CN101318099B - Process for removing organic sulfur in low-temperature condition - Google Patents

Process for removing organic sulfur in low-temperature condition Download PDF

Info

Publication number
CN101318099B
CN101318099B CN2008100586686A CN200810058668A CN101318099B CN 101318099 B CN101318099 B CN 101318099B CN 2008100586686 A CN2008100586686 A CN 2008100586686A CN 200810058668 A CN200810058668 A CN 200810058668A CN 101318099 B CN101318099 B CN 101318099B
Authority
CN
China
Prior art keywords
organic sulfur
absorption liquid
gas
regeneration
sulphur
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
CN2008100586686A
Other languages
Chinese (zh)
Other versions
CN101318099A (en
Inventor
唐晓龙
于丽丽
易红宏
宁平
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.)
Kunming University of Science and Technology
Original Assignee
Kunming University of Science and Technology
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 Kunming University of Science and Technology filed Critical Kunming University of Science and Technology
Priority to CN2008100586686A priority Critical patent/CN101318099B/en
Publication of CN101318099A publication Critical patent/CN101318099A/en
Application granted granted Critical
Publication of CN101318099B publication Critical patent/CN101318099B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Landscapes

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

Abstract

The invention provides a technological method for desorbing organic sulphur at low temperatures; wherein, the organic sulphur is hydrolyzed into H2 and CO2 and H2S is absorbed after being cooled by waste gas and absorbed by absorbing fluid for organic sulphur; the absorbing fluid for organic sulphur is regenerated by aerating gaseous CO, and the regenerated H2S is then aerated into H2S absorbing liquid so as to regenerate the H2S absorbing liquid in the air-blow method; the sulfur product can be obtained after the sulfur generated in the regeneration process goes through working procedures of centrifugal separation, washing, dehydration and fusion. The invention has the advantages that sulphur in the high-concentration organic sulphur waste gas can be effectively desorbed, with an absorbing and purifying efficiency more than 95 percent; meanwhile, the used catalysts, namely, the absorbing liquid for organic sulphur and H2S absorbing liquid are guaranteed for regeneration; the simple substance of sulphur absorbed by the catalyst can be effectively recycled at the same time of regeneration. The invention has simple process, small investment, low running cost and simple operation, requires low labor intensity, and does not pollute the environment.

Description

The process of removing organic sulfur in low-temperature condition
Technical field
The present invention relates to remove under a kind of cryogenic conditions the process of organic sulfur in cos, hydrogen sulfide and the carbon disulfide.Specifically be a kind of low temperature hydrolysis cos and carbon disulfide of being used for, and will produce or unstripped gas in the process of hydrogen sulfide stripping.
Background technology
Cos (COS) and hydrogen sulfide (H 2S) extensively being present in coal, oil, natural gas is unstripped gas, in the waste gas that carries out being produced when synthetic ammonia, methanol production and viscose rayon are produced.The existence of sulfide not only pollutes the environment, but also the meeting corrosion pipeline can cause the catalyst poisoning inactivation in the subsequent production process, thereby influence the quality of postorder chemical products.Especially in the commercial production of synthetic ammonia, they are the principal elements that make catalysqt deactivations such as methyl alcohol, methanation, ammonia synthesis.In recent years, along with the sustainable growth of economy, make energy supply and demand contradiction become increasingly conspicuous, the particularly rise of oil price causes some chemical fertilizer factories and the pure factory of couplet to have to adopt colm and sulphur coal gas making at a low price, and sulfur content increases in the unstripped gas thereby make.H 2S and COS are typical sulfide in these unstripped gas.Because COS is neutrality or faintly acid, its chemical property torpescence, the method that very difficult usefulness removes hydrogen sulfide removes it, brings new challenge therefore for existing desulfur technology.
Traditional fine desulfurizing technology mainly contains two kinds: a kind of is hydrogenation method, promptly at high temperature adopts cobaltmolybdate catalyst series connection zinc oxide, with COS and CS 2Change into H Deng organic sulfur 2S utilizes zinc oxide with H again 2S removes.This method process route is complicated, operating condition is harsh, energy consumption is big, investment cost is high, is difficult to promote in China.
Another kind is the organic sulfur hydrolyst of all developing both at home and abroad in recent years.Its course of reaction is: COS+H 2O → H 2S+CO 2, CS 2+ 2H 2O → 2H 2S+CO 2, under the effect of hydrolyst, utilize water vapour in the unstripped gas with COS and CS 2Be converted into the ripe H of treatment process 2Carry out subsequent treatment behind the S.
Relevant organic sulfur catalyzing hydrolysis Study on Technology mainly concentrates on middle low temperature both at home and abroad at present, discloses smart removal of organic sulfur of a kind of normal temperature and inorganic sulfur new technology like Chinese patent CN1067828A, is about to contain 0~30ppmH 2S and COS and CS 2Process gas earlier through one-level modified activated carbon or iron oxide desulfurization, absorb sulphur through the ordinary-temp hydrolysis catalyst 30~120 ℃ of following hydrolysis again, and then, make total sulfur<0.1ppm in the smart processed gas through desulfurization under second level modified activated carbon or the iron oxide normal temperature.
Chinese patent CN1081424A discloses a kind of constant temperature fine desulfurizing production technology, is about to contain the H of 0~30ppm 2S+COS+CS 2Process gas,---water or steam heater are heated to 40~80 ℃, and---hydrolyst---cooling tower is cooled to normal temperature---desulfurizing agent sweetening process makes total sulfur<0.1ppm in the smart processed gas through desulfurizing agent.
Chinese patent CN1130151A discloses a kind of inversion absorption type constant temperature fine desulfurizing technology, and it is with containing 0~30ppmH 2S+COS+CS 2Synthetic ammonia or petrochemical materials gas, the sweetening process of the desulfurizing agent through taking off inorganic sulfur and the desulfurizing agent of inversion absorption type removal of organic sulfur, at 20~60 ℃, smart desulfurization under normal pressure~10MPa pressure condition, total sulfur (H in the gas after the desulfurization 2S+COS+CS 2)<0.1ppm.
Chinese patent CN1226873 discloses a kind of method that reclaims said compound except that hydrogen sulfide, sulfur dioxide, carbonyl sulfide and/or carbon disulfide sulfide contained in the desulfuration factory residual gas and with the form of sulphur.The process route of this method is with containing H with formation behind the residual gas catalyzing hydrolysis 2S and SO 2And do not contain COS and CS 2Water decomposition gas, after the cooling, the gas of this hydrolysis one of is introduced in parallel two Crouse's catalytic domains installing, another catalytic domain is used for regeneration, then cooling.The operating temperature of this technology is higher, is not easy to removing of organic sulfur under the cryogenic conditions.
Chinese patent CN1147010A discloses a kind of artificial coal gas constant temperature fine desulfurizing technology; It is characteristics high as organic sulfur content in the artificial coal gas of raw material (combustion) gas to industries such as electronics, chemical industry, metallurgy, complex shape; Adopt the multiple catalyst and the desulfurizing agent of Hubei Prov. Chemical Research Inst development and production; Under normal temperature or normal temperature~150 ℃, normal pressure~3.0MPa condition, with COS<250mg/Nm in the coal gas 3, CS 2<120mg/Nm 3, RSH<8mg/Nm 3, thiophene<10mg/Nm 3Be removed to total sulfur (with H 2The S meter) content difference≤112mg/Nm 3With≤7mg/Nm 3Two kinds of raw materials (combustion) gas.
Chinese patent CN1218421A discloses a kind of gas cleaning method to sulfide hydrogen or carbonyl sulfide, promptly adopts biological oxidation process to handle the sulfide in the waste gas cleaning solution, thereby obtains elementary sulfur.Elementary sulfur is separated, and treated cleaning solution is looped back in the gas scrubbing step.This method technology is complicated, and adaptability is relatively poor.
Chinese patent CN1323735A discloses the purification method of warm anti-sulphur hydrolysis organic sulfur in a kind of unstripped gas.And warm anti-sulfide hydrolysis in described tower, loading, this catalyst H in unstripped gas are set before unstripped gas decarburization and constant temperature fine desulfurizing with the middle temperature hydrolysis tower of anti-sulphur 2S50~10000ppm and COS20~1500ppm, O 2Content 0~0.6%, pressure normal pressure~30Mpa directly uses under 85~250 ℃ of conditions of temperature or after sulfuration, uses, and with organic sulfur in its hydrolytic purification gas, gas goes the decarburization of postorder operation then.
The technology of the organic sulfide removal that above-mentioned patent is mentioned only is applicable to the organic sulfur of low concentration mostly, and the solid catalyst of use all can not be regenerated, and organic sulfur transforms the H that generates 2S is prone to absorbed by solid catalyst, can not reclaim sulphur simple substance wherein.Particularly in current industrial chemicals shortage, under the situation of rise in oil price, sulphur is the important chemical raw materials for production, and the sulphur resource that reclaims in the sulphur-containing exhaust gas has important practical significance.
Summary of the invention
To the problem that removes of sulphur in (>80%) the organic sulphur waste gas under the present high concentration CO atmosphere, the present invention provides that a kind of cost is low, efficient is high and takes into account the process of organic sulfur removal under the cryogenic conditions of recovery of regeneration and sulphur of catalyst.
The present invention accomplishes through following technical proposal: a kind of process of removing organic sulfur in low-temperature condition is characterized in that through the following step:
A, the waste gas that will contain organic sulfur are cooled to 20~100 ℃, are 100~500h by gas liquid ratio -1Amount, waste gas is fed in the organic sulfur absorption liquid of following volume ratio, and makes it saturated, so that tempreture organic sulphur hydrolysis is become H 2S and CO 2, and absorb H 2S:
Hexahydropyridine 1~15%
1mol/L hydroxide 0.01~10%
Ethanol 40~60%
Water surplus;
B, be 100~500h by gas liquid ratio -1Amount, CO gas is fed in the organic sulfur absorption liquid of A step after saturated, carry out the regeneration of organic sulfur absorption liquid, the temperature of regeneration is 80~100 ℃, the recovery time is 5~8 hours, produces H in the time of regeneration 2S;
C, the H that B step regenerative process is produced 2S gas is 100~500h by gas liquid ratio -1Amount, feed H 2In the S absorption liquid, absorb H 2S is to saturated, with H 2The S absorption liquid takes out and filters;
D, in the filtered fluid of C step, be 100~500h by gas liquid ratio -1The amount bubbling air, carry out H with air Bubbling method of the prior art 2The regeneration of S absorption liquid, absorption liquid pH value to 8~9 after the regeneration of adjustment drum oxygen; The sulphur that regenerative process produces is through centrifugation, washing, dehydration, the fusion operation of prior art, get final product sulfur product.
Oxide in the organic sulfur absorption liquid of said A step is KOH, K 2CO 3, NaOH, Na 2CO 3, NaHCO 3, NH 4Among the OH one or more.
Hexahydropyridine, ethanol in the organic sulfur absorption liquid of said A step are chemical pure solution, and water is distilled water.
The H of said C step 2The S absorption liquid and the preparation as follows: at Fe 3+Content is in the solution of 0.03~0.06mol/L, is 10~50% amount by the mass ratio of Mn and Fe, adds Mn (NO 3) 2Or Mn (CH 3COO) 2Again by metal cations Fe 3+With the stabilizing agent integral molar quantity than the amount that is 15~50%, add in ethylenediamine tetra-acetic acid (EDTA), sulfosalicylic acid, the citric acid one or more, as the metal ion stabilizing agent; Use Na 2CO 3And NaHCO 3Adjustment pH value of solution value to 8~10 get H 2S GAS ABSORPTION liquid.
The present invention compared with prior art has advantage and effect: adopt such scheme, the sulphur in the ability effective elimination high concentrated organosulfur waste gas reaches more than 95% its absorption cleaning efficient, and can make catalyst system therefor simultaneously is organic sulfur absorption liquid, H 2The S absorption liquid obtains regeneration, can effectively reclaim the sulphur simple substance that absorbs in the catalyst in the time of regeneration, and this is in current industrial chemicals shortage, under the situation of rise in oil price; Can reclaim the sulphur resource in the sulphur-containing exhaust gas, make it to have important practical significance as important chemical raw materials for production---sulphur; Technology of the present invention is simple, small investment, and operating cost is low; Simple to operate, labour intensity is low, and is free from environmental pollution.
Description of drawings
Fig. 1 is a low temperature organic sulfur removal process chart.
Among the figure, 1 is impact flow reactor, and 2 is filter, and 3 is the sulphur foam tank, and 4 is regeneration tank, and 5 is centrifugal separator, and 6 is washer, and 7 is dehydrator, and 8 is sulfur melting kettle, and 9 is condenser, and 10 is cooling tower, and 11 is centrifugal pump, and 12 is air blast.
The specific embodiment
Embodiment 1
One, absorption liquid preparation:
1, organic sulfur absorption liquid and preparation thereof: with 5ml hexahydropyridine (chemical pure), 50ml ethanol (chemical pure), 1ml concentration is the KOH of 1mol/L and the organic sulfur absorption liquid that distilled water is mixed with 100ml, and is for use.
2, regeneration gas H 2The preparation of S absorption liquid: take by weighing 1.62 gram FeCl 3Mn (NO with 0.72 gram 50% 3) 2(element mol ratio Mn: Fe=0.2), together be dissolved in the 200mL deionized water, fully stirring and dissolving is processed Fe to solution 3+Concentration is the compound ion absorption liquid of 0.05mol/L; Interpolation 2.92 gram EDTA and 2.18 gram sulfosalicylic acids are done stabilizing agent (metal cations Fe 3+With stabilizing agent integral molar quantity ratio be 1: 2); Use NaCO 3And NaHCO 3The control pH value of solution is 9, and is for use.
Two, low temperature organic sulfur removal processing step is:
1, sulphur-containing exhaust gas (after wherein COS<3000ppm=is cooled to 40 ℃, is equipped with in the reactor of the above-mentioned organic sulfur absorption liquid of 50ml with the gas flow feeding of 125ml/min, reacted 12 hours, make the organic sulfur absorption liquid saturated, so that tempreture organic sulphur hydrolysis is become H 2S and CO 2, and absorb H 2S;
2, be 150h by gas liquid ratio -1Amount, regeneration gas CO is fed in the saturated organic sulfur absorption liquid of 1 step, under 80 ℃ of temperature, regenerated 6 hours, behind the organic sulfur regeneration of absorption solution under this condition, its purification efficiency is 100% still, produces H in the time of regeneration 2S;
3, the H that the regeneration of 2 steps is produced 2S presses the gas flow of 200mL/min, feeds the above-mentioned H of 50ml is housed 2In the impact flow reactor of S absorption liquid, wherein, the H that regeneration produces 2Hydrogen sulfide content in the S waste gas is 750mg/m 3, oxygen content is 10% (volume ratio), is under 60~70 ℃ in reaction temperature, H 2The S absorption liquid has reached 99% in the purification efficiency in the initial moment, is reflected in 500 minutes, and absorption cleaning efficient is all more than 98%, with H 2The S absorption liquid takes out and filters;
4, be 250h by gas liquid ratio -1Amount, air is fed in the filtered fluid of 3 steps, adopt air Bubbling method of the prior art to carry out H 2The regeneration of S absorption liquid, the absorption liquid pH value to 8 after the regeneration of adjustment drum oxygen continues to react to purification efficiency and reaches 96.5%; The sulphur that regenerative process produces is through centrifugation, washing, dehydration, the fusion operation of prior art, get final product sulfur product.
Embodiment 2
One, absorption liquid preparation:
1, organic sulfur absorption liquid: with the hexahydropyridine of 10ml, the ethanol of 50ml, the concentration of 1ml is the Na of 1mol/L 2CO 3Be mixed with the organic sulfur absorption liquid of 100ml with distilled water, for use.
2, regeneration gas H 2S absorption liquid: take by weighing 1.62 gram FeCl 3With 0.87 gram Mn (CH 3COO) 2Be dissolved in the 200mL deionized water that (element mol ratio Mn: Fe=0.5), fully stirring and dissolving is processed Fe 3+Concentration is the solution of 0.05mol/L; Add 4.36 gram sulfosalicylic acids and 5.84 gram EDTA used as stabilizers (metal cations Fe 3+With stabilizing agent integral molar quantity ratio be 1: 4); Use NaCO 3And NaHCO 3The control pH value of solution is 10.
Two, low temperature organic sulfur removal processing step is:
1, is after the waste gas of COS<3000ppm is cooled to 20 ℃ with sulphur-containing exhaust gas, feeds with the gas flow of 50ml/min and be equipped with in the reactor of the above-mentioned organic sulfur absorption liquid of 20ml, reacted 24 hours, make the organic sulfur absorption liquid saturated, so that tempreture organic sulphur hydrolysis is become H 2S and CO 2, and absorb H 2S;
2, regeneration gas CO (>99%) is fed in the saturated organic sulfur absorption liquid of 1 step with the flow of 50ml/min, under 80 ℃ of temperature, regenerated 6 hours, behind the organic sulfur regeneration of absorption solution under this condition, its purification efficiency is 100% still, produces H in the time of regeneration 2S;
3, the H that the regeneration of 2 steps is produced 2S feeds 50mlH is housed with the gas flow of 300mL/min 2In the impact flow reactor of S absorption liquid, wherein, H 2Hydrogen sulfide content in the S waste gas is 1000mg/m 3, oxygen content is 15%, under 60 ℃ of temperature, after sustained response to treatment effeciency drops to 70%, absorption liquid is taken out filtration;
4, be 350h by gas liquid ratio -1Amount, air is blasted in the filtered fluid of 3 steps, filtrating being roused oxygen regeneration, the absorption liquid pH value to 9 after the regeneration of adjustment drum oxygen continues to react to purification efficiency and reaches 96.5%; The sulphur that regenerative process produces is through centrifugation, washing, dehydration, the fusion operation of prior art, get final product sulfur product.。
Table 1 is the COS hydrolysis conversion of variable concentrations hexahydropyridine.
Table 2 is the COS hydrolysis conversion behind the different purge times.
The COS hydrolysis conversion of table 1 variable concentrations hexahydropyridine
Figure S2008100586686D00061
COS hydrolysis conversion behind the different purge times of table 2
Figure S2008100586686D00062

Claims (4)

1. the process of a removing organic sulfur in low-temperature condition is characterized in that through the following step:
A, the waste gas that will contain organic sulfur are cooled to 20~100 ℃, are 100~500h by gas liquid ratio -1Amount, waste gas is fed in the organic sulfur absorption liquid of following volume ratio, and makes it saturated, so that tempreture organic sulphur hydrolysis is become H 2S and CO 2, and absorb H 2S:
Figure FSB00000768307700011
B, be 100~500h by gas liquid ratio -1Amount, CO gas is fed in the organic sulfur absorption liquid of A step after saturated, carry out the regeneration of organic sulfur absorption liquid, the temperature of regeneration is 80~100 ℃, the recovery time is 5~8 hours, produces H in the time of regeneration 2S;
C, the H that B step regenerative process is produced 2S gas is 100~500h by gas liquid ratio -1Amount, feed H 2In the S absorption liquid, absorb H 2S is to saturated, with H 2The S absorption liquid takes out and filters;
D, in the filtered fluid of C step, be 100~500h by gas liquid ratio -1The amount bubbling air, carry out H with the air Bubbling method 2The regeneration of S absorption liquid, absorption liquid pH value to 8~9 after the regeneration of adjustment bubbling; The sulphur that regenerative process produces is through centrifugation, washing, dehydration, fusion operation, get final product sulfur product.
2. the process of removing organic sulfur in low-temperature condition according to claim 1 is characterized in that the hydroxide in the organic sulfur absorption liquid of said A step is KOH, NaOH, NH 4Among the OH one or more.
3. the process of removing organic sulfur in low-temperature condition according to claim 1 is characterized in that hexahydropyridine, the ethanol in the organic sulfur absorption liquid of said A step is chemical pure solution, and water is distilled water.
4. the process of removing organic sulfur in low-temperature condition according to claim 1 is characterized in that the H of said C step 2The S absorption liquid and the preparation as follows: at Fe 3+Content is in the solution of 0.03~0.06mol/L, is 10~50% amount by the mass ratio of Mn and Fe, adds Mn (NO 3) 2Or Mn (CH 3COO) 2Again by metal cations Fe 3+With the stabilizing agent integral molar quantity than the amount that is 15~50%, add in edta edta, sulfosalicylic acid, the citric acid one or more, as the metal ion stabilizing agent; Use Na 2CO 3And NaHCO 3Adjustment pH value of solution value to 8~10 get H 2S GAS ABSORPTION liquid.
CN2008100586686A 2008-07-10 2008-07-10 Process for removing organic sulfur in low-temperature condition Expired - Fee Related CN101318099B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2008100586686A CN101318099B (en) 2008-07-10 2008-07-10 Process for removing organic sulfur in low-temperature condition

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2008100586686A CN101318099B (en) 2008-07-10 2008-07-10 Process for removing organic sulfur in low-temperature condition

Publications (2)

Publication Number Publication Date
CN101318099A CN101318099A (en) 2008-12-10
CN101318099B true CN101318099B (en) 2012-07-04

Family

ID=40178521

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2008100586686A Expired - Fee Related CN101318099B (en) 2008-07-10 2008-07-10 Process for removing organic sulfur in low-temperature condition

Country Status (1)

Country Link
CN (1) CN101318099B (en)

Families Citing this family (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102295953B (en) * 2011-07-23 2013-11-27 太原理工大学 Method for removing carbon disulfide
EA202192874A1 (en) 2013-03-14 2022-01-19 Стамикарбон Б.В. Эктин Андер Те Нейм Оф Мт Инновейшн Сентр METHOD TO REMOVE COS AND CS2
CN104629700B (en) * 2015-02-03 2018-05-01 成都理工大学 A kind of sulfur elimination for being used to produce water oil well and water-producing gas well
CN104910970A (en) * 2015-05-22 2015-09-16 张玲 Series-process coal gas desulfurization process method and desulfurization device therefor
EP3331634B8 (en) * 2015-08-06 2023-06-21 Fluor Technologies Corporation Systems and methods for improved sulfur recovery from claus process tail gas
CN110835556A (en) * 2019-11-29 2020-02-25 中冶南方都市环保工程技术股份有限公司 Blast furnace gas wet desulphurization system and method
CN112263894A (en) * 2020-11-26 2021-01-26 西南石油大学 Ionic liquid desulfurization method and device for sulfur-containing gas
CN114191929B (en) * 2021-12-24 2022-12-06 常州化工设计院有限公司 Chemical tail gas treatment process

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1307498A (en) * 1998-06-29 2001-08-08 巴斯福股份公司 Method for removing acid gas components from gases
CN101091869A (en) * 2007-04-06 2007-12-26 昆明理工大学 Method for cleansing exhaust gas of sulfureted hydrogen in low concentration

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1307498A (en) * 1998-06-29 2001-08-08 巴斯福股份公司 Method for removing acid gas components from gases
CN101091869A (en) * 2007-04-06 2007-12-26 昆明理工大学 Method for cleansing exhaust gas of sulfureted hydrogen in low concentration

Also Published As

Publication number Publication date
CN101318099A (en) 2008-12-10

Similar Documents

Publication Publication Date Title
CN101318099B (en) Process for removing organic sulfur in low-temperature condition
AU2014253837B2 (en) Absorbent, process for producing an absorbent, and process and device for separating off hydrogen sulphide from an acidic gas
CN102559316B (en) Methane purifying method and equipment thereof
CN103203242B (en) Catalytic system and process for desulfuration of industrial sulfur-bearing waste gas
CN103111177B (en) Method and device for removing hydrogen sulfide in gas phase through oxidation
CN101352653B (en) Low-temperature micro-oxygen purification method for removing harmful gas in yellow phosphorus tail gas
CN103254957B (en) Device and method for removing hydrogen sulfide out of methane by utilizing collagenous fiber/polyester composite material to load Fe(III)
CN103204470A (en) Gas transformation deep purifying technique for separating and purifying CO and H2 of calcium carbide furnace
CN103768916A (en) Oxidative desulphurization and brimstone recycling method
CN102125802B (en) Method for recovering and purifying waste gas during crude benzene hydrogenation refining production
CN102078813A (en) Catalyst for hydrolyzing carbonyl sulfide at low temperature and preparation method of catalyst
CN100469420C (en) Method for cleansing exhaust gas of sulfureted hydrogen in low concentration
CN103846003B (en) A kind of method removing hydrogen sulfide gas
CN102631832B (en) Slight hydrogen sulfide removal device and method in acidic gas
Kasulla et al. A Retrospection of hydrogen sulphide removal technologies in biogas purification
CN101367718A (en) Method for preparing high-purity sodium formate with tail gas of yellow phosphorus stove
Wan et al. Simultaneous oxidation and absorption of nitric oxide and sulfur dioxide by peroxymonosulfate activated by bimetallic metal-organic frameworks
CN103706323A (en) Method for preparing and regenerating hydrogen cyanide adsorbent
CN101462041A (en) Activated coal modified material for removing thiophen compounds in gasoline and method for preparing and using the same
CN1125163C (en) Coke-oven gas desulfurizing and decyanating process
CN100482319C (en) One-step purifying process for ammonia and methanol
CN107789969A (en) The processing method and device of a kind of sour gas
Mohammadi et al. Analysis and evaluation of the biogas purification technologies from H2S
CN105542873A (en) A purification process system for coke oven gas
CN105567341A (en) Wet purification apparatus for coke oven gas

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
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20120704

Termination date: 20150710

EXPY Termination of patent right or utility model