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

Inactive Publication Date: 2014-04-09
珠海市德莱环保科技有限公司
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

[0003] At present, domestic and foreign papermaking wastewater treatment methods mainly include physicochemical (sedimentation, air flotation, etc.), biochemical treatment (anaerobic, hydrolysis, aerobic, etc.), advanced treatment (Fenton advanced oxidation, air flotation advanced treatment, etc.), etc., Various treatment methods and process combinations have their own advantages and disadvantages, but it is difficult to achieve a certain efficiency, and it is difficult to achieve the emission target after treatment in a broad spectrum, effectively and economically.
Due to the existence of a large number of difficult-to-degrade components contained in papermaking wastewater, the biochemical efficiency is not high, and the COD of the effluent cr Unable to meet the emission standards, many companies have adopted subsequent advanced treatment processes, such as Fenton treatment. Fenton treatment is a treatment process that degrades refractory pollutants in water bodies by adding ferrous iron and hydrogen peroxide to form a strong oxidant. The effect is good, but its operating cost is high, the amount of sludge generated is large, and the requirements for equipment operation and management are relatively high. The most troublesome thing for the company is its high operating cost. Under the low profit of paper companies, This kind of treatment is very difficult for enterprises to survive

Method used

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Examples

Experimental program
Comparison scheme
Effect test

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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PUM

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Abstract

The invention aims to provide a strong oxidant for papermaking waste water CODcr degradation and a method for degrading CODcr in waste water, wherein the requirements on equipment operation and management are low, the equipment operating cost is low, the processing treatment efficiency is high, and secondary pollution can be prevented. The strong oxidant comprises the following components in parts by weight: 1 part of potassium permanganate, 10-60 parts of aluminum sulfate, 10-50 parts of ferric sulfate, and 10-50 parts of aluminum polychlorid. The method for degrading CODcr in waste water by utilizing the strong oxidant comprises the following steps: dissolving the strong oxidant in water in a proportion of 1: (5-20), then feeding in a coagulating basin for waste water treatment so as to carry out oxidation treatment, controlling the stirring speed at 50-100 rpm during the process and the reaction time to be 15-60 min, then feeding polyacrylamide as an auxiliary to complete the process of oxidation separation, and keeping the control time of the oxidant after dissolution within 1-12 hours. The strong oxidant and the method can be applied to the field of papermaking waste water treatment.

Description

technical field [0001] The invention relates to a papermaking wastewater COD cr Strong oxidizing agent for degradation and its effect on COD in wastewater cr The method of degradation treatment. Background technique [0002] With the process of world economy and industrialization, the discharge of industrial water and wastewater is gradually increasing, but the living environment of human beings is changing with the process of industrialization and the discharge of wastewater, and the living environment is getting worse and worse. Emissions have developed a relatively stringent emission standards. As a part of the industrialization process, papermaking has undoubtedly caused part of the environmental damage due to its huge water consumption and drainage. Papermaking wastewater accounts for about one-third of the country's total discharge, and its COD cr The emissions also accounted for one-third, in this case, the treatment of papermaking wastewater is even more importan...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): C02F1/72C02F1/56C02F103/28
Inventor 孙立金杨巧邹亮
Owner 珠海市德莱环保科技有限公司
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