CN108558146A - Process and device associated with organic matter advanced oxidation and electrolytic catalysis in a kind of high-salt wastewater - Google Patents

Process and device associated with organic matter advanced oxidation and electrolytic catalysis in a kind of high-salt wastewater Download PDF

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CN108558146A
CN108558146A CN201810612639.3A CN201810612639A CN108558146A CN 108558146 A CN108558146 A CN 108558146A CN 201810612639 A CN201810612639 A CN 201810612639A CN 108558146 A CN108558146 A CN 108558146A
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waste water
palladium
advanced oxidation
oxidation
catalytic
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向家勇
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Jiangsu Huda Chemical Technology Co Ltd
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Jiangsu Huda Chemical Technology Co Ltd
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/38Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
    • B01J23/40Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals of the platinum group metals
    • B01J23/44Palladium
    • B01J35/56
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • C02F1/04Treatment of water, waste water, or sewage by heating by distillation or evaporation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • C02F1/32Treatment of water, waste water, or sewage by irradiation with ultraviolet light
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/467Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
    • C02F1/4672Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electrooxydation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/722Oxidation by peroxides
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/78Treatment of water, waste water, or sewage by oxidation with ozone
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
    • C02F1/46109Electrodes
    • C02F2001/46133Electrodes characterised by the material
    • C02F2001/46138Electrodes comprising a substrate and a coating
    • C02F2001/46142Catalytic coating
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • C02F2101/345Phenols
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/08Chemical Oxygen Demand [COD]; Biological Oxygen Demand [BOD]
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/04Flow arrangements
    • C02F2301/046Recirculation with an external loop
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/08Multistage treatments, e.g. repetition of the same process step under different conditions
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/10Photocatalysts
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage

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  • Chemical & Material Sciences (AREA)
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  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
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Abstract

The invention discloses process and devices associated with organic matter advanced oxidation in a kind of high-salt wastewater and electrolytic catalysis, include the following steps:Industrial wastewater carries out oil removing, filtering by coarse filter, removes the suspended matter and colloidal substance in waste water;Industrial wastewater after coarse filtration is re-fed into advanced oxidation device, is passed through hydrogen peroxide and ozone, carries out advanced catalytic oxidation reaction;The waste water handled by advanced oxidation is then sent into catalytic and oxidative electrolysis technology device, under the action of catalyst filling, apply 5~24V voltages, and under ultraviolet light, carry out hardly degraded organic substance in electrolytic oxidation degrading waste water, by detecting the COD contents of waste water at sample outlet, when hit the target, is discharged;Waste water after catalytic and oxidative electrolysis technology is sent into crystallizing evaporator and is evaporated condensing crystallizing and recycles to obtain the Nacl of recycling;Waste water after evaporative condenser, which continues to be fed into, carries out biochemical treatment in biochemical device, discharged or recycled after meeting discharge standard.

Description

Process associated with organic matter advanced oxidation and electrolytic catalysis in a kind of high-salt wastewater And device
Technical field
The invention belongs to environmental protective chemical industry technical fields, more particularly to the processing equipment containing sodium phenolate waste water difficult to degrade and processing Method.
Background technology
As China's industry is grown rapidly, sewage discharge increasingly increases, and is largely difficult to biodegradable chemicals with waste water Form is discharged into environment, causes the serious pollution of water resource, has become the pain spot of social development and the hot spot of concern.Especially exist That is discharged in the industrial processes such as coking, petrochemical industry, printing and dyeing, pharmacy, organic synthesis is anhydrous containing a large amount of toxic organic compounds and height Concentration salt, such as sodium sulphate, sodium chloride, sodium nitrate, copper sulphate etc. so that can not be needed pair directly by biochemical treatment means After Nacl carries out Crystallization Separation in waste water, then biochemical treatment is carried out, to generate toxic industrial waste salt, can not accomplish industry Salt recycling treatment;Simultaneously because useless Organic substance in water contains such as formaldehyde, alcohols and difficult to degrade and high boiling phenolic material Matter, at present Conventional catalytic oxidation can not also be handled, and for brine waste, and the salt obtained by distillation crystallization is abraum salt, It can not recycling treatment.Oxidation means of the advanced oxidation as new development obtain extremely strong energy of oxidation by screening suitable catalyst The macromolecular debirs of high bond energy in water body are oxidized to degradable, hypotoxicity small molecule by the free radical of power, but it is catalyzed Agent and core process technology be all from external import, it is of high cost, be unfavorable for the development of domestic sewage disposal technology.
Invention content
Goal of the invention:For above-mentioned existing problem and shortage, the object of the present invention is to provide a kind of high-salt wastewaters Process unit and method associated with middle organic matter advanced oxidation and electrolytic catalysis.
Technical solution:In order to solve the above-mentioned technical problem, the present invention uses following technical scheme:Have in a kind of high-salt wastewater Processing method associated with machine object advanced oxidation and electrolytic catalysis, includes the following steps:
Step 1:Industrial wastewater carries out oil removing, filtering by coarse filter, removes the suspended matter and colloidal substance in waste water;
Step 2:Industrial wastewater after coarse filtration is re-fed into advanced oxidation device, is passed through hydrogen peroxide and ozone, and Under the action of catalyst filling, advanced catalytic oxidation reaction is carried out, the advanced oxidation device is the catalytic tower of plural serial stage, Catalyst filling is mounted in every grade of catalytic tower, and tower top is formed with bottom of tower by pipeline pump and is connected by circulation, and in tower Waste water carries out cycle catalysis oxidation;
Step 3:The waste water handled by advanced oxidation is then sent into catalytic and oxidative electrolysis technology device, in the work of catalyst filling Under, apply 5~24V voltages, and under ultraviolet light, carries out hardly degraded organic substance in electrolytic oxidation degrading waste water, pass through The COD contents of waste water at sample outlet are detected, when hit the target is discharged;
Step 4:Waste water after catalytic and oxidative electrolysis technology is sent into crystallizing evaporator and is evaporated condensing crystallizing and recycles To the Nacl of recycling;Waste water after evaporative condenser, which continues to be fed into, carries out biochemical treatment in biochemical device, meet discharge standard After discharged or recycled.
Preferably, the catalyst filling be using silica gel as carrier, carried metal palladium, iron or silver active component.
Preferably, active component is the oxide of Metal Palladium or/and iron in the catalyst.
Preferably, the load capacity of the oxide of the Metal Palladium or/and iron is 4~12%.
Preferably, the preparation method of the catalyst is as follows:
First, the sodium silicate solution of 20% mass concentration is prepared, be used in combination sodium hydroxide adjust pH value 12~13 it Between, formation obtains weighing solution;In addition palladium bichloride is dissolved in 20~30% dilute hydrochloric acid and obtains palladium chloride solution, then stirred It mixes down, which is slowly added to carry out hybrid reaction in sodium silicate solution, the hydroxide for obtaining silica gel and palladium is total The sediment of doping, during being somebody's turn to do, the mass ratio of sodium metasilicate and Metal Palladium is 10:0.5~1.2.
Then, ph values are adjusted in the range of 6-8, continue to keep aging reaction at least 2h or more, then will be sunk after aging Starch is filtered separation, and organic palladium catalyst is dried to obtain at 50~60 DEG C;
Then, by organic palladium catalyst and methyl cellulose binder according to 1:0.1~0.2 mass ratio is mixed, Honeycomb green body, and dry 24 or more are formed under mould action, green body liquid phase component content are reduced, when avoiding high-temperature roasting Chap and the surface layer oversintering for causing filling body, influence catalytic activity;
Finally, after carrying out 0.5~2h of roasting at a temperature of green body being placed in 400~600 DEG C, the catalysis of high-specific surface area is obtained Agent honeycomb filling body.
The present invention also provides process unit associated with organic matter advanced oxidation in a kind of high-salt wastewater and electrolytic catalysis, packets Include wastewater disposal basin, and connect with wastewater disposal basin successively by pipeline pump coarse filter, advanced oxidation device, tubular reactor, buffering Pond, evaporator, crystallization apparatus and centrifuge, the tubular reactor include inner tube, middle tube and outer tube, the middle tube The anode of power supply is connected as electrolytic anode, the surfaces externally and internally of the middle tube is coated with carbon nanotube loaded palladium metal oxidation Object coating, the inner tube and outer tube are separately connected power cathode, are equipped between the middle tube and inner tube and outer tube Catalyst filling.
Preferably, the carbon nanotube loaded palladium metal oxide coating preparation process of the middle tube surfaces externally and internally is such as Under:
Step 1:Titanium base is dried after oil removing, pickling successively spare;
Step 2:At 50~60 DEG C, carbon nanotube is immersed in chloroazotic acid carry out it is acidic activated after, with pure water to ph Then value is dried in 6-8;
Step 3:Then after tetra-triphenylphosphine palladium being dissolved in benzole soln, by 1:0.5~1.2 mass ratio is added step 2 and obtains To carbon nanotube, after being dispersed with stirring uniformly, brush several times in titanium-based surface, and dried at a temperature of 60~80 DEG C;
Step 4:The titanium-base of the carbon nanotube loaded palladium coating of drying is finally sintered 0.5 at 400~600 DEG C ~2h forms carbon nanotube loaded palladium oxide catalyst coatings in titanium-based plate surface.
Advantageous effect:Compared with prior art, the present invention has the following advantages:(1) by advanced oxidation to easy in waste water The organic matters such as degradation of organic substances such as formaldehyde, ethyl alcohol carry out efficiently quickly oxidation, while to difficult to degrade as phenolate carries out level-one oxygen Change;Into two level catalysis oxidation is continued in the light-catalysed tubular reactor of electrolytic catalysis-, organic removal rate in waste water can ensure that And efficiency, it is often more important that the dosage of active noble metals palladium substantially reduces in catalyst filling, reduces palladium number of dropouts and technique Catalyst cost;By honeycomb cellular silica gel load active metal oxidation catalyst, and energy under the conditions of catalytic and oxidative electrolysis technology Enough to carry out effectively degradation removal, especially hardly degraded organic substance your such as phenol to useless Organic substance in water, removal rate is more than 98%; It (2), effectively will be in waste water by using the catalyst filling block of honeycomb cellular active metal load silica gel as catalyst Debirs difficult to degrade carry out catalysis oxidation, to realize the biochemical treatment of high-salt wastewater organic matter, and acquire in recycling waste water Technical grade salt, realize industrial waste salt resource recycling utilize;(3) double-tube type catalytic and oxidative electrolysis technology is used, electrolysis is improved Catalytic efficiency can effectively improve the release of hydroxyl radical free radical using the Ti base anodes of carbon nanotube loaded Metal Palladium oxide covering Efficiency improves anode region oxidation operation removal efficiency.
Description of the drawings
Fig. 1 is the structure of process unit associated with organic matter advanced oxidation and electrolytic catalysis in high-salt wastewater of the present invention Schematic diagram.
Wherein, wastewater disposal basin 1, coarse filter 2, advanced oxidation device 3, tubular reactor 4, buffer pool 5, evaporator 6, crystallization dress Set 7, centrifuge 8.
Specific implementation mode
In the following with reference to the drawings and specific embodiments, the present invention is furture elucidated, it should be understood that these embodiments are merely to illustrate It the present invention rather than limits the scope of the invention, after having read the present invention, those skilled in the art are to of the invention each The modification of kind equivalent form falls within the application range as defined in the appended claims.
The preparation process of silicon substrate supported active palladium catalyst is as follows:
First, the sodium silicate solution of 20% mass concentration is prepared, be used in combination sodium hydroxide adjust pH value 12~13 it Between, formation obtains weighing solution;In addition palladium bichloride is dissolved in 20~30% dilute hydrochloric acid and obtains palladium chloride solution, then stirred It mixes down, which is slowly added to carry out hybrid reaction in sodium silicate solution, the hydroxide for obtaining silica gel and palladium is total The sediment of doping, during being somebody's turn to do, the mass ratio of sodium metasilicate and Metal Palladium is 10:2~2.5.
Then, ph values are adjusted in the range of 6-8, continue to keep aging reaction at least 2h or more, it is ensured that the hydrogen of Metal Palladium Oxide carries out being bonded load completely with silica gel during being co-deposited with silica gel, reduces Metal Palladium turnover rate.Then by aging Sediment is filtered separation afterwards, and organic palladium catalyst is dried to obtain at 50~60 DEG C;
Then, by organic palladium catalyst and methyl cellulose binder according to 1:0.1~0.2 mass ratio is mixed, Honeycomb green body is formed under mould action, and 24 or more drying avoids high-temperature roasting to reduce green body liquid phase component content The uneven oversintering of Shi Zaocheng filling bodies influences catalytic activity;
Finally, after carrying out 0.5~2h of roasting at a temperature of green body being placed in 400~600 DEG C, the catalysis of high-specific surface area is obtained Agent honeycomb filling body.
The preparation of electrolytic catalysis anode:
Step 1:Titanium base is dried after oil removing, pickling successively spare;
Step 2:At 50~60 DEG C, carbon nanotube is immersed in chloroazotic acid carry out it is acidic activated after, with pure water to ph Value is in 6-8, then drying for standby;
Step 3:Then after tetra-triphenylphosphine palladium being dissolved in benzole soln, by 1:0.7 mass ratio addition step 2 obtains carbon and receives Mitron after being dispersed with stirring uniformly, is uniformly brushed and is dried at a temperature of 60~80 DEG C after the pipe surface of titanium-based middle level;It repeats to brush and dry Dry step 3 time or more;
Step 4:The titanium-base of the carbon nanotube loaded palladium coating of drying is finally sintered 0.5 at 400~600 DEG C ~2h, in titanium-based middle level, pipe surface forms carbon nanotube loaded palladium oxide catalyst coatings.
As shown in Figure 1, high-salt wastewater organic matter catalytic and oxidative electrolysis technology treatment process device, including wastewater disposal basin, and pass through Coarse filter that pipeline pump is connect with wastewater disposal basin successively, advanced oxidation device, tubular reactor, buffer pool, evaporator, crystallization apparatus And centrifuge, the tubular reactor include inner tube, middle tube and outer tube, the positive conduct of the middle tube connection power supply The surfaces externally and internally of electrolytic anode, the middle tube is coated with carbon nanotube loaded palladium metal oxide coating, the inner tube It is separately connected power cathode with outer tube, catalyst filling is equipped between the middle tube and inner tube and outer tube.
When work, waste water, which is fed in by pipeline pump in tubular reactor, to be flowed, and electrolysis generation hydroxyl is powered certainly in 5~24V By carrying out oxidative degradation removal to useless Organic substance in water under base and catalytic filler effect.
Jiangxi petrochemical industry synthesis factory waste water is handled, waste water quality is as follows:Sodium sulphate salt content about 7%, COD contents For 224ppm, ammonia-nitrogen content is 4~5ppm, and sodium phenolate is 2~4%, the also cyanide containing 0.1~0.2ppm, by processing Afterwards, COD is down to 12ppm, removal rate 94% in waste water, and recycling obtains the sulfuric acid for meeting technical grade that impurity content is less than 1% Sodium salt.

Claims (7)

1. processing method associated with organic matter advanced oxidation and electrolytic catalysis in a kind of high-salt wastewater, it is characterised in that:Including with Lower step:
Step 1:Industrial wastewater carries out oil removing, filtering by coarse filter, removes the suspended matter and colloidal substance in waste water;
Step 2:Industrial wastewater after coarse filtration is re-fed into advanced oxidation device, is passed through hydrogen peroxide and ozone, and be catalyzed Under the action of agent filler, carry out advanced catalytic oxidation reaction, the advanced oxidation device be plural serial stage catalytic tower, every grade Catalyst filling is mounted in catalytic tower, and tower top is formed with bottom of tower by pipeline pump and is connected by circulation, and to waste water in tower Carry out cycle catalysis oxidation;
Step 3:The waste water handled by advanced oxidation is then sent into catalytic and oxidative electrolysis technology device, in the effect of catalyst filling Under, apply 5~24V voltages, and under ultraviolet light, carries out hardly degraded organic substance in electrolytic oxidation degrading waste water, pass through inspection The COD contents of waste water at sample outlet are surveyed, when hit the target is discharged;
Step 4:Waste water after catalytic and oxidative electrolysis technology, is sent into crystallizing evaporator to be evaporated condensing crystallizing and recycle and is provided The Nacl in source;Waste water after evaporative condenser, which continues to be fed into, carries out biochemical treatment in biochemical device, it is laggard to meet discharge standard Row discharge recycles.
2. processing method associated with organic matter advanced oxidation and electrolytic catalysis in high-salt wastewater according to claim 1, special Sign is:The catalyst filling be using silica gel as carrier, carried metal palladium, iron or silver active component.
3. processing method associated with organic matter advanced oxidation and electrolytic catalysis in high-salt wastewater according to claim 2, special Sign is:Active component is the oxide of Metal Palladium or/and iron in the catalyst.
4. processing method associated with organic matter advanced oxidation and electrolytic catalysis in high-salt wastewater according to claim 3, special Sign is:The load capacity of the oxide of the Metal Palladium or/and iron is 4~12%.
5. processing method associated with organic matter advanced oxidation and electrolytic catalysis in high-salt wastewater according to claim 4, special Sign is:The preparation method of the catalyst is as follows:
First, the sodium silicate solution of 20% mass concentration is prepared, is used in combination sodium hydroxide to adjust pH value between 12~13, shape At obtaining weighing solution;In addition palladium bichloride is dissolved in 20~30% dilute hydrochloric acid and obtains palladium chloride solution, then under stiring, The palladium chloride solution is slowly added to carry out hybrid reaction in sodium silicate solution, obtains the hydroxide codope of silica gel and palladium Sediment, during being somebody's turn to do, the mass ratio of sodium metasilicate and Metal Palladium is 10:0.5~1.2.
Then, ph values are adjusted in the range of 6-8, continue to keep aging reaction at least 2h or more, then by sediment after aging It is filtered separation, and is dried to obtain organic palladium catalyst at 50~60 DEG C;
Then, by organic palladium catalyst and methyl cellulose binder according to 1:0.1~0.2 mass ratio is mixed, in mould Honeycomb green body, and dry 24 or more are formed under tool effect, are reduced green body liquid phase component content, are avoided causing when high-temperature roasting The chap of filling body and surface layer oversintering, influence catalytic activity;
Finally, after carrying out 0.5~2h of roasting at a temperature of green body being placed in 400~600 DEG C, the catalyst bee of high-specific surface area is obtained Nest filling body.
6. process unit associated with organic matter advanced oxidation and electrolytic catalysis in a kind of high-salt wastewater, it is characterised in that:Including useless Pond, and connect with wastewater disposal basin successively by pipeline pump coarse filter, advanced oxidation device, tubular reactor, buffer pool, steaming Device, crystallization apparatus and centrifuge are sent out, the tubular reactor includes inner tube, middle tube and outer tube, the middle tube connection The anode of power supply is coated with carbon nanotube loaded palladium metal oxide and applies as electrolytic anode, the surfaces externally and internally of the middle tube Layer, the inner tube and outer tube are separately connected power cathode, and catalysis is equipped between the middle tube and inner tube and outer tube Agent filler.
7. high-salt wastewater organic matter electrolytic catalysis couples advanced oxidation processing unit according to claim 6, it is characterised in that: The carbon nanotube loaded palladium metal oxide coating preparation process of the middle tube surfaces externally and internally is as follows:
Step 1:Titanium base is dried after oil removing, pickling successively spare;
Step 2:At 50~60 DEG C, carbon nanotube is immersed in chloroazotic acid carry out it is acidic activated after, existed with pure water to ph values Then 6-8 is dried;
Step 3:Then after tetra-triphenylphosphine palladium being dissolved in benzole soln, by 1:0.5~1.2 mass ratio is added step 2 and obtains carbon Nanotube is brushed in titanium-based surface, and dried at a temperature of 60~80 DEG C several times after being dispersed with stirring uniformly;
Step 4:The titanium-base of the carbon nanotube loaded palladium coating of drying is finally sintered 0.5 at 400~600 DEG C~ 2h forms carbon nanotube loaded palladium oxide catalyst coatings in titanium-based plate surface.
CN201810612639.3A 2018-06-13 2018-06-13 Process and device associated with organic matter advanced oxidation and electrolytic catalysis in a kind of high-salt wastewater Pending CN108558146A (en)

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Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109550771A (en) * 2018-12-11 2019-04-02 中化环境控股有限公司 The minimizing technology and removal device of organic pollutant in industrial waste salt
CN110117115A (en) * 2019-06-05 2019-08-13 南京大学盐城环保技术与工程研究院 A kind of processing method and equipment of industrial waste salt recycling
CN113336485A (en) * 2021-05-27 2021-09-03 中节能元泰(山东)环保科技有限公司 Pretreatment technology of acidic organic waste
CN113754149A (en) * 2021-09-28 2021-12-07 天津工业大学 Spherical porous filler and electrolytic oxidation system for treating organic matters in high-salt water
CN114314772A (en) * 2022-01-07 2022-04-12 万华化学集团股份有限公司 Resource utilization process of salt residues in beta-aminopropionic acid production
CN114455762A (en) * 2021-11-29 2022-05-10 成都硕特科技股份有限公司 Wastewater treatment system and application thereof in wastewater treatment in battery anode material production
CN116924596A (en) * 2023-05-30 2023-10-24 深圳市新西林园林景观有限公司 Electrochemical device for sponge urban sewage treatment and treatment method thereof

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