CN108570337A - A kind of dry decontamination method of natural gas - Google Patents

A kind of dry decontamination method of natural gas Download PDF

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Publication number
CN108570337A
CN108570337A CN201810360211.4A CN201810360211A CN108570337A CN 108570337 A CN108570337 A CN 108570337A CN 201810360211 A CN201810360211 A CN 201810360211A CN 108570337 A CN108570337 A CN 108570337A
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CN
China
Prior art keywords
natural gas
absorbent
dry decontamination
decontamination method
gas
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Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201810360211.4A
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Chinese (zh)
Inventor
姬中强
郭依勇
张鹏莱
吕鹏
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Pizhou China Combustion City Gas Development Co Ltd
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Pizhou China Combustion City Gas Development Co Ltd
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 Pizhou China Combustion City Gas Development Co Ltd filed Critical Pizhou China Combustion City Gas Development Co Ltd
Priority to CN201810360211.4A priority Critical patent/CN108570337A/en
Publication of CN108570337A publication Critical patent/CN108570337A/en
Pending legal-status Critical Current

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    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L3/00Gaseous fuels; Natural gas; Synthetic natural gas obtained by processes not covered by subclass C10G, C10K; Liquefied petroleum gas
    • C10L3/06Natural gas; Synthetic natural gas obtained by processes not covered by C10G, C10K3/02 or C10K3/04
    • C10L3/10Working-up natural gas or synthetic natural gas
    • C10L3/101Removal of contaminants
    • C10L3/102Removal of contaminants of acid contaminants
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L3/00Gaseous fuels; Natural gas; Synthetic natural gas obtained by processes not covered by subclass C10G, C10K; Liquefied petroleum gas
    • C10L3/06Natural gas; Synthetic natural gas obtained by processes not covered by C10G, C10K3/02 or C10K3/04
    • C10L3/10Working-up natural gas or synthetic natural gas
    • C10L3/101Removal of contaminants
    • C10L3/102Removal of contaminants of acid contaminants
    • C10L3/103Sulfur containing contaminants
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L3/00Gaseous fuels; Natural gas; Synthetic natural gas obtained by processes not covered by subclass C10G, C10K; Liquefied petroleum gas
    • C10L3/06Natural gas; Synthetic natural gas obtained by processes not covered by C10G, C10K3/02 or C10K3/04
    • C10L3/10Working-up natural gas or synthetic natural gas
    • C10L3/101Removal of contaminants
    • C10L3/102Removal of contaminants of acid contaminants
    • C10L3/104Carbon dioxide
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L3/00Gaseous fuels; Natural gas; Synthetic natural gas obtained by processes not covered by subclass C10G, C10K; Liquefied petroleum gas
    • C10L3/06Natural gas; Synthetic natural gas obtained by processes not covered by C10G, C10K3/02 or C10K3/04
    • C10L3/10Working-up natural gas or synthetic natural gas
    • C10L3/101Removal of contaminants
    • C10L3/106Removal of contaminants of water

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

Abstract

The present invention relates to a kind of dry decontamination methods of natural gas, belong to natural gas processing technical field.The dry decontamination method of the natural gas of the present invention, includes the following steps:1) sour gas in absorbent removing natural gas, the natural gas and the absorbent after absorption that sour gas must be removed are utilized;2) natural gas flow for removing sour gas is dried through hollow cellulose film, obtains purified natural gas.The dry decontamination method of the natural gas of the present invention, first removes the sour gas in natural gas such as hydrogen sulfide and carbon dioxide using absorbent, and the absorbent after absorption can also be obtained by heat treatment and be lived again to recycle;Remaining sour gas is further removed while dehydration using hollow cellulose film, dehydration draws addition, no additional materials consumption, non-secondary pollution without reagent;The dry decontamination method of the natural gas of the present invention, environmentally friendly, at low cost and purification efficiency is high, the application prospect having had.

Description

A kind of dry decontamination method of natural gas
Technical field
The present invention relates to a kind of dry decontamination methods of natural gas, belong to natural gas processing technical field.
Background technology
In heat treatment, using natural gas as air source better than methanol, ethyl alcohol, acetone etc., with adding for city gasification rate Soon, natural gas has become ordinary energy particularly important in people's daily life.But the problems such as sulfur-bearing, water of natural gas, to heat Processing equipment and effect have an adverse effect, and therefore, need when in use first to selexol process processing.Selexol process generally may be used It is divided into dry and wet two major classes.Wet method is big in the prevalence of power consumption, equipment volume is huge, operating cost is high, control strip The shortcomings of part is harsh;Dry method is simple for process with its, easy to operate, desulfurization precision is high, low energy consumption suitable for lean sulphurous gas processing And it is widely used.Existing sulfur removal technology is mainly by following several absorption processes:Absorption process includes chemistry, physics, physical chemistry Absorption process.But whether being which kind of method, the wet purification gas generated after sulfur removal technology contains a large amount of steam.Steam with Natural gas forms hydrate under certain condition and blocks pipeline, influences cooling liquid process.In addition, due to the presence of moisture It can cause unnecessary power consumption;Since natural gas liquefaction temperature is relatively low, the presence of moisture and sour gas, which also results in, to be set Standby frozen block, therefore must remove.
Invention content
The purpose of the present invention is to provide a kind of dry decontamination methods of natural gas, can efficiently be removed using this method Sour gas in natural gas and moisture.
In order to achieve the above object, the technical scheme is that:
A kind of dry decontamination method of natural gas, includes the following steps:
1) sour gas in absorbent removing natural gas, the natural gas that sour gas must be removed and the suction after absorption are utilized Receive agent;
2) natural gas flow for removing sour gas is dried through hollow cellulose film, obtains purified natural gas.
Absorbent in step 1) is the aqueous solution of methyl diethanolamine and activator.Since methyl diethanolamine only has one A tertiary amine nitrogen-atoms, because tertiary amine nitrogen-atoms is without active hydrogen, unlike primary amine, secondary amine directly and carbon dioxide reaction, to two Carbonoxide absorption efficiency is not high, and the adsorption effect of water and activator appropriate to improve absorbent to carbon dioxide is added, and dissociates Hydrogen bond between amine and water enhances the activity reacted, and promotes the aquation of carbon dioxide.The absorbent of the present invention is provided simultaneously with The characteristics of physical absorption and chemisorption, improve the analyzing efficiency of carbon dioxide reduces energy consumption again.
The mass fraction of methyl diethanolamine is 30~50% in the absorbent.
The mass fraction of activator is 1~5% in the absorbent.The mass fraction of activator of the present invention is only 1~ 5%, concentration is smaller, not corrosive equipment, moreover it is possible to ensure the absorption efficiency to sour gas.
Under conditions of each concentration of above-mentioned absorbent, absorbent all has high absorption to hydrogen sulfide and carbon dioxide and imitates Rate substantially can thoroughly remove sour gas hydrogen sulfide and carbon dioxide in natural gas.
The activator is appointing in monoethanolamine, diethanol amine, diethylenetriamine, triethylene tetramine, piperazine, sulfolane Meaning is a kind of.Different activators plays the role of different, thus it is possible to vary MDEA and CO2The reaction mechanism mechanism of reaction, accelerate reaction rate, improve The absorption rate of carbon dioxide can also reduce the equilibrium partial pressure of solution surface carbon dioxide, improve gas purification degree.
Absorbent after absorption in step 1) is heated to 60~150 DEG C of release of acid so that absorbent is lived again.
Hollow cellulose film in step 2) is polysulfone hollow fibre element film, cellulose acetate hollow cellulose film, polyamides Any one in imines hollow cellulose film, cellulose/polyethersulfone blended hollow cellulose film.
Hollow cellulose film in step 2) is one kind of ultrafiltration membrane.It is residual when pending natural gas flow is through film surface Acidic components (the H stayed2O、CO2With a small amount of H2S it) is preferentially removed through seperation film.Using natural gas pressure itself as The motive force of purification, almost without the pressure loss;Hollow cellulose film is dehydrated, and no reagent is added, and belongs to dry cleaning, purge drying It is consumed in the process without additional materials, without regeneration, non-secondary pollution;It is dehydrated using hollow cellulose film, process compatibility is strong, tool Have while detachability, the carbon dioxide and hydrogen sulfide that not can be completely removed in step 1) can be also removed while dehydration, it is right Natural gas is further purified.
The dry decontamination method of the natural gas of the present invention, first for example vulcanizes the sour gas in natural gas using absorbent Hydrogen and carbon dioxide are removed, and the absorbent after absorption can also be obtained by heat treatment and be lived again to recycle;It utilizes Remaining sour gas is further removed while hollow cellulose film is dehydrated, dehydration draws addition, no volume without reagent Outer material consumption, non-secondary pollution;The dry decontamination method of the natural gas of the present invention, environmentally friendly, at low cost and purification efficiency is high, tool The application prospect having had.
Specific implementation mode
The present invention is described further with reference to embodiments, but not limited to this.
Embodiment 1
The dry decontamination method of the natural gas of the present embodiment, includes the following steps:
1) sour gas (H in the aqueous solution of methyl diethanolamine and diethanol amine removing natural gas is utilized2S and CO2), The natural gas and the absorbent after absorption that sour gas must be removed;Wherein the mass fraction of methyl diethanolamine is 30%, diethyl The mass fraction of hydramine is 2%;
2) natural gas flow for removing sour gas is dried through cellulose acetate hollow cellulose film, is obtained purified Natural gas;
3) absorbent in step 1) after absorption is heated to 80 DEG C to desorb sour gas, enables absorbent cycle profit With.
Embodiment 2
The dry decontamination method of the natural gas of the present embodiment, includes the following steps:
1) sour gas (H in the aqueous solution of methyl diethanolamine and triethylene tetramine removing natural gas is utilized2S and CO2), the natural gas and the absorbent after absorption that sour gas must be removed;Wherein the mass fraction of methyl diethanolamine is 40%, The mass fraction of triethylene tetramine is 1%;
2) natural gas flow for removing sour gas is dried through polyimide hollow fiber element film, obtains purified day Right gas;
3) absorbent in step 1) after absorption is heated to 100 DEG C to desorb sour gas, enables absorbent cycle profit With.
Embodiment 3
The dry decontamination method of the natural gas of the present embodiment, includes the following steps:
1) sour gas (H in the aqueous solution of methyl diethanolamine and piperazine removing natural gas is utilized2S and CO2), it obtains de- Except the absorbent after the natural gas of sour gas and absorption;Wherein the mass fraction of methyl diethanolamine is 50%, the matter of piperazine It is 5% to measure score;
2) natural gas flow for removing sour gas is dried through cellulose/polyethersulfone blended hollow cellulose film, is obtained Purified natural gas;
3) absorbent in step 1) after absorption is heated to 60 DEG C to desorb sour gas, enables absorbent cycle profit With.
Embodiment 4
The dry decontamination method of the natural gas of the present embodiment, includes the following steps:
1) sour gas (H in the aqueous solution of methyl diethanolamine and piperazine removing natural gas is utilized2S and CO2), it obtains de- Except the absorbent after the natural gas of sour gas and absorption;Wherein the mass fraction of methyl diethanolamine is 50%, the matter of piperazine It is 5% to measure score;
2) natural gas flow for removing sour gas is dried through cellulose/polyethersulfone blended hollow cellulose film, is obtained Purified natural gas;
3) absorbent in step 1) after absorption is heated to 150 DEG C to desorb sour gas, enables absorbent cycle profit With.
It will be apparent to those skilled in the art that technical solution that can be as described above and design, make various other Corresponding change and deformation, and all these changes and deformation should all belong to the protection domain of the claims in the present invention Within.

Claims (7)

1. a kind of dry decontamination method of natural gas, which is characterized in that include the following steps:
1) sour gas in absorbent removing natural gas, the natural gas that sour gas must be removed and the absorption after absorption are utilized Agent;
2) natural gas flow for removing sour gas is dried through hollow cellulose film, obtains purified natural gas.
2. the dry decontamination method of natural gas according to claim 1, which is characterized in that the absorbent in step 1) is first The aqueous solution of base diethanol amine and activator.
3. the dry decontamination method of natural gas according to claim 2, which is characterized in that methyl diethyl in the absorbent The mass fraction of hydramine is 30~50%.
4. the dry decontamination method of natural gas according to claim 2, which is characterized in that activator in the absorbent Mass fraction is 1~5%.
5. the dry decontamination method of natural gas according to claim 2, which is characterized in that the activator is an ethyl alcohol Any one in amine, diethanol amine, diethylenetriamine, triethylene tetramine, piperazine, sulfolane.
6. to go the dry decontamination method of the natural gas described in 2 according to right, which is characterized in that by the suction after absorption in step 1) It receives agent and is heated to 60~150 DEG C of release of acid so that absorbent is lived again.
7. the dry decontamination method of natural gas according to claim 1, which is characterized in that the hollow cellulose in step 2) Film is polysulfone hollow fibre element film, cellulose acetate hollow cellulose film, polyimide hollow fiber element film, cellulose/polyethers Any one in hollow cellulose film is blended in sulfone.
CN201810360211.4A 2018-04-20 2018-04-20 A kind of dry decontamination method of natural gas Pending CN108570337A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112831349A (en) * 2020-12-11 2021-05-25 中国石油天然气股份有限公司 Method for improving utilization efficiency of associated gas of oil field operation station

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112831349A (en) * 2020-12-11 2021-05-25 中国石油天然气股份有限公司 Method for improving utilization efficiency of associated gas of oil field operation station

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Application publication date: 20180925

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