CN203971736U - A kind of smoke carbon dioxide capture system - Google Patents
A kind of smoke carbon dioxide capture system Download PDFInfo
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- CN203971736U CN203971736U CN201420436545.2U CN201420436545U CN203971736U CN 203971736 U CN203971736 U CN 203971736U CN 201420436545 U CN201420436545 U CN 201420436545U CN 203971736 U CN203971736 U CN 203971736U
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- ammonia
- carbon dioxide
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- absorption tower
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- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 title claims abstract description 268
- 229910002092 carbon dioxide Inorganic materials 0.000 title claims abstract description 131
- 239000001569 carbon dioxide Substances 0.000 title claims abstract description 130
- 239000000779 smoke Substances 0.000 title claims abstract description 25
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims abstract description 386
- 229910021529 ammonia Inorganic materials 0.000 claims abstract description 193
- 238000010521 absorption reaction Methods 0.000 claims abstract description 92
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims abstract description 63
- 239000003546 flue gas Substances 0.000 claims abstract description 63
- 238000005261 decarburization Methods 0.000 claims abstract description 54
- 235000011114 ammonium hydroxide Nutrition 0.000 claims abstract description 32
- 230000005532 trapping Effects 0.000 claims abstract description 32
- 230000002745 absorbent Effects 0.000 claims abstract description 30
- 239000002250 absorbent Substances 0.000 claims abstract description 30
- 238000002360 preparation method Methods 0.000 claims abstract description 23
- 229910052799 carbon Inorganic materials 0.000 claims abstract description 22
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 21
- 230000008929 regeneration Effects 0.000 claims abstract description 17
- 238000011069 regeneration method Methods 0.000 claims abstract description 17
- 239000002918 waste heat Substances 0.000 claims abstract description 9
- 239000007789 gas Substances 0.000 claims description 77
- 238000011084 recovery Methods 0.000 claims description 67
- 239000007788 liquid Substances 0.000 claims description 65
- 238000005507 spraying Methods 0.000 claims description 22
- 238000013459 approach Methods 0.000 claims description 19
- 239000003517 fume Substances 0.000 claims description 19
- 230000008676 import Effects 0.000 claims description 18
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 16
- 239000003795 chemical substances by application Substances 0.000 claims description 15
- 239000007921 spray Substances 0.000 claims description 9
- 238000009826 distribution Methods 0.000 claims description 8
- 238000012856 packing Methods 0.000 claims description 7
- 150000001875 compounds Chemical class 0.000 claims description 3
- 239000002737 fuel gas Substances 0.000 claims description 3
- 238000000034 method Methods 0.000 abstract description 12
- 238000005265 energy consumption Methods 0.000 abstract description 9
- 238000010438 heat treatment Methods 0.000 abstract description 5
- 230000008569 process Effects 0.000 abstract description 5
- 238000004064 recycling Methods 0.000 abstract description 4
- 239000012141 concentrate Substances 0.000 abstract 1
- 230000001172 regenerating effect Effects 0.000 abstract 1
- 229960004424 carbon dioxide Drugs 0.000 description 108
- 238000005516 engineering process Methods 0.000 description 12
- 238000005406 washing Methods 0.000 description 9
- 235000011089 carbon dioxide Nutrition 0.000 description 7
- HZAXFHJVJLSVMW-UHFFFAOYSA-N 2-Aminoethan-1-ol Chemical compound NCCO HZAXFHJVJLSVMW-UHFFFAOYSA-N 0.000 description 6
- 238000007906 compression Methods 0.000 description 6
- 230000006835 compression Effects 0.000 description 6
- 238000009833 condensation Methods 0.000 description 6
- 230000005494 condensation Effects 0.000 description 6
- 230000007797 corrosion Effects 0.000 description 5
- 238000005260 corrosion Methods 0.000 description 5
- 238000001816 cooling Methods 0.000 description 4
- 238000011161 development Methods 0.000 description 4
- 230000018109 developmental process Effects 0.000 description 4
- 239000012530 fluid Substances 0.000 description 4
- 238000012545 processing Methods 0.000 description 4
- 230000008859 change Effects 0.000 description 3
- 238000006243 chemical reaction Methods 0.000 description 3
- 239000002994 raw material Substances 0.000 description 3
- 238000000926 separation method Methods 0.000 description 3
- 239000002904 solvent Substances 0.000 description 3
- 239000002699 waste material Substances 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 230000002411 adverse Effects 0.000 description 2
- 238000007599 discharging Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 238000003860 storage Methods 0.000 description 2
- 238000010792 warming Methods 0.000 description 2
- 230000002159 abnormal effect Effects 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 238000005049 combustion synthesis Methods 0.000 description 1
- 230000009615 deamination Effects 0.000 description 1
- 238000006481 deamination reaction Methods 0.000 description 1
- 230000018044 dehydration Effects 0.000 description 1
- 238000006297 dehydration reaction Methods 0.000 description 1
- 238000006477 desulfuration reaction Methods 0.000 description 1
- 230000023556 desulfurization Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000000284 extract Substances 0.000 description 1
- 239000000945 filler Substances 0.000 description 1
- 239000002803 fossil fuel Substances 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 238000007429 general method Methods 0.000 description 1
- 239000005431 greenhouse gas Substances 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 239000006210 lotion Substances 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 238000012544 monitoring process Methods 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 238000010525 oxidative degradation reaction Methods 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 238000010926 purge Methods 0.000 description 1
- 238000000197 pyrolysis Methods 0.000 description 1
- 230000036632 reaction speed Effects 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02C—CAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
- Y02C20/00—Capture or disposal of greenhouse gases
- Y02C20/40—Capture or disposal of greenhouse gases of CO2
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/10—Process efficiency
- Y02P20/129—Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/151—Reduction of greenhouse gas [GHG] emissions, e.g. CO2
Landscapes
- Treating Waste Gases (AREA)
- Gas Separation By Absorption (AREA)
Abstract
The utility model discloses a kind of smoke carbon dioxide capture system, comprise that carbon dioxide absorption tower, ammonia detect and reclaim integrated morphology, absorbent preparation device, heat exchange and revived structure and multi-stage compression-segmentation heat-obtaining structure.Said system adopts the carbon dioxide in ammoniacal liquor decarburization technique trapping flue gas in the time of operation; Ammonia concentration in flue gas after decarburization is detected, and during lower than preset concentration, flue gas directly discharges, and carries out ammonia recycling during higher than preset concentration; Carbon trapping rich solution is carried out to thermal regeneration reuse absorbent, produce high concentration carbon dioxide simultaneously; Take implements spatial scalable compression-segmentation heating picking process to concentrate regenerating carbon dioxide, and effective reuse waste heat.Carbon trapping ability of the present utility model is strong, and absorbent is cheap, and cost of investment is low.Can not only effective recycling waste heat, reduce absorbent regeneration energy consumption, solve the ammonia loss by volatilization problem of ammoniacal liquor capturing carbon dioxide, reduce operating cost, and do not produced secondary pollution.
Description
Technical field
The utility model relates to the technical field of flue gas managing technique, espespecially a kind of smoke carbon dioxide capture system.
Background technology
Combustion of fossil fuel is the main cause that produces great amount of carbon dioxide, and these carbon dioxide are discharged in atmosphere, causes the gas concentration lwevel in atmosphere significantly to raise since the industrial revolution, and has brought many harm.Scientist shows by research, and carbon dioxide is to cause greenhouse effects and cause the abnormal principal element of global climate.Greenhouse effects cause climate warming, and polar region and alpine glacier melt, thereby make that sea level rise, and observation shows, sea level rise in nearly more than 100 years 14-15 cm, and will continue rising can cause lowland to be flooded, drain off floodwaters freely and the problem such as inwelling like this.In addition, climate warming also will cause many species endangered, aggravation flood, harm humans health.Therefore, reduce in the world CO2 emissions extremely urgent.
China pays much attention to carbon dioxide discharge-reduction and control, in " National Program for Medium-to Long-term Scientific and Technological Development (2006-2020) ", " main industries carbon dioxide, the gas purging control of methane isothermal chamber and disposal utilize technology " listed in to the preferential theme of environmental area, and " develop the exploitation of fossil energy resources technology of efficient, clean and carbon dioxide near-zero release " in advanced energy technology direction proposition.Meanwhile, " country " 12 " scientific and technological development planning " proposes technology such as " utilization of development collecting carbonic anhydride with " sealing up for safekeeping." China's reply climate change science and technology special campaigns ", " country " 12 " reply climate change development in science and technology ad hoc planning " are all classified " collecting carbonic anhydride, utilization and Plugging Technology Applied " as emphasis support, are concentrated the focus technology field of tackling key problem and demonstration.
Carbon trapping, utilization and Plugging Technology Applied are emerging, to have extensive carbon dioxide discharge-reduction potentiality technology, are expected to realize the low-carbon (LC) utilization of fossil energy, are widely regarded as reply Global climate change, control one of important technology of greenhouse gas emission.
Current existing collecting carbonic anhydride method mainly contains before oxygen-enriched combusting trapping, burning after trapping and burning three kinds of trappings, and wherein, after burning, trapping is to apply comparatively general method.After burning, trapping is separation of C O the flue gas that produces at combustion synthesis in air from primary fuel of system
2.These systems are used liquid solvent conventionally, from main component is the flue gas of nitrogen (from air), catch a small amount of CO
2composition (generally accounting for the 3-15% of volume), wherein, chemical solvent is the most general as the absorption process application of liquid solvent.
At present, utilize the carbon dioxide in MEA (monoethanolamine) solution chemistry absorption and separation flue gas to drop into gradually commercial Application at home and abroad, but MEA solution self exists some inherent shortcomings, that wherein comparatively gives prominence to has MEA self price higher, regeneration temperature is too high, required energy consumption is large, and investment operating cost is high, and easily causes equipment corrosion.
Therefore, studying a kind of new collecting carbonic anhydride technique, reducing on the basis of energy consumption and cost, improve decarburization capacity and avoid corrosion and again pollute, is very necessary.
Utility model content
The purpose of this utility model is to provide a kind of smoke carbon dioxide capture system, can effectively improve decarburization capacity, reduces costs, and avoids the corrosion of equipment and again pollutes.
The technical scheme that the utility model provides is as follows:
A kind of smoke carbon dioxide capture system, comprising:
For the carbon dioxide absorption tower of collecting carbon dioxide from fuel gas, its underpart is provided with former gas approach and the outlet of carbon trapping rich solution, and its top is provided with exhanst gas outlet, and the inside of described carbon dioxide absorption tower is provided with the spraying layer that from up to down sprays ammonia absorption agent;
For the preparation of the absorbent preparation device of ammoniacal liquor, its liquid outlet is communicated with the spraying layer of described ammonia absorption agent;
Ammonia detects and reclaims integrated morphology, and it comprises that ammonia concentration detector, decarburization fume emission bypass line, ammonia reclaim bypass line, ammonia recovery tower and desorber; Wherein, the exhanst gas outlet pipeline of described carbon dioxide absorption tower reclaims bypass line with described decarburization fume emission bypass line and described ammonia simultaneously and is connected, and described ammonia concentration detector is arranged on described carbon dioxide absorption tower exhanst gas outlet pipeline; Described decarburization fume emission bypass line is provided with the first valve, and described ammonia reclaims bypass line place and is provided with the second valve, and described the first valve is connected with described ammonia concentration detector respectively with described the second valve; In the time that described ammonia concentration detector detects that the ammonia concentration of described carbon dioxide absorption tower smoke outlet is less than preset concentration, described the first valve opening, described the second valve closing, the exhanst gas outlet of described carbon dioxide absorption tower and the conducting of described decarburization fume emission bypass line; The ammonia concentration that described carbon dioxide absorption tower smoke outlet detected when described ammonia concentration detector is during greater than or equal to preset concentration, described the second valve opening, described the first valve closing, the exhanst gas outlet of described carbon dioxide absorption tower and described ammonia reclaim bypass line conducting; Wherein, described ammonia reclaims bypass line and is communicated with successively described ammonia recovery tower and described desorber, in described ammonia recovery tower, be provided with the shower for reclaiming ammonia, the bottom liquid outlet of described ammonia recovery tower is communicated with the top inlet of described desorber, the bottom liquid outlet of described desorber is communicated with for the shower that reclaims ammonia with in described ammonia recovery tower, and the gas outlet, top of described desorber is communicated with described absorbent preparation device;
Regenerator, its top is provided with gas outlet, and top is provided with the import of decarburization rich solution, and bottom is provided with the outlet of regeneration lean solution; The decarburization rich solution import of described regenerator is connected with the described carbon trapping rich solution outlet of described carbon dioxide absorption tower;
Multi-stage compression-segmentation heat-obtaining structure, it comprises the compound compressor connecting successively, the each correspondence of every stage compressor arranges a condenser, condensers at different levels are communicated with the outlet of same stage compressor and the entrance of next stage compressor respectively, and the gas access of compressor and the gas outlet of described regenerator are connected described in the first order.
Further preferably, before the former gas approach of described carbon dioxide absorption tower, be provided with booster fan and cooler, the gas outlet of described booster fan is communicated with the air inlet of described cooler, and the gas outlet of described cooler is communicated with the former gas approach of described carbon dioxide absorption tower.
Further preferably, described ammonia recovery tower is horizontal packed tower, and described ammonia recovery tower is disposed with gas approach, flue gas even distribution device, ammonia exhausting section, demister and clean exhanst gas outlet according to flow of flue gas direction; Wherein, described ammonia exhausting section is provided with liquid outlet at the bottom of water spraying layer, packing layer and tower from top to bottom successively, and described water spraying layer place is provided with described for reclaiming the shower of ammonia.
Further preferably, the bottom lean solution outlet of described regenerator is connected with described absorbent preparation device.
Further preferably, described smoke carbon dioxide capture system further comprises:
Heat-exchange system, it comprises First Heat Exchanger and the second heat exchanger;
Described First Heat Exchanger is arranged between described ammonia recovery tower and described desorber, the bottom liquid outlet of the top inlet of the bottom liquid outlet of described ammonia recovery tower, described desorber, described desorber, is describedly communicated with described First Heat Exchanger respectively for the shower that reclaims ammonia; Connecting pipe between the bottom liquid outlet of described ammonia recovery tower and the top inlet of described desorber, with, the bottom liquid outlet of described desorber and described for reclaiming the connecting pipe between the shower of ammonia, flows respectively and carries out heat exchange by described First Heat Exchanger and in described First Heat Exchanger;
Wherein, between the bottom liquid outlet of described ammonia recovery tower and described First Heat Exchanger, the first centrifugal pump is set;
Described the second heat exchanger is arranged between described carbon dioxide absorption tower and described regenerator, and the carbon trapping rich solution outlet of described carbon dioxide absorption tower, the decarburization rich solution import of described regenerator, described condensers at different levels are communicated with described the second heat exchanger respectively; Connecting pipe between carbon trapping rich solution outlet and the decarburization rich solution import of described regenerator of described carbon dioxide absorption tower, and the waste heat recovery passage of described condenser, flows respectively by described the second heat exchanger and in described the second heat exchanger and carries out heat exchange;
Wherein, between the outlet of the carbon of described carbon dioxide absorption tower trapping rich solution and described the second heat exchanger, the second centrifugal pump is set.
The smoke carbon dioxide capture system providing by the utility model, can bring following at least one beneficial effect:
1. can effectively reduce collecting carbonic anhydride cost, save the energy, avoid equipment corrosion.The utility model uses the better absorbent of ammoniacal liquor as a kind of capturing carbon dioxide, possesses good carbon dioxide reaction speed and relatively low regeneration energy consumption, and absorbability is the several times of MEA solution.And ammoniacal liquor is as the common raw material of one, and cost also reduces many compared with MEA solution, greatly reduced operating cost.Ammoniacal liquor, due to himself characteristic, has effectively been avoided the problem such as equipment corrosion and oxidative degradation simultaneously, and range of application is extremely wide.
2. effectively solve the volatilization loss problem of ammoniacal liquor, effectively avoid waste and the secondary pollution of ammonia.The utility model is first by the carbon dioxide in ammonia absorption agent trapping flue gas, and obtaining flue gas and trapping after decarburization has the absorption rich solution of carbon dioxide; Ammonia concentration in flue gas after decarburization is detected in real time, as lower than preset value, directly discharge flue gas after decarburization, and in the time being equal to or greater than preset value, represent that the ammon amount in flue gas is higher after decarburization, need recycle, and then in time volatilization ammonia be recycled to (can coordinate desorb processing to obtain ammonia by spray washing way of recycling), effectively avoided the loss of ammonia and again polluted; There is the absorption rich solution of carbon dioxide to produce high concentration carbon dioxide and ammonia absorption agent by the pyrolysis regeneration of regenerator to trapping.Said process, by can effectively solve the high volatilization loss problem of ammoniacal liquor to the recovery of ammonia, is effectively avoided the waste of ammonia.Meanwhile, the ammonia of recovery can repeat to prepare the ammonia absorption agent of collecting carbon dioxide from fuel gas, has not only improved the utilization rate of ammonia, can further effectively reduce costs simultaneously.
3. the energy consumption in effective reduction system running, saves the energy.The stage that the utility model can reclaim at the volatilization ammonia in decarburization flue gas, washing ammoniacal liquor and this washed ammoniacal liquor and carries out the stripping liquid that desorb processing obtains and carry out heat exchange recovery place of fountain ammonia, need in desorber, be desorbed with higher temperature owing to washing ammoniacal liquor, and the shower that stripping liquid need to be back to ammonia recovery place with low-temperature condition carries out secondary utilization, thereby in order effectively to utilize the heat of washing ammoniacal liquor and stripping liquid, its heat of balance, institute so that the two flow through a heat exchanger simultaneously and carry out heat exchange, obtain preferably duty temperature, improve capacity usage ratio, effectively reduce energy consumption.Simultaneously, to regeneration after carbon dioxide carry out in the process of multi-stage compression multi-stage condensing, not only can obtain liquid carbon dioxide, be convenient to transport and other operations, the heat that simultaneously also every grade of compression condensation can be produced reclaims, and be applied to collecting carbonic anhydride rich solution is entered to the heating before regenerator, effectively utilize the energy in system running, reduce energy consumption.
Brief description of the drawings
Below in conjunction with the drawings and specific embodiments, the utility model is described in further detail:
Fig. 1 is the structural representation of a kind of embodiment of smoke carbon dioxide capture system of the present utility model.
Drawing reference numeral explanation:
1, booster fan; 2, cooler; 3, carbon dioxide absorption tower; 4, ammonia concentration detector; 5, the first valve; 6, the second valve; 7, ammonia recovery tower; 701, flue gas even distribution device; 702, ammonia exhausting section; 703, demister; 8, the first centrifugal pump; 9, First Heat Exchanger; 10, desorber; 11, absorbent preparation device; 12, the second centrifugal pump; 13, the second heat exchanger; 14, regenerator; 15, a stage compressor; 16, first-stage condenser; 17, split-compressor; 18, secondary condenser; 19, three-stage blower; 20, three grades of condensers.
Detailed description of the invention
In order to be illustrated more clearly in the utility model embodiment or technical scheme of the prior art, to the accompanying drawing of required use in embodiment or description of the Prior Art be briefly described below, apparently, accompanying drawing in the following describes is only embodiment more of the present utility model, for those of ordinary skill in the art, do not paying under the prerequisite of creative work, can also obtain according to these accompanying drawings other accompanying drawing.
In embodiment mono-of the present utility model, a kind of smoke carbon dioxide capture system comprises:
(1) carbon dioxide absorption tower, its bottom is provided with former gas approach and the outlet of carbon trapping rich solution, its top is provided with exhanst gas outlet, and the inside of described carbon dioxide absorption tower is provided with the spraying layer that from up to down sprays ammonia absorption agent, the position of described spraying layer is higher than the position of described former gas approach.The utility model uses ammoniacal liquor carry out adverse current and react with the flue gas passing in carbon dioxide absorption tower as absorbent, the carbon dioxide in trapping flue gas.Wherein, to, higher than the position of former gas approach, so just can form the adverse current between flue gas and absorbent for the position of the spraying layer that sprays ammonia absorption agent.Meanwhile, the position of exhanst gas outlet can be set to just can realize content of the present utility model higher than former gas approach and liquid outlet, is arranged at top and is easier to discharge.
(2) for the preparation of the absorbent preparation device of ammoniacal liquor, its liquid outlet is communicated with described carbon dioxide absorption tower spraying layer.Absorbent preparation device is used to carbon dioxide absorption tower that ammonia absorption agent is provided, and the ammonia absorption agent of preparation is introduced into spraying layer and sprays, and can realize this process by water pump equal power device.
(3) ammonia detects and reclaims integrated morphology, and it comprises that ammonia concentration detector, decarburization fume emission bypass line, ammonia reclaim bypass line, ammonia recovery tower and desorber.Wherein, the exhanst gas outlet pipeline of described carbon dioxide absorption tower reclaims bypass line with described decarburization fume emission bypass line and described ammonia simultaneously and is connected, and described ammonia concentration detector is arranged on exhanst gas outlet pipeline; Described decarburization fume emission bypass line is provided with the first valve, and described ammonia reclaims bypass line place and is provided with the second valve, and described the first valve is connected respectively (can be electrical connection) with described ammonia concentration detector with the second valve.In the time that described ammonia concentration detector detects that the ammonia concentration of described carbon dioxide absorption tower smoke outlet is less than preset concentration, described the first valve opening, described the second valve closing, described carbon dioxide absorption tower exhanst gas outlet and the conducting of described decarburization fume emission bypass line; The ammonia concentration that described carbon dioxide absorption tower smoke outlet detected when described ammonia concentration detector is during greater than or equal to preset concentration, described the second valve opening, described the first valve closing, described carbon dioxide absorption tower exhanst gas outlet and described ammonia reclaim bypass line conducting; Wherein, described ammonia reclaims bypass line and is communicated with successively ammonia recovery tower and desorber, described ammonia recovery tower is provided with gas approach, exhanst gas outlet and liquid outlet, and in described ammonia recovery tower, be provided with the shower reclaiming for ammonia, described desorber top is respectively equipped with inlet, gas outlet, its underpart is provided with liquid outlet, and the liquid outlet of desorber is communicated with the shower reclaiming for ammonia.Because flue gas is after carbon dioxide absorption tower decarburization, can obtain flue gas and trapping after decarburization has the absorption liquid of carbon dioxide, i.e. decarburization rich solution.Because ammoniacal liquor is volatile, so flue gas is often mixed with a certain amount of ammonia after the decarburization of discharging, in the time that the ammon amount in flue gas after decarburization is lower, (can uses lower than a certain preset value and judge), flue gas directly discharges; And (can judge with being equal to or higher than a certain preset value) in the time that the ammon amount in flue gas after decarburization is higher, need reclaim, avoid secondary pollution and waste.One ammonia concentration detector can be set on the exhanst gas outlet passage of carbon dioxide absorption tower and detect in real time the ammon amount in outlet flue gas.Each one of them that only reclaims bypass line with decarburization fume emission bypass line or ammonia of the exhanst gas outlet of carbon dioxide absorption tower is communicated with, when difference, is communicated with two bypass line.(a) when the ammon amount detecting is during lower than a certain preset concentration, decarburization exhanst gas outlet is communicated with decarburization fume emission bypass line, does not reclaim bypass line with ammonia and is communicated with, and after decarburization, flue gas is discharged from decarburization fume emission bypass line.(b) and in the time that the ammon amount detecting is equal to or higher than a certain preset concentration, decarburization exhanst gas outlet reclaims bypass line with ammonia and is communicated with, be not communicated with decarburization fume emission bypass line, after decarburization, flue gas enters ammonia and reclaims bypass line, and introducing is carried out the recovery of ammonia with the ammonia recovery tower that ammonia recovery bypass line is communicated with.In the present embodiment, ammonia recovery tower adopts spray mode to reclaim ammonia, in ammonia recovery tower, be provided with the shower for spraying this place's absorbent, after spray, obtain except the clean flue gas after ammonia and trap the ammoniacal liquor of washing that has ammonia, clean flue gas directly discharges from the gas outlet of ammonia recovery tower, wash that ammoniacal liquor is imported in a desorber by the liquid outlet of ammonia recovery tower and heated desorb obtains ammonia, ammonia can be collected and further utilize; Ammonia recovery tower (the device place that can flow back into the agent of ammonia recovery tower place storage spray-absorption, also can be communicated with the second shower) is discharged and flow back into gained stripping liquid from the liquid outlet of desorber, again utilizes.So just complete the recovery of ammonia, efficiently solved the high volatile volatile problem of ammonia, avoided secondary pollution.
(4) regenerator, its top is provided with gas outlet, and top is provided with the import of decarburization rich solution, and bottom is provided with the outlet of regeneration lean solution; Wherein, the import of decarburization rich solution is connected with the carbon trapping rich solution outlet at the bottom of described carbon dioxide absorption tower tower.Flue gas is after carbon dioxide absorption tower decarburization, and the trapping obtaining has the absorption rich solution of carbon dioxide need to carry out the regeneration processing of carbon dioxide, just can obtain the carbon dioxide that purity is higher and be used; Treatment fluid after regeneration can be prepared ammonia absorption agent simultaneously, is again applied to carbon dioxide absorption tower place.
(5) multi-stage compression-segmentation heat-obtaining structure, it comprises the compound compressor connecting successively, every stage compressor arranges a condenser, condensers at different levels are communicated with compressor outlet at the same level and next stage suction port of compressor respectively, in multistage described compressor, the gas access of compressor is connected with described regenerator gas outlet described in the first order.The carbon dioxide of regenerator place regeneration is gaseous state, needs to obtain liquid carbon dioxide through multi-stage compression-segmentation heat-obtaining structure and can be convenient to storage and transport.
In embodiment bis-of the present utility model, embodiment mono-is improved.Booster fan and cooler are set before the gas approach of carbon dioxide absorption tower, and wherein, the gas outlet of described booster fan is communicated with the air inlet of described cooler, and the gas outlet of described cooler is communicated with the former gas approach of described carbon dioxide absorption tower.Flue gas flows through booster fan and cooler successively, after be introduced into carbon dioxide absorption tower.Because the general temperature of flue gas is higher, cooler can make flue gas cooling, meets the reaction temperature of ammoniacal liquor capturing carbon dioxide.
In embodiment tri-of the present utility model, embodiment mono-is improved.Can be set to horizontal packed tower by ammonia recovery tower, and in described ammonia recovery tower, be disposed with gas approach, flue gas even distribution device, ammonia exhausting section, demister and clean exhanst gas outlet according to flow of flue gas direction; Wherein, described ammonia exhausting section is provided with liquid outlet at the bottom of water spraying layer, packing layer and tower from top to bottom successively, and described water spraying layer place is provided with described for reclaiming the shower of ammonia.Packed tower is the one of tower, fills the suitably filler of height, to increase by two kinds of contact surfaces between fluid in tower.Ammonia recovery tower in the present embodiment is set to horizontal packed tower, air inlet is arranged on the left end of tower, gas outlet is arranged on the right-hand member of tower, and in tower, set gradually from left to right flue gas even distribution device, ammonia exhausting section and demister, wherein, flue gas even distribution device can make decarburization flue gas uniform in ammonia recovery tower, increases organic efficiency; Ammonia exhausting section adopts fountain to reclaim, and by shower shower water washing lotion, absorbs the ammonia in decarburization flue gas, and obtains the flue gas after deamination and wash ammoniacal liquor, and discharge smoke gas flow gas outlet through right-hand member after demister is removed droplet, washes ammoniacal liquor and discharge through liquid outlet.The packing layer of horizontal packed tower structure is arranged on ammonia exhausting section place, and is arranged on the below of water spraying layer, the top of liquid outlet.
In embodiment tetra-of the present utility model, embodiment mono-is improved, the gas outlet of desorber can be communicated with absorbent preparation device, because stripping gas is gaseous ammonia, can be recycled and reused for the ammonia absorption agent of preparing carbon dioxide absorption tower, effectively improve the utilization rate of ammonia in the utility model.In the same manner, the treatment fluid that obtains carbon dioxide and contain ammoniacal liquor due to regenerator regeneration, thereby the liquid outlet of regenerator can be communicated with absorbent preparation device, the treatment fluid that regenerator is obtained is again for the preparation of the absorbent of carbon dioxide absorption tower.
In embodiment five of the present utility model, embodiment mono-is improved, exist respectively because multistage of the present utility model is in service need heating or cooling after the situation of reacting again, for the consideration that reduces energy consumption, multiple heat exchangers can be set in the utility model, to carry out effectively mutual utilization of energy.In the present embodiment, system further comprises: heat-exchange system, and it comprises First Heat Exchanger and the second heat exchanger, concrete application is as follows:
Wash ammoniacal liquor and need heat the reaction temperature requirement that just can meet desorber inside due to what the liquid outlet at ammonia recovery tower place flowed out, and the stripping liquid simultaneously flowing out from the liquid outlet of desorber needs could meet better after cooling the temperature requirement of the spray liquid of ammonia recovery tower, wash like this and between ammoniacal liquor and stripping liquid, just can realize exchange heat.Thereby between described ammonia recovery tower and described desorber, First Heat Exchanger is set, ammonia recovery tower liquid outlet, desorber inlet, desorber liquid outlet, be communicated with First Heat Exchanger respectively for the shower that reclaims ammonia.Particularly, connecting pipe (washing ammoniacal liquor) between the liquid outlet of ammonia recovery tower and the inlet of desorber, with, the liquid outlet of desorber and for reclaiming the connecting pipe (stripping liquid) between the shower of ammonia, the described First Heat Exchanger carry out heat exchange in described First Heat Exchanger of flowing through respectively.
In the same manner, due to the absorption liquid of capturing carbon dioxide need to be in regenerator thermal regeneration, and the heat that multi-stage condensing device extracts can be used for the heating of this absorption liquid just, has improved the utilization rate of energy.Thereby between described carbon dioxide absorption tower and described regenerator, the second heat exchanger being set, this second heat exchanger traps rich solution outlet, the decarburization rich solution import of described regenerator, the waste heat recovery channel connection of condenser with the carbon of described carbon dioxide absorption tower simultaneously; Particularly, connecting pipe (absorption liquid of capturing carbon dioxide) between carbon trapping rich solution outlet and the decarburization rich solution import of described regenerator of described carbon dioxide absorption tower, with, the waste heat recovery passage of condenser, flows through respectively described the second heat exchanger and carry out heat exchange in described the second heat exchanger.
In embodiment six of the present utility model, above-described embodiment six is improved, at above-mentioned heat exchanger, place arranges respectively centrifugal pump, particularly, reclaims between liquid outlet and First Heat Exchanger the first centrifugal pump is set at ammonia; Between carbon dioxide absorption tower liquid outlet and the second heat exchanger, the second centrifugal pump is set, can carries better liquid.
In a full implementation example of the present utility model, with reference to Fig. 1, the structure of the smoke carbon dioxide capture system of the present embodiment, comprising: carbon dioxide absorption tower 3, ammonia detect and reclaim integrated morphology (4~10), absorbent preparation device 11, heat exchange and revived structure (12~14) and multi-stage compression-segmentation heat-obtaining structure (15~20).Before the smoke inlet of carbon dioxide absorption tower 3, be provided with booster fan 1 and cooler 2.Ammonia detects and reclaims integrated morphology (4~10) and is disposed with ammonia concentration detector 4, decarburization fume emission bypass line and ammonia recovery bypass line according to flow of flue gas direction, and is arranged on first valve 5 and the second valve 6, ammonia recovery tower 7, the first centrifugal pump 8, First Heat Exchanger 9 and the desorber 10 that are arranged on ammonia recovery bypass line place at decarburization fume emission bypass line place.Wherein, ammonia recovery tower 7 is horizontal packed tower, in tower, be disposed with gas approach, flue gas even distribution device 701, ammonia exhausting section 702, demister 703 and clean exhanst gas outlet according to flow of flue gas direction, described ammonia exhausting section 702 is provided with water spraying layer, packing layer and liquid outlet from top to bottom successively.
Heat exchange and revived structure (12~14) comprise the second centrifugal pump 12, the second heat exchanger 13 and regenerator 14 successively.
Described multi-stage compression-segmentation heat-obtaining structure (15~20) comprises a stage compressor 15, first-stage condenser 16, split-compressor 17, secondary condenser 18, three-stage blower 19 and three grades of condensers 20.One stage compressor 15 outlets are communicated with first-stage condenser 16 imports, first-stage condenser 16 outlets are communicated with split-compressor 17 imports, split-compressor 17 outlets are communicated with secondary condenser 18 imports, secondary condenser 18 outlets are communicated with the import of three-stage blower 19, the outlet of three-stage blower 19 is communicated with three grades of condenser 20 imports, and carbon dioxide condensation is drawn by three grades of condensers 20.The waste heat passage that compression condensation at different levels produce is communicated with the second heat exchanger 13.
Ammonia concentration detector 4 is arranged on the exhanst gas outlet flue of carbon dioxide absorption tower 3, ammonia concentration detector 4 connects two flue gas branch roads, article one, be decarburization fume emission bypass line, another,, for ammonia recovery bypass line, arranges respectively the first valve 5 and the second valve 6 in described two flue gas bypass line.
The valve 6 that ammonia reclaims on branch road is communicated with ammonia recovery tower 7 gas approach, the liquid outlet of described ammonia recovery tower 7 is communicated with successively with the first centrifugal pump 8 and First Heat Exchanger 9, and described First Heat Exchanger 9 is also connected respectively with the water spraying layer of desorber 10 inlets, desorber 10 bottom liquid outlets and ammonia exhausting section 702, make the ammoniacal liquor of washing from circulating between the liquid outlet of ammonia recovery tower 7 and the inlet of desorber 10, with, the stripping liquid circulating between desorber 10 bottom liquid outlets and the water spraying layer of ammonia exhausting section 702 carries out exchange heat at First Heat Exchanger 9 places.
The gas vent at desorber 10 tops is connected with absorbent preparation device 11, for the raw material using desorb gas ammonia as absorbent preparation device 11 places.
The tower top of carbon dioxide absorption tower 3 arranges exhanst gas outlet, tower top is provided with absorbent import, tower bottom is provided with former gas approach, tower bottom is provided with the rich solution outlet of capturing carbon dioxide, and the rich solution outlet of described capturing carbon dioxide is connected with the top inlet of the second centrifugal pump 12, the second heat exchanger 13 and regenerator 14 successively.The top gas outlet of described regenerator 14 is communicated with a stage compressor 15, and the bottom liquid outlet of regenerator 14 is communicated with absorbent preparation device 11.
Above-mentioned full implementation example, in the time of operation, mainly comprises the following steps, as shown in Figure 1:
Introduce carbon dioxide capture system through the coal-fired flue-gas after the techniques such as dedusting, denitration and FGD desulfurization by booster fan 1, first cooling through cooler 2, introducing carbon dioxide absorption tower 3 again, carbon dioxide absorption tower 3 is packed tower, former flue gas in carbon dioxide absorption tower 3 with ammonia absorption agent counter current contacting reacting, carbon dioxide in former flue gas is captured and removes, after decarburization, flue gas is drawn by carbon dioxide absorption tower 3 tower tops, and the rich solution after absorbent capturing carbon dioxide is discharged from the bottom of carbon dioxide absorption tower 3.
On the tower top outlet flue of carbon dioxide absorption tower 3, be provided with ammonia concentration detector 4, the concentration of on-line real time monitoring outlet ammonia in flue gas gas, when ammonia concentration is during lower than preset value, the first valve 5 is opened, and the second valve 6 is closed, and outlet flue gas directly discharges; When ammonia concentration is during higher than (or equaling) preset value, the first valve 5 is closed, and the second valve 6 is opened, and outlet flue gas is transfused to ammonia recovery tower 7.
Outlet flue gas enters after ammonia recovery tower 7, first make flue gas be uniformly distributed in ammonia recovery tower through flue gas even distribution device 701, flue gas enters ammonia exhausting section 702 subsequently, ammonia exhausting section 702 is provided with water spraying layer, packing layer and liquid outlet from top to bottom, flue gas contacts with shower water at packing layer, the volatilization ammonia carrying in flue gas is removed by washing, washes ammoniacal liquor and is discharged by the liquid outlet of ammonia exhausting section 702, and clean flue gas is emptying from ammonia recovery tower 7 right side exhaust pass after demister 703 is removed droplet.
Wash ammoniacal liquor after discharge ammonia exhausting section 7 bottoms, be delivered to First Heat Exchanger 9 by the first centrifugal pump 8, this with carry out heat exchange from the stripping liquid of desorber 10 bottoms, after heating up, enter desorber 10, can realize gas-water separation at desorber 10 wash-in ammoniacal liquors, absorbent preparation device 11 is drawn and be delivered to the ammonia after dehydration from tower top, and the water after desorb is discharged at the bottom of tower, first through First Heat Exchanger 9 with wash ammoniacal liquor heat exchange, after deliver to the spraying layer of the interior ammonia exhausting section 702 of ammonia recovery tower 7.
Carbon trapping rich solution is discharged from carbon dioxide absorption tower 3 bottoms, be delivered to the second heat exchanger 13 by the second centrifugal pump 12 heated, after be transported to regenerator 14, carbon trapping rich solution discharges carbon dioxide in the interior generation pyrolytic reaction of regenerator 14, carbon trapping rich solution is regenerated, absorbent preparation device 11 is discharged and sent back to lean solution after regeneration from regenerator 14 bottoms, and the high concentration carbon dioxide discharging is drawn from regenerator 14 tower tops.
From the high concentration carbon dioxide of regenerator 14 successively successively through a stage compressor 15 and first-stage condenser 16, split-compressor 17 and secondary condenser 18, three-stage blower 19 and three grades of condensers 20, through multi-stage compression and condensation, the waste heat that every grade of compression condensation produces is all recovered to the second heat exchanger 13, for carbon trapping rich solution thermal regeneration, the liquid carbon dioxide after compression condensation will or be sealed up for safekeeping processing as the raw material of industry.
Smoke carbon dioxide capture method of the present utility model, utilizes ammoniacal liquor to catch the CO in flue gas
2, removal efficiency can reach more than 99%, CO
2absorbability can reach 1.2Kg/NH
3, absorbability is strong, and absorbent is cheap, and cost of investment is low.
In addition, method of the present utility model can effective recycling gas concentration waste heat, has reduced absorbent regeneration energy consumption, improve resource utilization, reduce operating cost, and efficiently solved the ammonia loss by volatilization problem of ammoniacal liquor capturing carbon dioxide, avoided secondary pollution.
It should be noted that all independent assortments as required of above-described embodiment.The above is only preferred embodiment of the present utility model; it should be pointed out that for those skilled in the art, do not departing under the prerequisite of the utility model principle; can also make some improvements and modifications, these improvements and modifications also should be considered as protection domain of the present utility model.
Claims (5)
1. a smoke carbon dioxide capture system, is characterized in that, comprising:
For the carbon dioxide absorption tower of collecting carbon dioxide from fuel gas, its underpart is provided with former gas approach and the outlet of carbon trapping rich solution, and its top is provided with exhanst gas outlet, and the inside of described carbon dioxide absorption tower is provided with the spraying layer that from up to down sprays ammonia absorption agent;
For the preparation of the absorbent preparation device of ammoniacal liquor, its liquid outlet is communicated with the spraying layer of described ammonia absorption agent;
Ammonia detects and reclaims integrated morphology, and it comprises that ammonia concentration detector, decarburization fume emission bypass line, ammonia reclaim bypass line, ammonia recovery tower and desorber; Wherein, the exhanst gas outlet pipeline of described carbon dioxide absorption tower reclaims bypass line with described decarburization fume emission bypass line and described ammonia simultaneously and is connected, and described ammonia concentration detector is arranged on described carbon dioxide absorption tower exhanst gas outlet pipeline; Described decarburization fume emission bypass line is provided with the first valve, and described ammonia reclaims bypass line place and is provided with the second valve, and described the first valve is connected with described ammonia concentration detector respectively with described the second valve; In the time that described ammonia concentration detector detects that the ammonia concentration of described carbon dioxide absorption tower smoke outlet is less than preset concentration, described the first valve opening, described the second valve closing, the exhanst gas outlet of described carbon dioxide absorption tower and the conducting of described decarburization fume emission bypass line; The ammonia concentration that described carbon dioxide absorption tower smoke outlet detected when described ammonia concentration detector is during greater than or equal to preset concentration, described the second valve opening, described the first valve closing, the exhanst gas outlet of described carbon dioxide absorption tower and described ammonia reclaim bypass line conducting; Wherein, described ammonia reclaims bypass line and is communicated with successively described ammonia recovery tower and described desorber, in described ammonia recovery tower, be provided with the shower for reclaiming ammonia, the bottom liquid outlet of described ammonia recovery tower is communicated with the top inlet of described desorber, the bottom liquid outlet of described desorber is communicated with for the shower that reclaims ammonia with in described ammonia recovery tower, and the gas outlet, top of described desorber is communicated with described absorbent preparation device;
Regenerator, its top is provided with gas outlet, and top is provided with the import of decarburization rich solution, and bottom is provided with the outlet of regeneration lean solution; The decarburization rich solution import of described regenerator is connected with the described carbon trapping rich solution outlet of described carbon dioxide absorption tower;
Multi-stage compression-segmentation heat-obtaining structure, it comprises the compound compressor connecting successively, the each correspondence of every stage compressor arranges a condenser, condensers at different levels are communicated with the outlet of same stage compressor and the entrance of next stage compressor respectively, and the gas access of compressor and the gas outlet of described regenerator are connected described in the first order.
2. smoke carbon dioxide capture system according to claim 1, is characterized in that:
Before the former gas approach of described carbon dioxide absorption tower, be provided with booster fan and cooler, the gas outlet of described booster fan is communicated with the air inlet of described cooler, and the gas outlet of described cooler is communicated with the former gas approach of described carbon dioxide absorption tower.
3. according to the smoke carbon dioxide capture system described in claim 1-2 any one, it is characterized in that:
Described ammonia recovery tower is horizontal packed tower, and described ammonia recovery tower is disposed with gas approach, flue gas even distribution device, ammonia exhausting section, demister and clean exhanst gas outlet according to flow of flue gas direction; Wherein, described ammonia exhausting section is provided with liquid outlet at the bottom of water spraying layer, packing layer and tower from top to bottom successively, and described water spraying layer place is provided with described for reclaiming the shower of ammonia.
4. according to the smoke carbon dioxide capture system described in claim 1-2 any one, it is characterized in that:
The bottom lean solution outlet of described regenerator is connected with described absorbent preparation device.
5. according to the smoke carbon dioxide capture system described in claim 1-2 any one, it is characterized in that, further comprise:
Heat-exchange system, it comprises First Heat Exchanger and the second heat exchanger;
Described First Heat Exchanger is arranged between described ammonia recovery tower and described desorber, the bottom liquid outlet of the top inlet of the bottom liquid outlet of described ammonia recovery tower, described desorber, described desorber, is describedly communicated with described First Heat Exchanger respectively for the shower that reclaims ammonia; Connecting pipe between the bottom liquid outlet of described ammonia recovery tower and the top inlet of described desorber, with, the bottom liquid outlet of described desorber and described for reclaiming the connecting pipe between the shower of ammonia, flows respectively and carries out heat exchange by described First Heat Exchanger and in described First Heat Exchanger;
Wherein, between the bottom liquid outlet of described ammonia recovery tower and described First Heat Exchanger, the first centrifugal pump is set;
Described the second heat exchanger is arranged between described carbon dioxide absorption tower and described regenerator, and the carbon trapping rich solution outlet of described carbon dioxide absorption tower, the decarburization rich solution import of described regenerator, described condensers at different levels are communicated with described the second heat exchanger respectively; Connecting pipe between carbon trapping rich solution outlet and the decarburization rich solution import of described regenerator of described carbon dioxide absorption tower, and the waste heat recovery passage of described condenser, flows respectively by described the second heat exchanger and in described the second heat exchanger and carries out heat exchange;
Wherein, between the outlet of the carbon of described carbon dioxide absorption tower trapping rich solution and described the second heat exchanger, the second centrifugal pump is set.
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Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
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CN104107629A (en) * | 2014-08-04 | 2014-10-22 | 上海龙净环保科技工程有限公司 | System and method for capturing carbon dioxide in smoke |
CN108290112A (en) * | 2015-11-27 | 2018-07-17 | 株式会社Posco | The removal methods and its device of carbon dioxide in sour gas |
CN110508098A (en) * | 2019-07-22 | 2019-11-29 | 西安交通大学 | A kind of method of multipotency regulation tree-shaped hetero-junctions trapping carbon dioxide |
CN114159952A (en) * | 2021-09-29 | 2022-03-11 | 北京百利时能源技术股份有限公司 | Ammonia water method carbon trapping device |
CN115970447A (en) * | 2022-12-21 | 2023-04-18 | 中南大学 | Carbon desorption and carbon capture method, device and system |
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2014
- 2014-08-04 CN CN201420436545.2U patent/CN203971736U/en not_active Expired - Lifetime
Cited By (9)
Publication number | Priority date | Publication date | Assignee | Title |
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CN104107629A (en) * | 2014-08-04 | 2014-10-22 | 上海龙净环保科技工程有限公司 | System and method for capturing carbon dioxide in smoke |
CN104107629B (en) * | 2014-08-04 | 2016-08-24 | 上海龙净环保科技工程有限公司 | A kind of smoke carbon dioxide capture system and capture method |
CN108290112A (en) * | 2015-11-27 | 2018-07-17 | 株式会社Posco | The removal methods and its device of carbon dioxide in sour gas |
CN110508098A (en) * | 2019-07-22 | 2019-11-29 | 西安交通大学 | A kind of method of multipotency regulation tree-shaped hetero-junctions trapping carbon dioxide |
CN110508098B (en) * | 2019-07-22 | 2020-06-19 | 西安交通大学 | Method for trapping carbon dioxide by multi-energy regulation tree-shaped heterojunction |
CN114159952A (en) * | 2021-09-29 | 2022-03-11 | 北京百利时能源技术股份有限公司 | Ammonia water method carbon trapping device |
CN114159952B (en) * | 2021-09-29 | 2024-05-24 | 北京源碳环境股份有限公司 | Ammonia water method carbon trapping device |
CN115970447A (en) * | 2022-12-21 | 2023-04-18 | 中南大学 | Carbon desorption and carbon capture method, device and system |
CN115970447B (en) * | 2022-12-21 | 2024-05-28 | 中南大学 | Carbon desorption and carbon capture method, device and system |
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