Method for cutting down adverse effects of nano material on sewage biological denitrification and phosphorus removal system
A nanomaterial, sewage biological technology, applied in water/sewage treatment, chemical instruments and methods, biological water/sewage treatment, etc., can solve the problems of changing the characteristics of nanomaterials, affecting the application scope of nanomaterials, etc., to achieve easy operation, reduce Adverse effects, effects with significant reduction effects
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Embodiment 1
[0023] (1) The sewage containing nano-zinc oxide to be treated has a COD of 180 mg / L, a TN of 32 mg / L, and a TP of 9.0 mg / L. After being treated by a biological treatment system, the effluent COD is 85 mg / L , TN is 17 mg / L, TP is 19 mg / L;
[0024] (2) Kitchen waste (suspended solids, SS concentration is about 18,000 mg / L) was anaerobically fermented at a temperature of 30 °C and a pH of 9.0 for 6 days, and the concentration of propionic acid (calculated as COD) in the obtained fermentation solution was 1,580 mg / L, the protein concentration (calculated as COD) is 1450 mg / L;
[0025] (3) Add the solution produced by fermentation into the sewage to be treated, so that the concentration of propionic acid in the sewage after adding the fermentation solution is 90 mg / L, and the protein concentration is 75 mg / L;
[0026] (4) After biological treatment of the sewage to be treated, the effluent COD is 80 mg / L, TN is 6.5 mg / L, and TP is 3.5 mg / L; the reduction rates of the adverse eff...
Embodiment 2
[0028] (1) The sewage containing nano-zinc oxide to be treated has a COD of 120 mg / L, a TN of 40 mg / L, and a TP of 8.0 mg / L. After being treated by a biological treatment system, the effluent COD is 65 mg / L , TN is 21 mg / L, TP is 18 mg / L;
[0029] (2) Kitchen waste (SS concentration is about 13,800 mg / L) was anaerobically fermented at a temperature of 50°C and a pH of 11.0 for 8 days, and the concentration of propionic acid (calculated as COD) in the obtained fermentation solution was 1,260 mg / L. The protein concentration (calculated as COD) is 1780 mg / L;
[0030] (3) Add the solution produced by fermentation to the sewage to be treated, so that the concentration of propionic acid in the sewage after adding the fermentation solution is 70 mg / L, and the concentration of protein is 80 mg / L;
[0031] (4) After biological treatment of the sewage to be treated, the effluent COD is 90 mg / L, TN is 8.7 mg / L, and TP is 3.0 mg / L; the reduction rates of the adverse effects of nanomateri...
Embodiment 3
[0033] (1) The COD of the sewage containing nano-silver to be treated is 160 mg / L, TN is 36 mg / L, and TP is 12 mg / L. After being treated by the biological treatment system, the effluent COD is 80 mg / L. TN is 18 mg / L, TP is 25 mg / L;
[0034] (2) The excess sludge (SS concentration is about 19,500 mg / L) from the sewage plant was anaerobically fermented at 45°C and pH 9.0 for 8 days, and the concentration of propionic acid (calculated as COD) in the resulting solution was 1820 mg / L L, the protein concentration (in terms of COD) is 2950 mg / L;
[0035] (3) Add the solution produced by fermentation to the sewage to be treated, so that the concentration of propionic acid in the sewage after adding the fermentation solution is 65 mg / L, and the protein concentration is 70 mg / L;
[0036] (4) After the sewage to be treated is biologically treated, the effluent COD is 85 mg / L, TN is 6.0 mg / L, and TP is 5.0 mg / L; the reduction rates of the adverse effects of nanomaterials on phosphorus re...
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