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Sewage treatment method based on improved A2O process

A sewage treatment method and improved technology, applied in biological water/sewage treatment, light water/sewage treatment, water/sewage multi-stage treatment, etc., can solve the problems of insufficient denitrification reaction, insufficient carbon source, influence, etc. Achieve the effect of solving carbon source competition and sludge age difference, shortening reaction time and improving phosphorus removal efficiency

Inactive Publication Date: 2018-11-23
襄阳先创环保科技有限公司
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

In anaerobic / anoxic / aerobic (A 2 O) In the process of treating urban sewage, due to the water quality characteristics of urban sewage low in organic matter and high in nitrogen and phosphorus, the carbon source is insufficient, which makes denitrification and denitrification in this process unsatisfactory, and it is difficult to achieve a good simultaneous denitrification and phosphorus removal effect
[0003] Chinese Patent No. CN201310474121.5 discloses an improved A 2 O sewage treatment method, through the biological phase separator set in the aerobic tank, the sludge is preliminarily precipitated and then enters the sedimentation tank, and the supernatant in the biological phase separator is returned to the anoxic tank; although the good is increased to a certain extent However, the sludge returned from the aerobic tank will entrain more nitrate nitrogen, thereby increasing the consumption of organic matter in the anaerobic tank, hindering anaerobic phosphorus release, and then affecting the denitrification reaction and good performance of the anoxic tank. The phosphorus-accumulating bacteria in the aerobic tank absorb phosphorus; secondly, the insufficient denitrification reaction in the anoxic tank will cause the sewage entering the aerobic tank to contain a certain amount of nitrate nitrogen, resulting in a high concentration of ammonia nitrogen in the effluent and a high efficiency of total nitrogen purification. Low

Method used

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  • Sewage treatment method based on improved A2O process

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Effect test

Embodiment 1

[0051] A modified A 2 The sewage treatment method of O process, in the traditional A 2 Improvement is made on the basis of the O process, and the sewage passes through the anaerobic tank, the anoxic tank, the aerobic tank and the secondary sedimentation tank in turn, and the anaerobic tank is inoculated with domesticated anaerobic sludge, and the anaerobic sludge in the anaerobic sludge is inoculated. The dominant bacteria include Anammox bacteria, Anaerolinea, Bifidobacterium, Clostridium, Methanogenus, Moraxella, Serratia marcescens, Phycisphaerae, and Flavobacteriales. The Anammox bacteria include Candidatus Kuenenia, Scalindua, Anammoxoglobuspropionicus, and there are biofilm electrode reactions in the aerobic and anoxic pools The anode uses a cylindrical nickel electrode, and a layer of jade that can radiate far-infrared rays with a wavelength of 6 to 14 μm is glued inside the cylinder. It is located in the aerobic pool, and the cathode uses an activated carbon fiber elec...

Embodiment 2

[0059] A modified A 2 The sewage treatment method of the O process is improved on the basis of the traditional AO process. The sewage passes through the anaerobic tank, the anoxic tank, the aerobic tank and the secondary sedimentation tank in turn, and the anaerobic tank is inoculated with domesticated anaerobic sludge. , the dominant bacteria in the anaerobic sludge include Anammox bacteria, Anaerolinea, Bifidobacterium, Clostridium, Methanogenus, Moraxella, Serratia marcescens, Phycisphaerae and Flavobacteriales, the Anammox bacteria include Candidatus Kuenenia, Candidatus Brocadia, Anammoxoglobuspropionicus, and the aerobic tank and There is a biofilm electrode reactor in the anoxic pool, the anode is a cylindrical copper electrode, and a layer of biochar that can radiate far-infrared rays with a wavelength of 6-14 μm is bonded inside the tube, which is located in the aerobic pool, and the cathode is graphite carbon felt. The electrode, with denitrifying bacteria biofilm fi...

Embodiment 3

[0067] A modified A 2 The sewage treatment method of O process, in the traditional A 2 Improvement is made on the basis of the O process, and the sewage passes through the anaerobic tank, the anoxic tank, the aerobic tank and the secondary sedimentation tank in turn, and the anaerobic tank is inoculated with domesticated anaerobic sludge, and the anaerobic sludge in the anaerobic sludge is inoculated. The dominant bacteria include Anammox bacteria, Anaerolinea, Bifidobacterium, Clostridium, Methanogenus, Moraxella, Serratia marcescens, Phycisphaerae, and Flavobacteriales, and the Anammox bacteria include Candidatus Jettenia, Candidatus Brocadia, Scalindua, and there are biofilm electrodes in the aerobic and anoxic pools The anode of the reactor is a cylindrical titanium electrode, and a layer of far-infrared ceramics that can radiate far-infrared rays with a wavelength of 6-14 μm is bonded inside the cylindrical shape. It is located in the aerobic pool, and the cathode is a ca...

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Abstract

The invention provides a sewage treatment method based on an improved A2O process, belonging to the technical field of sewage treatment. The method concretely comprises the steps of enabling sewage tosequentially pass through an anaerobic pool, an anoxic pool, an aerobiotic pool and a secondary sedimentation tank; mixing reflux mixed liquid in the aerobiotic pool with inlet water of the anaerobicpool, and then enabling the mixed liquid to enter the anaerobic pool for treating; inoculating the anaerobic pool with domesticated anaerobic sludge. Total nitrogen is removed by means of a combinedaction of anammox bacteria and denitrifying bacteria, so that the nitrogen removal ability is high; furthermore, the bacteria do not compete with phosphorus-accumulating bacteria for a carbon source and a growth space, so that the phosphorous removal efficiency is high. The method solves the problem of contradiction of carbon source competition between the phosphorus-accumulating bacteria and thedenitrifying bacteria and sludge age difference in an anaerobic pool of the traditional A2O process.

Description

technical field [0001] The invention relates to the technical field of sewage treatment, in particular to an improved A 2 Sewage treatment method of O process. Background technique [0002] A 2 The O process, also known as the AAO process, is an anaerobic-anoxic-aerobic process. It is a commonly used secondary sewage treatment process, which has the effect of synchronous nitrogen and phosphorus removal. The process is: sewage and return sludge first enter The anaerobic tank (DO<0.2mg / L) is completely mixed, and after a certain period of anaerobic decomposition, part of the BOD is removed and part of the nitrogen-containing compounds are converted into N 2 Release, the phosphorus-accumulating microorganisms in the return sludge release phosphorus to meet the demand of bacteria for phosphorus, and then the sewage flows into the anoxic tank (DO≤0.5mg / L), and the denitrifying bacteria in the tank use the undecomposed carbon in the sewage The organic matter is the carbon so...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): C02F9/14C02F101/10C02F101/16
CPCC02F9/00C02F1/32C02F3/005C02F3/308C02F2101/105C02F2101/16
Inventor 姜云张俊杰
Owner 襄阳先创环保科技有限公司
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