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Desulphurization denitration method for ammonium sulfide solution

A technology for desulfurization, denitrification and ammonium sulfide, which is applied in the field of flue gas purification, can solve the problems of high desulfurization cost, large influence of flue gas components, and low denitration efficiency, and achieves high desulfurization and denitrification efficiency, easy storage and transportation, and high removal efficiency. Effect

Active Publication Date: 2016-01-13
KUNMING UNIV OF SCI & TECH
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

There are many problems in the existing desulfurization and denitrification technology, such as the large fixed investment and high desulfurization cost of the limestone-gypsum method, and the large amount of gypsum produced is difficult to handle, etc.; the SCR technology has problems such as large catalyst investment, large influence of flue gas components, and high operating costs. , SNCR technology has a series of problems such as high reaction temperature, poor mixing degree of reducing agent and flue gas, low denitrification efficiency, and large amount of ammonia overflow.
Therefore, the joint desulfurization and denitrification technology has problems such as high fixed investment, high operation and maintenance costs, and complicated operation.
ZL201410290112.5 "A method for flue gas desulfurization and denitrification using urea co-production technology" proposes that the ammonia gas produced by urea co-production technology can be used alone for flue gas desulfurization and denitrification, and the obtained cyanuric acid can also be used alone Flue gas desulfurization and denitrification, ammonia and cyanuric acid can also be combined for desulfurization and denitrification at the same time, ammonia desulfurization, ammonia denitration, cyanuric acid desulfurization, cyanuric acid denitrification are independent of each other, desulfurization The purpose of desulfurization and denitrification can only be achieved by combining the two parts of denitrification. The reaction temperature is between 500 ° C and 1100 ° C. It is also necessary to control the intake ratio of ammonia, cyanuric acid, sulfur dioxide and nitrogen oxides, although the efficiency of desulfurization and denitrification can be improved. , but the operation is complicated and the energy consumption is high
ZL200710052129.7 "Simultaneous desulfurization and denitrification wet ammonia flue gas cleaning process and its system" proposes: first oxidize the nitric oxide in the flue gas to form nitrogen dioxide, and then make the sulfur dioxide and carbon dioxide in the flue gas Nitrogen oxide reacts with ammonia water to generate ammonium sulfite, ammonium nitrate and ammonium nitrite, and then oxidizes the ammonium sulfite and ammonium nitrite to generate by-products ammonium sulfate and ammonium nitrate. At the same time, the flue gas after desulfurization and denitration is processed Eliminate fog and finally obtain clean flue gas. In this invention, nitrogen oxides are absorbed and nitrogen monoxide is produced at the same time, which has the problem of low denitrification efficiency.

Method used

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Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0052] SO in industrial furnace flue gas 2 and NO X The specific recycling methods are as follows:

[0053] (1) The flue gas to be treated in this example is zinc smelting flue gas, and the flue gas volume is 30,000m 3 / h, the flue gas at the furnace mouth contains SO 2 : 3%~4%, NO X : 1300~1700mg / m 3 , After the smelting flue gas is dedusted and washed with water, the temperature of the flue gas is cooled to below 50°C, and air is blown in (the amount of air is 10% of the flue gas amount);

[0054] (2) Ammonium sulfide solution with a concentration of 25% by mass and pH=7.2 (adjusted with a mixture of ammonium thiosulfate, ammonium bisulfite and ammonium nitrate, ammonium bisulfite, ammonium thiosulfate and ammonium nitrate The mass ratio is 3:1:1) atomized through the vortex nozzle of the absorption tower, and after cooling, the flue gas enters the secondary absorption tower countercurrently and fully contacts with the atomized ammonium sulfide solution. 2 and NO X Th...

Embodiment 2

[0059] SO in lead smelting flue gas 2 and NO X The recycling methods are as follows:

[0060] (1) The flue gas to be treated in this example is lead smelting flue gas, and the flue gas volume is 10000m 3 / h, the flue gas at the furnace mouth contains SO 2 : 0.8%~1%, NO X : 1000~1300mg / m 3 , the flue gas from industrial furnaces is dedusted and washed with water to cool the temperature of the flue gas to below 50°C, and blow in air (the amount of air is 15% of the flue gas amount);

[0061] (2) Ammonium sulfide solution with a mass percentage concentration of 10% and pH=7.5 (adjusted with ammonium thiosulfate, ammonium bisulfite and ammonium nitrate mixture, ammonium bisulfite, ammonium thiosulfate and ammonium nitrate The mass ratio is 5:1:1) atomized through the vortex nozzle of the absorption tower, and after cooling, the flue gas enters the secondary absorption tower countercurrently and fully contacts with the atomized ammonium sulfide solution. 2 and NO X The smelt...

Embodiment 3

[0066] SO in nickel smelting flue gas 2 and NO XThe recycling methods are as follows:

[0067] (1) The flue gas to be treated in this example is nickel smelting flue gas, and the flue gas volume is 20000m 3 / h, the flue gas at the furnace mouth contains SO 2 : 1%~2%, NO X : 900~1200mg / m 3 After the flue gas is dedusted and washed with water, the temperature of the flue gas is cooled to below 50°C, and air is blown in (the amount of air is 20% of the flue gas volume);

[0068] (2) Ammonium sulfide solution with a mass percentage concentration of 17% and pH=7 (adjusted with ammonium thiosulfate, ammonium bisulfite and ammonium nitrate mixture, ammonium bisulfite, ammonium thiosulfate and ammonium nitrate The mass ratio is 2:1:1) atomized through the vortex nozzle of the absorption tower, and after cooling, the flue gas enters the secondary absorption tower countercurrently and fully contacts with the atomized ammonium sulfide solution. 2 and NO X The smelting flue gas is ...

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Abstract

The invention discloses a desulphurization denitration method for ammonium sulfide solution, and belongs to the technical field of flue gas purification. The method comprises employing an ammonium sulfide solution as an absorbent to absorb sulfur dioxide (SO2) and nitrogen oxides (NOx); performing dust removal and water-washing pretreatment on industrial kiln and furnace flue gas, and blowing proper amount of air into a flue gas pipe, so as to oxidize nitrogen monoxide in the nitrogen oxides into nitrogen dioxide under a slight hot condition, performing two-stage absorption on the flue gas by ammonium sulfide, so as to enable sulfur dioxide and nitrogen oxides in the gas to be absorbed and converted into salts and left in the solution; after the absorption reaction is finished, filtering and recovering sulfur, and performing neutralization, oxidation, evaporation crystallization and drying processing on the filtrate, so as to obtain a solid mixture of ammonium sulfate and ammonium nitrate, wherein the solid mixture can be sold directly as a fertilizer. The method is simple in technology, easy to operate, high in desulphurization denitration efficiency, low in cost and suitable for industrialized application.

Description

technical field [0001] The invention relates to a method for desulfurization and denitrification of an ammonium sulfide solution, and belongs to the technical field of flue gas purification. Background technique [0002] my country's energy is dominated by coal-fired coal, which accounts for 75% of coal production. The raw coal is used for direct combustion. The coal combustion process produces serious pollution, and the sulfur dioxide produced will lead to acid rain. Nitrogen oxides are also one of the causes of acid rain. Human health, under certain conditions, can also destroy the ozone layer and produce photochemical smog. In short, coal-fired smoke is one of the largest pollution sources that cause damage to the ecological environment in our country. my country's energy consumption accounts for 8% to 9% of the world's total, sulfur dioxide emissions account for 15.1% of the world's total, and coal-fired sulfur dioxide emissions account for 87% of the national emissions. ...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): B01D53/78B01D53/60B01D47/00C01C1/18C01C1/246C01B17/04
CPCY02A50/20
Inventor 王学谦王郎郎宁平马懿星李林
Owner KUNMING UNIV OF SCI & TECH
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