CN107875819B - Wet flue gas desulfurization tower - Google Patents

Wet flue gas desulfurization tower Download PDF

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Publication number
CN107875819B
CN107875819B CN201711351258.6A CN201711351258A CN107875819B CN 107875819 B CN107875819 B CN 107875819B CN 201711351258 A CN201711351258 A CN 201711351258A CN 107875819 B CN107875819 B CN 107875819B
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China
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cylinder
stage
spraying
stage spray
flue gas
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CN201711351258.6A
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CN107875819A (en
Inventor
田富姣
辛银平
葛怀波
谭鹏宇
李瑶瑶
殷军翔
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Liaoning Teli Environmental Protection Technology Co ltd
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Liaoning Teli Environmental Protection Technology Co ltd
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    • 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
    • B01D53/48Sulfur compounds
    • B01D53/50Sulfur oxides
    • B01D53/501Sulfur oxides by treating the gases with a solution or a suspension of an alkali or earth-alkali or ammonium compound
    • B01D53/504Sulfur oxides by treating the gases with a solution or a suspension of an alkali or earth-alkali or ammonium compound characterised by a specific device
    • 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
    • B01D53/75Multi-step processes
    • 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
    • B01D53/80Semi-solid phase processes, i.e. by using slurries
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/40Alkaline earth metal or magnesium compounds
    • B01D2251/404Alkaline earth metal or magnesium compounds of calcium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • B01D2258/0283Flue gases

Abstract

A wet flue gas desulfurization tower comprises a tower body, wherein a spray layer in the tower body comprises a baffle plate, a first-stage spray cylinder, a second-stage spray cylinder and a third-stage spray cylinder; the partition board is connected with the inner wall of the tower body, the top of the first-stage spraying cylinder penetrates through the partition board and extends to the upper part of the partition board, the top of the second-stage spraying cylinder extends to the upper part of the top of the first-stage spraying cylinder, the top of the third-stage spraying cylinder extends to the upper part of the top of the second-stage spraying cylinder, and the bottoms of the first-stage spraying cylinder and the second-stage spraying cylinder are all opened, so that a first-stage spraying cavity is formed among the outer wall of the first-stage spraying cylinder, the partition board and the inner wall of the tower body, a second-stage spraying cavity is formed between the inner wall of the first-stage spraying cylinder and the outer wall of the second-stage spraying cylinder, and a third-stage spraying cavity is formed between the inner wall of the second-stage spraying cylinder and the outer wall of the third-stage spraying cylinder; the upper parts of the first-stage spray cavity, the second-stage spray cavity and the third-stage spray cavity are respectively provided with a first vent hole, a second vent hole and a third vent hole, and the top of the third-stage spray cylinder is provided with an air outlet. The flue gas is uniformly distributed in the tower body, the slurry is fully contacted with the flue gas, and the desulfurization effect is good.

Description

Wet flue gas desulfurization tower
Technical Field
The invention belongs to the technical field of desulfurization dust removal equipment, and particularly relates to a wet flue gas desulfurization tower.
Background
Flue gas desulfurization refers to the removal of Sulfur Oxides (SO) from flue gas or other industrial waste gases 2 And SO 3 ) SO in flue gas 2 Essentially an acidRemoving SO from flue gas by reaction with suitable alkaline substances 2 . The most common alkaline material for flue gas desulfurization is limestone (calcium carbonate, caCO) 3 ) Quicklime (calcium oxide, caO) and slaked lime (calcium hydroxide, ca (OH) 2 ). Limestone is produced in high yield and is therefore relatively inexpensive, and both quicklime and slaked lime are produced from limestone by heating. In wet flue gas desulfurization systems, alkaline material (typically an alkaline solution, more typically a slurry of the alkali) is encountered with the flue gas in a spray tower. SO in flue gas 2 Dissolved in water to form a dilute acid solution, and then subjected to neutralization reaction with an alkaline substance dissolved in water. The sulfite and sulfate salts formed by the reaction precipitate from the aqueous solution, depending on the relative solubilities of the different salts present in the solution.
The existing wet flue gas desulfurization tower generally comprises a slurry pond, a spraying layer and a demister, wherein the spraying layer is simple in structure, uneven in flue gas distribution, poor in desulfurization effect, capable of enabling slurry to be in insufficient contact with the flue gas, and capable of only performing primary desulfurization on the flue gas and the slurry, and if multiple desulfurization is required, the spraying layer can be added, so that the height of the desulfurization tower is increased, and the production cost is increased.
Disclosure of Invention
The invention aims at: aiming at the problem of poor desulfurization effect caused by uneven flue gas distribution in the spraying desulfurization of the existing wet flue gas desulfurization tower, the invention provides the wet flue gas desulfurization tower.
The technical scheme adopted by the invention is as follows:
the wet flue gas desulfurization tower comprises a tower body, wherein a slurry pool, a spray layer and a demister are sequentially arranged in the tower body from bottom to top, a flue gas inlet is formed in the lower part of the tower body, a flue gas outlet is formed in the top of the tower body, and the spray layer comprises a partition plate, a first-stage spray cylinder, a second-stage spray cylinder arranged in the first-stage spray cylinder and a third-stage spray cylinder arranged in the second-stage spray cylinder; the top of the first-stage spray cylinder penetrates through the partition plate and extends to the upper part of the partition plate, the top of the second-stage spray cylinder penetrates through the top of the first-stage spray cylinder and extends to the upper part of the top of the first-stage spray cylinder, the top of the third-stage spray cylinder penetrates through the top of the second-stage spray cylinder and extends to the upper part of the top of the second-stage spray cylinder, and the bottoms of the first-stage spray cylinder and the second-stage spray cylinder are both opened, so that a first-stage spray cavity is formed among the outer wall of the first-stage spray cylinder, the partition plate and the inner wall of the tower body, a second-stage spray cavity is formed among the inner wall of the first-stage spray cylinder and the outer wall of the second-stage spray cylinder, and a third-stage spray cavity is formed among the inner wall of the second-stage spray cylinder and the outer wall of the third-stage spray cylinder; the upper part of the primary spraying cavity is provided with a first vent hole communicated with the secondary spraying cavity, the upper part of the secondary spraying cavity is provided with a second vent hole communicated with the tertiary spraying cavity, the upper part of the tertiary spraying cavity is provided with a third vent hole communicated with the tertiary spraying cylinder, and the top of the tertiary spraying cylinder is provided with an air outlet; the upper parts of the primary spraying cavity, the secondary spraying cavity and the tertiary spraying cavity are respectively provided with an annular spray pipe connected with the slurry pool, and the annular spray pipes are provided with evenly distributed spray nozzles.
When the desulfurization tower works, flue gas to be desulfurized enters the tower body from the flue gas inlet, then is divided into three parts under the action of the first-stage spray cylinder, the second-stage spray cylinder and the third-stage spray cylinder, flue gas close to the inner wall of the tower body enters the first-stage spray cavity, flue gas positioned in the middle of the tower body enters the third-stage spray cavity, the rest flue gas enters the second-stage spray cavity, then slurry is introduced into the annular spray pipe through the slurry pond, and spray desulfurization is carried out through uniformly distributed nozzles, so that the flue gas entering the tower body can realize batch desulfurization, the flue gas is uniformly distributed in the tower body, full contact between the slurry and the flue gas is facilitated, and the desulfurization effect is good. Flue gas in the first-stage spraying cavity enters the second-stage spraying cavity through the first vent hole and is subjected to secondary desulfurization in the second-stage spraying cavity, similarly, flue gas in the second-stage spraying cavity enters the third-stage spraying cavity through the second vent hole to continuously perform desulfurization, flue gas in the third-stage spraying cavity enters the third-stage spraying cylinder through the third vent hole, and then is discharged from the air outlet to be defogged, and finally is discharged from the flue gas outlet, so that sprayed slurry re-enters the slurry pond.
Further, the slurry pool is connected with an oxidation fan. The oxidation blower provides oxygen for the slurry pool to react, so that the sulfite forms stable sulfate and is crystallized.
Further, a stirrer is arranged in the slurry pool. The stirrer prevents precipitation of the slurry pool and enhances the oxidation effect.
Further, the slurry pond pumps the slurry to the spray level via a circulation pump.
In summary, due to the adoption of the technical scheme, the beneficial effects of the invention are as follows:
1. according to the invention, the primary spraying cylinder, the secondary spraying cylinder and the tertiary spraying cylinder are arranged, so that the flue gas is uniformly distributed in the tower body, batch desulfurization is realized through the annular spray pipe, and the slurry is fully contacted with the flue gas, so that the desulfurization effect is good;
2. the flue gas in the first-stage spray cavity passes through the second-stage spray cavity and the third-stage spray cavity before entering the third-stage spray cylinder, so that three desulfurization is realized, the desulfurization is thorough, and similarly, the flue gas in the second-stage spray cavity can realize two desulfurization;
drawings
FIG. 1 is a schematic diagram of the structure of the present invention;
fig. 2 is a schematic view of the spray layer structure of the present invention.
The marks in the figure: the device comprises a 1-tower body, a 2-demister, a 3-air outlet, a 4-secondary spray cylinder, a 5-primary spray cylinder, a 6-circulating pump, a 7-oxidation fan, an 8-tertiary spray cylinder, a 9-slurry pool, a 10-stirrer, an 11-flue gas inlet, a 12-first vent hole, a 13-nozzle, a 14-annular spray pipe, a 15-partition plate, a 16-second vent hole, a 17-third vent hole and an 18-flue gas outlet.
Detailed Description
All of the features disclosed in this specification, except for mutually exclusive features and/or steps, may be combined in any manner.
The present invention will be described in detail with reference to fig. 1 and 2.
Example 1
The wet flue gas desulfurization tower comprises a tower body 1, wherein a slurry pool 9, a spray layer and a demister 2 are sequentially arranged in the tower body 1 from bottom to top, a flue gas inlet 11 is arranged at the lower part of the tower body 1, a flue gas outlet 18 is arranged at the top of the tower body 1, and the spray layer comprises a partition plate 15, a primary spray cylinder 5, a secondary spray cylinder 4 arranged in the primary spray cylinder 5 and a tertiary spray cylinder 8 arranged in the secondary spray cylinder 4; the partition plate 15 is in sealing connection with the inner wall of the tower body 1, the top of the first-stage spray cylinder 5 passes through the partition plate 15 and extends to the upper part of the partition plate 15, the top of the second-stage spray cylinder 4 passes through the top of the first-stage spray cylinder 5 and extends to the upper part of the top of the first-stage spray cylinder 5, the top of the third-stage spray cylinder 8 passes through the top of the second-stage spray cylinder 4 and extends to the upper part of the top of the second-stage spray cylinder 4, and the bottoms of the first-stage spray cylinder 5 and the second-stage spray cylinder 4 are both opened, so that a first-stage spray cavity is formed among the outer wall of the first-stage spray cylinder 5, the partition plate 15 and the inner wall of the tower body 1, a second-stage spray cavity is formed among the inner wall of the first-stage spray cylinder 5 and the outer wall of the second-stage spray cylinder 4, and a third-stage spray cavity is formed among the inner wall of the second-stage spray cylinder 4 and the outer wall of the third-stage spray cylinder 8; the upper part of the primary spraying cavity is provided with a first vent hole 12 communicated with the secondary spraying cavity, the upper part of the secondary spraying cavity is provided with a second vent hole 16 communicated with the tertiary spraying cavity, the upper part of the tertiary spraying cavity is provided with a third vent hole 17 communicated with the tertiary spraying cylinder 8, and the top of the tertiary spraying cylinder 8 is provided with an air outlet 3; the upper parts of the primary spraying cavity, the secondary spraying cavity and the tertiary spraying cavity are respectively provided with an annular spraying pipe 14 connected with the slurry pool 9, and the annular spraying pipes 14 are provided with evenly distributed nozzles 13.
When the desulfurization tower provided by the invention works, flue gas to be desulfurized enters the tower body 1 from the flue gas inlet 11, is then divided into three parts under the action of the primary spraying cylinder 5, the secondary spraying cylinder 4 and the tertiary spraying cylinder 8, flue gas close to the inner wall of the tower body 1 enters the primary spraying cavity, flue gas in the middle position of the tower body 1 enters the tertiary spraying cavity, the rest flue gas enters the secondary spraying cavity, then slurry pond 9 is filled with slurry into the annular spray pipe 14, and spray desulfurization is carried out through uniformly distributed nozzles 13, so that the flue gas entering the tower body 1 can realize batch desulfurization, the flue gas is uniformly distributed in the tower body 1, full contact between the slurry and the flue gas is facilitated, and the desulfurization effect is good. Flue gas in the first-stage spraying cavity enters the second-stage spraying cavity through the first vent hole 12 and is subjected to secondary desulfurization in the second-stage spraying cavity, and similarly, flue gas in the second-stage spraying cavity enters the third-stage spraying cavity through the second vent hole 16 to continuously perform desulfurization, flue gas in the third-stage spraying cavity enters the third-stage spraying cylinder 8 through the third vent hole 17, is discharged from the air outlet 3 and is defogged, and finally is discharged from the flue gas outlet 18, and the slurry after spraying enters the slurry pond 9 again.
Example 2
Based on embodiment 1, an oxidation blower 7 is connected to the slurry tank 9. The oxidation blower 7 supplies oxygen to the slurry tank 9 for reaction, so that the sulfite forms stable sulfate and is crystallized.
Example 3
Based on examples 1 and 2, a stirrer 10 is provided in the slurry tank 9. The agitator 10 prevents precipitation of the slurry pool 9 and enhances the oxidation effect.
Example 4
Based on examples 1 and 2, the slurry tank 9 pumps the slurry to the spray level by the circulation pump 6.
The above-described embodiments of the present invention. The present invention is not limited to the above embodiments, and any person who can learn about the structural changes made under the teaching of the present invention falls within the scope of protection of the present invention if the present invention has the same or similar technical solutions.

Claims (2)

1. The wet flue gas desulfurization tower comprises a tower body (1), wherein a slurry pool (9), a spraying layer and a demister (2) are sequentially arranged in the tower body (1) from bottom to top, a flue gas inlet (11) is formed in the lower part of the tower body (1), and a flue gas outlet (18) is formed in the top of the tower body (1), and the wet flue gas desulfurization tower is characterized in that the spraying layer comprises a partition plate (15), a primary spraying cylinder (5), a secondary spraying cylinder (4) arranged in the primary spraying cylinder (5) and a tertiary spraying cylinder (8) arranged in the secondary spraying cylinder (4);
the top of the first-stage spray cylinder (5) penetrates through the partition plate (15) and extends to the upper part of the partition plate (15), the top of the second-stage spray cylinder (4) penetrates through the top of the first-stage spray cylinder (5) and extends to the upper part of the top of the first-stage spray cylinder (5), the top of the third-stage spray cylinder (8) penetrates through the top of the second-stage spray cylinder (4) and extends to the upper part of the top of the second-stage spray cylinder (4), the bottoms of the first-stage spray cylinder (5) and the second-stage spray cylinder (4) are all open, so that a first-stage spray cavity is formed among the outer wall of the first-stage spray cylinder (5), the partition plate (15) and the inner wall of the tower (1), a second-stage spray cavity is formed among the inner wall of the first-stage spray cylinder (5) and the outer wall of the second-stage spray cylinder (4), and a third-stage spray cavity is formed among the inner wall of the second-stage spray cylinder (4) and the outer wall of the third-stage spray cylinder (8);
the upper part of the primary spraying cavity is provided with a first vent hole (12) communicated with the secondary spraying cavity, the upper part of the secondary spraying cavity is provided with a second vent hole (16) communicated with the tertiary spraying cavity, the upper part of the tertiary spraying cavity is provided with a third vent hole (17) communicated with the tertiary spraying cylinder (8), and the top of the tertiary spraying cylinder (8) is provided with an air outlet (3);
the upper parts of the primary spraying cavity, the secondary spraying cavity and the tertiary spraying cavity are respectively provided with an annular spraying pipe (14) connected with the slurry pool (9), and the annular spraying pipes (14) are provided with evenly distributed nozzles (13);
a stirrer (10) is arranged in the slurry pool (9);
the slurry pool (9) pumps the slurry to the spraying layer through the circulating pump (6).
2. Wet flue gas desulfurization tower according to claim 1, characterized in that the slurry tank (9) is connected with an oxidation fan (7).
CN201711351258.6A 2017-12-15 2017-12-15 Wet flue gas desulfurization tower Active CN107875819B (en)

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CN107875819B true CN107875819B (en) 2024-01-30

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Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109012038A (en) * 2018-08-10 2018-12-18 杨明超 A kind of equipment for treating industrial waste gas
CN112275114A (en) * 2020-09-09 2021-01-29 程学芳 Two-stage wet desulphurization tower

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CN206152618U (en) * 2016-08-30 2017-05-10 杭州玺清环保科技有限公司 Fit high -efficient desulphurization unit in four districts of doublestage
CN206199001U (en) * 2016-10-17 2017-05-31 上海锅炉厂有限公司 A kind of desulfurizer
CN206473953U (en) * 2017-01-19 2017-09-08 东莞市宇鑫净化工程有限公司 Waste gas water washing device
CN207786294U (en) * 2017-12-15 2018-08-31 河南省正大环境科技咨询工程有限公司 A kind of wet flue gas desulfurization tower

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CN1066721A (en) * 1991-09-18 1992-12-02 哈尔滨市永吉实业有限公司 Gas-washing method and multifunctional air purifying device
JP3051003U (en) * 1998-01-29 1998-08-11 台典汚染防治股▲ふん▼有限公司 Chimney improvement structure capable of capturing harmful substances from combustion waste gas
CN2384670Y (en) * 1999-07-15 2000-06-28 孙伊凡 Spiral-flow spray-type desulfuring dust remover
CN2683235Y (en) * 2004-03-16 2005-03-09 沈杞生 Smoke-eliminating, dust-reducing and desulfurizing device
CN201040229Y (en) * 2007-04-06 2008-03-26 东南大学 Flue gas simultaneous desulfurize denitrate integrated two-stage spraying type absorption reactor
CN101890281A (en) * 2010-03-25 2010-11-24 上海洁美环保科技有限公司 Forward flow and backward flow combined spray desulfurizing tower
CN201880482U (en) * 2010-11-19 2011-06-29 上海弗卡斯环保工程有限公司 Stepped spray tower for desulfurization by ammonia method
CN201871323U (en) * 2010-12-05 2011-06-22 长春高科能源环境工程有限公司 Energy-saving desulfurizing tower
JP2013176712A (en) * 2012-02-28 2013-09-09 Ricoh Co Ltd Fluid purification device
CN202570118U (en) * 2012-06-06 2012-12-05 上虞市双良化工设备有限公司 Spraying tower of improved spraying device
CN202983476U (en) * 2013-01-10 2013-06-12 蓝天环保设备工程股份有限公司 Flue spraying structure of absorption tower
CN203564949U (en) * 2013-11-12 2014-04-30 广东智雄新能源有限公司 Flue gas cleaning system for biomass boiler
CN203777913U (en) * 2014-03-26 2014-08-20 洛阳豫新工程技术有限公司 Gas purification device after pyrolyzing biomass fuel
CN104096471A (en) * 2014-07-08 2014-10-15 中国华电工程(集团)有限公司 Near-zero sulfur dioxide emission absorption tower for coal-fired power plant
CN203955028U (en) * 2014-07-11 2014-11-26 东方电气集团东方锅炉股份有限公司 The two circulation wet flue gas desulfurizers of concurrent-countercurrent list tower
CN104722194A (en) * 2015-03-19 2015-06-24 永清环保股份有限公司 Deep flue gas purification device for efficient desulphurization and dust removal
EP3100781A1 (en) * 2015-06-01 2016-12-07 RUDIS poslovno zdruzenje za inzeniring in izgradnjo objekov d.o.o. Process and apparatus for high performance flue gas cleaning
CN205235755U (en) * 2015-12-29 2016-05-18 神华集团有限责任公司 Desulfurizing spray tower
CN205650072U (en) * 2016-01-27 2016-10-19 南京碧林环保科技有限公司 Dual cycle desulfurization absorption tower
CN206152618U (en) * 2016-08-30 2017-05-10 杭州玺清环保科技有限公司 Fit high -efficient desulphurization unit in four districts of doublestage
CN206199001U (en) * 2016-10-17 2017-05-31 上海锅炉厂有限公司 A kind of desulfurizer
CN206473953U (en) * 2017-01-19 2017-09-08 东莞市宇鑫净化工程有限公司 Waste gas water washing device
CN207786294U (en) * 2017-12-15 2018-08-31 河南省正大环境科技咨询工程有限公司 A kind of wet flue gas desulfurization tower

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