CN111330560A - Preparation method of natural lignin-based photocatalytic material - Google Patents
Preparation method of natural lignin-based photocatalytic material Download PDFInfo
- Publication number
- CN111330560A CN111330560A CN202010272457.3A CN202010272457A CN111330560A CN 111330560 A CN111330560 A CN 111330560A CN 202010272457 A CN202010272457 A CN 202010272457A CN 111330560 A CN111330560 A CN 111330560A
- Authority
- CN
- China
- Prior art keywords
- lignin
- metal oxide
- natural
- photocatalytic
- nano
- 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.)
- Granted
Links
- 229920005610 lignin Polymers 0.000 title claims abstract description 78
- 239000000463 material Substances 0.000 title claims abstract description 41
- 230000001699 photocatalysis Effects 0.000 title claims abstract description 29
- 238000002360 preparation method Methods 0.000 title claims abstract description 16
- 229910044991 metal oxide Inorganic materials 0.000 claims abstract description 27
- 150000004706 metal oxides Chemical class 0.000 claims abstract description 20
- 239000011941 photocatalyst Substances 0.000 claims abstract description 20
- 230000003197 catalytic effect Effects 0.000 claims abstract description 16
- 238000000034 method Methods 0.000 claims abstract description 16
- 239000002131 composite material Substances 0.000 claims abstract description 15
- 239000003054 catalyst Substances 0.000 claims abstract description 11
- 239000012855 volatile organic compound Substances 0.000 claims abstract description 9
- 238000013033 photocatalytic degradation reaction Methods 0.000 claims abstract description 8
- 239000002351 wastewater Substances 0.000 claims abstract description 8
- 239000000203 mixture Substances 0.000 claims description 18
- 230000004048 modification Effects 0.000 claims description 17
- 238000012986 modification Methods 0.000 claims description 17
- 238000001035 drying Methods 0.000 claims description 15
- 238000002156 mixing Methods 0.000 claims description 11
- 238000000498 ball milling Methods 0.000 claims description 10
- 238000010438 heat treatment Methods 0.000 claims description 10
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 claims description 8
- 235000011089 carbon dioxide Nutrition 0.000 claims description 8
- 239000000178 monomer Substances 0.000 claims description 6
- 239000004065 semiconductor Substances 0.000 claims description 6
- 238000007334 copolymerization reaction Methods 0.000 claims description 5
- -1 metal oxide compound Chemical class 0.000 claims description 5
- 239000002105 nanoparticle Substances 0.000 claims description 3
- 230000008569 process Effects 0.000 claims description 3
- 150000001412 amines Chemical class 0.000 claims description 2
- BERDEBHAJNAUOM-UHFFFAOYSA-N copper(I) oxide Inorganic materials [Cu]O[Cu] BERDEBHAJNAUOM-UHFFFAOYSA-N 0.000 claims description 2
- KRFJLUBVMFXRPN-UHFFFAOYSA-N cuprous oxide Chemical compound [O-2].[Cu+].[Cu+] KRFJLUBVMFXRPN-UHFFFAOYSA-N 0.000 claims description 2
- SZVJSHCCFOBDDC-UHFFFAOYSA-N iron(II,III) oxide Inorganic materials O=[Fe]O[Fe]O[Fe]=O SZVJSHCCFOBDDC-UHFFFAOYSA-N 0.000 claims description 2
- JEIPFZHSYJVQDO-UHFFFAOYSA-N iron(III) oxide Inorganic materials O=[Fe]O[Fe]=O JEIPFZHSYJVQDO-UHFFFAOYSA-N 0.000 claims description 2
- 239000002245 particle Substances 0.000 abstract description 7
- 238000007146 photocatalysis Methods 0.000 abstract description 5
- 239000002957 persistent organic pollutant Substances 0.000 abstract description 4
- 230000015556 catabolic process Effects 0.000 abstract description 3
- 238000006731 degradation reaction Methods 0.000 abstract description 3
- 230000000694 effects Effects 0.000 abstract description 3
- QJGQUHMNIGDVPM-UHFFFAOYSA-N nitrogen group Chemical group [N] QJGQUHMNIGDVPM-UHFFFAOYSA-N 0.000 abstract description 3
- 238000009827 uniform distribution Methods 0.000 abstract description 2
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 description 36
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 16
- 239000004408 titanium dioxide Substances 0.000 description 12
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 10
- 239000003575 carbonaceous material Substances 0.000 description 9
- 239000000243 solution Substances 0.000 description 9
- 229910052799 carbon Inorganic materials 0.000 description 7
- 239000002114 nanocomposite Substances 0.000 description 7
- 238000003756 stirring Methods 0.000 description 7
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 6
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 5
- 239000003513 alkali Substances 0.000 description 5
- 238000005576 amination reaction Methods 0.000 description 5
- 229910021389 graphene Inorganic materials 0.000 description 5
- SOQBVABWOPYFQZ-UHFFFAOYSA-N oxygen(2-);titanium(4+) Chemical compound [O-2].[O-2].[Ti+4] SOQBVABWOPYFQZ-UHFFFAOYSA-N 0.000 description 5
- 239000010936 titanium Substances 0.000 description 5
- 238000013329 compounding Methods 0.000 description 4
- 238000002474 experimental method Methods 0.000 description 4
- 229920000642 polymer Polymers 0.000 description 4
- WSFSSNUMVMOOMR-UHFFFAOYSA-N Formaldehyde Chemical compound O=C WSFSSNUMVMOOMR-UHFFFAOYSA-N 0.000 description 3
- 229910010413 TiO 2 Inorganic materials 0.000 description 3
- 239000007864 aqueous solution Substances 0.000 description 3
- 239000002585 base Substances 0.000 description 3
- 150000001721 carbon Chemical class 0.000 description 3
- 230000000052 comparative effect Effects 0.000 description 3
- 235000013824 polyphenols Nutrition 0.000 description 3
- 239000002243 precursor Substances 0.000 description 3
- 239000000047 product Substances 0.000 description 3
- 238000010992 reflux Methods 0.000 description 3
- NWUYHJFMYQTDRP-UHFFFAOYSA-N 1,2-bis(ethenyl)benzene;1-ethenyl-2-ethylbenzene;styrene Chemical compound C=CC1=CC=CC=C1.CCC1=CC=CC=C1C=C.C=CC1=CC=CC=C1C=C NWUYHJFMYQTDRP-UHFFFAOYSA-N 0.000 description 2
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 2
- 239000002253 acid Substances 0.000 description 2
- 239000003957 anion exchange resin Substances 0.000 description 2
- 150000001450 anions Chemical class 0.000 description 2
- 239000006227 byproduct Substances 0.000 description 2
- 238000001354 calcination Methods 0.000 description 2
- 239000002041 carbon nanotube Substances 0.000 description 2
- 229910021393 carbon nanotube Inorganic materials 0.000 description 2
- 239000003729 cation exchange resin Substances 0.000 description 2
- 239000001913 cellulose Substances 0.000 description 2
- 229920002678 cellulose Polymers 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 238000009833 condensation Methods 0.000 description 2
- 230000005494 condensation Effects 0.000 description 2
- 238000001816 cooling Methods 0.000 description 2
- 239000012043 crude product Substances 0.000 description 2
- 230000007547 defect Effects 0.000 description 2
- 239000008367 deionised water Substances 0.000 description 2
- 229910021641 deionized water Inorganic materials 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 238000007590 electrostatic spraying Methods 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 238000003912 environmental pollution Methods 0.000 description 2
- 230000006870 function Effects 0.000 description 2
- 238000000227 grinding Methods 0.000 description 2
- 238000001027 hydrothermal synthesis Methods 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- WSFSSNUMVMOOMR-NJFSPNSNSA-N methanone Chemical compound O=[14CH2] WSFSSNUMVMOOMR-NJFSPNSNSA-N 0.000 description 2
- 229920005615 natural polymer Polymers 0.000 description 2
- ISWSIDIOOBJBQZ-UHFFFAOYSA-N phenol group Chemical group C1(=CC=CC=C1)O ISWSIDIOOBJBQZ-UHFFFAOYSA-N 0.000 description 2
- 239000000843 powder Substances 0.000 description 2
- 238000004537 pulping Methods 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 239000011347 resin Substances 0.000 description 2
- 229920005989 resin Polymers 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 238000005406 washing Methods 0.000 description 2
- 239000002699 waste material Substances 0.000 description 2
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 1
- XMWRBQBLMFGWIX-UHFFFAOYSA-N C60 fullerene Chemical compound C12=C3C(C4=C56)=C7C8=C5C5=C9C%10=C6C6=C4C1=C1C4=C6C6=C%10C%10=C9C9=C%11C5=C8C5=C8C7=C3C3=C7C2=C1C1=C2C4=C6C4=C%10C6=C9C9=C%11C5=C5C8=C3C3=C7C1=C1C2=C4C6=C2C9=C5C3=C12 XMWRBQBLMFGWIX-UHFFFAOYSA-N 0.000 description 1
- 229920000049 Carbon (fiber) Polymers 0.000 description 1
- PIICEJLVQHRZGT-UHFFFAOYSA-N Ethylenediamine Chemical compound NCCN PIICEJLVQHRZGT-UHFFFAOYSA-N 0.000 description 1
- 229920001732 Lignosulfonate Polymers 0.000 description 1
- 238000006683 Mannich reaction Methods 0.000 description 1
- 206010070834 Sensitisation Diseases 0.000 description 1
- DWAQJAXMDSEUJJ-UHFFFAOYSA-M Sodium bisulfite Chemical compound [Na+].OS([O-])=O DWAQJAXMDSEUJJ-UHFFFAOYSA-M 0.000 description 1
- LSNNMFCWUKXFEE-UHFFFAOYSA-N Sulfurous acid Chemical compound OS(O)=O LSNNMFCWUKXFEE-UHFFFAOYSA-N 0.000 description 1
- 230000004913 activation Effects 0.000 description 1
- 235000011114 ammonium hydroxide Nutrition 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000011230 binding agent Substances 0.000 description 1
- FPCJKVGGYOAWIZ-UHFFFAOYSA-N butan-1-ol;titanium Chemical compound [Ti].CCCCO.CCCCO.CCCCO.CCCCO FPCJKVGGYOAWIZ-UHFFFAOYSA-N 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 239000004917 carbon fiber Substances 0.000 description 1
- 238000003763 carbonization Methods 0.000 description 1
- 125000003178 carboxy group Chemical group [H]OC(*)=O 0.000 description 1
- 238000006555 catalytic reaction Methods 0.000 description 1
- 150000001768 cations Chemical class 0.000 description 1
- 239000012295 chemical reaction liquid Substances 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 239000011248 coating agent Substances 0.000 description 1
- 238000000576 coating method Methods 0.000 description 1
- 230000007797 corrosion Effects 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 230000000593 degrading effect Effects 0.000 description 1
- 239000012153 distilled water Substances 0.000 description 1
- 230000005284 excitation Effects 0.000 description 1
- 238000001125 extrusion Methods 0.000 description 1
- 239000012847 fine chemical Substances 0.000 description 1
- 229910003472 fullerene Inorganic materials 0.000 description 1
- 125000000524 functional group Chemical group 0.000 description 1
- 238000005469 granulation Methods 0.000 description 1
- 230000003179 granulation Effects 0.000 description 1
- 239000002638 heterogeneous catalyst Substances 0.000 description 1
- XQSBLCWFZRTIEO-UHFFFAOYSA-N hexadecan-1-amine;hydrobromide Chemical compound [Br-].CCCCCCCCCCCCCCCC[NH3+] XQSBLCWFZRTIEO-UHFFFAOYSA-N 0.000 description 1
- 229930195733 hydrocarbon Natural products 0.000 description 1
- 125000002887 hydroxy group Chemical group [H]O* 0.000 description 1
- 230000031700 light absorption Effects 0.000 description 1
- 230000004298 light response Effects 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000011159 matrix material Substances 0.000 description 1
- 230000007935 neutral effect Effects 0.000 description 1
- WVDDGKGOMKODPV-ZQBYOMGUSA-N phenyl(114C)methanol Chemical compound O[14CH2]C1=CC=CC=C1 WVDDGKGOMKODPV-ZQBYOMGUSA-N 0.000 description 1
- 239000002861 polymer material Substances 0.000 description 1
- 150000008442 polyphenolic compounds Chemical class 0.000 description 1
- 230000001376 precipitating effect Effects 0.000 description 1
- 238000000197 pyrolysis Methods 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 238000002390 rotary evaporation Methods 0.000 description 1
- 230000008313 sensitization Effects 0.000 description 1
- 235000010267 sodium hydrogen sulphite Nutrition 0.000 description 1
- 238000003980 solgel method Methods 0.000 description 1
- 230000002194 synthesizing effect Effects 0.000 description 1
- 239000004753 textile Substances 0.000 description 1
- 229910052719 titanium Inorganic materials 0.000 description 1
- XJDNKRIXUMDJCW-UHFFFAOYSA-J titanium tetrachloride Chemical compound Cl[Ti](Cl)(Cl)Cl XJDNKRIXUMDJCW-UHFFFAOYSA-J 0.000 description 1
- YONPGGFAJWQGJC-UHFFFAOYSA-K titanium(iii) chloride Chemical compound Cl[Ti](Cl)Cl YONPGGFAJWQGJC-UHFFFAOYSA-K 0.000 description 1
- 238000001291 vacuum drying Methods 0.000 description 1
- 239000002912 waste gas Substances 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J35/00—Catalysts, in general, characterised by their form or physical properties
- B01J35/30—Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
- B01J35/39—Photocatalytic properties
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/8678—Removing components of undefined structure
- B01D53/8687—Organic components
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J21/00—Catalysts comprising the elements, oxides, or hydroxides of magnesium, boron, aluminium, carbon, silicon, titanium, zirconium, or hafnium
- B01J21/06—Silicon, titanium, zirconium or hafnium; Oxides or hydroxides thereof
- B01J21/063—Titanium; Oxides or hydroxides thereof
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/70—Organic compounds not provided for in groups B01D2257/00 - B01D2257/602
- B01D2257/708—Volatile organic compounds V.O.C.'s
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/38—Organic compounds containing nitrogen
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/20—Total organic carbon [TOC]
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2305/00—Use of specific compounds during water treatment
- C02F2305/10—Photocatalysts
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Environmental & Geological Engineering (AREA)
- Organic Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Materials Engineering (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Biomedical Technology (AREA)
- Analytical Chemistry (AREA)
- Toxicology (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Water Supply & Treatment (AREA)
- Catalysts (AREA)
Abstract
The invention belongs to the technical field of catalyst material preparation, and discloses a preparation method of a natural lignin-based catalytic material. The lignin-based nano metal oxide composite photocatalyst prepared by the method has small metal oxide particle size, uniform distribution and obviously improved photocatalytic efficiency, has strong catalytic degradation effect on volatile organic compounds and high-concentration organic wastewater, can be applied to the field of photocatalysis, and particularly has potential application value in the field of photocatalytic degradation of difficultly-treated volatile organic compounds and nitrogen-containing organic pollutants.
Description
Technical Field
The invention belongs to the technical field of catalyst material preparation, and discloses a preparation method of a natural polymer lignin-based catalytic material. Can be applied to the field of photocatalysis, and particularly has potential application value in the field of photocatalytic degradation of difficultly-treated volatile organic compounds and degradation of nitrogen-containing organic pollutants.
Background
In recent years, with the development of society, organic wastewater discharged in the production process of textiles and fine chemicals causes serious environmental pollution, and has been paid high attention by global researchers. The photocatalysis technology is a novel effective green technology and has important application prospect in the fields of environment and energy. As an excellent semiconductor material, the nano titanium dioxide has the advantages of stable chemical property, corrosion resistance, acid and alkali resistance, low price and the like, is widely used as a photocatalyst and can be used for degrading organic pollutants in water. Lignin, one of the most widely occurring resources in nature, is a polyphenol polymer in the second largest amorphous state, second only to cellulose, in content in the plant world. It is a renewable, green and environment-friendly natural polymer material. Commercial lignin, which is a by-product of the paper industry, is present in black liquor and is rarely further processed and utilized, resulting in waste of resources and even environmental problems. The lignin contains abundant phenolic hydroxyl groups, so the lignin has certain reduction performance, and the heterogeneous catalyst taking the lignin as a carrier has attracted the attention of researchers,
however, the photocatalytic activity of titanium dioxide is limited by its forbidden bandwidth (the forbidden bandwidth of rutile phase is 3.0eV, and the forbidden bandwidth of anatase phase is 3.2eV), and it can only be excited by ultraviolet light having a wavelength of less than 380nm, and the solar light utilization rate is low. On the other hand, when the TiO2 photocatalyst is irradiated by sunlight, electrons and holes generated by excitation easily recombine on the surface and in the body, resulting in low photocatalytic efficiency. The carbon material has good electron transport capacity and a certain sensitization effect on the semiconductor material, and the defects can be overcome to a certain extent by compounding the semiconductor material and the carbon material together. A large number of researches show that the photocatalytic performance of the composite material can be obviously improved by compounding a carbon material (graphene, carbon fiber, carbon nanotube and the like) and TiO 2. The literature (ACS Applied Materials & Interfaces,2013,5(3): 1156-1164) discloses a method for preparing TiO 2/carbon (GR, CNT and C60) nanocomposites with different carbon material addition ratios through sol-gel method and hydrothermal method treatment, the photocatalytic performance of the synthesized TiO 2/carbon composites is researched through photocatalytic degradation of benzyl alcohol, the addition of GR, CNT and C60 can induce the increase of light absorption intensity in the visible light region, effectively promote the visible light response of Ti O2/GR, Ti O2/CNT and Ti O2/C60 nanocomposites, and promote the effective separation of photoexcited electron-hole pairs, thereby improving the photocatalytic efficiency. Chinese patent CN 107308929a discloses "a graphene-nano titanium dioxide composite photocatalyst" which is prepared by synthesizing graphene oxide with graphite powder, adding deionized water to prepare a graphene oxide solution, adding a cetyl ammonium bromide solution and a titanium trichloride solution, reacting in a high-pressure reaction kettle, precipitating, and washing to obtain the product. However, the preparation process of the carbon-based material (graphene, carbon nanotube, fullerene, etc.) of the carbon-based/Ti O2 composite photocatalyst is complex and expensive, strong acid and strong base are required in the preparation process, and the environmental pollution is serious; the prepared carbon-based material with a certain morphology is compounded with TiO2, so that the bonding force between the two materials is weak; meanwhile, carbon-based materials such as graphene are easy to agglomerate, so that the carbon-based materials and titanium dioxide in the prepared composite photocatalyst are not uniformly distributed. These problems greatly limit the photocatalytic performance and hinder the commercial application prospect.
The lignin is a high molecular polymer with a three-dimensional space network structure, has high carbon content and a plurality of active functional groups, is second to cellulose in the natural reserve, and is an excellent precursor for preparing carbon materials. Industrial lignin is mainly derived from by-products of the pulp and paper industry: most of the lignosulfonate in the red liquor of the sulfite pulping and the alkali lignin in the black liquor of the alkali pulping are treated and discharged as waste liquor. The effective utilization of the industrial lignin not only can save resources, but also is beneficial to reducing the environmental burden. For example, in the literature (forest engineering, 2015(3): 54-56), alkali lignin is used as a raw material, and a lignin amine salt obtained through a mannich reaction is added into a hydrochloric acid solution of butyl titanate to perform a hydrothermal reaction at 80-130 ℃ for 72 hours, and then the mixture is sintered at 500 ℃ for 10 hours to obtain titanium dioxide nanoparticles. Chinese patent CN106824151A discloses a lignin-based mesoporous titanium dioxide photocatalytic material, a preparation method and application, wherein titanium tetrachloride is added into an alkali lignin solution, the pH value is adjusted to 1-5, heating is carried out for a period of time at 60-100 ℃, ammonia water is added, centrifugal separation is carried out, after ball milling, calcination is carried out for 5 hours at 400-600 ℃, and the titanium dioxide is obtained after lignin is removed. Although the method for preparing titanium dioxide by using lignin as a template can obtain titanium dioxide with good performance, the preparation process is complex, the processes of hydrothermal, ball milling and the like are required, and in order to remove the template, long-time calcination is generally required, so that the cost is increased, and the lignin is not fully utilized
In the existing preparation of the lignin carbon/titanium dioxide composite photocatalyst, because titanium alkoxide serving as a titanium dioxide precursor is very easy to hydrolyze and cannot be well dispersed in a lignin solution, the titanium dioxide precursor can only be slowly added into the lignin aqueous solution, so that the obtained titanium dioxide particles are large, strong acting force does not exist between the titanium dioxide and the lignin, and the coating amount of the lignin is small. These factors have greatly limited the development of lignin-based nano-metal oxide photocatalysts prepared using lignin as a carbon source.
Disclosure of Invention
In order to solve the problem of the defect of limiting lignin as a raw material to prepare the photocatalyst, the preparation method of the natural lignin-based photocatalytic material is provided.
The technical scheme adopted by the invention for solving the problems is as follows: a method for preparing a natural lignin-based photocatalytic material comprises the following specific processes,
modification of S1: firstly, natural lignin separated from plants is modified;
s2 mixing: adding dry ice and nano metal oxide into the modified natural lignin, and placing the mixture into a ball mill for ball milling to prepare a lignin-nano metal oxide mixture;
s3, drying: heating the mixture at the temperature of 100-900 ℃ for 1-24 hours to prepare the nano-particle catalytic material.
Further, the S1 modification: lignin modification includes, but is not limited to, amine cationization, sulfomethylation, multi-monomer graft copolymerization, and the like.
Further, the S2 compounding: the amount of the added dry ice is 0.01 to 10 times of the mass amount of the lignin, and the amount of the added metal oxide is 0.01 to 1 time of the mass amount of the lignin.
Further, the S2 compounding: nano metal oxides include, but are not limited to, semiconductor catalytic materials such as ZnO, SeO and Cu2O, etc.; magnetic catalytic material, Fe2O3，Fe3O4NiO, CoO, etc.
Further, the step S3 is drying: the lignin-based nano metal oxide compound is heated to 400-800 ℃ in an inert atmosphere and calcined for 1-4 hours to obtain the lignin-based nano metal oxide composite photocatalyst, and the catalytic material can be directly applied to photocatalytic degradation of VOCs or high-concentration organic wastewater.
According to the method, a natural lignin polymer separated from plants is modified, amination modification, grafting modification and the like are carried out according to the property of an adsorbed substance when the natural lignin polymer is used as an adsorbing material according to the application requirement of a product, dry ice and nano metal oxide are mixed, and the mixture is placed into a ball mill for ball milling to prepare a lignin-metal oxide mixture, wherein the lignin-metal oxide mixture aims at removing branch chains on lignin, converting phenolic hydroxyl into carboxyl and embedding the metal oxide into the gaps of the lignin. And then the mixture is made into a granular catalytic material. The adopted preparation method comprises but is not limited to adding a binder for extrusion forming and electrostatic spraying granulation, or the obtained lignin-metal oxide mixture is subjected to pyrolysis carbonization and activation to prepare the porous adsorption-catalysis composite material.
The lignin-based nano metal oxide composite photocatalyst prepared by the method has small metal oxide particle size, uniform distribution and obviously improved photocatalytic efficiency, has strong catalytic degradation effect on volatile organic compounds and high-concentration organic wastewater, can be applied to the field of photocatalysis, and particularly has potential application value in the field of photocatalytic degradation of difficultly-treated volatile organic compounds and nitrogen-containing organic pollutants.
Detailed Description
The present invention will be described in further detail with reference to examples, but the embodiments of the present invention are not limited thereto. The materials referred to in the following examples are commercially available.
Example 1
A preparation method of a natural lignin-based photocatalytic material comprises the following specific steps:
modification of S1: taking 100g of lignin, adding 200g of water and 120mL of 1.5% (mass concentration) NaOH aqueous solution, stirring for 20 minutes, adding 10g of formaldehyde, continuing stirring for 20 minutes, adding 20mL of ethylenediamine while stirring, heating in a water bath at 100 ℃, and refluxing and stirring for 3 hours to obtain an aminated modified lignin sample;
s2, mixing: drying the sample obtained in S1 in an oven at a constant temperature of 105 ℃ for 24 hours, taking out, adding 10g of nano TiO2 (particle size 10nm) and 10g of dry ice, putting into a ball milling tank, and simultaneously adding 300g of Al with the diameter of 3mm2O3Grinding balls, placing in a planetary ball mill, setting the rotating speed at 500RPM, and ball-milling for 3 hours to obtain a lignin-based nano titanium dioxide mixture;
s3, drying: and (3) placing the nano titanium dioxide mixture obtained in the step (S2) in an atmosphere furnace, reacting for 3h at 700 ℃ in the atmosphere of N2, continuously introducing a small amount of water vapor, fully reacting for 1h at 900 ℃, and stopping heating until the temperature in the furnace is reduced to room temperature to obtain the lignin carbon-based nano metal oxide composite photocatalyst.
Example 2
A preparation method of a natural lignin-based photocatalytic material comprises the steps of taking natural high-molecular lignin, carrying out amination modification, adding nano TiO2 and dry ice according to the mass ratio, placing the mixture into a planetary ball mill, and carrying out ball milling on the mixture to obtain powder, wherein the powder is prepared into the nano composite matrix catalytic material by adopting an electrostatic spraying method.
The method comprises the following specific steps:
modification of S1: modifying lignin by amination in the same way as in example 1;
s2 mixing: drying the sample obtained in S1 in an oven at a constant temperature of 105 ℃ for 24 hours, taking out, adding 10g of nano TiO2 (particle size 10nm) and 10g of dry ice, putting into a ball milling tank, and simultaneously adding 300g of Al with the diameter of 3mm2O3Grinding balls, namely, setting the rotation speed of a planetary ball mill to be 500RPM, and carrying out ball milling for 3 hours to obtain a lignin-based nano titanium dioxide mixture;
s3, drying: and (3) placing the nano titanium dioxide mixture obtained in the step (S2) in an atmosphere furnace, reacting for 3h at 700 ℃ in the atmosphere of N2, continuously introducing a small amount of water vapor, fully reacting for 1h at 900 ℃, stopping heating, reducing the temperature in the furnace to room temperature, and removing the sample to obtain the lignin carbon-based nano metal oxide composite photocatalyst.
Example 3
Modification of S1: adding 1500g of deionized water into 100g of lignin, adding the lignin into a flask with a stirring rod and reflux condensation, heating to 40 ℃, slowly adding dilute hydrochloric acid to adjust the pH value to 2, adding 50g of 30% aqueous hydrogen peroxide, stirring and heating at 50 ℃ for 2 hours, then heating to 80 ℃, adding 40g of sodium bisulfite and 30g of 30% aqueous formaldehyde, reacting at constant temperature for 12 hours, and then cooling to room temperature to obtain a crude product. The anion resin was then soaked with 2M aqueous sodium hydroxide overnight and the cation resin was soaked with 2M aqueous hydrochloric acid overnight. Sequentially flowing the obtained crude product through anion exchange resin and cation exchange resin, washing the anion and cation exchange resin by using distilled water until the pH of the cleaning solution is nearly neutral to obtain an extracting solution, and performing rotary evaporation and vacuum drying on the extracting solution to obtain sulfomethylated modified lignin;
s2 mixing: the same as example 1;
s3, drying: the same as in example 1.
Example 4
Modification of S1: adding 200g of water into 100g of lignin, simultaneously adding 20g of phenol and 50g of 30-concentration formaldehyde aqueous solution, adding the lignin into a flask with a stirring rod and reflux condensation, heating to 100 ℃, reacting for 12 hours, stopping the reaction, cooling, removing water in reaction liquid by using a rotary evaporator, drying for 12 hours in a constant-temperature drying oven at 100 ℃, and drying to obtain a lignin molecular monomer graft copolymerization product;
s2 mixing: the same as example 1;
s3, drying: the same as in example 1.
Example 5
Modification of S1: performing sulfomethylation modification on lignin in the same way as in example 3;
s2 mixing: the same as example 2;
s3, drying: the same as example 2;
example 6
Modification of S1: grafting, copolymerizing and modifying the lignin multi-monomer in the same way as in example 4;
s2 mixing: the same as example 2;
s3, drying: the same as in example 2.
The use function of the invention is verified by UV photocatalytic degradation experiments on high-concentration organic wastewater.
Comparative example 1: no photocatalyst is added;
example 1: the catalyst is an amination modified nano composite particle photocatalytic material;
example 2: the catalyst is an amination modified nano composite photocatalytic material;
example 3: the catalyst is a lignin sulfomethylation modified nano composite base photocatalytic material;
example 4: the catalyst is a lignin multi-monomer graft copolymerization nano composite base photocatalysis material;
example 5: the catalyst is a lignin sulfomethylation modified carbon-based nano metal oxide composite photocatalyst;
example 6: the catalyst is a lignin multi-monomer graft copolymerization modified carbon-based nano metal oxide composite photocatalyst;
the TOC (total organic carbon) value of the high-concentration organic wastewater adopted in the experiment is 20000mg/L, and the dosage of the catalyst is 10g/1000g of wastewater
| Detecting items | TOC after 5min | TOC after 10min | TOC after 15min | TOC after 20min |
| Comparative example 1 | 19200 | 19100 | 18600 | 18500 |
| Example 1 | 14200 | 8900 | 5900 | 2800 |
| Example 2 | 14010 | 12140 | 8750 | 6800 |
| Example 3 | 10250 | 9800 | 7850 | 4850 |
| Example 4 | 8750 | 6500 | 3800 | 2950 |
| Example 5 | 6900 | 5500 | 2800 | 1800 |
| Example 6 | 5800 | 4500 | 2900 | 2200 |
The use function of the invention is verified by the experiment of UV photocatalytic degradation of VOCs.
Comparative example 2: no photocatalyst is added;
example 1: the photocatalyst is a particle catalytic material;
example 2: a nano metal oxide composite photocatalyst;
the total non-methane hydrocarbons in the waste gas VOCs adopted in the experiment are 1000mg/L, and the space velocity of the catalyst is 300--1。
The foregoing shows and describes the general principles, essential features, and advantages of the invention. It will be understood by those skilled in the art that the present invention is not limited to the embodiments described above, which are merely illustrative of the principles of the invention, but that various changes and modifications may be made without departing from the spirit and scope of the invention, which fall within the scope of the invention as claimed. The scope of the invention is defined by the appended claims and equivalents thereof.
Claims (6)
1. A preparation method of a natural lignin-based photocatalytic material is characterized in that the specific process is,
modification of S1: firstly, natural lignin separated from plants is modified;
s2 mixing: adding dry ice and nano metal oxide into the modified natural lignin, and placing the mixture into a ball mill for ball milling to prepare a lignin-nano metal oxide mixture;
s3, drying: heating the mixture at the temperature of 100-900 ℃ for 1-24 hours to prepare the nano-particle catalytic material.
2. The method for preparing a photocatalytic material based on natural lignin according to claim 1, wherein the modification of S1 is: lignin modification includes, but is not limited to, amine cationization, sulfomethylation, multi-monomer graft copolymerization, and the like.
3. The method for preparing a photocatalytic material based on natural lignin according to claim 1, wherein the S2 is prepared by mixing: the amount of the added dry ice is 0.01 to 10 times of the mass amount of the lignin, and the amount of the added metal oxide is 0.01 to 1 time of the mass amount of the lignin.
4. The method for preparing a photocatalytic material based on natural lignin according to claim 1, wherein the S2 is prepared by mixing: the nano-metal oxide includes, but is not limited to, semiconductor catalytic materials and magnetic catalytic materials.
5. The method for preparing a photocatalytic material based on natural lignin according to claim 4, wherein said S2 is prepared by mixing: the semiconductor catalyst material is selected from ZnO, SeO and Cu2O, etc.; the magnetic catalytic material is selected from Fe2O3，Fe3O4NiO, CoO, etc.
6. The method for preparing a photocatalytic material based on natural lignin according to claim 1, wherein the step of drying S3 comprises: the lignin-based nano metal oxide compound is heated to 400-800 ℃ in an inert atmosphere and calcined for 1-4 hours to obtain the lignin-based nano metal oxide composite photocatalyst, and the catalytic material can be directly applied to photocatalytic degradation of VOCs or high-concentration organic wastewater.
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN2019114141402 | 2019-12-31 | ||
| CN201911414140 | 2019-12-31 |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN111330560A true CN111330560A (en) | 2020-06-26 |
| CN111330560B CN111330560B (en) | 2023-05-16 |
Family
ID=71176976
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN202010272457.3A Active CN111330560B (en) | 2019-12-31 | 2020-04-09 | Preparation method of natural lignin-based photocatalytic material |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN111330560B (en) |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN112604669A (en) * | 2020-11-29 | 2021-04-06 | 张倩茹 | Composite resin aerogel and application thereof in sewage treatment |
| CN113019334A (en) * | 2021-03-11 | 2021-06-25 | 东北林业大学 | Preparation of modified lignin magnetic composite material and method for removing dye in wastewater by using modified lignin magnetic composite material |
| CN113275038A (en) * | 2021-01-11 | 2021-08-20 | 华南理工大学 | Method for photocatalytic oxidative cracking of lignin C-O bond and benzene ring |
| CN113426422A (en) * | 2021-07-07 | 2021-09-24 | 齐鲁工业大学 | Preparation method and application of lignin-based magnetic nano composite particles |
Citations (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1764602A (en) * | 2003-03-31 | 2006-04-26 | 东陶机器株式会社 | Surface-modified titanium dioxide fine particles and dispersion comprising the same, and method for producing the same |
| US20060264520A1 (en) * | 2003-03-31 | 2006-11-23 | Shuji Sonezaki | Surface-modified titanium dioxide fine particles and dispersion comprising the same, and method for producing the same |
| CN102311561A (en) * | 2011-04-27 | 2012-01-11 | 扬州斯培德化工有限公司 | Modified titanium dioxide grain, super-hydrophilic transparent thin film and preparation method thereof |
| CN103303962A (en) * | 2013-06-05 | 2013-09-18 | 江苏大学 | Method for preparing nanometre copper oxide by solid-phase template method |
| CN108114746A (en) * | 2016-11-29 | 2018-06-05 | 中国科学院大连化学物理研究所 | A kind of preparation method and application of lignin-base acidic catalyst |
| CN108938450A (en) * | 2018-06-26 | 2018-12-07 | 华南理工大学 | A kind of lignin modification titanium dioxide granule and the preparation method and application thereof |
| CN109482178A (en) * | 2018-11-19 | 2019-03-19 | 华南理工大学 | A kind of human lymph node type lignin carbon/nanometer titanium dioxide compound photocatalyst and its preparation method and application |
| CN109482168A (en) * | 2018-11-19 | 2019-03-19 | 华南理工大学 | A kind of lignin carbon/nanometer titanium dioxide compound photocatalyst and its preparation method and application |
| CN110255527A (en) * | 2019-07-23 | 2019-09-20 | 哈尔滨工业大学 | A kind of preparation method and applications of the oxygen-enriched hard carbon material of biomass derived |
-
2020
- 2020-04-09 CN CN202010272457.3A patent/CN111330560B/en active Active
Patent Citations (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1764602A (en) * | 2003-03-31 | 2006-04-26 | 东陶机器株式会社 | Surface-modified titanium dioxide fine particles and dispersion comprising the same, and method for producing the same |
| US20060264520A1 (en) * | 2003-03-31 | 2006-11-23 | Shuji Sonezaki | Surface-modified titanium dioxide fine particles and dispersion comprising the same, and method for producing the same |
| CN102311561A (en) * | 2011-04-27 | 2012-01-11 | 扬州斯培德化工有限公司 | Modified titanium dioxide grain, super-hydrophilic transparent thin film and preparation method thereof |
| CN103303962A (en) * | 2013-06-05 | 2013-09-18 | 江苏大学 | Method for preparing nanometre copper oxide by solid-phase template method |
| CN108114746A (en) * | 2016-11-29 | 2018-06-05 | 中国科学院大连化学物理研究所 | A kind of preparation method and application of lignin-base acidic catalyst |
| CN108938450A (en) * | 2018-06-26 | 2018-12-07 | 华南理工大学 | A kind of lignin modification titanium dioxide granule and the preparation method and application thereof |
| CN109482178A (en) * | 2018-11-19 | 2019-03-19 | 华南理工大学 | A kind of human lymph node type lignin carbon/nanometer titanium dioxide compound photocatalyst and its preparation method and application |
| CN109482168A (en) * | 2018-11-19 | 2019-03-19 | 华南理工大学 | A kind of lignin carbon/nanometer titanium dioxide compound photocatalyst and its preparation method and application |
| CN110255527A (en) * | 2019-07-23 | 2019-09-20 | 哈尔滨工业大学 | A kind of preparation method and applications of the oxygen-enriched hard carbon material of biomass derived |
Non-Patent Citations (2)
| Title |
|---|
| 林文胜: ""木质素碳/半导体复合材料的制备及其光催化性能"", 《中国优秀硕士学位论文全文数据库 工程科技Ⅰ辑》 * |
| 罗运军等: "《新型含能材料》", 31 January 2015, 北京：国防工业出版社 * |
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN112604669A (en) * | 2020-11-29 | 2021-04-06 | 张倩茹 | Composite resin aerogel and application thereof in sewage treatment |
| CN112604669B (en) * | 2020-11-29 | 2023-12-19 | 张倩茹 | Composite resin aerogel and application thereof in sewage treatment |
| CN113275038A (en) * | 2021-01-11 | 2021-08-20 | 华南理工大学 | Method for photocatalytic oxidative cracking of lignin C-O bond and benzene ring |
| CN113019334A (en) * | 2021-03-11 | 2021-06-25 | 东北林业大学 | Preparation of modified lignin magnetic composite material and method for removing dye in wastewater by using modified lignin magnetic composite material |
| CN113019334B (en) * | 2021-03-11 | 2022-09-23 | 东北林业大学 | Preparation of modified lignin magnetic composite material and method for removing dye in wastewater by using modified lignin magnetic composite material |
| CN113426422A (en) * | 2021-07-07 | 2021-09-24 | 齐鲁工业大学 | Preparation method and application of lignin-based magnetic nano composite particles |
Also Published As
| Publication number | Publication date |
|---|---|
| CN111330560B (en) | 2023-05-16 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN111330560B (en) | Preparation method of natural lignin-based photocatalytic material | |
| Wang et al. | Hollow spherical WO3/TiO2 heterojunction for enhancing photocatalytic performance in visible-light | |
| Gao et al. | Fabrication of visible-light responsive TiO2@ C photocatalyst with an ultra-thin carbon layer to efficiently degrade organic pollutants | |
| Zhang et al. | Synthesis of BiOCl/TiO2–zeolite composite with enhanced visible light photoactivity | |
| Ren et al. | In situ synthesis of gC 3 N 4/TiO 2 heterojunction nanocomposites as a highly active photocatalyst for the degradation of Orange II under visible light irradiation | |
| CN111453804B (en) | Preparation method of iron-doped graphite-like phase carbon nitride/graphene multifunctional nano composite material | |
| CN102698785B (en) | A kind of tripolite loading nitrogen-doped nanometer TiO 2the preparation method of catalysis material | |
| CN102039117B (en) | Method for preparing loaded nano TiO2 composite material by using precipitated white carbon black as carrier | |
| Zhang et al. | Immobilization laccase on heterophase TiO2 microsphere as a photo-enzyme integrated catalyst for emerging contaminants degradation under visible light | |
| CN110227453B (en) | Preparation method of AgCl/ZnO/GO composite visible light catalyst | |
| CN109482168B (en) | Lignin carbon/nano titanium dioxide composite photocatalyst and preparation method and application thereof | |
| CN109529872B (en) | Amorphous nano titanium dioxide visible light catalyst compound and preparation method thereof | |
| CN110624564A (en) | In2O3@ZnIn2S4Nanosheet material, preparation method and application thereof | |
| CN109806857A (en) | A kind of nano zinc oxide photocatalysis composite material and preparation method | |
| CN111905713A (en) | Vanadium-doped TiO2Preparation method of/reduced graphene composite nano photocatalyst | |
| CN112973744B (en) | Photoelectric catalyst and preparation method thereof | |
| CN113198515A (en) | Ternary photocatalyst and preparation method and application thereof | |
| CN104368338B (en) | A kind of have amido modified Pd/TiO2The preparation method of photocatalyst | |
| CN111821967B (en) | Heterojunction titanium dioxide composite photocatalyst and preparation method thereof | |
| CN115779889B (en) | Lignin charcoal/bismuth molybdate composite photocatalyst and preparation method and application thereof | |
| CN108404948B (en) | One kind (BiO)2CO3-BiO2-xComposite photocatalyst and preparation method and application thereof | |
| Jing et al. | β-FeOOH/TiO 2/cellulose nanocomposite aerogel as a novel heterogeneous photocatalyst for highly efficient photo-Fenton degradation | |
| CN110624532B (en) | TiO 22-BiVO4-graphene ternary composite photocatalytic material and preparation method thereof | |
| CN113181964B (en) | Nano nitrogen-doped titanium dioxide-chitosan composite material and preparation method and application thereof | |
| CN114618591A (en) | g-C3N4@ ZIF-8 composite photocatalyst and preparation method and application thereof |
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 | ||
| GR01 | Patent grant | ||
| GR01 | Patent grant | ||
| TR01 | Transfer of patent right | ||
| TR01 | Transfer of patent right |
Effective date of registration: 20240612 Address after: 116699, floors 1-4, ShuangD4 Street, Dalian Economic and Technological Development Zone, Dalian City, Liaoning Province Patentee after: Zhongke furfural (Liaoning) Technical Service Center Co.,Ltd. Country or region after: China Address before: Room 505, Building D09, No. 863-9, Shangshengou Village, Hunnan District, Shenyang City, Liaoning Province, 110015 Patentee before: Shenyang zhongkebio Energy Technology Co.,Ltd. Country or region before: China |