CN100531862C - Apparatus and method for removing grains with combined action of sound wave and additional seed grain - Google Patents

Apparatus and method for removing grains with combined action of sound wave and additional seed grain Download PDF

Info

Publication number
CN100531862C
CN100531862C CNB2007101326906A CN200710132690A CN100531862C CN 100531862 C CN100531862 C CN 100531862C CN B2007101326906 A CNB2007101326906 A CN B2007101326906A CN 200710132690 A CN200710132690 A CN 200710132690A CN 100531862 C CN100531862 C CN 100531862C
Authority
CN
China
Prior art keywords
granules
acoustic agglomeration
agglomeration chamber
seed grain
dust
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.)
Expired - Fee Related
Application number
CNB2007101326906A
Other languages
Chinese (zh)
Other versions
CN101219318A (en
Inventor
沈湘林
赵兵
陈厚涛
徐进
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.)
Southeast University
Original Assignee
Southeast University
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 Southeast University filed Critical Southeast University
Priority to CNB2007101326906A priority Critical patent/CN100531862C/en
Publication of CN101219318A publication Critical patent/CN101219318A/en
Application granted granted Critical
Publication of CN100531862C publication Critical patent/CN100531862C/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Abstract

The invention relates to a device used for removing absorbable granules PM2.5 based on acoustic wave and with the addition of associative action of seed granules and a method thereof, in particular to a set of devices used for removing the absorbable granules (hereinafter called PM2.5 for short) with grain diameter less than 2.5 micrometers in dusty gas and a method thereof. The device comprises a sound source, an acoustic agglomeration chamber, a feedway for the seed granules, subsequent normal dedusting equipment, etc. When flue gas discharged by various combustion sources or other dusty gas flows through the acoustic agglomeration chamber, fine granules in airflow arise entrainment of different degrees under the action of the acoustic wave, while the added seed granules nearly do not arise entrainment due to relatively large inertia thereof; meanwhile, the fine granules and the seed granules are different in gravity settling and acoustic drift. The three reasons lead to relative movement between the fine granules and the seed granules, thus generating quite high collision rate between the absorbable granules PM2.5 and the seed granules. After the absorbable granules PM2.5 collide with the seed granules, agglomeration happens between the absorbable granules PM2.5 collide with the seed granules; coacervate generated by the agglomeration is further removed by the subsequent normal dedusting equipment.

Description

The apparatus and method of sound wave and additional seed grain removing grains with combined action thing
Technical field
The present invention relates to a cover remove particle diameter in the dust-contained airflow less than 2.5 microns pellet (hereinafter to be referred as PM 2.5) apparatus and method, belong to the technical field that pollution control equipment is made.
Background technology:
In the current granular material discharged control technology, traditional method is the principles such as inertia, diffusion and electrostatic interaction according to particle, adopts routines such as electrostatic precipitator, cyclone separator, sack cleaner and ceramic filter to remove equipment and removes particle.Although the particle that these equipment remove greater than 5 μ m has reached very high efficient, to fine particle PM 2.5Removal efficiency lower, still have the fine particle of a myriad of to be disposed in the atmosphere, can not satisfy at present strict day by day environmental requirement.In general, adopt the approach that improves traditional dust collection method removal effect can run into actual difficulty, as adopting efficient cyclone separator, its resistance drop can increase greatly; In high-efficiency electrostatic dust remover, increase the electric field number, add long electrode and just can make originally that very big electric cleaner volume becomes huger, and power consumption also increases greatly.
Because general acoustic agglomeration method is being hanged down under the sound intensity PM 2.5Reunion efficient lower, only have about 40%.The present invention is based on the synergy of sound wave and additional seed grain,, adopt the bulky grain after follow-up conventional dust arrester will be reunited further to remove again, finally reach and efficiently remove PM as the preprocessing process that fine grained in the dust-contained airflow is carried out acoustic agglomeration 2.5Purpose.
Retrieve in existing patent, it is as follows to obtain relevant Chinese patent and document:
1, the patent No.: 02276809.2, vertical granule flow dust remover
2, the patent No.: 03132195.X, rotating fluidized bed blowback gravel bed filter
3, the patent No.: 200510095431, some cloth technique for dust removal combined and equipment thereof
4, the patent No.: 200510032204, flue type dust removal and purification apparatus
5, the patent No.: 01130066.3, coagulation type electrostatic dust removing method and device thereof
6, the patent No.: 96105749.1, the type of bleeding dust collection method and dust arrester
7, the patent No.: 92102104.6, high efficiency dust remover by magnetization adsorption
8, the patent No.: 99106814.9, a kind of ultrasonic concussion dust collection method and device
In the patent of the above-mentioned relevant particulate removal that retrieves, all can not remove effectively and can suck particle PM 2.5Wherein the 8th patent is to adopt the dedusting of ultrasonic concussion method, because the supersonic dust removal effect under the lower-wattage is relatively poor, energy consumption is bigger when adopting the ultrasonic wave of higher-wattage, so be difficult to guarantee reliably working steady in a long-term.This devices and methods therefor adopts sound wave and seed grain synergy method under reliable and stable low-frequency sound source, remove particle size range effectively and be the ultra-fine grain that the conventional cleaner of 0.01~2.5 μ m is difficult to capture.
Summary of the invention
Technical problem: the objective of the invention is to adopt a kind of sound wave and additional seed grain synergy to remove PM 2.5Apparatus and method, to the pellet PM in smoke evacuation, diesel engine vent gas and other dust-contained airflow of coal-burning power plant 2.5Remove, reach control PM 2.5The purpose of discharging.The present invention utilizes sound source, by sound wave and the symphyogenetic preprocessing process of additional seed grain, in conjunction with follow-up dust arrester, can remove the PM in the dust-contained airflow efficiently 2.5
Technical scheme: sound wave of the present invention and additional seed grain synergy remove PM 2.5Device in, an end of the horizontal flue of dust-contained airflow import is connected with the upper end of vertical acoustic agglomeration chamber; The seed grain feeder is connected with the top with vertical acoustic agglomeration chamber; Two sides at middle part, vertical acoustic agglomeration chamber are connected with horizontally disposed two reducing tube connectors by adpting flange respectively, and the other end of two reducing tube connectors is connected with two sound sources with flange respectively; The lower part outlet end of vertical acoustic agglomeration chamber is connected with particle first order separator, and the outlet of first order separator is connected with second level separator again, and the port of export of second level separator is connected with air-introduced machine through flue; Air-flow after will being handled by air-introduced machine is at last discharged.
Sound wave of the present invention and additional seed grain synergy remove PM 2.5Device remove PM 2.5Method be:
1) determining of sound source operating frequency: after the operating frequency of sound source is determined, calculate wavelength at this operating frequency lower plane sound wave, make that by the length that changes the reducing tube connector spacing between two sound sources is the half-wavelength integral multiple, when two sound sources are installed on the position of integral multiple of half-wavelength, in the acoustic agglomeration chamber, form standing wave;
2) determining of vertical acoustic agglomeration chamber total height: the total length of vertical acoustic agglomeration chamber is the difference in height that dust-contained airflow passes in and out vertical acoustic agglomeration chamber, according to the gas flow of handling, determine the cross section and the total length of acoustic agglomeration chamber, guarantee that dust-contained airflow is not less than 3 seconds in indoor total time of staying of acoustic agglomeration;
3) adding of seed grain: additional seed grain is added by the seed grain feeder by the top of vertical acoustic agglomeration chamber, seed grain is solid particle or liquid particles, select the size of particle according to the frequency of sound wave, the seed grain that adds relies on the gravity of self, imports air-flow and enters vertical acoustic agglomeration chamber;
4) start sound source, open the particle feeder at top, vertical acoustic agglomeration chamber simultaneously, seed grain is added in the vertical acoustic agglomeration chamber with specified feeding coal.Pending dust-contained airflow, enter vertical acoustic agglomeration reunion chamber by passage after, the PM in the air-flow 2.5What be subjected to sound wave simultaneously carries and adds oarse-grained capture effect secretly, and the dust-contained airflow after processed enters first order separator and second level separator separator again, and last air-introduced machine is discharged.
Symphyogenetic theoretical foundation and computational process
(1) sound wave is carried the relative motion that causes secretly
Because the effect of stickiness makes particle vibrate with the vibration of gas molecule, it is the distinctive character of granule that sound wave is carried secretly to granule in acoustic wavefield.Fine grained carrying secretly in acoustic wavefield is expressed from the next
η = 1 1 + ( ωτC ) 2 - - - ( 1 )
Its physical significance is the ratio of particle vibration amplitude and air particle vibration amplitude.ω in the formula 1 is an angular frequency, ω=2 π f, and f is a frequency; τ is the relaxation time of particle, and expression formula is
τ = ρ d d p 2 18 μ - - - ( 2 )
ρ in the formula 2 pIt is grain density; d pIt is particle radius; μ gIt is the gas medium dynamic viscosity.C is the Ken Ninghan correction factor, and its definition is
C = 1 + 2 λ g d p ( 1.257 + 0.400 e - 0.55 d p / λ g ) - - - ( 3 )
λ in the formula 3 gIt is the air molecule mean free path.
According to formula 1, for the particle that varies in size, it is carried coefficient secretly and there are differences.Shown the bigger relative velocity of generation between granule of fully carrying secretly and the seed grain of being carried secretly hardly, reunited for the particle collision and created condition.For seed grain among the present invention captures PM 2.5Theoretical foundation is provided.
(2) relative motion that causes of gravitational settling
According to particle sinking speed in air
U G = ρ p gd p 2 C 18 μ - - - ( 4 )
Wherein g is an acceleration of gravity.The big or small particle sinking speed different with density is by difference.In the vertical acoustic agglomeration chamber of this patent, there is different particle sinking speeds in the seed grain that yardstick is bigger with fine grained, and produces relative velocity.Gravitational settling also is one of foundation that increases collision rate between particle.
(3) sound causes the relative motion that drift causes
The asymmetric particle that causes of the stickiness of particle in sound wave is carried secretly drifts about in standing-wave sound field, and the sound of particle causes drift velocity by following expression
U drift = 1 24 μ kd p 2 η U 0 sin ( 2 kx ) - - - ( 5 )
Wherein k is a wave number, U 0Be the SVEL amplitude, x is position in the acoustic wavefield.From formula 5 as can be known, bigger seed grain and can suck particle PM 2.5Between different drift velocities is arranged in sound field, and make and produce relative velocity between particle.
Beneficial effect: under reliable sound source and additional seed grain synergy,, remove several peak concentration particle diameters PM in the dust-contained airflow in sub-micron regions effectively in conjunction with follow-up cleaner 2.5It is important feature of the present invention.By test, device of the present invention can make fine grained PM in the dust-contained airflow 2.5Several concentration removal efficiencies reach 68%, the removal efficiency of mass concentration reaches 80%.This device is applicable to the occasion that environmental protection and air cleaning have higher requirements.
Description of drawings
Fig. 1 is a general structure schematic diagram of the present invention.Wherein have: flue 1, vertical acoustic agglomeration chamber 2, sound source 3, seed grain feeder 4, first order separator 5, second level separator 6, air-introduced machine 7.
The specific embodiment
Whole device of the present invention is divided into three parts as shown in Figure 1: sound source; Dust-contained airflow channel system (reunion chamber); Add particle system and follow-up conventional cleaner.Follow-up conventional cleaner among this figure as an example, adopts the two-stage expansion chamber to separate, and has corresponding cutting particle diameter.Can adopt single-stage or multistage all kinds of conventional cleaner during actual the use.
Concrete connected mode is as follows: an end of the horizontal channel of dust-contained airflow import is connected with the upper end of vertical acoustic agglomeration chamber; The vibrating material feeding device that adds particle is connected with the top with vertical acoustic agglomeration chamber; Two sides at middle part, acoustic agglomeration chamber are installed adpting flange respectively, are connected with horizontally disposed two reducing tube connectors; The other end of two reduced pipes is connected with two sound sources with flange; The port of export of acoustic agglomeration chamber (lower port) is connected with the particle separation chamber, for guaranteeing that separating effect can contact to connect multistage conventional separator is set; The downstream of separator is connected with air-introduced machine through flue by flange; Air-flow after will being handled by air-introduced machine is at last discharged.
The operating frequency of sound source calculates the wavelength at this operating frequency lower plane sound wave after determining, makes that by the length that changes reduced pipe the spacing between two loudspeaker is the half-wavelength integral multiple.When two sound sources are installed on the position of integral multiple of half-wavelength, in the acoustic agglomeration chamber, form standing wave.
Determining of vertical acoustic agglomeration chamber total height: the total length of acoustic agglomeration chamber is the difference in height that dust-contained airflow passes in and out vertical acoustic agglomeration chamber.According to the gas flow of handling, determine the cross section and the total length of acoustic agglomeration chamber, guarantee that dust-contained airflow is not less than 3 seconds in indoor total time of staying of acoustic agglomeration.
Additional seed grain is added by the top of acoustic agglomeration chamber.Seed grain can be solid particle or liquid particles, selects the size of particle according to the frequency of sound wave, and when being 1kHz as frequency of sound wave, the seed grain size is 15~20 μ m, and corresponding seed grain concentration magnitude is 10 4Individual/cm 3.The seed grain that adds relies on the gravity of self, imports air-flow and enters the acoustic agglomeration chamber.
The bulky grain that should guarantee to remove after the reunion to choosing of separation equipment can all be separated from air-flow, and the cut diameter of separation equipment is chosen for D 50Be no more than the diameter of seed grain,, can adopt multi-stage separation in order to guarantee the later separation effect.
The concrete running of this apparatus system is as follows: start sound source, open the charging gear at top, acoustic agglomeration chamber simultaneously, with specified feeding coal seed grain is added in the acoustic agglomeration chamber.Pending dust-contained airflow, enter vertical acoustic agglomeration reunion chamber by passage after, the PM in the air-flow 2.5What be subjected to sound wave simultaneously carries and adds oarse-grained capture effect secretly, and the dust-contained airflow after processed enters conventional separation equipment (for example first and second grades of conventional separators among Fig. 1) again, and last air-introduced machine is discharged.

Claims (2)

1. the device of sound wave and additional seed grain removing grains with combined action thing is characterized in that an end of the horizontal flue (1) of dust-contained airflow import is connected with the upper end of vertical acoustic agglomeration chamber (2); Seed grain feeder (4) is connected with the top with vertical acoustic agglomeration chamber (2); Two sides at middle part, vertical acoustic agglomeration chamber (2) are connected with horizontally disposed two reducing tube connectors (22) by adpting flange (21) respectively, and the other end of two reducing tube connectors (22) uses flange to be connected with two sound sources (3) respectively; The lower part outlet end of vertical acoustic agglomeration chamber (2) is connected with particle first order separator (5), and the outlet of first order separator (5) is connected with second level separator (6) again, and the port of export of second level separator (6) is connected with air-introduced machine (7) through flue; Air-flow after will being handled by air-introduced machine is at last discharged.
2. the method that removes the microparticle thing of the device of sound wave as claimed in claim 1 and additional seed grain removing grains with combined action thing is characterized in that this method is:
1) determining of sound source (3) operating frequency: after the operating frequency of sound source is determined, calculate wavelength at this operating frequency lower plane sound wave, make that by the length that changes reducing tube connector (22) spacing between two sound sources (3) is the half-wavelength integral multiple, when two sound sources (3) are installed on the position of integral multiple of half-wavelength, in the acoustic agglomeration chamber, form standing wave;
2) determining of vertical acoustic agglomeration chamber (2) total height: the total length of vertical acoustic agglomeration chamber (2) is the difference in height that dust-contained airflow passes in and out vertical acoustic agglomeration chamber, according to the gas flow of handling, determine the cross section and the total length of acoustic agglomeration chamber, guarantee that dust-contained airflow is not less than 3 seconds in indoor total time of staying of acoustic agglomeration;
3) adding of seed grain: additional seed grain is added by seed grain feeder (4) by the top of vertical acoustic agglomeration chamber (2), seed grain is solid particle or liquid particles, select the size of particle according to the frequency of sound wave, the seed grain that adds relies on the gravity of self, imports air-flow and enters vertical acoustic agglomeration chamber;
4) start sound source (3), open the particle feeder (4) at top, vertical acoustic agglomeration chamber (2) simultaneously, with specified feeding coal seed grain is added in the vertical acoustic agglomeration chamber (2), pending dust-contained airflow, after entering vertical acoustic agglomeration chamber by passage, microparticle thing in the air-flow is subjected to carrying secretly of sound wave simultaneously and adds oarse-grained capture effect, and the dust-contained airflow after processed enters first order separator (5) again to be separated with second level separator (6), and last air-introduced machine is discharged.
CNB2007101326906A 2007-09-18 2007-09-18 Apparatus and method for removing grains with combined action of sound wave and additional seed grain Expired - Fee Related CN100531862C (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CNB2007101326906A CN100531862C (en) 2007-09-18 2007-09-18 Apparatus and method for removing grains with combined action of sound wave and additional seed grain

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CNB2007101326906A CN100531862C (en) 2007-09-18 2007-09-18 Apparatus and method for removing grains with combined action of sound wave and additional seed grain

Publications (2)

Publication Number Publication Date
CN101219318A CN101219318A (en) 2008-07-16
CN100531862C true CN100531862C (en) 2009-08-26

Family

ID=39629559

Family Applications (1)

Application Number Title Priority Date Filing Date
CNB2007101326906A Expired - Fee Related CN100531862C (en) 2007-09-18 2007-09-18 Apparatus and method for removing grains with combined action of sound wave and additional seed grain

Country Status (1)

Country Link
CN (1) CN100531862C (en)

Families Citing this family (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103706219B (en) * 2013-12-26 2015-10-07 浙江大学 Acoustic agglomeration combines the devices and methods therefor that spraying synergy removes fine particulates
CN103736356B (en) * 2014-01-09 2015-11-04 东南大学 The device removing fine particle of a kind of sonic agglomeration-conventional dust removal compound
CN103949135B (en) * 2014-04-29 2015-12-02 中国人民解放军国防科学技术大学 For the treatment of the strong acoustic agglomeration device and method of suspended particulate
CN103933822A (en) * 2014-04-29 2014-07-23 中国人民解放军国防科学技术大学 Resonant cavity type sound agglomeration system and method for treating suspended particles
CN104587789B (en) * 2015-01-26 2016-03-23 中国人民解放军国防科学技术大学 Based on the suspended particulate acoustic agglomeration system and method for Helmholtz resonator array
CN104689675A (en) * 2015-02-12 2015-06-10 中国计量学院 Device and method for removing fine particulate matters by acoustic agglomeration with flying ash recirculating
CN104923403B (en) * 2015-06-29 2018-03-16 浙江大学 The devices and methods therefor of sound wave combined electric field action removing fine particle
CN105089742B (en) * 2015-07-09 2018-02-02 东南大学 A kind of method that diesel engine vent gas suspended particulate substance is reduced in sound field environment
CN105999979B (en) * 2016-05-31 2017-11-24 东南大学 A kind of devices and methods therefor of discrete differential wall manipulation suspended particulate
CN106890730B (en) * 2017-03-27 2018-06-26 南京信息工程大学 A kind of resonant space particle purifying device and control method
CN109442395A (en) * 2018-12-12 2019-03-08 中国华能集团清洁能源技术研究院有限公司 A kind of system and method for realizing circulating fluidized bed boiler flexibility operation based on technology of acoustic wave
CN112023604B (en) * 2020-08-04 2022-06-24 西安建筑科技大学 Dual-band composite sound wave mist suppression method

Also Published As

Publication number Publication date
CN101219318A (en) 2008-07-16

Similar Documents

Publication Publication Date Title
CN100531862C (en) Apparatus and method for removing grains with combined action of sound wave and additional seed grain
KR101550514B1 (en) Process for separating particulate solids from a gas stream
JP2010525937A (en) Electrostatic recirculation process and equipment for dust removal and gas cleaning
CN104190199A (en) Device and method for removing fine particles by virtue of acoustic wave and phase change coupling effect
CN104128047B (en) Acoustic agglomerator and cyclonic separation synergy fine particle remove device and method
CN102380275A (en) Dedusting device and dedusting method therefor
CN102091496A (en) Double-effect dust remover with long service life
CN110327723B (en) Acoustic-electric coupling fine particulate matter removing device and fine particulate matter removing method
CN210544073U (en) Device of many fields desorption fine particles thing in coordination
Jaworek et al. Hybrid electrostatic filtration system for fly ash particles emission control
CN201094885Y (en) High concentration bag-type dust remover
CN2576316Y (en) Novel bag-type composite duster
CN101648094B (en) Double-inlet turbulence mixing type bag dust remover and dust removing method thereof
CN204973331U (en) Granule condenses inertial dust collection processing apparatus
CN201120317Y (en) Electric dust collector with advance dust receiving apparatus
CN105195320A (en) Constant-magnetism-enhancing dust removal device
CN206762577U (en) A kind of dust arrester based on acoustic agglomeration
CN110975504A (en) Drum formula whirlwind sack cleaner
CN202666642U (en) Parasitic combined dust collecting device
CN106512563B (en) A kind of reunion trapping of sintering flue gas subparticle and discharge-reducing method
CN107126801B (en) A kind of flue gas purification device of super gravity field combined electric field
JPH05501678A (en) Method and device for purifying waste gas
CN109876925A (en) Flue gas waste heat utilization and intelligent electric field intensity adjusting system thereof
CN210729030U (en) Acoustic-electric coupling fine particulate matter removing device
CN209697194U (en) A kind of cyclone separator

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20090826

Termination date: 20140918

EXPY Termination of patent right or utility model