CN106582711A - Wastewater precipitation and purification method - Google Patents

Wastewater precipitation and purification method Download PDF

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Publication number
CN106582711A
CN106582711A CN201611049112.1A CN201611049112A CN106582711A CN 106582711 A CN106582711 A CN 106582711A CN 201611049112 A CN201611049112 A CN 201611049112A CN 106582711 A CN106582711 A CN 106582711A
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CN
China
Prior art keywords
catalyst
reaction tank
wastewater
mixed liquid
settlement
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Withdrawn
Application number
CN201611049112.1A
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Chinese (zh)
Inventor
张春花
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Nanning Heivr Information Technology Co Ltd
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Nanning Heivr Information Technology Co Ltd
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Priority to CN201611049112.1A priority Critical patent/CN106582711A/en
Publication of CN106582711A publication Critical patent/CN106582711A/en
Withdrawn legal-status Critical Current

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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
    • B01J23/70Catalysts 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
    • B01J23/894Catalysts 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 rare earths or actinides
    • 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
    • B01J23/8906Iron and noble metals
    • 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
    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
    • C02F1/5245Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents using basic salts, e.g. of aluminium and iron
    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/54Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
    • C02F1/56Macromolecular compounds
    • 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
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • 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

Abstract

The invention discloses a wastewater precipitation and purification method. The method includes the following steps that wastewater is discharged into a reaction tank; lime powder is added into the reaction tank and stirred for 0.5-1 hour; still standing is conducted for 1 hour, the lime powder reacts with sulfate radicals, phosphate radicals, carbonate radicals, fluoride ions and the like in the reaction tank, and calcium precipitation dregs are obtained to adsorb dispersed oil in the wastewater; primary filtration is conducted on the reaction tank, the calcium precipitation dregs are discharged, and the pH value is regulated to 3.0-6.0; an oxidizing agent and a catalyst are added to a treating tank, the treating tank is pressurized and heated, stirring is conducted for 1 hour, the wastewater makes sufficient contact and reacts with the oxidizing agent and the catalyst, and a mixed liquid A is obtained; the pH value of the mixed liquid A is regulated to 8.0-9.0, and polyacrylamide is added to obtain a mixed liquid B; the mixed liquid B is stirred for 5 minutes at a constant speed, and still standing is conducted for precipitation. The catalyst contains precious metals, the activity is high, the service life is long, the COD removal rate is high, the dispersed oil and partial anions in the wastewater are effectively adsorbed and removed, and the desalinization effect is achieved.

Description

A kind of settlement of sewage purifying treatment method
Technical field
The present invention relates to sewage disposal, specifically a kind of settlement of sewage purifying treatment method.
Background technology
With the fast development of industry, also mouth becomes serious to water environment pollution problem, especially the row such as medicine, chemical industry, dyestuff The development of industry so that high concentration hard-degraded organic waste water is more and more, is a big difficult point of wastewater treatment;
In recent years, in the world developed country all attached great importance to develop the substitute technology of innovation, to scheme to improve treatment effeciency and drop Reduction process expense;Then quickly with new vitality appearance, it can reduce the pressure and temperature required for reacting to CWO, Accelerate reaction rate, so as to carry out extensively in states such as the U.S., mouth sheet, the European Community and in-depth study and exploitation;Substantial amounts of research The noble metal catalyst series for showing have very high activity and stability in catalytic wet air oxidation processes waste water.
The content of the invention
It is an object of the invention to provide a kind of catalyst activity height, long service life, effectively COD clearances height, absorption Dispersed oil, anionic part in waste water is removed, the settlement of sewage purifying treatment method of desalination is played, to solve above-mentioned background The problem proposed in technology.
For achieving the above object, the present invention provides following technical scheme:
A kind of settlement of sewage purifying treatment method, comprises the following steps:1), waste water entered in reaction tank;2), in reaction tank Input pulverized limestone, and stir 0.5-1 hours;3), stand 1 hour, reaction tank sodalime powder and sulfate radical, phosphate radical, carbonate Calcium precipitate slag, the dispersed oil in calcium precipitate slag absorption waste water are obtained with the reaction such as fluorine ion;4), mistake for the first time is carried out to reaction tank Filter, discharges calcium precipitate slag, and regulation pH value is 3.0-6.0;5), in processing pond add oxidant, catalyst, to processing pond plus Pressure, heating, stir 1 hour, and sewage is fully contacted, reacts with oxidant, catalyst, obtains mixed liquor A;6)By mixed liquor A PH value is adjusted to 8.0-9.0, adds polyacrylamide, then is sufficiently mixed, and obtains mixed liquid B, wherein, in every 5L sewage, poly- third Acrylamide is 1-2mg;7)Mixed liquid B is at the uniform velocity stirred 5 minutes, make coagulating fully, after staticly settling, supernatant is process Water outlet;The catalyst is load metal carbonyl catalyst, and catalyst precarsor is one kind or its combination of carbonyl nail and carbonyl cobalt, Add the second component Ce or Fe simultaneously, the carrier of catalyst is selected from activated carbon, γ-A1203, Ti02In one kind or its composite oxygen Compound;The metallic element weight percentage of the catalyst is 0.1-5%, wherein, the weight percentage of noble metal Ru is The weight percentage of 0.01-0.3%, Ce or Fe is 0.1-5%.
As further scheme of the invention:The carrier of catalyst is activated carbon, γ-A1203, Ti02Equal quality mixes Composition.
As further scheme of the invention:The weight percentage of noble metal Ru is the weight hundred of 0.20%, Ce or Fe Content is divided to be 3.5%.
As further scheme of the invention:Institute's carbonyl nail is followed closely for ten dicarbapentaborane three.
As further scheme of the invention:The carbonyl cobalt is cobalt octacarbonyl.
Compared with prior art, the invention has the beneficial effects as follows:
In the present invention, with the light Base Metal of the load of high dispersive as catalyst, bullion content is very low in catalyst, and activity is high, make With life-span length, high temperature resistant, hyperbaric environment, it is adaptable to which the process of various different high concentrated organic wastewaters, reaction condition is gentleer, COD clearances are high;
To feeding lime in waste water in the present invention, combine with sulfate radical, phosphate radical, carbonate and fluorine ion etc. and generate calcium precipitate slag As adsorbent, not only can dispersed oil effectively in Adsorption waste water, reduce COD, COD can be down to 100mg/L, and Successfully anionic part is removed, desalination is served, is processed without the need for initial adsorbent material regeneration.
Specific embodiment
The technical scheme of this patent is described in more detail with reference to specific embodiment.
A kind of settlement of sewage purifying treatment method, comprises the following steps:1), waste water entered in reaction tank;2), to reaction Pulverized limestone is put in pond, and stirs 0.5-1 hours;3), stand 1 hour, reaction tank sodalime powder and sulfate radical, phosphate radical, carbon The reaction such as acid group and fluorine ion obtains calcium precipitate slag, the dispersed oil in calcium precipitate slag absorption waste water;4), reaction tank carried out for the first time Filter, discharge calcium precipitate slag, regulation pH value is 3.0-6.0;5), in processing pond add oxidant, catalyst, to processing pond plus Pressure, heating, stir 1 hour, and sewage is fully contacted, reacts with oxidant, catalyst, obtains mixed liquor A;6)By mixed liquor A PH value is adjusted to 8.0-9.0, adds polyacrylamide, then is sufficiently mixed, and obtains mixed liquid B, wherein, in every 5L sewage, poly- third Acrylamide is 1-2mg;7)Mixed liquid B is at the uniform velocity stirred 5 minutes, make coagulating fully, after staticly settling, supernatant is process Water outlet;The catalyst is load metal carbonyl catalyst, and catalyst precarsor is one kind or its combination of carbonyl nail and carbonyl cobalt, Add the second component Ce or Fe simultaneously, the carrier of catalyst is selected from activated carbon, γ-A1203, Ti02In one kind or its composite oxygen Compound;The metallic element weight percentage of the catalyst is 0.1-5%, wherein, the weight percentage of noble metal Ru is The weight percentage of 0.01-0.3%, Ce or Fe is 0.1-5%;Wherein, institute's carbonyl nail is followed closely for ten dicarbapentaborane three, and carbonyl cobalt is Cobalt octacarbonyl.
In the present invention, with the light Base Metal of the load of high dispersive as catalyst, bullion content is very low in catalyst, activity High, long service life, high temperature resistant, hyperbaric environment, it is adaptable to the process of various different high concentrated organic wastewaters, reaction condition temperature With COD clearances are high;
To feeding lime in waste water in the present invention, combine with sulfate radical, phosphate radical, carbonate and fluorine ion etc. and generate calcium precipitate slag As adsorbent, not only can dispersed oil effectively in Adsorption waste water, reduce COD, COD can be down to 100mg/L, and Successfully anionic part is removed, desalination is served, is processed without the need for initial adsorbent material regeneration.
The better embodiment of this patent is explained in detail above, but this patent is not limited to above-mentioned embodiment party Formula, in the ken that one skilled in the relevant art possesses, can be with the premise of without departing from this patent objective Make a variety of changes.

Claims (5)

1. a kind of settlement of sewage purifying treatment method, it is characterised in that comprise the following steps:1), waste water entered in reaction tank; 2), put into in reaction tank pulverized limestone, and stir 0.5-1 hours;3), stand 1 hour, reaction tank sodalime powder and sulfate radical, The reaction such as phosphate radical, carbonate and fluorine ion obtains calcium precipitate slag, the dispersed oil in calcium precipitate slag absorption waste water;4), to reaction Pond is filtered for the first time, discharges calcium precipitate slag, and regulation pH value is 3.0-6.0;5), in processing pond add oxidant, catalyst, To processing pond pressurization, heating, stir 1 hour, sewage is fully contacted, reacts with oxidant, catalyst, obtains mixed liquor A;6)Will The pH value of mixed liquor A is adjusted to 8.0-9.0, adds polyacrylamide, then is sufficiently mixed, and obtains mixed liquid B, wherein, it is dirty per 5L In water, polyacrylamide is 1-2mg;7)Mixed liquid B is at the uniform velocity stirred 5 minutes, make coagulating fully, after staticly settling, on Clear liquid is process water outlet;The catalyst is load metal carbonyl catalyst, and catalyst precarsor is the one of carbonyl nail and carbonyl cobalt Plant or its combination, while adding the second component Ce or Fe, the carrier of catalyst is selected from activated carbon, γ-A1203, Ti02In one Plant or its composite oxides;The metallic element weight percentage of the catalyst is 0.1-5%, wherein, the weight of noble metal Ru It is 0.1-5% that percentage composition is the weight percentage of 0.01-0.3%, Ce or Fe.
2. settlement of sewage purifying treatment method according to claim 1, it is characterised in that the carrier of catalyst is activity Charcoal, γ-A1203, Ti02Equal quality mixing composition.
3. settlement of sewage purifying treatment method according to claim 1, it is characterised in that the weight percent of noble metal Ru contains Measure for 0.20%, Ce or Fe weight percentage be 3.5%.
4. settlement of sewage purifying treatment method according to claim 1, it is characterised in that institute's carbonyl nail is ten dicarbapentaborane three Nail.
5. settlement of sewage purifying treatment method according to claim 1, it is characterised in that the carbonyl cobalt is eight carbonyls two Cobalt.
CN201611049112.1A 2016-11-25 2016-11-25 Wastewater precipitation and purification method Withdrawn CN106582711A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111763575A (en) * 2020-06-19 2020-10-13 武汉工程大学 Detergent composition not resistant to calcium and magnesium ions

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20070278158A1 (en) * 2006-06-01 2007-12-06 Green Shelter Innovations Limited Wastewater treatment system and method
CN102101053A (en) * 2009-12-18 2011-06-22 中国科学院兰州化学物理研究所 Catalyst for treating organic wastewater and preparation method thereof
CN103373757A (en) * 2013-07-10 2013-10-30 上海睿优环保工程技术有限公司 Method for treating nondegradable organic wastewater by oxidation by transition metal catalyst
CN105198139A (en) * 2015-10-22 2015-12-30 北京赛科康仑环保科技有限公司 Hydrometallurgy industry raffinate waste water COD removal method

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20070278158A1 (en) * 2006-06-01 2007-12-06 Green Shelter Innovations Limited Wastewater treatment system and method
CN102101053A (en) * 2009-12-18 2011-06-22 中国科学院兰州化学物理研究所 Catalyst for treating organic wastewater and preparation method thereof
CN103373757A (en) * 2013-07-10 2013-10-30 上海睿优环保工程技术有限公司 Method for treating nondegradable organic wastewater by oxidation by transition metal catalyst
CN105198139A (en) * 2015-10-22 2015-12-30 北京赛科康仑环保科技有限公司 Hydrometallurgy industry raffinate waste water COD removal method

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111763575A (en) * 2020-06-19 2020-10-13 武汉工程大学 Detergent composition not resistant to calcium and magnesium ions

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Application publication date: 20170426

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