CN104860470A - Acrolein wastewater treatment method and device - Google Patents

Acrolein wastewater treatment method and device Download PDF

Info

Publication number
CN104860470A
CN104860470A CN201510205891.9A CN201510205891A CN104860470A CN 104860470 A CN104860470 A CN 104860470A CN 201510205891 A CN201510205891 A CN 201510205891A CN 104860470 A CN104860470 A CN 104860470A
Authority
CN
China
Prior art keywords
waste water
treatment
propenal
quartz burner
uviolizing
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.)
Pending
Application number
CN201510205891.9A
Other languages
Chinese (zh)
Inventor
杨齐伟
邹亚波
李凯
任八玉
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.)
Shandong Cynda Chemical Co Ltd
Original Assignee
Shandong Cynda Chemical 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 Shandong Cynda Chemical Co Ltd filed Critical Shandong Cynda Chemical Co Ltd
Priority to CN201510205891.9A priority Critical patent/CN104860470A/en
Publication of CN104860470A publication Critical patent/CN104860470A/en
Pending legal-status Critical Current

Links

Landscapes

  • Physical Water Treatments (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

The invention particularly discloses an acrolein wastewater treatment method and device and belongs to the field of wastewater treatment. Formaldehyde, n-butyl aldehyde and other organic matter are contained in EA (Ethyl Acrylate) wastewater and accordingly the biochemical treatment cannot be directly performed. The acrolein wastewater treatment method comprises distillation, acid adjustment, ultraviolet radiation treatment and biochemical treatment. The cross radiation of ultraviolet rays is adopted, hydrogen peroxide serves as a catalyst, and accordingly the degradation speed of the organic matter is improved and meanwhile the degradation of the organic matter is thorough, wherein the wavelengths of the ultraviolet rays are 254 nm and 185 nm. According to the acrolein wastewater treatment device, the structure is simple, the use is convenient, the treatment cost is low, solid waste is not produced, and the continuous automatic wastewater treatment can be performed.

Description

A kind for the treatment of process of propenal waste water and treatment unit
Technical field
The present invention relates to field of waste water treatment, particularly a kind of structure is simple, easy to use, processing cost is low and do not produce solid waste, can continuous and automatic process waste water propenal waste water treatment unit and use the treatment process of this device process propenal waste water.
Background technology
Propenal is the intermediate producing Imazethapyr, and Imazethapyr belongs to imidazolinone herbicide, is side chain amino acid synthetic inhibitor, uses before bud or after bud.Excellent preventive effect is had, as three-coloured amaranth, knotweed, lamb's-quarters, black nightshade, Siberian cocklebur, barnyard grass, Herba Setariae Viridis, lady's-grass, broomcorn millet etc. to the gramineous weeds in Soybean Field and other leguminous plants fields and some broadleaf weeds.In state-owned soybean 800,000,000 mu, especially northeastward area and in be covered with very large cultivated area, Imazethapyr is by a large number for Soybean Field control gramineous weeds.The intermediate propenal that one important is needed, because 30% formaldehyde solution is used in propenal synthesis, so produce the aldehydes waste water being difficult to degrade of one high density in the one-tenth product process of Imazethapyr.Propenal waste water contains the organism such as formaldehyde, acetaldehyde, butyraldehyde-n, propenal, and COD is very high, has no idea directly to carry out biochemical treatment.
Prior art generally adopts burning method process propenal waste water, namely at incinerator combust fuel gas or oil fuel, add the waste water of discharging in vinylformic acid production process after making in-furnace temperature reach 700-850 DEG C, make the volatile organic matter in waste water at high temperature oxygenolysis become carbonic acid gas and the water of environmental sound.Adopt this technique, substantially achieve the oxidizable organism such as oxygenolysis propenal formaldehyde in waste water, acetaldehyde, propenal, thus reach the object of wastewater discharge standard.But because heating power burning process needs a large amount of steam raising waste water on the one hand, need a large amount of fuel combustion supporting, energy consumption is very high, significantly increase the expense that vinylformic acid is produced, in addition, in waste water, some high boiling organism are not recycled, and reduce the economic benefit of enterprise.
Therefore treatment process and the device of developing low, the simple propenal waste water of a kind of cost are problem demanding prompt solutions.
Summary of the invention
The object of the present invention is to provide that a kind of structure is simple, easy to use, processing cost is low and do not produce solid waste, can continuous and automatic process waste water propenal waste water treatment unit and use the treatment process of this device process propenal waste water.
Technical scheme of the present invention is:
A treatment process for propenal waste water, comprises step:
1) distill; Distillation propenal waste water, to remove high boiling point polymkeric substance;
2) acid adjustment; Regulate the pH value of the rear waste water of distillation to 2-3;
3) uviolizing process; Immersed by ultraviolet radiation device in the waste water after acid adjustment, using hydrogen peroxide as catalyzer, the organism under ultraviolet irradiation in waste water is degraded; It is 180-260nm that described ultraviolet radiation device sends ultraviolet wavelength;
4) biochemical treatment; Waste water after step 3) process passes into biochemical treatment tank and carries out biochemical treatment.
Preferably, step 2) in, adopt hydrochloric acid, sulfuric acid or organic acid to regulate the pH value of waste water.Adopt hydrochloric acid, sulfuric acid or organic acid for adjusting pH, be convenient to post-processed, reduce secondary pollution.
As preferably, in step 3), the concentration of hydrogen peroxide in waste water is 3wt%-5wt%.Hydrogen peroxide concentration, within the scope of this, can play preferably katalysis, can not waste hydrogen peroxide simultaneously.
Preferably, in step 3), catalyzer also comprises ferrous ion, and the concentration of ferrous ion in waste water is 0.1 wt-0.3 wt %.Increase ferrous ion as the catalyzer of degradation of organic substances, degradation speed and degradation rate can be increased further.
Preferably, in step 3), the time of uviolizing process is 2-5h.
Described propenal method of wastewater treatment treatment unit used, comprise be communicated with successively retort, acid adjustment pond, uviolizing pond and biochemistry pool; Wherein, in described uviolizing pond, be provided with ultraviolet radiation device, in described ultraviolet radiation device, be provided with some quartz burners be installed in transparent quartz glass tube.
As preferably, described quartz burner comprises the quartz burner A that can send 254nm UV-light and the quartz burner B that can send 185nm UV-light; Described quartz burner A and quartz burner B arranged crosswise.Ultraviolet kind is more, just can process a greater variety of organism in waste water; And adopt 254nm and 185nm UV treatment propenal waste water, expand greatly and propenal is given up the scope of Organic substance in water process and ability; Meanwhile, the uniformity coefficient of irradiation is added.
Further, described quartz burner A and quartz burner B is 6000 watts of super high power quartz burners.Described ultraviolet radiation device adopts the quartz burner of super high power, the application of 6000 watts of super high power quartz burners, increases waste treatment capacity.
Beneficial effect of the present invention is:
Water and oxygen produce a large amount of hydroxyl radical free radicals and oxyradical under ultraviolet effect, because hydroxyl radical free radical and oxyradical have very strong oxidisability, overwhelming majority organic pollutant is degraded to carbonic acid gas, water and nitrogen, COD and ammonia nitrogen reduce greatly, substantially increase the biodegradability of waste water, ensure that biochemical system long-term stability is run.Adopt wavelength to be 254nm and 185nm ultraviolet cross-fire, and be catalyzer with hydrogen peroxide, the speed accelerating organic matter degradation makes organic matter degradation more thorough simultaneously.
Propenal wastewater treatment equipment structure of the present invention is simple, easy to use, processing cost is low and do not produce solid waste, can continuous and automatic process waste water.
Accompanying drawing explanation
In order to be illustrated more clearly in the embodiment of the present invention or technical scheme of the prior art, be briefly described to the accompanying drawing used required in embodiment or description of the prior art below, apparently, accompanying drawing in the following describes is only some embodiments of the present invention, for those of ordinary skill in the art, under the prerequisite not paying creative work, other accompanying drawing can also be obtained according to these accompanying drawings.
Fig. 1 is a kind of process flow sheet of propenal method of wastewater treatment of the present invention;
Fig. 2 is the another kind of process flow sheet of propenal method of wastewater treatment of the present invention.
Embodiment
Comparative example 1
A treatment process for propenal waste water, comprises step:
1) distill; Distillation propenal waste water, to remove high boiling point polymkeric substance; Wherein, the COD value of propenal waste water is 20000ppm;
2) acid adjustment; Hydrochloric acid, sulfuric acid or organic acid is adopted to regulate the pH value to 2.5 of the rear waste water of distillation;
3) uviolizing process; Ultraviolet radiation device is placed in the top of waste water after acid adjustment, using hydrogen peroxide as catalyzer, the organism under ultraviolet irradiation in waste water is degraded; It is 185nm, 254nm that ultraviolet radiation device sends ultraviolet wavelength; Wherein, the concentration of hydrogen peroxide in waste water is 4wt%, and the time of uviolizing process is 8h; After uviolizing process, the COD value of waste water is 3500ppm;
4) biochemical treatment; Waste water after step 3) process passes into biochemical treatment tank and carries out biochemical treatment.
Aforesaid propylene aldehyde method of wastewater treatment treatment unit used, comprise be communicated with successively retort, acid adjustment pond, uviolizing pond and biochemistry pool; Wherein, uviolizing is provided with ultraviolet radiation device above pond, is provided with some quartz burners be installed in transparent quartz glass tube in ultraviolet radiation device.Quartz burner comprises the quartz burner A that can send 254nm UV-light and the quartz burner B that can send 185nm UV-light; Quartz burner A and quartz burner B arranged crosswise.Quartz burner A and quartz burner B is 6000 watts of super high power quartz burners.
Comparative example 2
A treatment process for propenal waste water, comprises step:
1) distill; Distillation propenal waste water, to remove high boiling point polymkeric substance; Wherein, the COD value of propenal waste water is 20000ppm;
2) acid adjustment; Hydrochloric acid, sulfuric acid or organic acid is adopted to regulate the pH value to 2.5 of the rear waste water of distillation;
3) uviolizing process; Immersed by ultraviolet radiation device in the waste water after acid adjustment, using hydrogen peroxide as catalyzer, the organism under ultraviolet irradiation in waste water is degraded; It is 185nm that ultraviolet radiation device sends ultraviolet wavelength; Wherein, the concentration of hydrogen peroxide in waste water is 4wt%, and the time of uviolizing process is 3h; After uviolizing process, the COD value of waste water is 2700ppm;
4) biochemical treatment; Waste water after step 3) process passes into biochemical treatment tank and carries out biochemical treatment.
Aforesaid propylene aldehyde method of wastewater treatment treatment unit used, comprise be communicated with successively retort, acid adjustment pond, uviolizing pond and biochemistry pool; Wherein, uviolizing is provided with ultraviolet radiation device in pond, is provided with some quartz burners be installed in transparent quartz glass tube in ultraviolet radiation device.Quartz burner is only some can send 185nm ultraviolet tube; This quartz burner is 6000 watts of super high power quartz burners.
Comparative example 3
A treatment process for propenal waste water, comprises step:
1) distill; Distillation propenal waste water, to remove high boiling point polymkeric substance; Wherein, the COD value of propenal waste water is 20000ppm;
2) acid adjustment; Hydrochloric acid, sulfuric acid or organic acid is adopted to regulate the pH value to 2.5 of the rear waste water of distillation;
3) uviolizing process; The organism immersed by ultraviolet radiation device in the waste water after acid adjustment under ultraviolet irradiation in waste water is degraded; It is 185nm, 254nm that ultraviolet radiation device sends ultraviolet wavelength; Wherein, the time of uviolizing process is 3h; After uviolizing process, the COD value of waste water is 11300ppm;
4) biochemical treatment; Waste water after step 3) process passes into biochemical treatment tank and carries out biochemical treatment.
Aforesaid propylene aldehyde method of wastewater treatment treatment unit used, comprise be communicated with successively retort, acid adjustment pond, uviolizing pond and biochemistry pool; Wherein, uviolizing is provided with ultraviolet radiation device in pond, is provided with some quartz burners be installed in transparent quartz glass tube in ultraviolet radiation device.Quartz burner comprises the quartz burner A that can send 254nm UV-light and the quartz burner B that can send 185nm UV-light; Quartz burner A and quartz burner B arranged crosswise.Quartz burner A and quartz burner B is 6000 watts of super high power quartz burners.
Embodiment 1
As shown in Figure 1, a kind for the treatment of process of propenal waste water, comprises step:
1) distill; Distillation propenal waste water, to remove high boiling point polymkeric substance; Wherein, the COD value of propenal waste water is 20000ppm;
2) acid adjustment; Hydrochloric acid, sulfuric acid or organic acid is adopted to regulate the pH value to 2.5 of the rear waste water of distillation;
3) uviolizing process; Immersed by ultraviolet radiation device in the waste water after acid adjustment, using hydrogen peroxide as catalyzer, the organism under ultraviolet irradiation in waste water is degraded; It is 185nm, 254nm that ultraviolet radiation device sends ultraviolet wavelength; Wherein, the concentration of hydrogen peroxide in waste water is 4wt%, and the time of uviolizing process is 3h; After uviolizing process, the COD value of waste water is 2000ppm;
4) biochemical treatment; Waste water after step 3) process passes into biochemical treatment tank and carries out biochemical treatment.
Aforesaid propylene aldehyde method of wastewater treatment treatment unit used, comprise be communicated with successively retort, acid adjustment pond, uviolizing pond and biochemistry pool; Wherein, uviolizing is provided with ultraviolet radiation device in pond, is provided with some quartz burners be installed in transparent quartz glass tube in ultraviolet radiation device.Quartz burner comprises the quartz burner A that can send 254nm UV-light and the quartz burner B that can send 185nm UV-light; Quartz burner A and quartz burner B arranged crosswise.Quartz burner A and quartz burner B is 6000 watts of super high power quartz burners.
Embodiment 1 is with unique difference of comparative example 1, is immersed in waste water by ultraviolet radiation device, and be placed in above waste water by ultraviolet radiation device in comparative example 1 in embodiment 1.This difference causes embodiment 1 faster than comparative example 1 processing speed, and degradation effect of organic compound is high.
Embodiment 1 is with unique difference of comparative example 2, and embodiment 1 middle-ultraviolet lamp fluorescent tube comprises the quartz burner A that can send 254nm UV-light and the quartz burner B that can send 185nm UV-light; And comparative example 2 middle-ultraviolet lamp fluorescent tube only comprises the quartz burner B that can send 185nm UV-light.This difference causes embodiment 1 faster than comparative example 2 processing speed, and degradation effect of organic compound is high.
Embodiment 1 is with unique difference of comparative example 3, in embodiment 1 when uviolizing process, adds hydrogen peroxide as catalyzer, and do not add any catalyzer in comparative example 3 in waste water.This difference causes embodiment 1 to have great lifting than comparative example 3 treatment effect.
Embodiment 2
As shown in Figure 1, a kind for the treatment of process of propenal waste water, comprises step:
1) distill; Distillation propenal waste water, to remove high boiling point polymkeric substance; Wherein, the COD value of propenal waste water is 20000ppm;
2) acid adjustment; Hydrochloric acid, sulfuric acid or organic acid is adopted to regulate the pH value to 2.5 of the rear waste water of distillation;
3) uviolizing process; Immersed by ultraviolet radiation device in the waste water after acid adjustment, using hydrogen peroxide as catalyzer, the organism under ultraviolet irradiation in waste water is degraded; It is 185nm, 254nm that ultraviolet radiation device sends ultraviolet wavelength; Wherein, the concentration of hydrogen peroxide in waste water is 3wt%, and the time of uviolizing process is 5h; After uviolizing process, the COD value of waste water is 1900ppm;
4) biochemical treatment; Waste water after step 3) process passes into biochemical treatment tank and carries out biochemical treatment.
Aforesaid propylene aldehyde method of wastewater treatment treatment unit used, comprise be communicated with successively retort, acid adjustment pond, uviolizing pond and biochemistry pool; Wherein, uviolizing is provided with ultraviolet radiation device in pond, is provided with some quartz burners be installed in transparent quartz glass tube in ultraviolet radiation device.Quartz burner comprises the quartz burner A that can send 254nm UV-light and the quartz burner B that can send 185nm UV-light; Quartz burner A and quartz burner B arranged crosswise.Quartz burner A and quartz burner B is 6000 watts of super high power quartz burners.
Embodiment 3
As shown in Figure 1, a kind for the treatment of process of propenal waste water, comprises step:
1) distill; Distillation propenal waste water, to remove high boiling point polymkeric substance; Wherein, the COD value of propenal waste water is 20000ppm;
2) acid adjustment; Hydrochloric acid, sulfuric acid or organic acid is adopted to regulate the pH value to 3 of the rear waste water of distillation;
3) uviolizing process; Immersed by ultraviolet radiation device in the waste water after acid adjustment, using hydrogen peroxide as catalyzer, the organism under ultraviolet irradiation in waste water is degraded; It is 185nm, 254nm that ultraviolet radiation device sends ultraviolet wavelength; Wherein, the concentration of hydrogen peroxide in waste water is 5wt%, and the time of uviolizing process is 2h; After uviolizing process, the COD value of waste water is 2200ppm;
4) biochemical treatment; Waste water after step 3) process passes into biochemical treatment tank and carries out biochemical treatment.
Aforesaid propylene aldehyde method of wastewater treatment treatment unit used, comprise be communicated with successively retort, acid adjustment pond, uviolizing pond and biochemistry pool; Wherein, uviolizing is provided with ultraviolet radiation device in pond, is provided with some quartz burners be installed in transparent quartz glass tube in ultraviolet radiation device.Quartz burner comprises the quartz burner A that can send 254nm UV-light and the quartz burner B that can send 185nm UV-light; Quartz burner A and quartz burner B arranged crosswise.Quartz burner A and quartz burner B is 6000 watts of super high power quartz burners.
Embodiment 4
As shown in Figure 1, a kind for the treatment of process of propenal waste water, comprises step:
1) distill; Distillation propenal waste water, to remove high boiling point polymkeric substance; Wherein, the COD value of propenal waste water is 20000ppm;
2) acid adjustment; Hydrochloric acid, sulfuric acid or organic acid is adopted to regulate the pH value to 2.5 of the rear waste water of distillation;
3) uviolizing process; Immersed by ultraviolet radiation device in the waste water after acid adjustment, using hydrogen peroxide as catalyzer, the organism under ultraviolet irradiation in waste water is degraded; Ultraviolet radiation device sends that ultraviolet wavelength is 190,220nm; Wherein, the concentration of hydrogen peroxide in waste water is 4wt%, and the time of uviolizing process is 3h; After uviolizing process, the COD value of waste water is 2200ppm;
4) biochemical treatment; Waste water after step 3) process passes into biochemical treatment tank and carries out biochemical treatment.
Aforesaid propylene aldehyde method of wastewater treatment treatment unit used, comprise be communicated with successively retort, acid adjustment pond, uviolizing pond and biochemistry pool; Wherein, uviolizing is provided with ultraviolet radiation device in pond, is provided with some quartz burners be installed in transparent quartz glass tube in ultraviolet radiation device.Quartz burner comprises the quartz burner A that can send 254nm UV-light and the quartz burner B that can send 185nm UV-light; Quartz burner A and quartz burner B arranged crosswise.Quartz burner A and quartz burner B is 6000 watts of super high power quartz burners.
Embodiment 5
As shown in Figure 2, a kind for the treatment of process of propenal waste water, comprises step:
1) distill; Distillation propenal waste water, to remove high boiling point polymkeric substance; Wherein, the COD value of propenal waste water is 20000ppm;
2) acid adjustment; Hydrochloric acid, sulfuric acid or organic acid is adopted to regulate the pH value to 2.5 of the rear waste water of distillation;
3) uviolizing process; Immersed by ultraviolet radiation device in the waste water after acid adjustment, using ferrous ion and hydrogen peroxide as catalyzer, the organism under ultraviolet irradiation in waste water is degraded; It is 185nm, 254nm that ultraviolet radiation device sends ultraviolet wavelength; Wherein, the concentration of hydrogen peroxide in waste water is 4wt%, and the concentration of ferrous ion in waste water is 0.2 wt %; The time of uviolizing process is 3h; After uviolizing process, the COD value of waste water is 1600ppm;
4) biochemical treatment; Waste water after step 3) process passes into biochemical treatment tank and carries out biochemical treatment.
Aforesaid propylene aldehyde method of wastewater treatment treatment unit used, comprise be communicated with successively retort, acid adjustment pond, uviolizing pond and biochemistry pool; Wherein, uviolizing is provided with ultraviolet radiation device in pond, is provided with some quartz burners be installed in transparent quartz glass tube in ultraviolet radiation device.Quartz burner comprises the quartz burner A that can send 254nm UV-light and the quartz burner B that can send 185nm UV-light; Quartz burner A and quartz burner B arranged crosswise.Quartz burner A and quartz burner B is 6000 watts of super high power quartz burners.

Claims (8)

1. a treatment process for propenal waste water, is characterized in that, comprises step:
1) distill; Distillation propenal waste water, to remove high boiling point polymkeric substance;
2) acid adjustment; Regulate the pH value of the rear waste water of distillation to 2-3;
3) uviolizing process; Immersed by ultraviolet radiation device in the waste water after acid adjustment, using hydrogen peroxide as catalyzer, the organism under ultraviolet irradiation in waste water is degraded; It is 180-260nm that described ultraviolet radiation device sends ultraviolet wavelength;
4) biochemical treatment; Waste water after step 3) process passes into biochemical treatment tank and carries out biochemical treatment.
2. the treatment process of propenal waste water as claimed in claim 1, is characterized in that: step 2) in, adopt hydrochloric acid, sulfuric acid or organic acid to regulate the pH value of waste water.
3. the treatment process of propenal waste water as claimed in claim 1 or 2, it is characterized in that: in step 3), the concentration of hydrogen peroxide in waste water is 3wt%-5wt%.
4. the treatment process of propenal waste water as claimed in claim 1, it is characterized in that: in step 3), catalyzer also comprises ferrous ion, and the concentration of ferrous ion in waste water is 0.1 wt-0.3 wt %.
5. the treatment process of the propenal waste water as described in claim 1 or 4, is characterized in that: in step 3), and the time of uviolizing process is 2-5h.
6. propenal method of wastewater treatment treatment unit used as claimed in claim 1, is characterized in that: comprise be communicated with successively retort, acid adjustment pond, uviolizing pond and biochemistry pool; Wherein, in described uviolizing pond, be provided with ultraviolet radiation device, in described ultraviolet radiation device, be provided with some quartz burners be installed in transparent quartz glass tube.
7. treatment unit as claimed in claim 6, is characterized in that: described quartz burner comprises the quartz burner A that can send 254nm UV-light and the quartz burner B that can send 185nm UV-light; Described quartz burner A and quartz burner B arranged crosswise.
8. treatment unit as claimed in claim 7, is characterized in that: described quartz burner A and quartz burner B is 6000 watts of super high power quartz burners.
CN201510205891.9A 2015-04-28 2015-04-28 Acrolein wastewater treatment method and device Pending CN104860470A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201510205891.9A CN104860470A (en) 2015-04-28 2015-04-28 Acrolein wastewater treatment method and device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201510205891.9A CN104860470A (en) 2015-04-28 2015-04-28 Acrolein wastewater treatment method and device

Publications (1)

Publication Number Publication Date
CN104860470A true CN104860470A (en) 2015-08-26

Family

ID=53906716

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201510205891.9A Pending CN104860470A (en) 2015-04-28 2015-04-28 Acrolein wastewater treatment method and device

Country Status (1)

Country Link
CN (1) CN104860470A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109437366A (en) * 2018-11-28 2019-03-08 山东大学 A method of poly-epoxy succinic acid is decomposed using ultraviolet oxidation
CN109851179A (en) * 2019-04-09 2019-06-07 岳阳天河环保科技有限公司 A kind of methacrylaldehyde production wastewater treatment process
CN117985810A (en) * 2024-03-21 2024-05-07 湖北圣灵科技有限公司 Wastewater recycling device for acrolein production

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003181473A (en) * 2001-12-17 2003-07-02 Kubota Corp Method and equipment for degrading persistent organic matter
CN1587091A (en) * 2004-08-04 2005-03-02 同济大学 Method for degradating organic chlorophenol in water
CN101863526A (en) * 2010-07-05 2010-10-20 李朝林 Method and device for degrading pollutants through ultraviolet catalytic wet oxidation
CN102198989A (en) * 2011-04-22 2011-09-28 安徽国星生物化学有限公司 Method for treating PMIDA wastewater
CN102229445A (en) * 2011-05-24 2011-11-02 江汉大学 Homogeneous phase photo-oxidation device capable of degrading aromatic compound waste water continuously and processing method thereof
CN202390277U (en) * 2011-07-25 2012-08-22 江门中顺纸业有限公司 Ultraviolet/hydrogen peroxide and biochemistry combined reactor for treating middle-stage wastewater during papermaking
CN103626345A (en) * 2013-12-13 2014-03-12 煤炭科学研究总院 Biochemical pretreatment method of coal chemical industry wastewater
CN103641274A (en) * 2013-12-12 2014-03-19 安徽科技学院 Novel technology for processing dye wastewater by combining advanced oxidation technology with biofilm process
CN103787538A (en) * 2012-11-01 2014-05-14 中国石油化工股份有限公司 Nitrile butadiene rubber wastewater recovery treatment method

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003181473A (en) * 2001-12-17 2003-07-02 Kubota Corp Method and equipment for degrading persistent organic matter
CN1587091A (en) * 2004-08-04 2005-03-02 同济大学 Method for degradating organic chlorophenol in water
CN101863526A (en) * 2010-07-05 2010-10-20 李朝林 Method and device for degrading pollutants through ultraviolet catalytic wet oxidation
CN102198989A (en) * 2011-04-22 2011-09-28 安徽国星生物化学有限公司 Method for treating PMIDA wastewater
CN102229445A (en) * 2011-05-24 2011-11-02 江汉大学 Homogeneous phase photo-oxidation device capable of degrading aromatic compound waste water continuously and processing method thereof
CN202390277U (en) * 2011-07-25 2012-08-22 江门中顺纸业有限公司 Ultraviolet/hydrogen peroxide and biochemistry combined reactor for treating middle-stage wastewater during papermaking
CN103787538A (en) * 2012-11-01 2014-05-14 中国石油化工股份有限公司 Nitrile butadiene rubber wastewater recovery treatment method
CN103641274A (en) * 2013-12-12 2014-03-19 安徽科技学院 Novel technology for processing dye wastewater by combining advanced oxidation technology with biofilm process
CN103626345A (en) * 2013-12-13 2014-03-12 煤炭科学研究总院 Biochemical pretreatment method of coal chemical industry wastewater

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109437366A (en) * 2018-11-28 2019-03-08 山东大学 A method of poly-epoxy succinic acid is decomposed using ultraviolet oxidation
CN109851179A (en) * 2019-04-09 2019-06-07 岳阳天河环保科技有限公司 A kind of methacrylaldehyde production wastewater treatment process
CN109851179B (en) * 2019-04-09 2021-12-10 岳阳天河环保科技有限公司 Acrolein production wastewater treatment process
CN117985810A (en) * 2024-03-21 2024-05-07 湖北圣灵科技有限公司 Wastewater recycling device for acrolein production
CN117985810B (en) * 2024-03-21 2024-07-02 湖北圣灵科技有限公司 Wastewater recycling device for acrolein production

Similar Documents

Publication Publication Date Title
Xu et al. Degradation effect and mechanism of gas-liquid phase dielectric barrier discharge on norfloxacin combined with H2O2 or Fe2+
Ioannou et al. Solar photo-Fenton oxidation against the bioresistant fractions of winery wastewater
Zhou et al. Intimate coupling of photocatalysis and biodegradation for degrading phenol using different light types: visible light vs UV light
Bernabeu et al. Solar photocatalysis as a tertiary treatment to remove emerging pollutants from wastewater treatment plant effluents
Belalcázar-Saldarriaga et al. Photo-Fenton processes in raceway reactors: technical, economic, and environmental implications during treatment of colored wastewaters
Murali et al. Evaluation of integrated anaerobic–aerobic biofilm reactor for degradation of azo dye methyl orange
Wang et al. Rapid degradation of norfloxacin by VUV/Fe2+/H2O2 over a wide initial pH: Process parameters, synergistic mechanism, and influencing factors
de Boer et al. Benchmarking tertiary water treatments for the removal of micropollutants and pathogens based on operational and sustainability criteria
Rizzo Addressing main challenges in the tertiary treatment of urban wastewater: are homogeneous photodriven AOPs the answer?
Monteagudo et al. Effect of light source on the catalytic degradation of protocatechuic acid in a ferrioxalate-assisted photo-Fenton process
CN104860470A (en) Acrolein wastewater treatment method and device
JP4673709B2 (en) Water treatment system
KR101585143B1 (en) Method and apparatus for treating 1,4-dioxane in waste water
CN101402506A (en) Process for treating dimethyl sulfoxide wastewater with photocatalysis and oxidization combined film bioreactor
da Silva et al. Study of effects of pharmaceuticals on the activated sludge process combining advanced oxidation using ultraviolet/hydrogen peroxide to increase their removal and mineralization of wastewater
CN110228898A (en) A kind of technique of catalytic ozonation-MBR Combined Treatment coal chemical industrial waste water
Davididou et al. Advanced oxidation processes for the treatment of winery wastewater: a review and future perspectives
Palas et al. Heterogeneous photo Fenton-like oxidation of Procion Red MX-5B using walnut shell based green catalysts
Patil et al. Decolorization of reactive blue 171 dye using ozonation and UV/H2O2 and elucidation of the degradation mechanism
Eskandarian et al. Energy-efficient removal of acid red 14 by UV-LED/persulfate advanced oxidation process: Pulsed irradiation, duty cycle, reaction kinetics, and energy consumption
CN105254117A (en) Treatment method of fine chemical engineering oily wastewater
KR101459376B1 (en) Water treatment apparatus having control system and water treatment process using thereof
Priyadarshini et al. Efficacious degradation of ethylene glycol by ultraviolet activated persulphate: reaction kinetics, transformation mechanisms, energy demand, and toxicity assessment
Wang et al. Sulfite activation by water film dielectric barrier discharge plasma for ibuprofen degradation: Efficiency, comparison of persulfate, mechanism, active substances dominant to pathway, and toxicity evaluation
Wright et al. Effect of humic acid on E. coli disinfection in a microbubble-gas plasma reactor

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
EXSB Decision made by sipo to initiate substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20150826