CN102974320B - A kind of preparation method of organically-modified attapulgite adsorbent - Google Patents

A kind of preparation method of organically-modified attapulgite adsorbent Download PDF

Info

Publication number
CN102974320B
CN102974320B CN201210550251.8A CN201210550251A CN102974320B CN 102974320 B CN102974320 B CN 102974320B CN 201210550251 A CN201210550251 A CN 201210550251A CN 102974320 B CN102974320 B CN 102974320B
Authority
CN
China
Prior art keywords
attapulgite
organically
modified
mixed liquor
adsorbent
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.)
Active
Application number
CN201210550251.8A
Other languages
Chinese (zh)
Other versions
CN102974320A (en
Inventor
吴雪平
徐艳青
高鹏
张先龙
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 CN201210550251.8A priority Critical patent/CN102974320B/en
Publication of CN102974320A publication Critical patent/CN102974320A/en
Application granted granted Critical
Publication of CN102974320B publication Critical patent/CN102974320B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Abstract

The invention discloses a kind of preparation method of organically-modified attapulgite adsorbent, for raw material with the natural attapulgite clay of cheapness and biomass cellulose carbon source, prepare attapulgite/carbon nanometer composite material by heterogeneous hydrothermal synthesis method, make the load of attapulgite plane of crystal have close organic trait containing-CH functional group amorphous carbon.Compared with natural, unmodified Concave-convex clay rod, modified attapulgite adsorbent can improve more than 3-5 times to the removal efficiency of organic pollutants phenol, is 97-99%, greatly shortens methylene blue adsorption number equilibration time water Methylene Blue removal efficiency.The organically-modified mild condition of the attapulgite that the present invention relates to, raw material sources are extensively cheap, and technical process is simple, gained modified attapulgite surface graft organo-functional group, the adsorption capacity of organic pollutants is significantly improved, can be used for the advanced treating of organic pollutants.

Description

A kind of preparation method of organically-modified attapulgite adsorbent
One, technical field
The present invention relates to a kind of organically-modified method of attapulgite adsorbent, to improve attapulgite as the adsorption capacity of adsorbent to organic pollution, be applied to micro quantity organic pollutant in water body and remove.
Two, background technology
Attapulgite is a kind of cheapness and the zeopan clay mineral with chain layer structure of rich reserves, its monocrystal diameter is 30-50nm, having huge specific area, show nano effect, adsorption activity and chemism, is a kind of natural nano-mineral material of excellent performance.The water of 3 types is there is: constitution water, the crystallization water and zeolite water in attapulgite.The crystallization water in attapulgite structure is positioned at its channel surfaces, and it easily forms hydrogen bond with the adsorbate entering duct and is connected.Thus, when using as adsorbent, attapulgite is more weak to organic absorption.The traditional close Organic method of modifying of attapulgite utilizes the modification in addition such as surfactant (as cetyl ammonium bromide, bromide sixteen alkyls pyridine etc.), coupling agent (as silane coupler and titanate coupling agent), high-temperature calcination organic matter and acid treatment.But surfactant, coupling agent and high temperature method modification also exist that method of modifying is loaded down with trivial details, cost is high and the shortcoming such as large that consumes energy.
Three, summary of the invention
The present invention aims to provide a kind of preparation method of organically-modified attapulgite adsorbent, and technical problem to be solved is that the close Organic by improving attapulgite improves its adsorption capacity to organic pollution.
Cellulose is a kind of polysaccharide that occurring in nature distribution is the widest, content is maximum, accounts for more than 50% of plant kingdom's carbon content.According to the literature, in the hydro-thermal reaction of temperature lower than 250 DEG C, cellulose first can be hydrolyzed and become oligosaccharide and monosaccharide, these materials rupture and generate the compound such as HMF and organic acid, the carbonization of these Small molecular polymerization afterwards generates the particulate carbon ball of nucleocapsid structure, is rich in the organic groups such as-OH ,-C=O ,-COOH.Because Hydrothermal Synthesis possesses reaction condition gentleness (less than 300 DEG C), energy consumption is low, and reaction time is short and experimental facilities simple, and the advantages such as growth characteristics is controlled, are described as " green reaction " usually.Owing to being low temperature synthesis, the carbon material surface of acquisition is generally all containing enriching organo-functional group.Therefore this cheapness of cellulose widely living beings can be used as hydro-thermal reaction and prepare the carbon source of composite.
Attapulgite has natural nanostructured, and about tens nanometers of diameter of single fiber crystalline substance, length can reach 1 μm.Utilize the natural hard template effect of attapulgite, the living beings carbon source cellulose adopting simple green one step hydro thermal method induction cheap is at attapulgite surface carbonation, thus obtain organically-modified attapulgite adsorbent, grafting organo-functional group, improve the close Organic of attapulgite, improve its adsorption capacity to organic pollution.
The present invention with Concave-convex clay rod and living beings carbon source cellulose for raw material, organically-modified attapulgite adsorbent is prepared by heterogeneous hydrothermal synthesis method, the amorphous carbon that the organically-modified attapulgite adsorbent of the present invention contains-CH functional group by attapulgite and plane of crystal load thereof forms, therefore also known as attapulgite/carbon nanometer composite material.
The preparation method of the organically-modified attapulgite adsorbent of the present invention, adopts the method for heterogeneous Hydrothermal Synthesis, it is characterized in that:
The Concave-convex clay rod raw ore of attapulgite content >=98wt% is pulverized and crosses 200 mesh sieves (d=74 μm) and obtain attapulgite powder; By the ratio mixing of cellulose and described attapulgite powder 2-4:1 in mass ratio, add catalyst, ultrasonic or the dispersed with stirring of adding water again is even, is warming up to 210-250 DEG C of reaction 12-48 hour, then through cooling, washing, dry and obtain organically-modified concave and convex rod stone powder after pulverizing; During hydro-thermal reaction, reactor volumetric filling ratio remains on 70-80%.
Described catalyst is six ferrous sulfate hydrate ammoniums, and the addition of catalyst is with Fe 2+count the 3-10% of cellulose and attapulgite powder gross mass, more preferably 5-7%, effectively can improve the carbonization degree of carbon source, promote the growth on attapulgite surface of charcoal particle and dispersion.
Organically-modified for the present invention attapulgite adsorbent is used for the adsorption treatment of Organic Pollutants In Water:
Carry out adsorption treatment using phenol as organic pollution, the concentration of phenol solution is 5mg/L, and the addition of the organically-modified attapulgite adsorbent of the present invention and the solid-to-liquid ratio of phenol solution are 1g:50mL, and at 25 DEG C, constant temperature oscillation absorption 12h, measures adsorbing and removing rate;
Adsorption treatment is carried out using methylene blue as organic pollution, the concentration of methylene blue solution is 5mg/L, the addition of the organically-modified attapulgite adsorbent of the present invention and the solid-to-liquid ratio of methylene blue solution are 1g:1600-2500mL, and at 25 DEG C, constant temperature oscillation absorption 4-12h, measures adsorbing and removing rate.
Compared with the prior art, beneficial effect of the present invention is embodied in:
1, the present invention adopts the method for Hydrothermal Synthesis, and attapulgite remains original pattern and crystal structure, and its plane of crystal has inductive effect, and after biomass cellulose hydro-thermal is carbonized, charcoal is in its superficial growth, obtains attapulgite/carbon nanometer composite material.Compared with preparing modified attapulgite method with 500 DEG C of-1000 DEG C of high-temperature calcinations of routine, the inventive method hydrothermal condition temperature is lower than 250 DEG C, and without the need to atmosphere protection, without the need to adding any surfactant, be a kind of organically-modified method of attapulgite of environmental protection; Compared with preparing modified attapulgite with the surfactant method of routine, the inventive method is raw materials used to be easy to get, cheap, modification route is simple, and energy consumption is little.
2, after the present invention carries Organic carbon by hydro-thermal method, the close Organic of attapulgite is improved, and the absorption property for Typical Organic Pollutants increases substantially.
Four, accompanying drawing explanation
Fig. 1 is cellulose and Concave-convex clay rod mass ratio is 2:1, and the addition of catalyst is with Fe 2+count 5wt%, reaction temperature 240 DEG C, the SEM photo of the organically-modified attapulgite that the reaction time obtains for 12h.As can be seen from Figure 1, nano carbon particle (50nm) is carried on attapulgite cluster surface.
Fig. 2 is cellulose and Concave-convex clay rod mass ratio is 4:1, and the addition of catalyst is with Fe 2+count 3.4wt%, reaction temperature 250 DEG C, the IR figure of the organically-modified attapulgite that the reaction time obtains for 48h.As can be seen from Figure 2,2930cm -1and 2851cm -1having there is the C-H vibration absorption peak of saturated hydrocarbons in place, illustrates that cellulosic molecule is surperficial containing creating abundant organo-functional group at attapulgite after hydro-thermal reaction, thus make prepared attapulgite/carbon composite material possess an engagement Organic.
Fig. 3 be under different temperatures (220-250 DEG C) obtain organically-modified attapulgite and unmodified attapulgite Pyrogentisinic Acid absorption property contrast (hydro-thermal time: 12h).As can be seen from Figure 3, after Organic carbon modification is carried on attapulgite surface, the adsorbing and removing ability of Pyrogentisinic Acid improves greatly.Compared to unmodified attapulgite raw ore, the removal efficiency of modified attapulgite Pyrogentisinic Acid can improve 3-5 times more than.
Fig. 4 cellulose and Concave-convex clay rod mass ratio are 2:1, and the addition of catalyst is with Fe 2+count 5wt%, reaction temperature 220 DEG C, the reaction time obtains by 48h organically-modified attapulgite and unmodified attapulgite to the adsorption equilibrium curve comparison (solid-to-liquid ratio 1:2500, adsorption time 4h, hunting speed 200r/min) of methylene blue.As can be seen from Figure 4, unmodified attapulgite raw ore is 6 hours to the time of equilibrium adsorption of methylene blue, and the attapulgite carrying Organic carbon modification is 2 hours to the time of equilibrium adsorption of methylenum careuleum.Carry charcoal parent organically-modified after, the time of equilibrium adsorption of attapulgite to methylene blue shortens 3 times.
Five, specific implementation method
Embodiment 1:
The Concave-convex clay rod raw ore of attapulgite content >=98wt% is pulverized and crossed 200 mesh sieves and obtains attapulgite powder, get 2.5g attapulgite powder and 5g cellulose, mix in 72ml distilled water, add iron ammonium sulfate 2.8g again, ultrasonic disperse is even obtains mixed liquor, and now the pH value of mixed liquor is 5;
Be transferred in polytetrafluoroethylene (PTFE) water heating kettle by described mixed liquor, filling rate remains on 75%, reaction temperature 250 DEG C, carbonizes 12 hours; Naturally cool to room temperature after reaction terminates, centrifugation obtains black product 60 DEG C of oven dry after also alternately washing with water and ethanol and is organically-modified attapulgite.
SEM and infrared spectrum analysis known, attapulgite area load contains the nano-sized carbon of the organo-functional groups such as C-H.
To get initial concentration be 5mg/L phenol solution is organic pollution, organically-modified attapulgite adsorbent is added in phenol solution, solid-to-liquid ratio is 1g:50mL, and with 200r/min rotating speed constant temperature oscillation absorption 12h at 25 DEG C, Adsorption of Phenol removal efficiency is that 70%(is shown in Fig. 3).
Embodiment 2:
The Concave-convex clay rod raw ore of attapulgite content >=98wt% is pulverized and crossed 200 mesh sieves and obtains attapulgite powder, get 2.5g attapulgite powder and 5g cellulose, mix in 72ml distilled water, add iron ammonium sulfate 2.8g again, ultrasonic disperse is even obtains mixed liquor, and now the pH value of mixed liquor is 5;
Be transferred in polytetrafluoroethylene (PTFE) water heating kettle by described mixed liquor, filling rate remains on 80%, reaction temperature 240 DEG C, carbonizes 12 hours; Naturally cool to room temperature after reaction terminates, centrifugation obtains black product 60 DEG C of oven dry after also alternately washing with water and ethanol and is organically-modified attapulgite.
Infrared analysis is known, and organically-modified attapulgite contains the organo-functional groups such as C-H; Sem analysis to show on attapulgite load amorphous carbon (see figure 1).
To get initial concentration be 5mg/L phenol solution is organic pollution, organically-modified attapulgite adsorbent is added in phenol solution, solid-to-liquid ratio is 1g:50mL, and with 200r/min rotating speed constant temperature oscillation absorption 12h at 25 DEG C, Adsorption of Phenol removal efficiency is that 66%(is shown in Fig. 3).
Embodiment 3:
The Concave-convex clay rod raw ore of attapulgite content >=98wt% is pulverized and crossed 200 mesh sieves and obtains attapulgite powder, get 2.5g attapulgite powder and 10g cellulose, mix in 72ml distilled water, add iron ammonium sulfate 3.0g again, ultrasonic disperse is even obtains mixed liquor, and now the pH value of mixed liquor is 5;
Be transferred in polytetrafluoroethylene (PTFE) water heating kettle by described mixed liquor, filling rate remains on 80%, reaction temperature 250 DEG C, carbonizes 48 hours; Naturally cool to room temperature after reaction terminates, centrifugation obtains black product 60 DEG C of oven dry after also alternately washing with water and ethanol and is organically-modified attapulgite.
Infrared analysis is known, and organically-modified attapulgite contains the organo-functional groups such as C-H.SEM characterizes and finds load amorphous carbon on attapulgite.
To get initial concentration be 5mg/L phenol solution is organic pollution, and in phenol solution, add organically-modified attapulgite adsorbent, solid-to-liquid ratio is 1g:50mL, and with 200r/min rotating speed constant temperature oscillation absorption 12h at 25 DEG C, Adsorption of Phenol removal efficiency is 92%.
Embodiment 4:
The Concave-convex clay rod raw ore of attapulgite content >=98wt% is pulverized and crossed 200 mesh sieves and obtains attapulgite powder, get 2.5g attapulgite powder and 8g cellulose, mix in 72ml distilled water, add iron ammonium sulfate 5.8g again, ultrasonic disperse is even obtains mixed liquor, and now the pH value of mixed liquor is 5;
Be transferred in polytetrafluoroethylene (PTFE) water heating kettle by described mixed liquor, filling rate remains on 70%, reaction temperature 210 DEG C, carbonizes 24 hours; Naturally cool to room temperature after reaction terminates, centrifugation obtains black product 60 DEG C of oven dry after also alternately washing with water and ethanol and is organically-modified attapulgite.
SEM and infrared spectrum analysis known, attapulgite area load contains the nano-sized carbon of the organo-functional groups such as C-H.
To get initial concentration be 5mg/L phenol solution is organic pollution, and in phenol solution, add organically-modified attapulgite adsorbent, solid-to-liquid ratio is 1g:50mL, and with 200r/min rotating speed constant temperature oscillation absorption 12h at 25 DEG C, Adsorption of Phenol removal efficiency is 60%.
Embodiment 5:
The Concave-convex clay rod raw ore of attapulgite content >=98wt% is pulverized and crossed 200 mesh sieves and obtains attapulgite powder, get 2.5g attapulgite powder and 5g cellulose, mix in 72ml distilled water, add iron ammonium sulfate 2.8g again, ultrasonic disperse is even obtains mixed liquor, and now the pH value of mixed liquor is 5;
Be transferred in polytetrafluoroethylene (PTFE) water heating kettle by described mixed liquor, filling rate remains on 80%, reaction temperature 220 DEG C, carbonizes 24 hours; Naturally cool to room temperature after reaction terminates, centrifugation obtains black product 60 DEG C of oven dry after also alternately washing with water and ethanol and is organically-modified attapulgite.
To get initial concentration be 5mg/L methylene blue solution is organic pollution, organically-modified attapulgite adsorbent is added in methylene blue solution, solid-to-liquid ratio is 1g:2500mL, and with 200r/min rotating speed constant temperature oscillation absorption 6h at 25 DEG C, methylene blue adsorption number removal efficiency is that 97%(is shown in Fig. 4).
Embodiment 6:
The Concave-convex clay rod raw ore of attapulgite content >=98wt% is pulverized and crossed 200 mesh sieves and obtains attapulgite powder, get 2.5g attapulgite powder and 5g cellulose, mix in 72ml distilled water, add iron ammonium sulfate 2.8g again, ultrasonic disperse is even obtains mixed liquor, and now the pH value of mixed liquor is 5;
Be transferred in polytetrafluoroethylene (PTFE) water heating kettle by described mixed liquor, filling rate remains on 80%, reaction temperature 220 DEG C, carbonizes 48 hours; Naturally cool to room temperature after reaction terminates, centrifugation obtains black product 60 DEG C of oven dry after also alternately washing with water and ethanol and is organically-modified attapulgite.
To get initial concentration be 5mg/L methylene blue solution is organic pollution, organically-modified attapulgite adsorbent is added in methylene blue solution, solid-to-liquid ratio is 1g:1600mL, and with 200r/min rotating speed constant temperature oscillation absorption 4h at 25 DEG C, methylene blue adsorption number removal efficiency is 99%.
Embodiment 7: contrast test
To get initial concentration be 5mg/L phenol solution is target contaminant, and attapulgite raw ore and phenol solution solid-to-liquid ratio are 1g:50mL, with 200r/min rotating speed constant temperature oscillation absorption 12h at 25 DEG C.Adsorption of Phenol removal efficiency is 18%.
Embodiment 8: contrast test
To get initial concentration be 5mg/L methylene blue solution is target contaminant, and attapulgite raw ore and methylene blue solution solid-to-liquid ratio are 1g:2500mL, with 200r/min rotating speed constant temperature oscillation absorption 6h at 25 DEG C.Methylene blue adsorption number removal efficiency is 94%.(see Fig. 4).

Claims (2)

1. a preparation method for organically-modified attapulgite adsorbent, adopts the method for heterogeneous Hydrothermal Synthesis, it is characterized in that:
The Concave-convex clay rod raw ore of attapulgite content 98wt% is pulverized and crossed 200 mesh sieves and obtains attapulgite powder, get 2.5g attapulgite powder and 10g cellulose, mix in 72ml distilled water, add iron ammonium sulfate 3.0g again, ultrasonic disperse is even obtains mixed liquor, and now the pH value of mixed liquor is 5;
Be transferred in polytetrafluoroethylene (PTFE) water heating kettle by described mixed liquor, filling rate remains on 80%, reaction temperature 250 DEG C, carbonizes 48 hours; Naturally cool to room temperature after reaction terminates, centrifugation obtains black product 60 DEG C of oven dry after also alternately washing with water and ethanol and is organically-modified attapulgite.
2. a preparation method for organically-modified attapulgite adsorbent, adopts the method for heterogeneous Hydrothermal Synthesis, it is characterized in that:
The Concave-convex clay rod raw ore of attapulgite content 98wt% is pulverized and crossed 200 mesh sieves and obtains attapulgite powder, get 2.5g attapulgite powder and 5g cellulose, mix in 72ml distilled water, add iron ammonium sulfate 2.8g again, ultrasonic disperse is even obtains mixed liquor, and now the pH value of mixed liquor is 5;
Be transferred in polytetrafluoroethylene (PTFE) water heating kettle by described mixed liquor, filling rate remains on 80%, reaction temperature 220 DEG C, carbonizes 48 hours; Naturally cool to room temperature after reaction terminates, centrifugation obtains black product 60 DEG C of oven dry after also alternately washing with water and ethanol and is organically-modified attapulgite.
CN201210550251.8A 2012-12-18 2012-12-18 A kind of preparation method of organically-modified attapulgite adsorbent Active CN102974320B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201210550251.8A CN102974320B (en) 2012-12-18 2012-12-18 A kind of preparation method of organically-modified attapulgite adsorbent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201210550251.8A CN102974320B (en) 2012-12-18 2012-12-18 A kind of preparation method of organically-modified attapulgite adsorbent

Publications (2)

Publication Number Publication Date
CN102974320A CN102974320A (en) 2013-03-20
CN102974320B true CN102974320B (en) 2015-09-16

Family

ID=47848837

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201210550251.8A Active CN102974320B (en) 2012-12-18 2012-12-18 A kind of preparation method of organically-modified attapulgite adsorbent

Country Status (1)

Country Link
CN (1) CN102974320B (en)

Families Citing this family (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103723824B (en) * 2013-12-26 2015-03-25 南京大学 Carbon-iron microbattery slow-release carbon source filler and preparation method thereof
CN104289179B (en) * 2014-09-24 2017-01-18 合肥工业大学 Method for preparing attapulgite/carbon composite adsorbent by one-step carbonization-activation
CN104289178B (en) * 2014-09-24 2016-08-31 合肥工业大学 The method preparing attapulgite/carbon adsorbent based on hydro-thermal-activation coupling technology
CN105396552B (en) * 2015-12-18 2018-08-03 中国科学技术大学 A kind of molding biological carbon and preparation method thereof
CN105669308A (en) * 2016-01-18 2016-06-15 李巍 Bioorganic fertilizer and method for improving soil by accurate application of bioorganic fertilizer
CN106311147A (en) * 2016-10-17 2017-01-11 中国矿业大学(北京) Illite loaded nanocarbon compound adsorbing material and preparation method thereof
CN106582555A (en) * 2016-12-13 2017-04-26 湖南大学 Preparation method and application of surface-organized montmorillonite/nano-manganese oxide composite material
CN109078611A (en) * 2018-09-16 2018-12-25 安徽乐农环保科技有限公司 Target heavy-metal adsorption material and preparation method thereof
CN113023851A (en) * 2021-03-24 2021-06-25 湖南久正环保科技有限公司 Medicament capable of removing activated carbon powder in wastewater
CN116459790B (en) * 2023-04-24 2024-03-29 西华师范大学 Preparation method of flying wadding fiber loaded zero-valent nano silver high-efficiency fixed gaseous iodine material

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101492165A (en) * 2009-03-09 2009-07-29 合肥工业大学 Organic modification method for attapulgite stone and uses of organic modified attapulgite stone

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101492165A (en) * 2009-03-09 2009-07-29 合肥工业大学 Organic modification method for attapulgite stone and uses of organic modified attapulgite stone

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
Catalytic deposition of nanocarbon onto palygorskite and its adsorption of phenol;Xueping Wu et al.,;《Applied Clay Science》;20110505(第52期);第401页的2.2节 *

Also Published As

Publication number Publication date
CN102974320A (en) 2013-03-20

Similar Documents

Publication Publication Date Title
CN102974320B (en) A kind of preparation method of organically-modified attapulgite adsorbent
CN103316639B (en) Preparation method of organic modified sepiolite adsorbent
CN104289179B (en) Method for preparing attapulgite/carbon composite adsorbent by one-step carbonization-activation
CN101492165A (en) Organic modification method for attapulgite stone and uses of organic modified attapulgite stone
CN103252214B (en) Active carbon fiber and graded porous Ni-Ni3P/active carbon fiber composite material as well as preparation and application of two
CN105329876B (en) A kind of preparation method of boron, nitrogen co-doped carbon quantum dot
Jiang et al. Platanus orientalis leaves based hierarchical porous carbon microspheres as high efficiency adsorbents for organic dyes removal
CN103881137A (en) Melamine flame retardant graft modified carbon nanotube and manufacturing method thereof
Qian et al. A delicate method for the synthesis of high-efficiency Hg (II) The adsorbents based on biochar from corn straw biogas residue
Qin et al. Removal of tetracycline onto KOH-activated biochar derived from rape straw: Affecting factors, mechanisms and reusability inspection
CN103146025A (en) Phosphazene fire retardant graft modification carbon nano tube and preparation method thereof
CN104289178B (en) The method preparing attapulgite/carbon adsorbent based on hydro-thermal-activation coupling technology
CN102626647A (en) Synthesizing method of playgouskite-loaded silver orthophosphate photochemical catalyst
Tu et al. Characterization and application of magnetic biochars from corn stalk by pyrolysis and hydrothermal treatment
CN113145134B (en) Visible light catalyst based on mineral composite material and preparation method thereof
Chen et al. Synthesis, characterization, and selective CO2 capture performance of a new type of activated carbon-geopolymer composite adsorbent
He et al. Liquefiable biomass-derived porous carbons and their applications in CO 2 capture and conversion
CN104607228A (en) Preparation method for alpha-Fe2O3 quantum dot/nitrogen-doped graphene composite material
Tang et al. Combination of graphene oxide with flax-derived cellulose dissolved in NaOH/urea medium to generate hierarchically structured composite carbon aerogels
Duan et al. Performance and characterization of bamboo-based activated carbon prepared by boric acid activation
CN108975328A (en) A kind of two steps method that carbonization prepares the biomass porous carbon material of nitrogen oxygen codope in advance
CN104437373A (en) Method for preparing nano flaky nitrogen-containing porous carbon material
CN111377446A (en) Preparation method of nitrogen and boron double-doped humic acid based porous carbon material with high thermal stability
CN106944001B (en) Preparation method of biological carbon adsorbent
Zeng et al. Sargassum horneri‐based carbon‐doped TiO2 and its aquatic naphthalene photodegradation under sunlight irradiation

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