MBR wastewater treatment system with deep denitrification and dephosphorization functions
A sewage treatment system and deep denitrification technology, applied in the field of MBR sewage treatment system, can solve the problems of high energy consumption of aerobic MBR operation and release of total nitrogen, so as to avoid the increase of effluent TN, alleviate slow membrane pollution, and improve the quality of effluent Effect
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[0032] Example 1
[0033] Such as figure 1 The system shown includes the anaerobic tank 1, the front anoxic tank 2, the aerobic tank 3, the rear anoxic tank 4 and the membrane tank 5 connected in sequence, and the anaerobic tank 1, the front anoxic tank 2 and the post anoxic tank A stirring device 6 is respectively arranged in the tank 4, an aeration device 7 is arranged in the aerobic tank 3, and a membrane assembly device 8 is arranged in the membrane tank 5.
[0034] The membrane unit 8 realizes horizontal reciprocating movement by setting the tie rod connected with the membrane unit and the motor 9. The reciprocating movement of the membrane unit can alleviate membrane pollution and avoid installing aeration device in the membrane tank 5, thereby reducing the dissolution in the membrane tank. Oxygen concentration.
[0035] Membrane tank 5 and anaerobic tank 1 are provided with 1# sludge mixed liquid return pipe 10, and the 1# sludge mixed liquid return pipe 10 is provided with ...
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[0043] Example 2
[0044] During operation, the influent COD concentration is 150~200mg / L, the TN concentration is 30~35mg / L, the TP concentration is 3~5mg / L, the ammonia nitrogen concentration is about 30mg / L, and the TP concentration reaches 10mg / L, a small amount of nitrate nitrogen returned by the membrane tank is also removed by denitrification. The front anoxic tank is used as the main denitrification and denitrification unit. The carbon source in the raw sewage and the nitrate nitrogen returned from the back anoxic tank are removed under the action of denitrifying bacteria. The nitrate in the front anoxic tank can be ensured by controlling the return flow. Nitrogen is sufficient to ensure full utilization of the original sewage carbon source. Then the mixed liquid enters the aerobic unit, the dissolved oxygen concentration of the aerobic pool can reach 0.5mg / L, the nitrifying bacteria use oxygen to completely oxidize the ammonia nitrogen in the raw sewage to nitrate nitro...
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[0045] Example 3
[0046] The influent COD concentration is 150~200mg / L, the TN concentration is 30~35mg / L, the TP concentration is 3~5mg / L, the ammonia nitrogen concentration is about 30mg / L, the sewage passes through the anaerobic, pre-anoxic and aerobic unit After the action, the concentration of nitrate nitrogen flowing into the post anoxic tank is about 5~7mg / L. In order to achieve a higher effluent water quality goal, the external carbon source dosing pump of the post anoxic tank is turned on to control the reasonable dosage and further denitrification. The effect is to remove the nitrate nitrogen in the back anoxic tank and increase the backflow flow of the back anoxic tank to the front anoxic tank to ensure the nitrate nitrogen concentration in the front anoxic tank. The removal concentration of TN of each biochemical unit is 1~2, 16~18, 0~1, 11~13, 2~3mg / L, and the removal amount of ΔTN is about 35mg / L, and the TN removal load of the post anoxic tank increases Up to 30~...
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