Catalytic ozonation and Fenton-like coupling reactor and method for treating toxic refractory wastewater

A wastewater treatment and ozonation technology, which is applied in the directions of oxidized water/sewage treatment, mining wastewater treatment, chemical instruments and methods, etc., can solve the problems of increasing equipment cost, small gas-liquid contact area, disadvantageous wastewater treatment cost, etc., to reduce the cost of wastewater treatment. The cost of wastewater treatment, the effect of increasing the gas-liquid contact area, and improving the efficiency of wastewater treatment

Active Publication Date: 2016-06-22
SICHUAN UNIV
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Problems solved by technology

But this type of device still has the following disadvantages: (1) the energy consumption of rotating the reactor or the packing drum is high, resulting in high operating costs; (2) although the rotating can make the packing turn over, it cannot make the packing in the whole reactor. In a fully fluidized state, the mass transfer efficiency is limited, which is not conducive to the improvement of wastewater treatment efficiency
In addition, the usual Fenton-like reactor needs to add a large amount of acid to maintain a high pollutant removal efficiency, which will also increase the operating cost of the Fenton-like reactor
[0004] Existing catalytic ozonation reactors mainly use the aeration head to introduce ozone into the wastewater, such as the ozone catalytic oxidation water treatment device disclosed in CN104150578A, the bubbles produced by aeration are usually large, and the excessive diameter of the bubbles directly causes The gas-liquid contact area is too small, resulting in a very low utilization rate of ozone in the reactor, and the existing catalytic ozonation reactor does not have the function of ozone recycling. In order to avoid ozone pollution to the environment, a large amount of unused ozone After coming out of the reactor, it needs to be treated with ozone removal
The low utilization rate of ozone not only affects the effect and efficiency of wastewater treatment, but also causes a large consumption of total ozone, increases the cost of wastewater treatment, and causes the cost of ozone removal to be too high
In addition, ozone will corrode and destroy the commonly used rubber-type microporous aerator heads, requiring the use of more expensive titanium alloy aerator heads, which will increase the cost of equipment and is not conducive to the reduction of wastewater treatment costs

Method used

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  • Catalytic ozonation and Fenton-like coupling reactor and method for treating toxic refractory wastewater
  • Catalytic ozonation and Fenton-like coupling reactor and method for treating toxic refractory wastewater

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Embodiment 1

[0033] Embodiment 1: Catalytic ozonation-Fenton-like coupling reactor

[0034] In this embodiment, the structure of the catalytic ozonation-like Fenton coupling reactor is as follows figure 1 As shown, it includes a reaction tank 1, an ozone generator 2, a residual ozone removal device 3, an ejector 4, an inlet pump 5, a return pump 6, a waste water return pipe 7, an outlet pipe 8, an ozone gas supply pipe 9, and an ozone delivery pipe 10 , Ozone return pipe 11, residual ozone discharge pipe 12 and gas flow meter 13.

[0035] The reaction tank 1 is composed of a cylindrical body with a closed lower end and an open upper end and a gas collecting hood 14 provided at the opening end of the cylindrical body. The reaction tank 1 is equipped with micron-sized iron-copper bimetallic particles, and the cylindrical body of the reaction tank is closed. The inner surface of the end is provided with a cone 15 with an upward apex, the cone angle θ of the cone is 160°, the ratio of the dia...

Embodiment 2

[0039] Embodiment 2: Catalytic ozonation-Fenton-like coupling reactor

[0040] In this embodiment, the structure of the catalytic ozonation-Fenton-like coupling reactor is basically the same as that of the catalytic oxidation-Fenton-like coupling reactor in Example 1, the difference is that the reaction tank 1 is equipped with micron zero Valence iron particles; the cone angle θ of the cone 15 arranged in the reaction tank is 120 °, and the ratio of the diameter d of the bottom surface of the cone to the diameter D of the reaction tank is 0.7; there are 7 circulating water inlets, and each circulating water inlet is uniform Distributed at the same height position of the cylinder and the angle α between the center line of each circulating water inlet and the tangent of the cylinder at the position is 5°; the length l of the vertical pipe 8-2 of the outlet pipe is 80cm.

Embodiment 3

[0041] Embodiment 3: catalytic ozonation-Fenton-like coupling reactor

[0042] In this embodiment, the structure of the catalytic ozonation-Fenton-like coupling reactor is basically the same as that of the catalytic oxidation-Fenton-like coupling reactor in Example 1, the difference is that the reaction tank 1 is equipped with micron iron Nickel bimetallic particles; the cone angle θ of the cone 15 provided in the reaction tank is 45°, and the ratio of the diameter d of the bottom surface of the cone to the diameter D of the reaction tank is 0.3; there are 5 circulating water inlets, each circulating water inlet Evenly distributed at the same height position of the cylinder and the angle α between the center line of each circulating water inlet and the tangent of the cylinder at the position is 30°; the length l of the vertical pipe 8-2 of the outlet pipe is 50cm .

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Abstract

The invention provides a catalytic ozonation and Fenton-like coupling reactor which comprises a reaction tank, an ozone generator, a residual ozone removal device, a jet device, a water inlet pump, a backflow pump, wastewater backflow pipes, a water outlet pipe, ozone gas supply pipes, an ozone delivery pipe, ozone backflow pipes, a residual ozone exhaust pipe and gas flow meters.The invention further provides a method for treating toxic refractory wastewater.The method is implemented by the aid of the reactor, and includes continuously filling the jet device with the to-be-treated wastewater and ozone; mixing the to-be-treated wastewater and the ozone with each other in the jet device to obtain a mixture and feeding the mixture into the reaction tank; starting the backflow pump to allow micron-grade iron-based catalytic materials in the reaction tank to be in fluidization states; continuously draining treated wastewater out of the reaction tank; delivering the ozone in a gas collecting hood into the ozone delivery pipe to be recycled and delivering the ozone into the residual ozone removal device to be treated.The catalytic ozonation and Fenton-like coupling reactor and the method have the advantages that the wastewater treatment efficiency can be effectively improved under the synergistic effects of catalytic ozonation and Fenton-like reaction, and the wastewater treatment cost can be effectively reduced under the synergistic effects of catalytic ozonation and Fenton-like reaction.

Description

technical field [0001] The invention belongs to the field of toxic and refractory wastewater treatment, in particular to a catalytic ozonation-Fenton-like coupled reactor and a treatment method for toxic and refractory wastewater. Background technique [0002] Fenton-like method and catalytic ozonation method are common methods for pretreatment or advanced treatment of toxic and refractory wastewater. The Fenton-like method refers to the transformation of zero-valent iron and iron-based multimetallic materials into O 2 reduced to H 2 o 2 , then at Fe 2+ Under the catalytic action of catalysis, strong oxidative OH is generated in situ, and OH can non-selectively and quickly mineralize toxic and refractory pollutants, or decompose and transform toxic and refractory pollutants into small molecules that are easy to biochemically treat, improving Biodegradability of wastewater. Catalytic ozonation mainly utilizes transition metal ions or oxides, such as MnO 2 、TiO 2 、Al 2...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): C02F1/72C02F1/78C02F103/06C02F103/10
CPCC02F1/72C02F1/725C02F1/78C02F2103/06C02F2103/10C02F2103/343
Inventor 赖波
Owner SICHUAN UNIV
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