CN109513439A - A kind of catalyst for waste water debirs advanced oxidation degradation - Google Patents

A kind of catalyst for waste water debirs advanced oxidation degradation Download PDF

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Publication number
CN109513439A
CN109513439A CN201810607904.9A CN201810607904A CN109513439A CN 109513439 A CN109513439 A CN 109513439A CN 201810607904 A CN201810607904 A CN 201810607904A CN 109513439 A CN109513439 A CN 109513439A
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China
Prior art keywords
solution
catalyst
waste water
debirs
sediment
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CN201810607904.9A
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Chinese (zh)
Inventor
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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Priority to CN201810607904.9A priority Critical patent/CN109513439A/en
Publication of CN109513439A publication Critical patent/CN109513439A/en
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    • 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
    • B01J23/54Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/56Platinum group metals
    • B01J23/58Platinum group metals with alkali- or alkaline earth metals
    • 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
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/89Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals
    • B01J23/8933Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals also combined with metals, or metal oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/8946Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals also combined with metals, or metal oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with alkali or alkaline earth metals
    • B01J35/56
    • 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
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • C02F2101/345Phenols

Abstract

The invention discloses a kind of catalyst for waste water debirs advanced oxidation degradation, preparation method includes: range of the sodium silicate solution by sulfuric acid or sodium hydroxide adjusting pH value in 12-13, formation clear solution;Soluble metal salt solution is mixed with sodium silicate solution, carries out neutralization-precipitation reaction, generation obtains the doping sediment of silica gel and metal hydroxides, then the pH value for adjusting mixed liquor by dilute sulfuric acid keeps mixing to continue aging reaction in 6-8;Sediment after reaction aging is separated by filtration and is dried, then the adhesive mixing of sediment 5-12% mass is added, and after being squeezed by mold and forming the body drying of honeycomb, is roasted at a temperature of 400~600 DEG C, obtain the catalyst monolith filling body of high specific area.The present invention efficiently can carry out catalysis oxidation to such as phenol of hardly degraded organic substance in waste water etc., recycle the salt in brine waste.

Description

A kind of catalyst for waste water debirs advanced oxidation degradation
Technical field
The invention belongs to the catalyst for catalytic oxidation of hardly degraded organic substance in technical field of environmental protection in chemical industry more particularly to waste water And preparation method thereof.
Background technique
As China's industry is grown rapidly, sewage discharge increasingly increases, and is difficult to biodegradable chemicals largely 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 discharges 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. need pair so that can not directly pass through 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 be abraum salt by the salt that distillation crystallization obtains for brine waste, 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 bond energy high 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 at high cost, be unfavorable for the development of domestic sewage disposal technology.
Summary of the invention
Goal of the invention: being directed to above-mentioned existing problem and shortage, and the object of the present invention is to provide one kind to be used for waste water The catalyst of debirs advanced oxidation degradation efficiently can carry out catalysis oxygen to such as phenol of hardly degraded organic substance in waste water etc. Change, recycles the salt in brine waste.
Technical solution: in order to solve the above-mentioned technical problem, the invention adopts the following technical scheme: a kind of organic for waste water The catalyst of waste advanced oxidation degradation, preparation method includes the following steps:
Step 1: raw material is prepared:
(1) it weighs sodium metasilicate and is dissolved in pure water, obtain the sodium silicate solution of 15-25% mass percentage concentration, and pass through Sulfuric acid or sodium hydroxide adjust pH value in the range of 12-13, form clear solution, spare;
(2) soluble metal salt solution with catalytic activity is chosen
Salt, and soluble metal salt solution is prepared by being dissolved in acid, it is spare;
(3) methylcellulose, hydroxybutyl cellulose, hydroxyethylmethylcellulose, hydroxypropyl cellulose or hydroxypropyl are selected from The adhesive of methylcellulose and its a variety of mixtures;
Step 2: soluble metal salt solution is mixed with sodium silicate solution, is carried out neutralization-precipitation reaction, is generated To the doping sediment of silica gel and metal hydroxides, then the pH value for adjusting mixed liquor by dilute sulfuric acid keeps mixing in 6-8 Continue aging reaction;
Step 3: the sediment after reaction aging is separated by filtration and is dried, and sediment 5-12% is then added The adhesive of quality mixes, and the green body to form honeycomb is squeezed by mold, and green body is by at least above for 24 hours drying;
Step 4: the green body that step 3 obtains is roasted at a temperature of 400~600 DEG C, obtains urging for high specific area Agent honeycomb filling body.
Preferably, the soluble metal salt solution is hydrochloric acid solution, palladium nitrate solution, the ferric chloride solution of palladium chloride Or the first in silver nitrate solution or a variety of mixing.
Preferably, the soluble metal salt solution is the solution that tetra-triphenylphosphine palladium is dissolved in ethyl alcohol or benzene, preferably benzene Solution.
Preferably, the mass ratio of sodium metasilicate and soluble metal salt solution is in step 2 in terms of active metal quality 10:1~4.
Preferably, the mass ratio of sodium metasilicate and soluble metal salt solution is in step 2 in terms of active metal quality 10:2~2.5.
Specific embodiment
Combined with specific embodiments below, the present invention is furture elucidated, it should be understood that these embodiments are merely to illustrate the present invention Rather than limit the scope of the invention, after the present invention has been read, those skilled in the art are to various equivalences of the invention The modification of form falls within the application range as defined in the appended claims.
Embodiment 1
Firstly, the sodium silicate solution of 20% mass concentration is prepared, and with sodium hydroxide adjust pH value 12~13 it Between, formation obtains weighing solution;Then tetra-triphenylphosphine palladium is dissolved in 1:1 ethanol water obtain mass concentration 10~ 20% organic palladium solution then under stiring is slowly added to the organic palladium solution to carry out hybrid reaction in sodium silicate solution, The sediment of silica gel Yu Metal Palladium hydroxide codope is obtained, during being somebody's turn to do, the mass ratio of sodium metasilicate and Metal Palladium is 10:2.
Then, ph value is adjusted in the range of 6-8, continues to keep aging reaction at least 2h or more, then by filtering point From, and organic palladium catalyst is dried to obtain at 50~80 DEG C;Then organic palladium catalyst is pressed with methyl cellulose binder It is mixed according to the mass ratio of 1:0.1~0.5, forms honeycomb green body, and dry 24 or more under mould action, reduce base Body fluid phase component content avoids the chap for causing filling body when high-temperature roasting and surface layer oversintering, influences catalytic activity.Finally, After carrying out 0.5~2h of roasting at a temperature of green body is placed in 400~600 DEG C, the catalyst monolith filling body of high-specific surface area is obtained.
Embodiment 2
Firstly, the sodium silicate solution of 20% mass concentration is prepared, and with sodium hydroxide adjust pH value 12~13 it Between, formation obtains weighing solution;In addition palladium chloride 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 10:2.5.
Then, ph value is adjusted in the range of 6-8, continues to keep aging reaction at least 2h or more, to ensure that Metal Palladium exists Load and uniformly bonding are consolidated in silica-gel carrier, the loss of Metal Palladium in catalytic reaction process are reduced, to improve catalyst The tolerance of catalytic activity, especially catalyst.
Then sediment after aging is filtered separation, and is dried to obtain organic palladium catalyst at 50~60 DEG C;It connects Organic palladium catalyst is mixed with methyl cellulose binder according to the mass ratio of 1:0.2, formed under mould action Honeycomb green body, and dry 24 or more, green body liquid phase component content is reduced, the chap for causing filling body when high-temperature roasting is avoided With surface layer oversintering, catalytic activity is influenced.Finally, being obtained after carrying out 0.5~2h of roasting at a temperature of green body is placed in 400~600 DEG C To the catalyst monolith filling body of high-specific surface area.
Embodiment 3
Firstly, the sodium silicate solution of 20% mass concentration is prepared, and with sodium hydroxide adjust pH value 12~13 it Between, formation obtains weighing solution;In addition the dilute hydrochloric acid that palladium chloride and iron chloride are dissolved in 20~30% according to the mass ratio of 2:1 is weighed In obtain the mixed solution of palladium chloride and iron chloride, then under stiring, by mixed solution be slowly added in sodium silicate solution into Row hybrid reaction obtains the sediment of the hydroxide codope of silica gel and palladium and iron, should during, sodium metasilicate and Metal Palladium and The mass ratio of iron is 10:2:1.
Then, adjust ph value in the range of 6-8, continue keep aging reaction at least 2h or more, with ensure Metal Palladium and Iron firm load in silica-gel carrier is bonded with uniform, and active metal is in catalytic reaction process in reduction catalytic reaction process It is lost, to improve the catalytic activity of catalyst, the especially tolerance of catalyst.
Then sediment after aging is filtered separation, and is dried to obtain organic palladium catalyst at 50~60 DEG C;It connects Organic palladium catalyst is mixed with methyl cellulose binder according to the mass ratio of 1:0.2, formed under mould action Honeycomb green body, and dry 24 or more, green body liquid phase component content is reduced, the chap for causing filling body when high-temperature roasting is avoided With surface layer oversintering, catalytic activity is influenced.Finally, being obtained after carrying out 0.5~2h of roasting at a temperature of green body is placed in 400~600 DEG C To the catalyst monolith filling body of high-specific surface area.
It is handled for Jiangxi petrochemical industry synthesis factory's waste water, the water quality of waste water is as follows: sodium sulphate salt content about 7%, COD Content is 224ppm, and ammonia-nitrogen content is 4~5ppm, and sodium phenolate is 2~4%, also containing the cyanide of 0.1~0.2ppm.With solid Fixed bed catalytic tower loads above-described embodiment catalyst as wastewater treatment reaction tower in reaction tower, and with ozone and dioxygen After water carries out catalysis oxidation as strong oxidizer, it is re-fed into waste water after biochemical device carries out biochemical treatment and is evaporated crystallization recycling Technical grade sulfuric acid sodium is obtained, it is the wastewater treatment rear impurity content of each embodiment below that liquid phase water, which meets discharge standard:
Sodium phenolate COD Ammonia-nitrogen content Cyanide Sodium sulfate salt
Embodiment 1 <5ppm 18ppm <1ppm 0 It is colourless, technical grade
Embodiment 2 <5ppm 12ppm <1ppm 0 It is colourless, technical grade
Embodiment 3 <5ppm 27ppm <1ppm 0 It is colourless, technical grade
And in the prior art, the hardly degraded organic substances such as sodium phenolate can not degrade, and further across biochemical treatment, and COD Content is still higher, and multistep treatment is needed to can be only achieved discharge standard.

Claims (5)

1. a kind of catalyst for waste water debirs advanced oxidation degradation, preparation method includes the following steps:
Step 1: raw material is prepared:
(1) it weighs sodium metasilicate and is dissolved in pure water, obtain the sodium silicate solution of 15-25% mass percentage concentration, and pass through sulfuric acid Or sodium hydroxide adjusts pH value in the range of 12-13, forms clear solution, it is spare;
(2) soluble metal salt solution with catalytic activity is chosen
Salt, and soluble metal salt solution is prepared by being dissolved in acid, it is spare;
(3) methylcellulose, hydroxybutyl cellulose, hydroxyethylmethylcellulose, hydroxypropyl cellulose or hydroxypropyl methyl are selected from The adhesive of cellulose and its a variety of mixtures;
Step 2: soluble metal salt solution is mixed with sodium silicate solution, carries out neutralization-precipitation reaction, and generation obtains silicon Then the doping sediment of glue and metal hydroxides, the pH value for adjusting mixed liquor by dilute sulfuric acid keep mixing to continue in 6-8 Aging reaction;
Step 3: the sediment after reaction aging is separated by filtration and is dried, and sediment 5-12% mass is then added Adhesive mixing, and the green body to form honeycomb is squeezed by mold, green body by least for 24 hours more than drying;
Step 4: the green body that step 3 obtains is roasted at a temperature of 400~600 DEG C, obtains the catalyst of high specific area Honeycomb filling body.
2. according to claim 1 be used for waste water debirs advanced oxidation degradation catalyst, it is characterised in that: it is described can Solube metallic salting liquid be the first in the hydrochloric acid solution of palladium chloride, palladium nitrate solution, ferric chloride solution or silver nitrate solution or A variety of mixing.
3. according to claim 1 be used for waste water debirs advanced oxidation degradation catalyst, it is characterised in that: it is described can Solube metallic salting liquid is the solution that tetra-triphenylphosphine palladium is dissolved in ethyl alcohol or benzene, preferably benzole soln.
4. being used for the catalyst of waste water debirs advanced oxidation degradation according to Claims 2 or 3, it is characterised in that: with Active metal quality meter, the mass ratio of sodium metasilicate and soluble metal salt solution is 10:1~4 in step 2.
5. being used for the catalyst of waste water debirs advanced oxidation degradation according to claim 4, it is characterised in that: with activity Metallic meter, the mass ratio of sodium metasilicate and soluble metal salt solution is 10:2~2.5 in step 2.
CN201810607904.9A 2018-06-13 2018-06-13 A kind of catalyst for waste water debirs advanced oxidation degradation Pending CN109513439A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113151693A (en) * 2020-12-03 2021-07-23 贵研铂业股份有限公司 Method for recovering palladium from tetrakis (triphenylphosphine) palladium waste liquid

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002096079A (en) * 2000-09-25 2002-04-02 Sumitomo Heavy Ind Ltd Method for processing waste water, method for regenerating adsorbent and waste water processing facility
CN101219371A (en) * 2007-01-08 2008-07-16 北京化工大学 Photocatalysis oxidation treated high concentration organic trade waste
CN103157474A (en) * 2011-12-09 2013-06-19 华东理工大学 Supported solid catalyst for heterogeneous Fenton system
CN103977757A (en) * 2014-06-05 2014-08-13 安徽理工大学 Preparation method of organic waste water adsorption degrading agent
CN104588111A (en) * 2014-12-24 2015-05-06 东华大学 Preparation method and application of silicon oxide/palladium hybridized material with surface grafted with ionic liquid
CN105688912A (en) * 2016-03-18 2016-06-22 博天环境集团股份有限公司 Preparation method of honeycomb-like ozone oxidation catalyst and catalyst prepared through same

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002096079A (en) * 2000-09-25 2002-04-02 Sumitomo Heavy Ind Ltd Method for processing waste water, method for regenerating adsorbent and waste water processing facility
CN101219371A (en) * 2007-01-08 2008-07-16 北京化工大学 Photocatalysis oxidation treated high concentration organic trade waste
CN103157474A (en) * 2011-12-09 2013-06-19 华东理工大学 Supported solid catalyst for heterogeneous Fenton system
CN103977757A (en) * 2014-06-05 2014-08-13 安徽理工大学 Preparation method of organic waste water adsorption degrading agent
CN104588111A (en) * 2014-12-24 2015-05-06 东华大学 Preparation method and application of silicon oxide/palladium hybridized material with surface grafted with ionic liquid
CN105688912A (en) * 2016-03-18 2016-06-22 博天环境集团股份有限公司 Preparation method of honeycomb-like ozone oxidation catalyst and catalyst prepared through same

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
王基铭等: "《石油化工技术进展》", 30 April 2002, 中国石化出版社 *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113151693A (en) * 2020-12-03 2021-07-23 贵研铂业股份有限公司 Method for recovering palladium from tetrakis (triphenylphosphine) palladium waste liquid

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