Middle mixing, stirs evenly.
Desulfurization system inlet flue gas SO2A concentration of 3000mg/m3, ore pulp solid-to-liquid ratio is 5%, and reaction temperature is 25 DEG C.Actual measurement 120min desulfuration efficiencies averagely improve about 14% up to 93% or more, than not doping desulfuration efficiency.
Embodiment 5
A kind of phosphorus ore slurry wet desulfurization additive, including ferric nitrate, zinc nitrate, di-iron trioxide and citric acid, the use of each component Amount is:The mass percent of ferric nitrate and phosphate ore pulp is 2%, and the mass percent of zinc nitrate and phosphate ore pulp is 2%, di-iron trioxide Mass percent with phosphate ore pulp is 5%, and the mass percent of citric acid and phosphate ore pulp is 2%.It adds it in phosphate ore pulp and mixes It closes, stirs evenly.
Desulfurization system inlet flue gas SO2A concentration of 3000mg/m3, ore pulp solid-to-liquid ratio is 5%, and reaction temperature is 25 DEG C.Actual measurement 120min desulfuration efficiencies averagely improve about 15% up to 95% or more, than not doping desulfuration efficiency.
Embodiment 6
A kind of phosphorus ore slurry wet desulfurization additive, including ferric nitrate, calcium nitrate, zinc oxide, sodium citrate, citric acid and oneself two The dosage of acid, each component is:The mass percent of ferric nitrate and phosphate ore pulp is 3%, and the mass percent of calcium nitrate and phosphate ore pulp is 1%, the mass percent of zinc oxide and phosphate ore pulp is 2%, and the mass percent of sodium citrate and phosphate ore pulp is 1%, citric acid and phosphorus The mass percent of ore pulp is 2%, and the mass percent of adipic acid and phosphate ore pulp is 2%.It adds it in phosphate ore pulp and mixes, stir It mixes uniformly.
Desulfurization system inlet flue gas SO2A concentration of 3000mg/m3, ore pulp solid-to-liquid ratio is 5%, and reaction temperature is 25 DEG C.Actual measurement 120min desulfuration efficiencies averagely improve about 17% up to 96% or more, than not doping desulfuration efficiency.
Embodiment 7
A kind of phosphorus ore slurry wet desulfurization additive, including ferric nitrate, calcium nitrate, zinc nitrate, manganese dioxide, citric acid and oneself two The dosage of acid, each component is:The mass percent of ferric nitrate and phosphate ore pulp is 3%, and the mass percent of calcium nitrate and phosphate ore pulp is 1%, the mass percent of zinc nitrate and phosphate ore pulp is 1%, and the mass percent of manganese dioxide and phosphate ore pulp is 0.5%, citric acid with The mass percent of phosphate ore pulp is 2%, and the mass percent of adipic acid and phosphate ore pulp is 2%.It adds it in phosphate ore pulp and mixes, It stirs evenly.
Desulfurization system inlet flue gas SO2A concentration of 3000mg/m3, ore pulp solid-to-liquid ratio is 5%, and reaction temperature is 25 DEG C.Actual measurement 120min desulfuration efficiencies averagely improve about 16% up to 97% or more, than not doping desulfuration efficiency.
It is sub that the foregoing is merely presently preferred embodiments of the present invention, is not intended to limit the invention, all the present invention's Within spirit and principle, any modification, equivalent substitution, improvement and etc. done should be included within the scope of the present invention.

Claims (4)

1. a kind of phosphorus ore slurry wet desulfurization additive, including nitrate, metal oxide and organic acid and salts substances, each component Dosage be:The mass percent of nitrate and phosphate ore pulp is 1 ~ 5%, and the mass percent of metal oxide and phosphate ore pulp is 0.5 ~ 5%, organic acid and the mass percent of salts substances and phosphate ore pulp are 1 ~ 5%.
2. phosphorus ore slurry wet desulfurization additive according to claim 1, which is characterized in that the nitrate includes nitric acid At least one of iron, calcium nitrate, zinc nitrate.
3. phosphorus ore slurry wet desulfurization additive according to claim 1, which is characterized in that the metal oxide includes two At least one of manganese oxide, di-iron trioxide, zinc oxide.
4. phosphorus ore slurry wet desulfurization additive according to claim 1, which is characterized in that the organic acid and salts substances Including at least one of sodium citrate, citric acid, adipic acid.
CN201810612132.8A 2018-06-14 2018-06-14 A kind of phosphorus ore slurry wet desulfurization additive Pending CN108744906A (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110201525A (en) * 2019-06-13 2019-09-06 昆明理工大学 A method of sulfur-containing smoke gas desulfurization is carried out using alkaline scrap material
CN113828140A (en) * 2021-11-10 2021-12-24 昆明理工大学 Strengthening method for wet desulphurization of phosphate slurry

Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2006075840A1 (en) * 2005-01-11 2006-07-20 Korea Institute Of Science And Technology Manganese oxide-titania aerogel catalysts, preparing method of the same, and oxidative destruction of chlorinated aromatic compounds using the same
CN102145252A (en) * 2011-01-31 2011-08-10 浙江润丰能源工程有限公司 Synergist for limestone-gypsum wet flue gas desulfurization
CN102380301A (en) * 2011-08-15 2012-03-21 西安热工研究院有限公司 Limestone-plaster wet method flue gas desulfurization composite synergistic agent
CN103191785A (en) * 2013-03-06 2013-07-10 南京工程学院 Energy-saving and synergizing wet desulfurization catalyst and using thereof
CN103949150A (en) * 2014-03-14 2014-07-30 云南磷化集团有限公司 Method using catalytic oxidation of sulfur dioxide tail gas for PH adjustment agent of phosphate rock ore dressing
CN104722205A (en) * 2015-04-09 2015-06-24 南京大学 Limestone-gypsum wet flue gas desulfurization synergist
CN105536493A (en) * 2015-12-28 2016-05-04 昆明理工大学 Method for removing SO2 and NOX from flue gas of coal-fired boiler by virtue of phosphoric ore pulp and phosphorus sludge
CN105983328A (en) * 2015-02-06 2016-10-05 陕西安得科技实业有限公司 Desulphurization synergist used for wet desulphurization
CN106000063A (en) * 2016-05-16 2016-10-12 上海燊安实业有限公司 Limestone-gypsum wet desulfurization enhancer and use method thereof
CN106731637A (en) * 2017-02-15 2017-05-31 鄂尔多斯市瀚博科技有限公司 A kind of compound additive for lime stone gypsum wet flue gas desulfurizing

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2006075840A1 (en) * 2005-01-11 2006-07-20 Korea Institute Of Science And Technology Manganese oxide-titania aerogel catalysts, preparing method of the same, and oxidative destruction of chlorinated aromatic compounds using the same
CN102145252A (en) * 2011-01-31 2011-08-10 浙江润丰能源工程有限公司 Synergist for limestone-gypsum wet flue gas desulfurization
CN102380301A (en) * 2011-08-15 2012-03-21 西安热工研究院有限公司 Limestone-plaster wet method flue gas desulfurization composite synergistic agent
CN103191785A (en) * 2013-03-06 2013-07-10 南京工程学院 Energy-saving and synergizing wet desulfurization catalyst and using thereof
CN103949150A (en) * 2014-03-14 2014-07-30 云南磷化集团有限公司 Method using catalytic oxidation of sulfur dioxide tail gas for PH adjustment agent of phosphate rock ore dressing
CN105983328A (en) * 2015-02-06 2016-10-05 陕西安得科技实业有限公司 Desulphurization synergist used for wet desulphurization
CN104722205A (en) * 2015-04-09 2015-06-24 南京大学 Limestone-gypsum wet flue gas desulfurization synergist
CN105536493A (en) * 2015-12-28 2016-05-04 昆明理工大学 Method for removing SO2 and NOX from flue gas of coal-fired boiler by virtue of phosphoric ore pulp and phosphorus sludge
CN106000063A (en) * 2016-05-16 2016-10-12 上海燊安实业有限公司 Limestone-gypsum wet desulfurization enhancer and use method thereof
CN106731637A (en) * 2017-02-15 2017-05-31 鄂尔多斯市瀚博科技有限公司 A kind of compound additive for lime stone gypsum wet flue gas desulfurizing

Non-Patent Citations (8)

* Cited by examiner, † Cited by third party
Title
吴国华等: "添加剂强化石灰/石灰石烟气脱硫过程的应用及研究进展 ", 《环境科学动态》 *
孙丽娜等: "常见金属氧化物烟气脱硫研究进展 ", 《化工进展》 *
孟蕾等: "磷矿与石灰双循环脱硫的工艺性能 ", 《环境科学学报》 *
宁平: "《工业废气液相催化氧化净化技术》", 31 May 2012, 中国环境科学出版社 *
王乃光等: "有机酸盐强化石灰石湿法烟气脱硫试验研究 ", 《中国电机工程学报》 *
贾丽娟等: "磷矿浆脱硫新技术及工业应用 ", 《磷肥与复肥》 *
陶雷等: "矿浆烟气脱硫及资源化研究进展 ", 《化工进展》 *
韩玉霞等: "有机酸添加剂强化石灰石湿法烟气脱硫过程的实验研究 ", 《动力工程》 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110201525A (en) * 2019-06-13 2019-09-06 昆明理工大学 A method of sulfur-containing smoke gas desulfurization is carried out using alkaline scrap material
CN113828140A (en) * 2021-11-10 2021-12-24 昆明理工大学 Strengthening method for wet desulphurization of phosphate slurry

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