CN103723816B - A kind of continuous degradation AES vacuum removal water Zhong diox method and treatment unit - Google Patents

A kind of continuous degradation AES vacuum removal water Zhong diox method and treatment unit Download PDF

Info

Publication number
CN103723816B
CN103723816B CN201310728769.0A CN201310728769A CN103723816B CN 103723816 B CN103723816 B CN 103723816B CN 201310728769 A CN201310728769 A CN 201310728769A CN 103723816 B CN103723816 B CN 103723816B
Authority
CN
China
Prior art keywords
ozone
diox
vacuum removal
treatment unit
aes
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.)
Active
Application number
CN201310728769.0A
Other languages
Chinese (zh)
Other versions
CN103723816A (en
Inventor
陶华东
黄亚茹
周大鹏
孔令鸟
任静
秦志荣
许荣年
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Jiaxing Zanyu Technology Co., Ltd.
Praise Technology Group Limited by Share Ltd
Original Assignee
Jiaxing Zanyu Technology Co Ltd
ZHEJIANG ZANYU TECHNOLOGY Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Jiaxing Zanyu Technology Co Ltd, ZHEJIANG ZANYU TECHNOLOGY Co Ltd filed Critical Jiaxing Zanyu Technology Co Ltd
Priority to CN201310728769.0A priority Critical patent/CN103723816B/en
Publication of CN103723816A publication Critical patent/CN103723816A/en
Application granted granted Critical
Publication of CN103723816B publication Critical patent/CN103723816B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Treatment Of Water By Oxidation Or Reduction (AREA)
  • Catalysts (AREA)

Abstract

The present invention relates to a kind of continuous degradation AES vacuum removal water Zhong diox method and treatment unit.The method that object is to provide can be degraded high density diox when producing AES in the vacuum removal water that produces; The treatment unit provided has structure feature simple and easy to use.Technical scheme is: a kind of method of continuous degradation AES vacuum removal water Zhong diox, comprises the following steps: 1) mixed with hydrogen peroxide by the vacuum removal water that AES vacuum removal diox produces, and pass into ozone and carry out pre-oxidation; 2) mixing water after step 1) process is passed in mixing tank, and pass into ozone and carry out initial breakdown reaction; 3) to through step 2) add catalyzer in degradation water after process, and pass into the further catalytic oxidation of ozone.A treatment unit for continuous degradation AES vacuum removal water Zhong diox, this treatment unit comprises preoxidation device, static mixer, catalytic oxidizer, and ozone source.

Description

A kind of continuous degradation AES vacuum removal water Zhong diox method and treatment unit
Technical field
The present invention relates to a kind of using metal or metal oxide as the method for catalyzer continuous catalysis ozone degradation diox and treatment unit.
Background technology
In the production process of tensio-active agent fatty alcohol polyoxyethylene ether sulfate (hereinafter referred to as AES), include the processing step of vacuum removal diox, waste water (diox content containing high density diox can be produced up to 200-500mg/L).
Diox (Isosorbide-5-Nitrae-dioxane) is a kind of colourless volatile liquid, and molecular formula is C 4h 80 2, relative molecular mass is 88.11, and another name dioxane or Isosorbide-5-Nitrae-dioxane, has ethereal odor, inflammable, fusing point 11.8 DEG C, boiling point 101.3 DEG C, can with water, arene and most of immiscible organic solvent.Diox wetting ability is strong, and in water, solvability is good and stable, does not have facile hydrolysis group, does not absorb natural light, not facile hydrolysis or photodissociation in physical environment in molecular structure.Diox is volatile, easily transfers in underground water from soil, diox is directly entered the easy atmosphere pollution of sewage lagoon process, soil and water.
The degradation method of diox mainly comprises biological degradation method; Biological degradation method is consuming time for a long time and run not easily, is therefore badly in need of a kind of quickness and high efficiency more and can the method for serialization degraded diox and treatment unit.
Summary of the invention
The object of this invention is to provide a kind of method of continuous treatment diox, the method can be degraded high density diox when producing AES in the vacuum removal water that produces, and has the high and simple feature of technique of degradation rate;
The present invention also provides a kind for the treatment of unit of continuous treatment diox, and this treatment unit has structure feature simple and easy to use.
Technical scheme of the present invention is:
A method for continuous degradation AES vacuum removal water Zhong diox, comprises the following steps:
1) mixed with hydrogen peroxide by the vacuum removal water that AES vacuum removal diox produces, and pass into ozone and carry out pre-oxidation, process air pressure is 0.02-0.05MPa;
2) mixing water after step 1) process is passed in mixing tank, and pass into ozone and carry out initial breakdown reaction;
3) to through step 2) add catalyzer in degradation water after process, and pass into the further catalytic oxidation of ozone.
The charging capacity of described hydrogen peroxide is 50-100mg/L.
Ozone charging capacity in described three steps is followed successively by 10-20mg/L, 20-60mg/L and 10-20mg/L.
Described catalyzer is metal or metallic compound.
Described catalyzer is TiO2, Al 2o 3, Mn or Fe.
A kind for the treatment of unit of continuous degradation AES vacuum removal water Zhong diox, it is characterized in that: this treatment unit comprises to be connected the preoxidation device, static mixer, the catalytic oxidizer that communicate and the ozone source be communicated with the inlet mouth of these three reactor bottoms of preoxidation device, static mixer and catalytic oxidizer respectively successively by material pipe.
The described discharge port of preoxidation device is communicated with the opening for feed of static mixer and the discharge port of static mixer is communicated with the opening for feed of catalytic oxidizer.
Described preoxidation device, static mixer and catalytic oxidizer, the top vent of these three reactors is communicated with ozone breaker respectively.
Described ozone source is ozonizer.
The invention has the beneficial effects as follows:
1, the present invention by adding hydrogen peroxide to improve the oxidation capacity of ozone in vacuum removal water, and using metal or metallic compound as catalyzer, more than 95% can be reached by Shi diox degradation rate, not only alleviate environmental protection treatment pressure, and the lower and technique of cost simple (cost more with high investment that biological degradation method needs and run difficulty larger);
2, the present invention uses ozone as oxygenant, not only less expensive, degradation treatment speed, and the product generated after ozone reduction is that oxygen , diox is finally converted into carbonic acid gas and water, can alleviate the burden of follow-up environmental protection treatment;
3, diox is a kind of cyclic ether compounds, not easily decomposition, needs to use oxidation potential to be greater than the oxygenant of 2.0eV; And UV+H 2o 2and O 3+ H 2o 2oxidation potential higher, may be used for degrade diox; In the present invention, the oxidation potential of ozone and hydrogen peroxide is 2.7eV, and the effect of degraded diox is higher;
4, according to the difference of used catalyzer, two class catalytic ozonations can be divided into: a class is homogeneous catalysis ozone oxidation, catalyzer is generally transition metal ion, as Fe (II), Mn (II), Ni (II), Co (II), Cd (II), Cu (II), Ag (I), Cr (III), Zn (II) etc.; Another kind of be use solid metal, metal oxide or load on carrier metal or metal oxide as catalyzer, carry out heterogeneous catalysis ozone oxidation; The present invention with metal or metal oxide for catalyzer, can adsorb ozone Yu diox carries out DeR, the catalytic decomposition efficiency of ozone and the generation of hydroxyl radical free radical can be improved simultaneously;
5, preoxidation device can increase the concentration of ordinary dissolution of ozone in water, thus improves the utilization ratio of ozone;
6, static mixer can make ozone fully contact Yu diox, thus improves the degradation efficiency of diox in catalyst-free situation, extends the work-ing life of catalyzer in catalytic oxidizer;
7, treatment unit of the present invention not only small volume, and be combined to form by maturing appts, can continuous treatment be realized, and combine simple and convenient, can also regulate according to wastewater treatment capacity and arrange, save processing cost.
Accompanying drawing explanation
Fig. 1 is the main TV structure schematic diagram for the treatment of unit of the present invention.
Embodiment
Chemical oxidization method is a kind of method of effective degraded diox, but in the process using ozonize diox, there is the problems such as the low and ozone oxidation of ozone utilization rate is not thorough; For this reason, the present invention adds H simultaneously 2o 2and catalyzer, significantly improve the degradation efficiency of Dui diox.
The invention will be further described below, but the present invention is not limited to following examples.
One, a method for continuous degradation diox, comprises the following steps:
The first step, by AES vacuum removal diox produce vacuum removal water mix with hydrogen peroxide (50-100mg/L), then pass into the ozone (10-20mg/L) produced by ozone source and carry out pre-oxidation; During process, air pressure remains on 0.02-0.05MPa;
Second step, the mixing water after the first step process to be mixed (preferably adopting static mixer) further, pass into the ozone (20-60mg/L) that produced by ozone source to carry out initial breakdown reaction simultaneously; Keep normal pressure in described static mixer and temperature is 40-60 DEG C;
3rd step, in the degradation water after second step process, add catalyzer, and pass into the ozone (10-20mg/L) that produced by ozone source to carry out catalytic oxidation; Normal pressure and temperature is 40-60 DEG C is kept during described catalysis; This catalyzer is metal or metallic compound; Catalyzer preferred TiO2, Al 2o 3, Mn or Fe.
Two, a treatment unit for continuous degradation diox, as shown in Figure 1, is comprised and to be connected successively the preoxidation device 1, static mixer 2, the catalytic oxidizer 3 that communicate by material pipe, and ozonizer 4 and ozone breaker 5;
The side-lower of described preoxidation device is shaped with opening for feed 1-1, and bottom is shaped with inlet mouth 1-3, is shaped with discharge port 1-2 above side, and top is shaped with venting port 1-4; The side-lower of described static mixer is shaped with opening for feed 2-1, and bottom is shaped with inlet mouth 2-3, is shaped with discharge port 2-2 above side, and top is shaped with venting port 2-4; The side-lower of described catalytic oxidizer is shaped with opening for feed 3-1, and bottom is shaped with inlet mouth 3-3, is shaped with discharge port 3-2 above side, and top is shaped with venting port 3-4;
The opening for feed input vacuum removal water A and hydrogen peroxide B of preoxidation device; The discharge port of preoxidation device is communicated with the opening for feed of static mixer by material pipe (omitting in figure) and the discharge port of static mixer is communicated with the opening for feed of catalytic oxidizer by material pipe; The discharge port of catalytic oxidizer then exports treated vacuum removal water;
Described ozone source is ozonizer; Described ozonizer is communicated with inlet mouth, the inlet mouth of static mixer, the inlet mouth of catalytic oxidizer of preoxidation device respectively by pipeline;
Described ozone breaker is communicated with venting port, the venting port of static mixer, the venting port of catalytic oxidizer of preoxidation device respectively by pipeline; Tail gas after ozone breaker process can directly discharge;
The wastewater treatment capacity of described treatment unit is preferably 1m 3/ h, and can by parallel for multiple treatment unit to increase waste treatment capacity;
Described pre-oxidation reactor, static mixer and catalytic oxidizer are prior art, and buyable obtains.
Three, experimental data
Check the effect of continuous degradation diox of the present invention, need utilising efficiency and the catalytic ozonation processing cost of comprehensive consideration ozone; Measure below by way of parameters such as change hydrogen peroxide dosage, ozone concn, metal or metallic compounds;
1, test case one
Keep ozone always throwing amount Yu the constant rate of diox concentration, keep the ozone feed ratio of preoxidation device, static mixer and catalytic oxidizer constant, with TiO 2as catalyzer, repeatedly adjust hydrogen peroxide Yu after diox concentration ratio, obtain diox degradation rate (shown in table 1):
Table 1: hydrogen peroxide concentration is on the impact of diox degradation rate
Visible: after adding hydrogen peroxide while ozonize, increase substantially diox degradation rate.
2, test case two
Keep hydrogen peroxide concentration Yu the constant rate of diox concentration, with TiO 2for catalyzer, repeatedly adjust ozone always throwing amount Yu diox concentration ratio also adjusts the ozone feed ratio of preoxidation device, static mixer and catalytic oxidizer simultaneously, obtain diox degradation rate (shown in table 2):
Table 2: ozone concn is on the impact of diox degradation rate
Visible: under different diox concentration levels, the feed intake impact of comparison diox degradation rate of ozone always throwing amount and ozone is little.
3, test case three
Keep hydrogen peroxide concentration Yu the constant rate of diox concentration, keep ozone always throwing amount Yu the constant rate of diox concentration, keep the ozone feed ratio of preoxidation device, static mixer and catalytic oxidizer constant, repeatedly adjust catalyzer, obtain diox degradation rate (shown in table 3):
Table 3: catalyzer is on the impact of diox degradation rate
Visible: metal oxide is as diox degradation rate during catalyzer, and outline is higher than diox degradation rate during using metal as catalyzer.

Claims (2)

1. the method for diox in continuous degradation AES vacuum removal water, comprises the following steps:
1) mixed with hydrogen peroxide by the vacuum removal water that the vacuum removal diox in AES production process produces, and pass into ozone and carry out pre-oxidation, process air pressure is 0.02-0.05MPa;
2) by through step 1) mixing water after process passes in mixing tank, and pass into ozone and carry out initial breakdown reaction;
3) to through step 2) add catalyzer in degradation water after process, and pass into the further catalytic oxidation of ozone;
The charging capacity of described hydrogen peroxide is 50-100mg/L;
Ozone charging capacity in described three steps is followed successively by 10-20mg/L, 20-60mg/L and 10-20mg/L;
Described catalyzer is metal or metallic compound;
Described catalyzer is TiO 2, Al 2o 3, Mn or Fe.
2. the treatment unit of a continuous degradation diox, it is characterized in that: this treatment unit comprises to be connected the preoxidation device (1), static mixer (2), the catalytic oxidizer (3) that communicate and the ozone source be communicated with the inlet mouth of these three reactor bottoms of preoxidation device, static mixer and catalytic oxidizer respectively successively by material pipe;
The described discharge port of preoxidation device is communicated with the opening for feed of static mixer and the discharge port of static mixer is communicated with the opening for feed of catalytic oxidizer;
Described preoxidation device, static mixer, catalytic oxidizer, the top vent of these three reactors is communicated with ozone breaker (5) respectively;
Described ozone source is ozonizer (4).
CN201310728769.0A 2013-12-25 2013-12-25 A kind of continuous degradation AES vacuum removal water Zhong diox method and treatment unit Active CN103723816B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201310728769.0A CN103723816B (en) 2013-12-25 2013-12-25 A kind of continuous degradation AES vacuum removal water Zhong diox method and treatment unit

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201310728769.0A CN103723816B (en) 2013-12-25 2013-12-25 A kind of continuous degradation AES vacuum removal water Zhong diox method and treatment unit

Publications (2)

Publication Number Publication Date
CN103723816A CN103723816A (en) 2014-04-16
CN103723816B true CN103723816B (en) 2015-07-29

Family

ID=50448162

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201310728769.0A Active CN103723816B (en) 2013-12-25 2013-12-25 A kind of continuous degradation AES vacuum removal water Zhong diox method and treatment unit

Country Status (1)

Country Link
CN (1) CN103723816B (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP4355693A1 (en) 2021-06-14 2024-04-24 Stepan Company Catalyst-free method for degrading dioxane in alkyl ether sulfate vacuum removal water

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006281000A (en) * 2005-03-31 2006-10-19 Kubota Corp Apparatus for reducing trace of hazardous substance in water
CN203668149U (en) * 2013-12-25 2014-06-25 浙江赞宇科技股份有限公司 Treatment device for continuously degrading dioxane

Also Published As

Publication number Publication date
CN103723816A (en) 2014-04-16

Similar Documents

Publication Publication Date Title
CN104355443B (en) A kind for the treatment of process of the waste water containing unsymmetrical dimethyl hydrazine
CN104710002A (en) Two-stage micro/nano aeration and catalytic ozonation wastewater treatment system
CN106882866A (en) The method that hydrogen peroxide synergy ozone heterogeneous catalytic oxidation processes waste water
CN104724852A (en) Method and device for stripping, oxidizing and degrading high-concentration nitrobenzene-containing wastewater
CN103058346A (en) Wastewater treatment method
CN101767859A (en) Waste water treatment method combining Fenton oxidization and microwave catalysis phase
CN107032476A (en) A kind of two-stage advanced oxidation advanced waste treatment method
CN110894096A (en) Multiphase Fenton reagent and application thereof
CN110436603A (en) The method and device of heterogeneous catalysis ozone degradation phenolic waste water in a kind of super gravity field
CN109264845A (en) A kind of device and method of reverse osmosis concentrated water organic matter and ammonia nitrogen removal simultaneously
CN109794155A (en) The method for handling VOCs and foul gas
CN107663152A (en) A kind of method for being catalyzed dust technology methyl nitrite
CN103723816B (en) A kind of continuous degradation AES vacuum removal water Zhong diox method and treatment unit
CN105642298A (en) Reductive graphene supported nano Ce0/Fe0 composite material, and preparation method and application thereof
CN111018289A (en) Sludge reduction treatment system and method based on ozone micro-nano bubbles
CN203668149U (en) Treatment device for continuously degrading dioxane
CN110092461A (en) One kind being based on Cu2+For active component catalyst to the processing method of bisphenol-A waste water
Liu et al. An innovative approach to oxidative removal of hydrogen sulfide using the solution of peroxo heteropolyacid
CN105562013B (en) A kind of nano Ce0Adulterate Fe0Composite material and methods for making and using same
CN109336332A (en) A kind of processing method and organic sewage treatment device suitable for high COD organic sewage
CN103474123A (en) Method of using nano Fe/Mn composite catalyst for oxidative decomposition of radioactive waste resin
Nguyen et al. Enhanced degradation of cefalexin using Co2SnO4@ rGO as an effective peroxymonosulfate activator in hybrid ozonation system
CN105753231A (en) Method of utilizing Fenton reaction to remove organic pollutants in wastewater
CN205472871U (en) Get rid of in high temperature high acid system organic matter and middle valence state metal ion's device
CN105107506A (en) Preparation method for modified activated carbon used for catalysis of hydrogen peroxide oxidation

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
C56 Change in the name or address of the patentee
CP01 Change in the name or title of a patent holder

Address after: Hangzhou City, Zhejiang province 310009 City Shangcheng District No. 128 Lane

Patentee after: Praise Technology Group Limited by Share Ltd

Patentee after: Jiaxing Zanyu Technology Co., Ltd.

Address before: Hangzhou City, Zhejiang province 310009 City Shangcheng District No. 128 Lane

Patentee before: Zhejiang Zanyu Technology Co., Ltd.

Patentee before: Jiaxing Zanyu Technology Co., Ltd.