WO2020082201A1 - Process and system for tail gas treatment - Google Patents

Process and system for tail gas treatment Download PDF

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Publication number
WO2020082201A1
WO2020082201A1 PCT/CN2018/111138 CN2018111138W WO2020082201A1 WO 2020082201 A1 WO2020082201 A1 WO 2020082201A1 CN 2018111138 W CN2018111138 W CN 2018111138W WO 2020082201 A1 WO2020082201 A1 WO 2020082201A1
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Prior art keywords
gas
tower
carried out
tail gas
alkyl
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PCT/CN2018/111138
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French (fr)
Inventor
Jun Wu
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Pujing Chemical Industry Co., Ltd
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Priority to PCT/CN2018/111138 priority Critical patent/WO2020082201A1/en
Priority to AU2018446174A priority patent/AU2018446174B2/en
Priority to RU2018145377A priority patent/RU2705073C1/en
Publication of WO2020082201A1 publication Critical patent/WO2020082201A1/en

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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/14Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
    • B01D53/1487Removing organic compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/14Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
    • B01D53/1493Selection of liquid materials for use as absorbents
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/8621Removing nitrogen compounds
    • B01D53/8625Nitrogen oxides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/10Oxidants
    • B01D2251/11Air
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/20Reductants
    • B01D2251/202Hydrogen
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/20Reductants
    • B01D2251/204Carbon monoxide
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/20Reductants
    • B01D2251/206Ammonium compounds
    • B01D2251/2062Ammonia
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2252/00Absorbents, i.e. solvents and liquid materials for gas absorption
    • B01D2252/10Inorganic absorbents
    • B01D2252/103Water
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2252/00Absorbents, i.e. solvents and liquid materials for gas absorption
    • B01D2252/20Organic absorbents
    • B01D2252/202Alcohols or their derivatives
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2252/00Absorbents, i.e. solvents and liquid materials for gas absorption
    • B01D2252/20Organic absorbents
    • B01D2252/202Alcohols or their derivatives
    • B01D2252/2021Methanol
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/10Noble metals or compounds thereof
    • B01D2255/102Platinum group metals
    • B01D2255/1021Platinum
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/10Noble metals or compounds thereof
    • B01D2255/102Platinum group metals
    • B01D2255/1023Palladium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/10Noble metals or compounds thereof
    • B01D2255/102Platinum group metals
    • B01D2255/1025Rhodium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/207Transition metals
    • B01D2255/20761Copper
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/40Nitrogen compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/40Nitrogen compounds
    • B01D2257/404Nitrogen oxides other than dinitrogen oxide
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2201/00Pretreatment
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/06Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23JREMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES 
    • F23J2215/00Preventing emissions
    • F23J2215/10Nitrogen; Compounds thereof
    • F23J2215/101Nitrous oxide (N2O)
    • 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

Definitions

  • the present invention relates processes and systems for treatment of tail gases comprising nitrogen oxides and alkyl nitrite gases.
  • Nitrogen oxides are mainly used to refer to NO 2 and NO.
  • NO x can stimulate lungs and cause damages to the lungs. NO x can also reduce visibility of the atmosphere.
  • NO x react with water in the air to form acid rain, which causes damages to the environment.
  • Methyl nitrite (MN) is a flammable and explosive gas with strong toxicity. MN can form methemoglobin with red blood cells in blood after inhalation, so that the red blood cells lose their ability to carry oxygen. The principle of the toxicity is similar to that of carbon monoxide (CO) , but MN toxicity is much stronger than that of CO.
  • the present invention provides treatment of a tail gas comprising nitrogen oxides and alkyl nitrite gas.
  • a process for treating a tail gas having nitrogen oxides and an alkyl nitrite comprises (a) contacting the tail gas with an effective amount of an alkyl alcohol in the presence of oxygen to absorb the alkyl nitrite, whereby an absorbed gas is generated; (b) contacting the absorbed gas with a reducing gas in the presence of an effective amount of a catalyst to reduce the nitrogen oxides, whereby an absorbed and reduced gas is generated; and (c) washing the absorbed and reduced gas, whereby a treated tail gas is prepared.
  • the treated tail gas may have a nitrogen oxide content less than 50 ppm.
  • the treated tail gas may have an alkyl nitrite content less than 10 ppm.
  • the molar ratio of the nitrogen oxides in step (a) to the oxygen in step (a) may be from 1: 10 to 10: 1.
  • the molar ratio of the alkyl alcohol in step (a) to the alkyl nitrite in step (a) may be from 1: 1 to 100: 1.
  • the alkyl alcohol may be selected from the group consisting of methanol, ethanol, propanol and butanol.
  • Step (a) may be carried out under an operation pressure of 0.1-1.0 MPa. Step (a) may be carried out at an operation temperature from -30 °C to 90 °C.
  • Step (a) may be carried out in a first absorption tower.
  • the first absorption tower may be a packing tower, a washing tower or a spraying tower.
  • the molar ratio of the reducing gas to the nitrogen oxides in step (b) may be from 1: 1 to 10: 1.
  • the reducing gas may comprise H 2 , CO, NH 3 , or a combination thereof.
  • the catalyst may comprise Pd, Pt, Cu, Rh or a combination thereof.
  • Step (b) may be carried out at a temperature from 50 °C to 500 °C.
  • Step (b) may be carried out under a pressure of 0-10 barG.
  • Step (b) may be carried out at a gas space velocity of 50-10,000 h -1 .
  • Step (b) may be carried out in a reactor.
  • the reactor may be a fixed bed reactor.
  • the absorbed and reduced gas may be washed with water or an alkyl alcohol in step (c) .
  • the alkyl alcohol used in step (c) may be methanol, ethanol, propanol or butanol.
  • the alkyl alcohol used in step (c) may be the same as the alkyl alcohol used in step (a) .
  • the molar ratio of the alkyl alcohol or water in step (c) to the alkyl nitrite in step (a) may be from 1: 1 to 1000: 1.
  • Step (c) may be carried out in a second absorption tower.
  • the second absorption tower may be a packing tower, a washing tower or a spraying tower.
  • FIG. 1 illustrating a process and a system for absorbing and removing nitrogen oxides (NO x ) and alkyl nitrites in a gas according to an embodiment of the invention.
  • the invention relates to a process for treating a tail gas having nitrogen oxides (NO x ) and alkyl nitrites (RONO) .
  • This invention was made based on the surprising discovery of novel treatment process by the inventors that removes RONO and NO x from a tail gas by absorption with an alkyl alcohol and by a catalytic reduction reaction, respectively, such that the treated tail has a NO x content below 50 ppm and a RONO content below 10 ppm.
  • a system for carrying out the treatment process is also provided.
  • a process for treating a tail gas is provided.
  • the tail gas has nitrogen oxides (NO x ) and alkyl nitrite (RONO) .
  • the process comprises contacting the tail gas with an effective amount of an alkyl alcohol in the presence of oxygen to absorb the alkyl nitrite, contacting the resulting absorbed gas with a reducing gas in the presence of an effective amount of a catalyst to reduce the nitrogen oxides, and washing the resulting absorbed and reduced gas.
  • a treated tail gas is prepared.
  • nitrogen oxides include nitrogen monoxide (NO) and nitrogen dioxide (NO 2 ) .
  • the tail gas may have an initial nitrogen oxide content greater than 50000 or 100000 ppm.
  • the treated tail gas may have a nitrogen oxide content less than about 60, 55, 50, 45, 40, 35, 30, 25, 20, 15 or 10 ppm, preferably less than about 50 ppm.
  • alkyl nitrite examples include methyl nitrite (MN) and ethyl nitrite.
  • the treated tail gas may have an alkyl nitrite content less than about 20, 15, 14, 13, 12, 11, 10, 9, 8, 7, 6, 5, 4, 3, 2 or 1 ppm, preferably less than about 10 ppm.
  • the molar ratio of the nitrogen oxides to the oxygen may be from about 1: 10 to about 10: 1, preferably from about 1: 5 to about 5: 1, more preferably from about 1: 2 to about 2: 1.
  • the molar ratio of the alkyl alcohol to the alkyl nitrite may be from about 1: 1 to about 100: 1, preferably from about 2: 1 to about 50: 1, more preferably from about 5: 1 to about 30: 1.
  • the alkyl alcohol may be selected from the group consisting of methanol, ethanol, propanol and butanol.
  • the alkyl nitrite absorption step may be carried out under an operation pressure of about 0.1-1.0 MPa, preferably about 0.1-0.7 MPa, more preferably about 0.1-0.3 MPa.
  • the alkyl nitrite absorption step may be carried out at an operation temperature from about -30 °C to about 90 °C, preferably from about -10 °C to about 60 °C, more preferably from about 0 °C to about 50 °C.
  • the alkyl nitrite absorption step may be carried out in an absorption tower, which may be a packing tower, a washing tower or a spraying tower.
  • an absorption tower which may be a packing tower, a washing tower or a spraying tower.
  • the molar ratio of the reducing gas to the nitrogen oxides may be from about 1: 1 to about 10: 1, preferably from about 1: 1 to about 5: 1, more preferably from about 1: 1 to about 3: 1.
  • the reducing gas may comprise H 2 , CO, NH 3 , or a combination thereof.
  • the catalyst may comprise Pd, Pt, Cu, Rh or a combination thereof.
  • the reduction step may be carried out at a temperature of about 50-500 °C, preferably about 100-450 °C, more preferably about 150-350 °C.
  • the reduction step may be carried out under a pressure of about 0-10 barG, preferably about 0-8 barG, more preferably about 0-5 barG.
  • the reduction step may be carried out at a gas space velocity of about 50-10,000 h -1 , preferably about 70-5,000 h -1 , more preferably about 100-2,000 h -1 .
  • the reduction step may be carried out in a reactor.
  • the reactor may be a fixed bed reactor.
  • the absorbed and reduced gas may be washed with water or an alkyl alcohol.
  • the alkyl alcohol used in the washing step may be methanol, ethanol, propanol or butanol.
  • the alkyl alcohol used in the washing step may be the same as the alkyl alcohol used in absorption step.
  • the molar ratio of the alkyl alcohol or water used in the washing step to the alkyl nitrite used in absorption step may be from about 1: 1 to about 1000: 1 , preferably from about 2: 1 to about 500: 1, more preferably from about 5: 1 to about 300: 1.
  • the washing step may be carried out in a second absorption tower.
  • the second absorption tower may be a packing tower, a washing tower or a spraying tower.
  • a system for treating a tail gas having nitrogen oxides and an alkyl nitrite comprises a first absorption tower, a reactor and a second absorption towner.
  • the first absorption towner the tail gas is exposed to an effective amount of an alkyl alcohol in the presence of oxygen to absorb the alkyl nitrite, whereby an absorbed gas is generated.
  • the reactor the absorbed gas is exposed to a reducing gas in the presence of an effective amount of a catalyst to reduce the nitrogen oxides, whereby an absorbed and reduced gas is generated.
  • the absorbed and reduced gas is washed. As a result, a treated tail gas is prepared.
  • the first absorption tower may be a packing tower, a washing tower or a spraying tower.
  • the reactor may be a fixed bed reactor.
  • the second absorption tower may be a packing tower, a washing tower or a spraying tower.
  • a tail gas was treated to generate Treated Gas 1.
  • a gas containing nitrogen oxides (NO x ) and methyl nitrite (MN) was introduced with air into a first washing tower.
  • the molar ratio of the NO x to the oxygen (O 2 ) in the air was 1: 10.
  • Methanol was introduced at a molar ratio of methanol to MN at 1: 1 to adsorb MN.
  • the operation pressure was 0.1 MPa.
  • the operation temperature was -30 °C.
  • the gas exiting from the top of the adsorption tower was passed together with hydrogen (H 2 ) into a fixed bed reactor equipped containing Pt catalyst for catalytic reduction in the presence of a reducing gas having a molar ratio of the reducing gas to the NO x at 1: 1.
  • the reaction temperature was 500 °C.
  • the reaction pressure was 0 barG.
  • the gas space velocity was 50 h -1 .
  • the reduced gas was passed from the fixed bed reactor into a second washing tower for washing with water at a molar ratio of 1000: 1 for the water to the methyl nitrate before treatment and, after washing, the used water was discarded as waste water.
  • the gas exiting from the top of the washing tower was Treated Gas 1. Treated Gas 1 was then subjected to combustion treatment.
  • Table 1 shows the key process conditions used to prepare Treated Gas 1 and its methyl nitrite content of 8 ppm and NOx content of 43 ppm.
  • a tail gas was treated to generate Treated Gas 2.
  • a gas containing nitrogen oxides (NO x ) and ethyl nitrite was introduced with air into a first packing tower.
  • the molar ratio of NO x to oxygen (O 2 ) in the air was 10: 1.
  • Ethanol was introduced at a molar ratio of ethanol to ethyl nitrite at 100: 1 to absorb ethyl nitrite.
  • the operation pressure was 1.0 Mpa.
  • the operation temperature was 90°C.
  • the gas existing from the top of the filler tower was passed together with CO into a fixed bed reactor equipped with Pd catalyst for catalytic reduction in the presence of a reducing gas having a molar ratio of the reducing gas to the NO x at 10: 1.
  • the reaction temperature was 50 °C.
  • the reaction pressure was 10 barG.
  • the gas space velocity was 10,000 h -1 .
  • the reduced gas was passed into a second packing tower for washing with ethanol at a molar ratio of 1: 1 for the ethanol to the ethyl nitrite in the tail gas before treatment and, after washing, the used ethanol was introduced into the first packing tower to be reused in the absorption step.
  • the gas exiting from the top of the washing tower was Treated Gas 2. Treated Gas 2 was then subjected to combustion treatment.
  • Table 1 shows the key process conditions used to prepare Treated Gas 2 and its methyl nitrite content of 9 ppm and nitrogen oxide content of 43 ppm.
  • Table 1 shows the process conditions used for preparing Treated Gases 3-6 and Comparative Treated Gases 1-3 and their methyl nitrite contents and nitrogen oxide contents.

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  • Engineering & Computer Science (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Environmental & Geological Engineering (AREA)
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Abstract

Presented is a process for treating a tail gas having nitrogen oxides and an alkyl nitrite. The process comprises contacting the tail gas with an alkyl alcohol in the presence of oxygen to absorb the alkyl nitrite, contacting the resulting absorbed gas with a reducing gas in the presence of a catalyst to reduce the nitrogen oxides, and washing the absorbed and reduced gas to generate a treated tail gas. Also provided is a system for treating a tail gas having nitrogen oxides and an alkyl nitrite. The treated tail gas has a low nitrogen oxide content and a low alkyl nitrite content.

Description

PROCESS AND SYSTEM FOR TAIL GAS TREATMENT FIELD OF THE INVENTION
The present invention relates processes and systems for treatment of tail gases comprising nitrogen oxides and alkyl nitrite gases.
BACKGROUND OF THE INVENTION
Nitrogen oxides (NO x) are mainly used to refer to NO 2 and NO. NO x can stimulate lungs and cause damages to the lungs. NO x can also reduce visibility of the atmosphere. In addition, NO x react with water in the air to form acid rain, which causes damages to the environment. Methyl nitrite (MN) is a flammable and explosive gas with strong toxicity. MN can form methemoglobin with red blood cells in blood after inhalation, so that the red blood cells lose their ability to carry oxygen. The principle of the toxicity is similar to that of carbon monoxide (CO) , but MN toxicity is much stronger than that of CO. Therefore, it is necessary to treat a tail gas containing NO x and alkyl nitrites (RONO) by removing NO x therein to lower its concentration to meet the relevant environmental standard, while simultaneously converting the MN therein before discharging the tail gas.
There remains a need for simple, low energy consumption and effective treatment and equipment for treating nitrogen oxides and alkyl nitrite gas.
SUMMARY OF THE INVENTION
The present invention provides treatment of a tail gas comprising nitrogen oxides and alkyl nitrite gas.
A process for treating a tail gas having nitrogen oxides and an alkyl nitrite is provided. The process comprises (a) contacting the tail gas with an effective amount of an alkyl alcohol in the presence of oxygen to absorb the alkyl nitrite, whereby an absorbed gas is generated; (b) contacting the absorbed gas with a reducing gas in the presence of an effective amount of a catalyst to reduce the nitrogen oxides, whereby an absorbed and reduced gas is generated; and (c) washing the absorbed and reduced gas, whereby a treated tail gas is prepared.
The treated tail gas may have a nitrogen oxide content less than 50 ppm. The treated tail gas may have an alkyl nitrite content less than 10 ppm.
The molar ratio of the nitrogen oxides in step (a) to the oxygen in step (a) may be from 1: 10 to 10: 1. The molar ratio of the alkyl alcohol in step (a) to the alkyl nitrite in step  (a) may be from 1: 1 to 100: 1. The alkyl alcohol may be selected from the group consisting of methanol, ethanol, propanol and butanol.
Step (a) may be carried out under an operation pressure of 0.1-1.0 MPa. Step (a) may be carried out at an operation temperature from -30 ℃ to 90 ℃.
Step (a) may be carried out in a first absorption tower. The first absorption tower may be a packing tower, a washing tower or a spraying tower.
The molar ratio of the reducing gas to the nitrogen oxides in step (b) may be from 1: 1 to 10: 1. The reducing gas may comprise H 2, CO, NH 3, or a combination thereof. The catalyst may comprise Pd, Pt, Cu, Rh or a combination thereof.
Step (b) may be carried out at a temperature from 50 ℃ to 500 ℃. Step (b) may be carried out under a pressure of 0-10 barG. Step (b) may be carried out at a gas space velocity of 50-10,000 h -1.
Step (b) may be carried out in a reactor. The reactor may be a fixed bed reactor.
The absorbed and reduced gas may be washed with water or an alkyl alcohol in step (c) . The alkyl alcohol used in step (c) may be methanol, ethanol, propanol or butanol. The alkyl alcohol used in step (c) may be the same as the alkyl alcohol used in step (a) . The molar ratio of the alkyl alcohol or water in step (c) to the alkyl nitrite in step (a) may be from 1: 1 to 1000: 1.
Step (c) may be carried out in a second absorption tower. The second absorption tower may be a packing tower, a washing tower or a spraying tower.
BRIEF DESCRIPTION OF THE DRAWINGS
FIG. 1 illustrating a process and a system for absorbing and removing nitrogen oxides (NO x) and alkyl nitrites in a gas according to an embodiment of the invention.
DETAILED DESCRIPTION OF THE INVENTION
The invention relates to a process for treating a tail gas having nitrogen oxides (NO x) and alkyl nitrites (RONO) . This invention was made based on the surprising discovery of novel treatment process by the inventors that removes RONO and NO x from a tail gas by absorption with an alkyl alcohol and by a catalytic reduction reaction, respectively, such that the treated tail has a NO x content below 50 ppm and a RONO content below 10 ppm. Also provided is a system for carrying out the treatment process.
A process for treating a tail gas is provided. The tail gas has nitrogen oxides (NO x) and alkyl nitrite (RONO) . The process comprises contacting the tail gas with an effective amount of an alkyl alcohol in the presence of oxygen to absorb the alkyl nitrite, contacting the resulting absorbed gas with a reducing gas in the presence of an effective amount of a catalyst to reduce the nitrogen oxides, and washing the resulting absorbed and reduced gas. As a result, a treated tail gas is prepared.
Examples of nitrogen oxides include nitrogen monoxide (NO) and nitrogen dioxide (NO 2) . The tail gas may have an initial nitrogen oxide content greater than 50000 or 100000 ppm. The treated tail gas may have a nitrogen oxide content less than about 60, 55, 50, 45, 40, 35, 30, 25, 20, 15 or 10 ppm, preferably less than about 50 ppm.
Examples of alkyl nitrite include methyl nitrite (MN) and ethyl nitrite. The treated tail gas may have an alkyl nitrite content less than about 20, 15, 14, 13, 12, 11, 10, 9, 8, 7, 6, 5, 4, 3, 2 or 1 ppm, preferably less than about 10 ppm.
In alkyl nitrite absorption step, the molar ratio of the nitrogen oxides to the oxygen may be from about 1: 10 to about 10: 1, preferably from about 1: 5 to about 5: 1, more preferably from about 1: 2 to about 2: 1.
The molar ratio of the alkyl alcohol to the alkyl nitrite may be from about 1: 1 to about 100: 1, preferably from about 2: 1 to about 50: 1, more preferably from about 5: 1 to about 30: 1. The alkyl alcohol may be selected from the group consisting of methanol, ethanol, propanol and butanol.
The alkyl nitrite absorption step may be carried out under an operation pressure of about 0.1-1.0 MPa, preferably about 0.1-0.7 MPa, more preferably about 0.1-0.3 MPa.
The alkyl nitrite absorption step may be carried out at an operation temperature from about -30 ℃ to about 90 ℃, preferably from about -10 ℃ to about 60 ℃, more preferably from about 0 ℃ to about 50 ℃.
The alkyl nitrite absorption step may be carried out in an absorption tower, which may be a packing tower, a washing tower or a spraying tower.
In the reduction step, the molar ratio of the reducing gas to the nitrogen oxides may be from about 1: 1 to about 10: 1, preferably from about 1: 1 to about 5: 1, more preferably from about 1: 1 to about 3: 1. The reducing gas may comprise H 2, CO, NH 3, or a combination thereof. The catalyst may comprise Pd, Pt, Cu, Rh or a combination thereof.
The reduction step may be carried out at a temperature of about 50-500 ℃, preferably about 100-450 ℃, more preferably about 150-350 ℃. The reduction step may be carried out under a pressure of about 0-10 barG, preferably about 0-8 barG, more preferably about 0-5 barG. The reduction step may be carried out at a gas space velocity of about 50-10,000 h -1, preferably about 70-5,000 h -1, more preferably about 100-2,000 h -1.
The reduction step may be carried out in a reactor. The reactor may be a fixed bed reactor.
In the washings step, the absorbed and reduced gas may be washed with water or an alkyl alcohol. The alkyl alcohol used in the washing step may be methanol, ethanol, propanol or butanol. The alkyl alcohol used in the washing step may be the same as the alkyl alcohol used in absorption step. The molar ratio of the alkyl alcohol or water used in the washing step to the alkyl nitrite used in absorption step may be from about 1: 1 to about 1000: 1 , preferably from about 2: 1 to about 500: 1, more preferably from about 5: 1 to about 300: 1.
The washing step may be carried out in a second absorption tower. The second absorption tower may be a packing tower, a washing tower or a spraying tower.
A system for treating a tail gas having nitrogen oxides and an alkyl nitrite is also provided. The system comprises a first absorption tower, a reactor and a second absorption towner. In the first absorption towner, the tail gas is exposed to an effective amount of an alkyl alcohol in the presence of oxygen to absorb the alkyl nitrite, whereby an absorbed gas is generated. In the reactor, the absorbed gas is exposed to a reducing gas in the presence of an effective amount of a catalyst to reduce the nitrogen oxides, whereby an absorbed and reduced gas is generated. In the second absorption towner, the absorbed and reduced gas is washed. As a result, a treated tail gas is prepared.
The first absorption tower may be a packing tower, a washing tower or a spraying tower. The reactor may be a fixed bed reactor. The second absorption tower may be a packing tower, a washing tower or a spraying tower.
The term “about” as used herein when referring to a measurable value such as an amount, a percentage, and the like, is meant to encompass variations of ±20%or ±10%, more preferably ±5%, even more preferably ±1%, and still more preferably ±0.1%from the specified value, as such variations are appropriate.
Example 1. Treated Gas 1
A tail gas was treated to generate Treated Gas 1. A gas containing nitrogen oxides (NO x) and methyl nitrite (MN) was introduced with air into a first washing tower. The molar ratio of the NO x to the oxygen (O 2) in the air was 1: 10. Methanol was introduced at a molar ratio of methanol to MN at 1: 1 to adsorb MN. The operation pressure was 0.1 MPa. The operation temperature was -30 ℃. The gas exiting from the top of the adsorption tower was passed together with hydrogen (H 2) into a fixed bed reactor equipped containing Pt catalyst for catalytic reduction in the presence of a reducing gas having a molar ratio of the reducing gas to the NO x at 1: 1. The reaction temperature was 500 ℃. The reaction pressure was 0 barG. The gas space velocity was 50 h -1. The reduced gas was passed from the fixed bed reactor into a second washing tower for washing with water at a molar ratio of 1000: 1 for the water to the methyl nitrate before treatment and, after washing, the used water was discarded as waste water. The gas exiting from the top of the washing tower was Treated Gas 1. Treated Gas 1 was then subjected to combustion treatment.
Table 1 shows the key process conditions used to prepare Treated Gas 1 and its methyl nitrite content of 8 ppm and NOx content of 43 ppm.
Example 2: Treated Gas 2
A tail gas was treated to generate Treated Gas 2. A gas containing nitrogen oxides (NO x) and ethyl nitrite was introduced with air into a first packing tower. The molar ratio of NO x to oxygen (O 2) in the air was 10: 1. Ethanol was introduced at a molar ratio of ethanol to ethyl nitrite at 100: 1 to absorb ethyl nitrite. The operation pressure was 1.0 Mpa. The operation temperature was 90℃. The gas existing from the top of the filler tower was passed together with CO into a fixed bed reactor equipped with Pd catalyst for catalytic reduction in the presence of a reducing gas having a molar ratio of the reducing gas to the NO x at 10: 1. The reaction temperature was 50 ℃. The reaction pressure was 10 barG. The gas space velocity was 10,000 h -1. The reduced gas was passed into a second packing tower for washing with ethanol at a molar ratio of 1: 1 for the ethanol to the ethyl nitrite in the tail gas before treatment and, after washing, the used ethanol was introduced into the first packing tower to be reused in the absorption step. The gas exiting from the top of the washing tower was Treated Gas 2. Treated Gas 2 was then subjected to combustion treatment.
Table 1 shows the key process conditions used to prepare Treated Gas 2 and its methyl nitrite content of 9 ppm and nitrogen oxide content of 43 ppm.
Example 3. Treated Gases 3-6 and Comparative Gas 1-3
Addition studies were carried out to treat a tail gas containing nitrogen oxide and alkyl nitrite according the process described in Example except the different conditions indicated in Table 1. Table 1 shows the process conditions used for preparing Treated Gases 3-6 and Comparative Treated Gases 1-3 and their methyl nitrite contents and nitrogen oxide contents.
Table 1. Preparation and properties of Treated Gases 1-6 and Comparative Gases 1-3
Figure PCTCN2018111138-appb-000001
Although the invention is illustrated and described herein with reference to specific embodiments, the invention is not intended to be limited to the details shown. Rather, various modifications may be made in the details within the scope and range of equivalents of the claims without departing from the invention. 

Claims (24)

  1. A process for treating a tail gas having nitrogen oxides and an alkyl nitrite, comprising:
    (a) contacting the tail gas with an effective amount of an alkyl alcohol in the presence of oxygen to absorb the alkyl nitrite, whereby an absorbed gas is generated;
    (b) contacting the absorbed gas with a reducing gas in the presence of an effective amount of a catalyst to reduce the nitrogen oxides, whereby an absorbed and reduced gas is generated; and
    (c) washing the absorbed and reduced gas, whereby a treated tail gas is prepared.
  2. The process of claim 1, wherein the treated tail gas has a nitrogen oxide content less than 50 ppm.
  3. The process of claim 1, wherein the treated tail gas has an alkyl nitrite content less than 10 ppm.
  4. The process of claim 1, wherein the molar ratio of the nitrogen oxides to the oxygen in step (a) is from 1: 10 to 10: 1.
  5. The process of claim 1, wherein the molar ratio of the alkyl alcohol in step (a) to the alkyl nitrite in step (a) is from 1: 1 to 100: 1.
  6. The process of claim 1, wherein the alkyl alcohol is selected from the group consisting of methanol, ethanol, propanol and butanol.
  7. The process of claim 1, wherein step (a) is carried out under an operation pressure of 0.1-1.0 MPa.
  8. The process of claim 1, wherein step (a) is carried out at an operation temperature from -30 ℃ to 90 ℃.
  9. The process of claim 1, wherein step (a) is carried out in a first absorption tower.
  10. The process of claim 9, wherein the first absorption tower is a packing tower, a washing tower or a spraying tower.
  11. The process of claim 1, wherein the molar ratio of the reducing gas to the nitrogen oxides in step (b) is from 1: 1 to 10: 1.
  12. The process of claim 1, wherein the reducing gas comprises H 2, CO, NH 3, or a combination thereof.
  13. The process of claim 1, wherein the catalyst comprises Pd, Pt, Cu, Rh or a combination thereof.
  14. The process of claim 1, wherein step (b) is carried out at a temperature from 50 ℃ to 500 ℃.
  15. The process of claim 1, wherein step (b) is carried out under a pressure of 0-10 barG.
  16. The process of claim 1, wherein step (b) is carried out at a gas space velocity of 50-10,000 h -1.
  17. The process of claim 1, wherein step (b) is carried out in a reactor.
  18. The process of claim 17, wherein the reactor is a fixed bed reactor.
  19. The process of claim 1, wherein the absorbed and reduced gas is washed with water in step (c) .
  20. The process of claim 1, wherein the absorbed and reduced gas is washed with the alkyl alcohol in step (c) .
  21. The process of claim 20, wherein the molar ratio of the alkyl alcohol in step (c) to the alkyl nitrite in step (a) is from 1: 1 to 1000: 1.
  22. The process of claim 20, further comprising introducing the alkyl alcohol after step (c) into step (a) .
  23. The process of claim 1, wherein step (c) is carried out in a second absorption tower.
  24. The process of claim 23, wherein the second absorption tower is a packing tower, a washing tower or a spraying tower.
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US4879401A (en) * 1987-09-29 1989-11-07 Union Carbide Chemicals And Plastics Company Inc. Process for removal of impurities in alkyl nitrite formation
CN101095997A (en) * 2006-06-27 2008-01-02 上海焦化有限公司 Method for expelling nitrous acid alkyl ester and nitrogen oxide gas from the discharged gas
CN106139898A (en) * 2015-04-14 2016-11-23 高化学株式会社 The method of the NO in regeneration, absorption and removing CO carbonyl coupling synthesis of oxalate process tail gas, alkyl nitrite and CO and N2O
CN108329210A (en) * 2018-04-08 2018-07-27 西安汉术化学工程股份有限公司 The recovery system and method for nitric oxide, methyl nitrite in a kind of tail gas of carbonylation dimethyl oxalate

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