CN108114570A - One kind contains CS for handling2And H2The method of S mixed pollutants exhaust gas - Google Patents
One kind contains CS for handling2And H2The method of S mixed pollutants exhaust gas Download PDFInfo
- Publication number
- CN108114570A CN108114570A CN201710236095.0A CN201710236095A CN108114570A CN 108114570 A CN108114570 A CN 108114570A CN 201710236095 A CN201710236095 A CN 201710236095A CN 108114570 A CN108114570 A CN 108114570A
- Authority
- CN
- China
- Prior art keywords
- exhaust gas
- adsorption
- temperature plasma
- handling
- low temperature
- 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
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/02—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/14—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
- B01D53/1456—Removing acid components
- B01D53/1468—Removing hydrogen sulfide
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/14—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
- B01D53/1487—Removing organic compounds
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/32—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by electrical effects other than those provided for in group B01D61/00
- B01D53/323—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by electrical effects other than those provided for in group B01D61/00 by electrostatic effects or by high-voltage electric fields
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2252/00—Absorbents, i.e. solvents and liquid materials for gas absorption
- B01D2252/10—Inorganic absorbents
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2253/00—Adsorbents used in seperation treatment of gases and vapours
- B01D2253/20—Organic adsorbents
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2259/00—Type of treatment
- B01D2259/80—Employing electric, magnetic, electromagnetic or wave energy, or particle radiation
- B01D2259/818—Employing electrical discharges or the generation of a plasma
Abstract
Contain CS the invention discloses one kind for handling2And H2The method of S mixed pollutants exhaust gas, belongs to technical field of waste gas treatment.The present invention contains CS for what is discharged during the industry productions such as synthetic fibers, leather, pharmacy2And with a small amount of H2The exhaust gas of S discloses a kind of method handled using absorption low temperature plasma oxidation absorption integrated technique, and super high cross-linked adsorbing resin is to CS2With high selective adsorption capacity, recyclable more than 99% CS2, avoid the wasting of resources;Low temperature plasma can be efficiently by a small amount of H2S and CS2It is oxidized to CO2, H2O and SO2, completely eliminate the foul odour of exhaust gas, SO in tail gas2It is absorbed using lye, so as to fulfill H2S、CS2And SO2Complete qualified discharge.
Description
Technical field
The invention belongs to exhaust-gas treatment fields, and in particular to be generated during to industry productions such as synthetic fibers, pharmacy
Containing CS2And H2The processing method of S exhaust gas, more specifically to a kind of adsorption-low temperature plasma oxidation-absorption integrated technique
Processing is containing CS2And H2The method of S exhaust gas.
Background technology
In the production process of the industries such as synthetic fibers, leather, pharmacy, often generate and largely contain CS2And with a small amount of
H2The exhaust gas of S, the two are the low odorant of threshold value, and can generate damage to the smell of human body and nervous system, therefore
It is very necessary and urgent effectively to administer such exhaust gas.For such tail gas, existing processing method all there are it is certain the defects of.
Such as Crouse's oxidizing process, principle is to make sulfide imperfect combustion, and element sulphur is made to be converted into elemental sulfur.The technique is for exhaust gas
Pressure there are certain requirements, while the technique handles CS in a manner of aoxidizing2, while wasting resource, SO can be generated2By-product,
Easily cause secondary pollution.For another example alkali absorption method, using lye (such as NaOH or NaHCO3) with more efficient can absorb in exhaust gas
H2S is simultaneously converted into the solid products such as NaHS, but lye is for CS2Absorption efficiency it is relatively low.
Such as the publication CN104474875A (times of disclosure:On 04 01st, 2015) disclose a kind of H2S and CS2Mixing
The absorption technique of gas.The technique is passed through air heating until going out by lye spray-absorption exhaust gas, and by the solution after neutralization
Existing simple substance S precipitations continue to be heated to precipitation dissolving, generate sodium polysulfide, and S elements can be fixed as Zhu by input Hg simple substance reactions
Sand (HgS).The for another example 102743969 A (times of disclosure of publication CN:On October 24th, 2012) disclose a kind of absorption-suction
Attached technical finesse contains H2S and CS2The processing method of exhaust gas.Technology utilization NaHCO3Solution absorbs the H in exhaust gas2S, and point
From obtaining NaHS;Tail gas is passed through adsorption recovery CS in the adsorption tower containing granular activated carbon again2, it is achieved thereby that containing CS2With
H2The improvement of S mixed pollutants exhaust gas.But there are some drawbacks for the invention:H in tail gas still containing below 10ppm2S is higher than
The discharge value (0.05ppm, GB14554-93) of national standard;Contain the moisture close to saturation in the exhaust gas absorbed by lye,
Consequent activities charcoal can be significantly reduced to CS2Adsorption efficiency (bibliography:Fan Huiling etc., activated carbon and fixed bed pair under aqueous vapor atmosphere
The adsorption dynamics adsorption kinetics behavior of carbon disulfide, ACTA Scientiae Circumstantiae, 1999,5 (9), 489-493);Moreover, after vapor parsing
Activated carbon needs drying, cool processing, and otherwise the moisture of activated carbon adsorption can also reduce next cycle to CS2Absorption, but
This extends processing technological flow, increases operating cost.In addition, the H not absorbed by lye2S, can be under activated carbon catalysis effect
Simple substance S is oxidized to, so that activated carbon blocks (bibliography:Wu Lang, with activated carbon removing low concentration H2The research of S gases,
Dalian University of Technology's master thesis, 2005).
Lower temperature plasma technology is to generate high energy electron isoreactivity component using high voltage, contaminant molecule is carried out thorough
Bottom oxidative degradation has the characteristics that processing is thorough, simple for process, reaction speed is fast.Low temperature plasma and adsorbing coupled technology
It is widely used in the removal of VOCs, still, usually adsorbent is filled in inside reaction of low temperature plasma device with reinforcing etc.
Gas ions regenerate the adsorbent of adsorption saturation to the degradation of VOCs or using low temperature plasma, can not all realize
The recycling of useful resources.
The content of the invention
1. it to solve the problems, such as
Contain H for existing lye absorption-active carbon adsorption technology processing2S and CS2Shortcomings present in exhaust gas, such as alkali
Liquid removes H2S efficiency is low, H2S is oxidized to elemental sulfur by activated carbon catalysis and causes adsorbent bed blocking, moisture that activated carbon is caused to remove energy
H in power and mechanical strength decline and tail gas2S and CS2It is difficult to up to standard etc., the present invention proposes a kind of hypercrosslinked polymeric resin and inhales
The integrated new process that attached-low-temperature plasma degradation-lye absorbs, can improve to CS2Organic efficiency and H2The removal efficiency of S,
Realize CS2High efficiente callback and H2S and CS2Stably reaching standard discharges.The present invention not only solves exhaust emission as topic, and realizes
The recycling of useful resources.
2. technical solution
To solve the above-mentioned problems, the technical solution adopted in the present invention is as follows:
One kind contains CS for handling2And H2The process system of S mix waste gas, including sequentially connected adsorption tower, low temperature etc.
Gas ions processing unit and lye absorption tower, the bottom of the adsorption tower set gas inlet end, top set vapor into
Enter end, polystyrene super high cross-linked adsorbing resin is filled in adsorption tower;The electric discharge of the reaction of low temperature plasma device
Mode is dielectric barrier discharge, corona discharge or creeping discharge.
Further, there are two the adsorption towers, one is set between adsorption tower and apparatus for low-temperature plasma treatment
Grade condenser and secondary condenser, for being condensed to absorption regeneration steam.
One kind contains CS for handling2And H2The method of S mixed pollutants exhaust gas, using above-mentioned hypercrosslinked polymeric resin absorption-
Low temperature plasma oxidation-lye absorbs integrated technique and is handled, and specific steps include:
(1) CS will be contained2And H2The adsorption tower that the exhaust gas introducing of S is filled with absorption resin carries out adsorption treatment, selective absorption
Recycle CS in exhaust gas2;It is polystyrene super high cross-linked adsorbing resin wherein to adsorb resin, and specific surface area is more than 900m2/ g,
Micropore volume is more than 0.3mL/g and micropore size is distributed between 0.5-1.0nm.
(2) exhaust gas crossed through adsorption treatment is passed through reaction of low temperature plasma device, for removing H2S and minute quantity not by
The CS of sorbing material absorption2, effectively by H2S and CS2It is degraded to CO2, H2O and SO2, H2S and CS2Concentration reaches country's discharge mark
It is accurate;
(3) lye absorption tower will be passed through through the processed exhaust gas of reaction of low temperature plasma device, absorbs low temperature plasma
Oxidative degradation H2By-product SO caused by S2, make SO2Qualified discharge.
Further, in the step (1) adsorption tower altogether there are two, adsorption and desorption process on two towers alternately,
One of adsorption tower is in absorption CS2Meanwhile another adsorption tower is desorbed using 100-130 DEG C of vapor, desorption steams
Gas is condensed recyclable to obtain CS2, the switching of the adsorption and desorption process of two adsorption towers automatically controlled by PLC program.
Further, the discharge mode of the reaction of low temperature plasma device in the step (2) for dielectric barrier discharge,
Corona discharge or creeping discharge etc., apply between two electrodes voltage be 10-25kV, the adjustable high-voltage electricity that frequency is 10-20MHz.
Further, the Alkali absorption liquid in the step (3) can be NaOH, NaHCO3、Na2CO3、K2CO3、KOH、Ca
(OH)2One or more combinations therein, solution concentration is generally in 5wt%-20wt%.
3. advantageous effect
Compared with the prior art, beneficial effects of the present invention are:
(1) sorbing material of the invention is using polystyrene super high cross-linked adsorbing resin, and surface is high hydrophobicity, moisture
Son with absorption resin intermolecular forces it is extremely weak, thus in exhaust gas moisture to CS2Absorption do not influence, to CS in humid gas2It protects
Hold high adsorption capacity;Due to surface hydrophobic, after absorption resin is using vapor desorption, processing need not be dried, letter
Change technical process, reduce energy consumption;Moreover, the micropore size of absorption resin is distributed in 0.5-1.0nm, it is wide in range compared to aperture
The super high cross-linked adsorbing resin of distribution is substantially increased to high volatile CS2Adsorption capacity;
(2) sorbing material of the invention is high molecular polymer, is not had using polystyrene super high cross-linked adsorbing resin
Catalysis, thus H2When S gases pass through adsorption bed, it will not be elemental sulfur by catalysis oxidation, avoid activated carbon adsorption
The problem of elemental sulfur blocks in journey;
(3) " hypercrosslinked polymeric resin adsorption-low temperature plasma oxidation-lye absorbs " process H of the invention2S and
CS2Mixed pollutants exhaust gas, recyclable more than 95% CS2, avoid the wasting of resources, and H2S、CS2And SO2Complete row up to standard
It puts;
(4) present invention contains CS for what is discharged during the industry productions such as synthetic fibers, leather, pharmacy2And with a small amount of
H2The characteristics of S exhaust gas, it is proposed that the integrated treatment process that hypercrosslinked polymeric resin adsorption-low temperature plasma oxidation-lye absorbs,
To realize to CS2Resource reclaim and H2S and CS2The purpose of qualified discharge.
Description of the drawings
Fig. 1 is the structure diagram of the process system of the present invention;
In figure:1st, gas inlet end;2nd, air inducing wind turbine;3rd, emptier;4th, 5- adsorption towers;6th, Low Temperature Plasma Treating
Device;7th, lye absorption tower;8th, vapor upstream end;9th, first-stage condenser;10th, secondary condenser;11st, collecting tank.
Specific embodiment
The present invention is further described below with reference to specific embodiment.
Embodiment 1
As shown in Figure 1, a kind of contain CS for handling2And H2The process system of S mix waste gas, including sequentially connected suction
Attached tower 4,5, apparatus for low-temperature plasma treatment 6 and lye absorption tower 7, adsorption tower 4 and adsorption tower 5 connect side by side, adsorption and desorption
On two towers alternately, the switching of the adsorption and desorption process of two adsorption towers is automatically controlled process by PLC program, adsorption tower
4th, 5 bottom sets gas inlet end 1, air inducing wind turbine 2 and emptier 3, and 4,5 top of adsorption tower sets vapor upstream end 8,
Polystyrene super high cross-linked adsorbing resin is filled in adsorption tower 4;Between adsorption tower 4 and apparatus for low-temperature plasma treatment 6
First-stage condenser 9 and secondary condenser 10 are set, collecting tank 11, first-stage condenser 9 and two level are connected on secondary condenser 10
The effect of condenser 10 is that absorption regeneration steam is condensed.
Processing contains CS2And H2The method of S mixed pollutants exhaust gas, including absorption process, Low Temperature Plasma Treating process
With desorption process, detailed process is as follows:
1. absorption process
Containing CS2With H2The exhaust gas of S carries out absorption behaviour under the action of air inducing wind turbine 2 from gas inlet end 1 into adsorption tower 4
Make, the CS in selective removal exhaust gas2.When absorption, which reaches, to be penetrated, PLC program control air intake valve is closed, and is transferred to desorption rank
Section, while adsorption tower 5 initially enters absorption phase, two adsorption towers carry out adsorption and desorption operation in turn.
2. Low Temperature Plasma Treating process
Gas enters plasma reactor 6, which can be by H2S and a small amount of CS not to be adsorbed2It is oxidized to CO2,
H2O and SO2.Purified gas eventually enters into lye absorption tower 7, to remove the SO in tail gas2, so far, exhaust gas obtains thoroughly
Processing.
3. it is desorbed process
Vapor carries out desorption manipulation from entrance 8 into adsorption tower upper end to the adsorption tower 4 or 5 of adsorption penetration.Outlet
Contain high concentration CS2Steam first pass through first-stage condenser 9 and cool, then by 10 deep condensation of secondary condenser, make CS2
Liquid is condensed into, is collected in collecting tank 11.Contain a small amount of CS2Fixed gas and adsorption tower tail gas import low temperature plasma
Reactor carries out advanced treating.
When being in an emergency, emptying operation can be carried out from the evacuated tube 3 of inlet end.
Embodiment 2
Handle CS2With H2The exhaust gas of S mixtures, main parameter have:Air inducing fan delivery 80CMH, CS2Inlet gas concentration 5g/
m3, H2S concentration 1000mg/m3Intake air temperature room temperature, pressure normal pressure;Absorber diameter DN=180mm, adsorbent are superhigh cross-linking
Resin NDA-150 resins are adsorbed, load height H=300mm, adsorption time 90min, vapor desorption time 60min, level-one
Condenser uses normal temperature circulation water, and secondary condenser uses 5 DEG C of chilled brine;Low temperature plasma uses corona discharge side
Formula, voltage 25kV, frequency 20MHz;Absorbing liquid is the NaOH solution of concentration 5wt%.Exhaust gas is after integrated technique is handled, row
Put CS in tail gas2With H2S is not detected, and collecting tank recycles CS altogether for 24 hours29.3Kg, the rate of recovery 96.9%.
Embodiment 3
Adsorbent in embodiment 2 is changed to macroporous absorbent resin AMBERLITETMXAD-4, other conditions are constant.Discharge
CS in tail gas2Concentration is 103mg/m3, treatment effeciency 97.94%, H2S concentration does not detect.Collecting tank recycles altogether for 24 hours
CS26.9Kg, the rate of recovery 71.9%.
Embodiment 4
Low-temperature plasma bulk voltage in embodiment 2 is changed to 10kV, other conditions are constant.CS in emission2Concentration
For 42mg/m3, treatment effeciency 99.16%;H2S concentration is 8mg/m3, treatment effeciency 99.2%.
Embodiment 5
Low-temperature plasma bulk voltage in embodiment 2 is changed to 15kV, other conditions are constant.CS in emission2Concentration
For 5mg/m3, treatment effeciency 99.9%;H2S is not detected.
Embodiment 6
Low-temperature plasma body frequency in embodiment 2 is changed to 10MHz, other conditions are constant.CS in emission2Concentration
For 18mg/m3, treatment effeciency 99.64%, H2S concentration does not detect.
Embodiment 7
Low-temperature plasma body frequency in embodiment 2 is changed to 15MHz, other conditions are constant.CS in emission2Concentration
For 6mg/m3, treatment effeciency 99.88%, H2S is not detected.
Claims (9)
1. one kind contains CS for handling2And H2The method of S mixed pollutants exhaust gas, it is characterised in that:Using a kind of superhigh cross-linking
Resin adsorption-low temperature plasma oxidation-lye absorbs integrated technique system and is handled, and processing step includes:
(1) CS will be contained2And H2The adsorption tower that the exhaust gas introducing of S is filled with absorption resin carries out adsorption treatment, the absorption resin
For polystyrene super high cross-linked adsorbing resin, specific surface area is more than 900m2/ g, Micropore volume are more than 0.3mL/g and micropore
Pore-size distribution is between 0.5-1.0nm;
(2) exhaust gas crossed through adsorption treatment is passed through reaction of low temperature plasma device, to H2S and CS not to be adsorbed2It is aoxidized
Degradation;
(3) lye absorption tower will be passed through through the processed exhaust gas of reaction of low temperature plasma device, absorbs low temperature plasma oxidation
The by-product that degradation generates.
2. one kind according to claim 1 contains CS for handling2And H2The method of S mixed pollutants exhaust gas, feature exist
In:The integrated technique system includes sequentially connected adsorption tower (4), apparatus for low-temperature plasma treatment (6) and lye and inhales
Tower (7) is received, the bottom of the adsorption tower (4) sets gas inlet end (1), and top sets vapor upstream end (8), adsorption tower
(4) polystyrene super high cross-linked adsorbing resin is filled in.
3. one kind according to claim 2 contains CS for handling2And H2The method of S mixed pollutants exhaust gas, feature exist
In:There are two the adsorption towers (4), adsorption and desorption process on two towers alternately, the adsorption and desorption mistake of two adsorption towers
The switching of journey is automatically controlled by PLC program.
4. one kind according to claim 3 contains CS for handling2And H2The method of S mixed pollutants exhaust gas, feature exist
In:First-stage condenser (9) and secondary condenser (10) are further included in integrated technique system, absorption regeneration steam is condensed.
5. one kind according to claim 3 contains CS for handling2And H2The method of S mixed pollutants exhaust gas, feature exist
In:Desorption process is recycled after desorption steam is condensed to be desorbed using 100-130 DEG C of vapor and obtains CS2。
6. one kind according to claim 1 or 2 contains CS for handling2And H2The method of S mixed pollutants exhaust gas, it is special
Sign is:The discharge mode of reaction of low temperature plasma device described in step (2) is dielectric barrier discharge, corona discharge or edge
It discharges in face.
7. one kind according to claim 6 contains CS for handling2And H2The method of S mixed pollutants exhaust gas, feature exist
In:Between two electrodes of reaction of low temperature plasma device apply voltage be 10-25kV, the adjustable high pressure that frequency is 10-20MHz
Electricity.
8. one kind according to claim 3 or 5 contains CS for handling2And H2The method of S mixed pollutants exhaust gas, it is special
Sign is:Alkali absorption liquid in step (3) is NaOH, NaHCO3、Na2CO3、K2CO3、KOH、Ca(OH)2It is therein a kind of or more
Kind combination.
9. one kind according to claim 8 contains CS for handling2And H2The method of S mixed pollutants exhaust gas, feature exist
In:The concentration of Alkali absorption liquid is 5wt%-20wt%.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710236095.0A CN108114570B (en) | 2017-04-12 | 2017-04-12 | methods for treating plants containing CS2And H2S mixed pollutant waste gas method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710236095.0A CN108114570B (en) | 2017-04-12 | 2017-04-12 | methods for treating plants containing CS2And H2S mixed pollutant waste gas method |
Publications (2)
Publication Number | Publication Date |
---|---|
CN108114570A true CN108114570A (en) | 2018-06-05 |
CN108114570B CN108114570B (en) | 2020-01-31 |
Family
ID=62228103
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201710236095.0A Active CN108114570B (en) | 2017-04-12 | 2017-04-12 | methods for treating plants containing CS2And H2S mixed pollutant waste gas method |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN108114570B (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN112275089A (en) * | 2020-10-15 | 2021-01-29 | 河南中烟工业有限责任公司 | Effluent disposal polluted gas purification system |
CN112642273A (en) * | 2020-12-18 | 2021-04-13 | 阿拉尔市中泰纺织科技有限公司 | Incineration recovery system and process for converting low-concentration waste gas into high-concentration waste gas through degassing |
Citations (13)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101314124A (en) * | 2008-07-15 | 2008-12-03 | 南京大学 | Hydrophobic high-micropore polymeric adsorbent, preparation and uses thereof |
CN101496978A (en) * | 2008-11-27 | 2009-08-05 | 南京大学 | Method for recycling halogenated hydrocarbon compound in gas using hydrophobic high-crosslinking adsorption resin |
CN101530726A (en) * | 2008-04-11 | 2009-09-16 | 玛纳斯澳洋科技有限责任公司 | Method for processing waste gas from the production of viscose chemical fiber |
CN102179129A (en) * | 2011-01-14 | 2011-09-14 | 海湾石油设备(北京)有限公司 | Treatment process for absorbed condensate waste gas |
KR20110103766A (en) * | 2010-03-15 | 2011-09-21 | 삼성중공업 주식회사 | System for desulfurization and denitrification of exhaust gas using wind power generation |
CN102253137A (en) * | 2011-05-03 | 2011-11-23 | 天津出入境检验检疫局化矿金属材料检测中心 | Detection method of trace volatile sulfide in gypsum board |
CN102743969A (en) * | 2012-07-16 | 2012-10-24 | 北京绿创环保设备股份有限公司 | Treatment method for mixed waste gas containing H2S and CS2 |
CN103111166A (en) * | 2013-03-08 | 2013-05-22 | 山东科源化工有限公司 | Method for treating 2, 4-D waste gas |
CN103394248A (en) * | 2013-08-03 | 2013-11-20 | 河北联合大学 | Method used for processing waste gas containing benzene series volatile organic compounds by adsorbent resins |
CN103721524A (en) * | 2014-01-23 | 2014-04-16 | 石家庄科英化工技术有限公司 | Recycling treatment method of CS2 and H2S in waste gas in production of viscose fiber |
CN104107621A (en) * | 2014-08-06 | 2014-10-22 | 南京大学 | Nitrogen purging-assisted organic exhaust gas recycling method through pressure swing adsorption of adsorbent resin |
CN105749714A (en) * | 2016-04-19 | 2016-07-13 | 中国石油化工股份有限公司 | Method and equipment for treating volatile organic compounds by coupling of adsorption and low-temperature plasmas |
CN105983295A (en) * | 2016-01-15 | 2016-10-05 | 中国科学院等离子体物理研究所 | Low-temperature plasma synergistic adsorption type industrial waste gas treatment method |
-
2017
- 2017-04-12 CN CN201710236095.0A patent/CN108114570B/en active Active
Patent Citations (13)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101530726A (en) * | 2008-04-11 | 2009-09-16 | 玛纳斯澳洋科技有限责任公司 | Method for processing waste gas from the production of viscose chemical fiber |
CN101314124A (en) * | 2008-07-15 | 2008-12-03 | 南京大学 | Hydrophobic high-micropore polymeric adsorbent, preparation and uses thereof |
CN101496978A (en) * | 2008-11-27 | 2009-08-05 | 南京大学 | Method for recycling halogenated hydrocarbon compound in gas using hydrophobic high-crosslinking adsorption resin |
KR20110103766A (en) * | 2010-03-15 | 2011-09-21 | 삼성중공업 주식회사 | System for desulfurization and denitrification of exhaust gas using wind power generation |
CN102179129A (en) * | 2011-01-14 | 2011-09-14 | 海湾石油设备(北京)有限公司 | Treatment process for absorbed condensate waste gas |
CN102253137A (en) * | 2011-05-03 | 2011-11-23 | 天津出入境检验检疫局化矿金属材料检测中心 | Detection method of trace volatile sulfide in gypsum board |
CN102743969A (en) * | 2012-07-16 | 2012-10-24 | 北京绿创环保设备股份有限公司 | Treatment method for mixed waste gas containing H2S and CS2 |
CN103111166A (en) * | 2013-03-08 | 2013-05-22 | 山东科源化工有限公司 | Method for treating 2, 4-D waste gas |
CN103394248A (en) * | 2013-08-03 | 2013-11-20 | 河北联合大学 | Method used for processing waste gas containing benzene series volatile organic compounds by adsorbent resins |
CN103721524A (en) * | 2014-01-23 | 2014-04-16 | 石家庄科英化工技术有限公司 | Recycling treatment method of CS2 and H2S in waste gas in production of viscose fiber |
CN104107621A (en) * | 2014-08-06 | 2014-10-22 | 南京大学 | Nitrogen purging-assisted organic exhaust gas recycling method through pressure swing adsorption of adsorbent resin |
CN105983295A (en) * | 2016-01-15 | 2016-10-05 | 中国科学院等离子体物理研究所 | Low-temperature plasma synergistic adsorption type industrial waste gas treatment method |
CN105749714A (en) * | 2016-04-19 | 2016-07-13 | 中国石油化工股份有限公司 | Method and equipment for treating volatile organic compounds by coupling of adsorption and low-temperature plasmas |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN112275089A (en) * | 2020-10-15 | 2021-01-29 | 河南中烟工业有限责任公司 | Effluent disposal polluted gas purification system |
CN112642273A (en) * | 2020-12-18 | 2021-04-13 | 阿拉尔市中泰纺织科技有限公司 | Incineration recovery system and process for converting low-concentration waste gas into high-concentration waste gas through degassing |
Also Published As
Publication number | Publication date |
---|---|
CN108114570B (en) | 2020-01-31 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
KR101207532B1 (en) | Apparatus for performing drying and removing impurities process of bio-methane at high purity bio-methane purification system | |
CN106422667B (en) | The method of one-step removal acidic components and water from gas | |
US11285429B2 (en) | System for treating malodorous gas from sludge | |
CN104524918A (en) | Method and device for recycling VOC in low-concentration VOC-containing mixed gas | |
CN101219919B (en) | Method for purifying and recycling methyl hydride from garbage landfill gas | |
CN105833677A (en) | Method and equipment for treating volatile organic compounds by low-temperature plasma coupling adsorption | |
CN1951541A (en) | Process for purifying sulfur-containing foul waste gas | |
CN103252223A (en) | Method for regenerating saturated active carbon adsorbing organic matters through microwave activation of potassium persulfate | |
CN108114570A (en) | One kind contains CS for handling2And H2The method of S mixed pollutants exhaust gas | |
CN104624012A (en) | Gas treatment device and gas treatment method | |
CN105107461A (en) | Method for regenerating activated carbon by corona-dielectric barrier cooperative discharging | |
CN208449008U (en) | A kind of combined type organic waste-gas purification and recyclable device | |
CN102512905A (en) | Emission reduction method for tail gas in sulfuric acid production | |
CN207102266U (en) | A kind of low temperature plasma Coupling Adsorption method processing VOCs and foul gas device | |
CN212819023U (en) | Compression absorption film adsorption combined type oil gas recovery device | |
CN203540282U (en) | Treatment device of odor containing hydrocarbon and sulfide | |
CN220110728U (en) | A high-efficient device of taking off of inhaling for VOCs administers | |
CN202876608U (en) | Organic waste gas adsorption and vacuum desorption recycling device | |
CN112516745A (en) | Low-concentration sulfur hexafluoride waste gas adsorption and purification device | |
CN114887434B (en) | VOCs treatment process for finished oil | |
CN110935281A (en) | Adsorption and regeneration device and method for solid adsorbent for adsorbing volatile organic compounds | |
CN206276190U (en) | A kind of simple recyclable continuous absorbent charcoal adsorber for using | |
CN110743521B (en) | Mercury-absorbing coke sinking type rapid desorption system and method | |
CN108246061A (en) | The processing method for the exhaust gas containing VOCs that a kind of loss of sewage lifting pond goes out | |
CN113634104A (en) | Treatment process of waste gas generated in kitchen waste treatment process |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant |