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CN106582277B - A kind of denitrating system and its method using catalyzing hydrogen peroxide - Google Patents

A kind of denitrating system and its method using catalyzing hydrogen peroxide Download PDF

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CN106582277B
CN106582277B CN201611229271.XA CN201611229271A CN106582277B CN 106582277 B CN106582277 B CN 106582277B CN 201611229271 A CN201611229271 A CN 201611229271A CN 106582277 B CN106582277 B CN 106582277B
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hydrogen peroxide
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CN106582277A (en
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赵钦新
陈磊
王云刚
梁志远
徐志文
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Xian Jiaotong University
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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
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/8621Removing nitrogen compounds
    • B01D53/8625Nitrogen oxides
    • B01D53/8631Processes characterised by a specific device
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/10Oxidants
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
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    • B01D2255/207Transition metals
    • B01D2255/20707Titanium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/207Transition metals
    • B01D2255/20738Iron
    • 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

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Abstract

本发明涉及化石燃料燃烧的工业过程氧化催化及环境治理领域,公开了一种采用催化过氧化氢的脱硝系统及其方法,经除尘后的烟气从反应塔顶端进入,通过与汽化后的过氧化氢蒸汽充分混合后经过催化剂层,在波纹板催化剂的作用下完成催化氧化反应,生成的酸性气体经碱液吸收实现氮氧化物的脱除;本发明以锐钛矿形式存在的二氧化钛为基体,氧化铁为助催化剂;本发明所用氧化剂及催化剂具有脱硝效率高、工艺设计合理、环保无毒、造价低、产品质量稳定的优点,同时本发明工艺中的脱硝产物可作为农业化肥或工业原料,不会对环境造成二次污染。

The invention relates to the field of industrial process oxidation catalysis and environmental treatment of fossil fuel combustion, and discloses a denitrification system and method using catalytic hydrogen peroxide. After the hydrogen oxide vapor is fully mixed, it passes through the catalyst layer, and the catalytic oxidation reaction is completed under the action of the corrugated plate catalyst, and the generated acid gas is absorbed by the lye to realize the removal of nitrogen oxides; the present invention uses titanium dioxide in the form of anatase as the substrate , iron oxide is the co-catalyst; the oxidant and catalyst used in the present invention have the advantages of high denitrification efficiency, reasonable process design, environmental protection, non-toxicity, low cost, and stable product quality. , will not cause secondary pollution to the environment.

Description

一种采用催化过氧化氢的脱硝系统及其方法A denitrification system and method using catalytic hydrogen peroxide

技术领域technical field

本发明涉及氮氧化物治理技术领域,具体涉及一种采用催化过氧化氢的脱硝系统及其方法。The invention relates to the technical field of nitrogen oxide treatment, in particular to a denitrification system using catalytic hydrogen peroxide and a method thereof.

背景技术Background technique

化石燃料燃烧是大气中人为排放氮氧化物(NOX)的重要来源,而氮氧化物,如酸雨、光化学烟雾和臭氧枯竭,对居民的正常生活和生产产生了极大的危害。随着NOX污染问题的日趋严重,各国政府加大了对NOX排放的控制力度Fossil fuel combustion is an important source of man-made emissions of nitrogen oxides (NO x ) in the atmosphere, and nitrogen oxides, such as acid rain, photochemical smog and ozone depletion, have caused great harm to the normal life and production of residents. With the increasingly serious problem of NO X pollution, the governments of various countries have increased the control of NO X emissions

最常用的针对化石燃料燃烧的NOX治理方案为选择催化还原(SelectiveCatalytic Reduction,SCR),该方法存在一定的技术缺陷,如温度窗口高(320~400℃),投资运行成本昂贵和氨逃逸等;采用臭氧氧化脱硝克服了SCR脱硝温度较高的弊端,但仍然存在对NOX氧化不完全、反应产物需要进行二次处理的问题;而过氧化氢(H2O2)虽然具有氧化能力,但需要经过催化剂激活才能产生氧化能力更强的自由基。中国专利文献CN103463978A公开了一种使用H2O2催化氧化烟气同时脱硫脱硝的方法,但未考虑强氧化自由基的寿命很短的问题,因此H2O2利用率不高;美国专利US6793903也公开了一种H2O2催化脱硝的工艺流程,选取的催化剂可实现较高的脱硝效率,但未实现NOX的深度氧化,即反应后的亚硝酸根较多。The most commonly used NO X treatment solution for fossil fuel combustion is selective catalytic reduction (Selective Catalytic Reduction, SCR), which has certain technical defects, such as high temperature window (320-400 ° C), high investment and operation costs, and ammonia escape, etc. The use of ozone oxidation denitrification overcomes the disadvantages of high SCR denitrification temperature, but there are still problems of incomplete oxidation of NO X and the need for secondary treatment of the reaction product; and hydrogen peroxide (H 2 O 2 ) has the ability to oxidize, However, it needs to be activated by a catalyst to produce free radicals with stronger oxidizing ability. Chinese patent document CN103463978A discloses a method for simultaneous desulfurization and denitrification of flue gas by using H 2 O 2 catalytic oxidation, but does not consider the problem that the life of strong oxidizing free radicals is very short, so the utilization rate of H 2 O 2 is not high; US Patent US6793903 A H 2 O 2 catalyzed denitration process is also disclosed. The selected catalyst can achieve high denitration efficiency, but the deep oxidation of NO X has not been realized, that is, there are more nitrite radicals after the reaction.

综上所述,当前研发一种脱硝效率高、氧化完全且H2O2利用率高的催化剂及其工艺显得尤为必要。In summary, it is particularly necessary to develop a catalyst and its process with high denitrification efficiency, complete oxidation and high utilization of H 2 O 2 .

发明内容Contents of the invention

为了解决现有技术脱硝过程中H2O2利用率低和氧化不完全的问题,本发明提供了一种采用催化过氧化氢的脱硝系统及其方法,可对除尘后的烟气中的NOX实现深度氧化,处理后的尾气经碱液吸收即可实现NOX的高效脱除。 In order to solve the problems of low utilization rate of H2O2 and incomplete oxidation in the denitrification process of the prior art, the present invention provides a denitrification system and method using catalytic hydrogen peroxide, which can reduce NO in the flue gas after dedusting X realizes deep oxidation, and the treated tail gas can be absorbed by alkali solution to achieve efficient removal of NO X.

为了达到上述目的,本发明所采取的技术方案如下:In order to achieve the above object, the technical scheme that the present invention takes is as follows:

一种采用催化过氧化氢的脱硝系统,包括H2O2存储与输送系统、碱液存储与输送系统、催化剂单元,反应塔6和废液输送单元组成;所述H2O2存储与输运系统包括与反应塔6上部连通的H2O2溶液储存罐2,依次设置在H2O2溶液储存罐2与反应塔6连通管路上的一号流量计3、一号输送泵4和加热装置5,设置在反应塔6内、连通管路末端的格栅7,以及与H2O2溶液储存罐2连接的低温控制系统1,所述碱液存储与输运系统包括与反应塔6下部连通的碱液储蓄罐9,设置在碱液储蓄罐9与反应塔6连通管路上的二号流量计10和二号加压输送泵11,以及设置在反应塔6内、连通管路末端的喷淋装置12;所述催化剂单元为设置在反应塔6内且位于格栅7和喷淋装置12间的布满催化剂的波纹板8;所述废液输送单元为连接在反应塔6底部的3号输送泵13。 A denitrification system using catalytic hydrogen peroxide, comprising H2O2 storage and delivery system, lye storage and delivery system, catalyst unit, reaction tower 6 and waste liquid delivery unit ; the H2O2 storage and delivery system This system comprises the H2O2 solution storage tank 2 that communicates with the upper part of the reaction tower 6 , and the No. 1 flow meter 3, the No. 1 delivery pump 4 and the The heating device 5 is arranged in the reaction tower 6, communicates with the grid 7 at the end of the pipeline, and the low temperature control system 1 connected with the H2O2 solution storage tank 2 , and the lye storage and transportation system includes a reaction tower The lye storage tank 9 connected to the bottom of 6, No. two flow meter 10 and No. two pressurized delivery pump 11 arranged on the connecting pipeline between the lye storage tank 9 and the reaction tower 6, and the connecting pipeline arranged in the reaction tower 6 The spray device 12 at the end; the catalyst unit is a corrugated plate 8 that is arranged in the reaction tower 6 and is located between the grid 7 and the spray device 12; the waste liquid delivery unit is connected to the reaction tower 6 No. 3 transfer pump 13 at the bottom.

所述波纹板8上布满的催化剂为涂覆有负载铁元素的钛基催化剂,其中铁和钛的摩尔比为1~5:100。The catalyst covered on the corrugated plate 8 is a titanium-based catalyst coated with iron elements, wherein the molar ratio of iron to titanium is 1-5:100.

所述H2O2溶液储存罐2、H2O2溶液储存罐2与反应塔6连通管路即H2O2输送管道、格栅7的内表面以及反应塔6内H2O2蒸汽与烟气的混合区域涂覆惰性材料涂层,不会促进分解H2O2和消解羟基自由基。The H 2 O 2 solution storage tank 2, the H 2 O 2 solution storage tank 2 and the reaction tower 6 are connected to the pipeline, that is, the H 2 O 2 delivery pipeline, the inner surface of the grid 7, and the H 2 O 2 steam in the reaction tower 6 The mixing zone with the flue gas is coated with an inert material that does not promote the decomposition of H2O2 and the digestion of hydroxyl radicals.

所述惰性材料为二氧化硅或塑料或氟塑料。The inert material is silicon dioxide or plastic or fluoroplastic.

一种采用催化过氧化氢的脱硝方法,通过低温控制系统1控制H2O2溶液储存罐2中H2O2溶液的温度,H2O2溶液通过一号流量计3计量,由一号输送泵4输送流经加热装置5转变为H2O2蒸汽,H2O2蒸汽经过格栅7与从反应塔6的烟气入口A进入的除尘烟气进行混合为混合气体,混合气体通过涂覆有催化剂的波纹板8进行反应,混合气体中的H2O2蒸汽与烟气中的NOX反应生成包含亚硝酸和硝酸的酸性气体;碱液存储罐9中的碱液经二号流量计10计量,由二号输送泵11输送至喷淋装置12中形成碱性雾化液滴,碱性雾化液滴对酸性气体进行洗涤生成亚硝酸盐和硝酸盐溶液,亚硝酸盐和硝酸盐溶液通过三号输送泵13经出液口B抽离反应塔,然后再经过蒸发结晶转化为固体产物。 A denitrification method using catalytic hydrogen peroxide, the temperature of the H2O2 solution in the H2O2 solution storage tank 2 is controlled by the low temperature control system 1 , the H2O2 solution is measured by the No. 1 flow meter 3, and the No. 1 The delivery pump 4 transports the flow through the heating device 5 and turns it into H2O2 steam. The H2O2 steam passes through the grid 7 and mixes with the dedusted flue gas entering from the flue gas inlet A of the reaction tower 6 to form a mixed gas. The mixed gas passes through the The corrugated plate 8 coated with catalyst reacts, and the H2O2 steam in the mixed gas reacts with the NOx in the flue gas to generate acid gas containing nitrous acid and nitric acid; the lye in the lye storage tank 9 passes through the No. The flow meter 10 measures, and is transported by the second delivery pump 11 to the spray device 12 to form alkaline atomized droplets, which wash the acid gas to generate nitrite and nitrate solutions, nitrite and nitrate The nitrate solution is drawn out of the reaction tower through the liquid outlet B through the No. 3 delivery pump 13, and then converted into a solid product through evaporation and crystallization.

所述低温控制系统1控制的温度为5~10℃。The temperature controlled by the low temperature control system 1 is 5-10°C.

所述H2O2溶液的质量浓度为3~6%,H2O2与所述烟气中NOX的摩尔比为(10~15):1。The mass concentration of the H 2 O 2 solution is 3-6%, and the molar ratio of H 2 O 2 to NO X in the flue gas is (10-15):1.

所述加热装置5的加热温度为140~160℃。The heating temperature of the heating device 5 is 140-160°C.

所述的烟气温度为160-240℃。The flue gas temperature is 160-240°C.

本发明的反应原理如下:The reaction principle of the present invention is as follows:

(1)H2O2分子在二氧化钛表面生成羟基自由基,二氧化钛结构中部分钛原子被铁原子取代后可进一步促进羟基自由基的生成,其反应原理如下:(1) H 2 O 2 molecules generate hydroxyl radicals on the surface of titanium dioxide. Part of the titanium atoms in the titanium dioxide structure are replaced by iron atoms, which can further promote the generation of hydroxyl radicals. The reaction principle is as follows:

(≡Ti(IV)-OH)surf+H2O2→(≡Ti(IV)-OOH)surf+H2O(≡Ti(IV)-OH) surf +H 2 O 2 →(≡Ti(IV)-OOH) surf +H 2 O

H2O2+Fe→Fe-<OH>+·OHH 2 O 2 +Fe→Fe-<OH>+·OH

(2)羟基自由基与一氧化氮反应生成高价NOX,高价NOX(2) Hydroxyl radicals react with nitric oxide to generate high - priced NO X , which dissolves

于水生成亚硝酸和硝酸,其反应原理如下:In water, nitrous acid and nitric acid are generated, and the reaction principle is as follows:

Ti-<O>+2NO→Ti+N2O3 Ti-<O>+2NO→Ti+N 2 O 3

Ti-<O>+NO→Ti+NO2 Ti-<O>+NO→Ti+NO 2

3Ti-<O>+2NO→Ti+N2O5 3Ti-<O>+2NO→Ti+N 2 O 5

N2O3+H2O→2HNO2 N 2 O 3 +H 2 O→2HNO 2

N2O5+H2O→2HNO3 N 2 O 5 +H 2 O→2HNO 3

(3)亚硝酸和硝酸蒸汽经碱液吸收生成亚硝酸盐和硝酸盐(3) Nitrite and nitric acid vapors are absorbed by lye to generate nitrite and nitrate

(碱液以NaOH为例),反应原理如下:(lye is example with NaOH), and reaction principle is as follows:

NaOH+HNO2→NaNO2+H2ONaOH+HNO 2 →NaNO 2 +H 2 O

NaOH+HNO3→NaNO3+H2ONaOH+HNO 3 →NaNO 3 +H 2 O

与现有技术相比,本发明具有以下有益效果:Compared with the prior art, the present invention has the following beneficial effects:

1.充分考虑了强氧化物质寿命短的问题,采取H2O2汽化与烟气混合再经波纹板结构的布置方式,H2O2一经激活产生活性物质及时与NOX进行反应,在保证脱硝效率高达90%的同时极大提高了H2O2的利用率。1. Taking full account of the short life of strong oxidizing substances, the arrangement of H 2 O 2 vaporization and flue gas mixing and corrugated plate structure is adopted. Once H 2 O 2 is activated, active substances will react with NO X in time, ensuring While the denitrification efficiency is as high as 90%, the utilization rate of H 2 O 2 is greatly improved.

2.充分考虑了H2O2自身的物性,在H2O2储存到输送过程中增设了保护措施,如在低温保存和输送管道结构涂覆惰性材料,可最大程度的避免反应前H2O2的自身分解。2. The physical properties of H 2 O 2 have been fully considered, and protective measures have been added during the storage and transportation of H 2 O 2 , such as coating inert materials on low-temperature storage and transportation pipeline structures, which can avoid H 2 before the reaction to the greatest extent. Self-decomposition of O2 .

3.采用廉价的过渡金属氧化物催化剂(钛化铁材料),可实现NOX的深度氧化,大部分产物转化为硝酸盐,减免了废水溶液需进行二次处理的繁琐流程,且脱硝温区(180~220℃)远低于常规脱硝温度,工艺操作简单,易于实施,对各种化石燃料燃烧的工业过程均具有广泛的适用性,投资和运行成本低廉。3. The use of cheap transition metal oxide catalysts (iron titanide materials) can realize the deep oxidation of NO X , and most of the products are converted into nitrates, which reduces the cumbersome process of secondary treatment of wastewater solutions, and the denitrification temperature range (180-220°C) is far lower than the conventional denitrification temperature, the process operation is simple, easy to implement, it has wide applicability to various fossil fuel combustion industrial processes, and the investment and operation costs are low.

本发明以锐钛矿形式存在的二氧化钛为基体,氧化铁为助催化剂;本发明所用氧化剂及催化剂具有脱硝效率高、工艺设计合理、环保无毒、造价低、产品质量稳定的优点,同时本发明工艺中的脱硝产物可作为农业化肥或工业原料,不会对环境造成二次污染。In the present invention, titanium dioxide in the form of anatase is used as a substrate, and iron oxide is used as a cocatalyst; the oxidizing agent and catalyst used in the present invention have the advantages of high denitrification efficiency, reasonable process design, environmental protection, non-toxicity, low cost, and stable product quality. The denitration products in the process can be used as agricultural fertilizers or industrial raw materials without causing secondary pollution to the environment.

附图说明Description of drawings

图1为本发明脱硝系统示意图。Figure 1 is a schematic diagram of the denitrification system of the present invention.

图2为本发明波纹板的结构示意图。Fig. 2 is a structural schematic diagram of the corrugated plate of the present invention.

图中:1-低温控制系统;2-H2O2溶液储存罐;3-一号流量计;4-一号输送泵;5-加热装置;6-反应塔;7-格栅;8-波纹板;9-碱液储蓄罐;10-二号流量计;11-二号输送泵;12-喷淋装置;13-三号输送泵;A-烟气入口;B-出液口;C-净烟气出口。In the figure: 1-low temperature control system; 2-H 2 O 2 solution storage tank; 3-No. 1 flow meter; 4-No. 1 delivery pump; 5-heating device; 6-reaction tower; 7-grid; 8- Corrugated plate; 9-alkali storage tank; 10-No. 2 flow meter; 11-No. 2 delivery pump; 12-spray device; 13-No. 3 delivery pump; A-flue gas inlet; B-liquid outlet; C - Net flue gas outlet.

具体实施方式Detailed ways

为使本发明要解决的技术问题、技术方案和优点更加清楚,下面将结合附图及具体实施例进行详细描述。In order to make the technical problems, technical solutions and advantages to be solved by the present invention clearer, the following will describe in detail with reference to the drawings and specific embodiments.

如图1所示,本发明一种采用催化过氧化氢的脱硝方法如下:As shown in Figure 1, a kind of denitrification method that adopts catalytic hydrogen peroxide of the present invention is as follows:

通过低温控制系统1控制H2O2溶液储存罐2中H2O2溶液的温度,H2O2溶液通过一号流量计3计量,由一号输送泵4输送流经加热装置5转变为H2O2蒸汽,H2O2蒸汽经过格栅7与从反应塔6的烟气入口A进入的除尘烟气进行混合为混合气体,混合气体通过涂覆有钛化铁催化剂的波纹板8进行反应,混合气体中的H2O2蒸汽与烟气中的NOX反应生成包含亚硝酸和硝酸的酸性气体;碱液存储罐9中的碱液经二号流量计10计量,由二号输送泵11输送至喷淋装置12中形成碱性雾化液滴,碱性雾化液滴对酸性气体进行洗涤生成亚硝酸盐和硝酸盐溶液,亚硝酸盐和硝酸盐溶液通过三号输送泵13经出液口B抽离反应塔,然后再经过蒸发结晶转化为固体产物。The temperature of the H 2 O 2 solution in the H 2 O 2 solution storage tank 2 is controlled by the low temperature control system 1, and the H 2 O 2 solution is measured by the No. 1 flow meter 3, and is transferred by the No. 1 delivery pump 4 and flows through the heating device 5 into H 2 O 2 steam, H 2 O 2 steam passes through the grid 7 and mixes with the dust-removing flue gas entering from the flue gas inlet A of the reaction tower 6 to form a mixed gas, and the mixed gas passes through the corrugated plate 8 coated with iron titanium oxide catalyst To react, the H2O2 steam in the mixed gas reacts with the NOx in the flue gas to generate acid gas containing nitrous acid and nitric acid; the lye in the lye storage tank 9 is metered by the No. The delivery pump 11 is delivered to the spraying device 12 to form alkaline atomized droplets, which wash the acid gas to generate nitrite and nitrate solutions, and the nitrite and nitrate solutions pass through the No. 3 delivery pump 13 is withdrawn from the reaction tower through the liquid outlet B, and then transformed into a solid product through evaporation and crystallization.

如图2所示,为波纹板8的示意图。As shown in FIG. 2 , it is a schematic diagram of the corrugated plate 8 .

下述实施例中的百分含量如无特殊说明均为摩尔百分含量The percentages in the following examples are mole percentages unless otherwise specified

实施例1:Example 1:

H2O2溶液储存罐(2)中质量分数为3%的H2O2溶液通过一号流量计(3)计量,由一号输送泵(4)输送流经加热装置(5)转变为H2O2蒸汽,H2O2蒸汽经过格栅(7)与从反应塔(6)的烟气入口A进入的除尘烟气进行混合,烟气中NO含量为600ppm,入口烟温为180℃,混合气体通过涂覆有1%Fe-TiO2催化剂的波纹板(8)生成包含亚硝酸和硝酸的酸性气体,其中空速比为60000h-1。碱液存储罐9中的碱液经二号流量计(10)计量,由二号输送泵(11)输送至喷淋装置(12)中形成碱性雾化液滴,碱性雾化液滴对酸性气体进行洗涤生成亚硝酸盐和硝酸盐溶液,亚硝酸盐和硝酸盐溶液经三号输送泵(13)抽离反应塔,然后再经过蒸发结晶。脱硝效率高达90%,反应塔底部的废液经离子色谱进行检测硝酸根和亚硝酸根的摩尔比为7.2:1。H 2 O 2 mass fraction in the solution storage tank (2) is 3% H 2 O The solution is measured by the No. 1 flowmeter (3), and is transferred by the No. 1 delivery pump (4) and flows through the heating device (5) into H 2 O 2 steam, H 2 O 2 steam is mixed with the dedusted flue gas entering from the flue gas inlet A of the reaction tower (6) through the grid (7), the NO content in the flue gas is 600ppm, and the inlet flue temperature is 180 °C, the mixed gas passes through the corrugated plate (8) coated with 1% Fe-TiO 2 catalyst to generate acid gas containing nitrous acid and nitric acid, and the space velocity ratio is 60000h -1 . The lye in the lye storage tank 9 is metered by the No. 2 flow meter (10), and is transported to the spraying device (12) by the No. 2 delivery pump (11) to form alkaline atomized droplets, and the alkaline atomized droplets The acid gas is washed to generate nitrite and nitrate solutions, which are pumped out of the reaction tower through the No. 3 delivery pump (13), and then evaporated and crystallized. The denitrification efficiency is as high as 90%. The waste liquid at the bottom of the reaction tower is detected by ion chromatography, and the molar ratio of nitrate and nitrite is 7.2:1.

实施例2:Example 2:

使用实施例1的方法进行脱硝时,其中,处理烟气中一氧化氮浓度为750ppm,催化剂为2%Fe-TiO2,空速比为60000h-1,过氧化氢质量分数为4%,过氧化氢与一氧化氮摩尔比为12:1,入口烟温为200℃,氧化后的酸性气体经碱液喷淋吸收,脱硝效率达92%,反应塔底部的废液经离子色谱进行检测硝酸根和亚硝酸根的摩尔比为7.4:1。When using the method of Example 1 for denitrification, wherein the concentration of nitrogen monoxide in the treated flue gas is 750ppm, the catalyst is 2% Fe-TiO 2 , the space velocity ratio is 60000h -1 , the mass fraction of hydrogen peroxide is 4%, and the over The molar ratio of hydrogen oxide to nitrogen monoxide is 12:1, the inlet smoke temperature is 200°C, the oxidized acid gas is sprayed and absorbed by alkali solution, and the denitrification efficiency reaches 92%, and the waste liquid at the bottom of the reaction tower is detected by ion chromatography for nitric acid The molar ratio of root and nitrite is 7.4:1.

实施例3:Example 3:

使用实施例1的方法进行脱硝时,其中,处理烟气中一氧化氮浓度为550ppm,催化剂为3%Fe-TiO2,空速比为60000h-1,过氧化氢质量分数为4%,过氧化氢与一氧化氮摩尔比为16:1,入口烟温为220℃,氧化后的酸性气体经碱液喷淋吸收,脱硝效率达91%,反应塔底部的废液经离子色谱进行检测硝酸根和亚硝酸根的摩尔比为6.9:1。When using the method of Example 1 for denitrification, wherein the concentration of nitric oxide in the treated flue gas is 550ppm, the catalyst is 3% Fe-TiO 2 , the space velocity ratio is 60000h -1 , the mass fraction of hydrogen peroxide is 4%, and the over The molar ratio of hydrogen oxide to nitrogen monoxide is 16:1, and the inlet smoke temperature is 220°C. The oxidized acid gas is sprayed and absorbed by alkali solution, and the denitrification efficiency reaches 91%. The waste liquid at the bottom of the reaction tower is detected by ion chromatography for nitric acid The molar ratio of root to nitrite is 6.9:1.

以上所述方案中各个实施例采用递进的方式描述,每个实施例重点说明的都是与其他实施例的不同之处,各个实施例之间相同相似部分互相参见即可,各实施例中所涉及到的技术特征在彼此之间不构成冲突的前提下可以相互组合。Each embodiment in the above scheme is described in a progressive manner, and each embodiment focuses on the differences from other embodiments. The same and similar parts between the various embodiments can be referred to each other. In each embodiment The technical features involved can be combined with each other on the premise that they do not constitute conflicts with each other.

在本发明的描述中,术语“一号”、“二号”等仅用于描述目的,而不能理解为指示或暗示相对重要性。In the description of the present invention, the terms "No. 1", "No. 2" and so on are used for descriptive purposes only, and should not be understood as indicating or implying relative importance.

以上所述仅是本发明的优选实施方式,应当指出,对于本技术领域的普通技术人员来说,在不脱离本发明所述原理的前提下,还可以做出若干改进和润饰,这些改进和润饰也应视为本发明的保护范围。The above is only a preferred embodiment of the present invention, it should be pointed out that for those of ordinary skill in the art, without departing from the principle of the present invention, some improvements and modifications can also be made, these improvements and Retouching should also be regarded as the protection scope of the present invention.

Claims (6)

  1. A kind of 1. denitrification apparatus using catalyzing hydrogen peroxide, it is characterised in that:Including H2O2Storage is deposited with induction system, alkali lye Storage and induction system, catalyst elements, reaction tower (6) and waste liquid supply unit composition;The H2O2Storage includes with transport system The H connected with reaction tower (6) top2O2Solution storage tanks (2), are successively set on H2O2Solution storage tanks (2) and reaction tower (6) No.1 flowmeter (3), No.1 delivery pump (4) and heater (5) on connecting pipeline, it is arranged in reaction tower (6), communicating pipe The grid (7) of road end, and and H2O2The low-temperature control system (1) of solution storage tanks (2) connection;Alkali lye storage with it is defeated Fortune system includes the alkali lye accumulator tank (9) connected with reaction tower (6) bottom, is arranged on alkali lye accumulator tank (9) and connects with reaction tower (6) No. two flowmeters (10) and No. two pressurized delivered pumps (11) on siphunculus road, and be arranged in reaction tower (6), connecting pipeline end The spray equipment (12) at end;The catalyst elements are to be arranged in reaction tower (6) and be located at grid (7) and spray equipment (12) Between the corrugated plating (8) for being covered with catalyst;The waste liquid supply unit is No. 3 delivery pumps for being connected to reaction tower (6) bottom (13);
    The catalyst that is covered with the corrugated plating (8) is the Ti-base catalyst coated with load ferro element, and wherein iron and titanium rubs Your ratio is (1~5):100.
  2. A kind of 2. denitrification apparatus using catalyzing hydrogen peroxide according to claim 1, it is characterised in that:The H2O2It is molten Liquid holding vessel (2), H2O2Solution storage tanks (2) and reaction tower (6) connecting pipeline are H2O2The inner surface of conveyance conduit, grid (7) And reaction tower (6) interior H2O2The Mixed Zone coated inert material coating of steam and flue gas, will not promote decomposing H2O2And resolution Hydroxyl radical free radical.
  3. A kind of 3. denitrification apparatus using catalyzing hydrogen peroxide according to claim 2, it is characterised in that:The inertia material Expect for silica or plastics or fluoroplastics.
  4. 4. the method for denitration of the denitrification apparatus using catalyzing hydrogen peroxide described in claim any one of 1-3, it is characterised in that: H is controlled by low-temperature control system (1)2O2H in solution storage tanks (2)2O2The temperature of solution, H2O2Solution passes through No.1 flowmeter (3) measure, H is changed into by the heated device of No.1 delivery pump (4) transport Stream (5)2O2Steam, H2O2Steam by grid (7) with The dedusting flue gas entered from the smoke inlets (A) of reaction tower (6) be mixed into mixed gas, and mixed gas is by coated with urging The corrugated plating (8) of agent is reacted, the H in mixed gas2O2Steam and the NO in flue gasXReaction generation comprising nitrous acid and The sour gas of nitric acid;Alkali lye in alkali lye storage tank (9) measures through No. two flowmeters (10), is conveyed by No. two delivery pumps (11) To forming alkaline atomized drop in spray equipment (12), alkaline atomized drop sour gas is carried out washing generation nitrite and Nitrate solution, nitrite and nitrate solution detach reaction tower, Ran Houzai by No. three delivery pumps (13) through liquid outlet (B) Solid product is converted into by evaporative crystallization;
    The H2O2The mass concentration of solution is 3~6%, H2O2With NO in the flue gasXMol ratio be (10~15):1;
    The heating-up temperature of the heater (5) is 140~160 DEG C.
  5. 5. method of denitration according to claim 4, it is characterised in that the temperature that the low-temperature control system (1) controls is 5 ~10 DEG C.
  6. 6. method of denitration according to claim 5, it is characterised in that:Described flue-gas temperature is 160-240 DEG C.
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US6793903B1 (en) * 2001-03-08 2004-09-21 The United States Of America As Represented By The Administrator Of The National Aeronautics And Space Administration High temperature decomposition of hydrogen peroxide
CN103463978A (en) * 2013-09-30 2013-12-25 南京理工大学 Device and method for smoke simultaneous desulfurization and denitrification based on hydrogen peroxide catalytic oxidation
CN106031841A (en) * 2015-03-20 2016-10-19 北京博源恒升高科技有限公司 Denitration technology and equipment for gas

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Publication number Priority date Publication date Assignee Title
US6793903B1 (en) * 2001-03-08 2004-09-21 The United States Of America As Represented By The Administrator Of The National Aeronautics And Space Administration High temperature decomposition of hydrogen peroxide
CN103463978A (en) * 2013-09-30 2013-12-25 南京理工大学 Device and method for smoke simultaneous desulfurization and denitrification based on hydrogen peroxide catalytic oxidation
CN106031841A (en) * 2015-03-20 2016-10-19 北京博源恒升高科技有限公司 Denitration technology and equipment for gas

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