Ammonia desulphurization and denitrification process for flue gas by synchronization of complexing absorption and electrolytic regeneration

Abstract

The invention discloses an ammonia desulphurization and denitrification process for flue gas by synchronization of complexing absorption and electrolytic regeneration and solves the problem of low absorption liquid regeneration efficiency in an existing synchronous ammonia desulphurization and denitrification process for the flue gas. The technical scheme includes that the flue gas is pressurized and then fed into a concentration tower to realize contact reaction with concentration liquid in the tower, the flue gas discharged from the concentration tower is fed into an absorption tower to realize contact reaction with cyclic absorption liquid in the absorption tower, the concentration liquid at the bottom of the concentration tower is subjected to deferrization through a first electrolytic reactor after reaction and then fed into an ammonium sulfate crystallization system, the absorption liquid at the bottom of the absorption tower is regenerated and then fed back to the upper portion of the absorption tower to serve as the cyclic absorption liquid, the concentration liquid enters an anode chamber of a reaction unit of the first electrolytic reactor to realize oxidation reaction and then enters a cathode chamber to realize a reduction reaction, and an electrolytic solution is discharged through a short outlet connection pipe of the reactor after reaction and fed into the ammonium sulfate crystallization system. The ammonia desulphurization and denitrification process for the flue gas by synchronization of complexing absorption and electrolytic regeneration has the advantages of simplicity, low investment cost and operation cost, high conversion efficiency and effectiveness in deferrization, desulphurization and denitrification.

Description

technical field [0001] The invention relates to a flue gas desulfurization and denitrification process belonging to the field of energy saving and environmental protection, in particular to a flue gas ammonia desulfurization and denitrification process of complexation absorption and synchronous electrolysis regeneration. Background technique [0002] Wet flue gas synchronous desulfurization and denitrification technology, especially wet ammonia-complexation synchronous desulfurization and denitrification technology, has been highly valued by the industry due to its advantages of high desulfurization efficiency, low investment, low water consumption, effective use of by-products, and no secondary pollution. Fe(II)EDTA has a good complexing effect on NO and high denitrification efficiency. For example, the patent application with the publication number 104226095A and the title of the invention is "Synchronous denitrification process based on flue gas wet ammonia desulfurization...

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Problems solved by technology

[0003] In the iron removal step, alkali needs to be added to adjust the pH value, so that a large amount of alkali metal ions are brought into the concentrated solution into the absorption solution, which increases the production cost and is not conducive to the subsequent crystallization of ammonium sulfate, affecting the quality of desulfurization products

[0004] There are following problems in adopting the iron filings method in the regeneration step: (1) because the absorption liquid is acidic, the iron filings are easily corroded, resulting in a large consumption of iron filings, and the concentration of iron ions in the absorption liquid is too high, which not only increases the cost of iron removal, but also Affect the quality of desulfurization and denitrification by-products; (2) Since the elemental iron in the iron filings is oxidized and corroded into the solution, the pH value of the absorption solution increases, resulting in the weakening of the regenerative reduction ability of the iron filings to the complexing agent

In order to ensure the denitrification efficiency, acid needs to be added to the system, resulting in a further increase in denitrification costs

(3) The consumption of iron filings is relatively large, and a large amount of elemental iron is oxidized into the absorption liquid. Since the pH value of the absorption liquid is controlled above 5.0, the absorption liquid contains a large amount of ferric hydroxide colloid (suspended matter), which will lead to circulation The wear of the impeller of the pump is increased, and it will also cause the nozzle and pipeline to block

(4) Since iron filings are filled in the closed regeneration tower, and the consumption of iron filings is continuous, continuous replenishment of iron filings cannot be realized

[0010] (1) For the reaction system with good electrochemical reversibility between the reactant and the product, the existing electrolysis device will cause repeated conversion between the reactant and the product in the electrolysis reactor, which not only affects the conversion efficiency, but also waste of electricity;

[0011] (2) The existing electrolysis device cannot effectively use the flow of the electrolyte itself to provide a large turbulent force for rapid renewal of the reactants on the electrode surface, and the electrochemical reaction speed is relatively slow, thereby reducing the reaction conversion rate;

[0012] (3) For complex reaction systems containing side reactions, existing electrolysis devices cannot effectively remove electrochemical reaction products that cause side reactions in a timely manner;

[0013] (4) The existing electrolysis device has a complex structure and a large footprint

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