CN109499214A - Moving bed particle layer filter - Google Patents
Moving bed particle layer filter Download PDFInfo
- Publication number
- CN109499214A CN109499214A CN201811587671.7A CN201811587671A CN109499214A CN 109499214 A CN109499214 A CN 109499214A CN 201811587671 A CN201811587671 A CN 201811587671A CN 109499214 A CN109499214 A CN 109499214A
- Authority
- CN
- China
- Prior art keywords
- bed filter
- cylinder
- internal
- granular bed
- moving granular
- 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.)
- Granted
Links
- 239000002245 particle Substances 0.000 title claims abstract description 40
- 239000000779 smoke Substances 0.000 claims abstract description 25
- 238000001914 filtration Methods 0.000 claims abstract description 20
- 238000001816 cooling Methods 0.000 claims description 39
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims description 22
- 239000003546 flue gas Substances 0.000 claims description 22
- 239000007789 gas Substances 0.000 claims description 21
- 210000000498 stratum granulosum Anatomy 0.000 claims description 20
- PNEYBMLMFCGWSK-UHFFFAOYSA-N Alumina Chemical compound [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 claims description 9
- 229910000831 Steel Inorganic materials 0.000 claims description 6
- 239000010959 steel Substances 0.000 claims description 6
- 239000006004 Quartz sand Substances 0.000 claims description 3
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims description 3
- 239000008187 granular material Substances 0.000 claims description 3
- 239000000428 dust Substances 0.000 abstract description 15
- 238000004519 manufacturing process Methods 0.000 abstract description 7
- 239000002360 explosive Substances 0.000 abstract description 4
- 238000009825 accumulation Methods 0.000 abstract 1
- 238000003723 Smelting Methods 0.000 description 6
- 239000003500 flue dust Substances 0.000 description 6
- 238000004880 explosion Methods 0.000 description 5
- 239000000463 material Substances 0.000 description 5
- 238000000034 method Methods 0.000 description 5
- 239000002918 waste heat Substances 0.000 description 5
- 238000010586 diagram Methods 0.000 description 4
- 238000004064 recycling Methods 0.000 description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 4
- 229910000975 Carbon steel Inorganic materials 0.000 description 3
- 239000010962 carbon steel Substances 0.000 description 3
- 235000019504 cigarettes Nutrition 0.000 description 3
- 238000005299 abrasion Methods 0.000 description 2
- 230000002776 aggregation Effects 0.000 description 2
- 238000004220 aggregation Methods 0.000 description 2
- 238000010923 batch production Methods 0.000 description 2
- 238000010276 construction Methods 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 239000010419 fine particle Substances 0.000 description 2
- 238000002309 gasification Methods 0.000 description 2
- 230000001535 kindling effect Effects 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 239000007921 spray Substances 0.000 description 2
- 229920000742 Cotton Polymers 0.000 description 1
- 229920000914 Metallic fiber Polymers 0.000 description 1
- 241001417490 Sillaginidae Species 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 239000003034 coal gas Substances 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 238000010411 cooking Methods 0.000 description 1
- 239000002826 coolant Substances 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 238000006073 displacement reaction Methods 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 239000000706 filtrate Substances 0.000 description 1
- 239000003517 fume Substances 0.000 description 1
- 238000009413 insulation Methods 0.000 description 1
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N iron oxide Inorganic materials [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 1
- JEIPFZHSYJVQDO-UHFFFAOYSA-N iron(III) oxide Inorganic materials O=[Fe]O[Fe]=O JEIPFZHSYJVQDO-UHFFFAOYSA-N 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 210000003205 muscle Anatomy 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 230000005855 radiation Effects 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 239000011819 refractory material Substances 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 230000035939 shock Effects 0.000 description 1
- 238000005245 sintering Methods 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D46/00—Filters or filtering processes specially modified for separating dispersed particles from gases or vapours
- B01D46/24—Particle separators, e.g. dust precipitators, using rigid hollow filter bodies
- B01D46/2403—Particle separators, e.g. dust precipitators, using rigid hollow filter bodies characterised by the physical shape or structure of the filtering element
- B01D46/2411—Filter cartridges
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D46/00—Filters or filtering processes specially modified for separating dispersed particles from gases or vapours
- B01D46/0002—Casings; Housings; Frame constructions
- B01D46/0005—Mounting of filtering elements within casings, housings or frames
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D46/00—Filters or filtering processes specially modified for separating dispersed particles from gases or vapours
- B01D46/30—Particle separators, e.g. dust precipitators, using loose filtering material
- B01D46/32—Particle separators, e.g. dust precipitators, using loose filtering material the material moving during filtering
- B01D46/34—Particle separators, e.g. dust precipitators, using loose filtering material the material moving during filtering not horizontally, e.g. using shoots
Landscapes
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Physics & Mathematics (AREA)
- Geometry (AREA)
- Filtering Of Dispersed Particles In Gases (AREA)
Abstract
The invention discloses a moving bed particle layer filter, which comprises an inner layer cylinder (1), a middle cylinder (2) and an outer layer cylinder (3) which are sequentially sleeved from inside to outside, wherein a first annular cavity is formed between the inner layer cylinder (1) and the middle cylinder (2), a filtering particle layer (4) is arranged in the first annular cavity, the inner layer cylinder (1) comprises a plurality of inner baffle plates (11) which are arranged along the axial direction and are arranged in an inclined mode, and the middle cylinder (2) comprises a plurality of outer baffle plates (21) which are arranged along the axial direction and are arranged in an inclined mode. The moving bed particle layer filter can filter high-temperature smoke at 600-1000 ℃, and ensures that no high-energy particles which can become fire seeds exist on the clean smoke side. The problems of large-temperature-area cold and hot impact, large-concentration dust impact, explosive gas accumulation and the like under large flow caused by intermittent production are further solved, the service life is long, and the filtering efficiency is high.
Description
Technical field
The present invention relates to a kind of moving granular bed filters.
Background technique
The production method of the smelting furnaces such as converter be it is intermittent, i.e., smelting furnace is emptied, again before and after smelting production
The warming-up exercises such as new charging.
During warming-up exercise, there is no the smelting for having intensity, for smoke components based on air, flue-gas temperature is air heats
It is slightly improved after radiation, there is no the flue dust for having intensity.
During smelting production, with the raising of rate of driving, by the flue-gas temperature of fire door evolution up to 1600 DEG C, flue gas at
CO content may be up to 90% in point, and the dust that flue gas carries is up to 150g/Nm3, the complicated component of dust, mainly have FeO,
Fe2O3, CaO etc., the reaction such as oxidation heat liberation will also occur in subsequent flue for the flue gas and flue dust of evolution.
It smelts production duration to be usually no more than 20 minutes, warming-up exercise duration is generally also no more than 20 minutes.Due to
It is big to need very strong reply for the production method of this fast intermittent formula, the facility of converter gas treatment facility especially high temperature
Warm area cooling thermal impact, the ability of the impact of big concentration dust, explosion hazard gases aggregation.
At present both at home and abroad in prior art, the highest production method of energy recovery utilization efficiency is: sealed vapour is arranged
Change cooling stack, water vapour, setting spray or vaporation-type are transferred to the obvious heat of smoke that radiating heat form is 800 DEG C of chief commander or more
Direct cooling tower by flue-gas temperature be reduced to 70 DEG C or 250 DEG C hereinafter, recycle and utilizing CO content height and O2The low converter of content
Coal gas.800 DEG C of obvious heat of smoke below are not able to achieve Exposure degree due to smoke components are explosive, smoke content is high etc..
The direct cooling tower of fountain by flue-gas temperature be reduced to 70 DEG C hereinafter, can will portion big absolutely while cooled flue gas
Point flue dust washes down, but there are the problem of: sensible heat is unrecovered, water consume is big, sewage needs to handle.The direct cooling tower of vaporation-type is by cigarette
Temperature degree is reduced to 250 DEG C hereinafter, can separate part bulky grain flue dust while cooled flue gas, but existing asks
Topic: sensible heat is unrecovered, the steam consumption is big.To meet the needs of 800 DEG C of obvious heat of smoke below recycling, converter gas need to be subjected to high temperature
Dedusting.
Domestic and international relatively good high-temperature dust removal technology has at present:
Metallic fiber chimney filter, metal sintering web filter etc. can satisfy the requirement of high-temperature dust removal, but expensive.
Rigid surface filter of ceramic filter, too cotton etc. also can satisfy the requirement of high-temperature dust removal, but have frangible, afraid of water
The problems such as, and it is expensive.
Cyclone dust collectors (including multi-tube dust cleaner etc.) are the high-temperature dust removal technologies of comparative maturity, are widely used in fluidizing
Industrial circles are waited in bed boiler, but are difficult to trap 5 μm of particles below, it is impossible to be used in atmosphere emission control.
Granular-bed filter (including rake granular-bed filter, cyclone type granular-bed filter, moving-bed type stratum granulosum mistake
Filter etc.), have many advantages, such as that resistant to high temperatures, shock resistance, filtrate are from a wealth of sources, but the research experience without being used for batch production,
Also it is not applied to the research experience of explosion hazard gases, and is difficult to trap fine particle, it is impossible to be used in atmosphere emission control.
Summary of the invention
In order to solve the problems, such as that existing dust-extraction unit cannot trap high temperature fine particle.The present invention provides a kind of moving beds
Granular-bed filter, the moving granular bed filter can be filtered 600 DEG C~1000 DEG C of high-temperature flue gas, it is ensured that
The particle as kindling material of big energy is not present in neat stress side.It further solves big under batch production bring big flow
The problems such as warm area cooling thermal impact, the impact of big concentration dust, explosion hazard gases aggregation, long service life, filter efficiency are high.
The present invention solves technological invention used by its technical problem: a kind of moving granular bed filter, including from
Internal layer cylinder, middle cylinder and the outer layer barrel being successively arranged from inside to outside, form the first ring between internal layer cylinder and middle cylinder
Shape cavity, the first annular cavity is interior to be equipped with filtering stratum granulosum, and internal layer cylinder and middle cylinder are the louvered structure of annular, interior
Layer cylinder contains the Internal baffle item that axially aligned more are obliquely installed, and middle cylinder contains more axially aligned inclinations
The outer baffle item of setting.
Internal layer cylinder, middle cylinder and outer layer barrel are upright state, are additionally provided with support frame in the first annular cavity
The lower part of frame, the moving granular bed filter is equipped with smoke inlet, and the top of the moving granular bed filter is equipped with
Exhanst gas outlet.
Internal cavity is equipped in internal layer cylinder, middle cylinder and outer layer barrel form the second toroidal cavity;Smoke inlet with should
Internal cavity connection, exhanst gas outlet are connected to second toroidal cavity;Alternatively, smoke inlet is connected to second toroidal cavity, cigarette
Gas outlet is connected to the internal cavity.
Braced frame contains the more root posts evenly distributed along the circumferential direction of middle cylinder, and the first annular cavity is by described more
Root post is separated to form multiple fan-shaped warehouses, and filtering stratum granulosum is located in the fan-shaped warehouse.
Column is externally provided with gusset, and Internal baffle item and outer baffle item are fixed with the link of boards, and it is cold that master is equipped in column
But it manages.
The inside of Internal baffle item is equipped with Internal baffle cooling tube, and the outside of outer baffle item is equipped with outer baffle cooling tube, Internal baffle
Cooling tube and outer baffle cooling tube are connected to main cooling tube.
The inclined direction of Internal baffle item and the inclined direction of outer baffle item are on the contrary, the longitudinal section of adjacent Internal baffle item and outer
Mirror image each other between the longitudinal section of apron strip, along direction from the top down, between adjacent Internal baffle item and outer baffle item away from
From being gradually reduced.
The moving granular bed filter further includes net particle storehouse and charging valve, and the lower part in net particle storehouse passes through charging pipe
Road is connected to the top of the first annular cavity, and charging valve is set on the charging hole.
The moving granular bed filter further includes dirty particle storehouse and blow-off valve, and the top in dirty particle storehouse passes through drainage conduit
Road is connected to the lower part of the first annular cavity, and blow-off valve is set in the drainage line.
Filtering stratum granulosum is quartz sand layer, aluminium oxide granule granulosa or steel ball layer.
The beneficial effects of the present invention are: removing most flue dust of converter gas carrying at 800 DEG C~1000 DEG C, disappear
Hidden peril of explosion when in addition to the recycling of subsequent convection type waste heat alleviates the abrasion of subsequent convection type waste heat recycling heat-transfer surface.
Detailed description of the invention
The accompanying drawings constituting a part of this application is used to provide further understanding of the present invention, and of the invention shows
Examples and descriptions thereof are used to explain the present invention for meaning property, does not constitute improper limitations of the present invention.
Fig. 1 is the use state diagram of moving granular bed filter of the present invention.
Fig. 2 is the schematic diagram of moving granular bed filter.
Fig. 3 is the Longitudinal cross section schematic of internal layer cylinder and middle cylinder.
Fig. 4 is the cross-sectional view of internal layer cylinder and middle cylinder.
Fig. 5 is the schematic diagram of fan-shaped warehouse.
Fig. 6 is the connection schematic diagram of Internal baffle cooling tube and outer baffle cooling tube and main cooling tube.
1, internal layer cylinder;2, middle cylinder;3, outer layer barrel;4, stratum granulosum is filtered;5, braced frame;6, smoke inlet;
7, exhanst gas outlet;8, net particle storehouse;9, dirty particle storehouse;
11, Internal baffle item;12, Internal baffle cooling tube;
21, outer baffle item;22, outer baffle cooling tube;
31, moving granular bed filter;32, waste heat boiler;
51, column;52, main cooling tube.
Specific embodiment
It should be noted that in the absence of conflict, the features in the embodiments and the embodiments of the present application can phase
Mutually combination.The present invention will be described in detail below with reference to the accompanying drawings and embodiments.
A kind of moving granular bed filter, including internal layer cylinder 1, the middle cylinder 2 and outer being successively arranged from inside to outside
Layer cylinder 3, forms first annular cavity between internal layer cylinder 1 and middle cylinder 2, filtering particle is equipped in the first annular cavity
Layer 4, internal layer cylinder 1 and middle cylinder 2 are the louvered structure of annular, and internal layer cylinder 1 contains more axially aligned inclinations
The Internal baffle item 11 of setting, middle cylinder 2 contains the axially aligned more outer baffle items 21 being obliquely installed, such as Fig. 1 to Fig. 3
It is shown.
In the present embodiment, internal layer cylinder 1, middle cylinder 2 and outer layer barrel 3 are upright state, in internal layer cylinder 1
The center line of heart line, the center line of middle cylinder 2 and outer layer barrel 3 is overlapped, and Internal baffle item 11 and outer baffle item 21 are annulus
Shape is additionally provided with braced frame 5 in the first annular cavity, and the lower part of the moving granular bed filter is equipped with smoke inlet 6,
The top of the moving granular bed filter is equipped with exhanst gas outlet 7.
In the present embodiment, filtering stratum granulosum 4 from top to bottom, flue gas can in into it is outgoing, also outside into it is interior go out.To guarantee not
Occur flue gas residence, flue gas can also with bottom in and top out or upper entering and lower leaving, can not under into it is lower go out, also can not it is enterprising it is upper go out, such as Fig. 1
To shown in Fig. 3.
In the present embodiment, internal cavity is equipped in internal layer cylinder 1, it is empty that middle cylinder 2 and outer layer barrel 3 form the second annular
Chamber;Smoke inlet 6 is connected to the internal cavity, and exhanst gas outlet 7 is connected to second toroidal cavity;Alternatively, smoke inlet 6 and this
The connection of second ring cavity, exhanst gas outlet 7 are connected to the internal cavity.
It is preferred that smoke inlet 6 is connected to the internal cavity, exhanst gas outlet 7 is connected to second toroidal cavity.When in use, dirty
Dye flue gas initially enters the internal cavity of internal layer cylinder 1 from smoke inlet 6, then by the filtering of filtering stratum granulosum 4, enters back into
Between the second toroidal cavity between cylinder 2 and outer layer barrel 3, filtered purifying smoke is discharged from exhanst gas outlet 7 again.
In the present embodiment, braced frame 5 contains the more root posts 51 evenly distributed along the circumferential direction of middle cylinder 2, internal layer
The weight of cylinder 1, middle cylinder 2 and outer layer barrel 3 can be undertaken by braced frame 5, and the first annular cavity is by described more
Root post 51 is separated to form multiple (such as 3 to 15) fan-shaped warehouse, and filtering stratum granulosum 4 is located in the fan-shaped warehouse, such as Fig. 4
With shown in Fig. 5.
In the present embodiment, 51 fixed sleeves of column are equipped with gusset, Internal baffle item 11 and outer baffle item 21 with the muscle
Plate is connected and fixed, and main cooling tube 52 is equipped in column 51.The inside of Internal baffle item 11 is equipped with Internal baffle cooling tube 12, outer baffle item
21 outside is equipped with outer baffle cooling tube 22, and Internal baffle cooling tube 12 and outer baffle cooling tube 22 are connected to main cooling tube 52,
As shown in Figure 6.
In the present embodiment, the inclined direction of Internal baffle item 11 is with the inclined direction of outer baffle item 21 on the contrary, left and right is adjacent
The longitudinal section of Internal baffle item 11 and the longitudinal section of outer baffle item 21 between mirror image each other, along direction from the top down, left and right phase
The distance between adjacent Internal baffle item 11 and outer baffle item 21 are gradually reduced, as shown in Figure 3.Two neighbouring Internal baffle items
The distance between 11 are greater than the diameter that particle is filtered in filtering stratum granulosum 4, between two neighbouring outer baffle items 21 away from
From the diameter for being greater than filtering particle in filtering stratum granulosum 4.
In the present embodiment, the moving granular bed filter 31 further includes net particle storehouse 8, charging valve, dirty particle storehouse 9
And blow-off valve, the lower part in net particle storehouse 8 are connected to by charging hole with the top of the first annular cavity, charging valve is set to this
On charging hole.The top in dirty particle storehouse 9 is connected to by drainage line with the lower part of the first annular cavity, and blow-off valve is set to
In the drainage line.Filtering stratum granulosum 4 can be quartz sand layer, aluminium oxide granule granulosa or steel ball layer.
In the present invention, the moving granular bed filter 31 is set in converter fume high-temperature section, by the height of the overwhelming majority
Warm dust is separated with high-temperature flue gas, and explosion hazard gases is divided before entering explosive temperature range with kindling material (high-temperature dust particle)
From not only having solved explosive danger, but also reduce dust abrasion, and made it possible the waste heat recycling of high-temperature flue gas.
Biggish 4 total amount of filtering stratum granulosum is set, particle lamellar spacing is allow to collect the whole of primary smelting process generation
Flue dust.The method of operation of smoke catching discharge can be with as a result, are as follows: fixed-bed type high-temperature smoke traps under high-temperature flue gas state, low
Moving-bed type stratum granulosum carries dust discharge under warm smoke behavior.
In each indoor 4 upper entering and lower leaving of filtering stratum granulosum in fan-shaped storehouse.Fan-shaped warehouse realizes that area's internal granular layer can be complete
It is discharged from top to down entirely, also realizes the available effective cooling of the steel construction pieces such as louver baffle and braced frame.Interior cooling tube
Main pipe be set in braced frame, the branched pipe of interior cooling tube is set to the back side of louver baffle.Louver baffle and interior cooling
Pipe is close to, and braced frame is close to by gusset with interior cooling tube main pipe, by giving heat transfer to cooling medium in interior cooling tube, hundred
The steel construction pieces such as page baffle, braced frame are cooled down, and guarantee necessary intensity, rigidity.
Net particle storehouse and charging valve is arranged in top, and net particle storehouse, which has, pre-processes clean net particle, makees for charging
Industry.Blow-off valve and dirty particle storehouse is arranged in lower section.Dirty particle storehouse is for receiving the discharge of converter gas moving bed granular bed filter structure
Dirty particle.Dirty particle it is processed it is clean after be transported to net particle storehouse for being recycled.
The course of work of the moving granular bed filter is described below.
Converter is discharged high-temperature flue gas, flue gas pass sequentially through with radial pattern exchange heat based on gasification cooling flue (it is current at
Cooking technique), moving granular bed filter of the present invention 31, the convection column tube evaporimeter (waste heat boiler based on convection current
32), smoke temperature decreases below 150 DEG C, as shown in Figure 1.
For ash-laden gas from converter mouth upwards through gasification cooling flue, about 800~1000 DEG C of temperature whens, enter shifting of the invention
Dynamic bed granular-bed filter 31, ash-laden gas enter from bottom to top in internal layer cylinder 1, neat stress by stratum granulosum structure outer layer cylinder
It draws on the top of body 3.Internal layer cylinder 1, middle cylinder 2 and outer layer barrel 3
Moving granular bed filter 31 of the invention mainly uses carbon steel material.The outer wall of outer layer barrel 3 is insulation cigarette
Road part, using interior spray refractory material.Interior annular louver baffle, exterior annular louver baffle, louver baffle braced frame are equal
Using carbon steel material.The interior cooling tube of sheet with rib uses water cooling.Filter stratum granulosum 4 in particle use steel ball, partial size about 1~
2mm.Net particle storehouse, dirty particle storehouse are all made of carbon steel material, and dischargeable capacity is all larger than primary charging dosage.Charge valve, blow-off valve
It is all made of star valve.Particle thickness (the diameter of filtering stratum granulosum 4 between interior annular louver baffle, exterior annular louver baffle
To thickness) about 200mm~300mm.High-temperature flue gas outlet dust-laden is not higher than 5mg/Nm3, and high-temperature flue gas outlet particle maximum grain
Diameter is not more than 5 μm.
The above, only specific embodiments of the present invention cannot limit the range that invention is implemented with it, so it is equivalent
The displacement of component, or according to equivalent variations made by the invention patent protection scope and modification, should all still fall within what this patent was covered
Scope.In addition, between technical characteristic and technical characteristic in the present invention, between technical characteristic and technological invention, technological invention with
Use can be freely combined between technological invention.
Claims (10)
1. a kind of moving granular bed filter, which is characterized in that the moving granular bed filter include from inside to outside according to
The secondary internal layer cylinder (1) being arranged, middle cylinder (2) and outer layer barrel (3), form between internal layer cylinder (1) and middle cylinder (2)
First annular cavity, the first annular cavity is interior to be equipped with filtering stratum granulosum (4), and internal layer cylinder (1) and middle cylinder (2) are ring
The louvered structure of shape, internal layer cylinder (1) contain the axially aligned more Internal baffle items (11) being obliquely installed, middle cylinder
(2) contain the axially aligned more outer baffle items (21) being obliquely installed.
2. moving granular bed filter according to claim 1, which is characterized in that internal layer cylinder (1), middle cylinder
(2) and outer layer barrel (3) is upright state, is additionally provided in the first annular cavity braced frame (5), the moving bed particle
The lower part of layer filter is equipped with smoke inlet (6), and the top of the moving granular bed filter is equipped with exhanst gas outlet (7).
3. moving granular bed filter according to claim 2, which is characterized in that be equipped with interior sky in internal layer cylinder (1)
Chamber, middle cylinder (2) and outer layer barrel (3) form the second toroidal cavity;Smoke inlet (6) is connected to the internal cavity, and flue gas goes out
Mouth (7) is connected to second toroidal cavity;Alternatively, smoke inlet (6) is connected to second toroidal cavity, exhanst gas outlet (7) with
Internal cavity connection.
4. moving granular bed filter according to claim 2, which is characterized in that braced frame (5) contains along centre
The evenly distributed more root posts (51) of the circumferential direction of cylinder (2), the first annular cavity are separated to form by more root posts (51)
Multiple sector warehouses, filtering stratum granulosum (4) are located in the fan-shaped warehouse.
5. moving granular bed filter according to claim 4, which is characterized in that column (51) is externally provided with gusset, interior
Apron strip (11) and outer baffle item (21) are fixed with the link of boards, are equipped with main cooling tube (52) in column (51).
6. moving granular bed filter according to claim 5, which is characterized in that the inside of Internal baffle item (11) is equipped with
Internal baffle cooling tube (12), the outside of outer baffle item (21) are equipped with outer baffle cooling tube (22), Internal baffle cooling tube (12) and outside
Baffle cooling tube (22) is connected to main cooling tube (52).
7. moving granular bed filter according to claim 2, which is characterized in that the inclined direction of Internal baffle item (11)
Inclined direction with outer baffle item (21) is on the contrary, the longitudinal section of adjacent Internal baffle item (11) and the longitudinal section of outer baffle item (21)
Between mirror image each other, along direction from the top down, the distance between adjacent Internal baffle item (11) and outer baffle item (21) are gradually
Reduce.
8. moving granular bed filter according to claim 2, which is characterized in that the moving granular bed filter
It further include net particle storehouse (8) and charging valve, the lower part of net particle storehouse (8) passes through the top of charging hole and the first annular cavity
Connection, the charging valve are set on the charging hole.
9. moving granular bed filter according to claim 2, which is characterized in that the moving granular bed filter
It further include dirty particle storehouse (9) and blow-off valve, the top of dirty particle storehouse (9) passes through the lower part of drainage line and the first annular cavity
Connection, the blow-off valve are set in the drainage line.
10. moving granular bed filter according to claim 1, which is characterized in that filtering stratum granulosum (4) is quartz sand
Layer, aluminium oxide granule granulosa or steel ball layer.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201811587671.7A CN109499214B (en) | 2018-12-25 | 2018-12-25 | Moving bed particle layer filter |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201811587671.7A CN109499214B (en) | 2018-12-25 | 2018-12-25 | Moving bed particle layer filter |
Publications (2)
Publication Number | Publication Date |
---|---|
CN109499214A true CN109499214A (en) | 2019-03-22 |
CN109499214B CN109499214B (en) | 2024-03-26 |
Family
ID=65755290
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201811587671.7A Active CN109499214B (en) | 2018-12-25 | 2018-12-25 | Moving bed particle layer filter |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN109499214B (en) |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN2042374U (en) * | 1989-01-27 | 1989-08-09 | 王振声 | Filter for granular with auto-moving bed |
CN107019978A (en) * | 2016-01-29 | 2017-08-08 | 神华集团有限责任公司 | Moving granular bed filter, hot gas filtration system and method |
CN107511009A (en) * | 2017-09-18 | 2017-12-26 | 北京科技大学 | A kind of high-temperature dust-containing flue gas moving granular bed purification and residual neat recovering system |
CN108514807A (en) * | 2018-04-27 | 2018-09-11 | 浙江大学 | A kind of counterflow moving bed filter for installation |
CN209451525U (en) * | 2018-12-25 | 2019-10-01 | 北京京诚科林环保科技有限公司 | Moving bed particle layer filter |
-
2018
- 2018-12-25 CN CN201811587671.7A patent/CN109499214B/en active Active
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN2042374U (en) * | 1989-01-27 | 1989-08-09 | 王振声 | Filter for granular with auto-moving bed |
CN107019978A (en) * | 2016-01-29 | 2017-08-08 | 神华集团有限责任公司 | Moving granular bed filter, hot gas filtration system and method |
CN107511009A (en) * | 2017-09-18 | 2017-12-26 | 北京科技大学 | A kind of high-temperature dust-containing flue gas moving granular bed purification and residual neat recovering system |
CN108514807A (en) * | 2018-04-27 | 2018-09-11 | 浙江大学 | A kind of counterflow moving bed filter for installation |
CN209451525U (en) * | 2018-12-25 | 2019-10-01 | 北京京诚科林环保科技有限公司 | Moving bed particle layer filter |
Also Published As
Publication number | Publication date |
---|---|
CN109499214B (en) | 2024-03-26 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN106433700A (en) | Coke dry quenching dust removal system and process capable of efficiently recovering heat energy | |
CN107166977A (en) | A kind of closed vessel furnace furnace gas is reclaimed and cleaning treatment system | |
CN209451525U (en) | Moving bed particle layer filter | |
CN105021051B (en) | A kind of waste heat of cupola furnace utilizes dedusting and desulphurization integrated system | |
CN109499214A (en) | Moving bed particle layer filter | |
CN107670413A (en) | A kind of method of sack cleaner heat recovery | |
CN205640928U (en) | Fluidized bed waste incineration system | |
CN107023839B (en) | A kind of application method of processing absorption VOCs exhaust gas solid waste accumulation of heat fluidizing combustion furnaces | |
CN106989400B (en) | A kind of application method of absorption VOCs exhaust gas solid waste accumulation of heat Boiling Combustion subsiding and purifying devices | |
CN207132737U (en) | A kind of closed vessel furnace furnace gas recovery and cleaning treatment system | |
CN206244715U (en) | A kind of CDQ Emission Control System of energy high efficiente callback heat energy | |
CN202733916U (en) | Burning dregs fluidized bed boiler | |
CN102012097A (en) | Fluidized bed oil and water dual-medium circulation boiler | |
CN209292388U (en) | Dry-type dust removal and full waste heat recovery equipment for converter flue gas | |
CN109487031B (en) | Dry dust removal and full waste heat recovery equipment for converter flue gas | |
CN108006685A (en) | A kind of waste incineration CFB boiler of multistage gas-solid separating device arranged in series | |
CN109516462B (en) | Active carbon regeneration system | |
CN209493320U (en) | Activated carbon regeneration system | |
CN207880861U (en) | A kind of waste incineration CFB boiler of multistage gas-solid separating device arranged in series | |
CN107101219A (en) | A kind of circulation air path device of biomass boiler | |
CN106996566B (en) | A kind of processing absorption VOCs exhaust gas solid waste accumulation of heat fluidizing combustion furnaces | |
CN107023836B (en) | A kind of absorption VOCs exhaust gas solid waste accumulation of heat Boiling Combustion subsiding and purifying device | |
CN106964325B (en) | A kind of preparation method for adsorbing the dedicated fused salt patch of VOCs solid waste accumulation of heat fluidizing combustion furnace | |
CN2201582Y (en) | Dust romoving heat exchanger | |
CN106196028B (en) | A kind of organic heat carrier CFBB |
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 | ||
GR01 | Patent grant | ||
GR01 | Patent grant |