CN206566758U - A kind of SDA methods flue gas desulfurization technique accessory substance self-loopa synergistic device - Google Patents

A kind of SDA methods flue gas desulfurization technique accessory substance self-loopa synergistic device Download PDF

Info

Publication number
CN206566758U
CN206566758U CN201720215774.5U CN201720215774U CN206566758U CN 206566758 U CN206566758 U CN 206566758U CN 201720215774 U CN201720215774 U CN 201720215774U CN 206566758 U CN206566758 U CN 206566758U
Authority
CN
China
Prior art keywords
desulphurization
desulfurizing tower
flue gas
feed bin
tower
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
CN201720215774.5U
Other languages
Chinese (zh)
Inventor
吴朝刚
史德明
包自力
丁陈来
夏勇军
胡笳
方辉
蒋运安
夏小虎
孙廷宇
杨洪
何学愚
郑华权
李丰
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 XINCHUANG ENERGY-SAVING ENVIRONMENTAL PROTECTION TECHNOLOGY Co Ltd
Original Assignee
ANHUI XINCHUANG ENERGY-SAVING ENVIRONMENTAL PROTECTION 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 XINCHUANG ENERGY-SAVING ENVIRONMENTAL PROTECTION TECHNOLOGY Co Ltd filed Critical ANHUI XINCHUANG ENERGY-SAVING ENVIRONMENTAL PROTECTION TECHNOLOGY Co Ltd
Priority to CN201720215774.5U priority Critical patent/CN206566758U/en
Application granted granted Critical
Publication of CN206566758U publication Critical patent/CN206566758U/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Abstract

The utility model discloses a kind of SDA methods flue gas desulfurization technique accessory substance self-loopa synergistic device, including desulfurizing tower, deduster, Desulphurization feed bin;Wherein, desulfurizing tower is connected to deduster by pipeline;The ash discharge storehouse of desulfurizing tower and deduster bottom is connected to Desulphurization feed bin by pipeline, and the ash silo bottom of the Desulphurization feed bin is connected at the top of desulfurizing tower provided with a conveyance conduit, and conveyance conduit one end, which is provided with to dust, in desulfurizing tower tower uses shower nozzle.The utility model is connected at the top of desulfurizing tower in the ash silo bottom of Desulphurization feed bin provided with a conveyance conduit, the powder of conveying is sprayed by shower nozzle in tower, from top to bottom, with smoke contacts, complete desulfurization, it is fully contacted with flue gas, on the basis of absorption, promote absorption of the Desulphurization neutral and alkali material to sour gas, so as to promote desulfurizing and purifying to act on, both the utilization rate of desulfurizing agent can be improved, desulfurized effect can be improved again, contributes to gas cleaning.

Description

A kind of SDA methods flue gas desulfurization technique accessory substance self-loopa synergistic device
Technical field
The utility model belongs to flue gas desulfurization field, is related to a kind of SDA methods flue gas desulfurization technique accessory substance self-loopa synergy System, can be applied to now widely used SDA sulfur removal technologies, and application industry includes Ferrous Metallurgy flue gas desulfurization, coal-burning power plant The SDA method flue gas desulfurization techniques such as flue gas desulfurization and industrial furnace flue gas desulfurization.
Background technology
Rotary spraying and drying (SDA) Summary of Semi-dry Flue Gas Desulfurization, combines the advantage of wet method and semidry method, is a hair Transform into ripe flue gas desulfurization technique.The technology employs rotary sprayer, and investment is less than wet processing, in worldwide To extensive use, utilize more in the country such as Germany, the Italy in West Europe.
Spray dry absorbingatreatingastep technique is that undressed heat smoke is entered after spray dry absorbingatreatingastep tower immediately with being atomized Alkaline desulfurization slurry contact (Ca (OH)2), the acid ingredient (HCL/HF/SO in flue gas2/SO3) by alkaline droplet absorb it is same Shi Shuifen is evaporated, and becomes alkali grain, and flying dust and disengaging slag are discharged from tower bottom is absorbed.The flue gas handled continue into Enter rear deduster, remove remaining suspended particulate.Flue gas after being purified by smoke stack emission.At the same time, absorption tower and dedusting The drying powder granule of device bottom discharge is sent to feed bin, and referring to Fig. 1, spray dry absorbingatreatingastep (SDA) system is additionally provided with use Partial desulfurization slag is recycled for improving as charging to be absorbed and drying property.
Ma'anshan Iron and Steel Co., Ltd has number set SDA sulfur removal technologies to be purified applied to sintering flue gas desulfurization at present. In operation, with the country take numerous producers of SDA sulfur removal technologies as, in operation find there is problems with:
1st, resumed operation initial stage after desulphurization plant maintenance stops production, gas approach end temperature is less than below wet flue gas dew point When, if now carrying out whitewashing desulfuration operations, dust pelletizing system easily breaks down, and flue gas now is discharge beyond standards, is existed Time is typically about 1-5 hours;
Although the 2nd, system oneself provided with desulfurization slag as charging be recycled for improve absorb and drying property, process operation In, from the chemical composition of Desulphurization it is known that calcium hydroxide for flue gas desulfurization, its utilization rate is not high, it is domestic mostly The sorbent utilization of number producer is generally approximately 30% or so;
3rd, it is excessive to use desulfurization slag to be recycled for improving as charging and absorb and drying property, though to improving desulfurizing agent Utilization rate it is favourable, but used desulfurization slag is to the catharsis of flue gas, certainly less than the calcium hydroxide slurry newly produced, And secondary cycle is in use, be usually to be used in mixed way with the calcium hydroxide newly produced, it is substantially reduction of into atomization system The valid density of the calcium hydroxide of system, for chemically reacting, the not absorption using sulfur dioxide in desulfurizing tower and flue gas Qualified discharge.
Utility model content
The purpose of this utility model is to provide a kind of SDA methods flue gas desulfurization technique accessory substance self-loopa synergistic device, this It is to borrow SDA desulfurizing towers on system parenchyma, enhances absorption process, dexterously combined dry desulfurization with semi-dry desulphurization Come, spray desulfurization ashes is turned into a kind of assist type desulfurization means, combine with SDA techniques, formed it is a kind of it is brand-new, can improve The brand-new sulfur removal technology of gas cleaning effect and sorbent utilization.
The purpose of this utility model can be achieved through the following technical solutions:
A kind of SDA methods flue gas desulfurization technique accessory substance self-loopa synergistic device, including desulfurizing tower, deduster, desulfurization ash material Storehouse;Wherein, desulfurizing tower is connected to deduster by pipeline;Desulfurizing tower and the ash discharge storehouse of deduster bottom are connected to by pipeline Desulphurization feed bin, the ash silo bottom of the Desulphurization feed bin is connected at the top of desulfurizing tower provided with a conveyance conduit, in desulfurizing tower tower Conveyance conduit one end, which is provided with to dust, uses shower nozzle.
The conveyance conduit is provided with powder delivery system.
The beneficial effects of the utility model:The utility model connects in the ash silo bottom of Desulphurization feed bin provided with a conveyance conduit It is connected at the top of desulfurizing tower, the powder of conveying is sprayed by shower nozzle in tower, from top to bottom, with smoke contacts, completes desulfurization, make it Fully contacted with flue gas, on the basis of absorption, promote absorption of the Desulphurization neutral and alkali material to sour gas, so as to promote Desulfurizing and purifying is acted on, and can both improve the utilization rate of desulfurizing agent, desulfurized effect can be improved again, contributes to gas cleaning.
Brief description of the drawings
For the ease of it will be appreciated by those skilled in the art that being further described below in conjunction with the accompanying drawings to the utility model.
Fig. 1 is SDA desulphurization systems schematic diagram in the prior art;
Fig. 2 is a kind of SDA methods flue gas desulfurization technique accessory substance self-loopa synergistic device schematic diagram of the utility model.
Embodiment
The technical solution of the utility model is clearly and completely described below in conjunction with embodiment, it is clear that described Embodiment be only a part of embodiment of the utility model, rather than whole embodiment.Based on the reality in the utility model Example is applied, all other embodiment that those of ordinary skill in the art are obtained under the premise of creative work is not made all belongs to The scope protected in the utility model.
Routine SDA desulphurization systems in the prior art, as shown in figure 1, including desulfurizing tower 1, deduster 2, Desulphurization feed bin 3, Quick lime feed bin 4, digester 5;Wherein, desulfurizing tower 1 is connected to deduster 2 by pipeline, the dust flue gas that desulfurizing tower 1 is produced Discharged after the processing of deduster 2;Desulfurizing tower 1 and the ash discharge storehouse of the bottom of deduster 2 are connected to Desulphurization feed bin by pipeline 3, bottom of towe material is delivered to processing in Desulphurization feed bin 3, produces outside Desulphurization and arranges after the processing of Desulphurization feed bin 3;Quick lime feed bin 4 With outside circulating pulp-making pipeline communication, and digester 5 is connected to, the bottom of digester 5 is connected to de- by digestion pulping pipeline The top of sulphur tower 1;
The utility model provides a kind of SDA methods flue gas desulfurization technique accessory substance self-loopa synergistic device, to by Desulphurization Desulfurizing tower top spray powder is pipelined to, implements assist type dry method powder desulfurization, referring to Fig. 2;
It is connected on the top of desulfurizing tower 1, conveyance conduit 6 and sets provided with a conveyance conduit 6 in the ash silo bottom of Desulphurization feed bin 3 There is powder delivery system (being provided by pipeline compressed air or air compressor machine), by powder delivery system by the desulfurization of certain pressure To SDA desulfurization tower tops, in the tower of desulfurizing tower 1, conveyance conduit one end is provided with to dust grey gas-phase transport uses shower nozzle, and the powder of conveying leads to Cross shower nozzle to spray in tower, from top to bottom, with smoke contacts, complete desulfurization.
The Desulphurization powder of penetrating a, part falls into bottom of towe discharge, is partly into the dust pelletizing systems of SDA in itself and collects, Eventually enter into Desulphurization feed bin;The Desulphurization for the part that SDA techniques are produced is used only in powder injection desulphurization, in whole desulfurizer Recycle, eventually through discharging desulphurization system outside Desulphurization feed bin.
Implementation result:
By taking horse steel SDA desulfurizers as an example.The grey chemical composition of self-desulphurization used is shown in Table 1.
The chemical composition of the Desulphurization of table 1
When taking the low-temperature flue gas to enter desulfurizing tower, calcium hydroxide slurry is not sprayed, it is directly (non-using progress front end desulfurization of dusting Nominal situation, now flue gas flow is low, and temperature is low, it is impossible to desulfurization of whitewashing) actual operation data is shown in Table 2.
The single use SDA desulfurizing byproducts of table 2 circulate operation data in SDA processes itself
Data analysis shows, under conditions of not whitewashing, only powder injection desulphurization, in low-temperature flue gas and low-concentration sulfur dioxide Under, desulfuration efficiency is more than 70%!Counter in theory to push away, entrance point sulfur dioxide concentration is higher, constant flue-gas temperature, flow, Under the conditions of the amount of dusting, SDA itself accessory substances carry out front end recycling, it is possible to implement front end desulfurization.
During normal desulfurization production, whitewash and carried out with dusting with reference to synchronous.When shaft furnace opens stove, do not open bypass, desulphurization system with Shaft furnace 100% is run simultaneously.Progress desulfurization data are combined with SDA master operations and are shown in Table 3.
Service data when table 3 mixes desulfurization
Data analysis shows:
(1) in the case where atomizer whitewashing amount is constant, spray into accessory substance after 2-3 minute, arrange mouth sulfur dioxide concentration from 140mg/Nm3Drop to 50mg/Nm3Below;
(2) in the case where control row's mouth sulfur dioxide concentration is basicly stable, atomizer whitewashing amount drops to from 9.4t/h 7.7t/h。
The Desulphurization that SDA techniques are produced in itself, there is following characteristic:Superfine light alkaline particle powder, specific surface area pole Greatly, there is good physisorption to sour gas, solid state powder good fluidity is easily conveyed in the duct.
The Desulphurization directly produced in itself using SDA techniques is dusted in SDA itself desulfurizing tower, makes it abundant with flue gas Contact, on the basis of absorption, promotes absorption of the Desulphurization neutral and alkali material to sour gas, so as to promote desulfurizing and purifying to make With can both improve the utilization rate of desulfurizing agent, desulfurized effect can be improved again, contributes to gas cleaning.
The utility model preferred embodiment disclosed above is only intended to help and illustrates the utility model.Preferred embodiment is simultaneously There is no the details that detailed descriptionthe is all, it is only described embodiment that the utility model is not limited yet.Obviously, according to this theory The content of bright book, can make many modifications and variations.This specification is chosen and specifically describes these embodiments, is in order to preferably Principle of the present utility model and practical application are explained, so that skilled artisan can be best understood by and utilize this Utility model.The utility model is only limited by claims and its four corner and equivalent.

Claims (2)

1. a kind of SDA methods flue gas desulfurization technique accessory substance self-loopa synergistic device, including desulfurizing tower (1), deduster (2), desulfurization Grey feed bin (3);Wherein, desulfurizing tower (1) is connected to deduster (2) by pipeline;Desulfurizing tower (1) and the row of deduster (2) bottom Ash silo is connected to Desulphurization feed bin (3) by pipeline, it is characterised in that the ash silo bottom of the Desulphurization feed bin (3) is provided with One conveyance conduit (6) is connected at the top of desulfurizing tower (1), and conveyance conduit one end, which is provided with to dust, in desulfurizing tower (1) tower uses shower nozzle.
2. a kind of SDA methods flue gas desulfurization technique accessory substance self-loopa synergistic device according to claim 1, its feature exists In the conveyance conduit (6) is provided with powder delivery system.
CN201720215774.5U 2017-03-07 2017-03-07 A kind of SDA methods flue gas desulfurization technique accessory substance self-loopa synergistic device Active CN206566758U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201720215774.5U CN206566758U (en) 2017-03-07 2017-03-07 A kind of SDA methods flue gas desulfurization technique accessory substance self-loopa synergistic device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201720215774.5U CN206566758U (en) 2017-03-07 2017-03-07 A kind of SDA methods flue gas desulfurization technique accessory substance self-loopa synergistic device

Publications (1)

Publication Number Publication Date
CN206566758U true CN206566758U (en) 2017-10-20

Family

ID=60056531

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201720215774.5U Active CN206566758U (en) 2017-03-07 2017-03-07 A kind of SDA methods flue gas desulfurization technique accessory substance self-loopa synergistic device

Country Status (1)

Country Link
CN (1) CN206566758U (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109316934A (en) * 2018-10-29 2019-02-12 安徽欣创节能环保科技股份有限公司 A kind of flue gas desulphurization system for cancelling bypass
CN110075686A (en) * 2019-05-14 2019-08-02 河北华强科技开发有限公司 A kind of semi-dry method flue gas desulfurization technique system
CN112594728A (en) * 2020-12-07 2021-04-02 安徽欣创节能环保科技股份有限公司 Domestic waste incineration fly ash classification treatment system

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109316934A (en) * 2018-10-29 2019-02-12 安徽欣创节能环保科技股份有限公司 A kind of flue gas desulphurization system for cancelling bypass
CN110075686A (en) * 2019-05-14 2019-08-02 河北华强科技开发有限公司 A kind of semi-dry method flue gas desulfurization technique system
CN112594728A (en) * 2020-12-07 2021-04-02 安徽欣创节能环保科技股份有限公司 Domestic waste incineration fly ash classification treatment system

Similar Documents

Publication Publication Date Title
CN101559323B (en) Digestive circulating fluid bed flue gas desulfurization method and device
CN206566758U (en) A kind of SDA methods flue gas desulfurization technique accessory substance self-loopa synergistic device
CN108273370A (en) A kind of combination flue gas takes off white wet type fume sweetening device and its application method
CN105561753A (en) Novel dry process cement kiln flue gas online desulfurization device and technology
CN105107366B (en) A kind of concurrent spray semi-dry fume desulfuration method
CN201427021Y (en) Flue gas desulfurization device for digestive and circulating fluidized bed
CN106512696A (en) A circulating-fluidized-bed-method flue gas desulphurization process and a circulating-fluidized-bed-method flue gas desulphurization system
CN201195100Y (en) Flue-gas desulfurizing device with semi-dry process
CN201085994Y (en) Circulation fluidized bed smoke desulphurizing device
CN101829489A (en) Ammonia-plaster mode desulphurization system
CN112023681A (en) Method and system for performing circulating fluidized bed desulfurization by adopting rotary spray desulfurization ash
CN206295800U (en) A kind of semi-dry flue gas desulfurization device
CN107126830A (en) Coke oven flue gas sodium calcium base combined desulfurization dedusting SDG system and method based on SDA methods
CN111715069A (en) Ultra-clean discharge system and method for desulfurization and denitrification of sintering flue gas by using spray drying method
CN208275227U (en) A kind of combination flue gas takes off white wet type fume sweetening device
CN109304080B (en) Ultralow SO 2 Exhaust semi-dry circulating fluidized bed flue gas desulfurization system
CN206980448U (en) One kind is used for chemical industry tail gas multi-pollutant removing device
CN102000489A (en) Wet desulfurizer for thermal power plant and desulfurization method thereof
CN211936365U (en) System for utilize cement kiln tail to return ash and carry out flue gas desulfurization
CN210964601U (en) Sodium-based flue gas desulfurization byproduct treatment device
CN204073751U (en) A kind of dedusting and desulphurization integrated system based on spray drying tower
CN113559692A (en) Double-tower double-circulation semi-dry desulfurization device, process and application
CN210125282U (en) Quick denitrification facility of flue gas
CN108970373A (en) For chemical industry tail gas multi-pollutant removing device and its removal methods
CN207371337U (en) A kind of system for being classified oxidative absorption formula flue gas desulfurization and denitrification

Legal Events

Date Code Title Description
GR01 Patent grant
GR01 Patent grant