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Method for controlling photo-Fenton processing efficiency through low molecular weight organic acid combination

A low-molecular-weight, high-efficiency technology, applied in the direction of light water/sewage treatment, energy wastewater treatment, chemical instruments and methods, etc., can solve the problems of unusable sewage treatment, etc., achieve great application potential, no secondary pollution, and reduce inhibition The effect of action

Inactive Publication Date: 2015-08-19
DONGHUA UNIV
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

Therefore, in practical applications, if the content of malonic acid is high, it will not be possible to use the light-Fenton method for sewage treatment

Method used

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  • Method for controlling photo-Fenton processing efficiency through low molecular weight organic acid combination
  • Method for controlling photo-Fenton processing efficiency through low molecular weight organic acid combination
  • Method for controlling photo-Fenton processing efficiency through low molecular weight organic acid combination

Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0015] Take five reaction vessels, add 10 μmol / L rhodamine B, 1000 μmol / L malonic acid and 100 μmol / L ferric dye wastewater to each of them, add 0 μmol / L oxalic acid to reaction vessel 1, and add 10 μmol / L oxalic acid, add 100 μmol / L oxalic acid to reaction vessel 3, add 500 μmol / L oxalic acid to reaction vessel 4, add 1000 μmol / L oxalic acid to reaction vessel 5, and adjust the pH of the solution in the reaction vessel to 3. The reaction results are shown in Table 1 below:

[0016] Table 1 Rhodamine B degradation effect under different oxalic acid concentrations

[0017]

[0018] When there is no external low molecular weight organic acid, malonic acid can react with ferric iron, thereby inhibiting the degradation of rhodamine B. Table 1 shows that when oxalic acid is not added, the removal rate of Rhodamine B within 30 min is 0. When oxalic acid was added, the removal rate of rhodamine B changed significantly, and with the increase of oxalic acid concentration, the remo...

Embodiment 2

[0020] Take five reaction vessels, add 10 μmol / L rhodamine B, 1000 μmol / L malonic acid and 100 μmol / L ferric dye wastewater to each of them, add 0 μmol / L citric acid to reaction vessel 1, and add 0 μmol / L citric acid to reaction vessel 2 Add 10 μmol / L citric acid, add 100 μmol / L citric acid to reaction vessel 3, add 500 μmol / L citric acid to reaction vessel 4, add 1000 μmol / L citric acid to reaction vessel 5, and adjust the pH of the solution in the reaction vessel for 3. The reaction results are shown in Table 2 below:

[0021] Table 2 Rhodamine B degradation effect under different citric acid concentrations

[0022]

[0023] When there is no external low molecular weight organic acid, malonic acid can react with ferric iron, thereby inhibiting the degradation of rhodamine B. Table 2 shows that when citric acid is not added, the removal rate of Rhodamine B within 30min is 0. When citric acid was added, the removal rate of rhodamine B changed, and with the increase of ci...

Embodiment 3

[0025] Take five reaction vessels, add 10 μmol / L rhodamine B, 1000 μmol / L malonic acid and 100 μmol / L ferric dye wastewater to each of them, add 0 μmol / L tartaric acid to reaction vessel 1, and add 10 μmol / L tartaric acid, add 100 μmol / L tartaric acid in reaction vessel 3, add 500 μmol / L tartaric acid in reaction vessel 4, add 1000 μmol / L tartaric acid in reaction vessel 5, the solution pH in the reaction vessel is all adjusted to 3. The reaction results are shown in Table 3 below:

[0026] Table 3 Rhodamine B degradation effect under different tartaric acid concentrations

[0027]

[0028] When there is no external low molecular weight organic acid, malonic acid can react with ferric iron, thereby inhibiting the degradation of rhodamine B. Table 3 shows that when tartaric acid is not added, the removal rate of Rhodamine B within 30min is 0. When tartaric acid was added, the removal rate of rhodamine B changed, and with the increase of tartaric acid concentration, the rem...

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Abstract

The invention relates to a method for controlling photo-Fenton processing efficiency through low molecular weight organic acid combination. The method includes adding malonic acid and ferric iron into organic waste water, adjusting the pH, adding other low molecular weight organic acid with the molar ratio of 1:1 to 100 :1 with the malonic acid into the organic waste water, simulating sunlight irradiation, and reacting on the room temperature conditions finally. The method is implemented at normal temperature and pressure and has the advantages of simpleness, convenience for operation, environment protection and secondary pollution elimination, the malonic acid photo-Fenton method inhibiting effect can be reduced, the removing effect of organic compounds, heavy metals and other pollutants in water can be improved, and the large application potential is provided in the field of sewage treatment.

Description

technical field [0001] The invention belongs to the field of sewage treatment, and in particular relates to a method for regulating and controlling light-Fenton treatment efficiency by combining low-molecular-weight organic acids. Background technique [0002] In recent years, the photo-Fenton method has attracted people's attention as an efficient advanced oxidation technology. Because it can generate hydroxyl radicals (redox potential 1.8-2.7V) during the reaction process, it can oxidatively degrade most refractory Organic pollutants, in addition, can also produce ferrous iron, thereby reducing heavy metals in wastewater. It has developed into a new technology for treating refractory organic wastewater and heavy metal wastewater. The pure photo-Fenton system (Fe(III) / UV) has low quantum yield and is easily affected by organic matter. Although some organic acids will increase the efficiency, there are also some organic acids that will reduce the photo-Fenton efficiency. Th...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): C02F1/30C02F1/66C02F1/72C02F101/20C02F101/30
CPCY02W10/37
Inventor 肖冬雪王兆慧柳建设方长玲娄晓祎周骏黄颖刘文乾孙林燕
Owner DONGHUA UNIV