CN109011931B - Desulfurization denitration dust removal integration equipment - Google Patents

Desulfurization denitration dust removal integration equipment Download PDF

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Publication number
CN109011931B
CN109011931B CN201810656075.3A CN201810656075A CN109011931B CN 109011931 B CN109011931 B CN 109011931B CN 201810656075 A CN201810656075 A CN 201810656075A CN 109011931 B CN109011931 B CN 109011931B
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desulfurizer
dust remover
communicated
regulating valve
control valve
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CN109011931A (en
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万加兵
王加东
丰来国
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Yancheng Lanfeng Environmental Engineering Technology Co Ltd
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Yancheng Lanfeng Environmental Engineering Technology Co Ltd
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    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D47/00—Separating dispersed particles from gases, air or vapours by liquid as separating agent
    • B01D47/06—Spray cleaning
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34—Chemical or biological purification of waste gases
    • B01D53/46—Removing components of defined structure
    • B01D53/48—Sulfur compounds
    • B01D53/50—Sulfur oxides
    • B01D53/501—Sulfur oxides by treating the gases with a solution or a suspension of an alkali or earth-alkali or ammonium compound
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34—Chemical or biological purification of waste gases
    • B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86—Catalytic processes
    • B01D53/8621—Removing nitrogen compounds
    • B01D53/8625—Nitrogen oxides
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2251/00—Reactants
    • B01D2251/40—Alkaline earth metal or magnesium compounds
    • B01D2251/404—Alkaline earth metal or magnesium compounds of calcium
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2251/00—Reactants
    • B01D2251/60—Inorganic bases or salts
    • B01D2251/604—Hydroxides

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  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Treating Waste Gases (AREA)

Abstract

The invention provides desulfurization, denitrification and dust removal integrated equipment which comprises a first desulfurizer, a first dust remover, a second dust remover and a second desulfurizer, wherein the first desulfurizer, the first dust remover, the second dust remover and the second desulfurizer are communicated in sequence; the second desulfurizer can also be communicated with a preset SCR denitration device so as to facilitate denitration of flue gas; the first dust remover is communicated with the second dust remover through a fence baffle, and the first dust remover and the second dust remover are funnel-shaped dust removers. The invention can better realize the aims of desulfurization, denitration and dust removal based on a plurality of continuous processes. In the whole process flow, a plurality of desulfurizing agents and a plurality of dedusting agents are used, the automatic preparation of the dedusting agents and the automation of desulfurization and dedusting are realized, the desulfurization and dedusting efficiency is improved, and a better desulfurization and dedusting effect is achieved.

Description

Desulfurization denitration dust removal integration equipment
Technical Field
The invention relates to the field of environmental protection, in particular to desulfurization, denitrification and dust removal integrated equipment.
Background
Coal is used as a main primary energy source in China, occupies a large proportion in energy consumption of power plants, boilers, coking industries and the like, and particularly, along with the development of economy in China in the year, the energy demand is increased, and the consumption of coal is greatly increased. The coal can generate sulfur dioxide when burning, for the coking industry, a coke oven carbonization chamber is provided with a heat source by a coal gas heating vertical flue, the waste gas generated after the coal gas is heated contains more sulfur dioxide, nitrogen-containing oxides and particulate matters, and if the waste gas is directly discharged, the pollution to the air is serious.
In the conventional process, desulfurization and dust removal are respectively completed in respective devices as independent unit operations, and the independent waste gas treatment process has high cost, wastes space and is complex in process, so that a desulfurization, denitrification and dust removal integrated device needs to be developed, and the two purposes of desulfurization and dust removal are achieved together.
Disclosure of Invention
In order to solve the technical problem, the invention provides desulfurization, denitrification and dust removal integrated equipment.
The invention is realized by the following technical scheme:
a desulfurization, denitrification and dust removal integrated device comprises a first desulfurizer, a first dust remover, a second dust remover and a second desulfurizer, wherein the first desulfurizer, the first dust remover, the second dust remover and the second desulfurizer are communicated in sequence;
the second desulfurizer can also be communicated with a preset SCR denitration device so as to facilitate denitration of flue gas;
the first dust remover is communicated with the second dust remover through a fence baffle, and the first dust remover and the second dust remover are funnel-shaped dust removers.
Furthermore, a plurality of dedusting liquid nozzles are arranged in the horizontal direction of the second deduster, the dedusting liquid nozzles are communicated with a dedusting liquid storage tank through dedusting liquid connecting pipelines, each communicated passage is provided with a control valve, and the control valves are controlled by a master controller;
the mixture of sodium dodecyl sulfate and tung tree seed oil is stored in the dust removing liquid storage tank.
Further, a second atomizer is arranged at the upper part of the second desulfurizer, the second atomizer is communicated with a desulfurizer storage device, the desulfurizer storage device pumps a desulfurizer into the second atomizer through a dosing device and a solution pump, and the desulfurizer is atomized after passing through a bowl-shaped nozzle in the second atomizer;
the second desulfurizer is provided with a Venturi tube and a rotational flow plate behind the second atomizer along the airflow direction, and the flue gas and desulfurizer particles are fully mixed under the action of the Venturi tube and the rotational flow plate; the bottom of the second desulfurizer is also provided with a dehydrator so as to facilitate gas-liquid separation;
the second desulfurizationSO is also arranged near the second atomizer of the atomizer2Concentration detector, said SO2The concentration detector is communicated with the master controller SO as to realize the injection of the desulfurizer and the SO2Linkage of concentration with SO2The spraying amount of the desulfurizer is automatically adjusted according to the change of the concentration.
Further, the desulfurizer storage is communicated with a desulfurizer preparation device, the desulfurizer preparation device comprises a first main material injection port, a second main material injection port and a third main material injection port, the first main material injection port is communicated with the acetaldehyde storage tank through a first sub-control valve, the second main material injection port is communicated with the aminomethane storage tank through a second sub-control valve, and the third main material injection port is communicated with the sodium tripolyphosphate storage tank through a third sub-control valve;
the bottom of the desulfurizer preparation device is also provided with a heater and a temperature sensor, the heater, the temperature sensor, the first sub-control valve, the second sub-control valve and the third sub-control valve are all controlled by a third sub-controller, and the third sub-controller is controlled by the master controller;
in the preparation process of the desulfurizer, the temperature of the bottom of the desulfurizer preparation device is controlled to be about 75 ℃, and the preparation time is not shorter than 2.5 hours;
the desulfurizer preparation device is also provided with an additive filling port, the additive filling port is used for manually adding an additive which can be used for improving the performance of the desulfurizer, and the additive can be ethylene glycol;
the desulfurizer obtained by the desulfurizer preparation device can be used for desulfurization, and part of grease particles can be removed, so that the residue of the oily dedusting agent sprayed in the second deduster in flue gas is avoided.
The invention has the following beneficial effects:
(1) the purposes of desulfurization, denitration and dust removal can be well realized based on a plurality of continuous processes;
(2) in the whole process flow, a plurality of desulfurizing agents and a plurality of dedusting agents are used, the automatic preparation of the dedusting agents and the automation of desulfurization and dedusting are realized, the desulfurization and dedusting efficiency is improved, and a better desulfurization and dedusting effect is achieved.
Drawings
FIG. 1 is a schematic view of an integrated desulfurization, denitrification and dust removal device provided in this embodiment;
FIG. 2 is a schematic view of a first desulfurizer provided in the present embodiment;
FIG. 3 is a schematic diagram of an injectant preparation apparatus provided in this example;
fig. 4 is a schematic view of the first liquid-mixture chamber provided in the present embodiment;
fig. 5 is a schematic view of a second liquid-mixture chamber provided in the present embodiment;
FIG. 6 is a schematic view of a second dust collector provided in the present embodiment;
FIG. 7 is a schematic view of a desulfurizing agent preparation apparatus provided in this example.
Detailed Description
In order to make the objects, technical solutions and advantages of the present invention more apparent, the present invention will be described in further detail with reference to the accompanying drawings.
The embodiment of the invention provides desulfurization, denitrification and dust removal integrated equipment, which comprises a first desulfurizer 1, a first dust remover 2, a second dust remover 3 and a second desulfurizer 4, wherein the first desulfurizer 1, the first dust remover 2, the second dust remover 3 and the second desulfurizer 4 are communicated in sequence, as shown in figure 1.
Further, the second desulfurizer can also be communicated with a preset SCR denitration device so as to facilitate denitration of flue gas. The SCR denitration device comprises a catalyst injector for injecting powder catalyst into a flue gas flowing channel. The powder catalyst may be a catalyst that catalyzes a selective catalytic reduction reaction SCR for denitration. The passage can be also provided with a speed reducing plate with a porous structure, and the speed reducing plate is used for prolonging the retention time of the powder catalyst and increasing the catalytic efficiency.
The SCR denitration device may further include a catalyst transportation system, and the catalyst transportation system may include: a fan; and the rotary feeder is respectively connected with the catalyst source, the fan and the catalyst ejector, and transports the powder catalyst in the catalyst source to the catalyst ejector under the action of the fan.
The SCR denitration device may further include a regulator for regulating an amount of the powdered catalyst injected into the flue by the catalyst injector.
As shown in fig. 2, the first desulfurizer 1 is communicated with a smoke exhaust duct 100 of a boiler, a plurality of slaked lime injection holes 101 are formed at a position where the smoke exhaust duct 100 is separated from the first desulfurizer 1 by a first preset distance, and the slaked lime injection holes 101 are used for introducing slaked lime into the smoke exhaust duct 100 so that smoke can enter the first desulfurizer 1 together with the slaked lime; the bottom of the first desulfurizer 1 is provided with a condensed water injection hole 11, and the condensed water injection hole 11 is used for injecting condensed water into the first desulfurizer 1, so that the flue gas is subjected to primary desulfurization in the first desulfurizer 1.
First dust remover 2 with second dust remover 3 passes through fence baffle intercommunication, first dust remover 2 and second dust remover 3 are hopper-shaped dust remover, 2 bottoms in first dust remover are provided with first gravity flap valve 200, 3 bottoms in second dust remover are provided with second gravity flap valve 300, first gravity flap valve 200 with second gravity flap valve 300 all is controlled by total controller.
The first dust remover 2 is communicated with an injection preparation device 21, a first atomizer 22 is arranged at the top of the first dust remover 2, and an outlet of the injection preparation device 21 is communicated with the first atomizer 22, so that the first atomizer atomizes the injection and then injects the injection into the first dust remover 2.
As shown in fig. 3, the injectant preparation device 21 includes a first liquid mixing port 201 and a second liquid mixing port 202, the first liquid mixing port 201 is communicated with an outlet of a first liquid mixing chamber 203 through a first channel, the second liquid mixing port 202 is communicated with an outlet of a second liquid mixing chamber 204 through a second channel, a first control valve 205 is arranged at the first channel, a second control valve 206 is arranged at the second channel, and both the first control valve 205 and the second control valve 206 are controlled by the general controller.
The bottom of the spraying agent preparation device 21 is provided with a pressure sensor 23, the pressure sensor 23 is communicated with the master controller, if the pressure sensor senses that the bottom pressure of the spraying agent preparation device is smaller than a preset value, the master controller starts a first control valve 205 and a second control valve 206, and the flow ratio of the first control valve 205 to the second control valve 206 is 4: 3. The bottom of the spraying agent preparation device can be also provided with a stirring mechanism.
As shown in fig. 4, the first mixed solution chamber 203 includes a solvent injection port 2031, a first solute injection port 2032, and a second solute injection port 2033, the solvent injection port 2031 is communicated with a water inlet pipe through a first regulation valve 2034, the first solute injection port 2032 is communicated with a first solute storage tank 2035 through a second regulation valve 2036, and the second solute injection port 2033 is communicated with a second solute storage tank 2037 through a third regulation valve 2038. The first solute storage tank 2035 stores a solution of sodium dodecylbenzenesulfonate with a concentration of 0.15 weight percent, and the second solute storage tank 2037 stores a solution of fatty alcohol-polyoxyethylene ether with a concentration of 0.08 weight percent. The first regulating valve 2034, the second regulating valve 2036 and the third regulating valve 2038 are controlled by a first branch controller, and the first branch controller is controlled by the general controller.
The first liquid level meter 2039 is arranged in the first liquid mixing chamber 203, and if the liquid level in the first liquid mixing chamber is less than a preset liquid level low value, the first divider automatically opens the first regulating valve, the second regulating valve and the third regulating valve, and controls the first regulating valve, the second regulating valve and the third regulating valve so that the flow rates of the solvent injection port, the first solute injection port and the second solute injection port are 2:3: 2.
And if the liquid level in the first liquid mixing chamber reaches a high liquid level value, closing the first regulating valve, the second regulating valve and the third regulating valve.
A spiral stirrer 2040 is arranged at the bottom of the first liquid mixing chamber 203, and the spiral stirrer 2040 is controlled by the first divider.
As shown in fig. 5, the second liquid mixing chamber 204 includes a first component dispensing inlet 2041 and a second component dispensing inlet 2042, the first component dispensing inlet 2041 is communicated with a sodium chloride solution storage tank 2044 storing a weight percentage of 1.5 through a fourth regulating valve 2043, the second component dispensing inlet 2042 is communicated with a sodium sulfite solution storage tank 2046 storing a weight percentage of 2 through a fifth regulating valve 2045, and the fourth regulating valve 2043 and the fifth regulating valve 2045 are controlled by a second sub-controller controlled by the main controller.
A second liquid level meter 2047 is arranged in the second liquid mixing chamber, and if the liquid level in the second liquid mixing chamber is smaller than a preset lower liquid level limit, the second branch controller automatically opens the fourth regulating valve 2043 and the fifth regulating valve 2045, and controls the fourth regulating valve 2043 and the fifth regulating valve 2045 so that the flow rates of the first component dispensing inlet and the second component dispensing inlet are 1: 2.
If the liquid level in the second liquid mixing chamber reaches the upper liquid level limit, the fourth regulating valve 2043 and the fifth regulating valve 2045 are closed.
And a rod-shaped stirrer is arranged at the bottom of the second liquid mixing chamber and is controlled by the second branch controller. In particular, the rod beater is attached to a drive motor for rotationally driving the rod beater, the rod beater comprising a drive shaft having a distal end adapted to be coupled to the drive motor, and a beater head. The beater further comprises coupling means for releasably coupling the beater head to the drive shaft, thereby coupling the beater head to the drive shaft at different relative positions along the drive shaft.
And after the atomized spraying agent enters the first dust remover, the atomized spraying agent is fully contacted with the flue gas in the first dust remover, so that the wrapped flue gas is settled and then falls to the bottom of the funnel-type first dust remover, and when the sediment at the bottom of the first dust remover reaches a certain amount, the first gravity flap valve is opened, and the sediment can be discharged.
As shown in fig. 6, a plurality of vertically disposed first baffles 31 are horizontally disposed in the second dust collector 3, a plurality of triangular second baffles 32 are further disposed in the middle of the second dust collector along the flue gas flowing direction, and under the action of the first baffles and the second baffles, the flue gas flowing direction changes and the flowing speed is reduced.
The second dust remover horizontal direction is provided with a plurality of dust removal liquid nozzles, dust removal liquid spray set with first baffle is crisscross places, and the aim at placing like this in time contacts with dust removal liquid after the air current direction changes, maximize dust removal effect.
The dust removal liquid nozzle all communicates with dust removal liquid storage jar through dust removal liquid connecting tube, all is provided with the control valve on the passageway of every intercommunication, the control valve all is controlled by master controller.
The mixture of sodium dodecyl sulfate and tung tree seed oil is stored in the dust removing liquid storage tank. In the second dust remover, the specific flowing direction of the airflow is changed and the speed of the flue gas is reduced through the first baffle and the second baffle, so that the flue gas is fully contacted with the mixture of the sodium dodecyl sulfate and the tung tree seed oil, lipophilic particles in the flue gas are gathered to form larger particles, and the particles grow up and are deposited at the bottom of the second dust remover due to the lower speed of the airflow in the process. And when the sediment at the bottom of the second dust remover reaches a certain amount, the second gravity flap valve is opened, and the sediment can be discharged.
The upper portion of second desulfurizer 4 is provided with the second atomizer, second atomizer and desulfurizer memory intercommunication, the desulfurizer memory is through dosing device and solution pump with the desulfurizer pump into the second atomizer, the desulfurizer via be vaporific behind the bowl type nozzle in the second atomizer promptly.
The second desulfurizer is provided with venturi and whirl board along the air current direction after the second atomizer, process venturi and whirl board's effect, flue gas and desulfurizer particle intensive mixing. And the bottom of the second desulfurizer is also provided with a dehydrator so as to facilitate gas-liquid separation.
Specifically, SO is also arranged near the second atomizer of the second desulfurizer2Concentration detector, said SO2The concentration detector is communicated with the master controller SO as to realize the injection of the desulfurizer and the SO2Linkage of concentration with SO2The spraying amount of the desulfurizer is automatically adjusted according to the change of the concentration.
The desulfurizer storage is communicated with the desulfurizer preparation device 40, as shown in fig. 7, the desulfurizer preparation device 40 includes a first main material injection port 401, a second main material injection port 402, and a third main material injection port 403, the first main material injection port 401 is communicated with an acetaldehyde storage tank 404 through a first partial control valve 405, the second main material injection port 402 is communicated with an aminomethane storage tank 406 through a second partial control valve 407, and the third main material injection port 403 is communicated with a sodium tripolyphosphate storage tank 408 through a third partial control valve 409.
The bottom of the desulfurizer preparation device 40 is also provided with a heater 410 and a temperature sensor 411, the heater, the temperature sensor, the first sub-control valve, the second sub-control valve and the third sub-control valve are all controlled by a third sub-controller, and the third sub-controller is controlled by the main controller.
In the preparation process of the desulfurizer, the temperature of the bottom of the desulfurizer preparation device is controlled to be about 75 ℃, and the preparation time is not shorter than 2.5 hours.
The desulfurizer preparation device is also provided with an additive filling port for manually adding an additive which can be used for improving the performance of the desulfurizer, and the additive can be ethylene glycol.
The desulfurizer obtained by the desulfurizer preparation device can be used for desulfurization, and part of grease particles can be removed, so that the residue of the oily dedusting agent sprayed in the second deduster in flue gas is avoided. The dust content and the sulfur dioxide content in the flue gas obtained by the second desulfurizer can meet the national standard, and no new harmful substances are introduced in the process of sulfur removal and dust removal.
The above disclosure is only for the purpose of illustrating the preferred embodiments of the present invention, and it is therefore to be understood that the invention is not limited by the scope of the appended claims.

Claims (3)

1. The utility model provides a SOx/NOx control dust removal integration equipment which characterized in that:
the desulfurization device comprises a first desulfurizer, a first dust remover, a second dust remover and a second desulfurizer, wherein the first desulfurizer, the first dust remover, the second dust remover and the second desulfurizer are communicated in sequence; the second desulfurizer is also communicated with a preset SCR denitration device so as to facilitate denitration of flue gas;
the first dust remover is communicated with the second dust remover through a fence baffle, and the first dust remover and the second dust remover are funnel-shaped dust removers;
the SCR denitration device comprises a catalyst injector for injecting a powder catalyst into the flue gas flowing channel; the passageway department still is provided with porous structure's speed reduction board, SCR denitrification facility still includes catalyst transport system, catalyst transport system includes: a fan; the rotary feeder is respectively connected with a catalyst source, the fan and the catalyst ejector, and transports powder catalyst in the catalyst source to the catalyst ejector under the action of the fan; the SCR denitration device also comprises a regulator used for regulating the amount of the powder catalyst sprayed into the flue by the catalyst injector;
the first desulfurizer is communicated with a smoke exhaust pipeline of the boiler, a plurality of slaked lime injection holes are formed in the position, which is spaced from the first desulfurizer by a first preset distance, of the smoke exhaust pipeline, and the slaked lime injection holes are used for introducing slaked lime into the smoke exhaust pipeline so that smoke can carry the slaked lime to enter the first desulfurizer; the bottom of the first desulfurizer is provided with a condensed water injection hole, and the condensed water injection hole is used for injecting condensed water into the first desulfurizer so as to enable the flue gas to be subjected to primary desulfurization in the first desulfurizer;
the bottom of the first dust remover is provided with a first gravity flap valve, the bottom of the second dust remover is provided with a second gravity flap valve, and the first gravity flap valve and the second gravity flap valve are both controlled by a master controller;
the first dust remover is communicated with the spraying agent preparation device, a first atomizer is arranged at the top of the first dust remover, and an outlet of the spraying agent preparation device is communicated with the first atomizer, so that the spraying agent is atomized by the first atomizer and then sprayed into the first dust remover;
the injection preparation device comprises a first liquid mixing port and a second liquid mixing port, the first liquid mixing port is communicated with an outlet of the first liquid mixing chamber through a first channel, the second liquid mixing port is communicated with an outlet of the second liquid mixing chamber through a second channel, a first control valve is arranged at the first channel, a second control valve is arranged at the second channel, and the first control valve and the second control valve are both controlled by the master controller;
the bottom of the spraying agent preparation device is provided with a pressure sensor which is communicated with the master controller, if the pressure sensor senses that the bottom pressure of the spraying agent preparation device is smaller than a preset value, the master controller starts a first control valve and a second control valve, and the flow ratio of the first control valve to the second control valve is 4: 3; the bottom of the spraying agent preparation device is also provided with a stirring mechanism;
the first mixed solution chamber comprises a solvent injection port, a first solute injection port and a second solute injection port, the solvent injection port is communicated with the water inlet pipeline through a first regulating valve, the first solute injection port is communicated with the first solute storage tank through a second regulating valve, and the second solute injection port is communicated with the second solute storage tank through a third regulating valve; the first solute storage tank stores a sodium dodecyl benzene sulfonate solution with the concentration of 0.15 weight percent, and the second solute storage tank stores a fatty alcohol-polyoxyethylene ether solution with the concentration of 0.08 weight percent; the first regulating valve, the second regulating valve and the third regulating valve are all controlled by a first branch controller, and the first branch controller is controlled by the master controller;
a first liquid level meter is arranged in the first liquid mixing chamber, if the liquid level in the first liquid mixing chamber is smaller than a preset liquid level low value, the first divider controller automatically opens the first regulating valve, the second regulating valve and the third regulating valve, and controls the first regulating valve, the second regulating valve and the third regulating valve to enable the flow rates of the solvent injection port, the first solute injection port and the second solute injection port to be 2:3: 2;
if the liquid level in the first liquid mixing chamber reaches a high liquid level value, closing the first regulating valve, the second regulating valve and the third regulating valve;
a spiral stirrer is arranged at the bottom of the first liquid mixing chamber and controlled by the first divider;
the second mixed liquid chamber comprises a first component injection inlet and a second component injection inlet, the first component injection inlet is communicated with a sodium chloride solution storage tank stored with the weight percentage of 1.5 through a fourth regulating valve, the second component injection inlet is communicated with a sodium sulfite solution storage tank stored with the weight percentage of 2 through a fifth regulating valve, the fourth regulating valve and the fifth regulating valve are controlled by a second sub-controller, and the second sub-controller is controlled by the master controller;
a second liquid level meter is arranged in the second liquid mixing chamber, if the liquid level in the second liquid mixing chamber is smaller than a preset liquid level lower limit, the second branch controller automatically opens the fourth regulating valve and the fifth regulating valve, and controls the fourth regulating valve and the fifth regulating valve to enable the flow rate of the first component injection inlet and the second component injection inlet to be 1: 2;
if the liquid level in the second liquid mixing chamber reaches the upper limit of the liquid level, closing a fourth regulating valve and a fifth regulating valve;
a rod-shaped stirrer is arranged at the bottom of the second liquid mixing chamber and controlled by the second divider; the rod stirrer is attached to a drive motor for rotationally driving the rod stirrer, the rod stirrer comprising a drive shaft having a distal end adapted to be coupled to a drive motor and a stirrer head; the beater further comprises coupling means for releasably coupling the beater head to the drive shaft, thereby coupling the beater head to the drive shaft at different relative positions along the drive shaft;
the atomized spraying agent fully contacts with the flue gas in the first dust remover after entering the first dust remover, so that the wrapped flue gas is settled and then falls to the bottom of the funnel-type first dust remover, and when the sediment at the bottom of the first dust remover reaches a certain amount, the first gravity flap valve is opened, and the sediment is discharged;
a plurality of first baffle plates which are vertically arranged are arranged in the second dust remover in the horizontal direction, a plurality of triangular second baffle plates are also arranged in the middle of the second dust remover along the smoke flowing direction, and under the action of the first baffle plates and the second baffle plates, the smoke flowing direction is changed and the flowing speed is reduced; a plurality of dedusting liquid nozzles are arranged in the second deduster in the horizontal direction, and the dedusting liquid nozzles and the first baffle are arranged in a staggered mode;
the dedusting liquid nozzles are communicated with a dedusting liquid storage tank through dedusting liquid connecting pipelines, and each communicated passage is provided with a control valve which is controlled by the master controller;
a mixture of sodium dodecyl sulfate and tung tree oil is stored in the dedusting liquid storage tank;
in the second dust remover, the specific flowing direction of the airflow is changed and the speed of the flue gas is reduced through the first baffle and the second baffle, so that the flue gas is fully contacted with the mixture of sodium dodecyl sulfate and tung tree seed oil, lipophilic particles in the flue gas are gathered to form larger particles, and the particles grow and deposit at the bottom of the second dust remover due to the lower speed of the airflow in the process; and when the sediment at the bottom of the second dust remover reaches a certain amount, the second gravity flap valve is opened, and the sediment is discharged.
2. The integrated equipment of claim 1, which is characterized in that:
a second atomizer is arranged at the upper part of the second desulfurizer, the second atomizer is communicated with a desulfurizer storage, the desulfurizer storage pumps a desulfurizer into the second atomizer through a quantitative feeding device and a solution pump, and the desulfurizer is atomized after passing through a bowl-shaped nozzle in the second atomizer;
the second desulfurizer is provided with a Venturi tube and a rotational flow plate behind the second atomizer along the airflow direction, and the flue gas and desulfurizer particles are fully mixed under the action of the Venturi tube and the rotational flow plate; the bottom of the second desulfurizer is also provided with a dehydrator so as to facilitate gas-liquid separation;
SO is also arranged near the second atomizer of the second desulfurizer2Concentration detector, said SO2The concentration detector is communicated with the master controller SO as to realize the injection of the desulfurizer and the SO2Linkage of concentration with SO2The spraying amount of the desulfurizer is automatically adjusted according to the change of the concentration.
3. The integrated equipment of claim 2, which is characterized in that:
the desulfurizer storage device is communicated with the desulfurizer preparation device, the desulfurizer preparation device comprises a first main material injection port, a second main material injection port and a third main material injection port, the first main material injection port is communicated with the acetaldehyde storage tank through a first sub-control valve, the second main material injection port is communicated with the aminomethane storage tank through a second sub-control valve, and the third main material injection port is communicated with the sodium tripolyphosphate storage tank through a third sub-control valve;
the bottom of the desulfurizer preparation device is also provided with a heater and a temperature sensor, the heater, the temperature sensor, the first sub-control valve, the second sub-control valve and the third sub-control valve are all controlled by a third sub-controller, and the third sub-controller is controlled by the master controller;
in the preparation process of the desulfurizer, the temperature of the bottom of the desulfurizer preparation device is controlled to be about 75 ℃, and the preparation time is not shorter than 2.5 hours;
the desulfurizer preparation device is also provided with an additive filling port, the additive filling port is used for manually adding an additive capable of improving the performance of the desulfurizer, and the additive is ethylene glycol;
the desulfurizer obtained by the desulfurizer preparation device can be used for desulfurization, and part of grease particles can be removed, so that the residue of the oily dedusting agent sprayed in the second deduster in flue gas is avoided.
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Citations (7)

* Cited by examiner, † Cited by third party
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WO1990007467A1 (en) * 1988-12-23 1990-07-12 Quaker Chemical Corporation Composition and method for sweetening hydrocarbons
CN1136944C (en) * 2001-01-08 2004-02-04 陈鸣楼 Bag type wet desulfurizing and dust collecting system
CN101053746B (en) * 2007-06-06 2010-06-09 北京大学 Method for ethylene glycol removing SOx (X=2 or 3) in flue gas
CN205586708U (en) * 2016-03-30 2016-09-21 陈聪 Double -deck atomizing desulfurization dust collector of circulated flue gas
CN206621980U (en) * 2017-03-28 2017-11-10 中国华电科工集团有限公司 A kind of coal steam-electric plant smoke sulfur dioxide, dust and waste water coprocessing system
CN206688518U (en) * 2017-03-03 2017-12-01 大唐环境产业集团股份有限公司 A kind of minimum discharge processing system of the multi-pollutant Collaborative Control of coal-fired flue-gas
CN207287094U (en) * 2017-09-19 2018-05-01 浙江工匠环境科技有限公司 A kind of dust removal integrated equipment of waste gas of industrial kiln and furnace desulphurization denitration

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1990007467A1 (en) * 1988-12-23 1990-07-12 Quaker Chemical Corporation Composition and method for sweetening hydrocarbons
CN1136944C (en) * 2001-01-08 2004-02-04 陈鸣楼 Bag type wet desulfurizing and dust collecting system
CN101053746B (en) * 2007-06-06 2010-06-09 北京大学 Method for ethylene glycol removing SOx (X=2 or 3) in flue gas
CN205586708U (en) * 2016-03-30 2016-09-21 陈聪 Double -deck atomizing desulfurization dust collector of circulated flue gas
CN206688518U (en) * 2017-03-03 2017-12-01 大唐环境产业集团股份有限公司 A kind of minimum discharge processing system of the multi-pollutant Collaborative Control of coal-fired flue-gas
CN206621980U (en) * 2017-03-28 2017-11-10 中国华电科工集团有限公司 A kind of coal steam-electric plant smoke sulfur dioxide, dust and waste water coprocessing system
CN207287094U (en) * 2017-09-19 2018-05-01 浙江工匠环境科技有限公司 A kind of dust removal integrated equipment of waste gas of industrial kiln and furnace desulphurization denitration

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