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Electrochemical-chemical composite oxidation treatment method for seawater desulfurization recovery system

A composite oxidation and recovery system technology, applied in the direction of electrochemical water/sewage treatment, seawater treatment, oxidized water/sewage treatment, etc., can solve the problems of large area of ​​aeration tank, low drainage pH, small absorption capacity, etc. Achieve high sulfite oxidation efficiency, high pH value of drainage, and low COD value

Active Publication Date: 2015-10-14
BEIJING LONGYUAN ENVIRONMENTAL ENG CO LTD
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

[0006] Due to the high efficiency and convenience of electrochemical technology, it has been used as an auxiliary system for seawater desulfurization recovery, but there are also disadvantages such as high electrode cost and low pH of wastewater.
The existing seawater desulfurization recovery system, in use, due to the effect of seawater on SO 2 The absorption capacity is small and the concentration of dissolved oxygen is low, and a large amount of seawater is required, so that the aeration tank covers a large area, the aeration load is high, the energy consumption is high, and the pH value and COD of the drainage are not up to the standard, etc.

Method used

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  • Electrochemical-chemical composite oxidation treatment method for seawater desulfurization recovery system
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  • Electrochemical-chemical composite oxidation treatment method for seawater desulfurization recovery system

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Embodiment 1

[0040] like figure 1 As shown, a special equipment for realizing the method of the present invention includes: an aeration tank 10, the aeration tank is divided into a mixed aeration chamber, an aeration chamber and a mixing chamber, and in the mixed aeration chamber One end is provided with acidic seawater inlet 12 and the first fresh seawater inlet 14, is provided with up to standard seawater outlet 13 and the second fresh seawater inlet 15 at one end of said mixing chamber, and said acidic seawater inlet 12 is connected with absorption tower 1; Electrodes made of polyacrylonitrile carbon fiber material are also arranged in the mixed aeration chamber, which are respectively used as anode and cathode. A polyacrylonitrile carbon fiber tow 7 is fixed around the titanium wire 6 , and the anode and cathode are respectively connected to the positive pole and the negative pole of the DC power supply 4 through cables 5 .

Embodiment 2

[0042] First put the anode and cathode made of the polyacrylonitrile carbon fiber material into the aeration tank 10, connect the positive and negative poles of the DC power supply 4 with cables 5, and then mix the acidic seawater 2 discharged from the absorption tower with fresh seawater 3 Mixing once, in which the mixing ratio of acidic seawater 2 / fresh seawater 3 is controlled to 1:1~3, and then enters the aeration tank 10 for aeration and chemical oxidation, and at the same time turns on the DC power supply 4 to perform electrochemical Oxidation, where the working electrode potential of the anode is 0.8V SCE , the working electrode potential of the cathode is -0.6V SCE . Figure 5 For the above-mentioned combined oxidation treatment and comparative single aeration chemical oxidation treatment, the SO 3 2- The relationship between oxidation efficiency (A), pH (B) and oxidation time. Figure 5 In A, the composite oxidation reacted for 2 minutes with a mixing ratio of 1:2...

Embodiment 3

[0047] First put the anode and cathode made of the polyacrylonitrile carbon fiber material into the aeration tank 10, connect the positive and negative poles of the DC power supply 4 with cables 5 respectively, and then mix the acidic seawater 2 discharged from the absorption tower with fresh The seawater 3 is mixed once, and the mixing ratio of acidic seawater 2 / fresh seawater 3 is controlled to 1:2, and then enters the aeration tank 10 for aeration chemical oxidation, and at the same time, the DC power supply 4 is turned on, and the constant current control method is used for electrochemical oxidation , where the working electrode potential of the anode is 1.0V SCE , the working electrode potential of the cathode is -0.8V SCE ; After 2 min of the above combined oxidation treatment, SO 3 2- The oxidation rate can reach 91%, and the pH value is 5.91. After the combined oxidation treatment, the seawater is aerated separately for 2 minutes, not only the oxidation rate is furth...

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Abstract

The present invention discloses an electrochemical-chemical composite oxidation treatment method for a seawater desulfurization recovery system. The method comprises that: 1, acid seawater (2) discharged from an absorption tower (1) and fresh seawater (3) are mixed according to a ratio of 1:1-3, and the obtained mixture enters an aeration tank (10) and is concurrently subjected to an aeration chemical oxidation and electrochemical oxidation composite treatment, wherein the electrochemical oxidation treatment method respectively adopts electrodes produced from a polyacrylonitrile carbon fiber material as an anode and a cathode, and the anode and the cathode are placed into the aeration tank (10); and 2, the seawater (9) being subjected to the oxidation treatment and fresh seawater (3) are subjected to secondary mixing according to a ratio of 1:0.5-1 to obtain seawater (11) meeting the discharge standard. The method has advantages of less fresh seawater consumption, low aeration load, high sulfite oxidation efficiency, high pH value of the discharged water, low COD value and the like, and can meet energy saving and emission reduction requirements of the seawater desulfurization recovery system.

Description

technical field [0001] The invention relates to the technical field of industrial water treatment, in particular to an electrochemical-chemical composite oxidation treatment method used in a seawater desulfurization recovery system. Background technique [0002] Acid rain is an environmental problem of global concern. It is caused by the large amount of acid gases (sulfur dioxide, etc.) produced by human beings burning coal and so on, which are discharged into the atmosphere along with the flue gas. Most of the flue gas desulfurization systems of large and medium-sized thermal power plants use limestone-gypsum method and circulating fluidized bed technology, but there are disadvantages such as high cost, complex system and easy scaling and blockage. In recent years, flue gas seawater desulfurization system has become a mature new technology in coastal areas. A lot of research has been done on the principle of seawater desulfurization at home and abroad, and it is generally ...

Claims

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Application Information

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Patent Type & Authority Patents(China)
IPC IPC(8): C02F1/74C02F1/46C02F103/08
Inventor 何强陈玉乐王小立薛军
Owner BEIJING LONGYUAN ENVIRONMENTAL ENG CO LTD