CN101362051A - Acrylonitrile device tail-gas treatment technique - Google Patents

Acrylonitrile device tail-gas treatment technique Download PDF

Info

Publication number
CN101362051A
CN101362051A CNA200810200595XA CN200810200595A CN101362051A CN 101362051 A CN101362051 A CN 101362051A CN A200810200595X A CNA200810200595X A CN A200810200595XA CN 200810200595 A CN200810200595 A CN 200810200595A CN 101362051 A CN101362051 A CN 101362051A
Authority
CN
China
Prior art keywords
gas
acrylonitrile
catalyst
tail gas
tail
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
Application number
CNA200810200595XA
Other languages
Chinese (zh)
Inventor
赵小平
王伯超
顾俊璟
周杨炎
张超
张津驰
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.)
DONGHUA ENVIRONMENT ENGINEERING Co Ltd SHANGHAI
Original Assignee
DONGHUA ENVIRONMENT ENGINEERING Co Ltd SHANGHAI
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 DONGHUA ENVIRONMENT ENGINEERING Co Ltd SHANGHAI filed Critical DONGHUA ENVIRONMENT ENGINEERING Co Ltd SHANGHAI
Priority to CNA200810200595XA priority Critical patent/CN101362051A/en
Publication of CN101362051A publication Critical patent/CN101362051A/en
Pending 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals

Abstract

The invention discloses a technique for treating the tail gas of an acrylonitrile device, which is suitable for treating acrylonitrile tail gas discharged by the acrylonitrile device. The technique is characterized in that: after free water is separated out by a gas-liquid separator, the acrylonitrile tail gas is mixed with air, a noble metal monolithic catalyst is taken as a catalyst and catalytic oxidation reaction is carried out to turn harmful volatile organic compounds into carbon dioxide and water; then a selective reduction monolithic catalyst is taken as a catalyst and selective catalytic reduction reaction with added ammonia is carried out to reduce nitrogen oxide in the tail gas into nitrogen and water. The technique has the advantages of simple technique, turning the harmful volatile organic compounds and nitrogen oxide in the tail gas into carbon dioxide, nitrogen and water, without secondary pollution, the test results totally meeting the environmental protection control requirements of the State Standard of China, adopting a tail gas heat exchanger to recycle reaction heat to heat input tail gas, needing no additional fuel during the normal operation process, small system resistance and low operation cost.

Description

Acrylonitrile device tail-gas treatment technique
Technical field
The present invention relates to a kind of in industrial production acrylonitrile process tail gas treatment process, relate in particular to a kind of acrylonitrile device tail-gas treatment technique that adopts catalytic oxidation and catalytic reduction technology.
Background technology
Ammoxidation of propylene technology is adopted in the production of acrylonitrile installation, is primary raw material with propylene, ammonia and air, and under the effect of catalyst, reaction generates acrylonitrile and other byproduct, through over-quenching, recovery, technological process such as refining, obtains the acrylonitrile product afterwards.In removal process, be provided with acrylonitrile absorbing tower, discharge one gas, be referred to as tail gas from absorption tower (AOG) in this column overhead.The main component of acrylonitrile tail gas is nitrogen, water vapour and carbon dioxide, contains a certain amount of carbon monoxide, acrylonitrile, propylene, propane, nitrogen oxide etc. simultaneously, and wherein the harm composition to environment is mainly NMHC and nitrogen oxide.Because organic concentration is low in the tail gas from absorption tower of acrylonitrile installation, toxicity is high, adopts general tail gas treatment process can not satisfy environmental requirement.
Tail gas from absorption tower of acrylonitrile installation generally adopts the directly discharging of the high point of chimney at present, and environment is caused severe contamination.
Also there is part propylene nitrile device to adopt thermal oxidation method such as heating power burning process and heat accumulation type thermal oxidation technology to handle tail gas in addition, but the shortcoming of heating power burning process and heat accumulation type thermal oxidation technology is to need to consume a large amount of fuel, operating cost is higher, and it is bigger to burn capacity, has part nitrogen in the thermal oxidation process and is oxidized to nitrogen oxide.
Patent CN1903415 adopts catalytic oxidation process for treating, NMHC in the tail gas from absorption tower of acrylonitrile installation is converted into carbon dioxide and water, but and reckon without the processing of the another kind of environmental hazard composition nitrogen oxide in the acrylonitrile tail gas, and do not adopt an effective measure gas-liquid separation, the existence of small amount of liquid will reduce the service life of catalyst and the security of boiler in the tail gas.
Summary of the invention
Technical problem to be solved by this invention be propose that a kind of technology is simple, SR is little, need not add auxiliary fuel, do not make catalyst poisoning, operating cost is low, the acrylonitrile device tail-gas treatment technique of non-secondary pollution, thorough tail gas treatment.
In order to achieve the above object, the technical scheme that adopts is: acrylonitrile device tail-gas treatment technique, it is characterized in that: acrylonitrile tail gas mixes with air behind the gas-liquid separator separates free water, after the tail gas heat exchanger heating, enter catalyst oxidation reactor and carry out catalytic oxidation, the catalyst fixed bed noble metal honeycomb catalyst that is provided with of described catalyst oxidation reactor, at pressure 0~30kPa (G), inlet temperature is 100~450 ℃, outlet temperature is under 350~750 ℃ the condition, and harmful volatile organic matter is converted into carbon dioxide and water; The gas that comes out from catalyst oxidation reactor is behind heat reclaim unit recovery section heat, enter catalytic reduction reactor, the mid-selective reduction honeycomb catalyst of described catalytic reduction reactor, at pressure 0~30kPa (G), inlet temperature is 120~500 ℃, outlet temperature is to carry out selective catalytic reduction reaction with the ammonia of adding in 125~600 ℃ the catalytic reduction reactor, and the nitrogen oxide in the tail gas is reduced into the nitrogen G﹠W; At last cleaning of off-gas is entered atmosphere.Described catalyst oxidation reactor and catalytic reduction reactor all adopt fixed bed catalytic reactor.
The inlet temperature of described catalyst oxidation reactor is preferably 300 ℃; Outlet temperature is preferably in below 700 ℃.
The inlet temperature of described catalytic reduction reactor is preferably 400 ℃; Outlet temperature is preferably in below 500 ℃.
The noble metal honeycomb catalyst is noble metal honeycomb metallic catalyst or noble metal ceramic honeycomb catalyst in the described catalyst oxidation reactor, and the noble metal in the noble metal honeycomb catalyst is the combination of any one or two kinds of noble metals in platinum, the palladium.
As the preferred technical solution of the present invention, behind catalyst oxidation reactor tail gas discharged process heat reclaim unit tail gas heat exchanger recovery section energy, enter catalytic reduction reactor.The selective reduction honeycomb catalyst that is equipped with in the described catalytic reduction reactor is the vanadium/titanium/tungsten ceramic honeycomb catalyst that contains vanadium, titanium, tungsten.
As another optimal technical scheme of the present invention, behind catalyst oxidation reactor tail gas discharged process heat reclaim unit steam superheater and waste heat boiler recovery section energy, enter catalytic reduction reactor, directly enter atmosphere behind cleaning of off-gas or the process tail gas heat exchanger recovery section heat; Or the part cleaning of off-gas returned by circulating fan and with enter tail gas heat exchanger again after acrylonitrile tail gas mixes, enter catalyst oxidation reactor then and carry out catalytic oxidation, the part cleaning of off-gas directly enters atmosphere.
As the preferred technical solution of the present invention, acrylonitrile tail gas enters catalyst oxidation reactor with after air mixes after tail gas heat exchanger is heated to the catalyst initiation temperature.
As the preferred technical solution of the present invention, enter catalyst oxidation reactor after the preheating of acrylonitrile tail gas heater via when system's intensification goes into operation and carry out catalytic oxidation.
Carry out the system's heater go into operation that heats up and to adopt steam heater or electric heater or oil burner or gas burner; Tail gas heat exchanger is preferably welded plate type heat exchanger or heat exchange of heat pipe or finned tube exchanger.
There is the bypass valve of a conditioned reaction device inlet temperature described catalyst oxidation reactor porch.
As catalytic oxidation mechanism of the present invention, following chemical reaction has mainly taken place in the catalyst oxidation reactor:
4C 3H 3N+15O 2=12CO 2+6H 2O+2N 2+Q
2CO+O 2=2CO 2+Q
2C 3H 6+9O 2=6CO 2+6H 2O+Q
C 3H 8+5O 2=3CO 2+4H 2O+Q
4C 2H 3N+11O 2=8CO 2+6H 2O+2N 2+Q
As catalytic reduction mechanism of the present invention, following chemical reaction has mainly taken place in the catalytic reduction reactor:
4NH 3+4NO+O 2=4N 2+6H 2O+Q
4NH 3+2NO 2+O 2=3N 2+6H 2O+Q
Advantage of the present invention is: technology of the present invention is simple, with volatile organic matter and conversion of nitrogen oxides harmful in the acrylonitrile installation tail gas is carbon dioxide, water and nitrogen, non-secondary pollution, thorough tail gas treatment, testing result satisfy the environment protection control requirements of national Specification fully; In addition, the present invention has very broad opereating specification, and in the time of can guaranteeing that organic matter and amount of nitrogen oxides change in the acrylonitrile tail gas, system can stable operation; The catalyst that the present invention adopts, mechanical strength height, long service life, resistance are low; At last, the present invention adopts high-efficiency heat pipe heat exchanger, welded plate type heat exchanger and finned tube exchanger to reclaim reaction heat to add hot feed tail gas, need not additional fuel in the normal course of operation.
Description of drawings
Fig. 1 (uses tail gas heat exchanger recovery section heat for the process chart of acrylonitrile device tail-gas treatment technique of the present invention; The cleaning of off-gas emptying does not circulate);
Fig. 2 (uses steam superheater and waste heat boiler recovery section heat for the process chart of acrylonitrile device tail-gas treatment technique of the present invention; Emptying behind the cleaning of off-gas process tail gas heat exchanger recovery section heat);
Fig. 3 (uses steam superheater and waste heat boiler recovery section heat for the process chart of acrylonitrile device tail-gas treatment technique of the present invention; A part participates in circulation through tail gas heat exchanger again in the cleaning of off-gas).
Among the figure: 1 is gas-liquid separator; 2 is air-blaster; 3 is tail gas heat exchanger; 4 is electric heater or steam heater; 5 is catalyst oxidation reactor; 6 is steam superheater; 7 is waste heat boiler; 8 is catalytic reduction reactor; 9 is circulating fan; 10 is chimney.
The specific embodiment
Below in conjunction with drawings and Examples technology of the present invention is further elaborated.
By Fig. 1~3 as seen: acrylonitrile device tail-gas treatment technique, it is characterized in that: acrylonitrile tail gas at first enters gas-liquid separator 1 separated free water, mix with air by air-blaster 2 then, and with after tail gas heat exchanger 3 heating, enter catalyst oxidation reactor 5 and carry out catalytic oxidation, the catalyst fixed bed noble metal honeycomb catalyst that is provided with of described catalyst oxidation reactor 5, at pressure 0~30kPa (G), inlet temperature is 100~450 ℃, outlet temperature is under 350~750 ℃ the condition, and harmful volatile organic matter is converted into carbon dioxide and water; The gas that comes out from catalyst oxidation reactor 5 is behind heat reclaim unit recovery section heat, enter catalytic reduction reactor 8 and carry out catalytic reduction reaction, the catalyst fixed bed selective reduction honeycomb catalyst that is provided with of described catalytic reduction reactor 8, at pressure 0~30kPa (G), inlet temperature is 120~500 ℃, outlet temperature is under 125~600 ℃ the condition, the nitrogen oxide in the tail gas is carried out selective catalytic reduction reaction with the ammonia of adding change into the nitrogen G﹠W; Final purification tail gas enters atmosphere.
Described catalyst oxidation reactor 5 inlet temperatures are preferably 300 ℃, and outlet temperature is preferably below 700 ℃.
Described catalytic reduction reactor 8 inlet temperatures are preferably 400 ℃; Outlet temperature is preferably in below 500 ℃.
Described noble metal honeycomb catalyst is noble metal honeycomb metallic catalyst or noble metal ceramic honeycomb catalyst.Noble metal in the described noble metal catalyst is the combination of any one or two kinds of noble metals in platinum, the palladium.
Described selective reduction honeycomb catalyst is vanadium/titanium/tungsten ceramic honeycomb catalyst.
The preferred version of described recovery section heat is for entering catalytic reduction reactor 8 behind catalyst oxidation reactor 5 tail gas discharged process tail gas heat exchanger 3 recovery section energy.
Another preferred version of described recovery section heat directly enters atmosphere for enter catalytic reduction reactor 8 behind catalyst oxidation reactor 5 tail gas discharged process steam superheater 6 and waste heat boiler 7 recovery section energy behind the cleaning of off-gas process tail gas heat exchanger 3 recovery section heats.
A preferred version again of described recovery section heat is for entering catalytic reduction reactor 8 behind catalyst oxidation reactor 5 tail gas discharged process steam superheater 6 and waste heat boiler 7 recovery section energy, cleaning of off-gas is through behind the tail gas heat exchanger 3 recovery section heats, wherein a part of cleaning of off-gas return by circulating fan 9 and with enter tail gas heat exchanger 3 participation process cycles again after acrylonitrile tail gas mixes.
Acrylonitrile tail gas enters catalyst oxidation reactor 5 with after air mixes after tail gas heat exchanger 3 is heated to the catalyst initiation temperature.Described tail gas heat exchanger 3 is welded plate type heat exchanger or heat exchange of heat pipe or finned tube exchanger.
Enter catalyst oxidation reactor 5 after 4 preheatings of acrylonitrile tail gas heater via when system's intensification goes into operation and carry out catalytic oxidation.Carry out heater 4 employing steam heater or electric heater or oil burner or the gas burners that system heats up and goes into operation.
There is the bypass valve of a conditioned reaction device inlet temperature described catalyst oxidation reactor 5 porch.Tail gas among the embodiment derives from certain company's acrylonitrile installation, and working condition is as shown in table 1.
Certain company's acrylonitrile installation tail gas of table 1 is formed
Exhaust gas component Form (w%)
Propane 0.0026-0.0060
Propylene 0.0018-0.0029
Acrylonitrile 0.0001
Carbon monoxide 1.20
Carbon dioxide 3.25
Water 3.62
Oxygen 1.10
Acetonitrile 0.0032
NO X 0.068
Nitrogen 89.72
Add up to 100
Unstripped gas adds up to Kg/h 100000
Temperature ℃ 35
Pressure kPa (G) 20
Embodiment 1
After tail gas and air mix through after tail gas heat exchanger 3 and/or electric heater 4 heating, inlet temperature is 280 ℃, enter catalyst oxidation reactor 5 and on the noble metal platinum that places catalyst fixed bed layer, palladium honeycomb metallic catalyst, carry out catalytic oxidation, keep catalyst oxidation reactor 5 internal pressures to be about 16kPa (G), harmful volatile organic matter is converted into carbon dioxide and water, and discharging a large amount of heat, outlet temperature is 650 ℃.The gas that comes out from catalyst oxidation reactor 5 enters that temperature is 350 ℃ behind the tail gas heat exchanger 3 recovery section heats, enter catalytic reduction reactor 8, carry out catalytic reduction reaction at the vanadium/titanium/tungsten ceramic honeycomb catalyst that places catalyst fixed bed layer, keep catalytic reduction reactor 8 internal pressures to be about 12kPa (G), nitrogen oxide in the tail gas carries out selective catalytic reduction reaction with the ammonia of adding and becomes the nitrogen G﹠W, outlet temperature is 375 ℃, at last cleaning of off-gas is entered atmosphere.
Detect sending into the laboratory after the discharging gas sampling after handling, the content detection result of acrylonitrile, NMHC and nitrogen oxide is as shown in table 2 in the cleaning of off-gas.
Certain economizes environmental monitoring central station Monitoring Data and control index table 2
The pollutant title Concentration of emission Concentration of emission evaluation criterion (mg/m 3)
Acrylonitrile 15 22
NMHC 105 120
Nitrogen oxide NOx 170 240
Annotate: concentration of emission is repeatedly the mean value of sampling in the table
Embodiment 2
Catalyst oxidation reactor 5 adopts platinum honeycomb metallic catalysts, and catalyst oxidation reactor 5 internal pressures are about 5kPa (G), inlet temperature and are about 150 ℃, outlet temperature and are about 460 ℃; Catalytic reduction reactor 8 adopts vanadium/titanium/tungsten ceramic honeycomb catalysts, and catalytic reduction reactor 8 internal pressures are about 3kPa (G), inlet temperature and are about 150 ℃, outlet temperature and are about 160 ℃, and all the other are with embodiment 1.After testing, acrylonitrile concentration is 20mg/m in the cleaning of off-gas 3, amount of nitrogen oxides is 220mg/m 3, the content of NMHC is 116mg/m 3, reach national discharge standard of air pollutants.
Embodiment 3
Catalyst oxidation reactor 5 adopts palladium honeycomb metallic catalysts, and catalyst oxidation reactor 5 internal pressures are about 10kPa (G), inlet temperature and are about 200 ℃, outlet temperature and are about 510 ℃; Catalytic reduction reactor 8 adopts vanadium/titanium/tungsten ceramic honeycomb catalysts, and catalytic reduction reactor 8 internal pressures are about 8kPa (G), inlet temperature and are about 185 ℃, outlet temperature and are about 200 ℃, and all the other are with embodiment 1.After testing, acrylonitrile concentration is 19mg/m in the cleaning of off-gas 3, amount of nitrogen oxides is 200mg/m 3, the content of NMHC is 112mg/m 3, reach national discharge standard of air pollutants.
Embodiment 4
Catalyst oxidation reactor 5 adopts the platinum ceramic honeycomb catalysts, and catalyst oxidation reactor 5 internal pressures are about 14kPa (G), inlet temperature and are about 240 ℃, outlet temperature and are about 540 ℃; Catalytic reduction reactor 8 adopts vanadium/titanium/tungsten ceramic honeycomb catalysts, and catalytic reduction reactor 8 internal pressures are about 10kPa (G), inlet temperature and are about 220 ℃, outlet temperature and are about 240 ℃, and all the other are with embodiment 1.After testing, acrylonitrile concentration is 18mg/m in the cleaning of off-gas 3, amount of nitrogen oxides is 180mg/m 3, the content of NMHC is 108mg/m 3, reach national discharge standard of air pollutants.
Embodiment 5
After tail gas and air mix through after tail gas heat exchanger 3 and/or electric heater 4 heating, inlet temperature is 300 ℃, enter catalyst oxidation reactor 5, on the noble metal platinum that places catalyst fixed bed layer, palladium honeycomb metallic catalyst, carry out catalytic oxidation, keep catalyst oxidation reactor 5 internal pressures to be about 20kPa (G), harmful volatile organic matter is converted into carbon dioxide and water, and discharges a large amount of heat, outlet temperature is 620 ℃.The gas that comes out from catalyst oxidation reactor 5 enters that temperature is 380 ℃ behind steam superheater 7 and the waste heat boiler 8 recovery section heats, enter catalytic reduction reactor 8, place the vanadium/titanium/tungsten ceramic honeycomb catalyst of catalyst fixed bed layer to carry out catalytic reduction reaction, keep catalytic reduction reactor 8 internal pressures to be about 15kPa (G), nitrogen oxide in the tail gas carries out selective catalytic reduction reaction with the ammonia of adding and becomes the nitrogen G﹠W, outlet temperature is 400 ℃, enters at last to enter atmosphere after heat is reclaimed in tail gas heat exchanger 3 heat exchanges.
Detect sending into the laboratory after the discharging gas sampling after handling, the content detection result of acrylonitrile, NMHC and nitrogen oxide is as shown in table 3 in the cleaning of off-gas.
Certain economizes environmental monitoring central station Monitoring Data and control index table 3
The pollutant title Concentration of emission Concentration of emission evaluation criterion (mg/m 3)
Acrylonitrile 15 22
NMHC 105 120
Nitrogen oxide NOx 160 240
Annotate: concentration of emission is repeatedly the mean value of sampling in the table.
Embodiment 6
Catalyst oxidation reactor 5 adopts palladium honeycomb metallic catalysts, and catalyst oxidation reactor 5 internal pressures are about 15kPa (G), inlet temperature and are about 300 ℃, outlet temperature and are about 590 ℃; Catalytic reduction reactor 8 adopts vanadium/titanium/tungsten ceramic honeycomb catalysts, and catalytic reduction reactor 8 internal pressures are about 11kPa (G), inlet temperature and are about 280 ℃, outlet temperature and are about 300 ℃, and all the other are with embodiment 5.After testing, acrylonitrile concentration is 16mg/m in the cleaning of off-gas 3, amount of nitrogen oxides is 150mg/m 3, the content of NMHC is 105mg/m 3, reach national discharge standard of air pollutants.
Embodiment 7
Catalyst oxidation reactor 5 adopts platinum honeycomb metallic catalysts, and catalyst oxidation reactor 5 internal pressures are about 22kPa (G), inlet temperature and are about 340 ℃, outlet temperature and are about 660 ℃; Catalytic reduction reactor 8 adopts vanadium/titanium/tungsten ceramic honeycomb catalysts, and catalytic reduction reactor 8 internal pressures are about 17kPa (G), inlet temperature and are about 320 ℃, outlet temperature and are about 340 ℃, and all the other are with embodiment 5.After testing, acrylonitrile concentration is 15mg/m in the cleaning of off-gas 3, amount of nitrogen oxides is 140mg/m 3, the content of NMHC is 102mg/m 3, reach national discharge standard of air pollutants.
Embodiment 8
Catalyst oxidation reactor 5 adopts the palladium ceramic honeycomb catalysts, and catalyst oxidation reactor 5 internal pressures are about 25kPa (G), inlet temperature and are about 360 ℃, outlet temperature and are about 675 ℃; Catalytic reduction reactor 8 adopts vanadium/titanium/tungsten ceramic honeycomb catalysts, and catalytic reduction reactor 8 internal pressures are about 18kPa (G), inlet temperature and are about 360 ℃, outlet temperature and are about 380 ℃, and all the other are with embodiment 5.After testing, acrylonitrile concentration is 13mg/m in the cleaning of off-gas 3, amount of nitrogen oxides is 125mg/m 3, the content of NMHC is 98mg/m 3, reach national discharge standard of air pollutants.
Embodiment 9
After mixing, tail gas and air heat through tail gas heat exchanger 3 and/or electric heater 4, inlet temperature is 260 ℃, enter catalyst oxidation reactor 5, on the noble metal platinum that places catalyst fixed bed layer, palladium honeycomb metallic catalyst, carry out catalytic oxidation, keep catalyst oxidation reactor 5 internal pressures to be about 18kPa (G), harmful volatile organic matter is converted into carbon dioxide and water, and discharges a large amount of heat, outlet temperature is 630 ℃.After the gas that comes out from catalyst oxidation reactor 5 enters steam superheater 7 and waste heat boiler 8 recovery section heats, enter catalytic reduction reactor 8 and carry out catalytic reduction reaction, catalytic reduction reactor 8 inlet temperatures are 360 ℃.Tail gas carries out catalytic reduction reaction at the vanadium/titanium/tungsten ceramic honeycomb catalyst that places catalyst fixed bed layer, keep catalytic reduction reactor 8 internal pressures to be about 12kPa (G), temperature is about 380 ℃, nitrogen oxide in the tail gas carries out selective catalytic reduction reaction with the ammonia of adding and becomes the nitrogen G﹠W, and outlet temperature is 400 ℃.Final purification tail gas enter tail gas heat exchanger 3 heat exchanges reclaim heat after a part directly enter atmosphere, a part by circulating fan 9 with enter tail gas heat exchanger 3 again after acrylonitrile tail gas mixes.
Detect the content detection result of NMHC (concentration of emission is repeatedly the mean value of sampling) as shown in table 4 in the cleaning of off-gas to sending into the laboratory after the discharging gas sampling after handling.
Certain economizes environmental monitoring central station Monitoring Data and control index table 4
The pollutant title Concentration of emission Concentration of emission evaluation criterion (mg/m 3)
Acrylonitrile 15 22
NMHC 101 120
Nitrogen oxide NOx 160 240
Embodiment 10
Catalyst oxidation reactor 5 adopts platinum honeycomb metallic catalysts, and catalyst oxidation reactor 5 internal pressures are about 28kPa (G), inlet temperature and are about 400 ℃, outlet temperature and are about 720 ℃; Catalytic reduction reactor 8 adopts vanadium/titanium/tungsten ceramic honeycomb catalysts, and catalytic reduction reactor 8 internal pressures are about 20kPa (G), inlet temperature and are about 400 ℃, outlet temperature and are about 420 ℃, and all the other are with embodiment 9.After testing, acrylonitrile concentration is 12mg/m in the cleaning of off-gas 3, amount of nitrogen oxides is 110mg/m 3, the content of NMHC is 95mg/m 3, reach national discharge standard of air pollutants.
Embodiment 11
Catalyst oxidation reactor 5 adopts palladium honeycomb metallic catalysts, and catalyst oxidation reactor 5 internal pressures are about 27kPa (G), inlet temperature and are about 380 ℃, outlet temperature and are about 710 ℃; Catalytic reduction reactor 8 adopts vanadium/titanium/tungsten ceramic honeycomb catalysts, and catalytic reduction reactor 8 internal pressures are about 18kPa (G), inlet temperature and are about 450 ℃, outlet temperature and are about 480 ℃, and all the other are with embodiment 9.After testing, acrylonitrile concentration is 10mg/m in the cleaning of off-gas 3, amount of nitrogen oxides is 100mg/m 3, the content of NMHC is 92mg/m 3, reach national discharge standard of air pollutants.
Embodiment 12
Catalyst oxidation reactor 5 adopts the platinum ceramic honeycomb catalysts, and catalyst oxidation reactor 5 internal pressures are about 28kPa (G), inlet temperature and are about 440 ℃, outlet temperature and are about 750 ℃; Catalytic reduction reactor 8 adopts vanadium/titanium/tungsten ceramic honeycomb catalysts, and catalytic reduction reactor 8 internal pressures are about 18kPa (G), inlet temperature and are about 500 ℃, outlet temperature and are about 550 ℃, and all the other are with embodiment 9.After testing, acrylonitrile concentration is 8mg/m in the cleaning of off-gas 3, amount of nitrogen oxides is 90mg/m 3, the content of NMHC is 88mg/m 3, reach national discharge standard of air pollutants.
Certain company's acrylonitrile emission-control equipment builds up and comes into operation, be subjected to the trust of China Environmental Monitoring General Station, certain economizes the requirement of environmental monitoring central station according to China Environmental Monitoring General Station, the acrylonitrile emission-control equipment has been carried out the spot sampling monitoring checked and accepted, testing result satisfies the environment protection control requirements of national Specification fully.

Claims (15)

1, the treatment process of acrylonitrile installation tail gas, it is characterized in that acrylonitrile tail gas at first enters gas-liquid separator (1) separated free water, mix with air then, after tail gas heat exchanger (3) heating, enter catalyst oxidation reactor (5) and carry out catalytic oxidation, the catalyst fixed bed noble metal honeycomb catalyst that is provided with of described catalyst oxidation reactor (5), at pressure 0~30kPa (G), inlet temperature is 100~450 ℃, outlet temperature is under 350~750 ℃ the condition, and harmful volatile organic matter is converted into carbon dioxide and water; The gas that comes out from catalyst oxidation reactor (5) is behind heat reclaim unit recovery section heat, enter catalytic reduction reactor (8) and carry out catalytic reduction reaction, the catalyst fixed bed selective reduction honeycomb catalyst that is provided with of described catalytic reduction reactor (8), at pressure 0~30kPa (G), inlet temperature is 120~500 ℃, outlet temperature is under 125~600 ℃ the condition, the nitrogen oxide in the tail gas is carried out selective catalytic reduction reaction with the ammonia of adding change into the nitrogen G﹠W.
2, acrylonitrile device tail-gas treatment technique according to claim 1 is characterized in that: catalyst oxidation reactor (5) inlet temperature is preferably 300 ℃, and outlet temperature is preferably below 700 ℃.
3, acrylonitrile device tail-gas treatment technique according to claim 1 is characterized in that: catalytic reduction reactor (8) inlet temperature is preferably 400 ℃, and outlet temperature is preferably below 500 ℃.
4, acrylonitrile device tail-gas treatment technique according to claim 1 is characterized in that: described noble metal honeycomb catalyst is noble metal honeycomb metallic catalyst or noble metal ceramic honeycomb catalyst.
5, acrylonitrile device tail-gas treatment technique according to claim 1 is characterized in that: the noble metal in the described noble metal honeycomb catalyst is the combination of any one or two kinds of noble metals in platinum, the palladium.
6, acrylonitrile device tail-gas treatment technique according to claim 1 is characterized in that: described selective reduction honeycomb catalyst is vanadium/titanium/tungsten ceramic honeycomb catalyst.
7, acrylonitrile device tail-gas treatment technique according to claim 1 is characterized in that: acrylonitrile installation tail gas enters catalyst oxidation reactor (5) with after air or oxygen mixes after tail gas heat exchanger (3) is heated to the catalyst initiation temperature.
8, acrylonitrile device tail-gas treatment technique according to claim 1 is characterized in that: the technology of described recovery section heat is for entering catalytic reduction reactor (8) behind catalyst oxidation reactor (5) tail gas discharged process steam superheater (6) and waste heat boiler (7) recovery section energy.
9, acrylonitrile device tail-gas treatment technique according to claim 8 is characterized in that: directly enter atmosphere after the described cleaning of off-gas that comes out from catalytic reduction reactor (8) reclaims heat through tail gas heat exchanger (3).
10, acrylonitrile device tail-gas treatment technique according to claim 8, it is characterized in that: after the described cleaning of off-gas that comes out from catalytic reduction reactor (8) reclaims heat through tail gas heat exchanger (3), the part cleaning of off-gas return by circulating fan (9) and with enter tail gas heat exchanger (3) again after pending acrylonitrile tail gas mixes.
11, acrylonitrile device tail-gas treatment technique according to claim 1 is characterized in that: described tail gas heat exchanger (3) is welded plate type heat exchanger or heat exchange of heat pipe or finned tube exchanger.
12, acrylonitrile device tail-gas treatment technique according to claim 1 is characterized in that system heats up to enter catalyst oxidation reactor (5) after acrylonitrile tail gas heater via (4) preheating when going into operation and carry out catalytic oxidation.
13, acrylonitrile device tail-gas treatment technique according to claim 12 is characterized in that: carry out heater (4) employing steam heater or electric heater or oil burner or gas burner that system heats up and goes into operation.
14, acrylonitrile device tail-gas treatment technique according to claim 1 is characterized in that: there is the bypass valve of a conditioned reaction device inlet temperature described catalyst oxidation reactor (5) porch.
15, acrylonitrile device tail-gas treatment technique according to claim 1 is characterized in that: described catalyst oxidation reactor and catalytic reduction reactor all adopt fixed bed catalytic reactor.
CNA200810200595XA 2008-09-27 2008-09-27 Acrylonitrile device tail-gas treatment technique Pending CN101362051A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CNA200810200595XA CN101362051A (en) 2008-09-27 2008-09-27 Acrylonitrile device tail-gas treatment technique

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CNA200810200595XA CN101362051A (en) 2008-09-27 2008-09-27 Acrylonitrile device tail-gas treatment technique

Publications (1)

Publication Number Publication Date
CN101362051A true CN101362051A (en) 2009-02-11

Family

ID=40388768

Family Applications (1)

Application Number Title Priority Date Filing Date
CNA200810200595XA Pending CN101362051A (en) 2008-09-27 2008-09-27 Acrylonitrile device tail-gas treatment technique

Country Status (1)

Country Link
CN (1) CN101362051A (en)

Cited By (15)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102233231A (en) * 2011-07-21 2011-11-09 上海师范大学 Purification equipment and treatment process for tail gas from acrylonitrile absorption tower
CN102773120A (en) * 2012-07-17 2012-11-14 无锡威孚环保催化剂有限公司 Honeycomb catalyst for acrylonitrile device waste gas purification and preparation method thereof
CN102865585A (en) * 2012-09-21 2013-01-09 上海凯鸿环保工程有限公司 Sealed heating system and heating method
CN102872692A (en) * 2012-09-19 2013-01-16 上海凯鸿环保工程有限公司 Operation control system for acrylonitrile absorption tower tail gas treatment
CN103657404A (en) * 2013-12-06 2014-03-26 上海凯鸿环保工程有限公司 Tail gas catalysis combustion treatment system
CN104534486A (en) * 2014-12-18 2015-04-22 濮阳市华星化工有限公司 Cyanide-containing waste water treatment system
CN104772038A (en) * 2015-03-25 2015-07-15 中国石油天然气股份有限公司 Method for purifying acrylonitrile apparatus absorbing tower tail gas by using Pd-CeO2/Me-beta molecular sieve
CN104772037A (en) * 2015-03-25 2015-07-15 中国石油天然气股份有限公司 Method for purifying acrylonitrile apparatus absorbing tower tail gas by using Pd-CeO2/Me-SAPO molecular sieve
CN105605595A (en) * 2016-01-12 2016-05-25 北京化工大学 Integrated purification method and system for industrial waste gas containing cyanogen, hydrocarbon and NOx
CN107118293A (en) * 2017-05-22 2017-09-01 北京华福工程有限公司 A kind of method and system that polyacrylic acid is prepared with calcium carbide stove exhaust
CN108654369A (en) * 2018-07-03 2018-10-16 王氏港建贸易(上海)有限公司 A kind of scaling powder processing system and the reflow oven comprising it
CN109550388A (en) * 2017-09-25 2019-04-02 重展(上海)实业有限公司 House exhaust processing unit
CN113617224A (en) * 2021-08-23 2021-11-09 湖州乙戈环保设备有限公司 Treatment device and treatment method for nitrogen oxide waste gas for high-speed wire enamelling machine
CN114682086A (en) * 2020-12-31 2022-07-01 中国石油化工股份有限公司 Method and device for treating nitrogen-containing organic waste gas
CN116550121A (en) * 2022-09-13 2023-08-08 上海东化环境工程有限公司 Tail gas purifying treatment method for propane dehydrogenation device

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001213857A (en) * 2000-02-01 2001-08-07 Takuma Co Ltd Method of recovery and recovery system for acrylonitrile
CN1903415A (en) * 2005-07-27 2007-01-31 上海东化环境工程有限公司 Catalytic oxidation process for treating tail gas from absorption tower of acrylonitrile installation
CN1903412A (en) * 2005-07-27 2007-01-31 上海东化环境工程有限公司 Process for catalytic reduction treatment of waste-air contg. nitrogen oxiden
CN1903413A (en) * 2005-07-27 2007-01-31 上海东化环境工程有限公司 Process for treating waste-gas contg. acrylic acid

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001213857A (en) * 2000-02-01 2001-08-07 Takuma Co Ltd Method of recovery and recovery system for acrylonitrile
CN1903415A (en) * 2005-07-27 2007-01-31 上海东化环境工程有限公司 Catalytic oxidation process for treating tail gas from absorption tower of acrylonitrile installation
CN1903412A (en) * 2005-07-27 2007-01-31 上海东化环境工程有限公司 Process for catalytic reduction treatment of waste-air contg. nitrogen oxiden
CN1903413A (en) * 2005-07-27 2007-01-31 上海东化环境工程有限公司 Process for treating waste-gas contg. acrylic acid

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
崔金栋等: "丙烯腈气液分离器放大规律研究及工业应用", 《石油化工设备技术》 *
朱晓苓等: "催化燃烧法处理丙烯腈生产废气", 《上海环境科学》 *
李新城: "丙烯腈装置吸收塔尾气处理技术分析", 《化工设计》 *

Cited By (17)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102233231A (en) * 2011-07-21 2011-11-09 上海师范大学 Purification equipment and treatment process for tail gas from acrylonitrile absorption tower
CN102773120A (en) * 2012-07-17 2012-11-14 无锡威孚环保催化剂有限公司 Honeycomb catalyst for acrylonitrile device waste gas purification and preparation method thereof
CN102872692A (en) * 2012-09-19 2013-01-16 上海凯鸿环保工程有限公司 Operation control system for acrylonitrile absorption tower tail gas treatment
CN102865585A (en) * 2012-09-21 2013-01-09 上海凯鸿环保工程有限公司 Sealed heating system and heating method
CN103657404A (en) * 2013-12-06 2014-03-26 上海凯鸿环保工程有限公司 Tail gas catalysis combustion treatment system
CN104534486A (en) * 2014-12-18 2015-04-22 濮阳市华星化工有限公司 Cyanide-containing waste water treatment system
CN104772038A (en) * 2015-03-25 2015-07-15 中国石油天然气股份有限公司 Method for purifying acrylonitrile apparatus absorbing tower tail gas by using Pd-CeO2/Me-beta molecular sieve
CN104772037A (en) * 2015-03-25 2015-07-15 中国石油天然气股份有限公司 Method for purifying acrylonitrile apparatus absorbing tower tail gas by using Pd-CeO2/Me-SAPO molecular sieve
CN105605595A (en) * 2016-01-12 2016-05-25 北京化工大学 Integrated purification method and system for industrial waste gas containing cyanogen, hydrocarbon and NOx
WO2017121022A1 (en) * 2016-01-12 2017-07-20 北京化工大学 Integrated purification method and system for industrial waste gas containing cyanides, hydrocarbons and nox
US10315160B2 (en) 2016-01-12 2019-06-11 Beijing University Of Chemical Technology Integrated purification method and system for the industrial exhaust gas containing cyanides, hydrocarbons and NOx
CN107118293A (en) * 2017-05-22 2017-09-01 北京华福工程有限公司 A kind of method and system that polyacrylic acid is prepared with calcium carbide stove exhaust
CN109550388A (en) * 2017-09-25 2019-04-02 重展(上海)实业有限公司 House exhaust processing unit
CN108654369A (en) * 2018-07-03 2018-10-16 王氏港建贸易(上海)有限公司 A kind of scaling powder processing system and the reflow oven comprising it
CN114682086A (en) * 2020-12-31 2022-07-01 中国石油化工股份有限公司 Method and device for treating nitrogen-containing organic waste gas
CN113617224A (en) * 2021-08-23 2021-11-09 湖州乙戈环保设备有限公司 Treatment device and treatment method for nitrogen oxide waste gas for high-speed wire enamelling machine
CN116550121A (en) * 2022-09-13 2023-08-08 上海东化环境工程有限公司 Tail gas purifying treatment method for propane dehydrogenation device

Similar Documents

Publication Publication Date Title
CN101362051A (en) Acrylonitrile device tail-gas treatment technique
CN105605595B (en) The industrial waste gas integrated purifying method and system of class containing cyanogen, hydro carbons and NOx
US11667794B2 (en) Methods and systems for particulate matter removal from a process exhaust gas stream
CN101301580A (en) Tail gas treatment process of butane method maleic anhydride device
US8404200B2 (en) Cold selective catalytic reduction
CN103657404A (en) Tail gas catalysis combustion treatment system
CN107416963B (en) One-step combined purification method for (methyl) acrylic acid and (methyl) acrylic acid ester rectification residual liquid and wastewater
CN102470320A (en) Process and apparatus for denoxing of flue gases
US9067827B2 (en) Method and installation for producing cement clinker
RU2501596C2 (en) Method and plant for purification of combustion gases containing nitrogen oxides
JP2022522202A (en) Industrial exhaust gas storage / reduction / denitration system and method
CN100417433C (en) Catalytic oxidation process for treating tail gas from absorption tower of acrylonitrile installation
KR20130084983A (en) A process for removing nitrous oxide from a gas stream
CN103047662A (en) Catalytic combustion treatment device and treatment method for organic waste gases
CN101301578A (en) Catalytic oxidation process technique of benzene method maleic anhydride device tail gas
CN101301577A (en) Catalytic oxidation process technique of phenol-acetone device tail gas
US8029750B2 (en) Process and device for removal of exhaust gases
CN100417430C (en) Process for catalytic reduction treatment of waste-air contg. nitrogen oxiden
CN101785970A (en) Catalytic oxidation treatment process for carbon fiber oxidation unit tail gas
KR101910205B1 (en) A process for removing nitrous oxide from a gas stream
CN109012753A (en) A kind of preparation method of denitration catalyst carrier
CN113144842A (en) Waste gas treatment system
CN112844038B (en) Exhaust gas treatment system and exhaust gas treatment method
JPH11304132A (en) Apparatus and method for treating exhaust gas
CN113929247B (en) Vanadium-containing wastewater treatment method, vanadium-containing catalyst, preparation method and application

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C02 Deemed withdrawal of patent application after publication (patent law 2001)
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20090211