CN102500212A - Method for injecting surface discharge active material to oxidized ammonium sulfite or ammonium nitrite - Google Patents

Method for injecting surface discharge active material to oxidized ammonium sulfite or ammonium nitrite Download PDF

Info

Publication number
CN102500212A
CN102500212A CN2011103154915A CN201110315491A CN102500212A CN 102500212 A CN102500212 A CN 102500212A CN 2011103154915 A CN2011103154915 A CN 2011103154915A CN 201110315491 A CN201110315491 A CN 201110315491A CN 102500212 A CN102500212 A CN 102500212A
Authority
CN
China
Prior art keywords
ammonium
sulfite
nitrite
active material
surface discharge
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
CN2011103154915A
Other languages
Chinese (zh)
Inventor
李�杰
鲁娜
李悦
吴彦
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.)
Dalian University of Technology
Original Assignee
Dalian University of 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 Dalian University of Technology filed Critical Dalian University of Technology
Priority to CN2011103154915A priority Critical patent/CN102500212A/en
Publication of CN102500212A publication Critical patent/CN102500212A/en
Pending legal-status Critical Current

Links

Images

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

Landscapes

  • Treating Waste Gases (AREA)

Abstract

The invention provides a method for injecting a surface discharge active material to oxidized ammonium sulfite or ammonium nitrite. The method for injecting the surface discharge active material to oxidized ammonium sulfite or ammonium nitrite is characterized in that: in a wet desulphurization and denitration process of fire coal or fuel oil, sulfite or nitrite generated by absorbing SO2 or NOx in the gas through aqueous alkali is collected into a reaction tank, a gaseous-phase surface discharge system is placed in the reaction tank of ammonium sulfite or ammonium nitrite, oxygen-contained gas enters one end (called inlet) of the surface discharge system, is changed into active gas containing active materials, such as ozone, atomic oxygen, etc., and then injected to a solution in the reaction tank by a sprayer on the other end (called outlet) of the surface discharge system, the ammonium sulfite or ammonium nitrite in the solution is oxidized to ammonium sulfate or ammonium nitrate by the active materials as raw materials of chemical fertilizers. The method has the characteristics of high oxidation rate and efficiency of the ammonium sulfite or ammonium nitrite, high utilization efficiency of gas and energy saving.

Description

The creeping discharge active material injects the method for oxidation ammonium sulfite or ammonium nilrite
Technical field
The present invention relates to the method that a kind of creeping discharge active material injects oxidation ammonium sulfite or ammonium nilrite, belong to control of coal-fired flue-gas pollutant and chemical industry of chemical fertilizer production field.
Background technology
Produce sulfur dioxide (SO in fossil fuel (like coal and the oil) combustion process 2) and nitrogen oxide acidic gaseous pollutants such as (NOx), cause air environmental pollution, therefore, the coal-fired flue gas desulfurization and denitration technical research receives common concern.At present; The coal-fired flue gas desulfurization and denitration technology mainly is a wet method in the industry; Promptly utilize alkaline matter,, be mixed with the alkali lye absorption liquid like calcium oxide, calcium hydroxide, magnesia, magnesium hydroxide, ammonia (comprising ammoniacal liquor) or NaOH etc.; Absorption liquid fully contacts with flue gas in the absorption tower, alkaline matter in the absorption liquid and SO 2With the NOx reaction, generate sulphite and nitrite and be dissolved in the absorption liquid, through the aeration oxygenation, change sulphite and nitrite into sulfate and nitrate again, reach the purpose of flue gas desulfurization and denitrification.
In addition, in the chemical fertilizer raw material production technology, it is important chemical material production process very that sulfurous acid (or sulphite) and nitrous acid (or nitrite) oxidation are prepared sulfuric acid (or sulfate) and nitric acid (or nitrate).
Yet; In existing wet desulphurization denitration and the chemical industry of chemical fertilizer production technology; Basically be to utilize oxygen and sulfurous acid (or sulphite) and nitrous acid (or nitrite) reaction to generate sulfuric acid (or sulfate) and nitric acid (or nitrate); Technological means is to adopt blower fan that oxygen-containing gas (like air) is blasted the oxidation pond of sulfurous acid (or sulphite) and nitrous acid (or nitrite), has the low and bigger problem of blower fan power consumption of oxygen utilization efficient, and then causes operating cost higher.For this reason, carry out correlation technique research, improved the research work of the oxidation efficiency of sulfurous acid (or sulphite) and nitrous acid (or nitrite).
Documents 1 [Xu Guang etc.; CN1182035C] equipment that utilizes ionizing radiation oxidation ammonium sulfite and documents 2 [Xu Guang etc.; CN1199860C] the method for utilizing ionizing radiation oxidation ammonium sulfite; Be that the droplet that forms the ammonium sulfite salting liquid after gas and the liquid mixing gets into radiation chamber, the oxidized ammonium sulfate that is transformed into of the ammonium sulfite in the solution.Wherein, the ionizing radiation generating means is accelerator or radioactive source, can also be the X-ray generating means, or ultraviolet ray generating apparatus, and the ammonium sulfite solution that is used for the oxidation high concentration obtains the chemical technology field of ammonium sulfate.Its core methed is to utilize the irradiation electron gun to realize the oxidation of ammonium sulfite, has radiation generation technique complicated problems.
Summary of the invention
To the deficiency of prior art, the invention provides the method that a kind of creeping discharge active material injects oxidation ammonium sulfite or ammonium nilrite.
Technical scheme of the present invention is following:
In fire coal or gas from oil burning wet desulphurization denitrating technique, SO in the flue gas 2Or the sulphite that absorb to generate through aqueous slkali of NOx or nitrite be by reaction tank, and gas phase creeping discharge system directly is positioned in the reaction tank of ammonium sulfite or ammonium nilrite; And oxygen-containing gas gets into the creeping discharge system entry; Under the effect of surface discharge plasma, be transformed into the active gases that contains ozone and elemental oxygen isoreactivity material; Shower nozzle through the creeping discharge system outlet is injected in the solution of reaction tank; Active material generates ammonium sulfate or ammonium nitrate with ammonium sulfite in the solution or ammonium nilrite oxidation, is used for the production of chemical fertilizer raw material.
Compare with traditional aeration method, the invention has the beneficial effects as follows sulphite or nitrite-oxidizing speed is fast, oxidation efficiency is high, the gas utilization ratio is high and save energy.
Description of drawings
Fig. 1 is the sketch map that gas phase creeping discharge active material injects oxidation ammonium sulfite or ammonium nilrite method.
Fig. 2 is that 0.2mol/L ammonium sulfite autoxidation is handled and the discharge process effect contrast figure.
Among the figure: 1 reaction tank; 2 creeping discharge systems; 3 oxygen-containing gas; 4 air pumps; 5 inlets; 6 shower nozzles; 7 give the ac high voltage source of creeping discharge system power supply; 8 leads; 9 gas path pipes.
The specific embodiment
A kind of creeping discharge active material of the present invention injects the method for oxidation ammonium sulfite or ammonium nilrite; Be that the creeping discharge system is positioned in the reaction tank of ammonium sulfite or ammonium nilrite; Oxygen-containing gas gets into the inlet of creeping discharge system; Under the surface discharge plasma effect, oxygen-containing gas changes the active gases that contains ozone and elemental oxygen into, gets into the solution of reaction tank from the shower nozzle of creeping discharge system outlet; Ammonium sulfite in reaction tank in active material and the solution or ammonium nilrite reaction transform and generate ammonium sulfate or ammonium nitrate.
Below in conjunction with accompanying drawing and specific embodiment the present invention is described in further detail, the inferior salinity of employing is 0.1mol/L-0.3mol/L.
The creeping discharge system that adopts in the experiment is that internal diameter is 13mm, and external diameter is the quartz glass tube of 16mm; Shower nozzle is the quartz sand head; Air is as oxygen-containing gas, and throughput is 2000mL/min; Reaction tank is high 44mm, and internal diameter is 50mm, the lucite tube of wall thickness 2.9mm.
Fig. 2 is that discharge tube is handled the correlation curve of handling ammonium sulfite with traditional aeration.Wherein, ammonium sulfite solution concentration is that 0.2mol/L, volume are that 400mL, processing time are 25 minutes.Compare with traditional aeration, creeping discharge makes sulfite oxidation generate 1.74 times of ammonium sulfate speed raisings.
In addition, when least concentration 0.1mol/L and upper limit concentration 0.3mol/L, the conversion ratio of discharge process ammonium sulfite all can improve 1.3 times on the basis of traditional aeration.

Claims (2)

1. a creeping discharge active material injects the method for oxidation ammonium sulfite or ammonium nilrite, it is characterized in that, and in fire coal or gas from oil burning wet desulphurization denitrating technique, SO in the flue gas 2Or NOx is collected in reaction tank through sulphite or the nitrite that aqueous slkali absorb to generate, and gas phase creeping discharge system directly is positioned in the reaction tank of ammonium sulfite or ammonium nilrite.
2. a creeping discharge active material injects the method for oxidation ammonium sulfite or ammonium nilrite; Oxygen-containing gas gets into the creeping discharge system; Under the effect of surface discharge plasma; Be transformed into the active gases that contains ozone and elemental oxygen isoreactivity material, be injected in the solution of reaction tank through the shower nozzle of creeping discharge system outlet, active material generates ammonium sulfate or ammonium nitrate with ammonium sulfite in the solution or ammonium nilrite oxidation.
CN2011103154915A 2011-10-17 2011-10-17 Method for injecting surface discharge active material to oxidized ammonium sulfite or ammonium nitrite Pending CN102500212A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2011103154915A CN102500212A (en) 2011-10-17 2011-10-17 Method for injecting surface discharge active material to oxidized ammonium sulfite or ammonium nitrite

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2011103154915A CN102500212A (en) 2011-10-17 2011-10-17 Method for injecting surface discharge active material to oxidized ammonium sulfite or ammonium nitrite

Publications (1)

Publication Number Publication Date
CN102500212A true CN102500212A (en) 2012-06-20

Family

ID=46212379

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2011103154915A Pending CN102500212A (en) 2011-10-17 2011-10-17 Method for injecting surface discharge active material to oxidized ammonium sulfite or ammonium nitrite

Country Status (1)

Country Link
CN (1) CN102500212A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103768902A (en) * 2014-01-27 2014-05-07 武汉凯迪电力环保有限公司 Method and device for oxidizing sulphite grout in wet flue gas desulfurization process
CN115536124A (en) * 2022-08-16 2022-12-30 昆明理工大学 Method for improving quality and efficiency of ammonium sulfate product produced by ammonia-acid flue gas desulfurization wastewater

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1233195A (en) * 1996-10-09 1999-10-27 零排放技术公司 Barrier discharge conversion of SO2 and NOx to acids
CN101434428A (en) * 2008-12-03 2009-05-20 大连理工大学 Liquid electrode surface discharge plasma reactor for water treatment
CN102188883A (en) * 2011-04-12 2011-09-21 王晓晔 Novel smoke purification process and device capable of integrally desulphurizing, denitrifying and removing heavy metals

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1233195A (en) * 1996-10-09 1999-10-27 零排放技术公司 Barrier discharge conversion of SO2 and NOx to acids
CN101434428A (en) * 2008-12-03 2009-05-20 大连理工大学 Liquid electrode surface discharge plasma reactor for water treatment
CN102188883A (en) * 2011-04-12 2011-09-21 王晓晔 Novel smoke purification process and device capable of integrally desulphurizing, denitrifying and removing heavy metals

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
危海涛等: "臭氧对亚硫酸铵的氧化效果研究", 《安徽农业科学》 *
岳朝松等: "沿面放电臭氧发生器电极的研究", 《安全与环境工程》 *

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103768902A (en) * 2014-01-27 2014-05-07 武汉凯迪电力环保有限公司 Method and device for oxidizing sulphite grout in wet flue gas desulfurization process
CN103768902B (en) * 2014-01-27 2016-03-30 武汉凯迪电力环保有限公司 Wet fuel gas desulfurizing technology sulfite salt slurries method for oxidation and equipment thereof
CN115536124A (en) * 2022-08-16 2022-12-30 昆明理工大学 Method for improving quality and efficiency of ammonium sulfate product produced by ammonia-acid flue gas desulfurization wastewater
CN115536124B (en) * 2022-08-16 2024-01-09 昆明理工大学 Quality and efficiency improving method for ammonium sulfate product produced by using flue gas desulfurization wastewater by adopting ammonia-acid method

Similar Documents

Publication Publication Date Title
CN102343212B (en) Denitration process combining co-oxidation of ozone and hydrogen peroxide with wet absorption
CN105854542B (en) A method of purification nitrogen-containing oxide tail gas
CN103463978B (en) Based on the device and method of catalytic oxidation of hydrogen peroxide flue gas and desulfurizing and denitrifying
CN104587809B (en) A kind of desulfurizing and denitrifying process of ozone hydroxyl radical free radical dry-and-wet combined
KR101800517B1 (en) Wet-type Apparatus and Method for Removing Harmful Substance from Exhaust Gas
CN110787606B (en) Denitration and demercuration integrated device and method for sintering flue gas circulating fluidized bed desulfurization
Du et al. Desulfurization and denitrification experiments in SDA system: A new high-efficient semi-dry process by NaClO2
KR20150054140A (en) Apparatus for treating exhaust gas using fine bubble ozone water and method for treating exhaust gas using the same
CN1139422C (en) Wet urea additive process for simultanously desulfurizing and denitrification
Guo et al. Simultaneous removal of SO2 and NOx with ammonia combined with gas-phase oxidation of NO using ozone
CN108176208A (en) A kind of efficient wet denitration agent for coordinating preposition oxidation technology
He et al. Simultaneous absorption of NO and SO 2 by combined urea and Fe II EDTA reaction systems
CN109173718A (en) Calcium method-based combined desulfurization, denitrification and demercuration method and device
CN104258702B (en) A kind of method of desulfurizing and denitrifying flue gas by electron beam and device
CN208626983U (en) A kind of high concentration nitrogen oxide flue gas denitrification system
Li et al. Research and engineering practice of catalytic absorption of NO2 by tetrabutylammonium hydrogen sulfate for simultaneous removal of SO2/NOx
CN102358621A (en) Method for ammonium sulfite or ammonium nitrite oxidation by ozone
CN103611400A (en) Vertical type pneumatic rotary self-excitation waste gas purification apparatus
CN102500212A (en) Method for injecting surface discharge active material to oxidized ammonium sulfite or ammonium nitrite
CN105536466A (en) Device and method for removing various pollutants in flue gas through photoassisted catalytic oxidization
CN205386400U (en) Joint schizolysis of ozone oxidation arouses flue gas desulfurization denitration integrated device
CN111905541A (en) Pre-oxidation-based active coke combined desulfurization and denitrification system and method
CN112121616A (en) Flue gas multi-pollutant purification device for coupling microwave ultraviolet light with hydrogen peroxide
CN204637986U (en) Free radical pre-oxidation is in conjunction with the simultaneous SO_2 and NO removal demercuration system of wet absorption
Jakubiak et al. The effect of ozone feeding mode on the effectiveness of NO oxidation

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C02 Deemed withdrawal of patent application after publication (patent law 2001)
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20120620