CN112957902A - System and method for absorbing carbon dioxide in thermal power plant flue gas caustic soda solution - Google Patents
System and method for absorbing carbon dioxide in thermal power plant flue gas caustic soda solution Download PDFInfo
- Publication number
- CN112957902A CN112957902A CN202110160831.5A CN202110160831A CN112957902A CN 112957902 A CN112957902 A CN 112957902A CN 202110160831 A CN202110160831 A CN 202110160831A CN 112957902 A CN112957902 A CN 112957902A
- Authority
- CN
- China
- Prior art keywords
- carbon dioxide
- flue gas
- solution
- sodium hydroxide
- power plant
- 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
Links
Images
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/77—Liquid phase processes
- B01D53/79—Injecting reactants
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/346—Controlling the process
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/62—Carbon oxides
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12M—APPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
- C12M29/00—Means for introduction, extraction or recirculation of materials, e.g. pumps
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
- C12N1/12—Unicellular algae; Culture media therefor
-
- C—CHEMISTRY; METALLURGY
- C25—ELECTROLYTIC OR ELECTROPHORETIC PROCESSES; APPARATUS THEREFOR
- C25B—ELECTROLYTIC OR ELECTROPHORETIC PROCESSES FOR THE PRODUCTION OF COMPOUNDS OR NON-METALS; APPARATUS THEREFOR
- C25B1/00—Electrolytic production of inorganic compounds or non-metals
- C25B1/01—Products
- C25B1/14—Alkali metal compounds
- C25B1/16—Hydroxides
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/30—Alkali metal compounds
- B01D2251/304—Alkali metal compounds of sodium
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/60—Inorganic bases or salts
- B01D2251/604—Hydroxides
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2258/00—Sources of waste gases
- B01D2258/02—Other waste gases
- B01D2258/0283—Flue gases
-
- 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
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Health & Medical Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Organic Chemistry (AREA)
- Biomedical Technology (AREA)
- Biotechnology (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Zoology (AREA)
- Wood Science & Technology (AREA)
- Environmental & Geological Engineering (AREA)
- Bioinformatics & Cheminformatics (AREA)
- Analytical Chemistry (AREA)
- Genetics & Genomics (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Biochemistry (AREA)
- General Engineering & Computer Science (AREA)
- General Health & Medical Sciences (AREA)
- Microbiology (AREA)
- Sustainable Development (AREA)
- Virology (AREA)
- Tropical Medicine & Parasitology (AREA)
- Medicinal Chemistry (AREA)
- Cell Biology (AREA)
- Botany (AREA)
- Inorganic Chemistry (AREA)
- Electrochemistry (AREA)
- Materials Engineering (AREA)
- Metallurgy (AREA)
- Treating Waste Gases (AREA)
- Gas Separation By Absorption (AREA)
Abstract
The invention discloses a system and a method for absorbing carbon dioxide in a caustic soda solution in flue gas of a thermal power plant, wherein the system comprises a carbon dioxide reaction absorption tower, the lower part of the carbon dioxide reaction absorption tower is provided with a tower bottom gas pipeline provided with a flue gas inlet, and the upper part of the carbon dioxide reaction absorption tower is provided with a liquid inlet for inputting a sodium hydroxide solution; the flue gas inlet is connected to a boiler clean flue gas connecting pipeline of a thermal power plant, the carbon dioxide reaction absorption tower is connected with the sodium hydroxide feeding system through an absorption liquid supply pipeline, and the carbon dioxide reaction absorption tower is connected with the solution storage tank or the microalgae cultivation water tank through a reaction liquid discharge pipeline. The carbon dioxide absorption tower is utilized to carry out the convection mixing reaction of the sodium hydroxide solution and the flue gas through the aeration or spray atomization technology, and the low-price sodium hydroxide solution is utilized to realize the high-efficiency carbon dioxide absorption, namely carbon capture.
Description
Technical Field
The invention relates to the field of carbon dioxide emission reduction, in particular to a method for absorbing and capturing carbon dioxide in flue gas by using a carbon dioxide absorption tower.
Background
With the increasing level of industrialization in the world, the greenhouse effect of carbon dioxide in the atmosphere is intensified by the change of more and more fossil fuel use and land utilization. The increase in carbon dioxide content caused by human activities is being increasingly noticed. In all carbon dioxide gas emission sources, the amount of carbon dioxide emitted by a coal-fired thermal power plant accounts for the main part, so how to capture and treat the carbon dioxide gas in the boiler flue gas of the thermal power plant becomes the key for carbon emission reduction of the thermal power plant in the future.
Meanwhile, carbon dioxide is widely applied to various fields such as agriculture, machinery, chemical synthesis, food and the like. The recovery of carbon dioxide in the flue gas is not only the most direct and effective means for relieving the crisis of carbon dioxide emission, but also can reduce the production cost.
Methods for separating carbon dioxide from boiler flue gas generally include physical absorption, chemical absorption, membrane, and chemical adsorption, wherein chemical absorption is more common. The chemical treatment technology of carbon dioxide comprises one or more reversible reactions between carbon dioxide and other substances (such as various levels of alcohol amine, sodium hydroxide, sodium carbonate, ammonia gas or ammonia water and the like) to achieve the separation effect.
The existing chemical absorption method adopts a spraying or aerating process to mix the flue gas and the absorption liquid, and the mixing effect is common. Moreover, the cost of the existing absorption liquid is high, and if the existing absorption liquid can be replaced by the low-cost absorption liquid, the project economy is greatly improved.
Disclosure of Invention
The invention provides a system and a method for absorbing carbon dioxide in a caustic soda solution in flue gas of a thermal power plant, which can reduce the carbon dioxide absorption cost, namely carbon capture cost.
In order to achieve the purpose, the thermal power plant flue gas caustic soda solution carbon dioxide absorption system comprises a carbon dioxide reaction absorption tower, a sodium hydroxide feeding system and a sodium bicarbonate solution supply pipeline, wherein the lower part of the carbon dioxide reaction absorption tower is provided with a flue gas inlet connected with a tower bottom gas conveying pipeline, and the upper part of the carbon dioxide reaction absorption tower is provided with a liquid inlet used for inputting a sodium hydroxide solution; the flue gas entry is connected to the clean flue gas connecting line of the boiler of thermal power plant, and the inlet passes through absorption liquid confession liquid pipeline and sodium hydroxide charge-in system and connects, and carbon dioxide reaction absorption tower passes through reaction liquid discharge line and solution holding vessel and connects.
Furthermore, a sodium hydroxide feeding system is connected with an electrolytic cell for preparing caustic soda by electrolyzing brine in a thermal power plant, and the electrolytic cell for preparing caustic soda by electrolyzing brine is powered by peak-adjusting frequency-adjusting surplus electric power of the thermal power plant.
Further, a hydrogen outlet of the electrolytic tank for preparing the caustic soda by electrolyzing the brine is sent to a boiler for afterburning or a steel cylinder for storage or is sent to an external pipeline through a pipeline, and a chlorine outlet of the electrolytic tank for preparing the caustic soda by electrolyzing the brine is connected to a compression steel cylinder.
Further, the bottom of the carbon dioxide reaction absorption tower is provided with a sodium hydroxide solution or a reaction solution, the clean flue gas of the boiler is subjected to any one or combination of suspended jet flow, jet flow immersed in the solution, mixing of the flue gas and the sodium hydroxide solution through a jet flow guide air extractor and aeration of the flue gas from an aeration pipe at the bottom of the solution, so that the flue gas, the sodium hydroxide solution and the reaction solution are fully mixed and reacted.
Further, the sodium hydroxide solution is subjected to any one or combination of suspension jet flow, jet flow immersed in the solution and mixing of flue gas and the sodium hydroxide solution through an air jet drainage air extractor from the liquid inlet.
Furthermore, a spraying unit and/or an absorption liquid jet nozzle are arranged in the carbon dioxide reaction absorption tower, and the spraying unit and/or the absorption liquid jet nozzle are connected with a sodium hydroxide feeding system through an absorption liquid supply pipeline.
Furthermore, a carbon dioxide recovery pipeline is led out from the top of the carbon dioxide reaction absorption tower and connected to a boiler clean flue gas connecting pipeline, and a stop control valve and a gas dryer are arranged on the carbon dioxide recovery pipeline.
Further, a carbon dioxide concentration monitoring device is arranged at the top of the carbon dioxide reaction absorption tower.
A method for absorbing carbon dioxide in flue gas of a thermal power plant by using the absorption system, comprising the following steps:
s1: planning the scale of a flue gas carbon dioxide absorption system according to the surrounding land use condition of the thermal power plant, and determining the flow rate of flue gas entering the absorption system;
s2: according to the capacity of the thermal power plant unit, a device for preparing caustic soda by electrolyzing saline water or a purchased caustic soda preparation solution supply absorption system is arranged;
s3: according to the smoke discharge condition of a chimney of a thermal power plant, designing a clean smoke gas connecting pipeline to be connected to a carbon dioxide reaction absorption tower through a route, and sending the carbon dioxide in the smoke gas and a sodium hydroxide solution into a microalgae cultivation water tank or a solution storage tank for storage;
s4: and a system control program is set, and a control unit is used for monitoring the parameters of temperature, pressure, carbon dioxide concentration, nitrogen concentration, air pressure, sodium bicarbonate solution concentration, sodium hydroxide solution concentration and solution flow of each part of the system and accurately controlling the parameters in real time.
S5: and a carbon dioxide concentration monitoring device is arranged at the top of the carbon dioxide reaction absorption tower, when the concentration of carbon dioxide at the top is lower than a certain numerical value, an empty discharge valve of the led-out carbon dioxide recovery pipeline is opened, and the residual flue gas is discharged to a chimney of a thermal power plant or directly discharged to the air.
Further, in S3, the concentration of the sodium hydroxide solution input into the carbon dioxide reaction absorption tower by the sodium hydroxide feeding system is 10% -100%, and the concentration of the sodium bicarbonate solution sent into the microalgae cultivation water tank or the solution storage tank is 5% -80%.
Compared with the prior art, the invention has at least the following beneficial technical effects:
by utilizing the carbon dioxide absorption tower, the sodium hydroxide solution and the flue gas are fully mixed and reacted in the tower by any one or combination of the suspension jet flow, the jet flow immersed in the solution and the mixing mode of the flue gas and the sodium hydroxide solution through the jet flow guide air extractor, and the generated reaction liquid falls to the bottom of the absorption tower, so that the mixing and reaction of the high-efficiency carbon dioxide and the sodium hydroxide solution are realized. The low-price sodium hydroxide solution is utilized to realize high-efficiency carbon dioxide absorption, namely carbon capture.
Furthermore, the sodium hydroxide solution is produced at low price by electrolyzing the sodium chloride brine by utilizing the peak-adjusting frequency-modulating surplus electric power of the thermal power plant, and the sodium hydroxide solution is produced by electrolyzing the sodium chloride brine by utilizing the peak-adjusting frequency-modulating surplus electric power of the thermal power plant, so that the production cost is reduced, and the peak-adjusting frequency-modulating of the thermal power plant can be assisted.
Further, the final product sodium bicarbonate solution is used for cultivating microalgae, and final carbon capture and carbon sequestration are realized.
Furthermore, a carbon dioxide recovery pipeline is led out from the top of the carbon dioxide reaction absorption tower and connected to a boiler clean flue gas connecting pipeline, so that carbon dioxide gas which does not participate in reaction absorption escape returns to the clean flue gas connecting pipeline and reenters the reaction absorption tower for further reaction absorption.
Further, a carbon dioxide concentration monitoring device is arranged at the top of the carbon dioxide reaction absorption tower, when the concentration of carbon dioxide at the top is lower than a set value, an air discharge valve of a led-out carbon dioxide recovery pipeline is opened, and residual flue gas is discharged to a boiler chimney or directly discharged to the air.
According to the method, carbon dioxide is absorbed by using sodium hydroxide solution absorption liquid according to the flow rate of flue gas entering an absorption system; the chemical substance types of the absorption liquid and the specific absorption method and process route are determined, the carbon dioxide absorption efficiency is improved, and the carbon dioxide absorption cost is reduced.
Drawings
FIG. 1 is a schematic view of embodiment 1;
FIG. 2 is a schematic view of embodiment 2;
FIG. 3 is a schematic flow chart of example 4.
In the drawings: 1. carbon dioxide reaction absorption tower, 2, sodium hydroxide feeding system, 3, solution storage tank, 4, boiler clean flue gas connecting pipeline, 5, first gas dryer, 6, first pressure control valve, 7, first stop control valve, 8, reaction liquid discharging pipeline, 9, feeding pump, 10, thermal power plant, 12, microalgae cultivation water tank, 13, absorption liquid supply pipeline, 17, flue gas supply pipeline, 20, carbon dioxide recovery pipeline, 23, second stop control valve, 24, second gas dryer, 25, third stop control valve, 26, second pressure control valve, 27, NaHCO3A supply pipeline 28, an electrolytic tank for preparing caustic soda by electrolyzing saline water.
Detailed Description
In order to make the objects and technical solutions of the present invention clearer and easier to understand. The present invention will be described in further detail with reference to the following drawings and examples, wherein the specific examples are provided for illustrative purposes only and are not intended to limit the present invention.
In the description of the present invention, it is to be understood that the terms "center", "longitudinal", "lateral", "up", "down", "front", "back", "left", "right", "vertical", "horizontal", "top", "bottom", "inner", "outer", and the like, indicate orientations or positional relationships based on those shown in the drawings, and are used only for convenience in describing the present invention and for simplicity in description, and do not indicate or imply that the referenced devices or elements must have a particular orientation, be constructed and operated in a particular orientation, and thus, are not to be construed as limiting the present invention. Furthermore, the terms "first", "second" and "first" are used for descriptive purposes only and are not to be construed as indicating or implying relative importance or implicitly indicating the number of technical features indicated. Thus, a feature defined as "first" or "second" may explicitly or implicitly include one or more of that feature. In the description of the present invention, "a plurality" means two or more unless otherwise specified. In the description of the present invention, it should be noted that, unless otherwise explicitly specified or limited, the terms "mounted," "connected," and "connected" are to be construed broadly, e.g., as meaning either a fixed connection, a removable connection, or an integral connection; can be mechanically or electrically connected; they may be connected directly or indirectly through intervening media, or they may be interconnected between two elements. The specific meanings of the above terms in the present invention can be understood in specific cases to those skilled in the art.
Example 1
Referring to fig. 1, the flue gas caustic soda solution carbon dioxide absorption system of the thermal power plant comprises a boiler of the thermal power plant, a steam turbine, a generator and its accessories, a boiler clean flue gas connecting pipeline 4 of the thermal power plant 10 is connected to a tower bottom gas pipeline in a carbon dioxide reaction absorption tower 1 through a flue gas supply pipeline 17, a flue gas inlet is formed on the tower bottom gas pipeline, and a liquid inlet for inputting a sodium hydroxide solution is formed at the upper part of the carbon dioxide reaction absorption tower 1; the flue gas supply pipeline 17 is sequentially provided with a first gas drier 5, a first pressure control valve 6 and a first stop control valve 7 along the flow direction of the clean flue gas, and the carbon dioxide reaction absorption tower 1 is connected with the sodium hydroxide feeding system 2 through an absorption liquid supply pipeline 13; the absorption liquid supply pipeline 13 is provided with a feed pump 9 and a second stop control valve 23, and the carbon dioxide reaction absorption tower 1 is provided with a third stop control valve 25 through a reaction liquid discharge pipeline 8 and a reaction liquid discharge pipeline 8 of the solution storage tank 3.
The carbon dioxide reaction absorption tower 1 is connected with the flue gas supply pipeline 17 through a carbon dioxide recovery pipeline 20, and a second gas dryer 24 and a second pressure control valve 26 are sequentially arranged on the carbon dioxide recovery pipeline 20 along the medium conveying direction, so that the carbon dioxide gas which does not participate in the reaction absorption escape returns to the clean flue gas connection pipeline and enters the reaction absorption tower again for further reaction absorption.
The bottom of the carbon dioxide reaction absorption tower 1 is sodium hydroxide solution, and the flue gas is introduced into the solution from the bottom of the solution to react with the solution; or the flue gas enters the tower from the bottom, the sodium hydroxide solution enters the tower from the upper part of the tower through the atomizing nozzle, and the atomized solution droplets are mixed and reacted with the flue gas from top to bottom in a convection manner to generate the sodium bicarbonate solution.
The boiler clean flue gas is subjected to any one or combination of modes of suspended jet flow, jet flow immersed in the solution, mixing of the flue gas and the sodium hydroxide solution through a jet flow guide air extractor, aeration of the flue gas from an aeration pipe at the bottom of the solution and the like, so that the flue gas, the sodium hydroxide solution and the reaction liquid are fully mixed and reacted.
The bottom of the carbon dioxide reaction absorption tower 1 is provided with a sodium hydroxide solution or a reaction solution, the sodium hydroxide solution is fully mixed and reacted with the flue gas in any one or combination of modes of suspension jet flow, jet flow immersed in the solution, mixing of the flue gas and the sodium hydroxide solution through a jet flow guide air extractor and the like, the concentration of the sodium hydroxide solution is 10%, and the concentration range of the sodium bicarbonate solution is 5%.
The top of the carbon dioxide reaction absorption tower 1 is provided with a carbon dioxide concentration monitoring device, when the carbon dioxide concentration at the top of the carbon dioxide reaction absorption tower 1 is lower than a set value, an air discharge valve of the led-out carbon dioxide recovery pipeline 20 is opened, and the residual flue gas is discharged to a boiler chimney or directly discharged to the air.
Preferably, the carbon dioxide absorption system further comprises a parameter monitoring and controlling unit for monitoring and controlling the temperature, pressure, carbon dioxide concentration, nitrogen concentration, air pressure, sodium hydroxide solution concentration, reaction solution concentration, solution flow and other parameters of each part of the system, and the parameter monitoring and controlling unit is used for realizing real-time monitoring and accurate control of the parameters.
Example 2
Referring to fig. 2, the flue gas caustic soda solution carbon dioxide absorption system of the thermal power plant comprises a boiler, a steam turbine, a generator and its accessories of the thermal power plant, a boiler clean flue gas connecting pipeline 4 of the thermal power plant 10 is connected to a carbon dioxide reaction absorption tower 1 through a flue gas supply pipeline 17, a flue gas inlet connected to a tower bottom gas transmission pipeline is arranged at the lower part of the carbon dioxide reaction absorption tower 1, and an inlet for inputting sodium hydroxide solution is arranged at the upper part of the carbon dioxide reaction absorption tower 1A liquid port; a first gas drier 5, a first pressure control valve 6 and a first stop control valve 7 are sequentially arranged on the flue gas supply pipeline 17 along the flow direction of the purified flue gas, and the carbon dioxide reaction absorption tower 1 is connected with the sodium hydroxide feeding system 2 through an absorption liquid supply pipeline 13; the absorption liquid supply pipeline 13 is provided with a feed pump 9 and a second stop control valve 23, and the carbon dioxide reaction absorption tower 1 passes through NaHCO3The supply pipeline 27 is connected with the microalgae cultivation water tank 12, the reaction liquid discharge pipeline 8 is provided with a third stop control valve 25, the carbon supplement amount required in the culture solution is met, the pH value of the water tank solution is adjusted, the sodium bicarbonate solution is supplemented to the microalgae cultivation water tank, the absorption of the microalgae on the bicarbonate ions is met, and therefore the carbon supplement requirement of the microalgae is met. The reaction liquid discharge line 8 is provided with a third stop control valve 25.
The carbon dioxide reaction absorption tower 1 is connected with the flue gas supply pipeline 17 through a carbon dioxide recovery pipeline 20, and a second gas dryer 24 and a second pressure control valve 26 are sequentially arranged on the carbon dioxide recovery pipeline 20 along the medium conveying direction, so that the carbon dioxide gas which does not participate in the reaction absorption escape returns to the clean flue gas connection pipeline and enters the reaction absorption tower again for further reaction absorption.
The bottom of the carbon dioxide reaction absorption tower 1 is sodium hydroxide solution or reaction solution, the concentration of the sodium hydroxide solution is 45%, and the concentration range of the sodium bicarbonate solution is 42%.
The top of the carbon dioxide reaction absorption tower 1 is provided with a carbon dioxide concentration monitoring device, when the carbon dioxide concentration at the top of the carbon dioxide reaction absorption tower 1 is lower than a set value, an air discharge valve of the led-out carbon dioxide recovery pipeline 20 is opened, and the residual flue gas is discharged to a boiler chimney or directly discharged to the air.
The boiler clean flue gas is subjected to any one or combination of modes of suspended jet flow, jet flow immersed in the solution, mixing of the flue gas and the sodium hydroxide solution through a jet flow guide air extractor, aeration of the flue gas from an aeration pipe at the bottom of the solution and the like, so that the flue gas, the sodium hydroxide solution and the reaction liquid are fully mixed and reacted.
The sodium hydroxide solution enters the carbon dioxide reaction absorption tower 1 from the upper part through an atomizing nozzle or a spray nozzle, and the atomized or sprayed sodium hydroxide solution droplets are mixed and reacted with the flue gas from top to bottom in a convection manner, so that the generated reaction liquid falls into the bottom of the carbon dioxide reaction absorption tower 1.
Preferably, the carbon dioxide absorption system further comprises a parameter monitoring and controlling unit for monitoring and controlling the temperature, pressure, carbon dioxide concentration, nitrogen concentration, air pressure, sodium hydroxide solution concentration, reaction solution concentration, solution flow and other parameters of each part of the system, and the parameter monitoring and controlling unit is used for realizing real-time monitoring and accurate control of the parameters.
The sodium hydroxide solution comes from an electrolytic tank 11 for preparing caustic soda by electrolyzing brine in a thermal power plant; the power used by the electrolytic tank 11 for preparing caustic soda by electrolyzing saline water is the peak-load and frequency-modulation surplus power of a thermal power plant. Hydrogen generated by an electrolytic tank for preparing caustic soda by electrolyzing brine is sent to a boiler for afterburning or a steel cylinder for storage or an external pipeline for delivery, and the generated chlorine is compressed by the steel cylinder for storage and is sold for external use.
Example 3
Referring to fig. 2, the flue gas caustic soda solution carbon dioxide absorption system of the thermal power plant comprises a boiler of the thermal power plant, a steam turbine, a generator and its accessories, wherein a clean flue gas connection pipeline 4 of the boiler of the thermal power plant is connected to a carbon dioxide reaction absorption tower 1 through a flue gas supply pipeline 17, a flue gas inlet connected with a tower bottom gas transmission pipeline is arranged at the lower part of the carbon dioxide reaction absorption tower 1, and a liquid inlet for inputting a sodium hydroxide solution is arranged at the upper part of the carbon dioxide reaction absorption tower; a first gas drier 5, a first pressure control valve 6 and a first stop control valve 7 are sequentially arranged on the flue gas supply pipeline 17 along the flow direction of the purified flue gas, and the carbon dioxide reaction absorption tower 1 is connected with a sodium hydroxide feeding system 2 through an absorption liquid supply pipeline 13; the absorption liquid supply pipeline 13 is provided with a feed pump 9 and a second stop control valve 23, and the carbon dioxide reaction absorption tower 1 passes through NaHCO3The supply pipeline 27 is connected with the microalgae cultivation water tank 12, the reaction liquid discharge pipeline 8 is provided with a third stop control valve 25, the carbon supplement amount required in the culture solution is met, the pH value of the water tank solution is adjusted, the sodium bicarbonate solution is supplemented to the microalgae cultivation water tank, the absorption of the microalgae on the bicarbonate ions is met, and therefore the carbon supplement requirement of the microalgae is met. The reaction liquid discharge line 8 is provided with a third stop control valve 25.
The carbon dioxide reaction absorption tower 1 is connected with the flue gas supply pipeline 17 through a carbon dioxide recovery pipeline 20, and a second gas dryer 24 and a second pressure control valve 26 are sequentially arranged on the carbon dioxide recovery pipeline 20 along the medium conveying direction, so that the carbon dioxide gas which does not participate in the reaction absorption escape returns to the clean flue gas connection pipeline and enters the reaction absorption tower again for further reaction absorption.
The top of the carbon dioxide reaction absorption tower 1 is provided with a carbon dioxide concentration monitoring device, when the carbon dioxide concentration at the top of the carbon dioxide reaction absorption tower 1 is lower than a set value, an air discharge valve of the led-out carbon dioxide recovery pipeline 20 is opened, and the residual flue gas is discharged to a boiler chimney or directly discharged to the air.
The bottom of the carbon dioxide reaction absorption tower 1 is sodium hydroxide solution or reaction solution, the concentration of the sodium hydroxide solution is 100%, and the concentration range of the sodium bicarbonate solution is 85%.
The boiler clean flue gas is aerated by an aeration pipe at the bottom of the solution, so that the flue gas, the sodium hydroxide solution and the reaction liquid are fully mixed and reacted. The sodium hydroxide solution enters the carbon dioxide reaction absorption tower 1 from the upper part through an atomizing nozzle or a spray nozzle, and the atomized or sprayed sodium hydroxide solution droplets are mixed and reacted with the flue gas from top to bottom in a convection manner, so that the generated reaction liquid falls into the bottom of the carbon dioxide reaction absorption tower 1.
Preferably, the carbon dioxide absorption system further comprises a parameter monitoring and controlling unit for monitoring and controlling the temperature, pressure, carbon dioxide concentration, nitrogen concentration, air pressure, sodium hydroxide solution concentration, reaction solution concentration, solution flow and other parameters of each part of the system, and the parameter monitoring and controlling unit is used for realizing real-time monitoring and accurate control of the parameters.
The sodium hydroxide solution comes from an electrolytic tank 11 for preparing caustic soda by electrolyzing brine in a thermal power plant; the power used by the electrolytic tank 11 for preparing caustic soda by electrolyzing saline water is the peak-load and frequency-modulation surplus power of a thermal power plant. Hydrogen generated by an electrolytic tank for preparing caustic soda by electrolyzing brine is sent to a boiler for afterburning or a steel cylinder for storage or an external pipeline for delivery, and the generated chlorine is compressed by the steel cylinder for storage and is sold for external use.
Example 4
As shown in fig. 3, the method for absorbing carbon dioxide from flue gas based on the system of embodiment 1, embodiment 2 or embodiment 3 includes the following steps:
s1: planning and designing the scale of a flue gas carbon dioxide absorption system according to the surrounding land use condition of a thermal power plant, and particularly determining the flow rate of flue gas entering the absorption system;
s2: according to the condition of a thermal power plant unit (such as unit capacity), a device for preparing caustic soda by electrolyzing saline water or a system for supplying a purchased caustic soda preparation solution to a flue gas carbon dioxide absorption system is arranged;
s3: designing a clean flue gas connecting pipeline route to be connected to a carbon dioxide absorption tower according to the smoke discharging condition of a chimney of a thermal power plant, reacting carbon dioxide in flue gas with a sodium hydroxide solution in a carbon dioxide reaction absorption tower 1 to generate a sodium bicarbonate solution, and sending the sodium bicarbonate solution into a microalgae cultivation water tank 12 or a solution storage tank 3 for storage;
s4: and a system control program is set, and the system control program is used for monitoring and controlling the parameters of the temperature, the pressure, the carbon dioxide concentration, the nitrogen concentration, the air pressure, the sodium bicarbonate solution concentration, the sodium hydroxide solution concentration, the solution flow and the like of all parts of the system, and is used for realizing real-time monitoring and accurate control of the parameters.
S5: when the concentration of the carbon dioxide at the top is lower than a set value, an empty discharge valve of the carbon dioxide recovery pipeline 20 is opened, and the residual flue gas is discharged to a chimney of a thermal power plant or directly discharged to the air.
The embodiments in the present description are described in a progressive manner, each embodiment focuses on differences from other embodiments, and the same and similar parts among the embodiments are referred to each other.
The boiler flue gas carbon dioxide absorption system and the boiler flue gas carbon dioxide absorption method provided by the invention are described in detail above. The principles and embodiments of the present invention are explained herein using specific examples, which are presented only to assist in understanding the method and its core concepts. It should be noted that, for those skilled in the art, it is possible to make various improvements and modifications to the present invention without departing from the principle of the present invention, and those improvements and modifications also fall within the scope of the claims of the present invention.
Claims (10)
1. The system is characterized by comprising a carbon dioxide reaction absorption tower (1), a sodium hydroxide feeding system (2) and a sodium bicarbonate solution supply pipeline (13), wherein the lower part of the carbon dioxide reaction absorption tower (1) is provided with a flue gas inlet connected with a tower bottom gas pipeline, and the upper part of the carbon dioxide reaction absorption tower is provided with a liquid inlet used for inputting a sodium hydroxide solution; the flue gas entry is connected to the clean flue gas connecting line of boiler (4) of thermal power plant, the inlet passes through absorption liquid and supplies liquid pipeline (13) and sodium hydroxide charge-in system (2) to be connected, carbon dioxide reaction absorption tower (1) is connected through reaction liquid discharge pipeline (8) and solution holding vessel (3).
2. The carbon dioxide absorption system for the thermal power plant flue gas caustic soda solution is characterized in that the sodium hydroxide feeding system (2) is connected with an electrolytic tank (11) for electrolyzing brine to prepare caustic soda in the thermal power plant, and the electrolytic tank (11) for preparing caustic soda by electrolyzing brine is powered by peak-adjusting frequency-adjusting surplus power of the thermal power plant.
3. The carbon dioxide absorption system for the thermal power plant flue gas caustic soda solution is characterized in that a hydrogen outlet of the electrolytic brine caustic soda electrolytic tank (11) is fed into a boiler for afterburning or a steel cylinder for storage or an external pipeline for transportation through a pipeline, and a chlorine outlet of the electrolytic brine caustic soda electrolytic tank (11) is connected to a compression steel cylinder.
4. The boiler flue gas carbon dioxide absorption system according to claim 1, wherein the bottom of the carbon dioxide reaction absorption tower (1) is a sodium hydroxide solution or a reaction solution, the boiler clean flue gas is subjected to any one or combination of suspension jet, jet immersed in the solution, mixing of the flue gas and the sodium hydroxide solution through an air jet guide air extractor, and aeration of the flue gas from an aeration pipe at the bottom of the solution, so as to realize sufficient mixing and reaction of the flue gas, the sodium hydroxide solution and the reaction solution.
5. The carbon dioxide absorption system for the thermal power plant flue gas caustic soda solution according to claim 1, wherein the sodium hydroxide solution is injected from the liquid inlet in any one or combination of a suspension jet mode, a jet mode in which the solution is immersed, and a mixing mode in which the flue gas and the sodium hydroxide solution pass through a jet flow guide air extractor.
6. The carbon dioxide absorption system for the thermal power plant flue gas caustic soda solution is characterized in that a spraying unit and/or an absorption liquid jet nozzle (22) is arranged in the carbon dioxide reaction absorption tower (1), and the spraying unit and/or the absorption liquid jet nozzle (22) is connected with the sodium hydroxide feeding system (2) through an absorption liquid supply pipeline (13).
7. The system for absorbing the carbon dioxide in the caustic soda solution in flue gas of the thermal power plant as claimed in claim 1, wherein a carbon dioxide recovery pipeline (20) is led out from the top of the carbon dioxide reaction absorption tower (1), the carbon dioxide recovery pipeline (20) is connected to a boiler clean flue gas connecting pipeline (4), and a stop control valve and a gas dryer are arranged on the carbon dioxide recovery pipeline (20).
8. The carbon dioxide absorption system for the thermal power plant flue gas caustic soda solution according to claim 1, characterized in that a carbon dioxide concentration monitoring device is arranged at the top of the carbon dioxide reaction absorption tower (1).
9. A thermal power plant flue gas carbon dioxide absorption method using the absorption system according to any one of claims 1 to 8, comprising the steps of:
s1: planning the scale of a flue gas carbon dioxide absorption system according to the surrounding land use condition of the thermal power plant, and determining the flow rate of flue gas entering the absorption system;
s2: according to the capacity of the thermal power plant unit, a device for preparing caustic soda by electrolyzing saline water or a purchased caustic soda preparation solution supply absorption system is arranged;
s3: according to the smoke discharge condition of a chimney of a thermal power plant, a clean smoke gas connecting pipeline is designed to be connected to a carbon dioxide reaction absorption tower (1) in a routing mode, carbon dioxide in smoke gas reacts with a sodium hydroxide solution to generate a sodium bicarbonate solution, and the sodium bicarbonate solution is sent to a microalgae cultivation water tank (12) or a solution storage tank (3) for storage;
s4: a system control program is set, and a control unit is used for monitoring the parameters of temperature, pressure, carbon dioxide concentration, nitrogen concentration, air pressure, sodium bicarbonate solution concentration, sodium hydroxide solution concentration and solution flow of each part of the system, so as to realize real-time monitoring and accurate control of the parameters;
s5: the carbon dioxide reaction absorption tower (1) top sets up carbon dioxide concentration monitoring devices, and when top carbon dioxide concentration was less than certain numerical value, the empty discharge valve of carbon dioxide recovery pipeline (20) of drawing forth opened, discharges remaining flue gas to thermal power plant chimney or direct empty discharge.
10. The method for absorbing carbon dioxide from flue gas of a thermal power plant according to claim 9, wherein in S3, the sodium hydroxide solution fed from the sodium hydroxide feeding system (2) to the carbon dioxide reaction absorption tower (1) has a concentration of 10% to 100%, and the sodium bicarbonate solution fed to the microalgae cultivation water tank (12) or the solution storage tank (3) has a concentration of 5% to 80%.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202110160831.5A CN112957902A (en) | 2021-02-05 | 2021-02-05 | System and method for absorbing carbon dioxide in thermal power plant flue gas caustic soda solution |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202110160831.5A CN112957902A (en) | 2021-02-05 | 2021-02-05 | System and method for absorbing carbon dioxide in thermal power plant flue gas caustic soda solution |
Publications (1)
Publication Number | Publication Date |
---|---|
CN112957902A true CN112957902A (en) | 2021-06-15 |
Family
ID=76274402
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202110160831.5A Pending CN112957902A (en) | 2021-02-05 | 2021-02-05 | System and method for absorbing carbon dioxide in thermal power plant flue gas caustic soda solution |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN112957902A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113502485A (en) * | 2021-07-12 | 2021-10-15 | 中国华能集团清洁能源技术研究院有限公司 | System and method for producing hydrogen by electrolyzing seawater in thermal power plant |
CN114191965A (en) * | 2021-12-16 | 2022-03-18 | 北京博奇电力科技有限公司 | Automatic many bed layers of continuity decarbonization system of regulation |
CN115228259A (en) * | 2022-07-15 | 2022-10-25 | 江西新节氢能源科技有限公司 | Device and method for extracting carbon dioxide and distilled water in boiler flue gas |
Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2011129707A1 (en) * | 2010-04-15 | 2011-10-20 | Enpro As | Co2 scrubber/separator using a cyclic carbonator for controlled carbonate/bicarbonate production |
CN103432881A (en) * | 2013-03-18 | 2013-12-11 | 武汉工程大学 | Synthesis of novel energy by using sulfur dioxide or carbon dioxide as raw materials |
CN104190233A (en) * | 2014-09-09 | 2014-12-10 | 东南大学 | Undershoot jet-flow smoke desulphurization device |
CN106061583A (en) * | 2014-01-17 | 2016-10-26 | 斯凯约尼克公司 | Acid gas removal from a gaseous stream |
CN109012110A (en) * | 2018-06-28 | 2018-12-18 | 北京科技大学 | A method of carbon dioxide is trapped using sodium hydroxide and sodium carbonate |
CN109513323A (en) * | 2018-12-19 | 2019-03-26 | 伟明环保设备有限公司 | A kind of real-time monitoring for wet process depickling and energy-saving system and method |
-
2021
- 2021-02-05 CN CN202110160831.5A patent/CN112957902A/en active Pending
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2011129707A1 (en) * | 2010-04-15 | 2011-10-20 | Enpro As | Co2 scrubber/separator using a cyclic carbonator for controlled carbonate/bicarbonate production |
CN103432881A (en) * | 2013-03-18 | 2013-12-11 | 武汉工程大学 | Synthesis of novel energy by using sulfur dioxide or carbon dioxide as raw materials |
CN106061583A (en) * | 2014-01-17 | 2016-10-26 | 斯凯约尼克公司 | Acid gas removal from a gaseous stream |
CN104190233A (en) * | 2014-09-09 | 2014-12-10 | 东南大学 | Undershoot jet-flow smoke desulphurization device |
CN109012110A (en) * | 2018-06-28 | 2018-12-18 | 北京科技大学 | A method of carbon dioxide is trapped using sodium hydroxide and sodium carbonate |
CN109513323A (en) * | 2018-12-19 | 2019-03-26 | 伟明环保设备有限公司 | A kind of real-time monitoring for wet process depickling and energy-saving system and method |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113502485A (en) * | 2021-07-12 | 2021-10-15 | 中国华能集团清洁能源技术研究院有限公司 | System and method for producing hydrogen by electrolyzing seawater in thermal power plant |
CN114191965A (en) * | 2021-12-16 | 2022-03-18 | 北京博奇电力科技有限公司 | Automatic many bed layers of continuity decarbonization system of regulation |
CN114191965B (en) * | 2021-12-16 | 2022-11-01 | 北京博奇电力科技有限公司 | Automatic many bed layers of continuity decarbonization system of regulation |
CN115228259A (en) * | 2022-07-15 | 2022-10-25 | 江西新节氢能源科技有限公司 | Device and method for extracting carbon dioxide and distilled water in boiler flue gas |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN112957902A (en) | System and method for absorbing carbon dioxide in thermal power plant flue gas caustic soda solution | |
CN101543723B (en) | Process for processing nitrogen-oxide waste gas containing acidic gas | |
CN103274549A (en) | Cycle closed type filler-free high-efficiency ammonia nitrogen removing and nutrient recovery device of biogas slurry | |
CN111166915A (en) | Wheeled hypochlorous acid fog-making disinfection equipment | |
CN108816037A (en) | A kind of microbe treatment system and processing method for farm's exhaust gas | |
CN112957892B (en) | System and method for absorbing carbon dioxide in boiler flue gas | |
CN208939084U (en) | A kind of fuel cell system using online hydrogen supply based on water self-loopa | |
CN212316133U (en) | Integrated indigenous probiotic propagation system convenient to move | |
CN214715653U (en) | Carbon dioxide absorption reactor utilizing gas-liquid jet flow mixing | |
CN117085615A (en) | Underwater bubble discharge plasma nitrogen fixation device and method | |
CN208786130U (en) | A kind of arsine/phosphine emission-control equipment | |
CN105771554A (en) | In-situ denitrification method of ammonia-containing exhaust gas and denitrification device used in same | |
CN215404571U (en) | System for utilize flue gas electrochemistry of thermal power plant to make ammonia | |
CN218353768U (en) | Water and fertilizer integrated irrigation system based on hydrogen | |
CN108854487A (en) | A kind of arsine/phosphine emission-control equipment and arsine/phosphine waste gas processing method | |
CN201694833U (en) | Portable chlorine dioxide reacting apparatus | |
CN214715654U (en) | Reaction device for absorbing carbon dioxide by mixing absorption liquid jet with flue gas | |
CN210278756U (en) | Efficient SOx/NOx control device | |
CN211078529U (en) | Ammonia water pervaporation system without waste water generation | |
CN113087085A (en) | For military use disinfection electrolysis water spray truck that disinfects | |
CN208975511U (en) | A kind of desulfurization wastewater zero-discharge treatment system based on UTILIZATION OF VESIDUAL HEAT IN | |
CN201969386U (en) | Decomposer for ozone tail gas of gas-water mixing pump | |
CN111228993A (en) | Method and system for flue gas denitration by using chlorine dioxide and spray tower | |
CN205076931U (en) | No wastewater discharge's wet flue gas desulfurization system | |
CN214715594U (en) | Boiler waste gas treatment equipment |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination |