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a for sewage treatment 2 o Nitrogen and phosphorus removal device and method

A sewage treatment method, nitrogen and phosphorus removal technology, applied in the field of water treatment, can solve the problems of interfering with the phosphorus release reaction in the anaerobic stage, affecting the phosphorus removal efficiency, and unable to completely solve the contradiction of sludge age, so as to reduce energy consumption and achieve high dephosphorization The effect of nitrogen rate

Active Publication Date: 2022-08-02
CHINA CONSTR THIRD BUREAU GREEN IND INVESTMENT CO LTD
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

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Problems solved by technology

For example, CN201820609692.3 is an anaerobic-anoxic-aerobic biological denitrification and phosphorus removal device. This process cannot completely solve the contradiction between denitrification and phosphorus removal. Sludge concentration, that is, through the combination of activated sludge and biofilm to improve nitrogen removal efficiency; but for phosphorus removal, sludge return will introduce nitrate into the anaerobic tank, which interferes with the phosphorus release reaction in the anaerobic section and affects phosphorus removal efficiency

Method used

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  • a for sewage treatment  <sup>2</sup> o Nitrogen and phosphorus removal device and method
  • a for sewage treatment  <sup>2</sup> o Nitrogen and phosphorus removal device and method
  • a for sewage treatment  <sup>2</sup> o Nitrogen and phosphorus removal device and method

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Embodiment 1

[0053] refer to figure 1 , the embodiment of the present invention provides a kind of A for sewage treatment 2 O denitrification and phosphorus removal method, comprising the following steps:

[0054] S1: The sewage with 80% of the incoming water flow enters the pre-anoxic zone in the anaerobic tank, and the anaerobic reaction is carried out in the anaerobic tank, so that the organic nitrogen in the sewage is converted into ammonia nitrogen, and phosphorus is released in the anaerobic stage;

[0055] S2: discharging the anaerobic treated sewage in step S1 into the aerobic tank A to provide conditions for the obligate aerobic phosphorus accumulating bacteria to over-absorb the dissolved phosphorus, and at the same time use the nitrifying bacteria supplemented by the sedimentation tank B to carry out nitrification;

[0056] S3: the sewage after the nitrification treatment in step S2 is discharged into the sedimentation tank A, and the sewage is in the sedimentation tank A to co...

Embodiment 2

[0066] Similar to Example 1, the difference is that: the sectional water inflow is 90% in the anaerobic section and 10% in the anoxic section, the return ratio of phosphorus removal sludge in sedimentation tank A is Ra = 80%, and the sludge concentration in the anoxic tank is X = 5g / L control, the mixed liquid reflux ratio in aerobic tank B is controlled according to Ri=50%, and the ratio of sludge return from sedimentation tank B to aerobic tank A and anoxic tank is Rb1=20% and Rb2=30%, respectively. The number of days for controlling the sludge age of each section is as follows: the sludge age of phosphorus accumulating bacteria in the anaerobic and aerobic section is controlled by 5 days, and the sludge age of denitrification and nitrification bacteria in the anoxic and aerobic section is controlled by 15 days.

[0067] The method of this example can remove 90% of phosphorus through the anaerobic and aerobic system in the previous stage; because the aeration of the aerobic t...

Embodiment 3

[0069] Similar to Example 1, the difference is that: the sectional water inflow is 90% in the anaerobic section and 10% in the anoxic section, the return ratio of phosphorus removal sludge in sedimentation tank A is Ra = 80%, and the sludge concentration in the anoxic tank is X = 5g / L control, the mixed liquid reflux ratio in aerobic tank B is controlled according to Ri=50%, and the ratio of sludge return from sedimentation tank B to aerobic tank A and anoxic tank is Rb1=40% and Rb2=60%, respectively. The number of days for controlling the sludge age of each section is as follows: the sludge age of phosphorus accumulating bacteria in the anaerobic and aerobic section is controlled by 5 days, and the sludge age of denitrification and nitrification bacteria in the anoxic and aerobic section is controlled by 15 days.

[0070] The method of this example can remove 90% of phosphorus through the anaerobic and aerobic system in the previous stage; because the aeration of the aerobic t...

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Abstract

The present invention provides a kind of A for sewage treatment 2 A device and method for denitrifying and dephosphorizing O, the device includes an anaerobic tank, an aerobic tank A, a sedimentation tank A, an anoxic tank, an aerobic tank B and a sedimentation tank B which are connected in sequence and supply sewage to flow through, wherein the anaerobic tank is The inside of the tank is provided with a pre-anoxic zone for sewage to enter first; the sludge in the sedimentation tank A is returned to the anaerobic tank; the sludge in the sedimentation tank B is returned to the anoxic tank and the aerobic tank A respectively. The invention adopts two sets of precipitation and reflux systems to remove nitrogen in the incoming water by nitrification and denitrification, and uses the biological phosphorus removal method of releasing phosphorus and taking up phosphorus to remove phosphorus, and realizes the full utilization of carbon sources by means of sectional water inflow. , the device can control the sludge age of denitrification and phosphorus removal respectively, so as to achieve the purpose of efficient denitrification and phosphorus removal.

Description

technical field [0001] The invention relates to the technical field of water treatment, in particular to a kind of A 2 O denitrification and phosphorus removal device and method. Background technique [0002] In the process of urban municipal sewage treatment, denitrification and phosphorus removal affect each other. Nitrogen removal requires lower load and longer mud age, while phosphorus removal requires higher load and shorter mud age. Denitrification requires more nitrate for denitrification, and nitrate is not conducive to phosphorus removal. The requirements for sludge age, sludge load and aerobic residence time are opposite for nitrogen and phosphorus removal. Urban sewage plants usually focus on the removal of total nitrogen, and the removal of total phosphorus is largely accomplished by dosing. Therefore, how to simultaneously improve the removal rate of total nitrogen and total phosphorus in domestic sewage is one of the key issues in current urban sewage treatm...

Claims

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Application Information

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Patent Type & Authority Patents(China)
IPC IPC(8): C02F9/14
CPCC02F3/308C02F1/52C02F2203/006C02F2301/046C02F2301/08C02F2209/08C02F2209/14C02F2209/16C02F2209/44
Inventor 夏云峰霍培书汤丁丁赵皇秦雄周艳刘军龚杰黄文海
Owner CHINA CONSTR THIRD BUREAU GREEN IND INVESTMENT CO LTD