CN210434221U - Water mist spraying and wet corona oxidation combined process treatment device - Google Patents
Water mist spraying and wet corona oxidation combined process treatment device Download PDFInfo
- Publication number
- CN210434221U CN210434221U CN201921023424.4U CN201921023424U CN210434221U CN 210434221 U CN210434221 U CN 210434221U CN 201921023424 U CN201921023424 U CN 201921023424U CN 210434221 U CN210434221 U CN 210434221U
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- Prior art keywords
- spray
- drain pipe
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- pipe
- fixed plate
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 44
- 230000003647 oxidation Effects 0.000 title claims abstract description 16
- 238000007254 oxidation reaction Methods 0.000 title claims abstract description 16
- 238000005507 spraying Methods 0.000 title claims description 14
- 239000003595 mist Substances 0.000 title claims description 11
- 238000000034 method Methods 0.000 title claims description 10
- 239000007921 spray Substances 0.000 claims abstract description 57
- 239000000428 dust Substances 0.000 claims abstract description 27
- 239000000779 smoke Substances 0.000 claims abstract description 9
- 239000002351 wastewater Substances 0.000 claims abstract description 5
- 235000017166 Bambusa arundinacea Nutrition 0.000 claims description 7
- 235000017491 Bambusa tulda Nutrition 0.000 claims description 7
- 241001330002 Bambuseae Species 0.000 claims description 7
- 235000015334 Phyllostachys viridis Nutrition 0.000 claims description 7
- 239000011425 bamboo Substances 0.000 claims description 7
- 238000005516 engineering process Methods 0.000 claims description 4
- 238000001556 precipitation Methods 0.000 claims description 4
- 238000001035 drying Methods 0.000 claims description 3
- 239000002912 waste gas Substances 0.000 abstract description 20
- 239000012717 electrostatic precipitator Substances 0.000 abstract description 12
- 230000000694 effects Effects 0.000 abstract description 4
- 239000004744 fabric Substances 0.000 description 4
- 239000007789 gas Substances 0.000 description 4
- 238000004140 cleaning Methods 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 239000004753 textile Substances 0.000 description 3
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 2
- 238000001816 cooling Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000000835 fiber Substances 0.000 description 2
- 239000003546 flue gas Substances 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 239000013618 particulate matter Substances 0.000 description 2
- 230000000737 periodic effect Effects 0.000 description 2
- 239000012716 precipitator Substances 0.000 description 2
- 238000011084 recovery Methods 0.000 description 2
- 238000005406 washing Methods 0.000 description 2
- 239000004902 Softening Agent Substances 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000012141 concentrate Substances 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 230000005684 electric field Effects 0.000 description 1
- 230000005685 electric field effect Effects 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 239000004519 grease Substances 0.000 description 1
- 238000009998 heat setting Methods 0.000 description 1
- 238000001802 infusion Methods 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 239000011347 resin Substances 0.000 description 1
- 229920005989 resin Polymers 0.000 description 1
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Abstract
The utility model discloses a water smoke sprays and makes up processing apparatus with wet-type corona oxidation, including spray room and electrostatic precipitator, the spray room left end is connected with the intake pipe, the spray room right-hand member is connected with electrostatic precipitator through the outlet duct, the spray room bottom is provided with first drain pipe, the electrostatic precipitator bottom is provided with the second drain pipe, all install the valve on first drain pipe and the second drain pipe, the one end that the electrostatic precipitator was kept away from to one end, the second drain pipe that the spray room was kept away from to first drain pipe all is connected with the wastewater disposal basin, the electrostatic precipitator top is provided with the blast pipe, the utility model relates to a rationally, spray and combine together with corona dust removal with the water smoke, played better treatment effect to the high temperature waste gas of forming machine.
Description
Technical Field
The utility model relates to a waste gas treatment technical field specifically is a water smoke sprays and makes up technology processing apparatus with wet-type corona oxidation.
Background
The heat setting machine is a device which utilizes hot air to dry and arrange and set textile fabrics (such as cloth), and the cloth is subjected to softening treatment, so that the cloth is not easy to shrink. The working temperature of the setting machine can reach 130-200 ℃, the temperature of flue gas discharged after setting can reach 90-160 ℃, wax, oil, a softening agent, resin and the like attached to textiles are changed into gaseous state under the high temperature condition, meanwhile, dust such as yarn hair and the like in the textiles also enter the flue gas, so that the waste gas of the setting machine must be reasonably treated, and otherwise, the environment is seriously damaged.
SUMMERY OF THE UTILITY MODEL
An object of the utility model is to provide a water smoke sprays and makes up technology processing apparatus with wet-type corona oxidation to solve the problem that provides among the above-mentioned background art.
In order to achieve the above object, the utility model provides a following technical scheme:
the utility model provides a water smoke sprays and combines technology processing apparatus with wet-type corona oxidation, includes spray room and electrostatic precipitator, the spray room left end is connected with the intake pipe, the spray room right-hand member is connected with electrostatic precipitator through the outlet duct, the spray room bottom is provided with first drain pipe, the electrostatic precipitator bottom is provided with the second drain pipe, all install the valve on first drain pipe and the second drain pipe, the one end that the spray room was kept away from to first drain pipe, the one end that the electrostatic precipitator was kept away from to the second drain pipe all are connected with the wastewater disposal basin, the electrostatic precipitator top is provided with the blast pipe.
Preferably, a filter screen and a drying layer are sequentially arranged inside the spraying chamber from left to right.
Preferably, a plurality of evenly distributed's atomizer is installed on spray room top, atomizer is located between filter screen and the dry layer, atomizer's input is connected with the transfer line, atomizer's one end is kept away from to the transfer line extends to the spray room outside to be connected with the water pipe, the water pipe is connected with external water source.
Preferably, the left end of the spray chamber is provided with a movable door.
Preferably, the electric precipitation room internally mounted has a conductive tube, conductive tube is connected with external low voltage power supply through the wire, high voltage electrode is installed on the inside top of electric precipitation room, high voltage electrode is connected with external high voltage power supply through the wire.
Preferably, the indoor portion of electrostatic precipitator is provided with the fixed plate, the fixed plate is located the conducting cylinder top, the fixed plate bottom is provided with a plurality of evenly distributed's the board that sprays, the one end that sprays the board is rotated and is connected on the fixed plate, spray the board bottom and install a plurality of evenly distributed's nozzle, the input of nozzle is connected with external water source through the inlet tube, electric putter is installed on the fixed plate top, electric putter's flexible end extends to the fixed plate below to rotate the connection and spray on the board.
Compared with the prior art, the beneficial effects of the utility model are that: when the device is used, high-temperature waste gas discharged by the setting machine is guided into the spraying chamber, sprayed and cooled, and components such as larger particles, grease and the like in the waste gas are removed, the waste gas is cooled to about the temperature and contains a small amount of oil smoke particles, then the waste gas is introduced into the electric dust removal chamber, residual harmful substances in the waste gas are removed by corona dust removal, and gas meeting the standard is discharged; through spray cooling dust removal and corona dust removal, waste gas can be better treated, and the problems of low waste gas treatment efficiency and poor treatment effect of a single treatment mode are solved; the filter screen can intercept yarn hair, flying wadding and the like with larger volume in the waste gas, and the accumulated fibers are taken out through the movable door, so that the recovery treatment is convenient; after the waste gas treatment work, through the nozzle to the torch blowout cleaning water, wash the dust that adsorbs on the conductive tube, through electric putter periodic flexible, drive and spray the board and swing back and forth, constantly change the jet direction and the scope of rivers, avoid washing the dead angle, improve the cleaning performance. The utility model relates to a rationally, spray the water smoke and combine together with corona dust removal, played better treatment to the high temperature waste gas of forming machine.
Drawings
FIG. 1 is a schematic structural diagram of a water mist spraying and wet corona oxidation combined process treatment device;
FIG. 2 is a schematic structural view of a spray chamber in a combined treatment device of water mist spraying and wet corona oxidation;
fig. 3 is a schematic structural diagram of an electric dust removal chamber in a water mist spraying and wet corona oxidation combined process treatment device.
In the figure: 1-spray room, 2-air inlet pipe, 3-air outlet pipe, 4-electric dust removal room, 5-first water discharge pipe, 6-wastewater disposal basin, 7-second water discharge pipe, 8-valve, 9-exhaust pipe, 10-filter screen, 11-drying layer, 12-atomizer, 13-infusion pipe, 14-water pipe, 15-movable door, 16-high voltage electrode, 17-conductive cylinder, 18-fixed plate, 19-spray plate, 20-nozzle, 21-water inlet pipe, and 22-electric push rod.
Detailed Description
The technical solutions in the embodiments of the present invention will be described clearly and completely with reference to the accompanying drawings in the embodiments of the present invention, and it is obvious that the described embodiments are only some embodiments of the present invention, not all embodiments. Based on the embodiments in the present invention, all other embodiments obtained by a person skilled in the art without creative work belong to the protection scope of the present invention.
Referring to fig. 1 to 3, the present invention provides a technical solution: a water mist spraying and wet corona oxidation combined process treatment device comprises a spray room 1 and an electric dust removal room 4, wherein the left end of the spray room 1 is connected with an air inlet pipe 2, the right end of the spray room 1 is connected with the electric dust removal room 4 through an air outlet pipe 3, a first water discharge pipe 5 is arranged at the bottom end of the spray room 1, a second water discharge pipe 7 is arranged at the bottom end of the electric dust removal room 4, valves 8 are respectively arranged on the first water discharge pipe 5 and the second water discharge pipe 7, one end of the first water discharge pipe 5, which is far away from the spray room 1, and one end of the second water discharge pipe 7, which is far away from the electric dust removal room 4, are respectively connected with a wastewater pool 6, the top end of the electric dust removal room 4 is provided with an exhaust pipe 9, during use, high-temperature waste gas discharged by a setting machine is guided into the spray room 1, after being sprayed and cooled, and components such as larger particulate, introducing the waste gas into an electric dust removal chamber 4, removing residual harmful substances in the waste gas by using corona dust removal, and discharging gas meeting the standard; through spraying cooling dust removal and corona dust removal, can handle waste gas better, avoid single treatment mode exhaust-gas treatment inefficiency, the not good problem of treatment effect.
The spray chamber 1 is inside to turn right from a left side and has set gradually filter screen 10 and dry layer 11, and filter screen 10 can intercept the great yarn hair of volume, flying wadding etc. in the waste gas to take out accumulational fibre through dodge gate 15, the recovery processing of being convenient for.
A plurality of evenly distributed's atomizer 12 is installed on spray room 1 top, atomizer 12 is located between filter screen 10 and the dry layer 11, atomizer 12's input is connected with transfer line 13, the one end that atomizer 12 was kept away from to transfer line 13 extends to spray room 1 outside to be connected with water pipe 14, water pipe 14 is connected with external water source, through atomizer 12 blowout atomizing water liquid, and the particulate matter in water smoke and the waste gas combines, promotes harmful substance's settlement.
The left end of the spray room 1 is provided with a movable door 15.
The utility model discloses an electrostatic precipitator, including electro-precipitator 4, electro-precipitator 17, high voltage electrode 16, and electrically conductive section of thick bamboo 17 voltage to form the electric field between high voltage electrode 16 and electrically conductive section of thick bamboo 17, ionize the air between them, decompose the organic matter in the waste gas, and under the electric field effect, the dust particulate matter can concentrate the absorption on electrically conductive section of thick bamboo 17 surface, electrically conductive section of thick bamboo 17 is connected with external low voltage power supply through the wire to electrically conductive section of thick bamboo 17, high voltage electrode 16 is connected with external high voltage power supply through the wire, and high voltage electrode 16.
The inside fixed plate 18 that is provided with of electricity clean room 4, fixed plate 18 is located conductive tube 17 top, fixed plate 18 bottom is provided with a plurality of evenly distributed's spray board 19, spray board 19's one end is rotated and is connected on fixed plate 18, spray board 19 bottom is installed a plurality of evenly distributed's nozzle 20, nozzle 20's input is connected with external water source through inlet tube 21, electric putter 22 is installed on fixed plate 18 top, electric putter 22's flexible end extends to fixed plate 18 below to rotate and connect on spray board 19, after the exhaust-gas treatment work, through nozzle 20 to the clean water of torch 17 blowout, wash the dust that adsorbs on conductive tube 17, through electric putter 22 periodic flexible, drive spray board 19 swing back and forth, constantly change the jet direction and the scope of rivers, avoid washing the dead angle, the cleaning effect is improved.
It is obvious to a person skilled in the art that the invention is not restricted to details of the above-described exemplary embodiments, but that it can be implemented in other specific forms without departing from the spirit or essential characteristics of the invention. The present embodiments are therefore to be considered in all respects as illustrative and not restrictive, the scope of the invention being indicated by the appended claims rather than by the foregoing description, and all changes which come within the meaning and range of equivalency of the claims are therefore intended to be embraced therein. Any reference sign in a claim should not be construed as limiting the claim concerned.
Furthermore, it should be understood that although the present description refers to embodiments, not every embodiment may contain only a single embodiment, and such description is for clarity only, and those skilled in the art should integrate the description, and the embodiments may be combined as appropriate to form other embodiments understood by those skilled in the art.
Claims (6)
1. The utility model provides a water smoke sprays and wet-type corona oxidation combination technology processing apparatus, includes spray booth (1) and electric precipitation room (4), its characterized in that: spray room (1) left end is connected with intake pipe (2), spray room (1) right-hand member is connected with electric dust chamber (4) through outlet duct (3), spray room (1) bottom is provided with first drain pipe (5), electric dust chamber (4) bottom is provided with second drain pipe (7), all install valve (8) on first drain pipe (5) and second drain pipe (7), the one end that electric dust chamber (4) were kept away from in one end that spray room (1) was kept away from in first drain pipe (5), second drain pipe (7) all is connected with wastewater disposal basin (6), electric dust chamber (4) top is provided with blast pipe (9).
2. The water mist spraying and wet corona oxidation combined process treatment device according to claim 1, characterized in that: the spray room (1) is internally provided with a filter screen (10) and a drying layer (11) from left to right in sequence.
3. The water mist spraying and wet corona oxidation combined process treatment device according to claim 2, characterized in that: spray chamber (1) top is installed a plurality of evenly distributed's atomizer (12), atomizer (12) are located between filter screen (10) and dry layer (11), the input of atomizer (12) is connected with transfer line (13), the one end that atomizer (12) were kept away from in transfer line (13) extends to spray chamber (1) outside to be connected with water pipe (14), water pipe (14) are connected with external water source.
4. The water mist spraying and wet corona oxidation combined process treatment device according to claim 3, characterized in that: the left end of the spray room (1) is provided with a movable door (15).
5. The water mist spraying and wet corona oxidation combined process treatment device according to claim 1, characterized in that: electric dust removal room (4) internally mounted has electrically conductive section of thick bamboo (17), electrically conductive section of thick bamboo (17) are connected with external low voltage power supply through the wire, high voltage electrode (16) are installed on electric dust removal room (4) inside top, high voltage electrode (16) are connected with external high voltage power supply through the wire.
6. The water mist spraying and wet corona oxidation combined process treatment device according to claim 5, characterized in that: electric precipitation room (4) inside is provided with fixed plate (18), fixed plate (18) are located conducting cylinder (17) top, fixed plate (18) bottom is provided with a plurality of evenly distributed's spray board (19), the one end rotation of spray board (19) is connected on fixed plate (18), spray board (19) bottom and install a plurality of evenly distributed's nozzle (20), the input of nozzle (20) is connected with external water source through inlet tube (21), electric putter (22) are installed on fixed plate (18) top, the flexible end of electric putter (22) extends to fixed plate (18) below to rotate and connect on spray board (19).
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201921023424.4U CN210434221U (en) | 2019-07-03 | 2019-07-03 | Water mist spraying and wet corona oxidation combined process treatment device |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201921023424.4U CN210434221U (en) | 2019-07-03 | 2019-07-03 | Water mist spraying and wet corona oxidation combined process treatment device |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN210434221U true CN210434221U (en) | 2020-05-01 |
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Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201921023424.4U Expired - Fee Related CN210434221U (en) | 2019-07-03 | 2019-07-03 | Water mist spraying and wet corona oxidation combined process treatment device |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN210434221U (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN114261662A (en) * | 2021-12-29 | 2022-04-01 | 南京皇保电动车制造有限公司 | But sterile sanitation car railway carriage of automatically cleaning |
-
2019
- 2019-07-03 CN CN201921023424.4U patent/CN210434221U/en not_active Expired - Fee Related
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN114261662A (en) * | 2021-12-29 | 2022-04-01 | 南京皇保电动车制造有限公司 | But sterile sanitation car railway carriage of automatically cleaning |
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| Date | Code | Title | Description |
|---|---|---|---|
| GR01 | Patent grant | ||
| GR01 | Patent grant | ||
| DD01 | Delivery of document by public notice | ||
| DD01 | Delivery of document by public notice |
Addressee: Shanghai sanlan Environmental Protection Technology Co.,Ltd. Person in charge of patents Document name: payment instructions |
|
| DD01 | Delivery of document by public notice | ||
| DD01 | Delivery of document by public notice |
Addressee: Shanghai sanlan Environmental Protection Technology Co.,Ltd. Person in charge of patents Document name: payment instructions |
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| CF01 | Termination of patent right due to non-payment of annual fee | ||
| CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20200501 |