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Fenton-like oxidation device for waste resin and oxidation method of device

An oxidation device and waste resin technology, applied in chemical instruments and methods, water treatment of special compounds, water/sludge/sewage treatment, etc., to achieve the effects of simple process flow, low treatment cost and high degradation effect

Inactive Publication Date: 2020-02-07
JIANGSU ZHONGHAI HUA HE ENVIRONMENTAL PROTECTION CO LTD
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

The method waste resin and catalyst Fe 2+ with Mn 2+ or Co 2+ The mixed solution is stirred in the reaction vessel at the same time, the pH of the solution is adjusted, oxygen or aeration is introduced, and the reaction is carried out under the condition of electrification, and H is added dropwise to the reactor according to the reaction rate of the reaction system. 2 o 2 solution, waste resin is oxidatively degraded, the operating conditions are mild, and the waste resin does not need to be pretreated before the reaction, the waste resin is completely decomposed without secondary pollution, and the decomposition residue is filtered through the nanofiltration membrane, which is economically feasible and the nuclides contained in the resin It is almost completely enriched in the decomposition residue and residue and does not contain any radioactive nuclides in the gas phase. The whole reaction system has a good treatment effect on waste resin, high reactivity, high oxidation efficiency, mild reaction conditions, low catalyst price, and oxidant Environmentally friendly, low reaction temperature, high safety, good application prospects, solve the problem of secondary pollutants treatment to a certain extent, in order to achieve this purpose, the present invention provides a waste resin Fenton oxidation device, including Reactor shell, cathode plate, anode plate, aeration device, constant current power supply device, stirring device, reaction rate test device, filtration module, temperature indicator and controller, water outlet 1 and water outlet 2, water body detection port 1 and water body detection port 2, waste material export, waste resin import, pH adjustment port, catalyst addition port and H 2 o 2 Inlet, the cathode plate and the anode plate are alternately discharged in the reactor shell, and the reaction compartment is formed between the adjacent cathode plate and the anode plate, and the cathode plate and the anode plate are connected to the constant current power supply device through the connection line, The reactor shell is connected to a temperature indicator and a controller through a connection line, and there is a row of stirring devices at the bottom of the reactor shell, and the stirring device is magnetic stirring, and the top of the reactor shell has a pH adjustment port, Catalyst addition port and H 2 o 2 import, the H 2 o 2 Import to H 2 o 2 Inlet and reaction rate test feedback system, one end of the reaction rate test device extends into the reactor shell, the aeration part of the aeration device extends below the cathode plate and the anode plate in the reactor shell, and the reactor shell There is a waste resin inlet on one side of the bottom of the reactor shell. There are two filter compartments on one side of the reaction compartment of the reactor shell. The two filter chambers respectively have a water body detection port 1 and a water body detection port 2. The water body detection port 1 There is a filter module between the water body detection port 2, there is a water outlet 1 below the water body detection port 1, there is a water outlet 2 below the water body detection port 2, and there is a residue outlet at the bottom of the reactor shell

Method used

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  • Fenton-like oxidation device for waste resin and oxidation method of device
  • Fenton-like oxidation device for waste resin and oxidation method of device

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Effect test

Embodiment 1

[0036] The treated waste resin is an ion exchange resin with a water content of 40wt%-60wt%.

[0037] This invention handles the device of waste resin class Fenton oxidation method such as figure 2 As shown, the device includes a reactor shell 19, a cathode plate 2, an anode plate 3, an aeration device 15, a constant current power supply device 1, a stirring device 6, a reaction rate testing device 11, a filter module 12, a temperature indicator and a control Device 4, water outlet one 17 and water outlet two 18, water body detection port one 13 and water body detection port two 14, waste material outlet 16, waste resin import 5, pH adjustment port 7, catalyst addition port 8 and H 2 o 2 Inlet 9, the cathode plate 2 and the anode plate 3 are alternately arranged in the reactor shell 19, and a reaction compartment is formed between the adjacent cathode plate 2 and the anode plate 3, and the cathode plate 2 and the anode plate 3 The constant current power supply device 1 is c...

Embodiment 2

[0054] Embodiment 2: adopt different catalyst

[0055] The catalyst in the above mixed system is selected as Fe 2+ and Co 2+ mixed catalyst.

[0056] The temperature and pH value of the reaction system are consistent, and the reaction is carried out in a device-like Fenton reactor to complete the degradation of the ion exchange resin. After the reaction is completed, the COD value of the reaction system is measured, and the raffinate and filter residue are solidified with cement.

[0057] It can be seen that when Mn 2+ When the catalyst exists, the reaction rate of the system is greater than that of Co 2+ , which may be due to the fact that Mn has more chemical valence states, thus favoring H 2 o2 decomposition. And Mn 3+ The standard reduction potential of Mn is higher, therefore, Mn 3+ Can accept electrons to convert to Mn 2+ Than Co 3+ faster.

Embodiment 3

[0058] Embodiment 3: the selection of reaction system pH

[0059] Through the pH adjustment port, the pH in the system is adjusted to 2 or 5 to complete the degradation of the ion exchange resin. After the reaction is completed, the COD value of the reaction system is measured, and the raffinate and filter residue are solidified with cement.

[0060] It can be seen that when the pH is controlled at 3, the COD value of the reaction system at the same time point is lower; in comparison, when the pH is controlled at 2 or 5, the COD value is higher. Therefore, it is recommended to control the pH of the reaction system to 3.

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Abstract

The invention provides a Fenton-like oxidation method for waste resin. The method comprises the following steps: 1) mixing the radioactive waste resin having water generated in nuclear industry and acomposite catalyst, adding a certain amount of Na2SO4, and performing full stirring; and 2) controlling the reaction temperature and pH, introducing oxygen or performing aeration, adding H2O2 with a certain concentration by mass through valve control, and performing rapid degradation on the waste resin under the energization condition to make the organic components of the waste resin inorganic, wherein the catalyst is a mixture of Fe<2+> and Mn<2+> or Co<2+>. By using the oxidation method and device provided by the invention, the oxidative degradation efficiency of the waste resin can be improved in a shorter reaction time, the use amount of H2O2 during the treatment can be reduced, and the generation rate of an oxidant during the treatment can be improved; and the method has the advantages of a simple process, high efficiency and low production costs.

Description

technical field [0001] The invention relates to the technical field of nuclear power plant waste treatment and devices thereof, in particular to a waste resin Fenton oxidation device and an oxidation method thereof. Background technique [0002] One use of ion exchange resins (IERs) is the removal of radioactive contaminants (neutron activation and fission products leaked from fuel elements) from the purge water of nuclear facilities. As important low-level radioactive waste (LLW), used IERs are used to absorb 90 Sr, 137 Cs, 235 U, 238 U and other elements. Technologies used to treat and dispose of radioactive waste resins include immobilization (e.g. cementation, asphalt and plastic curing), advanced oxidation processes (e.g. incineration, pyrolysis, acid digestion, Fenton or Fenton-like reactions, supercritical water), plasma techniques and super compact. There are also some other methods such as pickling, microbial conversion treatment and high integrity container m...

Claims

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Application Information

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IPC IPC(8): C02F9/08C02F101/30
CPCC02F1/302C02F1/32C02F1/442C02F1/66C02F1/722C02F7/00C02F9/00C02F2101/006C02F2101/30C02F2305/026
Inventor 岳仁亮周宏宇冯丽华郑继龙宋平
Owner JIANGSU ZHONGHAI HUA HE ENVIRONMENTAL PROTECTION CO LTD
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