CN1052430C - Polyamine method for removing carbon dioxide and sulfide in gas - Google Patents

Polyamine method for removing carbon dioxide and sulfide in gas Download PDF

Info

Publication number
CN1052430C
CN1052430C CN93110579A CN93110579A CN1052430C CN 1052430 C CN1052430 C CN 1052430C CN 93110579 A CN93110579 A CN 93110579A CN 93110579 A CN93110579 A CN 93110579A CN 1052430 C CN1052430 C CN 1052430C
Authority
CN
China
Prior art keywords
solution
gas
weight
mdea
sulfide
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.)
Expired - Fee Related
Application number
CN93110579A
Other languages
Chinese (zh)
Other versions
CN1091332A (en
Inventor
张学模
过赘扶
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
INST OF NANJING CHEMICAL INDUS
Original Assignee
INST OF NANJING CHEMICAL INDUS
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by INST OF NANJING CHEMICAL INDUS filed Critical INST OF NANJING CHEMICAL INDUS
Priority to CN93110579A priority Critical patent/CN1052430C/en
Publication of CN1091332A publication Critical patent/CN1091332A/en
Application granted granted Critical
Publication of CN1052430C publication Critical patent/CN1052430C/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Images

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/40Capture or disposal of greenhouse gases of CO2

Landscapes

  • Gas Separation By Absorption (AREA)
  • Treating Waste Gases (AREA)

Abstract

The invention relates to a method for removing carbon dioxide and sulfide in mixed gas of synthetic ammonia, methanol, hydrogen production raw material gas, city gas, natural gas and the like by adding polyamine solution consisting of two secondary amines into N-methyldiethanolamine solution. It has the characteristics of high purification degree, low energy consumption of regenerative heat and the like.
The solution of the invention comprises three groups of components: the N-methyldiethanolamine accounts for 20 to 60 percent by weight. Suitable sulfur-free gases are: 1-5% by weight of piperazine and 1-10% by weight of diethanolamine; suitable sulfur-containing gases are two groups: 0.1-10% by weight of N-methyl-ethanolamine, 1-10% by weight of diethanolamine; 0.1-10% by weight of N-methyl-ethanolamine, 1-5% by weight of piperazine.

Description

Polyamine method for removing carbon dioxide and sulfide in gas
The present invention belongs to the field of separation technology, and relates to the field of gas separating technology by chemical-physical absorption. The invention relates to a method for removing carbon dioxide and sulfide from acid mixed gas by using polyamine solution of composite N-Methyldiethanolamine (MDEA) containing double activators.
The N-methyldiethanolamine solution is widely applied to the removal of carbon dioxide and sulfide from mixed gas of synthesis ammonia, methanol, hydrogen production raw gas, city gas, natural gas and the like. General N-methyldiethanolamineCalled MDEA) solution with a gas mixture under pressure, CO2And the sulfide is absorbed by the solution, after which the solution is subjected to atmospheric desorption and steam stripping to cause CO to be formed2And the sulfide is desorbed from the MDEA solution. Absorption and desorption of CO with a simple MDEA solution2Low speed, high heat consumption, CO2The purification degree is low. Therefore, various catalysts or activators are added into the MDEA solution in foreign countries to overcome the defects.
Patent DE1,904,428(70 years) reports the addition of N-methyl-ethanolamine (MMEA) as activator. The addition of diazocyclohexane (piperazine) as activator is reported in patent DE2,551,717 (77). The solutions of these patents have fast absorption and desorption speed, low heat consumption and high purification degree. Has been applied to dozens of large-scale industrial devices abroad. However, the method is to add an activator to MDEA solution only and singly to improve the absorption of CO into the solution2The mass transfer rate coefficient of (1). While the latter patent absorbs more rapidly than the former patent, the latter patent doesDue to the low boiling point, the partial pressure of steam is high. Therefore, in process applications, a washing system is required to be added, otherwise the loss is high, and in addition, the concentration of the washing system in the solution cannot be too high, otherwise the carbon steel can be corroded.
In the invention, besides piperazine or MMEA is respectively added into MDEA solution, Diethanolamine (DEA) is also added to form a novel composite activator. The components play the following roles in the polyamine process solution:
1. N-Methyldiethanolamine (MDEA); it is a tertiary amine. Absorption of CO2The carbonate is generated after the reaction, so that the heating regeneration can be carried out, and the steam consumption is low and is only half of that of the primary amine and the secondary amine. Primary, secondary amine and CO2Generates rather stable carbamate, and MDEA has high thermal degradation resistance and chemical degradation resistance; the corrosion to carbon steel is basically avoided: the vapor pressure of the solution is low, so that no obvious vaporization loss exists when a high-concentration solution of 50 percent is used; nonpolar gases such as hydrogen, nitrogen, methanol and higher hydrocarbons have a relatively low solubility in solution. The loss of cleaned gas is low.
MDEA has a special isothermal solubility curve (see figure one). For comparison, a 25% Monoethanolamine (MEA) solution and physical solution were usedCO of Propylene Carbonate (PC) as agent2Solubility is also shown in figure one. As can be seen from the figure, CO2The partial pressure is reduced from 5 bar to 1 bar, so that the equilibrium load of the MDEA solution is 57NM3/M3The solution dropped to 27NM3/M3Release of 30NM from solution3CO2/M3And (3) solution. The corresponding numbers for MEA and PC solutions are 11 and 9.8NM, respectively3/M3And (3) solution. The effect of flash regeneration on MDEA solution is much better than MEAand PC solutions. Can be designed according to the principleTwo-stage absorption, one-stage normal-pressure desorption and one-stage steam regeneration process for reducing CO2The total heat energy consumption (total removal) is shown in figure two. Can also design an absorption-normal pressure desorption simple flow path to remove partial CO2(half-threshing) see figure three.
As seen from the first figure: the curve for MDEA lies between the chemical (MEA) and Physical (PC) absorption, and is therefore said to be absorbing CO2It has chemical and physical absorption properties or is called chemical and physical absorbent. But has the disadvantage of only being indirectly connected to CO2The reaction is also very slow.
2. Activator-1, p-diazacyclo (piperazine). It is a secondary amine, and the absorption of CO is greatly improved after the addition of it in MDEA solution2The reaction rate of (2). But its boiling point is low (148 deg.C), and it is easy to volatilize. And the addition concentration must not be too high, which would cause corrosion of the carbon steel. Furthermore, it has a low toxicity.
3. Activator-2, N-methyl-ethanolamine (MMEA). Is also a secondary amine, and its addition can also increase MDEA and CO2The speed of the reaction. The rate of increase was slightly lower for the same concentration added than for piperazine. And it is very effective for absorbing sulfur-oxygen-Carbon (COS).
4. Activator-3, Diethanolamine (DEA), which is also a secondary amine, the addition of which can accelerate both MEDA and CO2Besides the reaction speed, the surface CO of the MDEA solution is reduced2The effect of the partial pressure.
The three activators can be combined into the following groups of solutions: group A adds DEA (1+3) to diazacyclo; b group MMEA adds DEA (2+3), C group adds three groups of compound activators such as MMEA (1+2) to diazacyclo. Group A masterTo be administeredFor gases containing no organic sulfur, such as COS, etc., groups B and C for gases containing organic sulfur or CO for regenerated gas2Has special application. Experiments prove that the addition of the second activator not only can not offset the original activation effect in the MDEA solution, but also can play a mutual promotion role. The absorption speed of the composite activator is improved by about 10-20% compared with that of a single activator. In addition, the group A can reduce the content of the activator-1 to the diazacyclo, thereby reducing the loss caused by high steam partial pressure and the corrosion to the carbon steel caused by high concentration.
The structural formula of the N-methyldiethanolamine is as follows:
Figure C9311057900061
abbreviation R2CH3The reaction process of NN-methyldiethanolamine and carbon dioxide is as follows: ………………(2)(1)+(2) … … … (3) the whole reaction is controlled by (1), (1) is hydration reaction, at 25 deg.C, the reaction rate constant KOH is 104Liter/mol/sec. [ OH]]=10-5~10-3Mols/liter. Therefore, the reaction (3) is a very slow reaction.
When adding activator secondary amine in MDEA solution, absorbing CO2The reaction of (3) was carried out according to the following scheme. …(5)(4)+(5): ……(6)
Equation (6) is controlled by equation (4), where equation (4) is a two-stage reaction with a reaction rate constant KAm ═ 10 at 25 ℃4Liter/mol/sec. Free amine [ R]after addition of activator2′NH]>10-2Mols/liter. It is thus seen that the reaction rate of reaction (4) is much faster than that of reaction (1). KAm [ R 2 ′ NH ] KOH [ OH ] = 10 ~ 1000
In summary, the addition of the activator alters the absorption of CO by the MDEA solution2The course of (2). The activator plays a role in transferring CO2The function of (1). The reaction speed is accelerated. The activator absorbs CO on the surface2Then transferring CO to the liquid phase (MDEA solution)2And the activator is regenerated.
The desulfurization of the MDEA solution is carried out smoothly during the decarburization. The total sulfur in the raw material gas can be reduced to about 1 P.P.m.
The polyamine method solution of the invention comprises the following components by weight: group A: 20-60% of MDEA, 1-5% of piperazine, 1-10% of DEA, and B: 20-60% of MDEA, 0.1-10% of MMEA, 1-10% of DEA, C: 20-60% of MDEA, 1-5% of piperazine and 0.1-10% of MMEA.
The concentration of the solution actually used depends onthe composition of the gas to be treated, the degree of purification required and the pressure of the gas.
The comparative data of technical and economic indexes of the decarburization method of the invention and other decarburization methods are shown in table (1).
TABLE 1 comparison of technical and economic indicators for several decarburization processes
Figure C9311057900081
As seen from Table (1): the invention has regeneration heat consumption of 1881KJ/NM3CO2. About 1/2-1/3 of a composite catalytic method (CN851038557), although the absorption capacity of the invention is smaller than that of the composite catalytic method, the proportion of power consumption to total energy consumption is very small, so the total energy consumption is far smaller than that of the composite catalytic method.
The total stripping process flow adopted by the invention is shown in the second figure. Raw material gas entersThe bottom of the absorption tower 1 is contacted with polyamine absorption solution in countercurrent in the tower to remove CO in the gas2And sulfide, and the purified gas is led out from the top of the absorption tower 1 and sent to the next process through a cooler 6 and a separator 4. Containing CO from the bottom of the absorption tower 12The rich solution is decompressed and then enters an atmospheric pressure desorption tower 2, most of the desorbed semi-barren solution is pumped into the middle part of an absorption tower 1 by a semi-barren solution pump 11, a small amount of semi-barren solution is sent into a solution heat exchanger 9 by a relay pump 13 to obtain heat and then is sent to the top of a regeneration tower 3 to be subjected to steam stripping thermal regeneration, and the stripped steam is obtained by a boiler 10. The hot barren liquor from the bottom of the regeneration tower 3 is driven into a barren liquor cooler 7 by a barren liquor pump 12 after heat is recovered by a solution heat exchanger 9 and then enters the top of the absorption tower 1. The hot regeneration gas from the top of the regeneration tower 3 enters the bottom of the atmospheric desorption tower 2 to recover heat. The regenerated gas from the top of the atmospheric desorption tower 2 passes through a cooler 8 and a separator 5 and then is sent to the next process. Condensate separated from the purification gas separator 4 and the regeneration gas separator 5 is pumped into the top of the atmospheric desorption tower 2 by a condensate pump 14 so as to keep the water balance of the system.
The process flow of the invention can be carried out according to the process flow when a factory is newly built. If the invention is used in old factories which adopt the catalytic hot potash decarburization, the original process equipment can be properly modified. The upper tower of the original regeneration tower is changed into an atmospheric desorption tower, and the lower tower of the original regeneration tower is changed into the regeneration tower.
The semi-dehydration process flow adopted by the invention is shown in the third figure. The raw gas enters the bottom of the absorption tower 1, and the purified gas is led out from the top of the absorption towerThe cooler 2 and the separator 3 are sent to the next process. Containing CO from the bottom of the absorption tower 12The rich liquid is decompressed and then enters a normal pressure desorption tower 5 through a heater 4. The desorbed solution is pumped into the top of the absorption tower through a cooler 6 by a pump 9. The gas from the top of the atmospheric desorption tower 5 is sent to the next process or vented through a cooler 7 and a separator 8. The condensed water obtained from the separators 3 and 8 is pumped into the atmospheric desorption tower 5 by a pump 10.
The invention uses polyamine solution to remove CO2And the main process conditions of sulfide (total removal) are as follows:
operating pressure of the absorption tower: 1.3 to 3.0MPa (absolute)
Temperature of absorption tower barren solution: 50-75 DEG C
Temperature of absorption tower semi-barren solution: 75-90 DEG C
Tower kettle temperature of the regeneration tower: 100 to 115 DEG C
Raw material gas CO2The content is as follows: 17 to 30 percent
Total sulfur of raw material gas: 0 to 2000mg/NM3
Total sulfur of purified gas: 1-3 P.P.m
Regenerated gas CO2The content is 98-99.8%
Solution absorption capacity: 13 to 25NM3CO2/M3Solutions of
Thermal energy consumption: 1881KJ/NM3CO2
(means Pco20.5MPa after the day)
H2·N2Loss: 15 to 25NM3/TNH3
Solvent loss: about 30g MDEA/TNH3
The invention uses polyamine solutions for partial CO removal2(semi-threshing) main workThe process conditions are as follows:
operating pressure of the absorption tower: 0.7 to 2.0MPa (absolute)
Temperature of absorption tower barren solution: 60-80 DEG C
Heater outlet solution temperature: 70-90 DEG C
Raw material gas CO2The content is as follows: 25 to 30 percent
Regenerated gas CO2The content is as follows: 96 to 99 percent
Solution absorption capacity: 7 to 16NM3CO2/M3Solutions of
H2、N2Loss: 15 to 25NM3/TNH3
Solvent loss: about 30g MDEA/TNH3
In conclusion, the invention has the advantages of high purification degree of the total-stripping process, low energy consumption of regenerative heat, stable solution, less loss, no corrosion of the solution to carbon steel equipment and no need of adding a preservative. The system equipment pipeline of the original catalytic hot potash can be utilized, and the solution can be replaced without great change, so that the energy consumption can be greatly saved. The economic benefit is very obvious.
Example 1
One-plant processing gas amount 5650NM3Industrial installation,/hr. Raw gas pressure 1.8MPa, CO content226.6% of total sulfur-430 mg/NM3. The solution B is decarbonized by the polyamine method. The purified gas contains CO20.1-0.2% and total sulfur less than or equal to 3 P.P.m. Regenerated gas CO2Not less than 99.8 percent. Thermal energy consumption 1881KJ/NM3CO2。H2、N2Loss 20NM3/TNH3. Solvent loss-30 g MDEA/TNH3
Example 2
A plant for producing four million tons of urea for synthesizing ammonia in one year. The original method adopts benzene-Fischer method for decarburization. The treated gas amount is 17200NM3Hr, raw gas pressure of 1.45MPa, CO content229.4 percent. The purified gas contains CO20.2 to 0.3 percent. The thermal energy consumption is 6815KJ/NM2CO2(16.5T vapor/hr). And then, slightly modifying the device, replacing the solution, and decarbonizing by adopting the solution A. The purified gas contains CO20.1% or less. Regenerated gas CO2≥98.5%。H2,N2Loss 20NM2/TNH3. Thermal energy consumption 3139KJ/NM3CO2. The energy consumption is reduced by more than half compared with the original energy consumption.
Example 3
One-factory processing gas quantity 14000NM3Industrial installation,/hr. Raw gas pressure 1.4MPa, CO content229 percent. CO is carried out by using the solution B in the polyamine method2And partially removed (half removed). Purification of gas CO2-21%. Regenerated gas CO2More than or equal to 98 percent. Heat energy consumption 1045KJ/NM3CO2。H2、N2Loss 25NM3/TNH3

Claims (1)

1. A polyamine method solution for removing carbon dioxide and sulfide in gas is characterized in that the solution comprises a composite activator formed by combining N-methyldiethanolamine solution and two secondary amines, and the solution components are respectively (weight concentration): group A, N-methyldiethanolamine 20-60%, piperazine 1-5%, and diethanolamine 1-10%; group B, N-methyldiethanolamine 20-60%, N-methyl monoethanolamine 0.1-10%, and diethanolamine 1-10%; group C, N-methyldiethanolamine 20-60%, piperazine 1-5%, and N-methyl monoethanolamine 0.1-10%.
CN93110579A 1993-02-25 1993-02-25 Polyamine method for removing carbon dioxide and sulfide in gas Expired - Fee Related CN1052430C (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN93110579A CN1052430C (en) 1993-02-25 1993-02-25 Polyamine method for removing carbon dioxide and sulfide in gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN93110579A CN1052430C (en) 1993-02-25 1993-02-25 Polyamine method for removing carbon dioxide and sulfide in gas

Publications (2)

Publication Number Publication Date
CN1091332A CN1091332A (en) 1994-08-31
CN1052430C true CN1052430C (en) 2000-05-17

Family

ID=4988429

Family Applications (1)

Application Number Title Priority Date Filing Date
CN93110579A Expired - Fee Related CN1052430C (en) 1993-02-25 1993-02-25 Polyamine method for removing carbon dioxide and sulfide in gas

Country Status (1)

Country Link
CN (1) CN1052430C (en)

Families Citing this family (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101786968B (en) * 2009-01-23 2012-09-05 智胜化工股份有限公司 Method for reducing decarburization energy consumption of N-Methyldiethanolamine (MDEA)
CN102049174A (en) * 2009-10-28 2011-05-11 中国石油化工股份有限公司 Method for partially separating carbon dioxide from gas mixture
CN101822932B (en) * 2010-06-12 2013-01-02 中国石油集团工程设计有限责任公司 Composite decarbonization solvent for eliminating carbon dioxide in natural gases
CN102423620B (en) * 2011-10-26 2013-10-30 康达新能源设备股份有限公司 Compound decarbonizing solvent for removing carbon dioxide from biogas
CN102989295A (en) * 2012-11-23 2013-03-27 中国华能集团清洁能源技术研究院有限公司 Absorbent which gathers carbon dioxide in flue gas or synthesis gas
CN106215667B (en) * 2016-09-09 2019-01-08 广州优华过程技术有限公司 A kind of desulphurization system and its processing method for reducing the loss of amine liquid and alleviating the foaming of amine liquid
CN106831326A (en) * 2016-12-22 2017-06-13 赛鼎工程有限公司 A kind of comprehensive utilization process of coke-stove gas synthesizing methanol co-production liquefied natural gas
CN110624363B (en) * 2019-09-12 2022-03-25 中国石油化工股份有限公司 Pressurization regeneration method for capturing carbon dioxide in flue gas by alcohol amine method
CN114015486A (en) * 2021-08-10 2022-02-08 陕西省石油化工研究设计院 Activation synergist based on MDEA method natural gas decarbonization

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
合成气脱二2碳技术经济评价 1992.1.1 化学工业部科学技术情报研究所 *

Also Published As

Publication number Publication date
CN1091332A (en) 1994-08-31

Similar Documents

Publication Publication Date Title
CN1163405C (en) Removal of acidic gases in gasification power system with production of hydrogen
KR101474929B1 (en) Method and absorbent composition for recovering a gaseous component from a gas stream
CN101143286B (en) Method for removing COS from acid airflow
CN101918104B (en) Method for treating a process gas flow containing CO2
GB2079307A (en) Selective separation of hydrogen sulphide from gaseous mixtures
CN102423620B (en) Compound decarbonizing solvent for removing carbon dioxide from biogas
CN110684574A (en) Decarbonization method for preparing liquefied natural gas from high-carbon-content natural gas
CN101745289A (en) Method for selectively removing H2S from gas mixture containing CO2
CN1052430C (en) Polyamine method for removing carbon dioxide and sulfide in gas
CN1169335A (en) Method for taking off hydrogen sulfide from mixed gas
CN111375274B (en) Containing SO 2 Gas treatment method and apparatus
CN101676018A (en) Method for selectively removing COS from acid gas flow
CN114712984B (en) Substitution process for recycling CO2 through full-temperature-range pressure swing adsorption for amine absorption decarburization in natural gas SMB hydrogen production
CN114015481B (en) Short-flow low-temperature methanol washing system and process thereof
AU2021104718A4 (en) Device and Method for Deeply Removing Sulfide in Circulating methanol of the rectisol by Extractive Distillation
CN1817410A (en) Complete equipment for decreasing push, increasing pressure and desulfurizing and desulfurization thereof
CN110564471A (en) Absorption liquid for desulfurization and decarburization in SNG synthesis gas
US8241603B1 (en) Process and system for removing sulfur from sulfur-containing gaseous streams
CN113019071A (en) High CO2Recycled semi-barren solution circulation low-temperature methanol washing process
CN111500333A (en) Solid waste and alkali liquor circulating desulfurization and decarburization system and working method thereof
SU1477454A1 (en) Method of removing carbon dioxide from gas
CN111362229A (en) Method for preparing hydrogen for fuel cell from yellow phosphorus tail gas
CN111662754A (en) Novel coke oven gas desulfurization method
CN113731098A (en) Environmental-friendly resourceful treatment system and process flow for fireflooding tail gas
CN113277511B (en) Production process for preparing electronic grade high-purity carbon dioxide by purifying synthesis gas

Legal Events

Date Code Title Description
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C06 Publication
PB01 Publication
C14 Grant of patent or utility model
GR01 Patent grant
C17 Cessation of patent right
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20000517

Termination date: 20110225