CN1425486A - Recovery technology for volatile organism in mixed gas - Google Patents

Recovery technology for volatile organism in mixed gas Download PDF

Info

Publication number
CN1425486A
CN1425486A CN 02137836 CN02137836A CN1425486A CN 1425486 A CN1425486 A CN 1425486A CN 02137836 CN02137836 CN 02137836 CN 02137836 A CN02137836 A CN 02137836A CN 1425486 A CN1425486 A CN 1425486A
Authority
CN
China
Prior art keywords
gas
organic matter
recovery
mist
separation
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.)
Granted
Application number
CN 02137836
Other languages
Chinese (zh)
Other versions
CN1248767C (en
Inventor
王祥云
谭念华
储政
毛松柏
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.)
Research Institute of Sinopec Nanjing Chemical Industry Co Ltd
Original Assignee
Research Institute of Nanjing Chemical Industry Group 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 Research Institute of Nanjing Chemical Industry Group Co Ltd filed Critical Research Institute of Nanjing Chemical Industry Group Co Ltd
Priority to CN 02137836 priority Critical patent/CN1248767C/en
Publication of CN1425486A publication Critical patent/CN1425486A/en
Application granted granted Critical
Publication of CN1248767C publication Critical patent/CN1248767C/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Images

Landscapes

  • Separation Of Gases By Adsorption (AREA)
  • Treating Waste Gases (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

The present invention relates to environment protection technology, and comprehensive compression and condensation separation-cascade membrane separation-adsorption separation recovering technology for mixed gas containing organic volatile of different composition and density. The said technology can recover toxic organic volatile up to 95-99% from mixed gas to make the mixed gas reach exhaust standard without secondary pollution. Experiments show that the technology of the present invention is practical, stable, reliable and low in recovering cost.

Description

The recovery technology of volatile organic matter in the mist
Technical field: the invention belongs to environmental protection technical field, mainly is the mist at the volatile organic matter that contains different compositions and concentration.
Background technology: VOC (Volatile Organic Compounds, be called for short VOCs) be a kind of common pollutant, its main source has toxic emission in the industries such as petrochemical industry, pharmacy, organic solvent volatilization in the technologies such as textile industry (melt spinning method), printed electronic circuit board manufacturing industry, paint, coating and process hides or the like.Most in the above-mentioned volatile organic matter owing to economically valuable should be reclaimed; Part is because toxic, can cause secondary pollution after can't thoroughly removing or handle with additive method (as burning method etc.), can not reach environmental requirement, and can only be reclaimed.Absorption method commonly used has carbon adsorption, solvent absorption, condensation method and membrane separation process.In recovery method, the industrialization already of carbon adsorption and solvent absorption, but limit and easily cause secondary pollution to some extent to removing the volatile organic matter kind; Condensation method is mainly used in the recovery of higher boiling and high concentration volatile organic matter, and its operating cost is higher, and the rate of recovery is lower, does not generally use separately, and normal and additive method is united use.
The recovery technology of having reported has:
1.R.W.Baker,V.L.Simmons,J.Kaschemekat?and?J.G.Wijmans,Membrane?systems?for?VOC?recovery?from?air?streams[J],Filtration&?Separation,1994,(5):231~235;
Article has been narrated MTR company and has been adopted compression-condensation and Membrane Gas Separation Processes to combine, and reclaims airborne VOCs.Its flow process is: the air that contains VOCs enters condenser system after compression, reclaims most VOCs in the condensate liquid, and noncondensable gas enters membrane module, contains VOCs hardly in the saturating residual air, can directly be discharged in the air; See through the import that the air-flow that is rich in VOCs in the gas returns compressor, the concentration of VOCs rises rapidly in the loop, when the compressed gas that enters condenser reaches when condensing concentration, and the VOCs recovery that can be condensed again.The VOCs that available this technology reclaims comprises benzene, about toluene, acetone, trichloro-ethylene, CFC-11/12/12 and HCFC-12320 kind.Wherein input concentration is after 6.3% HCFC-123 handles through this device in the industrial production, is discharged into that concentration is 0.01% in the atmosphere.
2.J.McCallion,Membrane?process?captures?vinyl?chloride,otherVOCs[J],Chemical?Processing,1994,9:33~36.
The recovery that film separation system and condensation process process combined are used for polyvinyl chloride, polyethylene and polypropylene waste gas narrated in article, and the rate of recovery reaches 90%~99%.
3.K.Ohlrogge,J.Wind?and?R.D.Behling,Off-gas?purificationby?means?of?membrane?vapor?separation?systems[J],Sep.Sci.andTechnol.1995,30:1625~1638;
Article has been narrated German GKSS research center and has been developed the film that is used for reclaiming tail gas VOCs, when the film selectivity greater than 10 the time, the removal process that is used for VOCs has very strong economic benefit, the system that the assembly that membrane area is 30m2 combines with condensation, and the rate of recovery of VOCs has reached 99%.
4.M.Leemann,G.Eigenbergr?and?H.Strathmannn,Vapor?permeationfor?the?recovery?of?organic?solvents?from?waste?air?streams:separation?capacities?and?process?optimization[J],J.of?Membr.Sci.1996,113:313~322;
The VOCs that utilizes in poly dimethyl silane oxygen (PDMS) the doughnut semipermeable membrane separation of air narrated in article, finds that the flux of dimethylbenzene, toluene and acrylic acid etc. is more than 100 times of air.
5.A.Fouda,J.Bai,S.Q.Zhang,O.Kutowy?and?T.Matsuura,Membrane?separation?of?low?volatile?organic?compounds?bypervaporation?and?vapor?permeation[J],Desalination,1993,90:209~233;
The phenmethylol that utilizes in recovery of poly dimethyl silane oxygen (PDMS) doughnut semipermeable membrane and the separation of nitrogen narrated in article, has effect preferably.
6.D.Bhaumik,S.Majumdar,and?K.K.Sirkar,Pilot-plant?andlaboratory?studies?on?vapor?permeation?removal?of?VOCs?from?wastegas?using?silicone-coated?hollow?fibers[J],J.of?Membr.Sci.,2000,167:107~122;
The device by plasma grafting polysiloxanes active layer narrated on the polypropylene hollow fiber counterdie in article, in laboratory and pilot plant, is used for methyl alcohol, toluene, acetone and chloroform in the waste gas.
7.P.V.Shanbhag,A.K.Guha?and?K.K.Sirkar,Membrane-basedIntegrated?absorption-oxidation?reactor?for?destroying?VOCs?inair[J],Environ.Sci.Technol.,1996,30:3435~3440;
Article has been narrated two groups of silicon rubber capillary-pipe films and one group of Teflon film has been seated in the carbon fluoride (FC), forms a device, is called film base-adsorption and oxidation integrated reactor.Handle trichloro-ethylene with this device and have extraordinary degradation effect.
8.T.K.Poddar,S.Majumdar?and?K.K.Sirkar,Membrane-basedabsorption?of?VOCs?from?a?gas?stream[J],AIChE?J.,1996,42(11):3267~3282;
Article has been narrated and has been used silicone oil as absorbent, removes airborne VOCs, and its principle is: the gas that contains VOCs is walked in the hollow-fibre membrane, and absorbent is walked shell side, and two-phase comes in contact in micropore, and a large amount of VOCs is absorbed agent and absorbs; Absorbent enters another hollow fiber film assembly and carries desorption and regeneration by gas, and gas is carried the film outside of assembly and coated the meable siloxanes cortex of VOCs, in case absorbent under low pressure runs off.
9.G.Obuskovic,T.K.Poddar,K.K.Sirkar,Flow?swing?membranebsorptionpermeation[J],Ind.Eng.Chem.Res.,1998,37:212~220;
Article has been narrated and the transformation adsorption theory is used for film Kiev has been helped absorption.The VOCs dividing potential drop of shell side is far smaller than tube side, and the waste gas batch (-type) enters in the film pipe, when the pipe internal pressure drops to when close with the shell side dividing potential drop, feeds waste gas once more, and such operation will improve absorption efficiency.
Summary of the invention: the present invention is directed to contain different form and the poisonous volatile organic matter of concentration (for example, decahydronaphthalene) mist, its treatment process requires not only that the rate of recovery of volatile organic matter reaches more than the 95-99% in the mist, and poisonous organic concentration must be lower than discharge standard in the mist after handling.Test only shows adopts " film separations " can't reach requirement, must increase " adsorbing separation ", comprising: the research absorption property is good, can regenerate after the adsorbent of use repeatedly, and corresponding apparatus.For this reason, need to develop the comprehensive recycling process technology of " compression condensation "-" separation of film cascade film "-" adsorbents adsorb separation ".
Technical scheme of the present invention:
(1), process of the test
1. testing program and purpose
(1) under certain pressure, adopt compression condensation-microporous barrier separation-adsorbent recovery volatile organic matter (VOCs) processing technology routine, test membrane separates correlation properties such as film separates under penetration operation pressure reduction, the condensation temperature effect, flux, determines the optimum membrane module size A of different feeds concentration and tolerance ModAnd by condensation temperature and pressure regulate speeding of being caused exit in the variation of VOCs content, for membrane module designs provides parameter.
(2) adsorption capacity, regeneration condition and the service life of research adsorbent.
2. experiment process
Compression condensation-microporous barrier separation-adsorption test process description: air enters VOCs evaporation distribution bottle and carries out distribution after the flowmeter metering, make the VOCs concentration in the mist reach 1000 ~ 6000ppm, deliver to condenser condenses and reclaim most VOCs after containing the compressed machine compression of the gas of certain VOCs concentration through mechanical separator separating and condensing liquid, remove VOCs remaining in the gas through film level separator again, last do not coagulate tail gas adsorbents adsorb, emptying after flowmeter measures.
Poisonous volatile organic matter is that concentration is the decahydronaphthalene of 1000-6000ppm in the mist that this test is adopted; Compression pressure is 0.2-0.6MPa; Tolerance is 2-3Nm 3/ h; The refrigerant of condenser adopts-3 ℃--15 ℃ 30% glycol water.
3. test procedure
Bath temperature is controlled at~90 ℃, opens compressor, the control pressure at expulsion is at 0.2-0.3MPa.Regulate the certain inspiratory capacity of suction port of compressor intake valve control, by regulating the distribution of feeding in raw material of quantity tube at the bottom of the evaporative flask, after the concentration of decahydronaphthalene reaches requirement in going out surge flask gas, begin to collect condensate liquid, analyze the concentration of each separator outlet gas phase decahydronaphthalene simultaneously.Do not coagulate tail gas and absorb, measure adsorption capacity and regeneration condition with adsorbent.
(2), result of the test
1. compression condensation separation test result
Be unkitted membrane module in this experimental film level separator.
Experimental condition is: pressure is 0.2-0.4MPa; Condensation temperature is-3 ℃ ~-10 ℃; Tolerance is 2-3Nm 3/ h; Decahydronaphthalene concentration is 1000-4000ppm in the gaseous mixture.The compression condensation result of the test sees table 1 for details, and interpretation of result is as follows.
(1) as can be known, when condensation temperature is-3 ℃, tolerance is 2.2Nm by result of the test 1# 3/ h, compression pressure are 0.38MPa, and when distribution concentration was 2000ppm, decahydronaphthalene concentration was~130ppm in the separator final outlet gas; Suitable, the trans isomer content of decahydronaphthalene is respectively 26%, 74% (standard specimen for~40% ,~60%) in the gas, and the rate of recovery be~93%, conforms to substantially with decahydronaphthalene concentration value by the theoretical calculating of poised state.As seen when decahydronaphthalene concentration is lower than 2000ppm in the inlet gas, will reach 95%-3 ℃ of lower compression condensation rate of recovery.
(2) as can be known, when condensation temperature is-8--10 ℃, tolerance is 2-3Nm by result of the test 2#, 3#, 4#, 5# 3/ h, compression pressure are 0.2-0.38MPa, when distribution concentration is 2000-4000ppm, and decahydronaphthalene concentration<100ppm in the separator final outlet gas; Suitable, the trans isomer content of decahydronaphthalene also is respectively 26%, 74% (standard specimen for~40% ,~60%) in the gas, and the rate of recovery be>95%, conforms to substantially with decahydronaphthalene concentration value by the theoretical calculating of poised state.As seen, when decahydronaphthalene concentration was higher than 2000ppm in the inlet gas, compression condensation separates the rate of recovery can reach 95%.
(3) as can be known, when condensation temperature is-10 ℃, tolerance is 2.65Nm by result of the test 6#, 7# 3/ h, compression pressure are 0.24-0.38MPa, and distribution concentration is~during 1200ppm, in the separator final outlet gas decahydronaphthalene concentration can<90ppm; Suitable, the trans isomer content of decahydronaphthalene also is respectively and is 24%, 76% (standard specimen for~40% ,~60%) in the gas, the rate of recovery is~95%, as seen, when decahydronaphthalene concentration is at 1200-1500ppm in the inlet gas, reduce condensation temperature, compression condensation separates the rate of recovery also can reach 95%, but reclaiming energy consumption has also increased.
2. compression condensation-absorption and regeneration test result
(1) adsorption temp is 0--3 ℃, and adsorptive pressure is~0.13MPa adsorbed gas speed 0.8-0.5m/s.
(2) regeneration temperature is 130-145 ℃, and regeneration pressure is-0.13MPa regeneration gas speed 0.15-0.2m/s.
By test to adsorption capacity, the rate of adsorption and the regeneration rate of eight kinds of adsorbents, selected the processing that a kind of adsorbent is used for the tail gas decahydronaphthalene, its absorption sees table 2 for details with the regeneration test result.As seen from the experiment, after using repeatedly, the adsorption capacity of adsorbent can maintain 0.2g substantially Dec./ g c(0.1g Dec./ ml C).Decahydronaphthalene concentration is surveyed not come out in the saturated exit gas before of adsorbent, and the time in saturated back to concentration~50ppm is about 2-3 hour.And decahydronaphthalene concentration is between 2500-200ppm in the regeneration gas, and regeneration gas speed only is 15% of adsorbed gas speed, and this regeneration gas can turn back to the suction port of compressor and reclaim once more, forms closed closed circuit.Therefore, adopting a small amount of decahydronaphthalene in the sorbent treatment tail gas to reach discharge standard is being feasible and economical in industrial applications.
3. compression condensation-microporous barrier separation-adsorbents adsorb result of the test
Compression condensation-microporous barrier separation-adsorbents adsorb result of the test sees table 3 for details.As seen from the experiment, the micropore membrane separation efficiency is separated high more than 50% than machinery; The flux of microporous barrier can reach 200m 3/ m 2.h, film level pressure reduction<0.06PMa.As seen, adopt microporous barrier to separate the recovery decahydronaphthalene and can improve separative efficiency significantly.
Adopt " compression condensation-microporous barrier separation-adsorbents adsorb is separated " technology to carry out the recovery of decahydronaphthalene in the gaseous mixture, comprehensive recovery can reach more than 98%, decahydronaphthalene content is lower than discharge standard (0-25ppm) in the gas of processing back, all is feasible technically and economically.
Table 1 compression condensation result of the test
Test number ??1# ??2# ??3# ??4# ??5# ??6# ??7#
Compression tolerance (Nm 3/h) ??2.2 ??2.2 ??2 ??2.8 ??3 ??2.65 ??2.65
Compression pressure (MPa Exhausted) ??0.38 ??0.38 ??0.3 ??0.3 ??0.2 ??0.38 ??0.24
Condensation temperature (℃) ??-3 ??-8 ??-8 ??-10 ??-10 ??-10 ??-10
Distribution concentration (ppm) ??2000 ??2000 ??4000 ??4000 ??4000 ??1200 ??1200
Suitable, trans isomer ratio (%) ????Trans- ??73 ??74 ??74 ??76 ??76 ??76 ??76
????Cis- ??27 ??26 ??26 ??24 ??24 ??24 ??24
Separator outlet concentration (ppm) ????1# ??140 ??81 ??109 ??78 ??121 ??63 ??105
????2# ??131 ??78 ??96 ??74 ??98 ??58 ??92
The rate of recovery (%) ????1# ??93.0 ??95.95 ??97.28 ??98.05 ??96.98 ??94.75 ??91.25
????2# ??93.45 ??96.1 ??97.60 ??98.15 ??97.55 ??95.17 ??92.33
Table 2 compression condensation-absorption and regeneration test result
Adsorption test Tolerance (Nm3/h) Decahydronaphthalene concentration (ppm) Adsorbance (g)
The suction port of compressor The tail gas outlet The suction port of compressor Separator outlet The tail gas outlet
Absorption for the first time ????2.8 ????2.5 ????1680 ????89 ??0~29 ??62
Absorption for the second time ????2.8 ????2.54 ????1314 ????184 ??0~87 ??15.2
Absorption for the third time ????2.8 ????3.14 ????1474 ????155 ??0~43 ??18.5
The 4th absorption ????2.2 ????2.8 ????2250 ????191 ??0~49 ??21.5
Regeneration test Regeneration tolerance (Nm3/h) Regeneration temperature ℃ Initial concentration Finish concentration Regeneration amount (g)
Regeneration for the first time ????0.49 ???90~110 ????457 ??62 ??15.5
Regeneration for the second time ????0.66 ????~132 ????1871 ??204 ??20.7
Regeneration for the third time ????0.66 ????~142 ????2355 ??83 ??20.5
The 4th regeneration ????0.68 ????~142 ????3302 ??128 ??22
Annotate: adsorbent volume: 197ml; Absorber diameter D=37mm.
Table 3. " compression condensation-microporous barrier separation-adsorbents adsorb is separated " result of the test
Test number ??8# ??9# ??10# ??11# Remarks
Compression tolerance (Nm 3/h) ??2.9 ??3.3 ??3.5 ??3.5
Compression pressure (MPa Exhausted) ??0.30 ??0.30 ??0.27 ??3.7
Condensation temperature (℃) ??-5 ??-5 ??-5 ??-10
Distribution concentration (ppm) ??2532 ??1805 ??1712 ??6322
Suitable, trans isomer ratio (%) ??Trans- ??77 ??78 ??79 ??78
???Cis- ??23 ??22 ??21 ??22
Separator outlet concentration (ppm) 1# (machinery) ??187 ??299 ??250 ??551
2# (film level) ??102 ??134 ??119 ??142
The film level is separated efficient (%) ??46 ??55 ??52 ??74
Adsorbent exit concentration (ppm) ??≤25 ??≤25 ??≤25 ??≤25 The control discharge standard
The rate of recovery (%) 1# (machinery) ??92.6 ??83.4 ??85.4 ??91.3
2# (film level) ??96.0 ??92.6 ??93.0 ??97.8
Comprehensive recovery (%) ??99.0 ??98.6 ??98.5 ??99.6 Containing regeneration gas reclaims
Annotate: membrane area 80 * 80mm.
The present invention compares with similar technology, have flow process simple, reclaim advantages such as organic gas efficient height, energy consumption are low, non-secondary pollution, can reach discharge standard by once reclaiming.Result of the test shows that technology of the present invention is a mature and feasible, and production run is reliable and stable, and cost recovery is low, satisfies requirement on environmental protection, and economic and social benefit is remarkable.
Description of drawings: accompanying drawing 1 is that VOCs experimental rig flow chart is reclaimed in compression condensation-film separation-absorption; Accompanying drawing 2 is that decahydronaphthalene experimental rig flow chart is reclaimed in compression condensation-film separation-absorption.
In the accompanying drawing 1, the 1-spinner flowmeter; The 2-water bath; 3-evaporation distribution bottle; The 4-surge flask; The 5-compressor; 6-chilled water unit; The 7-condenser; 8-mechanical separator 1; 9-film level separator 2; 10-film level separator 3; The 11-absorber; The 12-spinner flowmeter.
In the accompanying drawing 2, the combined gas heat exchanger; The 2-gas circulating compressor; The 3-condenser; The 4-gas-liquid separator; 5-film cascade separator; The 6-absorber; 7-cross air blasting nitrogen buffer tank; Path nitrogen buffer tank under the 8-; 9-regeneration gas preheater.
The specific embodiment:
The superhigh molecular weight polyethylene fibers pilot scale adopts decahydronaphthalene (Decalin) to make solvent, present embodiment adopts " compression condensation-microporous barrier separation-adsorbents adsorb " technology to reclaim decahydronaphthalene, process is: will contain the compressed machine compression of the nitrogen mixture body back condensation of finite concentration decahydronaphthalene, most of decahydronaphthalene can obtain reclaiming, the system condensing temperature can be decided according to the concentration of decahydronaphthalene in gas phase, as-20 ℃ ~ 20 ℃.And remaining decahydronaphthalene further reclaims through film cascade membrane separator device again in the mixing nitrogen, adopts adsorbents adsorb at last, make the concentration of decahydronaphthalene be reduced to discharge standard (≤25ppm) recycle afterwards or emptying.
Technological process explanation (seeing accompanying drawing 2): from the circulating nitrogen gas of superhigh molecular weight polyethylene fibers pilot-plant dry path outlet, after combined gas heat exchanger (E-101) heat exchange cooling, enter gas compressor (P-101), after being compressed to the pressure (as 0.4Mpa) of 0.2-0.6Mpa, after delivering to the temperature (as-10 ℃) that condenser (E-102) condenses to-20 ℃-20 ℃, enter gas-liquid separator (V-101), the separated recovery of decahydronaphthalene of most of (about 85%), gas enters film cascade separator (V-102) and further separates the decahydronaphthalene that reclaims remainder in the gas, go out the mixing nitrogen of V-102, most of (87.7%) is through gas buffer jar (V-103) and (E-101) heat exchange, after the decompression, deliver to the superhigh molecular weight polyethylene fibers pilot-plant as cross air blasting and path dry wind.Another part (12.3%) is after absorber (V-104a) further removes micro-decahydronaphthalene remaining in the gas, through gas buffer jar (V-105) and (E-101) heat exchange, decompression, deliver to the superhigh molecular weight polyethylene fibers pilot-plant as path dry wind down; Use for the adsorbent reactivation in the absorber (V-104b) wherein a part of nitrogen heater via (E-103) heating back, and two cover absorbers regularly switch, and born again gas turns back to the suction port of compressor and reclaims once more, forms closed closed circuit.The nitrogen that reaches discharge standard after a small amount of processing that (for example, prevent the accumulation of trace oxygen) is as required drawn emptying by V-105.

Claims (3)

1, the recovery technology of volatile organic matter in a kind of mist, it is characterized in that adopting the comprehensive recycling process technology of " compression, condensation; separation recovery "-" separation of film cascade film is reclaimed "-" adsorbents adsorb is separated recovery ", under the temperature of the pressure of 0.2-0.6Mpa and-20 ℃-20 ℃, make that the 95-99% of volatile organic matter is reclaimed in the mist, mist can reach discharge standard by once recycling, gas can recycle or emptying, and does not have problem of secondary pollution.
2, the recovery technology of volatile organic matter in a kind of mist as claimed in claim 1, it is characterized in that, adopt film cascade membrane separator device, under the temperature of the pressure of 0.2-0.5Mpa and-20 ℃-20 ℃, further reclaim organic compound wherein, diffusion barrier can be the microporous barrier or the permeability and separation film of not volatilized organic matter dissolving of material or destruction.
3, the recovery technology of volatile organic matter in a kind of mist as claimed in claim 1, it is characterized in that, adopt high efficiency, reproducible adsorbent, under the temperature of the pressure of 0.1-0.4Mpa and-20 ℃-20 ℃, the organic matter that absorption is relevant, make that organic concentration is reduced to discharge standard in the mist, gas can recycle or emptying, having adsorbed organic adsorbent reuses after regenerating, and regeneration gas is turned back to compression, condenser system reclaim wherein organic matter once more, form closed closed circuit.
CN 02137836 2002-06-25 2002-06-25 Recovery technology for volatile organism in mixed gas Expired - Lifetime CN1248767C (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN 02137836 CN1248767C (en) 2002-06-25 2002-06-25 Recovery technology for volatile organism in mixed gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN 02137836 CN1248767C (en) 2002-06-25 2002-06-25 Recovery technology for volatile organism in mixed gas

Publications (2)

Publication Number Publication Date
CN1425486A true CN1425486A (en) 2003-06-25
CN1248767C CN1248767C (en) 2006-04-05

Family

ID=4749135

Family Applications (1)

Application Number Title Priority Date Filing Date
CN 02137836 Expired - Lifetime CN1248767C (en) 2002-06-25 2002-06-25 Recovery technology for volatile organism in mixed gas

Country Status (1)

Country Link
CN (1) CN1248767C (en)

Cited By (16)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100436314C (en) * 2006-07-28 2008-11-26 华南理工大学 Method of preparing high hydrophobic active carbon and its device
CN101851792A (en) * 2010-06-25 2010-10-06 浙江四海氨纶纤维有限公司 Nitrogen supplementing device of spandex spinning channel and process thereof
CN102166463A (en) * 2011-03-21 2011-08-31 海湾石油设备(北京)有限公司 Simulation test device for recovering volatile organic gases
CN103277982A (en) * 2013-05-21 2013-09-04 南京九思高科技有限公司 Technology and device for circulating recycling of volatile organic compound in coating printing industry
CN103801104A (en) * 2012-11-08 2014-05-21 中国石油化工股份有限公司 Energy-saving method used for recovery of high-performance polyethylene fiber dry spinning solvent
CN103977669A (en) * 2014-06-05 2014-08-13 中膜科技(苏州)有限公司 VOCs (Volatile Organic Chemicals) processing method and corresponding system
CN104436982A (en) * 2013-09-17 2015-03-25 中国石油化工股份有限公司 Low concentration oxygen-containing organic waste gas recovery technology for dry spinning
CN105126531A (en) * 2015-07-22 2015-12-09 同济大学 Device of increasing adsorption bed thermal-circular gas desorption regeneration efficiency and method thereof
CN105413226A (en) * 2015-12-23 2016-03-23 南京九思高科技有限公司 Organic waste gas recycling device and organic waste gas recycling process based on membrane-method coupled condensation adsorption
CN105413383A (en) * 2015-11-13 2016-03-23 四川天采科技有限责任公司 Method for recycling light hydrocarbon from tail gas of petrochemical plant
CN107617294A (en) * 2016-07-15 2018-01-23 中国石油化工股份有限公司 A kind of preprocess method of the waste gas containing decahydronaphthalene
CN109200735A (en) * 2017-06-30 2019-01-15 中国石油化工股份有限公司 A kind of processing method of hydrogen peroxide oxidation tail gas
CN110114128A (en) * 2016-12-15 2019-08-09 切弗朗菲利浦化学公司 Membrane and pressure swing adsorption hybrid inru process
CN112023605A (en) * 2019-06-03 2020-12-04 中石化南京化工研究院有限公司 Organic steam retrieves experimental apparatus
CN112316450A (en) * 2020-09-22 2021-02-05 蓝旺节能科技(浙江)有限公司 High-efficient circulation vaporization system of traditional chinese medicine processing
WO2022214154A1 (en) * 2021-04-07 2022-10-13 Hasni Abdelmallek Device and method for eliminating dust, smoke, gas and vapours expelled into the environment

Cited By (23)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100436314C (en) * 2006-07-28 2008-11-26 华南理工大学 Method of preparing high hydrophobic active carbon and its device
CN101851792A (en) * 2010-06-25 2010-10-06 浙江四海氨纶纤维有限公司 Nitrogen supplementing device of spandex spinning channel and process thereof
CN102166463A (en) * 2011-03-21 2011-08-31 海湾石油设备(北京)有限公司 Simulation test device for recovering volatile organic gases
CN103801104B (en) * 2012-11-08 2015-10-14 中国石油化工股份有限公司 The power-economizing method of high-performance polyethylene fibres dry spinning solvent recovery
CN103801104A (en) * 2012-11-08 2014-05-21 中国石油化工股份有限公司 Energy-saving method used for recovery of high-performance polyethylene fiber dry spinning solvent
WO2014187242A1 (en) * 2013-05-21 2014-11-27 南京九思高科技有限公司 Process and device for recycling volatile organic compounds in coating and printing industries
US11273388B2 (en) 2013-05-21 2022-03-15 Jiangsu Jiumo High-Tech Co., Ltd. Technique and apparatus for recycling volatile organic compounds of coating printing
CN103277982A (en) * 2013-05-21 2013-09-04 南京九思高科技有限公司 Technology and device for circulating recycling of volatile organic compound in coating printing industry
CN104436982A (en) * 2013-09-17 2015-03-25 中国石油化工股份有限公司 Low concentration oxygen-containing organic waste gas recovery technology for dry spinning
CN103977669A (en) * 2014-06-05 2014-08-13 中膜科技(苏州)有限公司 VOCs (Volatile Organic Chemicals) processing method and corresponding system
CN105126531A (en) * 2015-07-22 2015-12-09 同济大学 Device of increasing adsorption bed thermal-circular gas desorption regeneration efficiency and method thereof
CN105126531B (en) * 2015-07-22 2017-12-26 同济大学 A kind of devices and methods therefor for improving adsorbent bed circulation of hot gases desorption and regeneration efficiency
CN105413383A (en) * 2015-11-13 2016-03-23 四川天采科技有限责任公司 Method for recycling light hydrocarbon from tail gas of petrochemical plant
CN105413226A (en) * 2015-12-23 2016-03-23 南京九思高科技有限公司 Organic waste gas recycling device and organic waste gas recycling process based on membrane-method coupled condensation adsorption
CN107617294A (en) * 2016-07-15 2018-01-23 中国石油化工股份有限公司 A kind of preprocess method of the waste gas containing decahydronaphthalene
CN110114128A (en) * 2016-12-15 2019-08-09 切弗朗菲利浦化学公司 Membrane and pressure swing adsorption hybrid inru process
CN110114128B (en) * 2016-12-15 2022-09-13 切弗朗菲利浦化学公司 Membrane and pressure swing adsorption hybrid INRU process
CN109200735A (en) * 2017-06-30 2019-01-15 中国石油化工股份有限公司 A kind of processing method of hydrogen peroxide oxidation tail gas
CN109200735B (en) * 2017-06-30 2021-06-04 中国石油化工股份有限公司 Method for treating hydrogen peroxide oxidized tail gas
CN112023605A (en) * 2019-06-03 2020-12-04 中石化南京化工研究院有限公司 Organic steam retrieves experimental apparatus
CN112316450A (en) * 2020-09-22 2021-02-05 蓝旺节能科技(浙江)有限公司 High-efficient circulation vaporization system of traditional chinese medicine processing
CN112316450B (en) * 2020-09-22 2022-07-15 蓝旺节能科技(浙江)有限公司 High-efficient circulation vaporization system of traditional chinese medicine processing
WO2022214154A1 (en) * 2021-04-07 2022-10-13 Hasni Abdelmallek Device and method for eliminating dust, smoke, gas and vapours expelled into the environment

Also Published As

Publication number Publication date
CN1248767C (en) 2006-04-05

Similar Documents

Publication Publication Date Title
CN1248767C (en) Recovery technology for volatile organism in mixed gas
US5772734A (en) Membrane hybrid process for treating low-organic-concentration gas streams
CN1229167C (en) Vacuum rotary adsorptive process utilizing controlled waste gas extraction
CN1176736C (en) Gas separating and purifying method and its apparatus
CN100553740C (en) Method for organic waste gas recovery
CN101391154A (en) Improved volatile organic compounds recovery method
CN105498446A (en) Method for recycling organic matter through organic waste gas adsorption, steam desorption and fractional condensation
CN101259357A (en) Method and device for recovering organic solvent from waste gases of printing industry
CN101633600B (en) Method and device for enriching and recovering methyl chloride by membrane separation method
CN1806894A (en) Oil gas absorptive reclaiming method and apparatus
KR101715826B1 (en) Method for removing organic solvent, and removal device
CN101759246B (en) Device for treatment of waste water containing organic solvents
CN101015760A (en) Oil-gas recovery method and device using absorption and adsorbing integration technology
CN106621711B (en) A kind of processing method of the benzene gas containing high concentration
CN203469759U (en) Volatile organic waste gas recycling device
CN106310698A (en) Oil and gas recycling method
CN107670454A (en) A kind of recovery system and its recovery process of toluene waste gas vacuum deep cooling
CN110156016A (en) The combined recovery device and method of carbon dioxide in flue gas, nitrogen and oxygen
CN1112228C (en) Method of treating organic waste gas containing vapor
CN212819023U (en) Compression absorption film adsorption combined type oil gas recovery device
CN102029100A (en) Dry desorption process for activated carbon adsorption of organic waste gas
CN110935281B (en) Adsorption and regeneration device and method for solid adsorbent for adsorbing volatile organic compounds
CN111437622A (en) Oil gas treatment system and method
CN101862547B (en) Rotary solvent recovery device and method
KR20090093077A (en) Apparatus and method for recovery of volatile organic compounds

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CX01 Expiry of patent term
CX01 Expiry of patent term

Granted publication date: 20060405