CN106607007A - Preparation method for MgO loaded china-hemp stalk activated carbon - Google Patents

Preparation method for MgO loaded china-hemp stalk activated carbon Download PDF

Info

Publication number
CN106607007A
CN106607007A CN201510680420.3A CN201510680420A CN106607007A CN 106607007 A CN106607007 A CN 106607007A CN 201510680420 A CN201510680420 A CN 201510680420A CN 106607007 A CN106607007 A CN 106607007A
Authority
CN
China
Prior art keywords
activated carbon
fructus cannabis
mgo
preparation
cannabis stalk
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
CN201510680420.3A
Other languages
Chinese (zh)
Inventor
陈瑶
高建民
张骥
郝新敏
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.)
Beijing Forestry University
Original Assignee
Beijing Forestry University
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 Beijing Forestry University filed Critical Beijing Forestry University
Priority to CN201510680420.3A priority Critical patent/CN106607007A/en
Publication of CN106607007A publication Critical patent/CN106607007A/en
Pending legal-status Critical Current

Links

Abstract

The invention provides a preparation method for MgO loaded china-hemp stalk activated carbon. With china-hemp stalks as a raw material, the nano MgO loaded china-hemp stalk activated carbon having rich micropore structure and large specific surface area is prepared by a KOH activation method. After the KOH activation, the prepared china-hemp stalk activated carbon well inherits the pore structure of a precursor. At the same time, the china-hemp stalks are used as a carrier, so the problem of difficult recovery after nano MgO is used can be solved, the specific surface area of nano MgO is increased, the reaction activity is increased, and activated carbon as a carrier is combined with the performance of catalytic degradation of MgO. On one hand, good adsorption properties of activated carbon on wastewater, dyes and the like are used, on the other hand, MgO is used for complete degradation of pollutants, and the efficiency of adsorption and degradation of the pollutants is greatly increased.

Description

A kind of MgO loads the preparation method of Fructus Cannabis stalk activated carbon
Technical field
The present invention relates to a kind of MgO loads the preparation method of Fructus Cannabis stalk activated carbon, belong to the technical field of activated carbon manufacture and modified aspect.Additionally, Also relate to the recycling treatment of solid waste in industrial and agricultural production.
Background technology
Fructus Cannabis are the herbaceous plant that a class has natural fibre construction, and the plant growing cycle is shorter, stronger to the adaptability of environment, south China Regional plantation amount is larger.At present for the main application of Fructus Cannabis or using its phloem fiber manufacturing textile, and it is overall big for plant is accounted for About 80% Fructus Cannabis stalk is not but fully utilized, therefore to a great extent, causes the waste of resource.The constituent of Fructus Cannabis stalk and structure It is similar to common wood, wherein containing the pore structure of cellulose, hemicellulose, lignin and prosperity.Meanwhile, Fructus Cannabis stalk material has day Right nano micropore structure, this structure can be preserved after carbonization, therefore are prepared rich in the splendid of a large amount of microporous activated Carbon Materials Raw material.
Nano magnesia is the critical function material for being widely used in the fields such as the improvement of toxic waste, catalysis, antibacterial, its surface exist a large amount of defects, Side, angle, step isoreactivity position allow which as adsorbent, adsorb harmful gass or remove harmful metal ion in eliminating water.Nano oxidized magnesium raw material Low cost, preparation technology are easy, and the catalytic degradation process of the important point nano magnesia does not need light to excite, need not rely on ultraviolet light light According to, therefore nano magnesia is a kind of nano anti-biotic material being most widely used.If nano magnesia is carried on activated carbon, then its ratio Surface area will be higher, and chemical property also further can be lifted, so the preparation of the activated carbon supported type catalyst of nano magnesia and property in recent years The emphasis for becoming domestic and international research can be tested.
Activated carbon as a kind of common adsorbing material, with cheap, pore structure it is flourishing, specific surface area is big, absorbability relatively strong and machine The advantages of tool intensity is reliable.Fructus Cannabis stalk is a kind of agricultural crop straw with natural void structure, after KOH activation, the Fructus Cannabis being prepared from Stalk activated carbon inherits the aperture structure of presoma well.Using Fructus Cannabis stalk activated carbon as carrier, nano magnesia use can be solved well The problem of the recovery difficulty for occurring afterwards, and the specific surface area of nano magnesia is improve, so as to improve reactivity.
The content of the invention
The purpose of the present invention aims to the deficiencies in the prior art, there is provided a kind of MgO loads the preparation method of Fructus Cannabis stalk activated carbon.The preparation method Simple process, inexpensive, it is easy to control, and activated carbon is combined as carrier with the catalytic degradation performance of magnesium oxide, greatly improve suction The efficiency of attached degradation of contaminant.
The technical solution adopted in the present invention is:A kind of MgO loads the preparation method of Fructus Cannabis stalk activated carbon, and which comprises the following steps that:
(1) Fructus Cannabis stalk is cut into the billet of 5~8cm length, carries out charing process in retort being placed on after being dried.Carbonization temperature is 500 DEG C, Carbonization time is 2 hours.
(2) using pulverizer by the raw material pulverizing after carbonization into can cross 80~100 mesh sieve carbon powder.Again with potassium hydroxide as activator, will Fructus Cannabis stalk powdered carbon impregnates 24h post-dryings in potassium hydroxide solution.
(3) sample after drying is placed in chamber type electric resistance furnace carries out activation processing, and activation temperature is 800 DEG C, and soak time is 2h.Activate it Afterwards sample is taken out and is washed to neutral post-drying, that is, Fructus Cannabis stalk activated carbon is obtained
(4) the Fructus Cannabis stalk active carbon powder of a certain amount of 80~100 mesh is placed in certain density magnesium nitrate solution and sodium hydroxide solution and is mixed Uniformly.
(5) sample after mix homogeneously is put in ultrasonic washing unit carries out ultrasonic wave concussion.After concussion again deionized water clean repeatedly with Remove impurity
(6) sample after cleaning up is put in drying baker and is dried after 30min, place into calcining in chamber type electric resistance furnace, that is, obtain MgO loads Fructus Cannabis stalk activated carbon.
In step 2, the mass ratio of potassium hydroxide and carbonized stock powder is 1~4: 1, and the concentration of potassium hydroxide solution is 50%.
In step 4, the concentration of magnesium nitrate solution is 0.2~0.6mol/L, and the concentration of sodium hydroxide solution is 0.2~0.6mol/L.
In steps of 5, the response time of ultrasonic wave concussion is 20~60min, and reaction temperature is 40~80 DEG C.
In step 6, calcining heat is 500 DEG C, and calcination time is 2h.
Compared with prior art, the present invention has advantages below and effect:
1st, with Fructus Cannabis stalk as raw material, the nano magnesia that loaded containing flourishing microcellular structure and bigger serface is prepared for by KOH activation methods Fructus Cannabis stalk activated carbon, it is achieved thereby that the absorption degradation and the improvement and protection to environment to toxic gas and sewage.
2nd, activated carbon is combined as carrier with the catalytic degradation performance of magnesium oxide.On the one hand waste water and dyestuff etc. are had using activated carbon On the other hand pollutant are thoroughly degraded by good absorption property using magnesium oxide, greatly improve the efficiency of absorption degradation pollutant.
3rd, the preparation method flow process is simple, and simple process, inexpensive, it is easy to control have good development prospect and further deeply expand The value of research.
Specific embodiment
With reference to example is embodied as, the present invention is described in detail:
Embodiment 1
(1) Fructus Cannabis stalk is cut into the billet of 5~8cm length, carries out charing process in retort being placed on after being dried.Carbonization temperature is 500 DEG C, Carbonization time is 2 hours.
(2) using pulverizer by the raw material pulverizing after carbonization into can cross 100 mesh sieve carbon powder.(the potassium hydroxide with potassium hydroxide as activator again Mass ratio with carbonized stock powder is 4: 1, and the concentration of potassium hydroxide solution is 50%), Fructus Cannabis stalk powdered carbon to be impregnated in potassium hydroxide solution 24h Post-drying.
(3) sample after drying is placed in chamber type electric resistance furnace carries out activation processing, and activation temperature is 800 DEG C, and soak time is 2h.Activate it Afterwards sample is taken out and is washed to neutral post-drying, that is, Fructus Cannabis stalk activated carbon is obtained
(4) the Fructus Cannabis stalk active carbon powder of a certain amount of 100 mesh is placed in into certain density magnesium nitrate solution (concentration of magnesium nitrate solution is 0.2mol/L) With in sodium hydroxide solution (concentration of sodium hydroxide solution be 0.4mol/L) and mix homogeneously.
(5) sample after mix homogeneously is put in ultrasonic washing unit carries out ultrasonic wave concussion.The response time of ultrasonic wave concussion is 20min, instead Temperature is answered to be 60 DEG C.After concussion, deionized water cleans to remove impurity repeatedly again
(6) sample after cleaning up is put in drying baker and is dried after 30min, place into calcining in chamber type electric resistance furnace, calcining heat is 500 DEG C, Calcination time is 2h.The Fructus Cannabis stalk activated carbon of MgO loads is obtained.
The Fructus Cannabis stalk activated carbon specific surface area for measuring obtained MgO loads is 1589.27m2/ g, micropore specific area are 1420.52m2/ g, micropore hole Volume is 0.751cm3/ g, average particle diameter size are 40nm, for the degradation rate of methyl orange and paraoxon is respectively 90.32% and 94.34%.
Embodiment 2
(1) Fructus Cannabis stalk is cut into the billet of 5~8cm length, carries out charing process in retort being placed on after being dried.Carbonization temperature is 500 DEG C, Carbonization time is 2 hours.
(2) using pulverizer by the raw material pulverizing after carbonization into can cross 80 mesh sieve carbon powder.Again with potassium hydroxide as activator (potassium hydroxide and The mass ratio of carbonized stock powder is 3: 1, and the concentration of potassium hydroxide solution is 50%), Fructus Cannabis stalk powdered carbon to be impregnated after 24h in potassium hydroxide solution Drying.
(3) sample after drying is placed in chamber type electric resistance furnace carries out activation processing, and activation temperature is 800 DEG C, and soak time is 2h.Activate it Afterwards sample is taken out and is washed to neutral post-drying, that is, Fructus Cannabis stalk activated carbon is obtained
(4) the Fructus Cannabis stalk active carbon powder of a certain amount of 80 mesh is placed in into certain density magnesium nitrate solution (concentration of magnesium nitrate solution is 0.4mol/L) With in sodium hydroxide solution (concentration of sodium hydroxide solution be 0.6mol/L) and mix homogeneously.
(5) sample after mix homogeneously is put in ultrasonic washing unit carries out ultrasonic wave concussion.The response time of ultrasonic wave concussion is 40min, instead Temperature is answered to be 60 DEG C.After concussion, deionized water cleans to remove impurity repeatedly again
(6) sample after cleaning up is put in drying baker and is dried after 30min, place into calcining in chamber type electric resistance furnace, calcining heat is 500 DEG C, Calcination time is 2h.The Fructus Cannabis stalk activated carbon of MgO loads is obtained.
The Fructus Cannabis stalk activated carbon specific surface area for measuring obtained MgO loads is 1275.08m2/ g, micropore specific area are 1188.75m2/ g, micropore hole Volume is 0.630cm3/ g, average particle diameter size are 50nm, for the degradation rate of methyl orange and paraoxon is respectively 88.65% and 91.23%.

Claims (4)

1. a kind of MgO loads the preparation method of Fructus Cannabis stalk activated carbon, it is characterised in that including following several steps:
(1) Fructus Cannabis stalk being cut into the billet of 5~8cm length, charing process being carried out in retort being placed on after being dried, carbonization temperature is 500 DEG C, Carbonization time is 2 hours;
(2) using pulverizer by the raw material pulverizing after carbonization into the carbon powder that can cross 80~100 mesh sieve, the then (hydrogen with potassium hydroxide as activator The mass ratio of potassium oxide and carbonized stock powder is 1~4: 1, and the concentration of potassium hydroxide solution is 50%), by Fructus Cannabis stalk powdered carbon in potassium hydroxide solution Dipping 24h post-dryings;
(3) sample after drying is placed in chamber type electric resistance furnace carries out activation processing, and activation temperature is 800 DEG C, and soak time is 2h, activates it Afterwards sample is taken out and is washed to neutral post-drying, that is, Fructus Cannabis stalk activated carbon is obtained;
(4) the Fructus Cannabis stalk active carbon powder of a certain amount of 80~100 mesh is placed in certain density magnesium nitrate solution and sodium hydroxide solution and is mixed Uniformly;
(5) sample after mix homogeneously is put in ultrasonic washing unit carries out ultrasonic wave concussion, after concussion again deionized water clean repeatedly with Remove impurity;
(6) sample after cleaning up is put in drying baker and is dried after 30min, place into calcining in chamber type electric resistance furnace, that is, obtain MgO loads Fructus Cannabis stalk activated carbon.
2. a kind of MgO according to claim 1 loads the preparation method of Fructus Cannabis stalk activated carbon, it is characterised in that in the step (4), The concentration of magnesium nitrate solution is 0.2~0.6mol/L, and the concentration of sodium hydroxide solution is 0.2~0.6mol/L.
3. a kind of MgO according to claim 1 loads the preparation method of Fructus Cannabis stalk activated carbon, it is characterised in that in the step (5), The response time of ultrasonic wave concussion is 20~60min, and reaction temperature is 40~80 DEG C.
4. a kind of MgO according to claim 1 loads the preparation method of Fructus Cannabis stalk activated carbon, it is characterised in that in the step (6), Calcining heat is 500 DEG C, and calcination time is 2h.
CN201510680420.3A 2015-10-20 2015-10-20 Preparation method for MgO loaded china-hemp stalk activated carbon Pending CN106607007A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201510680420.3A CN106607007A (en) 2015-10-20 2015-10-20 Preparation method for MgO loaded china-hemp stalk activated carbon

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201510680420.3A CN106607007A (en) 2015-10-20 2015-10-20 Preparation method for MgO loaded china-hemp stalk activated carbon

Publications (1)

Publication Number Publication Date
CN106607007A true CN106607007A (en) 2017-05-03

Family

ID=58610183

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201510680420.3A Pending CN106607007A (en) 2015-10-20 2015-10-20 Preparation method for MgO loaded china-hemp stalk activated carbon

Country Status (1)

Country Link
CN (1) CN106607007A (en)

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107416828A (en) * 2017-08-31 2017-12-01 贺守印 A kind of preparation method of magnesium oxide-based activated carbon
CN109534339A (en) * 2018-11-21 2019-03-29 常熟理工学院 It is a kind of pine squama matrix activated carbon and its nanocomposite preparation method
CN110652961A (en) * 2019-10-08 2020-01-07 安徽建筑大学 Preparation method of magnesium oxide porous nano material loaded activated carbon fiber felt
CN111495322A (en) * 2020-04-28 2020-08-07 海南省农业科学院农产品加工设计研究所 Rambutan peel modified charcoal and preparation method and application thereof
CN111939872A (en) * 2020-08-12 2020-11-17 华南农业大学 Preparation method and application of activated hemp carbon adsorbent
CN112456521A (en) * 2020-11-07 2021-03-09 宝鸡文理学院 Method for preparing porous nano magnesium oxide by using corn straw template method and application thereof
CN112755961A (en) * 2020-12-31 2021-05-07 中国科学院城市环境研究所 MgO-loaded activated carbon and preparation method and application thereof
CN113209937A (en) * 2018-09-14 2021-08-06 蚌埠越昇科技服务有限公司 Method for preparing nano metal oxide loaded active carbon and application thereof
CN113578267A (en) * 2021-08-05 2021-11-02 福州大学 Polycrystalline nano-magnesia charcoal adsorbent for enriching uranium in nuclear wastewater
CN113697832A (en) * 2021-09-16 2021-11-26 安徽建筑大学 Preparation method of basic magnesium carbonate nanosheet loaded activated carbon sponge

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103979537A (en) * 2014-06-11 2014-08-13 福建省鑫森炭业股份有限公司 Hemp-stalk activated charcoal and preparation method thereof
CN104692379A (en) * 2014-12-24 2015-06-10 无限极(中国)有限公司 Hemp-stem active carbon and preparation method, forming method and application thereof

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103979537A (en) * 2014-06-11 2014-08-13 福建省鑫森炭业股份有限公司 Hemp-stalk activated charcoal and preparation method thereof
CN104692379A (en) * 2014-12-24 2015-06-10 无限极(中国)有限公司 Hemp-stem active carbon and preparation method, forming method and application thereof

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
孙金菊等: "KOH 活化法制备汉麻秆活性炭及其微孔结构的研究", 《功能材料》 *
董静等: "改性棕榈纤维活性炭对活性染料的吸附性能", 《纺织学报》 *

Cited By (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107416828A (en) * 2017-08-31 2017-12-01 贺守印 A kind of preparation method of magnesium oxide-based activated carbon
CN113209937A (en) * 2018-09-14 2021-08-06 蚌埠越昇科技服务有限公司 Method for preparing nano metal oxide loaded active carbon and application thereof
CN113209937B (en) * 2018-09-14 2022-11-18 乐山中科正光农林科技有限公司 Method for preparing nano metal oxide loaded active carbon and application thereof
CN109534339A (en) * 2018-11-21 2019-03-29 常熟理工学院 It is a kind of pine squama matrix activated carbon and its nanocomposite preparation method
CN110652961A (en) * 2019-10-08 2020-01-07 安徽建筑大学 Preparation method of magnesium oxide porous nano material loaded activated carbon fiber felt
CN111495322A (en) * 2020-04-28 2020-08-07 海南省农业科学院农产品加工设计研究所 Rambutan peel modified charcoal and preparation method and application thereof
CN111939872B (en) * 2020-08-12 2021-11-02 华南农业大学 Preparation method and application of activated hemp carbon adsorbent
CN111939872A (en) * 2020-08-12 2020-11-17 华南农业大学 Preparation method and application of activated hemp carbon adsorbent
CN112456521A (en) * 2020-11-07 2021-03-09 宝鸡文理学院 Method for preparing porous nano magnesium oxide by using corn straw template method and application thereof
CN112755961A (en) * 2020-12-31 2021-05-07 中国科学院城市环境研究所 MgO-loaded activated carbon and preparation method and application thereof
CN112755961B (en) * 2020-12-31 2023-12-01 中国科学院城市环境研究所 MgO-loaded activated carbon and preparation method and application thereof
CN113578267A (en) * 2021-08-05 2021-11-02 福州大学 Polycrystalline nano-magnesia charcoal adsorbent for enriching uranium in nuclear wastewater
CN113697832A (en) * 2021-09-16 2021-11-26 安徽建筑大学 Preparation method of basic magnesium carbonate nanosheet loaded activated carbon sponge
CN113697832B (en) * 2021-09-16 2023-07-14 安徽建筑大学 Preparation method of basic magnesium carbonate nanosheet-loaded activated carbon sponge

Similar Documents

Publication Publication Date Title
CN106607007A (en) Preparation method for MgO loaded china-hemp stalk activated carbon
CN109019597B (en) Preparation method and application of cellulose/graphene oxide carbon aerogel
CN104289179B (en) Method for preparing attapulgite/carbon composite adsorbent by one-step carbonization-activation
CN105056882A (en) Preparation method of modified charcoal-based adsorbent for removing hydrogen sulfide
CN103480330B (en) Biomass-modified adsorbent for adsorbing coking wastewater, and preparation method and application thereof
CN104289188B (en) A kind of preparation of the modified Pericarpium Musae adsorbent of pyromellitic acid anhydride
CN109225132B (en) Biochar-based silicon-loaded adsorbent and preparation method and application thereof
CN112121766B (en) Ramie fiber-based biochar and preparation method and application thereof
CN104084126B (en) The preparation method of biomass-based iron aluminium complex spherical charcoal
CN110935280B (en) Nitrogen-doped mesoporous bamboo-based biochar and application thereof
CN103193228B (en) Efficient adsorption CO 2the preparation method of melon-seed hull matrix activated carbon
CN102220665B (en) Method for preparing activated carbon fibers with high specific surface by use of cotton linters
CN107867688A (en) A kind of preparation method for the shaddock peel activated carbon for being used for purification of air and sewage disposal
CN103480336B (en) A kind of modified biomass activates burnt demercuration adsorbent and preparation method thereof
CN104326471A (en) Method for preparing active carbon from licorice waste residue
CN109569519A (en) The method for preparing active sludge carbon base formaldehyde adsorbent using municipal sludge
CN108940192A (en) A kind of wooden biological carbon materials and preparation method thereof adsorbing heavy metal
CN112938969A (en) Method for preparing nitrogen-sulfur co-doped activated carbon by pore-forming/doping integrated activating agent and application of method
CN104001371A (en) Method for recycling waste dust removal filter material
CN112705166A (en) Preparation method and application of ammonia water modified eucalyptus activated carbon adsorbent
CN106904610B (en) A method of terylene textile waste matrix activated carbon is prepared using bittern solution for template-chemical activating agent
CN101912767B (en) Method for preparing modified furfural residue heavy metal adsorbent
CN102423693B (en) Preparation and application methods of sulfur dioxide rice straw adsorbent
CN109364875A (en) A kind of preparation method and application of modified coal ash-carbon composite
CN103301811A (en) preparation method of biomass charcoal adsorbent and method for treating oily wastewater by biomass charcoal adsorbent

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
WD01 Invention patent application deemed withdrawn after publication
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20170503