CN108654605A - The preparation method of the porous carbon-based titanium dioxide photochemical catalyst of modified by silver for degradation of phenol - Google Patents

The preparation method of the porous carbon-based titanium dioxide photochemical catalyst of modified by silver for degradation of phenol Download PDF

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Publication number
CN108654605A
CN108654605A CN201710709473.2A CN201710709473A CN108654605A CN 108654605 A CN108654605 A CN 108654605A CN 201710709473 A CN201710709473 A CN 201710709473A CN 108654605 A CN108654605 A CN 108654605A
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China
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silver
titanium dioxide
modified
photochemical catalyst
porous carbon
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范冬梅
徐清
陈高健
张靖桢
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Ningbo University
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Ningbo University
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/38Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
    • B01J23/48Silver or gold
    • B01J23/50Silver
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/39Photocatalytic properties
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/60Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/02Impregnation, coating or precipitation
    • B01J37/0201Impregnation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/08Heat treatment
    • B01J37/082Decomposition and pyrolysis
    • B01J37/086Decomposition of an organometallic compound, a metal complex or a metal salt of a carboxylic acid
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • C02F2101/345Phenols
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/10Photocatalysts

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Materials Engineering (AREA)
  • Physics & Mathematics (AREA)
  • Thermal Sciences (AREA)
  • Inorganic Chemistry (AREA)
  • Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Catalysts (AREA)

Abstract

The present invention relates to environmental technology fields, and in particular to a kind of preparation method for the porous carbon-based titanium dioxide photochemical catalyst of modified by silver of phenol in water body of degrading includes the following steps:Using titanium-based metal organic frame compound as presoma, it first passes through high temperature pyrolytic cracking (HTP) and prepares titaniferous C-base composte material, it is obtained for the porous carbon-based titanium dioxide photochemical catalyst of the modified by silver of phenol in water body of degrading after silver nitrate solution impregnates, then by high temperature pyrolytic cracking (HTP).Preparation method of the present invention is simple, practical, the performance of photochemical catalyst can also be adjusted by changing type, the pyrolysis temperature of titanium-based metal organic frame compound, the porous carbon-based titanium dioxide photochemical catalyst of the modified by silver obtained has many advantages, such as that good porosity, reconfigurable control of hole, catalytic activity are high.

Description

The preparation of the porous carbon-based titanium dioxide photochemical catalyst of modified by silver for degradation of phenol Method
Technical field
The present invention relates to environmental technology fields, and in particular to a kind of modified by silver for phenol in water body of degrading is porous carbon-based The preparation method of titanium dioxide optical catalyst.
Background technology
At present in water body in the photocatalytic degradation research of phenol, common photochemical catalyst is the light such as titanium dioxide and zinc oxide Catalyst, its advantage is that non-toxic inexpensive, catalytic activity is high, and selectivity is good, and reaction condition is mild, not etching apparatus, and secondary Pollute small, preparation process is simple.But the photocatalysis efficiency of degradation of phenol is relatively low when these material photocatalysts, because these Material itself is poor to the adsorption capacity of organic matter.In addition, these material specific surface areas are big, surface energy is high, easily reunite, Disperse that uneven, inactivation is fast, separation and recycling are difficult during organic matter in water body of degrading, it is also possible to become pollutant, Its application is set to be restricted.
In order to solve the problems, such as that these photochemical catalysts exist, people have carried out numerous studies, these researchs are concentrated mainly on Three aspects below:(1) changed by the noble-metal-supported of photocatalyst surface, metal ion mixing, rare earth modified, photosensitizer Property, Material cladding excitation separation of charge, improve photohole efficiency, expand wave-length coverage, change selectivity of product;(2) will Titanium dioxide is compound with other catalysis materials, such as titanium dioxide/zirconium dioxide, titanium dioxide/molybdenum trioxide, titanium dioxide/ Tungstic acid etc. changes material structure characteristic and surface nature, improves the photocatalysis performance of material;(3) with other porous materials The combination of material, such as molecular sieve, film, porous carbon carry out the joint technology of carried titanium dioxide as carrier.But about titanium dioxide Report is seldom seen in compound research with porous carbon, silver.
The present invention uses the metal organic framework compound presoma with different pore passage structures and chemical characteristic, passes through height Warm solution prepares the porous carbon-based titanium dioxide photochemical catalyst of modified by silver, when the photochemical catalyst obtained is used for degradation of phenol, tool Have the advantages that good porosity, reconfigurable control of hole, catalytic activity are high, is a feasible approach.
Invention content
It is a kind of for phenol in water body of degrading the technical problem to be solved by the present invention is to provide for the above-mentioned prior art Porosity is good, reconfigurable control of hole, the high porous carbon-based titanium dioxide photochemical catalyst of modified by silver of catalytic activity preparation side Method.
Technical solution is used by the present invention solves above-mentioned technical problem:A kind of modified by silver for degradation of phenol is porous The preparation method of carbon-based titanium dioxide photochemical catalyst, it is characterised in that include the following steps:A weighs a certain amount of titanium-based metal Organic frame compound is put into tube furnace, under argon stream, is warming up to 400 DEG C of pyrolysis 5h, titaniferous C-base composte material is made; B, silver nitrate solution is added by obtained titaniferous C-base composte material, impregnates 48h in 20 DEG C;C takes out precipitation, vacuum drying Afterwards, it is put into tube furnace, under argon stream, is warming up to certain temperature pyrolysis 5h, obtains the porous carbon-based titanium dioxide of modified by silver Titanium photochemical catalyst.
Preferably, the titanium-based metal organic frame compound described in step a is ZTOF-1, MIL-125, NH2-MIL- 125 one or more.
Preferably, the porous carbon-based titanium dioxide photochemical catalyst of modified by silver described in step c, pyrolysis temperature is when preparation 400~1000 DEG C.
Compared with the prior art, the advantages of the present invention are as follows:Preparation method is simple, practical, can also be by changing titanium-based The performance of photochemical catalyst is adjusted in type, the pyrolysis temperature of metal organic framework compound presoma, and the silver obtained is repaiied Adoring porous carbon-based titanium dioxide photochemical catalyst has many advantages, such as that good porosity, reconfigurable control of hole, catalytic activity are high, the present invention It can be used for environmental technology field, in the water body that is especially used to degrade in the preparation of the photochemical catalyst of phenol.
Description of the drawings
Fig. 1 is the XRD diagram for the porous carbon-based titanium dioxide photochemical catalyst of modified by silver that embodiment 1 obtains;
Fig. 2 is the SEM figures for the porous carbon-based titanium dioxide photochemical catalyst of modified by silver that embodiment 1 obtains.
Specific implementation mode
Present invention is further described in detail with reference to embodiments.
Embodiment 1:
The ZTOF-1 for weighing 0.4g is put into tube furnace, and 400 DEG C are warming up to the rate of 10 DEG C/min under argon stream, and 5h is kept the temperature, 0.19g titaniferous C-base composte materials are made.It is by obtained titaniferous C-base composte material addition 20mL mass concentrations In 43% silver nitrate solution, after 20 DEG C impregnate 48h, precipitation is taken out, vacuum is dried for 24 hours at 80 DEG C, is put into tube furnace, 1000 DEG C are warming up to the rate of 10 DEG C/min under argon stream, and keeps the temperature 5h, obtains the porous carbon-based titanium dioxide of 0.27g modified by silver Titanium photochemical catalyst is denoted as 1# photochemical catalysts.
The porous carbon-based titanium dioxide photochemical catalyst of modified by silver tests the photocatalytic degradation of phenol use in aqueous solution Xi'an photochemical reactor more multi-functional than bright instrument company BILON-GHX-1D, and using the high pressure xenon lamp of 1000W as light source. The 1# photochemical catalysts for weighing 0.06g, are then added into the phenol solution of a concentration of 0.06g/L of 60mL, and constantly stir It mixes, for the phenol of addition 1# photochemical catalysts under xenon lamp irradiation after 1.5h photocatalytic degradations, phenol degrading rate reaches 90.3%, is A kind of efficient catalysis material.
Embodiment 2:
Other are with 1# photochemical catalysts, and pyrolysis temperature is 800 DEG C when prepared by modified by silver porous carbon-based titanium dioxide photochemical catalyst, The porous carbon-based titanium dioxide of 0.29g modified by silver is obtained, is denoted as 2# photochemical catalysts, other with embodiment 1 is similar.2# light is added For the phenol of catalyst under xenon lamp irradiation after 1.5h photocatalytic degradations, phenol degrading rate reaches 100%.
Embodiment 3:
Other are with 1# photochemical catalysts, and pyrolysis temperature is 600 DEG C when prepared by modified by silver porous carbon-based titanium dioxide photochemical catalyst, The porous carbon-based titanium dioxide of 0.3g modified by silver is obtained, is denoted as 3# photochemical catalysts, other with embodiment 1 is similar.3# light is added For the phenol of catalyst under xenon lamp irradiation after 1.5h photocatalytic degradations, phenol degrading rate reaches 95.4%.
Embodiment 4:
Other are with 1# photochemical catalysts, and pyrolysis temperature is 400 DEG C when prepared by modified by silver porous carbon-based titanium dioxide photochemical catalyst, The porous carbon-based titanium dioxide of 0.31g modified by silver is obtained, is denoted as 4# photochemical catalysts, other with embodiment 1 is similar.Light is added to urge For the phenol of agent under xenon lamp irradiation after 1.5h photocatalytic degradations, phenol degrading rate reaches 60.7%.
Embodiment 5:
Other are MIL-125 with 2# photochemical catalysts, titanium-based metal organic frame compound, and it is porous to obtain 0.32g modified by silver Carbon-based titanium dioxide, is denoted as 5# photochemical catalysts, and other with embodiment 2 is similar.The phenol that photochemical catalyst is added shines in xenon lamp Penetrate lower after 1.5h photocatalytic degradations, phenol degrading rate reaches 85.2%.
Embodiment 6:
, with 2# photochemical catalysts, titanium-based metal organic frame compound is NH for other2- MIL-125 obtains 0.34g modified by silver Porous carbon-based titanium dioxide, is denoted as 6# photochemical catalysts, and other with embodiment 2 is similar.The phenol of photochemical catalyst is added in xenon Under light irradiation after 1.5h photocatalytic degradations, phenol degrading rate reaches 80.5%.

Claims (3)

1. a kind of preparation method of the porous carbon-based titanium dioxide photochemical catalyst of modified by silver for degradation of phenol, it is characterised in that packet Include following steps:A weighs a certain amount of titanium-based metal organic frame compound and is put into tube furnace, under argon stream, is warming up to 400 DEG C of pyrolysis 5h, are made titaniferous C-base composte material;Silver nitrate solution is added in obtained titaniferous C-base composte material by b, in 20 DEG C of dipping 48h;C takes out precipitation, after vacuum drying, is put into tube furnace, under argon stream, is warming up to certain temperature Degree pyrolysis 5h, obtains the porous carbon-based titanium dioxide photochemical catalyst of modified by silver.
2. preparation method according to claim 1, it is characterised in that:The titanium-based metal organic frame compound of step a is ZTOF-1、MIL-125、NH2The one or more of-MIL-125.
3. preparation method according to claim 1, it is characterised in that:In step c, the porous carbon-based titanium dioxide of modified by silver Pyrolysis temperature is 400~1000 DEG C when prepared by photochemical catalyst.
CN201710709473.2A 2017-08-05 2017-08-05 The preparation method of the porous carbon-based titanium dioxide photochemical catalyst of modified by silver for degradation of phenol Pending CN108654605A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109603589A (en) * 2019-01-04 2019-04-12 东北师范大学 A kind of Ag@NH2- MIL-125/ polyether sulphone hydridization dense form reactivity ultrafiltration membrane and preparation method thereof
CN109718859A (en) * 2019-01-08 2019-05-07 东北师范大学 A kind of Ag/TiO2/ MIL-125 (Ti) composite material and preparation method and Morphological control
CN111821967A (en) * 2020-07-27 2020-10-27 湖南大学 Heterojunction titanium dioxide composite photocatalyst and preparation method thereof

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WO2013076742A1 (en) * 2011-11-25 2013-05-30 Council Of Scientific & Industrial Research A process for the synthesis of magnetically recoverable, high surface area carbon-fe3o4 nano composite using metal organic framework (mof)
CN105321719A (en) * 2015-11-30 2016-02-10 福州大学 Hierarchical mesoporous TiO2 prepared by taking MOF as precursor and application
CN106611847A (en) * 2017-01-13 2017-05-03 昆明理工大学 Preparation method of titanium-doped nano tungsten oxide negative electrode material

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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109603589A (en) * 2019-01-04 2019-04-12 东北师范大学 A kind of Ag@NH2- MIL-125/ polyether sulphone hydridization dense form reactivity ultrafiltration membrane and preparation method thereof
CN109603589B (en) * 2019-01-04 2021-02-05 东北师范大学 Ag @ NH2-MIL-125/polyarylethersulfone hybridized compact reactive ultrafiltration membrane and preparation method thereof
CN109718859A (en) * 2019-01-08 2019-05-07 东北师范大学 A kind of Ag/TiO2/ MIL-125 (Ti) composite material and preparation method and Morphological control
CN111821967A (en) * 2020-07-27 2020-10-27 湖南大学 Heterojunction titanium dioxide composite photocatalyst and preparation method thereof
CN111821967B (en) * 2020-07-27 2022-11-18 湖南大学 Heterojunction titanium dioxide composite photocatalyst and preparation method thereof

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