CN109603820A - The monatomic method for preparing catalyst of room temperature degradation of formaldehyde under a kind of Oxygen Condition - Google Patents
The monatomic method for preparing catalyst of room temperature degradation of formaldehyde under a kind of Oxygen Condition Download PDFInfo
- Publication number
- CN109603820A CN109603820A CN201910020986.1A CN201910020986A CN109603820A CN 109603820 A CN109603820 A CN 109603820A CN 201910020986 A CN201910020986 A CN 201910020986A CN 109603820 A CN109603820 A CN 109603820A
- Authority
- CN
- China
- Prior art keywords
- tio
- catalyst
- monatomic
- solution
- obtains
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
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
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/38—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
- B01J23/48—Silver or gold
- B01J23/52—Gold
-
- 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
- B01D53/8668—Removing organic compounds not provided for in B01D53/8603 - B01D53/8665
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Environmental & Geological Engineering (AREA)
- Health & Medical Sciences (AREA)
- Organic Chemistry (AREA)
- Materials Engineering (AREA)
- Biomedical Technology (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Catalysts (AREA)
- Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
Abstract
The invention discloses a kind of monatomic method for preparing catalyst of room temperature degradation of formaldehyde under Oxygen Condition, comprising the following steps: (1) hydrogen reducing obtains the defective TiO with surface Lacking oxygen2Carrier;(2) sediment Au/ defect TiO is prepared in deposition-precipitation method2;(3) dry, calcining obtains the monatomic Au/ defect TiO of final product2Catalyst.Compared with existing catalyst, present invention has an advantage that catalyst Au/ defect TiO2High-efficient, the service life is long, and monatomic catalyst has stronger anti-poisoning capability, has very big advantage in degradation of formaldehyde reaction;Using Au/ defect TiO2Monatomic catalyst, being built with conducive to the dispersion between metallic atom for defect, can be realized O2Under the conditions of be detached from ozone auxiliary room-temperature catalytic oxidation.
Description
Technical field
The present invention relates to method for preparing catalyst more particularly to a kind of monatomic catalyst systems of room-temperature catalytic oxidation formaldehyde
Preparation Method.
Background technique
Aldehydes is that one of maximum component of content, formaldehyde are one of the most common type aldehydes in global reactivity VOCs in atmosphere
VOCs, it is one of the main source for controlling the new free radical that ozone is formed.Formaldehyde is mainly derived from VOCs (alcohols and other carbon
Hydrogen compound) oxidative degradation during multiple.In either indoor or outdoor air, formaldehyde is all a kind of preferential pollution
Object, with toxicity and irritation.
Using active carbon, the adsorbents such as aluminium oxide can effectively remove HCHO, but adsorb usually by the limit of adsorption capacity
System, room-temperature catalytic oxidation technology are the most effective technologies of VOCs degradation, which is usually catalysis with metal, metal oxide
Agent is oxidized the formaldehyde under normal temperature conditions in conjunction with strong oxidizing property free radical as CO2、H2O.Compared with conventional catalyst combustion method, often
Warm catalytic oxidation technologies may be implemented in efficient, safety, VOCs exhaust gas of degrading to low energy consumption under the conditions of room temperature (20-50 DEG C).Currently,
The research for having document report room-temperature catalytic oxidation processing formaldehyde, benzene, toluene etc. proposes monatomic urge on this basis
The concept of change, monatomic catalysis, which refers to, is carried on isolated monatomic active site on carrier, realizes that active site is high
Spend a kind of emerging catalysis concept of dispersion.Existing research show monatomic catalysis can significantly reduce catalysis needed for reaction temperature with
Pressure, it is most likely that realize the VOCs constant temperature catalyzing degradation without additional ozone auxiliary.
Currently used various VOCs processing techniques cannot degradation of formaldehyde gas well, be on the one hand easier to cause to urge
Agent inactivation, on the other hand may cause secondary pollution.The monatomic catalytic oxidation technologies of room temperature utilize monatomic work at normal temperature
Property site and O2Double action exhaustive oxidation formaldehyde gas, have easy to operate, safe, high-efficient, catalyst persistently etc. excellent
Point.Compared to carrier nanometer catalyst, monatomic catalyst has many unique advantages, for example, active bit architecture it is uniform,
Metallic atom utilization efficiency can realize maximization, have unique high activity, can link up homogeneously with multiphase etc., these advantages are equal
Be confirmed in early-stage study, the fields such as CO oxidation reaction, Water gas shift/WGS, hydrogenation reaction and electrochemical catalysis all
It is widely used.Experiment and theoretical research show that monatomic high activity of catalyst and selectivity are attributable to active metal original
Interaction and thus caused electronic structure change between son and carrier.Monatomic catalyst surface with higher
Can, it is monatomic more liquid, tend to assemble in catalytic reaction process, influence catalytic activity, currently, existing monatomic
Catalyst, such as Ag/TiO2Also need to realize the degradation of formaldehyde under higher temperature conditions, and easy in inactivation, stability are poor.
Summary of the invention
The purpose of the present invention is to overcome the disadvantages of the prior art, provides room-temperature catalytic oxidation formaldehyde under a kind of Oxygen Condition
Method for preparing catalyst, this method can prepare catalyst at normal temperature, with monatomic catalyst prepared by this method have compared with
Strong monatomic stability, the Degradation Formaldehyde reaction temperature carried out with the monatomic catalyst is low, greatly reduces reaction activation
Can, catalytic efficiency is significantly promoted.
The technical scheme is that
The monatomic method for preparing catalyst of room temperature degradation of formaldehyde under a kind of Oxygen Condition of the invention, including following step
It is rapid:
Step 1: the TiO for being 40-60nm by diameter2Nanometer powder is placed in tube furnace, and gas stream is passed through in tube furnace
Speed is the H of 50-100mL/min2And N2Gaseous mixture, the H2And N2Volume ratio is 1:(18-20), tubular type furnace temperature is adjusted to
200-400 DEG C of heat treatment TiO2Nanometer powder 1.5-2.5h obtains the defective TiO with surface Lacking oxygen2Carrier;
Step 2: firstly, will be the defective TiO of 1:(45-55) with deionized water quality ratio2Carrier suspends
In deionized water, 12-16min is stirred with glass bar, the sal volatile of 0.8-1.2mol/L is added into suspension, obtains
Solution A;
It then, will be the HAuCl of 1:(9.2-11.7) with deionized water quality ratio4·4H2O is dissolved in deionized water, so
After be added dropwise in solution A, obtain solution B, in the solution B, ammonium carbonate and HAuCl4·4H2The ratio between the amount of O substance is
(2-3): 1, the defective TiO2Carrier and HAuCl4·4H2The mass ratio of O is (10-50): 1;
Finally, solution B is stirred 0.8-1.1h at a temperature of -10-50 DEG C, it is collected by filtration with funnel and is formed by precipitating
Precipitating is washed with deionized in object;
Step 3: by the sediment after washing in drying box at 60-80 DEG C dry 3-5h, then in tube furnace in
H is passed through at 200-400 DEG C2And N2Gaseous mixture calcines 1.5-2.5h, wherein H2And N2Volume ratio is 1:(18-20), gas flow rate is
50-100mL/min obtains monatomic Au/ defect TiO2Catalyst.
Present invention has an advantage that catalyst Au/ defect TiO2High-efficient, the service life is long, and monatomic catalyst has stronger
Anti- poisoning capability has very big advantage in degradation of formaldehyde reaction;TiO2As carrier, except having, nontoxic, performance is stable, price
Outside the advantages that cheap, anticorrosive, also as aluminium oxide, there are polymolecularity, high porosity;Using Au/ defect TiO2It is monatomic
Catalyst, being built with conducive to the dispersion between metallic atom for defect, can be realized O2Under the conditions of be detached from ozone auxiliary room temperature
Catalysis oxidation.
Detailed description of the invention
Fig. 1 is that deposition-precipitation method of the present invention prepares Au/ defect TiO2Catalyst process schematic diagram.
Specific embodiment
Below in conjunction with case study on implementation of the present invention, the technical solution in case study on implementation of the present invention is carried out clear, complete
Description, it is clear that described embodiment is only a part of the embodiments of the present invention, instead of all the embodiments.Based on this
The embodiment of invention, every other implementation obtained by those of ordinary skill in the art without making creative efforts
Example, shall fall within the protection scope of the present invention.
Of the invention the reaction mechanism is as follows: compared to complete TiO2Nano particle, the TiO of aerobic vacancy defect2Nanometer
Grain surface forms Ti-Au-Ti structure, has better stability, and due to steric hindrance and electrostatic effect, O2Primary attachment in
HCHO is adsorbed in the site Ti in the site Au, adjacent bit, and this absorption mechanism alleviates HCHO and O2Competition on the same site Au
Absorption, Au is monatomic due to its raised d track center of gravity energy level, to the O of absorption2It is activated, the drop of energy barrier needed for oxidation of formaldehyde
It is low, promote the progress of catalytic process.
Based on the above mechanism, the monatomic catalyst preparation side of room temperature degradation of formaldehyde under a kind of Oxygen Condition of the invention
Method, comprising the following steps:
Step 1: the TiO for being 40-60nm by diameter2Nanometer powder is placed in tube furnace, and gas stream is passed through in tube furnace
Speed is the H of 50-100mL/min2And N2Gaseous mixture, the H2And N2Volume ratio is 1:(18-20), tubular type furnace temperature is adjusted to
200-400 DEG C of heat treatment TiO2Nanometer powder 1.5-2.5h obtains the defective TiO with surface Lacking oxygen2Carrier;
Step 2: firstly, will be the defective TiO of 1:(45-55) with deionized water quality ratio2Carrier suspends
In deionized water, 12-16min is stirred with glass bar, the sal volatile of 0.8-1.2mol/L is added into suspension, obtains
Solution A;
It then, will be the HAuCl of 1:(9.2-11.7) with deionized water quality ratio4·4H2O is dissolved in deionized water, so
After be added dropwise in solution A, obtain solution B, in the solution B, ammonium carbonate and HAuCl4·4H2The ratio between the amount of O substance is
(2-3): 1, the defective TiO2Carrier and HAuCl4·4H2The mass ratio of O is (10-50): 1;
Finally, solution B is stirred 0.8-1.1h at a temperature of -10-50 DEG C, it is collected by filtration with funnel and is formed by precipitating
Precipitating is washed with deionized in object;
Step 3: by the sediment after washing in drying box at 60-80 DEG C dry 3-5h, then in tube furnace in
H is passed through at 200-400 DEG C2And N2Gaseous mixture calcines 1.5-2.5h, wherein H2And N2Volume ratio is 1:(18-20), gas flow rate is
50-100mL/min obtains monatomic Au/ defect TiO2Catalyst.
Embodiment 1
Step 1: the TiO for being 40nm by diameter2Nanometer powder is placed in tube furnace, and gas flow rate is passed through in tube furnace
For the H of 50mL/min2And N2Gaseous mixture, the H2And N2Volume ratio is 1:18, and tubular type furnace temperature is adjusted to 200 DEG C of heat treatments
TiO2Nanometer powder 1.5h obtains the defective TiO with surface Lacking oxygen2Carrier;
Step 2: firstly, by with deionized water quality than the defective TiO for 1:452Carrier is suspended in
In ionized water, 12min is stirred with glass bar, the sal volatile of 0.8mol/L is added into suspension, obtains solution A;
Then, by with deionized water quality than the HAuCl for 1:9.24·4H2O is dissolved in deionized water, is then added dropwise
Enter in solution A, obtains solution B, in the solution B, ammonium carbonate and HAuCl4·4H2The ratio between amount of O substance is 2:1, described
Defective TiO2Carrier and HAuCl4·4H2The mass ratio of O is 10:1;
Finally, solution B is stirred 0.8h at a temperature of -10 DEG C, be collected by filtration with funnel and be formed by sediment, spend from
Sub- water washing precipitating;
Step 3: the sediment after washing to be dried to 3h in drying box at 60 DEG C, then in 200 DEG C in tube furnace
Under be passed through H2And N2Gaseous mixture calcines 1.5h, wherein H2And N2Volume ratio is 1:18, and gas flow rate 50mL/min obtains single original
Sub- Au/ defect TiO2Catalyst.
The evaluation of catalyst oxidation effectiveness carries out in Degradation Formaldehyde reaction unit, and the present embodiment is packed into reactor and is made
Catalyst 1g to be measured, for the reaction of room-temperature catalytic oxidation formaldehyde under Oxygen Condition, reaction condition are as follows: concentration of formaldehyde is
1000mg/m3, air speed 20000h-1, with the concentration of gas chromatograph detection reactants and products.The catalysis of monatomic catalyst
Performance is shown in Table 1.
Embodiment 2
Step 1: the TiO for being 50nm by diameter2Nanometer powder is placed in tube furnace, and gas flow rate is passed through in tube furnace
For the H of 75mL/min2And N2Gaseous mixture, the H2And N2Volume ratio is 1:19, and tubular type furnace temperature is adjusted to 300 DEG C of heat treatments
TiO2Nanometer powder 2h obtains the defective TiO with surface Lacking oxygen2Carrier;
Step 2: firstly, by with deionized water quality than the defective TiO for 1:502Carrier is suspended in
In ionized water, 15min is stirred with glass bar, the sal volatile of 1mol/L is added into suspension, obtains solution A;
Then, by with deionized water quality than the HAuCl for 1:10.54·4H2O is dissolved in deionized water, is then added dropwise
Enter in solution A, obtains solution B, in the solution B, ammonium carbonate and HAuCl4·4H2The ratio between amount of O substance is 2.5:1, institute
The defective TiO stated2Carrier and HAuCl4·4H2The mass ratio of O is 30:1;
Finally, solution B is stirred 1h at a temperature of 20 DEG C, it is collected by filtration with funnel and is formed by sediment, use deionization
Water washing precipitating;
Step 3: the sediment after washing to be dried to 4h in drying box at 70 DEG C, then in 300 DEG C in tube furnace
Under be passed through H2And N2Gaseous mixture calcines 2h, wherein H2And N2Volume ratio is 1:19, and gas flow rate 75mL/min is obtained monatomic
Au/ defect TiO2Catalyst.
The evaluation of catalyst oxidation effectiveness carries out in Degradation Formaldehyde reaction unit, and the present embodiment is packed into reactor and is made
Catalyst 1g to be measured, for the reaction of room-temperature catalytic oxidation formaldehyde under Oxygen Condition, reaction condition are as follows: concentration of formaldehyde is
1000mg/m3, air speed 20000h-1, with the concentration of gas chromatograph detection reactants and products.The catalysis of monatomic catalyst
Performance is shown in Table 1.
Embodiment 3
Step 1: the TiO for being 50nm by diameter2Nanometer powder is placed in tube furnace, and gas flow rate is passed through in tube furnace
For the H of 75mL/min2And N2Gaseous mixture, the H2And N2Volume ratio is 1:18, and tubular type furnace temperature is adjusted to 300 DEG C of heat treatments
TiO2Nanometer powder 2h obtains the defective TiO with surface Lacking oxygen2Carrier;
Step 2: firstly, by with deionized water quality than the defective TiO for 1:502Carrier is suspended in
In ionized water, 15min is stirred with glass bar, the sal volatile of 1mol/L is added into suspension, obtains solution A;
Then, by with deionized water quality than the HAuCl for 1:10.54·4H2O is dissolved in deionized water, is then added dropwise
Enter in solution A, obtains solution B, in the solution B, ammonium carbonate and HAuCl4·4H2The ratio between amount of O substance is 2:1, described
Defective TiO2Carrier and HAuCl4·4H2The mass ratio of O is 30:1;
Finally, solution B is stirred 1h at a temperature of 20 DEG C, it is collected by filtration with funnel and is formed by sediment, use deionization
Water washing precipitating;
Step 3: the sediment after washing to be dried to 4h in drying box at 70 DEG C, then in 300 DEG C in tube furnace
Under be passed through H2And N2Gaseous mixture calcines 2h, wherein H2And N2Volume ratio is 1:18, and gas flow rate 80mL/min is obtained monatomic
Au/ defect TiO2Catalyst.
The evaluation of catalyst oxidation effectiveness carries out in Degradation Formaldehyde reaction unit, and the present embodiment is packed into reactor and is made
Catalyst 1g to be measured, for the reaction of room-temperature catalytic oxidation formaldehyde under Oxygen Condition, reaction condition are as follows: concentration of formaldehyde is
1000mg/m3, air speed 20000h-1, with the concentration of gas chromatograph detection reactants and products.The catalysis of monatomic catalyst
Performance is shown in Table 1.
Embodiment 4
Step 1: the TiO for being 60nm by diameter2Nanometer powder is placed in tube furnace, and gas flow rate is passed through in tube furnace
For the H of 100mL/min2And N2Gaseous mixture, the H2And N2Volume ratio is 1:20, and tubular type furnace temperature is adjusted to 400 DEG C of heat treatments
TiO2Nanometer powder 2.5h obtains the defective TiO with surface Lacking oxygen2Carrier;
Step 2: firstly, by with deionized water quality than the defective TiO for 1:552Carrier is suspended in
In ionized water, 16min is stirred with glass bar, the sal volatile of 1.2mol/L is added into suspension, obtains solution A;
Then, by with deionized water quality than the HAuCl for 1:11.74·4H2O is dissolved in deionized water, is then added dropwise
Enter in solution A, obtains solution B, in the solution B, ammonium carbonate and HAuCl4·4H2The ratio between amount of O substance is 3:1, described
Defective TiO2Carrier and HAuCl4·4H2The mass ratio of O is 50:1;
Finally, solution B is stirred 1.1h at 50 °C, be collected by filtration with funnel and be formed by sediment, spend from
Sub- water washing precipitating;
Step 3: the sediment after washing to be dried to 5h in drying box at 80 DEG C, then in 400 DEG C in tube furnace
Under be passed through H2And N2Gaseous mixture calcines 2.5h, wherein H2And N2Volume ratio is 1:20, and gas flow rate 100mL/min obtains single original
Sub- Au/ defect TiO2Catalyst.
The evaluation of catalyst oxidation effectiveness carries out in Degradation Formaldehyde reaction unit, and the present embodiment is packed into reactor and is made
Catalyst 1g to be measured, for the reaction of room-temperature catalytic oxidation formaldehyde under Oxygen Condition, reaction condition are as follows: concentration of formaldehyde is
1000mg/m3, air speed 20000h-1, with the concentration of gas chromatograph detection reactants and products.The catalysis of monatomic catalyst
Performance is shown in Table 1.
1 Au/ defect TiO of table2Monatomic catalyst oxidation of formaldehyde reactivity worth
Claims (1)
1. the monatomic method for preparing catalyst of room temperature degradation of formaldehyde under a kind of Oxygen Condition, it is characterised in that: including following step
It is rapid:
Step 1: the TiO for being 40-60nm by diameter2Nanometer powder is placed in tube furnace, and gas flow rate is passed through in tube furnace and is
The H of 50-100mL/min2And N2Gaseous mixture, the H2And N2Volume ratio is 1:(18-20), tubular type furnace temperature is adjusted to 200-
400 DEG C of heat treatment TiO2Nanometer powder 1.5-2.5h obtains the defective TiO with surface Lacking oxygen2Carrier;
Step 2: firstly, will be the defective TiO of 1:(45-55) with deionized water quality ratio2Carrier is suspended in
In ionized water, 12-16min is stirred with glass bar, the sal volatile of 0.8-1.2mol/L is added into suspension, obtains solution
A;
It then, will be the HAuCl of 1:(9.2-11.7) with deionized water quality ratio4·4H2O is dissolved in deionized water, is then dripped
It is added in solution A, obtains solution B, in the solution B, ammonium carbonate and HAuCl4·4H2The ratio between amount of O substance is (2-3):
1, the defective TiO2Carrier and HAuCl4·4H2The mass ratio of O is (10-50): 1;
Finally, solution B is stirred 0.8-1.1h at a temperature of -10-50 DEG C, it is collected by filtration with funnel and is formed by sediment, is used
Deionized water washing precipitating;
Step 3: the sediment after washing to be dried to 3-5h in drying box at 60-80 DEG C, then in 200- in tube furnace
H is passed through at 400 DEG C2And N2Gaseous mixture calcines 1.5-2.5h, wherein H2And N2Volume ratio is 1:(18-20), gas flow rate 50-
100mL/min obtains monatomic Au/ defect TiO2Catalyst.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201910020986.1A CN109603820A (en) | 2019-01-09 | 2019-01-09 | The monatomic method for preparing catalyst of room temperature degradation of formaldehyde under a kind of Oxygen Condition |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201910020986.1A CN109603820A (en) | 2019-01-09 | 2019-01-09 | The monatomic method for preparing catalyst of room temperature degradation of formaldehyde under a kind of Oxygen Condition |
Publications (1)
Publication Number | Publication Date |
---|---|
CN109603820A true CN109603820A (en) | 2019-04-12 |
Family
ID=66018459
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201910020986.1A Pending CN109603820A (en) | 2019-01-09 | 2019-01-09 | The monatomic method for preparing catalyst of room temperature degradation of formaldehyde under a kind of Oxygen Condition |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN109603820A (en) |
Cited By (11)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110479342A (en) * | 2019-08-09 | 2019-11-22 | 上海应用技术大学 | A kind of monatomic catalyst of cuprum nickle duplex metal of N-rGO load and its preparation and application |
CN110479372A (en) * | 2019-08-16 | 2019-11-22 | 天津大学 | The atom level method for preparing catalyst that a kind of organic film is carrier room temperature degradation VOCs |
CN110560051A (en) * | 2019-09-26 | 2019-12-13 | 塞文科技(上海)有限公司 | Titanium dioxide modified activated carbon supported silver monatomic catalyst and application thereof in formaldehyde oxidation |
CN111135823A (en) * | 2020-01-14 | 2020-05-12 | 厦门大学 | Wet oxidation catalyst and preparation method and application thereof |
CN111517278A (en) * | 2020-03-24 | 2020-08-11 | 中南大学 | Ti3C2TxApplication of MXenes non-noble metal heterogeneous catalyst in formic acid dehydrogenation |
CN112691660A (en) * | 2020-12-28 | 2021-04-23 | 廊坊市北辰创业树脂材料股份有限公司 | Method for preparing ammonia oxidation catalyst based on deposition precipitation method |
CN112871202A (en) * | 2021-01-11 | 2021-06-01 | 宁波方太厨具有限公司 | Preparation method of catalyst for catalytic decomposition of formaldehyde |
CN113559852A (en) * | 2021-07-23 | 2021-10-29 | 华侨大学 | Hg removal suitable for medium and low temperature conditions0Catalyst and preparation method thereof |
CN114162907A (en) * | 2021-11-30 | 2022-03-11 | 上海交通大学 | Monoatomic electrode and preparation method and application thereof |
CN114602462A (en) * | 2022-03-10 | 2022-06-10 | 北京理工大学 | Defective TiO (titanium dioxide)2Load monatomic noble metal catalyst, preparation method and application thereof |
CN116272991A (en) * | 2023-03-28 | 2023-06-23 | 华中师范大学 | Copper/oxygen-containing vacancy defect titanium dioxide catalyst and preparation method and application thereof |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104492431A (en) * | 2014-12-10 | 2015-04-08 | 青岛农业大学 | Preparation method of Au-Pd/TiO2 NBs photocatalyst |
CN104475089B (en) * | 2014-11-25 | 2017-01-04 | 三明学院 | Universal light source response modifying titanium dioxide solid acid catalyst and preparation method |
CN106622225A (en) * | 2016-12-29 | 2017-05-10 | 天津大学 | Photochemical preparation method of single atom Au for catalytic degradation of VOCs |
CN107115861A (en) * | 2017-05-16 | 2017-09-01 | 嘉兴学院 | A kind of Au TiO2‑xCatalyst and its application |
-
2019
- 2019-01-09 CN CN201910020986.1A patent/CN109603820A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104475089B (en) * | 2014-11-25 | 2017-01-04 | 三明学院 | Universal light source response modifying titanium dioxide solid acid catalyst and preparation method |
CN104492431A (en) * | 2014-12-10 | 2015-04-08 | 青岛农业大学 | Preparation method of Au-Pd/TiO2 NBs photocatalyst |
CN106622225A (en) * | 2016-12-29 | 2017-05-10 | 天津大学 | Photochemical preparation method of single atom Au for catalytic degradation of VOCs |
CN107115861A (en) * | 2017-05-16 | 2017-09-01 | 嘉兴学院 | A kind of Au TiO2‑xCatalyst and its application |
Non-Patent Citations (1)
Title |
---|
JIAWEI WAN 等: "Defect Effects on TiO2 Nanosheets: Stabilizing Single Atomic Site Au and Promoting Catalytic Properties", 《ADVANCED MATERIALS》 * |
Cited By (15)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110479342A (en) * | 2019-08-09 | 2019-11-22 | 上海应用技术大学 | A kind of monatomic catalyst of cuprum nickle duplex metal of N-rGO load and its preparation and application |
CN110479342B (en) * | 2019-08-09 | 2023-04-28 | 上海应用技术大学 | N-rGO supported copper-nickel bimetallic single-atom catalyst and preparation and application thereof |
CN110479372B (en) * | 2019-08-16 | 2022-04-29 | 天津大学 | Preparation method of atomic-scale catalyst for normal-temperature degradation of VOCs (volatile organic compounds) by taking organic film as carrier |
CN110479372A (en) * | 2019-08-16 | 2019-11-22 | 天津大学 | The atom level method for preparing catalyst that a kind of organic film is carrier room temperature degradation VOCs |
CN110560051A (en) * | 2019-09-26 | 2019-12-13 | 塞文科技(上海)有限公司 | Titanium dioxide modified activated carbon supported silver monatomic catalyst and application thereof in formaldehyde oxidation |
CN111135823A (en) * | 2020-01-14 | 2020-05-12 | 厦门大学 | Wet oxidation catalyst and preparation method and application thereof |
CN111135823B (en) * | 2020-01-14 | 2021-06-11 | 厦门大学 | Wet oxidation catalyst and preparation method and application thereof |
CN111517278A (en) * | 2020-03-24 | 2020-08-11 | 中南大学 | Ti3C2TxApplication of MXenes non-noble metal heterogeneous catalyst in formic acid dehydrogenation |
CN112691660A (en) * | 2020-12-28 | 2021-04-23 | 廊坊市北辰创业树脂材料股份有限公司 | Method for preparing ammonia oxidation catalyst based on deposition precipitation method |
CN112871202A (en) * | 2021-01-11 | 2021-06-01 | 宁波方太厨具有限公司 | Preparation method of catalyst for catalytic decomposition of formaldehyde |
CN113559852A (en) * | 2021-07-23 | 2021-10-29 | 华侨大学 | Hg removal suitable for medium and low temperature conditions0Catalyst and preparation method thereof |
CN113559852B (en) * | 2021-07-23 | 2023-10-31 | 华侨大学 | Hg removing device suitable for medium and low temperature conditions 0 Catalyst and preparation method thereof |
CN114162907A (en) * | 2021-11-30 | 2022-03-11 | 上海交通大学 | Monoatomic electrode and preparation method and application thereof |
CN114602462A (en) * | 2022-03-10 | 2022-06-10 | 北京理工大学 | Defective TiO (titanium dioxide)2Load monatomic noble metal catalyst, preparation method and application thereof |
CN116272991A (en) * | 2023-03-28 | 2023-06-23 | 华中师范大学 | Copper/oxygen-containing vacancy defect titanium dioxide catalyst and preparation method and application thereof |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN109603820A (en) | The monatomic method for preparing catalyst of room temperature degradation of formaldehyde under a kind of Oxygen Condition | |
TWI826408B (en) | A catalyst for catalyzing formaldehyde oxidation and the preparation and use of the same | |
CN104646029B (en) | A kind of metal alloy catalyst for purifying formaldehyde and preparation method thereof | |
CN109248679B (en) | VOCs normal-temperature degradation efficient catalyst and preparation and application thereof | |
CN107159202B (en) | Manganese-doped palladium supported catalyst and preparation method and application thereof | |
WO2015149499A1 (en) | Low-temperature and highly efficient denitration catalyst and preparation method therefor | |
CN106732572A (en) | A kind of scavenging material of gaseous contaminant and its preparation method and application | |
CN104607240A (en) | Bi/g-C3N4 semimetal-organic composite photocatalyst and preparation method | |
CN108816233A (en) | A kind of preparation method of the copper-cobalt composite oxide catalysts for benzene catalysis oxidation | |
CN108176396A (en) | A kind of formaldehyde remover and its preparation method and application | |
CN106964348A (en) | A kind of formaldehyde pollutants room temperature catalytic oxidation catalyst and its preparation method and application | |
CN104174425B (en) | It is a kind of for catalyst of volatile organic matter catalysis oxidation and preparation method thereof | |
CN103599774A (en) | Pt/Al2O3 catalyst and application thereof in room-temperature catalytic oxidation of formaldehyde | |
CN108187690A (en) | A kind of cobalt manganese composite oxide loaded catalyst that formaldehyde is removed for room temperature and preparation method thereof | |
CN108479762A (en) | A kind of manganese oxide catalyst and its preparation method and application | |
CN114618589A (en) | Preparation method and application of ozone degradation catalyst based on iron-based organic framework | |
CN108069497A (en) | A kind of method of catalytic wet oxidation processing organic wastewater | |
CN113976115B (en) | Layered core-shell structured catalyst, preparation method and application of catalyst in low-temperature catalytic oxidation of toluene | |
CN113385184B (en) | Mn-Co-La composite catalyst for catalyzing and degrading VOCs (volatile organic compounds) by synergistic discharge plasma and preparation method and application thereof | |
CN101693193A (en) | Rare earth-Cu-Fe active carbon adsorbent, preparation method and application thereof | |
CN109433251B (en) | Bi-component supported catalyst for olefin catalytic combustion process and preparation and application thereof | |
CN108069495A (en) | A kind of catalytic wet oxidation processing method of organic wastewater | |
CN107552045A (en) | Preparation method for the catalyst of catalytic combustion volatility organic compound | |
CN104043460A (en) | Preparation method for nickel oxide loaded palladium catalyst and application to room-temperature CO catalytic oxidation | |
CN114471695A (en) | Catalyst capable of efficiently degrading cyanogen-containing waste gas 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 |