Strong oxidant for papermaking waste water CODcr degradation and method for degrading CODcr in waste water
A technology for strong oxidant and papermaking wastewater, which is applied in oxidation water/sewage treatment, processing wastewater treatment, flocculation/sedimentation water/sewage treatment, etc. It can solve the problems of difficult discharge targets, high operating costs, and low biochemical efficiency. To achieve the effect of simple control of operating conditions, reduction of CODcr, and increase of compactness
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Embodiment 1
[0035] Embodiment one: The strong oxidizing agent is applied to the advanced treatment of papermaking white water
[0036] The white water (biochemical effluent) water samples of three paper mills were taken respectively, and the COD was 75mg / L for 1# sample, 62mg / L for 2# sample, and 69mg / L for 3# sample. To reduce COD.
[0037] Calculated in parts by mass, with the quality of 1 part of potassium permanganate as a standard, aluminum sulfate, ferric sulfate, and polyaluminum chloride are used to compound the raw materials in a ratio of 1:60:50:50 to obtain the strong oxidant, Then, the prepared strong oxidizing agent is dissolved according to a ratio of 1:10 to obtain a solution, and three 1L beakers are taken for a coagulation experiment, and the dosing amount is accurately measured by a pipette, according to the solid mass g and the waste water volume L The ratio is 1:2.5, the reaction speed is controlled at 60 rpm, and the stirring time is 20 minutes. After that, polyacry...
Embodiment 2
[0039] Embodiment two: The strong oxidizing agent is applied to the advanced treatment of papermaking deinking wastewater
[0040] The biochemical effluent water samples of three deinking paper mills were taken respectively. The COD of the 1# sample was 159mg / L, the 2# sample was 189mg / L, and the 3# sample was 218mg / L. In this embodiment, COD is reduced by adding the strong oxidant.
[0041] Calculated in parts by mass, with the quality of 1 part of potassium permanganate as the standard, aluminum sulfate, ferric sulfate, and polyaluminum chloride are used to compound the raw materials in a ratio of 1:10:10:10 to obtain the strong oxidizing agent. Then, the prepared strong oxidizing agent is dissolved according to a ratio of 1:10 to prepare a solution. Take three 1L beakers for coagulation experiment, and accurately measure the dosage by pipette. According to the ratio of solid mass g to waste water volume L is 1:1.5; 1:1 and 1:0.8, the reaction speed is controlled at 60 r...
Embodiment 3
[0043] Embodiment three: The strong oxidizing agent is applied to the advanced treatment of papermaking packaging paper wastewater
[0044] The biochemical effluent water samples from three paper mills producing packaging paper were taken respectively. The COD of the 1# sample was 05mg / L, the 2# sample was 148mg / L, and the 3# sample was 137mg / L. In this embodiment, COD is reduced by adding the strong oxidant.
[0045] Calculated in parts by mass, with the quality of 1 part of potassium permanganate as the standard, aluminum sulfate, ferric sulfate, and polyaluminum chloride are used to compound the raw materials in a ratio of 1:20:20:30 to obtain the strong oxidizing agent. Then, the prepared strong oxidizing agent is dissolved according to a ratio of 1:10 to prepare a solution. Take three 1L beakers for coagulation experiment, and accurately measure the dosage by pipette. Dosing according to the ratio of solid mass g to wastewater volume L is 1:2; 1:1.5 and 1:1.5, control...
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