Method and system for denitrifying low-carbon high-nitrogen sewage by utilizing plant carbon source-enhanced artificial wetland
A constructed wetland, low-carbon and high-nitrogen technology, applied in chemical instruments and methods, biological water/sewage treatment, water/sludge/sewage treatment, etc. Nitrification denitrification effect is good, the extraction method is simple, and the effect of strong carbon release ability
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Embodiment 1
[0047] This embodiment provides a system that uses plant carbon sources to strengthen constructed wetlands to denitrify low-carbon and high-nitrogen sewage. The main structure is shown in the attached figure 1 shown, with figure 1 Among them, 1 is the hydrolyzate release pool, 2 is the main pipe for carbon source supplementation, 3 is the branch pipe for carbon source supplementation, 4 is the wetland plant, and 5 is the matrix.
[0048] The constructed wetland system is located in a certain area of Huizhou City, with a utilization and treatment scale of 500 m 3 / d's combined constructed wetland is used for advanced treatment of the tail water of the low-carbon and high-nitrogen sewage treatment plant. The processing steps are as follows:
[0049] S1. Soaking the plant material in the soaking solution and hydrolyzing it to obtain a hydrolyzed solution;
[0050] S2. Adding the hydrolyzate obtained in S1 to the constructed wetland;
[0051] S3. The hydrolyzate added to the...
Embodiment 2
[0059] This embodiment provides a system for denitrifying low-carbon and high-nitrogen sewage by utilizing plant carbon sources to strengthen constructed wetlands, the main structure of which is the same as that of Embodiment 1.
[0060] The constructed wetland system is located in a certain area of Huizhou City, with a utilization and treatment scale of 500 m 3 / d's combined constructed wetland is used for advanced treatment of urban river sewage with low carbon, high nitrogen and high concentration of ammonia nitrogen. The processing steps are as follows:
[0061] S1. Soaking the plant material in the soaking solution and hydrolyzing it to obtain a hydrolyzed solution;
[0062] S2. Adding the hydrolyzate obtained in S1 to the constructed wetland;
[0063] S3. The hydrolyzate added to the constructed wetland decomposes to release low-molecular-weight organic matter that can be used by denitrifying bacteria, and strengthens the denitrification of low-carbon and high-nitrog...
Embodiment 3
[0071] Others are the same as Example 2, except that the solid-to-liquid ratio is 1:30.
[0072]The operation mode of the constructed wetland adopts intermittent water intake, and the water intake pipes are evenly distributed on the surface of the constructed wetland, and the water intake is 12 hours, and the interval is 12 hours. Hydraulic load according to 1.0 m 3 / (m 2 d) run.
[0073] The concentration of CODcr in the influent is about 20 mg / L. After supplementing the hydrolyzate, the concentration of CODcr in the influent can reach 65.5 mg / L, the concentration of TN is 10.2-14.8 mg / L, and the concentration of NO 3 - -N2.9~9.2 mg / L, NH 4 + -N 3~8.1 mg / L.
[0074] The experimental results show that at this time, the flow rate of the hydrolyzate is controlled according to Example 2, and the plant hydrolyzate is added to adjust the C / N to only about 6. When the hydraulic load is 1.0 m / d, all indicators can achieve a good removal effect: TN The removal rate can be as hi...
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