CN105935540A - Apparatus and method for removing and recovering sulfur dioxide in mixed gas - Google Patents

Apparatus and method for removing and recovering sulfur dioxide in mixed gas Download PDF

Info

Publication number
CN105935540A
CN105935540A CN201610383137.9A CN201610383137A CN105935540A CN 105935540 A CN105935540 A CN 105935540A CN 201610383137 A CN201610383137 A CN 201610383137A CN 105935540 A CN105935540 A CN 105935540A
Authority
CN
China
Prior art keywords
regenerator
tower
tail
absorbent
desulfurization
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.)
Pending
Application number
CN201610383137.9A
Other languages
Chinese (zh)
Inventor
夏碧波
戴如康
付文英
朱海峰
吴尤嘉
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
QUZHOU JUHUA POLYAMIDE FIBRE LLC
Original Assignee
QUZHOU JUHUA POLYAMIDE FIBRE LLC
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by QUZHOU JUHUA POLYAMIDE FIBRE LLC filed Critical QUZHOU JUHUA POLYAMIDE FIBRE LLC
Priority to CN201610383137.9A priority Critical patent/CN105935540A/en
Publication of CN105935540A publication Critical patent/CN105935540A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/14Separation 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 by absorption
    • B01D53/1406Multiple stage absorption
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/14Separation 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 by absorption
    • B01D53/1418Recovery of products
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/14Separation 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 by absorption
    • B01D53/1425Regeneration of liquid absorbents
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/14Separation 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 by absorption
    • B01D53/1456Removing acid components
    • B01D53/1481Removing sulfur dioxide or sulfur trioxide
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/14Separation 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 by absorption
    • B01D53/1493Selection of liquid materials for use as absorbents
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/14Separation 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 by absorption
    • B01D53/18Absorbing units; Liquid distributors therefor
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2252/00Absorbents, i.e. solvents and liquid materials for gas absorption
    • B01D2252/30Ionic liquids and zwitter-ions
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • B01D2258/0283Flue gases

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Gas Separation By Absorption (AREA)
  • Treating Waste Gases (AREA)

Abstract

The invention discloses an apparatus for removing and recovering sulfur dioxide in a mixed gas. The apparatus comprises a hypergravity desulphurization device, a tail gas absorption tower, an absorbent cycle storage tank, a lean solution tank, a heat exchanger, a regeneration tower, a circulating pump, a lean solution pump, a rich solution pump, a lean solution cooler, a regeneration tower cooler and a regeneration tower separator which are connected in a certain manner. The invention also discloses a method for removing and recovering sulfur dioxide in the mixed gas through using the apparatus. The apparatus and the method have the advantages of simple structure, high desulphurization efficiency, low production cost, high safety and environmental protection.

Description

A kind of for removing and reclaim the devices and methods therefor of sulfur dioxide in mixed gas
Technical field
The present invention relates to tail gas disposal technique field, be specifically related to a kind of for removing and reclaim sulfur dioxide in mixed gas Devices and methods therefor.
Background technology
2005, China's sulfur dioxide (SO2) emissions total amount was up to 25,490,000 tons, ranks first in the world, and sulfur dioxide (SO2) emissions cause Economic loss be about 500,000,000,000 yuan, its economic loss accounts for the 2.6% of GDP.Sulfur dioxide pollution has become restriction China's economy, the key factor of social sustainable development, control sulfur dioxide pollution imperative.
Flue gas desulfurization (FGD) is the desulfurization method of the most unique large-scale commercial application, is to control titanium dioxide The technical way of sulphur pollution.The main flue gas desulfurization technique of domestic application mainly has " the limestone-gypsum of external introduction Wet method ", " rotary spraying and drying method " and the domestic dust removal integrated technology of simple desulfurization.All there is improvement SO in these methods2 While pollution, the side-product of generation gets nowhere without market, can bring residue contamination, ammonia and nitrogen pollution, increase CO2 simultaneously The environmental issues such as discharge.
Wherein wet desulfurization of flue gas by limestone-gypsum method Technology is the prevailing technology technology of China, according to statistics, put into operation, In the flue gas desulphurization Technology built, Gypsum Wet technology accounts for more than 90%.This technology exists such as Lower two shortcomings: the value of (1) by-produced gypsum recycling is little, it has to abandon process, create new taking off Sulfur Gypsum Fibrosum pollutes.(2) often process one ton of sulfur dioxide and to discharge 0.7 ton of carbon dioxide, administer the titanium dioxide in flue gas Sulphur pollution, has increased again the discharge of greenhouse gases carbon dioxide newly.
In recent years, along with the development of high-gravity technology, high gravity desulfurization equipment such as cross_flow rotating packed bed, hypergravity machine It is widely used Deng in flue gas desulfurization.High gravity desulfurization equipment utilizes gas-liquid strengthening mass transfer contact to realize, It is that the multiple dust removal mechanisms such as centrifugal sedimentation, filtration, machinery rotary collision, inertial collision capture and diffusion, moisture film are combined in The separation of flow cleaner of one.High gravity desulfurization equipment greatly reduce can desulphurization plant dimension and weight, the most by force Change mass transfer, diabatic process, improve desulfuration efficiency.
Such as China Patent Publication No. CN 102049176 A, denomination of invention: adopting high-gravity solvent cycle absorption method flue gas desulfurization Technological process.This invention by cross_flow rotating packed bed at the flue gas desulfurization course of the desulfurization solvent such as ionic liquid, organic amine And the application in desulfurization solvent regenerative process, and the gas such as nitrogen, air is used to participate in desulfurization solvent as gas stripping gas The desorbing of SO 2 and the regeneration of desulfurization solvent, and combine the filtration, purification of desulfurization solvent, adsorption cleaning and desalination purification skill Art, defines adopting high-gravity solvent cycle absorption method flue gas desulfurization technique.Weak point is that technological process is long, and operation is many, behaviour Make loaded down with trivial details, operating cost is high, and produces a large amount of waste water and mud in running, not environmentally.
Summary of the invention
The present invention is directed to the deficiency that prior art exists, it is provided that a kind of technique is simple, desulfuration efficiency is high, production cost is low, Safety and environmental protection for removing and reclaim the devices and methods therefor of sulfur dioxide in mixed gas.
For achieving the above object, the technical solution used in the present invention is: one is used for removing and reclaim dioxy in mixed gas Change the device of sulfur, inhale tower, absorbent circulating storage groove, lean flow container, heat exchanger, again including high gravity desulfurization device, tail Raw tower, circulating pump, lean pump, rich solution pump, lean solution cooler, regenerator cooler and regenerator separator, described The gas phase import that the gaseous phase outlet of high gravity desulfurization device inhales tower with described tail is connected, and described high gravity desulfurization device leads to Crossing described rich solution pump to be connected with the rich solution import of described heat exchanger, the rich solution of described heat exchanger exports with described The rich solution import of regenerator be connected, the top gaseous phase of described regenerator exports by described regenerator cooler and institute The import of the regenerator separator stated connects, the liquid-phase outlet of described regenerator separator and the coolant of described regenerator Import connects, and the tower bottoms outlet of described regenerator is connected with the lean solution import of described heat exchanger, described heat friendship The lean solution outlet of parallel operation is sequentially connected with described lean flow container and described lean pump by described lean solution cooler, described Lean solution delivery side of pump respectively with the absorbent entrance of described absorbent circulating storage groove, described tail inhale tower absorbent enter Mouth connects, and described tail is inhaled the tower bottoms outlet of tower and is connected with the rich solution import of described absorbent circulating storage groove, described The outlet of absorbent circulating storage groove is connected with described high gravity desulfurization device absorbent entrance by described circulating pump.
Described high gravity desulfurization device is preferably hypergravity machine.
The present invention also provides for using said apparatus removing and reclaiming the method for sulfur dioxide in mixed gas, including walking as follows Rapid:
A () sulfur-bearing gaseous mixture enters high gravity desulfurization device, be fully contacted with absorbent, the SO in gas2With absorption Agent reaction is absorbed, and obtains desulfurization and absorbs rich solution and the tail gas after partial desulfurization, desulfurization absorb rich solution through rich solution pump, Heat exchanger, to regenerator, adds Thermal desorption at regenerator through stripped vapor, obtains regenerative mixed gas and regenerator tower reactor Liquid, regenerative mixed gas obtains SO through regenerator cooler, regenerator separator cooled dehydrated2Product;
The b tail gas after partial desulfurization that () step (a) obtains enters tail and inhales tower, enters with from tower top in tail inhales tower The absorbent counter current contacting entered, absorbs the SO in tail gas further2, obtain desulfurization and absorb lean solution and purify gas, will purify Gas inhales tower top qualified discharge from tail.
Described sulfur-bearing mixture temperature is preferably 40~60 DEG C.
Described absorbent can be selected for the one in guanidine, imidazoles, pyridines and alcamines plasma liquid-absorbant or Several, preferably 1,1,3,3-tetramethyl guanidine lactate, ethanolamine and acetate mixture, diethanolamine and lactic mixt In one.
Described tail is inhaled tower temperature and is preferably controlled to 30~50 DEG C, and the tail gas after partial desulfurization is preferred with the mass ratio of absorbent For 1:1~3.
Described high gravity desulfurization unit temp is preferably controlled to 30~70 DEG C.
Described regenerator temperature is preferably controlled to 100~130 DEG C, and pressure is preferably controlled to 30~70KPa.
Described lean solution chiller temperature is preferably controlled to 20~40 DEG C, and described regenerator chiller temperature is preferably controlled to 20~40 DEG C.
As the preferred embodiment of the present invention, regenerator tower bottoms tentatively can be lowered the temperature through heat exchanger, then through lean solution Cooler enters in lean solution tank after lowering the temperature further, then pressurizes through lean pump, returns to tail and inhales tower absorbent entrance, successively Cyclic absorption.Regenerator tower bottoms is not up to saturated solution state, returns it to tail and inhales tower continuation absorption SO2, permissible Make absorbent recycle, reduce production cost, and reduce three waste discharge.
As the preferred embodiment of the present invention, desulfurization can be absorbed lean solution and return to surpass through absorbent circulating storage groove, circulating pump Gravity desulfurizer, successively cyclic absorption.The desulfurization absorption lean solution obtained from tail suction tower is not up to saturated solution state, will It returns to high gravity desulfurization device and continues to absorb SO2, on the one hand absorbent can be made to recycle, reduce production cost; On the other hand double absorption can make continuation absorb SO2After solution reach saturated, and then in subsequent regeneration tower reclaim height The SO of concentration2Time, improve organic efficiency.
The present invention uses high gravity desulfurization device to carry out desulfurization, under Elevated Gravity, and the intermolecular diffusion of different size and phase Between mass transport process all than conventional articulated gravity more much faster, it is possible to realize good gas-to-liquid contact and microcosmic mixing, reach SO2Deep removal.
Absorbent in the present invention is to SO2Gas has good absorption and desorption ability, absorbs titanium dioxide at low temperatures Sulfur, regenerates out by sulfur dioxide in absorbent under high temperature, thus reaches SO in removing and recovered flue gas2Purpose.This Absorbent in invention can recycle, and reduce further production cost.
The present invention is used for removing and reclaim sulfur dioxide in mixed gas, is possible not only to reach SO2Deep removal, and The SO of recyclable high concentration2Gas, has good Social and economic benef@.
Compared with prior art, the invention have the advantages that
1, simple in construction, desulfuration efficiency height, when the present invention is used for removing and reclaiming sulfur dioxide in mixed gas, produce Stable and reliable operation, operating condition is gentle, it is achieved that SO2Deep removal;
2, production cost is low, good in economic efficiency, when the present invention is used for removing and reclaiming sulfur dioxide in mixed gas, no Only fume treatment cost is relatively low, SO2Removal efficiency is high, and can reclaim purity SO more than 99.5%2, and inhale Receiving agent can recycle, reduce further production cost, economic and social benefit is notable;
3, the three wastes are few, safety and environmental protection, and the present invention is in efficient removal SO2, reclaim the SO of high concentration2While, without extra Side-product produce, absorbent can recycle, and three waste discharge is few, environmental friendliness, meets the development of environmental protection Requirement.
Accompanying drawing explanation
Fig. 1 is the process chart of the present invention.
In figure: high gravity desulfurization device 1, tail inhale tower 2, absorbent circulating storage groove 3, lean flow container 4, heat exchanger 5, Regenerator 6, circulating pump 7, lean pump 8, rich solution pump 9, lean solution cooler 10, regenerator cooler 11, regenerator Separator 12
Detailed description of the invention
By the following examples the present invention is explained in further detail, but the invention is not limited in this.Any with this Based on invention, for realizing essentially identical technique effect, done simple change, equivalent or modification etc., All contain within protection scope of the present invention.
As it is shown in figure 1, the present invention for removing and reclaim the device of sulfur dioxide in mixed gas, take off including hypergravity Sulfur device 1, tail inhale tower 2, absorbent circulating storage groove 3, lean flow container 4, heat exchanger 5, regenerator 6, circulating pump 7, Lean pump 8, rich solution pump 9, lean solution cooler 10, regenerator cooler 11 and regenerator separator 12, hypergravity takes off The gas phase import that the gaseous phase outlet of sulfur device 1 inhales tower 2 with tail is connected, and high gravity desulfurization device 1 is by rich solution pump 9 and warm The rich solution import of exchanger 5 connects, and the rich solution outlet of heat exchanger 5 is connected with the rich solution import of regenerator 6, regenerator The top gaseous phase outlet of 6 is connected by the import of regenerator cooler 11 with regenerator separator 12, regenerator separator The liquid-phase outlet of 12 is connected with the cooling liquid inlet of regenerator 6, and the tower bottoms outlet of regenerator 6 is lean with heat exchanger 5 Liquid import is connected, and the lean solution outlet of heat exchanger 5 is connected with lean flow container 4 and lean pump 8 successively by lean solution cooler 10 Connecing, the outlet of lean pump 8 inhales the absorbent entrance of tower 2 even with the absorbent entrance of absorbent circulating storage groove 3, tail respectively Connecing, tail is inhaled the tower bottoms outlet of tower 2 and is connected with the rich solution import of absorbent circulating storage groove 3, absorbent circulating storage groove 3 Outlet is connected with high gravity desulfurization device 1 absorbent entrance by circulating pump 7.
When using said apparatus removing and reclaim sulfur dioxide in mixed gas, technological process is: driving forward direction lean solution Tank 4 adds absorbent, squeezes into high gravity desulfurization device 1 respectively by lean pump 8 and tail inhales tower 2, at device Running is periodically added absorbent.Sulfur-bearing gaseous mixture enters high gravity desulfurization device 1, fully connects with absorbent Touch, the SO in gas2React with absorbent and absorbed, obtain desulfurization and absorb rich solution and the tail gas after partial desulfurization, Desulfurization absorption rich solution, through rich solution pump 9, heat exchanger 5 to regenerator 6, adds Thermal desorption at regenerator 6 through stripped vapor, Obtaining regenerative mixed gas and regenerator tower bottoms, regenerative mixed gas is through regenerator cooler 11, regenerator separator 12 SO is obtained by regenerator separator 12 gaseous phase outlet after cooling, dehydration2Product.Regenerator tower bottoms is through heat exchange Device 5 is tentatively lowered the temperature, then enters after lean solution cooler 10 is lowered the temperature further in lean solution tank 4, then through lean pump 8 Pressurization, returns to tail and inhales tower 2 absorbent entrance, cyclic absorption successively.Tail gas after partial desulfurization enters tail and inhales tower 2, with the absorbent counter current contacting entered from tower top in tail inhales tower 2, absorb the SO in tail gas further2, Absorb lean solution to desulfurization and purify gas, purification gas is inhaled tower top qualified discharge from tail.Desulfurization is absorbed lean solution through absorbing Agent circulating storage groove 3, circulating pump 7 return to high gravity desulfurization device 1, successively cyclic absorption.
Embodiment 1
Sulfur-bearing mixed gas flow is 120000Nm3/ h, temperature is 50 DEG C, SO2Content is 5%.Sulfur-bearing gaseous mixture enters Enter hypergravity machine 1 (Zhong Chao Machinery Co., Ltd. of Huludao City, Φ 2000*2500), form with diethanolamine and lactic acid Absorbent be fully contacted, the SO in gas2React with absorbent and absorbed, obtain desulfurization and absorb rich solution and through portion Dividing the tail gas after desulfurization, hypergravity machine 1 operates temperature and controls to be 70 DEG C, and desulfurization absorbing liquid is handed over through rich solution pump 9, heat Parallel operation 5 to regenerator 6, adds Thermal desorption at regenerator 6 through stripped vapor, obtains regenerative mixed gas and regenerator tower Still liquid, regenerator operating condition is: temperature 120 DEG C, pressure 50KPa, regenerative mixed gas is through regenerator cooler 11, regenerator separator 12 cooled dehydrated obtains SO2Product, it is 20 DEG C that regenerator cooler 11 temperature controls. Regenerator tower bottoms is tentatively lowered the temperature through heat exchanger 5, then enters lean solution tank after lean solution cooler 10 is lowered the temperature further In 4, then pressurizeing through lean pump 8, return to tail and inhale tower 2 absorbent entrance, cyclic absorption successively, lean solution cools down It is 30 DEG C that device 10 temperature controls.Tail gas after partial desulfurization enters tail and inhales tower 2, in tail inhales tower 2 and from tower The absorbent counter current contacting that portion enters, absorbs the SO in tail gas further2, obtain desulfurization and absorb lean solution and purify gas, Tail is inhaled tower temperature and is controlled to be 30 DEG C, and the tail gas after partial desulfurization is 1:1 with the mass ratio of absorbent.By purification gas from Tail inhales tower top qualified discharge, inhales top gaseous phase pipe sample analysis from tail, is not detected by SO2.Desulfurization is absorbed lean solution Hypergravity machine 1, successively cyclic absorption is returned to through absorbent circulating storage groove 3, circulating pump 7.
From regenerator separator 12 gaseous phase outlet sample analysis, SO2Gas purity 99.5%.
Embodiment 2
Sulfur-bearing mixed gas flow is 130000Nm3/ h, temperature is 60 DEG C, SO2Content is 4%.Sulfur-bearing gaseous mixture enters Enter hypergravity machine 1 (Zhong Chao Machinery Co., Ltd. of Huludao City, Φ 2500*2500), with absorbent 1,1,3,3-tetramethyl Guanidine lactate is fully contacted, the SO in gas2React with absorbent and absorbed, obtain desulfurization and absorb rich solution and through portion Dividing the tail gas after desulfurization, hypergravity machine 1 operates temperature and controls to be 55 DEG C, and desulfurization absorbing liquid is handed over through rich solution pump 9, heat Parallel operation 5 to regenerator 6, adds Thermal desorption at regenerator 6 through stripped vapor, obtains regenerative mixed gas and regenerator tower Still liquid, regenerator operating condition is: temperature 130 DEG C, pressure 70KPa, regenerative mixed gas is through regenerator cooler 11, regenerator separator 12 cooled dehydrated obtains SO2Product, it is 40 DEG C that regenerator cooler 11 temperature controls. Regenerator tower bottoms is tentatively lowered the temperature through heat exchanger 5, then enters lean solution tank after lean solution cooler 10 is lowered the temperature further In 4, then pressurizeing through lean pump 8, return to tail and inhale tower 2 absorbent entrance, cyclic absorption successively, lean solution cools down It is 20 DEG C that device 10 temperature controls.Tail gas after partial desulfurization enters tail and inhales tower 2, in tail inhales tower 2 and from tower The absorbent counter current contacting that portion enters, absorbs the SO in tail gas further2, obtain desulfurization and absorb lean solution and purify gas, Tail is inhaled tower temperature and is controlled to be 35 DEG C, and the tail gas after partial desulfurization is 1:1.5 with the mass ratio of absorbent, will purify gas Inhale tower top qualified discharge from tail, inhale top gaseous phase pipe sample analysis from tail, be not detected by SO2.Desulfurization is absorbed lean Liquid returns to hypergravity machine 1, successively cyclic absorption through absorbent circulating storage groove 3, circulating pump 7.
From regenerator separator 12 gaseous phase outlet sample analysis, SO2Gas purity 99.6%.
Embodiment 3
Sulfur-bearing mixed gas flow is 100000Nm3/ h, temperature is 45 DEG C, SO2Content is 8%.Sulfur-bearing gaseous mixture enters Enter hypergravity machine 1 (Zhong Chao Machinery Co., Ltd. of Huludao City, Φ 2000*2000), form with ethanolamine and acetic acid Absorbent is fully contacted, the SO in gas2React with absorbent and absorbed, obtain desulfurization and absorb rich solution and through part Tail gas after desulfurization, hypergravity machine 1 operates temperature and controls to be 40 DEG C, and desulfurization absorbing liquid is through rich solution pump 9, heat exchange Device 5 to regenerator 6, adds Thermal desorption at regenerator 6 through stripped vapor, obtains regenerative mixed gas and regenerator tower reactor Liquid, regenerator operating condition is: temperature 110 DEG C, pressure 40KPa, regenerative mixed gas through regenerator cooler 11, Regenerator separator 12 cooled dehydrated obtains SO2Product, it is 30 DEG C that regenerator cooler 11 temperature controls.Regeneration Tower tower bottoms is tentatively lowered the temperature through heat exchanger 5, then enters lean solution tank 4 after lean solution cooler 10 is lowered the temperature further In, then pressurize through lean pump 8, return to tail and inhale tower 2 absorbent entrance, cyclic absorption successively, lean solution cooler It is 40 DEG C that 10 temperature control.Tail gas after partial desulfurization enters tail and inhales tower 2, in tail inhales tower 2 and from tower top The absorbent counter current contacting entered, absorbs the SO in tail gas further2, obtain desulfurization and absorb lean solution and purify gas, Tail is inhaled tower temperature and is controlled to be 40 DEG C, and the mass ratio of the tail gas after partial desulfurization and absorbent is 1:2, by purification gas from Tail inhales tower top qualified discharge, inhales top gaseous phase pipe sample analysis from tail, is not detected by SO2.Desulfurization is absorbed lean solution Hypergravity machine 1, successively cyclic absorption is returned to through absorbent circulating storage groove 3, circulating pump 7.
From regenerator separator 12 gaseous phase outlet sample analysis, SO2Gas purity 99.7%.
Embodiment 4
Sulfur-bearing mixed gas flow is 110000Nm3/ h, temperature is 55 DEG C, SO2Content is 7%.Sulfur-bearing gaseous mixture enters Enter hypergravity machine 1 (Zhong Chao Machinery Co., Ltd. of Huludao City, Φ 2000*2500), with absorbent 1,1,3,3-tetramethyl Guanidine lactate is fully contacted, the SO in gas2React with absorbent and absorbed, obtain desulfurization and absorb rich solution and through portion Dividing the tail gas after desulfurization, hypergravity machine 1 operates temperature and controls to be 30 DEG C, and desulfurization absorbing liquid is handed over through rich solution pump 9, heat Parallel operation 5 to regenerator 6, adds Thermal desorption at regenerator 6 through stripped vapor, obtains regenerative mixed gas and regenerator tower Still liquid, regenerator operating condition is: temperature 100 DEG C, pressure 30KPa, regenerative mixed gas is through regenerator cooler 11, regenerator separator 12 cooled dehydrated obtains SO2Product, it is 35 DEG C that regenerator cooler 11 temperature controls. Regenerator tower bottoms is tentatively lowered the temperature through heat exchanger 5, then enters lean solution tank after lean solution cooler 10 is lowered the temperature further In 4, then pressurizeing through lean pump 8, return to tail and inhale tower 2 absorbent entrance, cyclic absorption successively, lean solution cools down It is 35 DEG C that device 10 temperature controls.Tail gas after partial desulfurization enters tail and inhales tower 2, in tail inhales tower 2 and from tower The absorbent counter current contacting that portion enters, absorbs the SO in tail gas further2, obtain desulfurization and absorb lean solution and purify gas, Tail is inhaled tower temperature and is controlled to be 50 DEG C, and the mass ratio of the tail gas after partial desulfurization and absorbent is 1:3, by purification gas from Tail inhales tower top qualified discharge, inhales top gaseous phase pipe sample analysis from tail, is not detected by SO2.Desulfurization can be absorbed lean Liquid returns to hypergravity machine 1, successively cyclic absorption through absorbent circulating storage groove 3, circulating pump 7.
From regenerator separator 12 gaseous phase outlet sample analysis, SO2Gas purity 99.8%.

Claims (10)

1., for removing and reclaim a device for sulfur dioxide in mixed gas, inhale including high gravity desulfurization device, tail Tower, absorbent circulating storage groove, lean flow container, heat exchanger, regenerator, circulating pump, lean pump, rich solution pump, lean solution are cold But device, regenerator cooler and regenerator separator, it is characterised in that the gaseous phase outlet of described high gravity desulfurization device with Described tail is inhaled the gas phase import of tower and is connected, and described high gravity desulfurization device is by described rich solution pump and described heat friendship The rich solution import of parallel operation connects, and the rich solution outlet of described heat exchanger is connected with the rich solution import of described regenerator, institute The top gaseous phase outlet of the regenerator stated is connected by the import of described regenerator cooler with described regenerator separator Connecing, the liquid-phase outlet of described regenerator separator is connected with the cooling liquid inlet of described regenerator, described regenerator Tower bottoms outlet is connected with the lean solution import of described heat exchanger, and the lean solution of described heat exchanger exports by described Lean solution cooler is sequentially connected with described lean flow container and described lean pump, and described lean solution delivery side of pump is respectively with described The absorbent entrance of absorbent circulating storage groove, described tail inhale the absorbent entrance of tower and connect, described tail inhales the tower of tower The outlet of still liquid is connected with the rich solution import of described absorbent circulating storage groove, and the outlet of described absorbent circulating storage groove is passed through Described circulating pump is connected with described high gravity desulfurization device absorbent entrance.
The most according to claim 1 for removing and reclaim the device of sulfur dioxide in mixed gas, its feature exists It is hypergravity machine in described high gravity desulfurization device.
3. using the device removing described in claim 1 and reclaim the method for sulfur dioxide in mixed gas, its feature exists In comprising the steps:
A () sulfur-bearing gaseous mixture enters high gravity desulfurization device, be fully contacted with absorbent, the SO in gas2Anti-with absorbent Should be absorbed, obtain desulfurization and absorb rich solution and the tail gas after partial desulfurization, desulfurization absorbs rich solution and hands over through rich solution pump, heat Parallel operation, to regenerator, adds Thermal desorption at regenerator through stripped vapor, obtains regenerative mixed gas and regenerator tower bottoms, then Raw gaseous mixture obtains SO through regenerator cooler, regenerator separator cooled dehydrated2Product;
The b tail gas after partial desulfurization that () step (a) obtains enters tail and inhales tower, enters with from tower top in tail inhales tower Absorbent counter current contacting, absorb further the SO in tail gas2, obtain desulfurization and absorb lean solution and purify gas, gas will be purified Tower top qualified discharge is inhaled from tail.
The method of sulfur dioxide in removing the most according to claim 3 and recovery mixed gas, it is characterised in that institute The sulfur-bearing mixture temperature stated is 40~60 DEG C.
The method of sulfur dioxide in removing the most according to claim 3 and recovery mixed gas, it is characterised in that institute The absorbent stated is 1,1,3,3-tetramethyl guanidine lactate, ethanolamine and acetate mixture, diethanolamine and lactic mixt In one.
The method of sulfur dioxide in removing the most according to claim 3 and recovery mixed gas, it is characterised in that institute The tail stated is inhaled tower temperature and is controlled to be 30~50 DEG C, and the tail gas after partial desulfurization is 1:1~3 with the mass ratio of absorbent.
The method of sulfur dioxide in removing the most according to claim 3 and recovery mixed gas, it is characterised in that institute It is 30~70 DEG C that the high gravity desulfurization unit temp stated controls.
The method of sulfur dioxide in removing the most according to claim 3 and recovery mixed gas, it is characterised in that institute It is 100~130 DEG C that the regenerator temperature stated controls, and Stress control is 30~70KP, described lean solution chiller temperature control Being made as 20~40 DEG C, it is 20~40 DEG C that described regenerator chiller temperature controls.
The method of sulfur dioxide in removing the most according to claim 3 and recovery mixed gas, it is characterised in that will Regenerator tower bottoms is tentatively lowered the temperature through heat exchanger, then enters after lean solution cooler is lowered the temperature further in lean solution tank, then Pressurize through lean pump, return to tail and inhale tower absorbent entrance, cyclic absorption successively.
The method of sulfur dioxide in removing the most according to claim 3 and recovery mixed gas, it is characterised in that will Desulfurization absorbs lean solution and returns to high gravity desulfurization device, successively cyclic absorption through absorbent circulating storage groove, circulating pump.
CN201610383137.9A 2016-05-31 2016-05-31 Apparatus and method for removing and recovering sulfur dioxide in mixed gas Pending CN105935540A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610383137.9A CN105935540A (en) 2016-05-31 2016-05-31 Apparatus and method for removing and recovering sulfur dioxide in mixed gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610383137.9A CN105935540A (en) 2016-05-31 2016-05-31 Apparatus and method for removing and recovering sulfur dioxide in mixed gas

Publications (1)

Publication Number Publication Date
CN105935540A true CN105935540A (en) 2016-09-14

Family

ID=57151649

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610383137.9A Pending CN105935540A (en) 2016-05-31 2016-05-31 Apparatus and method for removing and recovering sulfur dioxide in mixed gas

Country Status (1)

Country Link
CN (1) CN105935540A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109621684A (en) * 2019-01-17 2019-04-16 北京化工大学 A kind of device and method that alkylation spent acid recycles

Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101837237A (en) * 2009-12-29 2010-09-22 中国恩菲工程技术有限公司 Flue gas desulphurization system
CN102019137A (en) * 2010-12-01 2011-04-20 中北大学 Method and device for removing low-concentration sulfur dioxide in flue gas
CN102049176A (en) * 2009-11-06 2011-05-11 成都华西工业气体有限公司 Flue gas desulfurization process adopting high-gravity solvent cycle absorption method
CN102658000A (en) * 2012-05-03 2012-09-12 中国药科大学 Method and absorption solvent for removing sulfur dioxide from flue gas
CN103301716A (en) * 2013-06-30 2013-09-18 金川集团股份有限公司 Irregular exhaustion flue gas treatment system and method in metal sulphide ore smelting
CN103463936A (en) * 2013-09-07 2013-12-25 中北大学 Device and method for removing sulfur dioxide contained in waste gas
CN103480259A (en) * 2013-09-07 2014-01-01 中北大学 Flue gas desulfurization device and process
CN104368232A (en) * 2014-10-22 2015-02-25 陕西华陆化工环保有限公司 Sulfuric acid tail gas recovery device
US9216377B1 (en) * 2015-02-24 2015-12-22 Chevron U.S.A. Inc. Method and system for removing impurities from gas streams using rotating packed beds
CN205760479U (en) * 2016-05-31 2016-12-07 衢州巨化锦纶有限责任公司 A kind of for removing and reclaim the device of sulfur dioxide in mixed gas

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102049176A (en) * 2009-11-06 2011-05-11 成都华西工业气体有限公司 Flue gas desulfurization process adopting high-gravity solvent cycle absorption method
CN101837237A (en) * 2009-12-29 2010-09-22 中国恩菲工程技术有限公司 Flue gas desulphurization system
CN102019137A (en) * 2010-12-01 2011-04-20 中北大学 Method and device for removing low-concentration sulfur dioxide in flue gas
CN102658000A (en) * 2012-05-03 2012-09-12 中国药科大学 Method and absorption solvent for removing sulfur dioxide from flue gas
CN103301716A (en) * 2013-06-30 2013-09-18 金川集团股份有限公司 Irregular exhaustion flue gas treatment system and method in metal sulphide ore smelting
CN103463936A (en) * 2013-09-07 2013-12-25 中北大学 Device and method for removing sulfur dioxide contained in waste gas
CN103480259A (en) * 2013-09-07 2014-01-01 中北大学 Flue gas desulfurization device and process
CN104368232A (en) * 2014-10-22 2015-02-25 陕西华陆化工环保有限公司 Sulfuric acid tail gas recovery device
US9216377B1 (en) * 2015-02-24 2015-12-22 Chevron U.S.A. Inc. Method and system for removing impurities from gas streams using rotating packed beds
CN205760479U (en) * 2016-05-31 2016-12-07 衢州巨化锦纶有限责任公司 A kind of for removing and reclaim the device of sulfur dioxide in mixed gas

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109621684A (en) * 2019-01-17 2019-04-16 北京化工大学 A kind of device and method that alkylation spent acid recycles

Similar Documents

Publication Publication Date Title
CN102218261B (en) Method and equipment for collecting carbon dioxide from fuel gas by using ammonia water fine spraying
JP5945333B2 (en) Carbon dioxide recovery method and apparatus for power plant flue gas
CA2742533C (en) Reabsorber for ammonia stripper offgas
CN103203174B (en) SO in a kind of trapping coal-fired plant flue gas 2and CO 2and the method for production chemical product
CN102985161B (en) The separation equipment and process thereof of producing gases at high pressure is purged by gas pressurized
CN201244430Y (en) Apparatus for collecting carbonic anhydride in coal-fired plant flue gas
CN102500195B (en) Two-phase carbon dioxide collecting device
WO2012051879A1 (en) Method and apparatus for capturing carbon dioxide in flue gas with activated sodium carbonate
CN109126392B (en) Method for carrying out CO (carbon monoxide) in flue gas by adopting ionic liquid2Trapping device and process
CN102872680B (en) Flue gas desulphurization system and fume desulphurization method
CN101716458A (en) System for trapping carbon dioxide in flue gas of coal-fired power plant and corresponding treatment method
CN101177267B (en) Method for preparing food-grade carbon-dioxide by using power station smoke gas and system thereof
JPS63501549A (en) Ammonia treatment method and equipment
CN101314102A (en) Method and apparatus for collecting carbonic anhydride in coal-fired plant flue gas
CN1887405A (en) Process of removing and recovering CO2 from fume
AU2011205517A1 (en) Water wash method and system for a carbon dioxide capture process
CN112387071A (en) CO2Trapping method and apparatus
CN103143249B (en) Method and device for capturing carbon dioxide in flue gas of power station boiler
CN101874967A (en) Process for removing acid gas with low-temperature methanol solution
CN104066494B (en) Ammonia is trapped in aqueous wash liquid by carbon dioxide product liquid
CN212166984U (en) CO2Trapping system
CN108977236A (en) A kind of providing method of rectisol system and synthesis gas
CN201138116Y (en) System for preparing food-grade carbon-dioxide by using power station smoke gas
KR20130047470A (en) Improved method for capturing carbon dioxide using aqueous ammonia and apparatus implementing the same
CN1872679A (en) Method for preparing liquid carbon dioxide in foodstuff level by using tail gas of cement kiln

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20160914

RJ01 Rejection of invention patent application after publication