CN103721678A - Efficient absorbent used for purification of biogass and coalbed methane and preparation method thereof - Google Patents

Efficient absorbent used for purification of biogass and coalbed methane and preparation method thereof Download PDF

Info

Publication number
CN103721678A
CN103721678A CN201210384714.8A CN201210384714A CN103721678A CN 103721678 A CN103721678 A CN 103721678A CN 201210384714 A CN201210384714 A CN 201210384714A CN 103721678 A CN103721678 A CN 103721678A
Authority
CN
China
Prior art keywords
adsorbent
starch
preparation technology
raw material
phenolic resins
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201210384714.8A
Other languages
Chinese (zh)
Inventor
刘克欣
杨金涛
张宏敏
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to CN201210384714.8A priority Critical patent/CN103721678A/en
Publication of CN103721678A publication Critical patent/CN103721678A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/40Capture or disposal of greenhouse gases of CO2

Landscapes

  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Separation Of Gases By Adsorption (AREA)

Abstract

The invention relates to an efficient absorbent used for purification of biogass and coalbed methane and a preparation method thereof. The absorbent is prepared from raw materials such as starch, phenolic resin and coal powder. The main preparation technology comprises crushing, mixing, forming, carbonization, activation and the like. The obtained absorbent has abundant micropores and is used in separation process of methane and carbon dioxide, the separation obtained methane gas has the purity more than 97%, and the absorbent is applicable to pressure swing adsorption apparatuses.

Description

Be used for high-efficiency adsorbent of biogas, coal bed gas purification and preparation method thereof
Technical field
The present invention relates to high-efficiency adsorbent and the manufacture method of biogas, coal bed gas purification.
Background technology
In recent years, the fossil fuels such as coal, oil, natural gas non-renewable, and all environmental problems such as greenhouse effects of causing of petroleum refining industry, acid rain, dust pollution, cause people's common concern, greatly promoted the research and development of the regenerative resource industries such as wind energy, solar energy, water energy, biomass energy, geothermal energy, ocean energy.Biogas is subject to common concern as a kind of biomass energy general, that easily obtain with the extensive utilization of its efficient stable, and compared with other combustion gas, its capability of antidetonance is better, is a kind of generally acknowledged clean type recyclable fuel.
Improve biogas quality, first want purifying marsh gas, remove various impurity components (removing sulfide, halide, amine etc.), then carry out CH 4purify and (remove CO 2).Purification method is divided and can be divided into wet method and dry method by absorbent state; By the principle of processing, divide, can be divided into chemical absorption method, Physical Absorption method, membrane separation process, pressure swing adsorption method and bioanalysis etc.The above several separation methods of contrast, the film using in membrane separation process needs often to change, and operating cost is higher, and pressure-variable adsorption agent and chemical absorbent can be recycled, therefore, pressure swing adsorption method and chemical absorption method are wider compared with the practical application of membrane separation technique.Pressure swing adsorption method, compared with chemical absorption method, does not have adding of other medicaments in addition, to equipment non-corrosiveness, almost without " three wastes ", produce, can not cause new environmental pollution, and operation at normal temperatures, can save heating or cooling energy consumption, reduce operating cost.In addition the product purity of pressure swing adsorption method technique is high and can flexible modulation, and can arbitrarily regulate in the larger context according to the variation of process conditions the purity of product methane.Meanwhile, pressure swing adsorption method purification facility scale is flexible, in the purification project of small-scale, especially has superiority.And whole technique is by computer control, easy to operate, device can be realized full automatic working.Visible, pressure swing adsorption method is the one preferred technique in gas purification.
In pressure swing adsorption method technique, key technology is the performance of adsorbent; In general, adsorbent has appropriate surfaces structure and pore structure, easily manufactured, generally do not react with adsorbate, easily regeneration, has good mechanical strength, and adsorbent is all widely used in various fields such as petroleum industry, gas industry, medical science, environmental protection, pharmaceuticals industries.Current adsorbent kind used is a lot, but conventional has active carbon, molecular sieve, silica gel, activated alumina and a clay etc.Conventional adsorbent has two kinds, active carbon and molecular sieve.
The microcrystal of active carbon is that the laminated structure accumulation of being arranged with hexagonal lattice by carbon atom forms, be difficult for broken, the space generating between lattice forms various shapes and big or small pore, there is abundant microcellular structure, make active carbon there is large specific area and strong absorption property, belong to apolar substance.
In microporous molecular sieve, there is the hole of many marshallings, these holes not only provide bigger serface, can also play the effect of screening molecule, the molecule that is less than aperture enters molecular sieve endoporus, the molecule larger than aperture is blocked in molecular sieve surface, thereby the shape of making and the molecule varying in size are separated, belong to polar adsorbent, polar molecule is had to strong absorption property, can carry out depth drying and purification to gas, the in the situation that of higher temperature and certain humidity, also have higher selective.
The achievement in research of acticarbon mainly contains two aspects at present, and the one, to the modification of active carbon, for example, adopt the metal ions such as calcium, copper, magnesium to do after surface modification treatment active carbon, charcoal absorption CO 2performance have clear improvement.The 2nd, the new raw material of activated carbon is manufactured in exploitation, such as coal-based and biomass-based etc.Aspect the developmental research of molecular sieve, mainly concentrate on the study on the modification of molecular sieve.
It is raw material that adsorbent of the present invention adopts phenolic resins, starch and coal, and the adsorbent obtaining has the dual-use function of active carbon and molecular sieve, has good absorption property.
Summary of the invention
The object of this invention is to provide a kind of high-efficiency adsorbent for biogas, coal bed gas purification.
Another object of the present invention is to provide the simple preparation method of one of above-mentioned adsorbent, and this adsorbent can be used for pressure-variable adsorption by suitable stride rapid and the reverse methane and carbon dioxide vacuumizing in step concentrating and separating biogas or coal bed gas.
Object of the present invention realizes by following technical proposal:
(1) needed raw material starch, phenolic resins and coal dust are crushed to below 15 μ m;
(2) add by a certain percentage kneader, add water simultaneously, machine and mix;
(3) material mixing is shaped to cylinder on forming machine;
(4) put into drier, dry 12h at 80 ℃;
(5) dried material is put into heating furnace, under nitrogen protection, with the programming rate of 10 ℃/min, be heated to 300 ℃, and then with the programming rate of 5 ℃/min, be heated to 850 ℃, constant temperature 90min.
(6) after cooling, by the good sample of carbonization, under nitrogen protection, carry out steam activation, activation temperature is 700~800 ℃, and soak time is 1~6h.
(7) after cooling, then obtain granular adsorbent after washing, being dried.
Described adsorbent raw material, phenolic resins is thermosetting resin, starch can be cornstarch, tapioca, potato starch or wheaten starch, is preferably tapioca.
After crushed, particle diameter should be controlled at 10~20 μ m to described raw material.
The quality proportioning of described raw material: starch: phenolic resins: coal dust=5%~20%: 20~60%: 20~60%, preferred value is starch: phenolic resins: coal dust=10%: 45%: 45%.
The addition of described adsorbent-shaping process water is 1~10% (quality) of material quantity, and preferred value is 3%.
After described adsorbent-shaping, the suitable column diameter that is of a size of of granular material is 1~3mm, height 2-10mm, and preferred value is Φ 2 × 4mm.
After described adsorbent-shaping, need be at 80 ℃, dry 12h; And then under nitrogen protection, carry out carbonization at 850 ℃.
After described adsorbent carbonization, need be under nitrogen protection, use steam to activate at 700-800 ℃, preferred activation temperature is 750 ℃.
On pressure-swing absorption apparatus, test the separating property of this adsorbent to methane and carbon dioxide, test condition is: adsorptive pressure 0.4Mpa, desorption pressure-0.098Mpa, adsorption column Φ 20 × 300mm, raw gas flow 40ml/min, the concentration of separation of methane is greater than 97%.
Compared with prior art, adsorbent of the present invention has following features:
(1) preparation method's technique is simple, has low, the free of contamination feature of cost.
(2) granular adsorbent of preparing has the dual-use function of active carbon and molecular sieve and good absorption property.
(3) prepare adsorbent and there is abundant micropore, for the separation process of methane, carbon dioxide, separate the methane gas purity obtaining and exceed 97%, can be used for pressure-swing absorption apparatus.
(4) adsorbent of the present invention can be processed into difformity, meets the demand of different industries.
The specific embodiment
Embodiment 1
First needed raw material tapioca, phenolic resins and coal dust are pulverized, be then sized to 10~20 μ m, by following mass fraction, prepare burden, starch: phenolic resins: coal dust=10%: 45%: 45%; Put into kneader, add the water of 3% (quality) simultaneously, mix 1h; On forming machine, be molded into Φ 2 × 4mm cylinder, put into drier, dry 12h at 80 ℃; Put into carbide furnace, under nitrogen protection, with the programming rate of 10 ℃/min, be heated to 300 ℃, and then be heated to 850 ℃ with the programming rate of 5 ℃/min, constant temperature 90min, after cooling, injects gasification furnace by water with the amount of 10ml/min, and is 0.5m by flow 3the nitrogen of/h is brought steam into activation furnace, at 750 ℃, and activation 2h; At nitrogen protection borehole cooling, obtain product.Properties of product are: the following microporosity 86% of 0.8nm, specific area: 1100m 2/ g; On pressure-swing absorption apparatus, test the separating property of this adsorbent to methane and carbon dioxide, test condition is: adsorptive pressure 0.4Mpa, desorption pressure-0.098Mpa, adsorption column Φ 20 × 300mm, raw gas flow 40ml/min, the concentration 99% of separation of methane.
Embodiment 2
First needed raw material tapioca, phenolic resins and coal dust are pulverized, be then sized to 10~20 μ m, by following mass fraction, prepare burden, starch: phenolic resins: coal dust=5%: 50%: 45%; Put into kneader, add the water of 3% (quality) simultaneously, mix 1h; On forming machine, be molded into Φ 2 × 4mm cylinder, put into drier, dry 12h at 80 ℃; Put into carbide furnace, under nitrogen protection, with the programming rate of 10 ℃/min, be heated to 300 ℃, and then be heated to 850 ℃ with the programming rate of 5 ℃/min, constant temperature 90min, after cooling, injects gasification furnace by water with the amount of 10ml/min, and is 0.5m by flow 3the nitrogen of/h is brought steam into activation furnace, at 750 ℃, and activation 2h; At nitrogen protection borehole cooling, obtain product.Properties of product are: the following microporosity 82% of 0.8nm, specific area: 960m 2/ g; On pressure-swing absorption apparatus, test the separating property of this adsorbent to methane and carbon dioxide, test condition is: adsorptive pressure 0.4Mpa, desorption pressure-0.098Mpa, adsorption column Φ 20 × 300mm, raw gas flow 40ml/min, the concentration 98% of separation of methane.
Embodiment 3
First needed raw material tapioca, phenolic resins and coal dust are pulverized, be then sized to 10~20 μ m, by following mass fraction, prepare burden, starch: phenolic resins: coal dust=20%: 40%: 40%; Put into kneader, add the water of 1% (quality) simultaneously, mix 1h; On forming machine, be molded into Φ 2 × 4mm cylinder, put into drier, dry 12h at 80 ℃; Put into carbide furnace, under nitrogen protection, with the programming rate of 10 ℃/min, be heated to 300 ℃, and then be heated to 850 ℃ with the programming rate of 5 ℃/min, constant temperature 90min, after cooling, injects gasification furnace by water with the amount of 10ml/min, and is 0.5m by flow 3the nitrogen of/h is brought steam into activation furnace, at 750 ℃, and activation 2h; At nitrogen protection borehole cooling, obtain product.Properties of product are: the following microporosity 76% of 0.8nm, specific area: 840m 2/ g; On pressure-swing absorption apparatus, test the separating property of this adsorbent to methane and carbon dioxide, test condition is: adsorptive pressure 0.4Mpa, desorption pressure-0.098Mpa, adsorption column Φ 20 × 300mm, raw gas flow 40ml/min, the concentration 96% of separation of methane.
Embodiment 4
Change tapioca into cornstarch, other condition is identical with enforcement 1.Properties of product are: the following microporosity 82% of 0.8nm, specific area: 930m 2/ g; On pressure-swing absorption apparatus, test the separating property of this adsorbent to methane and carbon dioxide, test condition is: adsorptive pressure 0.4Mpa, desorption pressure-0.098Mpa, adsorption column Φ 20 × 300mm, raw gas flow 40ml/min, the concentration 97% of separation of methane.
Embodiment 5
Change tapioca into potato starch, other condition is identical with enforcement 1.Properties of product are: the following microporosity 77% of 0.8nm, specific area: 860m 2/ g; On pressure-swing absorption apparatus, test the separating property of this adsorbent to methane and carbon dioxide, test condition is: adsorptive pressure 0.4Mpa, desorption pressure-0.098Mpa, adsorption column Φ 20 × 300mm, raw gas flow 40ml/min, the concentration 95% of separation of methane.

Claims (8)

1. for an adsorbent for biogas, coal bed gas purification, it is characterized in that its physical property is:
Shape: cylindric;
The following microporosity of microporosity: 0.8nm is greater than 70%;
Specific area: 500~1500m 2/ g.
2. adsorbent according to claim 1, is characterized in that by starch, phenolic resins and coal dust being that raw material makes.
3. adsorbent according to claim 1, is characterized in that preparation technology comprises the following steps successively:
(1) pulverize: raw material is less than to 15 μ m through being crushed to particle diameter;
(2) mix: three kinds of raw materials are mixed by a certain percentage;
(3) moulding: mixed material is through being molded into cylindrical pellet;
(4) carbonization: the cylindric material obtaining carries out carbonization under nitrogen protection;
(5) activation: after carbonization treatment, use steam activation under nitrogen protection.
4. adsorbent raw material according to claim 2, is characterized in that phenolic resins is thermosetting resin, and starch can be cornstarch, tapioca, potato starch or wheaten starch.
5. preparation technology according to claim 3, is characterized in that the mass fraction of starch, phenolic resins and coal dust is respectively: 5%~20%, 20~60%, 20~60%.
6. preparation technology according to claim 3, is characterized in that the particle diameter of raw material is controlled at 10~20 μ m.
7. preparation technology according to claim 3, is characterized in that carburizing temperature is 750~880 ℃.
8. preparation technology according to claim 3, is characterized in that activation temperature is 700~800 ℃.
CN201210384714.8A 2012-10-12 2012-10-12 Efficient absorbent used for purification of biogass and coalbed methane and preparation method thereof Pending CN103721678A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201210384714.8A CN103721678A (en) 2012-10-12 2012-10-12 Efficient absorbent used for purification of biogass and coalbed methane and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201210384714.8A CN103721678A (en) 2012-10-12 2012-10-12 Efficient absorbent used for purification of biogass and coalbed methane and preparation method thereof

Publications (1)

Publication Number Publication Date
CN103721678A true CN103721678A (en) 2014-04-16

Family

ID=50446118

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201210384714.8A Pending CN103721678A (en) 2012-10-12 2012-10-12 Efficient absorbent used for purification of biogass and coalbed methane and preparation method thereof

Country Status (1)

Country Link
CN (1) CN103721678A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115924884A (en) * 2022-12-12 2023-04-07 宣城市中兴分子筛有限公司 Method for extracting carbon molecular sieve for methane from biogas

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5688313A (en) * 1996-06-21 1997-11-18 Amcol International Corporation Activated carbon foundry sand additives and method of casting metal for reduced VOC emissions
CN1258638A (en) * 1998-12-25 2000-07-05 中国科学院山西煤炭化学研究所 Preparation of active carbon adsorbing and storing methane
CN101653721A (en) * 2009-09-15 2010-02-24 重庆大学 Preparation method of coal-based granular activated carbon with molecular sieving effect and application thereof in pressure-transformation adsorption and separation concentrated gas

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5688313A (en) * 1996-06-21 1997-11-18 Amcol International Corporation Activated carbon foundry sand additives and method of casting metal for reduced VOC emissions
CN1258638A (en) * 1998-12-25 2000-07-05 中国科学院山西煤炭化学研究所 Preparation of active carbon adsorbing and storing methane
CN101653721A (en) * 2009-09-15 2010-02-24 重庆大学 Preparation method of coal-based granular activated carbon with molecular sieving effect and application thereof in pressure-transformation adsorption and separation concentrated gas

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
刘立恒等: "粘结剂对颗粒活性炭PSA分离CH4/N2性能的影响", 《材料研究学报》 *
刘立恒等: "粘结剂对颗粒活性炭PSA分离CH4/N2性能的影响", 《材料研究学报》, vol. 25, no. 3, 30 June 2011 (2011-06-30) *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115924884A (en) * 2022-12-12 2023-04-07 宣城市中兴分子筛有限公司 Method for extracting carbon molecular sieve for methane from biogas

Similar Documents

Publication Publication Date Title
Aghel et al. CO2 capture from biogas by biomass-based adsorbents: A review
Li et al. Efficient nitrogen doped porous carbonaceous CO2 adsorbents based on lotus leaf
Yaumi et al. Recent advances in functionalized composite solid materials for carbon dioxide capture
Li et al. A review on biomass-derived CO2 adsorption capture: adsorbent, adsorber, adsorption, and advice
Chen et al. The structure evolution of biochar from biomass pyrolysis and its correlation with gas pollutant adsorption performance
Xu et al. Excellent CO2 adsorption performance of nitrogen-doped waste biocarbon prepared with different activators
Shi et al. Nitrogen-doped activated carbons derived from microalgae pyrolysis by-products by microwave/KOH activation for CO2 adsorption
Zhang et al. Preparation and evaluation of fine-tuned micropore biochar by lignin impregnation for CO2 and VOCs adsorption
Gopalan et al. Insight into metal-impregnated biomass based activated carbon for enhanced carbon dioxide adsorption: A review
Gil et al. Carbon adsorbents for CO2 capture from bio-hydrogen and biogas streams: Breakthrough adsorption study
Lee et al. A review on solid adsorbents for carbon dioxide capture
Song et al. Surface characterization studies of walnut-shell biochar catalysts for simultaneously removing of organic sulfur from yellow phosphorus tail gas
CN101531365B (en) Preparation method of pressed active carbon for pressure swing adsorption/separation of methane/nitrogen
Jin et al. Sawdust wastes-derived porous carbons for CO2 adsorption. Part 1. Optimization preparation via orthogonal experiment
Ridassepri et al. Activated carbon from bagasse and its application for water vapor adsorption
KR102197821B1 (en) Porous carbon made from plastics and a method for producing the same
Dong et al. Ultramicroporous carbon granules with narrow pore size distribution for efficient CH4 separation from coal‐bed gases
CN102745879A (en) Sludge-based adsorbent used for desulfurization and demercuration of flue-gas and preparation method thereof
CN103086354A (en) Carbon molecular sieve for concentrating and extracting CH4 from coal bed gas and preparation method thereof
Cheng et al. Nitrogen-doped microporous carbon material decorated with metal nanoparticles derived from solid Zn/Co zeolitic imidazolate framework with high selectivity for CO2 separation
Luo et al. Preparation of N-doped activated carbons with high CO 2 capture performance from microalgae (Chlorococcum sp.)
CN103691399A (en) Preparation method of high-performance carbon molecular sieve for separating carbon dioxide/methane
Cheng et al. Enhanced CO2 selectivity of mixed matrix membranes with carbonized Zn/Co zeolitic imidazolate frameworks
US9120079B1 (en) High capacity carbon dioxide sorbent
Dali et al. General study about activated carbon for adsorption carbon dioxide

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
DD01 Delivery of document by public notice

Addressee: Yang Jintao

Document name: the First Notification of an Office Action

DD01 Delivery of document by public notice

Addressee: Liu Kexin

Document name: Notification that Application Deemed to be Withdrawn

C02 Deemed withdrawal of patent application after publication (patent law 2001)
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20140416