CN112295391A - Desulfurization and denitrification flue gas advanced treatment method - Google Patents

Desulfurization and denitrification flue gas advanced treatment method Download PDF

Info

Publication number
CN112295391A
CN112295391A CN202011117602.7A CN202011117602A CN112295391A CN 112295391 A CN112295391 A CN 112295391A CN 202011117602 A CN202011117602 A CN 202011117602A CN 112295391 A CN112295391 A CN 112295391A
Authority
CN
China
Prior art keywords
washing
air
flue gas
liquid
air inlet
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
CN202011117602.7A
Other languages
Chinese (zh)
Inventor
马树良
马树营
李红丽
张腾
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.)
Anhui Cisco Environment System Engineering Technology Co ltd
Original Assignee
Anhui Cisco Environment System Engineering 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 Anhui Cisco Environment System Engineering Technology Co ltd filed Critical Anhui Cisco Environment System Engineering Technology Co ltd
Priority to CN202011117602.7A priority Critical patent/CN112295391A/en
Publication of CN112295391A publication Critical patent/CN112295391A/en
Pending legal-status Critical Current

Links

Images

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/77Liquid phase processes
    • B01D53/78Liquid phase processes with gas-liquid contact
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/60Simultaneously removing sulfur oxides and nitrogen oxides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • B01D2258/0283Flue gases

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Treating Waste Gases (AREA)

Abstract

The invention relates to a flue gas advanced treatment method for desulfurization and denitrification. Comprises a washing tank, wherein a plurality of transverse partition plates are arranged in the washing tank to divide the interior of the washing tank into a plurality of independent washing areas; an air inlet chamber is arranged at the bottom of the washing tank, the flue gas is introduced into the air inlet chamber through an air inlet channel, an exhaust channel is arranged at the top of the washing tank, and the exhaust channel is communicated with a draught fan; when the cleaning solution overflows from the liquid discharge port, the induced draft fan is started, a negative pressure environment is formed in each washing area from top to bottom, finally, the negative pressure environment is formed in the air inlet cavity, the flue gas is guided into the submerged area by the first air guide pipe to be washed and then is introduced into the next washing area, and after the flue gas sequentially passes through each submerged area to be washed, the flue gas is finally sprayed and washed by the original solution of the cleaning solution in the exhaust passage, so that the washing effect on the flue gas can be effectively improved; the circulation process of washing liquid is located the inside of washing jar, lies in that the flue gas can fully retrieve after carrying out absorption reaction, does benefit to and carries out deepening processing after retrieving.

Description

Desulfurization and denitrification flue gas advanced treatment method
Technical Field
The invention relates to the field of flue gas treatment, in particular to a flue gas advanced treatment method for desulfurization and denitrification.
Background
The flue gas desulfurization and denitration technology is a boiler flue gas purification technology applied to the chemical industry of generating multi-nitrogen oxides and sulfur oxides. Nitrogen oxides and sulfur oxides are one of the main sources of air pollution. The application of this technology is of considerable benefit for ambient air purification.
Wherein, the washing and absorption of the nitrogen oxides and the sulfur oxides contained in the flue gas by various washing liquids are widely applied to the treatment of the flue gas due to the simple equipment required and good washing effect;
however, the existing washing mode is usually a mode of single washing by spraying, the contact time of the washing liquid and the flue gas is short, deep absorption cannot be carried out, and the washing effect is poor;
how to improve the washing mode and improve the washing effect of the flue gas is urgently needed to be solved.
Disclosure of Invention
Aiming at the technical problems in the prior art, the invention provides a flue gas advanced treatment method for desulfurization and denitrification.
The technical scheme for solving the technical problems is as follows:
a flue gas advanced treatment method for desulfurization and denitrification,
comprises a washing tank, wherein a plurality of transverse partition plates are arranged in the washing tank to divide the interior of the washing tank into a plurality of independent washing areas;
an air inlet chamber is arranged at the bottom of the washing tank, the flue gas is introduced into the air inlet chamber through an air inlet channel, an exhaust channel is arranged at the top of the washing tank, and the exhaust channel is communicated with a draught fan;
a first air duct is arranged on each transverse partition plate, the first air duct is of an inverted U-shaped structure, one end of the first air duct penetrates through the transverse partition plate, and the first air duct is communicated with the space below the transverse partition plate;
an overflow pipe is arranged between any adjacent forest washing areas, the upper end of the overflow pipe is communicated with the upper part of the washing area positioned above, and the lower end of the overflow pipe is communicated with the bottom of one washing area positioned below;
the lower end of an overflow pipe of a washing area positioned at the lowest part of the washing tank is communicated with the bottom of the air inlet chamber, and the side wall of the middle part of the air inlet chamber is connected with a liquid outlet;
the air inlet channel is connected to the upper part of the air inlet chamber;
a spray pipe is arranged in the exhaust passage and is connected with a liquid supply mechanism;
the processing steps comprise:
s1, introducing a washing liquid, starting a liquid supply mechanism to introduce the washing liquid into the washing tank through a spray pipe, collecting the washing liquid in a washing area at the top after the washing liquid enters the washing tank, overflowing the washing liquid into a next washing area through an overflow pipe when the liquid level of the washing liquid in the washing area rises to the height of the overflow pipe, and sequentially collecting washing liquid submerging areas with a certain depth in each washing area;
s2, introducing the flue gas, starting the induced draft fan after the washing liquid overflows in the liquid discharge port, forming a negative pressure environment in each washing area from top to bottom, finally forming a negative pressure environment in the air inlet cavity, introducing the flue gas, sequentially and upwards introducing the flue gas into each washing area through the first air guide pipe for washing, and finally discharging the flue gas out of the washing tank after the raw liquid passing through the washing liquid in the exhaust passage is sprayed and washed.
Further limiting, a plurality of air distribution holes are formed in the side wall of the exhaust end of the first air guide pipe, and the air distribution holes are located below the liquid level of the washing liquid.
Further limiting, an air guide inner tube is arranged in the exhaust end of the first air guide tube, and a fixing ring for fixing the upper end of the air guide inner tube is arranged above the air distribution hole in the first air guide tube;
the lower end of the air guide inner pipe is positioned in the first air guide pipe;
the ratio of the inner diameter of the air guide inner pipe to the inner diameter of the first air guide pipe is 1: 3-1: 2, and an air distribution channel is arranged between the outer wall of the air guide inner pipe and the inner wall of the first air guide pipe.
The upper end of the overflow pipe extends into the washing area and bends downwards to extend to the bottom of the washing area;
and the overflow pipes are provided with regulating valves for regulating the flux of the overflow pipes.
Further limiting, a dust remover is arranged at the air inlet end of the air inlet channel, and the dust remover is any one of a cyclone dust remover or a bag-type dust remover.
Further limiting, an air baffle is arranged in the air inlet cavity, and the air baffle divides the inner wall of the air inlet cavity into an air collecting chamber which is positioned above the air baffle and used for introducing and spreading smoke and an liquid collecting chamber which is positioned below the air baffle and used for collecting washing liquid;
the upper end of the second air duct is communicated with the air collection chamber, and the lower end of the second air duct extends below the liquid level of the liquid collection chamber;
the air inlet end of the first air duct of the washing area positioned at the lowest part extends downwards into the liquid collecting chamber and is positioned above the liquid level of the liquid collecting chamber;
the structure of the lower end of the second air duct is the same as that of the air outlet end of the first air duct.
The invention has the beneficial effects that:
the flue gas is guided into each washing zone from bottom to top in the guiding direction by arranging the plurality of washing zones, the washing liquid is collected and reserved in each washing zone to serve as a submerging zone, the flue gas is guided into the submerging zone by the first gas guide pipe to be washed, then is guided into the next washing zone, passes through each submerging zone in sequence to be washed, and finally is sprayed and washed by the raw liquid of the washing liquid in the exhaust passage, so that the washing effect on the flue gas can be effectively improved;
the circulation process of washing liquid is located the inside of washing jar, lies in that the flue gas can fully retrieve after carrying out absorption reaction, does benefit to and carries out deepening processing after retrieving.
Drawings
FIG. 1 is a schematic view of the construction of a wash tank;
FIG. 2 is a schematic view of the structure of the outlet end of the first airway tube;
in the drawings, the components represented by the respective reference numerals are listed below:
the device comprises a washing tank 1, a transverse partition plate 2, a washing area 3, an air inlet cavity chamber 4, an air inlet channel 5, an exhaust channel 6, an induced draft fan 7, a first air duct 8, an overflow pipe 9, a liquid outlet 10, a spray pipe 11, a regulating valve 12, a dust remover 13, an air baffle 14, an air collection chamber 15, an air collection chamber 16, a second air duct 17, an air distribution hole 18, an air guide inner tube 19 and a fixing ring 20.
Detailed Description
The principles and features of this invention are described below in conjunction with the following drawings, which are set forth by way of illustration only and are not intended to limit the scope of the invention.
As shown in fig. 1 and fig. 2, a flue gas advanced treatment method for desulfurization and denitrification,
comprises a washing tank 1, a plurality of transverse clapboards 2 are arranged in the washing tank 1, and the interior of the washing tank 1 is divided into a plurality of independent washing areas 3;
an air inlet chamber 4 is arranged at the bottom of the washing tank 1, the flue gas is introduced into the air inlet chamber 4 through an air inlet channel 5, an exhaust channel 6 is arranged at the top of the washing tank 1, and the exhaust channel 6 is communicated with an induced draft fan 7;
a first air duct 8 is arranged on each transverse partition plate 2, the first air duct 8 is of an inverted U-shaped structure, one end of the first air duct penetrates through the transverse partition plate 2, and the first air duct is communicated with the space below the transverse partition plate 2;
an overflow pipe 9 is arranged between any adjacent forest washing areas 3, the upper end of the overflow pipe 9 is communicated with the upper part of the washing area 3 positioned above, and the lower end of the overflow pipe 9 is communicated with the bottom of one washing area 3 positioned below;
the lower end of an overflow pipe 9 of the washing area 3 positioned at the lowest part of the washing tank 1 is communicated with the bottom of the air inlet chamber 4, and the side wall of the middle part of the air inlet chamber 4 is connected with a liquid outlet 10;
the air inlet 5 is connected to the upper part of the air inlet chamber 4;
a spray pipe 11 is arranged in the exhaust passage 6, and the spray pipe 11 is connected with a liquid supply mechanism;
the processing steps comprise:
s1, introducing a washing liquid, starting a liquid supply mechanism to introduce the washing liquid into the washing tank 1 through the spray pipe 11, collecting the washing liquid in one washing area 3 at the uppermost part after the washing liquid enters the washing tank 1, overflowing the washing liquid into the next washing area 3 through the overflow pipe 9 when the liquid level of the washing liquid in the washing area 3 rises to the height of the overflow pipe 9, and sequentially collecting a washing liquid submerged area with a certain depth in each washing area 3;
s2, introducing the flue gas, starting the induced draft fan 7 after the washing liquid overflows from the liquid discharge port 10, forming a negative pressure environment in each washing area 3 from top to bottom, finally forming a negative pressure environment in the air inlet cavity 4 for introducing the flue gas, sequentially introducing the flue gas upwards into each washing area 3 through the first air guide pipe 8 for washing, and finally discharging the flue gas out of the washing tank 1 after the raw liquid passing through the washing liquid is sprayed and washed in the exhaust passage 6.
The side wall of the exhaust end of the first air duct 8 is provided with a plurality of air distribution holes 18, and the air distribution holes 18 are positioned below the liquid level of the washing liquid.
An air guide inner tube 19 is arranged in the exhaust end of the first air guide tube 8, and a fixing ring 20 for fixing the upper end of the air guide inner tube 19 is arranged above the air distribution holes 18 in the first air guide tube 8;
the lower end of the air guide inner tube 19 is positioned in the first air guide tube 8;
the ratio of the inner diameter of the air guide inner tube 19 to the inner diameter of the first air guide tube 8 is 1:3 to 1:2, and an air distribution channel is arranged between the outer wall of the air guide inner tube 19 and the inner wall of the first air guide tube 8.
The upper end of the overflow pipe 9 extends into the washing area 3 and bends downwards to extend to the bottom of the washing area 3;
the overflow pipes 9 are all provided with regulating valves 12 for regulating the flux of the overflow pipes 9.
The air inlet end of the air inlet channel 5 is provided with a dust remover 13, and the dust remover 13 is any one of a cyclone dust remover 13 or a bag-type dust remover 13.
An air baffle plate 14 is arranged in the air inlet chamber 4, and the air baffle plate 14 divides the inner wall of the air inlet chamber 4 into an air collecting chamber 15 which is positioned above the air baffle plate 14 and used for introducing and spreading flue gas and a liquid collecting chamber 16 which is positioned below the air baffle plate 14 and used for collecting washing liquid;
a second air duct 17 is arranged on the air baffle 14, the upper end of the second air duct 17 is communicated with the air collection chamber 15, and the lower end of the second air duct 17 extends below the liquid level of the liquid collection chamber 16;
the air inlet end of the first air duct 8 of the lowest washing zone 3 extends downwards into the liquid collecting chamber 16 and is positioned above the liquid level of the liquid collecting chamber 16;
the structure of the lower end of the second air duct 17 is the same as that of the air outlet end of the first air duct 8.
In this embodiment:
by arranging the plurality of washing areas 3, the smoke is introduced into each washing area 3 from the bottom to the top in the introduction direction, the washing liquid is collected and reserved in each washing area 3 to serve as a submerged area, the smoke is introduced into the submerged area by the first air duct 8 for washing, then introduced into the next washing area 3, sequentially passes through each submerged area for washing, and finally passes through the original liquid of the washing liquid for spraying and washing in the exhaust duct 6, so that the washing effect on the smoke can be effectively improved;
the circulation process of the washing liquid is located in the washing tank 1, the washing liquid can be fully recovered after the flue gas is subjected to absorption reaction, and the deep treatment is favorably carried out after the recovery.
The above description is only for the purpose of illustrating the preferred embodiments of the present invention and is not to be construed as limiting the invention, and any modifications, equivalents, improvements and the like that fall within the spirit and principle of the present invention are intended to be included therein.

Claims (6)

1. A desulfurization and denitrification flue gas advanced treatment method is characterized by comprising the following steps:
comprises a washing tank, wherein a plurality of transverse partition plates are arranged in the washing tank to divide the interior of the washing tank into a plurality of independent washing areas;
an air inlet chamber is arranged at the bottom of the washing tank, the flue gas is introduced into the air inlet chamber through an air inlet channel, an exhaust channel is arranged at the top of the washing tank, and the exhaust channel is communicated with a draught fan;
a first air duct is arranged on each transverse partition plate, the first air duct is of an inverted U-shaped structure, one end of the first air duct penetrates through the transverse partition plate, and the first air duct is communicated with the space below the transverse partition plate;
an overflow pipe is arranged between any adjacent forest washing areas, the upper end of the overflow pipe is communicated with the upper part of the washing area positioned above, and the lower end of the overflow pipe is communicated with the bottom of one washing area positioned below;
the lower end of an overflow pipe of a washing area positioned at the lowest part of the washing tank is communicated with the bottom of the air inlet chamber, and the side wall of the middle part of the air inlet chamber is connected with a liquid outlet;
the air inlet channel is connected to the upper part of the air inlet chamber;
a spray pipe is arranged in the exhaust passage and is connected with a liquid supply mechanism;
the processing steps comprise:
s1, introducing a washing liquid, starting a liquid supply mechanism to introduce the washing liquid into the washing tank through a spray pipe, collecting the washing liquid in a washing area at the top after the washing liquid enters the washing tank, overflowing the washing liquid into a next washing area through an overflow pipe when the liquid level of the washing liquid in the washing area rises to the height of the overflow pipe, and sequentially collecting washing liquid submerging areas with a certain depth in each washing area;
s2, introducing the flue gas, starting the induced draft fan after the washing liquid overflows in the liquid discharge port, forming a negative pressure environment in each washing area from top to bottom, finally forming a negative pressure environment in the air inlet cavity, introducing the flue gas, sequentially and upwards introducing the flue gas into each washing area through the first air guide pipe for washing, and finally discharging the flue gas out of the washing tank after the raw liquid passing through the washing liquid in the exhaust passage is sprayed and washed.
2. The desulfurization and denitrification flue gas advanced treatment method according to claim 1, characterized in that: the side wall of the exhaust end of the first air duct is provided with a plurality of air distribution holes, and the air distribution holes are positioned below the liquid level of the washing liquid.
3. The desulfurization and denitrification flue gas advanced treatment method according to claim 2, characterized in that: an air guide inner pipe is arranged in the exhaust end of the first air guide pipe, and a fixing ring for fixing the upper end of the air guide inner pipe is arranged above the air distribution hole in the first air guide pipe;
the lower end of the air guide inner pipe is positioned in the first air guide pipe;
the ratio of the inner diameter of the air guide inner pipe to the inner diameter of the first air guide pipe is 1: 3-1: 2, and an air distribution channel is arranged between the outer wall of the air guide inner pipe and the inner wall of the first air guide pipe.
4. The desulfurization and denitrification flue gas advanced treatment method according to claim 3, characterized in that: the upper end of the overflow pipe extends into the washing area and bends downwards to extend to the bottom of the washing area;
and the overflow pipes are provided with regulating valves for regulating the flux of the overflow pipes.
5. The desulfurization and denitrification flue gas advanced treatment method according to claim 4, characterized in that: the air inlet end of the air inlet channel is provided with a dust remover, and the dust remover is any one of a cyclone dust remover or a bag-type dust remover.
6. The desulfurization and denitrification flue gas advanced treatment method according to claim 5, characterized in that: an air baffle is arranged in the air inlet cavity, and the inner wall of the air inlet cavity is divided into an air collecting chamber which is positioned above the air baffle and used for introducing and spreading smoke and a liquid collecting chamber which is positioned below the air baffle and used for collecting washing liquid by the air baffle;
the upper end of the second air duct is communicated with the air collection chamber, and the lower end of the second air duct extends below the liquid level of the liquid collection chamber;
the air inlet end of the first air duct of the washing area positioned at the lowest part extends downwards into the liquid collecting chamber and is positioned above the liquid level of the liquid collecting chamber;
the structure of the lower end of the second air duct is the same as that of the air outlet end of the first air duct.
CN202011117602.7A 2020-10-19 2020-10-19 Desulfurization and denitrification flue gas advanced treatment method Pending CN112295391A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202011117602.7A CN112295391A (en) 2020-10-19 2020-10-19 Desulfurization and denitrification flue gas advanced treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202011117602.7A CN112295391A (en) 2020-10-19 2020-10-19 Desulfurization and denitrification flue gas advanced treatment method

Publications (1)

Publication Number Publication Date
CN112295391A true CN112295391A (en) 2021-02-02

Family

ID=74327821

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202011117602.7A Pending CN112295391A (en) 2020-10-19 2020-10-19 Desulfurization and denitrification flue gas advanced treatment method

Country Status (1)

Country Link
CN (1) CN112295391A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114288826A (en) * 2021-12-30 2022-04-08 苏州赢众环保有限公司 Height difference overflow water supplementing method for multistage waste gas spray tower

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP2653210A1 (en) * 2012-04-18 2013-10-23 Siemens Aktiengesellschaft Combustion assembly with flue gas washing and CO2 removal and method for operating same
CN105597513A (en) * 2016-01-29 2016-05-25 石家庄宇清环保科技有限公司 Flue gas desulfurizing and dust removing device of coal-fired boiler
CN205461533U (en) * 2016-04-01 2016-08-17 临沂金誉石化有限公司 Washing tank of petrochemical production usefulness
CN106178752A (en) * 2016-08-28 2016-12-07 安徽天承科自动化科技有限公司 A kind of assembled smoke gas washing tank
CN208406627U (en) * 2018-05-30 2019-01-22 安徽思科环境系统工程技术有限公司 A kind of flue gas desulfurization and denitrification device

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP2653210A1 (en) * 2012-04-18 2013-10-23 Siemens Aktiengesellschaft Combustion assembly with flue gas washing and CO2 removal and method for operating same
CN105597513A (en) * 2016-01-29 2016-05-25 石家庄宇清环保科技有限公司 Flue gas desulfurizing and dust removing device of coal-fired boiler
CN205461533U (en) * 2016-04-01 2016-08-17 临沂金誉石化有限公司 Washing tank of petrochemical production usefulness
CN106178752A (en) * 2016-08-28 2016-12-07 安徽天承科自动化科技有限公司 A kind of assembled smoke gas washing tank
CN208406627U (en) * 2018-05-30 2019-01-22 安徽思科环境系统工程技术有限公司 A kind of flue gas desulfurization and denitrification device

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114288826A (en) * 2021-12-30 2022-04-08 苏州赢众环保有限公司 Height difference overflow water supplementing method for multistage waste gas spray tower
CN114288826B (en) * 2021-12-30 2024-03-19 苏州赢众环保有限公司 Height difference overflow water supplementing method of multi-stage waste gas spray tower

Similar Documents

Publication Publication Date Title
US8496742B2 (en) Wet flue-gas desulfurization equipment
CN1021020C (en) Method and apparatus for treatment of waste gas containing dusts and chemical contaminants
JP2018023967A (en) Desulfurization process based on ammonia via ammonia addition in different chambers and device
CN206198997U (en) Flue gas desulfurization denitration dust-removing system
CN105148699B (en) A kind of single column oxidation sweetening denitrification apparatus and its desulfurization denitration method
CN112295391A (en) Desulfurization and denitrification flue gas advanced treatment method
CN105833719A (en) Industrial smoke multi-pollutant deep purification device and technology
CN109499287A (en) A kind of wet scrubber tower and medical wastes incineration acid gas processing method
CN112023636A (en) Flue gas treatment washing tower
CN210278778U (en) Industrial purification system for removing sulfide gas
CN208865434U (en) A kind of flue gas during smelting desulfurization removing heavy metals integrated synthesis governing system
CN107126840B (en) Flue gas desulfurization denitration equipment line
KR101448459B1 (en) Wet scrubber
CN212417551U (en) Waste gas treatment system
CN212262795U (en) Waste gas discharge system
CN210845840U (en) Flue gas purification system
CN210814672U (en) Novel alkaline washing tower for treating volatile organic waste gas
CN206642511U (en) Differential submersible gas wash tower
CN210699518U (en) Flue gas desulfurization absorption device
CN209451612U (en) A kind of integrated efficient absorption reaction device
CN111634990A (en) Device for removing carbonate and bicarbonate radical in cobaltic wastewater
CN210021582U (en) Processing equipment for discharging flue gas by slag discharging roller
CN206391852U (en) Biomass boiler nitrogen rejection facility
CN109364719A (en) A kind of boiler smoke scrubbing tower
CN217627911U (en) Waste gas treatment equipment for sewage treatment

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20210202

RJ01 Rejection of invention patent application after publication