CN100434162C - Biological matter pyrolysis gasifying detarring catalyst and preparing method - Google Patents

Biological matter pyrolysis gasifying detarring catalyst and preparing method Download PDF

Info

Publication number
CN100434162C
CN100434162C CNB2007100206216A CN200710020621A CN100434162C CN 100434162 C CN100434162 C CN 100434162C CN B2007100206216 A CNB2007100206216 A CN B2007100206216A CN 200710020621 A CN200710020621 A CN 200710020621A CN 100434162 C CN100434162 C CN 100434162C
Authority
CN
China
Prior art keywords
catalyst
dolomite
concave
convex clay
clay rod
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
CNB2007100206216A
Other languages
Chinese (zh)
Other versions
CN101024172A (en
Inventor
陈天虎
庆承松
崔康平
朱承驻
石莹
何宏平
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.)
Hefei University of Technology
Original Assignee
Hefei University of 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 Hefei University of Technology filed Critical Hefei University of Technology
Priority to CNB2007100206216A priority Critical patent/CN100434162C/en
Publication of CN101024172A publication Critical patent/CN101024172A/en
Application granted granted Critical
Publication of CN100434162C publication Critical patent/CN100434162C/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Landscapes

  • Catalysts (AREA)

Abstract

The invention relates to a catalyst of taking off biomass Thermal Gasification tar,Dolomite concavo convex stone clay get the granular or columnar or ring catalyst through crushing,molding and activating, the special surface is 25-1252/g, pore volume is 0.3-0.4ml/g. the described activation after molding calcine 2 to 4 hours under 500-900deg.C. The catalyst tar removal rate reaches more than 90%.

Description

A kind of biological matter pyrolysis gasifying detarring catalyst and preparation method thereof
One, technical field:
The present invention relates to a kind of Catalysts and its preparation method, exactly is a kind of biological matter pyrolysis gasifying detarring catalyst and preparation method thereof.
Two, technical background
Annual about 1,000,000,000 tons of the various stalks of producing of China, agriculture and forestry product and be that the industrial enterprise of raw material also produces several hundred million tons residual processing thing with living beings.Biomass resource is a kind of reproducible clean energy resource, can realize CO 2Zero-emission alleviates greenhouse effects and environmental pollution greatly.With new and high technology development and utilization biomass energy, replace the mineral matter energy such as oil, coal, be one of important channel that solves the energy and environment problem.From present progress, the biomass pyrogenation gasification technology has the advantage that efficient is higher, adaptability to raw material is strong, equipment is simple, investment is lower, relatively be suitable for technology, the economic level of China rural area present stage and following regular period, and not limited by region, weather.Utilize in the technology in numerous living beings, biomass pyrogenation gasification is the most rising, by this technology, can produce valuable combustion gas for civilian and industrial use.
In biomass pyrogenation gasification technology, can contain a certain amount of tar inevitably.When being main purpose with process gas fuel, the existence of tar not only causes factor of created gase and the thermal efficiency to reduce, and also can be condensed into liquid state when low temperature, stops up and etching apparatus thereby be easy to combine with water and dust, causes the equipment can't operate as normal in the time of seriously.The water resource of water elution tar Technology Need consume valuable commonly used and very easily cause serious secondary pollution is difficult to tar in the combustion gas is removed clean simultaneously.Because the tar blockage problem is serious in the biomass gasification burning, the straw from village gasification central gas supply station majority that has built up at present can not run well, and existing small-sized household biomass gasifying furnace is ubiquity tar blockage problem also, and has constituted potential safety hazard.
At the problem that biomass gasification tar causes, Chinese scholars is being studied and is being adopted the catalytic cracking of tar method to solve.Catalytic cracking method be by catalyst at high temperature coke tar cracking be H 2, CH 4, reduce CO simultaneously 2Content, improve flammable composition ratio in the combustion gas.Ni-Al 2O 3, loaded with nano MgO has obligate catalytic action and effect preferably to coke tar cracking, and the catalytic pyrolysis temperature reduces (at 350-500 ℃) greatly, but catalyst cost height.The common white marble is as catalyst, because catalytic activity is low, catalysis detar efficient is low.Chinese patent publication number CN1686606A, title is biomass gasification catalyst and production method." a kind of biomass gasification catalyst and production method " disclosed.Described catalyst is by " Concave-convex clay rod, alumine, iron oxide, magnesia calcium oxide and anthracite are formed ".Above-mentioned catalyst makes goudron lysis rate more than 75%, and rate of gasification improves 15%, and fuel gases calorific value has improved 20%.
In Jiangsu and border land, Anhui abundant Concave-convex clay rod resource is arranged.The Concave-convex clay rod ore type is divided into four kinds: Concave-convex clay rod (attapulgite content is greater than 70%), montmorillonite Concave-convex clay rod (attapulgite content 20-50%, smectite content is greater than 50%), opal Concave-convex clay rod (containing more opal), dolomite Concave-convex clay rod (dolomite content is greater than 20%).Symbiosis has a large amount of dolomite Concave-convex clay rods in the Concave-convex clay rod ore deposit, and with the Concave-convex clay rod alternating layers output of other type.When the exploitation Concave-convex clay rod, the dolomite Concave-convex clay rod is used as abandoned mine and long-term the stacking.The dolomite Concave-convex clay rod is not well utilized at present, has not only increased the Concave-convex clay rod cost of winning, and because a large amount of the stacking caused serious environmental destruction.
Typical case's dolomite Concave-convex clay rod ore chemistry composition is: SiO 2, 33.14%; CaO, 15.9%; MgO, 15.7%; Fe 2O 3, 2.48%; Al 2O 3, 3.69%; TiO 2, 0.39%; Loss on ignition, 28.14%
The applicant discovers the dolomite Concave-convex clay rod with high-resolution-ration transmission electric-lens and ESEM, about the dolomite particle diameter 200nm in the dolomite Concave-convex clay rod, there is the growth or the corrosion step of several nanometers on the surface, and inside has abundant nanometer corrosion hole.This is the very rare nanostructured feature (Fig. 1,2) of nature that the applicant finds first.About attapulgite diameter 40 nanometers wherein, length 300~800 nanometers.The dolomite Concave-convex clay rod is the natural nano-material with unique mineral composition, microstructure and special performance.
Three, summary of the invention
The tar that produces when the present invention is intended to remove biomass pyrogenation gasification, technical problem to be solved are to use cracking catalyst tar.
The alleged detar catalyst of the present invention is that dolomite content is 20~70%, attapulgite content be 20~80% dolomite Concave-convex clay rod through pulverizing, moulding with under 500~900 ℃ of conditions, calcine column or ring-type or the granular catalyst that activation in 2~4 hours obtains, specific area is 25~125m 2/ g, pore volume are 0.3~0.4ml/g.
This Preparation of catalysts method, with the dolomite Concave-convex clay rod is raw material, wherein dolomite content is 20~70%, attapulgite content is 20~80%, comprise pulverizing, moulding and activation, it is characterized in that described activation promptly is to calcine 2~4 hours after the moulding, calcines 2~3 hours under preferred 600~750 ℃ of conditions under 500~900 ℃ of conditions.
The dolomite Concave-convex clay rod is after high-temperature calcination, and palygorskite nano crystal morphology and adsorption activity remain unchanged, and dolomite decomposes about 20 nanometers of generation nano-MgO particle, and loads on the attapulgite plane of crystal, constitutes the nano complex (see figure 4).This complex has very high specific area and to the absorption and the catalytic pyrolysis activity of tar.The MgO particle that the dolomite thermal activation produces in the dolomite Concave-convex clay rod is little more than the MgO particle that common dolime produces, and is close with the MgO granular size of artificial synthetic special load, has very high adsorption capacity and catalytic activity.
Through test shows that the tar clearance reaches more than 90% to the stalk gasifier catalytic cracking of tar.
This catalyst raw material cheapness, be easy to get, preparation technology is simple, and tar clearance height is easy to popularize.
Four, description of drawings
Fig. 1 catalyst raw material dolomite Concave-convex clay rod field emission scanning electron microscope image.Show that the mutual embedding of attapulgite (fibrous crystal) and dolomite (granular solid matter) is living, grow the space, show higher voidage, the about 200-300nm of DOLOMITE CRYSTALS particle diameter, be the dolomite of the particle diameter minimum of present nature discovery, it is active to have higher heat.
Fig. 2 catalyst raw material dolomite Concave-convex clay rod field emission scanning electron microscope image.Show that the DOLOMITE CRYSTALS in the dolomite Concave-convex clay rod contains the microstructure features of nanoscales such as abundant cavity, corrosion step.
Fig. 3 catalyst raw material dolomite Concave-convex clay rod high-resolution-ration transmission electric-lens image shows dolomite pattern in the clay, shows to have nano-mineral features such as nanometer particle size and nanometer cavity.
Fig. 4 the present invention prepares the high-resolution-ration transmission electric-lens image of catalyst, show that the nano-MgO crystal (20 nano-granular particle) that the dolomite thermal activation produces in the catalyst loads on the attapulgite plane of crystal, constitute nano complex, this complex has very high specific area and to the absorption and the catalytic pyrolysis activity of tar.
Five, the specific embodiment
(1) Preparation of catalysts
Now the dolomite Concave-convex clay rod ore with Jiangsu and border land, Anhui is an example as the raw material for preparing catalyst, wherein dolomite content is 60%, the content of attapulgite is 35%, and impure mineral content quartzy and feldspar is about 5%, and non-limiting examples is described below:
1. the fragmentation of dolomite Concave-convex clay rod, screening are obtained the granular material of 0.5~6mm,, promptly obtain graininess detar catalyst through 700 ℃ of calcinings 2 hours.
2. the dolomite Concave-convex clay rod is crushed to granularity≤0.1mm powder.Powder joined throw in the clothing machine, spraying adds an amount of water, and dolomite Concave-convex clay rod powder rolling balling obtains the particle of particle diameter 1~6mm, then 105 ℃ of dryings in baking oven.The particle of preparation was calcined 3 hours for 650 ℃, promptly obtained graininess detar catalyst.
3. the dolomite Concave-convex clay rod is crushed to granularity≤0.1mm powder.Powder and adhesive C MC and water are mixed the back mold pressing be diameter 1~6mm, long 8~10mm's is cylindric or circular, puts in the baking oven earlier to dehydrate, and calcining 2 hours in the time of 750 ℃ then promptly gets column or ring-type detar catalyst.
(2) detar test
The detar catalyst of preparation is loaded into catalytic reactor, is that the catalytic pyrolysis object carries out catalysis experiment with the stalk gasifier tar that condenses, and during 600 ℃ of catalytic reaction temperature, the tar clearance reaches more than 90%.

Claims (3)

1, a kind of biological matter pyrolysis gasifying detarring catalyst, it is characterized in that: this catalyst is that dolomite content is 20~70%, attapulgite content be 20~80% from the marble Concave-convex clay rod through pulverizing, moulding with under 500~900 ℃ of conditions, calcine graininess or column or the ring-type catalyst that activation in 2~4 hours obtains, specific area is 25~125m 2/ g, pore volume are 0.3~0.4ml/g.
2, the described Preparation of catalysts method of claim 1, this method is a raw material with the dolomite Concave-convex clay rod, wherein dolomite content is 20~70%, attapulgite content is 20~80%, this method comprises pulverizing, moulding and activation, it is characterized in that: described activation is to calcine 2~4 hours under 500~900 ℃ of conditions after the moulding.
3, preparation method according to claim 2 is characterized in that: described activation is to calcine 2~3 hours under 600~750 ℃ of conditions after the moulding.
CNB2007100206216A 2007-03-16 2007-03-16 Biological matter pyrolysis gasifying detarring catalyst and preparing method Expired - Fee Related CN100434162C (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CNB2007100206216A CN100434162C (en) 2007-03-16 2007-03-16 Biological matter pyrolysis gasifying detarring catalyst and preparing method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CNB2007100206216A CN100434162C (en) 2007-03-16 2007-03-16 Biological matter pyrolysis gasifying detarring catalyst and preparing method

Publications (2)

Publication Number Publication Date
CN101024172A CN101024172A (en) 2007-08-29
CN100434162C true CN100434162C (en) 2008-11-19

Family

ID=38742998

Family Applications (1)

Application Number Title Priority Date Filing Date
CNB2007100206216A Expired - Fee Related CN100434162C (en) 2007-03-16 2007-03-16 Biological matter pyrolysis gasifying detarring catalyst and preparing method

Country Status (1)

Country Link
CN (1) CN100434162C (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102145298B (en) * 2010-02-09 2013-04-17 广州金安源节能科技股份有限公司 Catalytic conversion agent of tar in gas for biomass boiler
CN103801278A (en) * 2014-02-25 2014-05-21 合肥工业大学 Method for preparing nanometer magnesium oxide composite material through dolomite attapulgite thermal activation and application thereof
CN112246823A (en) * 2020-09-08 2021-01-22 新奥生物质能(天津)有限公司 High ash pyrolytic carbon utilization method and system

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1667086A (en) * 2005-02-25 2005-09-14 许庆华 Purifying system for biomass gasifying oven
CN1686606A (en) * 2005-02-25 2005-10-26 许庆华 Biomass gasification catalyst and its production method
JP2006068723A (en) * 2004-08-06 2006-03-16 Takuma Co Ltd Gasification catalyst, producing method therefor and gasification system

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006068723A (en) * 2004-08-06 2006-03-16 Takuma Co Ltd Gasification catalyst, producing method therefor and gasification system
CN1667086A (en) * 2005-02-25 2005-09-14 许庆华 Purifying system for biomass gasifying oven
CN1686606A (en) * 2005-02-25 2005-10-26 许庆华 Biomass gasification catalyst and its production method

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
生物质焦油的催化裂解研究. 周劲松,王铁柱等.燃料化学学报,第31卷第2期. 2003
生物质焦油的催化裂解研究. 周劲松,王铁柱等.燃料化学学报,第31卷第2期. 2003 *

Also Published As

Publication number Publication date
CN101024172A (en) 2007-08-29

Similar Documents

Publication Publication Date Title
Ma et al. CO2 capture performance of calcium-based synthetic sorbent with hollow core-shell structure under calcium looping conditions
Buentello-Montoya et al. The use of gasification solid products as catalysts for tar reforming
Nizami et al. The potential of Saudi Arabian natural zeolites in energy recovery technologies
Nguyen-Thi et al. Recent advances in hydrogen production from biomass waste with a focus on pyrolysis and gasification
Wang et al. Heterogeneous ZnO-containing catalysts for efficient biodiesel production
Yan et al. Hydrogen production from absorption-enhanced steam gasification of Enteromorpha prolifera and its char using Ce-doped CaO material
CN106582663A (en) Method for in situ catalytic removal of tar in biomass pyrolysis process
Gao et al. Co-pyrolysis of municipal solid waste (MSW) and biomass with Co/sludge fly ash catalyst
CN100434162C (en) Biological matter pyrolysis gasifying detarring catalyst and preparing method
Hossain et al. Hydrogen production by gasification of biomass and opportunity fuels
CN103357411A (en) Calcium-based catalyst for regulating and controlling gas components generated in thermal decomposition and preparation method of calcium-based catalyst
CN101920975A (en) Method for reducing comprehensive energy consumption of coal synthesis ammonia
CN106010667B (en) A kind of method of biomass gas tar oil catalytic pyrolysis purification
CN101348234B (en) Method for preparing hydrogen from biomass
CN101041136A (en) Modification dolomite and the preparing method and the application
CN107202325A (en) The controllable pyrolysis carbonizing kiln of swinging
CN106732704B (en) A kind of antigravity system reducing biomass char oil content in bio oil
Liu et al. A clean route of biodiesel production using red mud-based potassium catalyst
CN109970057A (en) Cellular activated carbon based on coal liquefaction residue and semi-coke end
CN104910934A (en) Biomass organic charcoal preparation method
CN107937011B (en) Biomass rapid pyrolysis device and process
CN101455969A (en) Catalyst for biomass combustible gas transformation
CN106929064A (en) It is a kind of to be suitable to the molding mass containing low-order coal, biomass and rubbish of tamping coking
CN105062604B (en) Preparation method of high-performance coal briquettes and technology for preparing water gas from coal briquettes
Al-Sakkari et al. Inorganic wastes as heterogeneous catalysts for biodiesel production

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
C17 Cessation of patent right
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20081119

Termination date: 20120316