Multipoint water-in sludge in-situ reduction synchronous coupling nitrogen and phosphorus removal method
A synchronous coupling, denitrification and dephosphorization technology, applied in the direction of water/sludge/sewage treatment, water pollutants, biological sludge treatment, etc., can solve the problem that sludge cannot be reduced in situ, so as to reduce infrastructure investment and improve Effect of Nitrogen and Phosphorus Removal Efficiency
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[0021] Example 1
[0022] Step 1, the raw sewage enters the anaerobic tank 2 and the anoxic tank 3 respectively according to the volume distribution ratio of 5:5. The raw sewage CODCr concentration, TN concentration, NH3-N concentration, TP concentration, water temperature, anaerobic tank 2 and anoxic The HRT of pool 3 was determined to be 396mg / L, 36mg / L, 34mg / L, 3mg / L, 28°C, 1.89h, 0.94h, respectively;
[0023] Step 2, the aerobic tank 4 receives the mud-water mixture discharged from the anaerobic tank 2 and the anoxic tank 3, and the HRT, DO concentration and temperature of the aerobic tank 4 are determined to be 1.85h, 2mg / L and 28°C respectively;
[0024] Step 3, the mud-water mixture discharged from the aerobic tank 4 enters the sedimentation tank 5 and the anoxic tank 3 respectively according to the volume distribution ratio of 1:2.5, and the sedimentation time of the sedimentation tank 5 is determined to be 1h;
[0025] In step 4, after the separation of mud and water...
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[0028] Example 2
[0029] Step 1, the raw sewage enters the anaerobic tank 2 and the anoxic tank 3 respectively according to the volume distribution ratio of 5:5. The raw sewage CODCr concentration, TN concentration, NH3-N concentration, TP concentration, water temperature, anaerobic tank 2 and anoxic The HRT of pool 3 was determined to be 512mg / L, 64mg / L, 52mg / L, 9mg / L, 28°C, 1.89h, 0.94h, respectively;
[0030] Step 2, the aerobic tank 4 receives the mud-water mixture discharged from the anaerobic tank 2 and the anoxic tank 3, and the HRT, DO concentration and temperature of the aerobic tank 4 are determined to be 1.85h, 2mg / L and 28°C respectively;
[0031] Step 3, the mud-water mixture discharged from the aerobic tank 4 enters the sedimentation tank 5 and the anoxic tank 3 respectively according to the volume distribution ratio of 1:2.5, and the sedimentation time of the sedimentation tank 5 is determined to be 1h;
[0032] In step 4, after the separation of mud and water...
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