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Nano catalytic electrolysis flocculation device

A technology of electrolytic flocculation and nanocatalysis, which is applied in chemical instruments and methods, water treatment of special compounds, special treatment targets, etc., can solve problems such as high energy consumption, high overpotential, and channeling, and achieve high electrocatalytic activity, The effect of reducing the impact

Inactive Publication Date: 2011-04-13
BOYING XIAMEN SCI & TECH
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

However, some problems have been exposed during the operation of the existing electrolysis device. One is that after a period of operation of the fixed packing micro-electrolysis treatment device, the packing is easy to agglomerate and channeling occurs, which greatly reduces the treatment effect; Although the fluidized bed solves the problem of agglomeration, in order to ensure a fluidized state, the filler needs to be continuously circulated, the power consumption is large, and the filler is easy to lose
The existing electrolysis device also exposed some problems during the operation process. First, the electrode consumption is large, and the electrode material pollutes the water body; The third is that after electrolysis, the solid-liquid separation effect is not ideal, and a second solid-liquid separation is required, and the process is long

Method used

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Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0062] Treatment effect on fresh water purification and disinfection

[0063] Pump fresh water into the nano catalytic electrolysis flocculation device for electrolysis, the voltage between the two electrodes is 5-8V, and the electrolysis density is 10-200mA / cm 2 The catalytic electrolysis machine keeps the residence time of fresh water in the nano-catalytic electrolytic flocculation device at 0.5-1min, and the electricity consumption of fresh water electrolysis is controlled at 0.009-0.010 degrees / m 3 . The effects before and after treatment are shown in Table 1 (indices of untreated fresh water) and Table 2 (indices of fresh water treated by nanocatalytic electrolytic flocculation device).

[0064] Table 1

[0065] serial number

project

index

serial number

project

index

1

smelly and smelly

No smell

5

COD (mg / L)

9

[0066] 2

pH

6.9

6

Ammonia nitrogen (mg / L)

0.5

3

...

Embodiment 2

[0070] The treatment effect on the purification and disinfection of seawater

[0071] Pump seawater into the nano-catalytic electrolysis flocculation device for electrolysis, the voltage between the two electrodes is 3-5V, and the electrolysis density is 10-260mA / cm 2 The catalytic electrolysis machine keeps the residence time of seawater in the nano-catalytic electrolysis flocculation device at 0.5-1min, and the electricity consumption of seawater electrolysis is controlled at 0.003-0.004 degrees / m 3 . The effects before and after treatment are shown in Table 3 (indices of untreated seawater) and Table 4 (indices of seawater after purification and disinfection treatment by nanocatalytic electrolysis device).

[0072] table 3

[0073] serial number

[0074] Table 4

[0075] serial number

[0076] 1

Embodiment 3

[0078] Treatment effect on printing and dyeing advanced treatment wastewater

[0079] The printing and dyeing advanced treatment wastewater from the secondary sedimentation tank treated by A / O flows into the nano-catalyzed electrolytic flocculation device for electrolysis, the voltage between the two electrodes is 3-6V, and the electrolysis density is 10-300mA / cm 2 Catalytic electrolysis, keeping the residence time of wastewater in the nano-catalytic electrolytic flocculation device is 2-5 minutes, and the electricity consumption of wastewater electrolysis is controlled at 0.8-1.0 degrees / m 3 . The effects before and after treatment are shown in Table 5 (indices of comprehensive printing and dyeing wastewater in the untreated mixing pool) and Table 6 (indices of printing and dyeing wastewater after nanocatalytic electrolysis treatment).

[0080] table 5

[0081] serial number

project

unit

measured value

serial number

project

unit

measured...

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Abstract

The invention discloses a nano catalytic electrolysis flocculation device, relating to an electrolysis flocculation device. The nano catalytic electrolysis flocculation device has the advantages of extremely low working voltage between two adjacent electrodes, large current density, small energy consumption, high electrical efficiency and no electrode consumption and electrolysis, and integrates solid-liquid separation function and gas-liquid separation function. The bottom of a shell is provided with a water inlet; the shell is internally provided with a scum baffle and a watertight shutter; the scum baffle and one inner side of the shell form a water discharging chamber; a gap is reserved between the bottom of the scum baffle and the bottom of the shell; the scum baffle and the other inner side of the shell form a slag discharging chamber; a gap is reserved between the top of the watertight shutter and the top of the shell; a hydrogen exhaust port is arranged on the top of the shell; an electrolyzer is arranged between the scum baffle and the watertight shutter; the top of the electrolyzer is open and the gap is reserved between the top of the electrolyzer and the top of the shell; electrodes are installed in the electrolyzer; a gas-liquid separation chamber is formed in the shell on the upper part of the electrolyzer; and a drain outlet is arranged at the bottom of the shell and us positioned between the watertight shutter and the adjacent electrolyzer.

Description

technical field [0001] The invention relates to an electrolytic flocculation device, in particular to a nano-catalytic electrolytic flocculation device with a titanium electrode covered with a nano-catalytic material as an anode. Background technique [0002] At present, chemical methods and biochemical methods are mostly used for sterilization and purification of water and wastewater, and a large amount of chemical agents need to be added and a large amount of sludge is generated during the treatment process. For example, in the production of tap water, chlorine or sodium hypochlorite is mostly used to disinfect the water body, followed by flocculation, sedimentation and filtration. In wastewater treatment, flocculants are usually added for flocculation reaction, followed by sedimentation or air flotation separation, and then biochemical treatment. Although this treatment method can play a certain role, there are disadvantages such as high operating cost, large amount of s...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): C02F1/463
CPCC02F1/463C02F1/465C02F1/4672C02F2001/46133C02F2001/46142C02F2001/46157C02F2103/24C02F1/4674C02F2301/028C02F2303/04C02F2305/023C02F2305/08C02F2001/46171C02F2101/101C02F2101/16C02F2101/308C02F2201/46135C02F2201/4614C02F2303/24
Inventor 潘美平张世文庹孝军
Owner BOYING XIAMEN SCI & TECH
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