CN102151558A - Method for producing efficient absorbent by utilizing pyrolysis method - Google Patents

Method for producing efficient absorbent by utilizing pyrolysis method Download PDF

Info

Publication number
CN102151558A
CN102151558A CN 201110065054 CN201110065054A CN102151558A CN 102151558 A CN102151558 A CN 102151558A CN 201110065054 CN201110065054 CN 201110065054 CN 201110065054 A CN201110065054 A CN 201110065054A CN 102151558 A CN102151558 A CN 102151558A
Authority
CN
China
Prior art keywords
solids
thermal cracking
pyrolysismethod
efficiency adsorbent
rice husk
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
CN 201110065054
Other languages
Chinese (zh)
Inventor
吴克
刘虎
俞志敏
张晓敏
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.)
ANHUI DONGYANG BIO-ENERGY Ltd Co Ltd
Original Assignee
ANHUI DONGYANG BIO-ENERGY Ltd Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by ANHUI DONGYANG BIO-ENERGY Ltd Co Ltd filed Critical ANHUI DONGYANG BIO-ENERGY Ltd Co Ltd
Priority to CN 201110065054 priority Critical patent/CN102151558A/en
Publication of CN102151558A publication Critical patent/CN102151558A/en
Pending legal-status Critical Current

Links

Abstract

The invention mainly aims to provide a method for producing an efficient absorbent by utilizing a pyrolysis method. Through the method, pyrolysis solids can be recovered and reused. In order to realize the aim, the invention adopts the technical scheme that the method for producing the efficient absorbent by utilizing the pyrolysis method comprises the following steps: a, conveying rice hull into a thermal cracking furnace for thermal cracking and collecting solids generated by the thermal cracking; b, adding zinc salt into the collected solids for activation under the oxygen-free condition; and c, filtering the activated solids and washing the solids to be neutral to obtain the efficient absorbent. According to the processing method, after being collected, the solids generated by the thermal cracking are further activated to obtain the efficient absorbent with both the hydrophilcity and the lipophilicity. Compared with the common active carbon, the absorption effect of the absorbent is improved by 10 percent; and through the reutilization of the solids, the environmental pollution is reduced, and the production efficiency is also improved.

Description

A kind of pyrolysismethod is produced the method for high-efficiency adsorbent
Technical field
The present invention relates to a kind of pyrolysismethod and produce the method for high-efficiency adsorbent, specifically is a kind of processing method of producing high-efficiency adsorbent with rice husk.
Background technology
The main component of rice husk is carbon and silicon, after handling through pyrolysis liquefaction, can form siliceous and pyrolysis solids charcoal, silicon possess hydrophilic property in this pyrolysis solids, and charcoal has lipophile.Pyrolysis liquefaction is meant under complete anoxic or oxygen content situation seldom, rice husk is heated fast and pyrolysis is a kind of mixed vapour and a spot of pyrolysis solids, the wherein rapid condensation of mixed vapour and become a kind of primary liquid fuel, and the pyrolysis solids is directly as offal treatment, and this has just caused very big waste to resource.
Summary of the invention
Main purpose of the present invention provides the method that a kind of pyrolysismethod is produced high-efficiency adsorbent, and this method can be carried out recycling to the pyrolysis solids.
In order to realize the foregoing invention purpose, the technical solution adopted in the present invention is: a kind of pyrolysismethod is produced the method for high-efficiency adsorbent, may further comprise the steps:
A, rice husk delivered to carry out thermal cracking in the pyrocrack furnace, and collect the solids that thermal cracking produces;
Under b, the oxygen free condition, in the solids of collecting, add zinc salt and carry out activation processing;
C, the solids of activated processing is filtered, and washing is to neutral high-efficiency adsorbent.
According to processing method of the present invention, the solids that thermal cracking produces is collected further activation processing of back, both possess hydrophilic properties have just been obtained, has oil loving high-efficiency adsorbent again, this adsorbents adsorb effect is compared common activated carbon and has been improved 10%, the utilization again of solids has reduced environmental pollution, has also improved productivity effect simultaneously.
The specific embodiment
A kind of pyrolysismethod is produced the method for high-efficiency adsorbent, may further comprise the steps:
A, rice husk delivered to carry out thermal cracking in the pyrocrack furnace, and collect the solids that thermal cracking produces.This step promptly is the thermal cracking processes of rice husk, and rice husk is heated fast and pyrolysis is a kind of mixed vapour and a spot of pyrolysis solids, the wherein rapid condensation of mixed vapour and become a kind of primary liquid fuel, and the pyrolysis solids then collects to be done activation and handles.
Under b, the oxygen free condition, in the solids of collecting, add zinc salt and carry out activation processing.Activation processing is the adsorbent process that its aperture forms under the zinc salt effect, and the aperture forms can improve its adsorption capacity.
C, the solids of activated processing is filtered, and washing is to neutral high-efficiency adsorbent.This step is that unnecessary activator is removed by filter, and the activator that water will remain in the adsorbent cleans up, the solids that obtains at last is exactly a high-efficiency adsorbent, this adsorbents adsorb effect is compared common activated carbon and has been improved 10%, the utilization again of solids has reduced environmental pollution, has also improved productivity effect simultaneously.
Before being carried out thermal cracking, rice husk earlier rice husk is done pulverization process.Rice husk is crushed to the material of a certain size particle diameter, helps improving the effect of thermal cracking like this.
Described thermal cracking temperature is 400~600 ℃, and the time is 1~5 second.Here be to utilize the air-flow transport control system that the operation of thermal cracking is controlled.Rice husk is cracked into steam and small fraction of solid rapidly under this temperature, the gas phase time of staying of thermal cracking is difficult for long, otherwise solids can further be heated and destroyed after the cracking.
Described zinc salt is a zinc chloride, and zinc oxide concentration is 15~30%, and the mass ratio of described solids and zinc chloride is 0.5~2.Utilize zinc chloride to make solids form hole, make the solids of carbon containing synthesize nonvolatile polycondensation carbon, thereby produce the adsorbent of loose structure prosperity by effects such as dehydration, condensation, profit rise.So, adding activator, adsorbent can produce the porous of structure prosperity, and absorption property will improve.
Described activation temperature is 400~600 ℃, and the time is 1~2 hour.With this understanding, the activation of adsorbent reaches optimum adsorption effect.
Embodiment 1
Pulverization process is done to rice husk by a, elder generation, rice husk is delivered to carried out thermal cracking in the pyrocrack furnace then, and the thermal cracking temperature is 400 ℃, and the time is 5 seconds, and thermal cracking finishes the back and collects the solids that thermal cracking produces;
Under b, the oxygen free condition, add zinc chloride and carry out activation processing in the solids of collecting, wherein zinc oxide concentration is 15%, and the mass ratio of solids and zinc chloride is 0.5, and activation temperature is 400 ℃, and the time is 2 hours.
C, the solids of activated processing is filtered, and be washed with water to neutral high-efficiency adsorbent.
Embodiment 2
Pulverization process is done to rice husk by a, elder generation, rice husk is delivered to carried out thermal cracking in the pyrocrack furnace then, and the thermal cracking temperature is 600 ℃, and the time is 1 second, and thermal cracking finishes the back and collects the solids that thermal cracking produces;
Under b, the oxygen free condition, add zinc chloride and carry out activation processing in the solids of collecting, wherein zinc oxide concentration is 30%, and the mass ratio of solids and zinc chloride is 2, and activation temperature is 600 ℃, and the time is 1 hour.
C, the solids of activated processing is filtered, and be washed with water to neutral high-efficiency adsorbent.
Embodiment 3
Pulverization process is done to rice husk by a, elder generation, rice husk is delivered to carried out thermal cracking in the pyrocrack furnace then, and the thermal cracking temperature is 500 ℃, and the time is 3 seconds, and thermal cracking finishes the back and collects the solids that thermal cracking produces;
Under b, the oxygen free condition, add zinc chloride and carry out activation processing in the solids of collecting, wherein zinc oxide concentration is 25%, and the mass ratio of solids and zinc chloride is 1.2, and activation temperature is 500 ℃, and the time is 1.5 hours.
C, the solids of activated processing is filtered, and be washed with water to neutral high-efficiency adsorbent.
Measured through adsorption experiment by the high-efficiency adsorbent that above examples of implementation obtain, its I value is all greater than 900mg/g, and the methylene blue value is all greater than 90mg/g, and its adsorption effect is compared common active carbon and significantly improved.

Claims (5)

1. a pyrolysismethod is produced the method for high-efficiency adsorbent, may further comprise the steps:
A, rice husk delivered to carry out thermal cracking in the pyrocrack furnace, and collect the solids that thermal cracking produces;
Under b, the oxygen free condition, in the solids of collecting, add zinc salt and carry out activation processing;
C, the solids of activated processing is filtered, and washing is to neutral high-efficiency adsorbent.
2. a kind of pyrolysismethod according to claim 1 is produced the method for high-efficiency adsorbent, it is characterized in that: earlier rice husk was done pulverization process before rice husk is carried out thermal cracking.
3. a kind of pyrolysismethod according to claim 1 is produced the method for high-efficiency adsorbent, and it is characterized in that: described thermal cracking temperature is 400~600 ℃, and the time is 1~5 second.
4. a kind of pyrolysismethod according to claim 1 is produced the method for high-efficiency adsorbent, and it is characterized in that: described zinc salt is a zinc chloride, and zinc oxide concentration is 15~30%, and the mass ratio of described solids and zinc chloride is 0.5~2.
5. a kind of pyrolysismethod according to claim 1 is produced the method for high-efficiency adsorbent, and it is characterized in that: described activation temperature is 400~600 ℃, and the time is 1~2 hour.
CN 201110065054 2011-03-17 2011-03-17 Method for producing efficient absorbent by utilizing pyrolysis method Pending CN102151558A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN 201110065054 CN102151558A (en) 2011-03-17 2011-03-17 Method for producing efficient absorbent by utilizing pyrolysis method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN 201110065054 CN102151558A (en) 2011-03-17 2011-03-17 Method for producing efficient absorbent by utilizing pyrolysis method

Publications (1)

Publication Number Publication Date
CN102151558A true CN102151558A (en) 2011-08-17

Family

ID=44433425

Family Applications (1)

Application Number Title Priority Date Filing Date
CN 201110065054 Pending CN102151558A (en) 2011-03-17 2011-03-17 Method for producing efficient absorbent by utilizing pyrolysis method

Country Status (1)

Country Link
CN (1) CN102151558A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108421524A (en) * 2018-03-27 2018-08-21 天津大学 A kind of carried non-crystal Mn oxide, preparation method and the usage

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CH589007A5 (en) * 1973-05-04 1977-06-30 Boehlen Bruno Active carbon prodn. from organic polymers - by carbonisation in presence of zinc chloride
CN1319033A (en) * 1998-09-23 2001-10-24 农业技术股份有限公司 Highly activated carbon from caustic digestion of rice hull ash and method
CN1587036A (en) * 2004-07-09 2005-03-02 华东理工大学 Use of biomass cracking residual carbon
CN1876566A (en) * 2006-03-24 2006-12-13 大连理工大学 Microwave radiation method for preparing active carbon from biomass

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CH589007A5 (en) * 1973-05-04 1977-06-30 Boehlen Bruno Active carbon prodn. from organic polymers - by carbonisation in presence of zinc chloride
CN1319033A (en) * 1998-09-23 2001-10-24 农业技术股份有限公司 Highly activated carbon from caustic digestion of rice hull ash and method
CN1587036A (en) * 2004-07-09 2005-03-02 华东理工大学 Use of biomass cracking residual carbon
CN1876566A (en) * 2006-03-24 2006-12-13 大连理工大学 Microwave radiation method for preparing active carbon from biomass

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
《中南大学博士学位论文》 20100228 杨素文 "生物质真空热解液化制生物油及真空化学活化制活性炭研究" , *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108421524A (en) * 2018-03-27 2018-08-21 天津大学 A kind of carried non-crystal Mn oxide, preparation method and the usage

Similar Documents

Publication Publication Date Title
WO2021082761A1 (en) Lanthanum carbonate modified co-pyrolysis sludge biochar and preparation method and application thereof
Jin et al. Characterization of biochars derived from various spent mushroom substrates and evaluation of their adsorption performance of Cu (II) ions from aqueous solution
CN109603749B (en) Preparation method and application of modified straw stalk biochar
WO2016176906A1 (en) Method for producing canna indica biochar capable of adsorbing ammonia nitrogen and cadmium simultaneously
CN103566883A (en) Preparation method of hydrothermal liquefied biochar-based porous carbon and magnetic carbon material and applications of porous carbon and magnetic carbon material
CN103145126B (en) A kind of take waste leather as the method for raw material microwave legal system for gac
CN102078791A (en) Sludge activated carbon and preparation method thereof
CN103480330B (en) Biomass-modified adsorbent for adsorbing coking wastewater, and preparation method and application thereof
CN105753608A (en) Preparation method and application of novel iron-based biochar
CN109173999A (en) A kind of preparation method and applications of biology carbon microspheres
CN102600799A (en) Method for treating wasterwater containing copper by utilizing Spartina alterniflora Loisel-based biochar
CN106881071A (en) A kind of preparation method of modified activated carbon/diatomite adsorbant
Qian et al. A delicate method for the synthesis of high-efficiency Hg (II) The adsorbents based on biochar from corn straw biogas residue
CN105502390A (en) Method for preparing activated carbon from rice husks and sludge in sewage plant
CN103496700A (en) Method for preparing active carbon from pyrolysis residues of cedarwood sawdust
CN104148016A (en) Method for preparing ceramic granule absorption material through fly ash coupled with biochar
CN110773123A (en) Biochar/zeolite composite adsorbent material and preparation method thereof
CN105536698A (en) Preparation method of papermaking sludge activated biochar
CN103771411A (en) Preparation method for active carbon
CN101234332A (en) Method for using sewage sludge and waste graphite to prepare activated adsorption material
CN102838112B (en) Preparation method of activated carbon
CN102423690B (en) Preparation method of mesoporous tomato stem active carbon
CN102190298A (en) Method for preparing active carbon from carbon byproduct in fast pyrolysis of forest remainder
CN106744949A (en) A kind of method for preparing activated carbon as raw material with sesame stalk
CN105080482A (en) Production method for biomass charcoal adsorbents

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C12 Rejection of a patent application after its publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20110817