CN106669668A - Catalyst for ammonia odor gas purification as well as preparation method and application of catalyst - Google Patents

Catalyst for ammonia odor gas purification as well as preparation method and application of catalyst Download PDF

Info

Publication number
CN106669668A
CN106669668A CN201710035247.0A CN201710035247A CN106669668A CN 106669668 A CN106669668 A CN 106669668A CN 201710035247 A CN201710035247 A CN 201710035247A CN 106669668 A CN106669668 A CN 106669668A
Authority
CN
China
Prior art keywords
catalyst
presoma
solution
auxiliary agent
active component
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
Application number
CN201710035247.0A
Other languages
Chinese (zh)
Other versions
CN106669668B (en
Inventor
欧阳李科
陈耀壮
李洁
王磊
乔莎
张云贤
雷菊梅
赵英
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Hao Hua Chengdu Technology Co ltd
Original Assignee
Southwest Research and Desigin Institute of Chemical Industry
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Southwest Research and Desigin Institute of Chemical Industry filed Critical Southwest Research and Desigin Institute of Chemical Industry
Priority to CN201710035247.0A priority Critical patent/CN106669668B/en
Publication of CN106669668A publication Critical patent/CN106669668A/en
Application granted granted Critical
Publication of CN106669668B publication Critical patent/CN106669668B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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
    • B01J23/002Mixed oxides other than spinels, e.g. perovskite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/8668Removing organic compounds not provided for in B01D53/8603 - B01D53/8665
    • 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
    • B01J23/54Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/56Platinum group metals
    • B01J23/64Platinum group metals with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/648Vanadium, niobium or tantalum or polonium
    • B01J23/6482Vanadium
    • 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
    • B01J23/54Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/56Platinum group metals
    • B01J23/64Platinum group metals with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/652Chromium, molybdenum or tungsten
    • B01J23/6527Tungsten
    • 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
    • B01J23/54Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/56Platinum group metals
    • B01J23/64Platinum group metals with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/656Manganese, technetium or rhenium
    • B01J23/6562Manganese
    • 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
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/89Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals
    • B01J23/8906Iron and noble metals
    • 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
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/89Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals
    • B01J23/8933Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals also combined with metals, or metal oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/8986Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals also combined with metals, or metal oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with manganese, technetium or rhenium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/70Organic compounds not provided for in groups B01D2257/00 - B01D2257/602
    • B01D2257/708Volatile organic compounds V.O.C.'s
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2523/00Constitutive chemical elements of heterogeneous catalysts

Abstract

The invention provides a catalyst for ammonia odor gas purification as well as a preparation method and an application of the catalyst and solves the problems that a catalyst has high ignition temperature and low activity, cannot generate N2, CO2 and H2O with high selectivity, and produces secondary pollution in the prior art. The active component of the catalyst is any one or more of Pd, Pt, Au and Ru, and the content is 0.01wt%-5wt% based on the single metal element; the auxiliary agent is a binary or multicomponent composite oxide of Ti, V, W, Mn, Fe and Ce, and the content is 1wt%-40wt% based on the oxide; the remaining component is a catalyst carrier Al2O3. After an aid is supported on a catalyst carrier with a mixing kneading method, a co-current co-precipitation method or a sol-gel method, drying and calcination are performed, and a modified carrier is obtained; the active component is supported on the modified carrier with an impregnation method, drying and calcination are performed, and the catalyst is obtained.

Description

A kind of catalyst for amine odor purification and its preparation method and application
Technical field
The invention belongs to field of gas purification, specially a kind of catalyst for amine odor purification and preparation method thereof And application.
Background technology
Nitrogenous volatile organic matter (predominantly amine gas) is widely present in rubbish as one of the main component of foul smell In all kinds of waste gas in the fields such as landfill gas, biofermentation, food, sewage disposal, leather chemical industry.Because its is volatile and zest Abnormal smells from the patient is strong, very easily to environment.Clear stipulaties have all been done in country and place to the discharge standard of amine gas.Mesh The method of pre-treatment amine foul smell includes absorption method, chemical oxidization method, bioanalysises, plasma method, combustion method and catalysis burning Method etc.., mainly using activated carbon, active hargil etc. as adsorbent, removal efficiency is high, but it is little, easy to there is adsorption capacity for absorption method Secondary pollution is caused, the shortcomings of changing adsorbent and fixed-end forces is needed;Chemical oxidization method removal efficiency is high, but needs using high The strong oxidizers such as potassium manganate, efficiency is low, is also easy to produce secondary pollution;Bioanalysises process is simple, operating cost are low, secondary pollution is little, But more harsh, time of staying requirement length is required place, operating condition, and equipment volume is big, purification speed is slow;Plasma method Process is simple, easy to maintenance, energy consumption is low, more more cost-effective than traditional method, but treating capacity is less, and power supply is had high demands, easily Produce nitrogen oxides (NOx) and ozone (O3) etc. secondary pollution;Conventional heat combustion method is high due to ignition temperature, is also easy to produce NOx, Cause secondary pollution.Catalytic combustion technology has treatment effeciency high, and ignition temperature is low, suppresses nitrogen over oxidation to generate NOx The advantages of, have a high potential.
Patent CN105107503A discloses a kind of loaded catalyst for amine waste gas burning, using spherical alumina Aluminum loads copper sulfate, is obtained after drying calcining, can efficiently remove dimethylamine, trimethylamine.But the catalyst reaction temperatures compared with Height, may produce NO in course of reactionx, cause secondary pollution.
Therefore, initiation temperature is researched and developed low, activity height can catalytic amine type organic high selectivity generation N2、CO2And H2The height of O Performance amine selective catalyst combustion catalyst, becomes those skilled in the art's problem demanding prompt solution.
The content of the invention
The invention provides a kind of catalyst for amine odor purification, for catalysis burning removing amine Organic substance; The catalyst light-off temperature is low, and activity is high, can catalytic amine type organic high selectivity generation N2、CO2And H2O, significantly inhibits NOx Produce, it is to avoid secondary pollution.
The invention provides a kind of preparation method of the catalyst for amine odor purification.
Present invention also offers a kind of application of the catalyst for amine odor purification.
The technical solution used in the present invention is as follows:
The invention provides a kind of catalyst for amine odor purification, including catalyst carrier, active component and help Agent, the gross mass percentage composition sum of catalyst is 100%;Active component is any one or more in Pd, Pt, Au, Ru, living The content of property component accounts for 0.01~5wt% of catalyst in terms of metal simple-substance;Auxiliary agent for Ti, V, W, Mn, Fe, Ce binary or Multicomponent composite oxide, the content of auxiliary agent accounts for 1~40wt% of catalyst in terms of oxide;Remaining component is catalyst load Body, catalyst carrier is Al2O3
Preferably, the presoma of active component is nitrate, chloride or the acetate of active component.
Preferably, in auxiliary agent, the presoma of V is ammonium metavanadate, and the presoma of Ti is the nano oxidized of 25~50nm of particle diameter Titanium powder, titanyl sulfate or tetrabutyl titanate, the presoma of W is ammonium metatungstate, and the presoma of Mn is manganese nitrate or manganese carbonate, Fe Presoma be ferric nitrate or ferric ammonium citrate, the presoma of Ce is cerous nitrate or cerous carbonate.
Preferably, Al2O3Any one in activated alumina, boehmite, the aluminum nitrate of presoma.
Present invention also offers a kind of preparation method of the catalyst for amine odor purification, the method includes following step Suddenly:
Step 1:Auxiliary agent is carried on by catalysis using a kind of method in kneading method, co-precipitation method or sol-gal process After agent carrier, in 110~120 DEG C of 4~12h of drying, 300~600 DEG C of 3~5h of calcining, modified support is obtained;
Step 2:Active component is carried on step 1 gained modified support using infusion process, in 110~120 DEG C of dryings 4 After~12h, then at 300~600 DEG C of 3~5h of calcining, catalyst is obtained.
Further, in step 1, add molding during auxiliary agent is carried on into catalyst carrier using kneading method and help Agent, the method is comprised the following steps:It is molten that one or more in the presoma of selection auxiliary agent V, W, Mn, Fe, Ce is configured to auxiliary agent Liquid;Take and add compounding agent solution after nano oxidized titanium powder or the one kind in manganese carbonate, boehmite, shaping assistant mix homogeneously In, mix homogeneously mediates extruded moulding;Shaping assistant is any one in sesbania powder, attapulgite, sheep Montmorillonitum, Kaolin Kind, addition is 1~3wt% of catalyst.
Further, in step 1, auxiliary agent is carried on by catalyst carrier using co-precipitation method, is comprised the following steps: Choose in the presoma of auxiliary agent Ti, V, W, Mn, Fe, Ce any two or it is various, and aluminum nitrate is configured to mixed aqueous solution;Match somebody with somebody Sodium carbonate, potassium carbonate or ammonia spirit are put, as precipitant solution;Using simultaneously stream mode while Deca mixed aqueous solution and precipitation Agent solution in the container for filling water, generate precipitation, during be kept stirring for, control pH=9~10, into change 4~18h;Gained Precipitate with deionized water is washed 3~5 times, sucking filtration.
Further, in step 1, auxiliary agent is carried on by catalyst carrier using sol-gal process, is comprised the following steps:Take One or more in one kind, the presoma of auxiliary agent V, W, Mn, Fe, Ce in citric acid or oxalic acid, aluminum nitrate be added to quality Than for 1:In 1 alcoholic solvent, mixed solution A is obtained, butyl titanate is dissolved in into dehydrated alcohol and obtains mixed solution B, will be mixed Close solution A to be slowly dropped in mixed solution B, stirring is not stopped under room temperature, then evaporate solution in 60~90 DEG C of water-bath, formed Gel.
Further, infusion process is comprised the following steps in step 2:In choosing active component Pd, Pt, the presoma of Au, Ru One or more, be configured to mixed aqueous solution or alcoholic solution, obtain active component precursor solution;Using equi-volume impregnating, Step 1 gained modified support is impregnated into 8~12h in active component precursor solution, active component is carried on into step 1 gained On modified support.
The invention provides the application of amine odor purification catalyst, it is characterised in that:Using fixed bed reactors, air speed For 1000~20000h-1, reaction temperature is 150~350 DEG C, and methylamine content is 100~10000mg/Nm in amine foul smell3, amine Ammonia concentration is 100~10000mg/Nm in class foul smell3
Compared with prior art, beneficial effects of the present invention:
Using catalyst of the present invention, amine Organic substance can be effectively removed, catalytic amine type organic high selectivity generates N2、 CO2And H2O, significantly inhibits NOxProduce, it is to avoid secondary pollution.Initiation temperature of the present invention is low, and activity is high, and preparation method is simple.
Specific embodiment
The foregoing invention content of the present invention is described in further detail with reference to specific embodiment.But should not be by This scope for being interpreted as above-mentioned theme of the invention is only limitted to following embodiments.Raw material derives from commercially available in embodiment.
Embodiment 1-7 is catalyst carrier preparation.
Embodiment 1:
Weigh the ammonium metavanadate 1.28g 60mL that add water and be configured to compounding agent solution.Weigh boehmite 138g, titanium dioxide powder 9g, after sesbania powder 2g mix homogeneously, in adding compounding agent solution, mix homogeneously mediates extruded moulding, 110~120 DEG C of dryings of Jing 8h, 300 DEG C of calcining 4h, is obtained the VTiO of V, Ti oxide total content 10%x/Al2O3Carrier.
Embodiment 2:
Weigh ammonium metavanadate 1.28g, the ammonium metatungstate 12g 60mL that add water are configured to compounding agent solution.Weigh boehmite 92g, titanium dioxide powder 29g, after sesbania powder 2g mix homogeneously, in adding compounding agent solution, mix homogeneously mediates extruded moulding, Jing 110~120 DEG C are dried 8h, 500 DEG C of calcining 4h, and the VWTiO of V, W, Ti oxide total content 40% is obtainedx/Al2O3Carrier.
Embodiment 3:
Weigh the cerous nitrate 25.2g 60mL that add water and be configured to compounding agent solution.Boehmite 107g, manganese carbonate 29.1g are weighed, After sesbania powder 2g mix homogeneously, in adding compounding agent solution, mix homogeneously mediates extruded moulding, and 110~120 DEG C of Jing is dried 8h, 500 DEG C of calcining 4h, are obtained the MnCeO of Mn, Ce oxide total content 30%x/Al2O3Carrier.
Embodiment 4:
Weigh cerous nitrate 12.6g, the manganese nitrate 45.3g 40mL that add water are configured to compounding agent solution.Boehmite 107g is weighed, Titanium dioxide powder 15g, after sesbania powder 2g mix homogeneously, in adding compounding agent solution, mix homogeneously, kneading extruded moulding, Jing 110~ 120 DEG C are dried 8h, 500 DEG C of calcining 4h, and the MnCeTiO of Mn, Ce oxide total content 30% is obtainedx/Al2O3Carrier.
Embodiment 5:
Weigh the ferric nitrate 10.1g 60mL that add water and be configured to compounding agent solution.Weigh boehmite 122g, titanium dioxide powder 18g, after sesbania powder 2g mix homogeneously, in adding compounding agent solution, mix homogeneously mediates extruded moulding, 110~120 DEG C of dryings of Jing 8h, 400 DEG C of calcining 4h, is obtained the FeTiO of Fe, Ti oxide total content 20%x/Al2O3Carrier.
Embodiment 6:
Manganese nitrate 45.3g is weighed, cerous nitrate 12.6g, ferric nitrate 25.3g, aluminum nitrate 589g are dissolved in 1000ml water to be mixed Solution is closed, the sodium carbonate liquor of another configuration 0.35mol/L delays mixed solution and sodium carbonate liquor under room temperature, stirring condition Slow addition is pre-loaded with the container of 500mL water, while adjusting pH=9~10.Stir in air at room temperature after completion of dropping Change 10h, filtration washing, repetitive operation 3~5 times, 110~120 DEG C of Jing is dried 12h, 500 DEG C of calcining 3h, prepared Fe, Mn, The FeMnCeO of Ce oxides total content 20%x/Al2O3Carrier.
Embodiment 7:
Configuration quality ratio is 1:1 water-ethanol mixed solvent, weigh ferric nitrate 5g, manganese nitrate 4.5g, aluminum nitrate 114g, Citric acid 62g is dissolved in 250ml mixed solvents and obtains solution A, 98ml butyl titanates is dissolved in 200ml ethanol and obtains solution B, solution A is slowly dropped in solution B, and stirring is not stopped under room temperature, and solution is then evaporated in 60 DEG C of water-bath, forms gel, Again 110~120 DEG C of Jing is dried 12h, 500 DEG C of calcining 3h, and the FeMnTiO of Fe, Mn, Ti oxide total content 25% is obtainedx/Al2O3 Carrier.
Embodiment 8-11 is catalyst preparation and performance test.
Embodiment 8:
Weigh six hydration chloroplatinic acid 0.267g and add water and be configured to 100ml aqueous solutions, 10ml platinum acid chloride solutions are taken respectively, altogether 7 parts, per part adds 90ml water to obtain chloroplatinic acid diluent, and the carrier immersion chloroplatinic acid for respectively obtaining 100g embodiments 1-7 is dilute Release and keep in liquid 8h, then 110~120 DEG C are dried 12h, 600 DEG C of calcining 4h, respectively obtain catalyst Pt/VTiOx/Al2O3、 Pt/VWTiOx/Al2O3、Pt/MnCeOx/Al2O3、Pt/MnCeTiOx/Al2O3、Pt/FeTiOx/Al2O3、Pt/FeMnCeOx/ Al2O3、Pt/FeMnTiOx/Al2O3, Pt load capacity is 0.01%.
Above-mentioned catalyst is placed in fixed bed reactors respectively, volume space velocity 1000h-1, 150 DEG C of reaction temperature, front three Amine concentration 100mg/Nm3, ammonia concentration 100mg/Nm3, remaining is air.The results are shown in Table 1.
Catalyst removal methylamine performance described in the embodiment 8 of table 1
Note:N.d. represent and be not detected by.
As shown in Table 1, using catalyst of the present invention, amine Organic substance can be effectively removed, initiation temperature of the present invention is low, Jing The air crossed after the de- amine of catalyst of the present invention is processed, methylamine concentration is less than 0.5mg/Nm3And generation NOxConcentration is less than 10mg/Nm3
Embodiment 9:
Palladium 0.21g is weighed, acetic acid gold 0.095g is dissolved in 100ml ethanol, mixed solution is obtained, by 99.85g embodiments The 6 carrier immersion mixed solutions for obtaining keep 10h, and 12h, 450 DEG C of calcining 4h are then dried in 110~120 DEG C, obtain catalyst Pd-Au/FeMnTiOx/Al2O3, PdAu load capacity is 0.15%.The catalyst is placed in fixed bed reactors, volume space velocity 20000h-1, 250 DEG C of reaction temperature, trimethylamine 1000mg/Nm3, ammonia concentration 1000mg/Nm3, remaining is air, three after reaction Methylamine concentration is less than 0.1mg/Nm3And generation NOxConcentration is less than 10mg/Nm3
Embodiment 10:
Chloride hydrate ruthenium 1.3g is weighed, Palladous chloride. 1.05g is dissolved in the dilute hydrochloric acid that 100ml concentration is 1%, must mix molten Liquid, in the carrier immersion mixed solution that 99g embodiments 5 are obtained 12h is kept, and then 110~120 DEG C are dried 12h, and 400 DEG C are forged 4h is burnt, catalyst Pd-Ru/FeTiO is obtainedx/Al2O3, PdAu load capacity is 1%.The catalyst is placed in into fixed bed reactors It is interior, volume space velocity 10000h-1, 350 DEG C of reaction temperature, trimethylamine 5000mg/Nm3, ammonia concentration 5000mg/Nm3, remaining is sky Gas, methylamine concentration is less than 0.1mg/Nm after reaction3And generation NOxConcentration is less than 10mg/Nm3
Embodiment 11:
Palladous chloride. 8.33g is weighed, obtained solution in 100ml dilute hydrochloric acid solutions, the carrier that 95g embodiments 5 are obtained is added 12h is kept in immersion mixed solution, then 110~120 DEG C are dried 12h, 400 DEG C of calcining 4h, obtain catalyst Pd/MnCeOx/ Al2O3, Pd load capacity is 5%.The catalyst is placed in fixed bed reactors, volume space velocity 15000h-1, reaction temperature 280 DEG C, methylamine concentration is 10000ppm, ammonia concentration 10000ppm, and methylamine concentration is less than 0.1mg/Nm after reaction3And generation NOxIt is dense Degree is less than 10mg/Nm3
To sum up, catalyst light-off temperature of the present invention is low, and activity is high, can catalytic amine type organic high selectivity generation N2、CO2 And H2O, significantly inhibits NOxProduce, it is to avoid secondary pollution.
Above-described embodiment is only one of the preferred embodiment of the present invention, should not be taken to limit the protection model of the present invention Enclose, as long as the body design thought and the change or polishing of having no essential meaning mentally made in the present invention, it is solved Technical problem still with this with new consistent, should be included within protection scope of the present invention.

Claims (10)

1. a kind of catalyst for amine odor purification, it is characterised in that:The catalyst includes catalyst carrier, activearm Divide and auxiliary agent, the gross mass percentage composition sum of the catalyst is 100%;
The active component is any one or more in Pd, Pt, Au, Ru, and its content accounts for the catalyst in terms of metal simple-substance 0.01~5wt%;
The auxiliary agent is the binary or multicomponent composite oxide of Ti, V, W, Mn, Fe, Ce, and its content accounts for described urging in terms of oxide 1~40wt% of agent;
Remaining component is the catalyst carrier, and the catalyst carrier is Al2O3
2. a kind of catalyst for amine odor purification according to claim 1, it is characterised in that:The active component Presoma be the active component nitrate, chloride or acetate.
3. a kind of catalyst for amine odor purification according to claim 1, it is characterised in that:In the auxiliary agent, The presoma of the V is ammonium metavanadate, and the presoma of the Ti is nano oxidized titanium powder, the titanyl sulfate of 25~50nm of particle diameter Or tetrabutyl titanate, the presoma of the W is ammonium metatungstate, and the presoma of the Mn is manganese nitrate or manganese carbonate, the Fe's Presoma is ferric nitrate or ferric ammonium citrate, and the presoma of the Ce is cerous nitrate or cerous carbonate.
4. a kind of catalyst for amine odor purification according to claim 1, it is characterised in that:The Al2O3Before Drive any one of body in activated alumina, boehmite, aluminum nitrate.
5. the preparation method of a kind of catalyst for amine odor purification according to any one of claim 1-4, it is special Levy and be:The method is comprised the following steps:
Step 1:The auxiliary agent is carried on using a kind of method in kneading method, co-precipitation method or sol-gal process described After catalyst carrier, in 110~120 DEG C of 4~12h of drying, 300~600 DEG C of 3~5h of calcining, modified support is obtained;
Step 2:The active component is carried on step 1 gained modified support using infusion process, in 110~120 DEG C of dryings 4 After~12h, then at 300~600 DEG C of 3~5h of calcining, the catalyst is obtained.
6. preparation method according to claim 5, it is characterised in that:In the step 1, will be described using the kneading method Auxiliary agent adds shaping assistant during being carried on the catalyst carrier, the method is comprised the following steps:Help described in choosing One or more in the presoma of agent V, W, Mn, Fe, Ce is configured to compounding agent solution;Take the nano oxidized titanium powder or described Add in the compounding agent solution after a kind of, described boehmite, the shaping assistant mix homogeneously in manganese carbonate, mixing is equal It is even, mediate extruded moulding;Any one of the shaping assistant in sesbania powder, attapulgite, sheep Montmorillonitum, Kaolin, plus Enter 1~3wt% that amount is the catalyst.
7. preparation method according to claim 5, it is characterised in that:In the step 1, using the co-precipitation method The auxiliary agent is carried on into the catalyst carrier, is comprised the following steps:Choose the forerunner of described auxiliary agent Ti, V, W, Mn, Fe, Ce In body any two or it is various, and the aluminum nitrate is configured to mixed aqueous solution;Configuration sodium carbonate, potassium carbonate or ammonia are molten Liquid, as precipitant solution;Using and stream mode simultaneously mixed aqueous solution described in Deca and the precipitant solution in filling water Container in, generate precipitation, during be kept stirring for, control pH=9~10, into change 4~18h;Gained precipitate with deionized water Washing 3~5 times, sucking filtration.
8. preparation method according to claim 4, it is characterised in that:In the step 1, will using the sol-gal process The auxiliary agent is carried on the catalyst carrier, comprises the following steps:Take citric acid or a kind of, the described auxiliary agent V in oxalic acid, W, One or more in the presoma of Mn, Fe, Ce, the aluminum nitrate be added to mass ratio for 1:In 1 alcoholic solvent, it is obtained mixed Solution A is closed, butyl titanate is dissolved in into dehydrated alcohol and is obtained mixed solution B, the mixed solution A is slowly dropped into into the mixing molten In liquid B, stirring is not stopped under room temperature, solution is then evaporated in 60~90 DEG C of water-bath, form gel.
9. preparation method according to claim 4, it is characterised in that:Infusion process described in the step 2 includes following step Suddenly:One or more in the presoma of active component Pd, Pt, Au, Ru is chosen, mixed aqueous solution is configured to or alcohol is molten Liquid, obtains active component precursor solution;Using equi-volume impregnating, by step 1 gained modified support before the active component Drive and impregnate in liquid solution 8~12h, the active component is carried on step 1 gained modified support.
10. according to right 1 amine odor purification catalyst application, it is characterised in that:Using fixed bed reactors, air speed For 1000~20000h-1, reaction temperature is 150~350 DEG C, and methylamine content is 100~10000mg/ in the amine foul smell Nm3, ammonia concentration is 100~10000mg/Nm in the amine foul smell3
CN201710035247.0A 2017-01-17 2017-01-17 A kind of catalyst and its preparation method and application for amine odor purification Expired - Fee Related CN106669668B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710035247.0A CN106669668B (en) 2017-01-17 2017-01-17 A kind of catalyst and its preparation method and application for amine odor purification

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710035247.0A CN106669668B (en) 2017-01-17 2017-01-17 A kind of catalyst and its preparation method and application for amine odor purification

Publications (2)

Publication Number Publication Date
CN106669668A true CN106669668A (en) 2017-05-17
CN106669668B CN106669668B (en) 2019-02-19

Family

ID=58860112

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710035247.0A Expired - Fee Related CN106669668B (en) 2017-01-17 2017-01-17 A kind of catalyst and its preparation method and application for amine odor purification

Country Status (1)

Country Link
CN (1) CN106669668B (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107983346A (en) * 2017-12-04 2018-05-04 合肥神舟催化净化器股份有限公司 A kind of preparation method of noble metal-base metal mixed catalyst
CN109847746A (en) * 2019-03-11 2019-06-07 浙江师范大学 A kind of catalyst and preparation method thereof for itrogenous organic substance purification
CN110681398A (en) * 2019-10-25 2020-01-14 西南化工研究设计院有限公司 Noble metal catalyst for purifying carbon dioxide gas and preparation and application thereof
CN110935470A (en) * 2019-11-25 2020-03-31 北京化工大学 Preparation method of exhaust gas purification catalyst
CN111215048A (en) * 2020-03-02 2020-06-02 中自环保科技股份有限公司 Ozone purification catalyst and preparation method and application thereof
CN111617735A (en) * 2020-05-27 2020-09-04 青岛华世洁环保科技有限公司 Amine odor removal material
CN113996291A (en) * 2021-11-09 2022-02-01 康纳新型材料(杭州)有限公司 Low-temperature HVOCs catalytic combustion catalyst, and preparation method and application thereof
CN114515586A (en) * 2022-02-25 2022-05-20 金华铂锐催化科技有限公司 Catalyst for purifying volatile organic compounds and preparation method thereof

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS57119819A (en) * 1981-01-17 1982-07-26 Takeda Chem Ind Ltd Treatment of gas
CN101371985A (en) * 2007-08-23 2009-02-25 中国石油化工股份有限公司 Catalyst for removing trace amounts of CO as well as preparation method and use thereof

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS57119819A (en) * 1981-01-17 1982-07-26 Takeda Chem Ind Ltd Treatment of gas
CN101371985A (en) * 2007-08-23 2009-02-25 中国石油化工股份有限公司 Catalyst for removing trace amounts of CO as well as preparation method and use thereof

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
HE JUNJUN ET AL.: "The Effect of pH on the Soot Elimination Performance of Pt/CeO2-TiO2-Al2O3", 《贵金属》 *
李翔 等: "CeO2对Pt/TiO2-Al2O3催化剂氧化及抗老化性能的影响", 《稀有金属》 *

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107983346A (en) * 2017-12-04 2018-05-04 合肥神舟催化净化器股份有限公司 A kind of preparation method of noble metal-base metal mixed catalyst
CN109847746A (en) * 2019-03-11 2019-06-07 浙江师范大学 A kind of catalyst and preparation method thereof for itrogenous organic substance purification
CN110681398A (en) * 2019-10-25 2020-01-14 西南化工研究设计院有限公司 Noble metal catalyst for purifying carbon dioxide gas and preparation and application thereof
CN110935470A (en) * 2019-11-25 2020-03-31 北京化工大学 Preparation method of exhaust gas purification catalyst
CN111215048A (en) * 2020-03-02 2020-06-02 中自环保科技股份有限公司 Ozone purification catalyst and preparation method and application thereof
CN111617735A (en) * 2020-05-27 2020-09-04 青岛华世洁环保科技有限公司 Amine odor removal material
CN111617735B (en) * 2020-05-27 2022-07-05 青岛华世洁环保科技有限公司 Amine odor removal material
CN113996291A (en) * 2021-11-09 2022-02-01 康纳新型材料(杭州)有限公司 Low-temperature HVOCs catalytic combustion catalyst, and preparation method and application thereof
CN114515586A (en) * 2022-02-25 2022-05-20 金华铂锐催化科技有限公司 Catalyst for purifying volatile organic compounds and preparation method thereof

Also Published As

Publication number Publication date
CN106669668B (en) 2019-02-19

Similar Documents

Publication Publication Date Title
CN106669668B (en) A kind of catalyst and its preparation method and application for amine odor purification
CN105597777B (en) A kind of ordered mesopore carbon loaded Cu-Mn bimetallic denitration catalysts and preparation method thereof
CN104785302B (en) Denitrifying catalyst with selective catalytic reduction and its preparation method and application
CN107159202B (en) Manganese-doped palladium supported catalyst and preparation method and application thereof
CN102824909B (en) Catalyst for low-temperature catalytic combustion of volatile organic compounds and preparation method thereof
CN107824177A (en) A kind of CeO using Ce MOF as cerium precursor2/TiO2The preparation method of low-temperature SCR catalyst
CN106179440A (en) N doping multi-stage porous charcoal and its preparation method and application
CN105833901B (en) A kind of PrOx-MnOx/ SAPO-34 low-temperature SCR catalyst for denitrating flue gas and the preparation method and application thereof
CN108816233A (en) A kind of preparation method of the copper-cobalt composite oxide catalysts for benzene catalysis oxidation
CN105289651A (en) Bimetallic catalyst for catalytic oxidation of VOCs and preparation method and application of bimetallic catalyst
JP2001293480A (en) Waste water treating method and waste water treating device using the same
CN105597775A (en) Graphene /Cu-Mn-Ce compound catalyst, and preparation method and applications thereof
CN108906044B (en) Manganese-cerium-ruthenium composite oxide catalyst and preparation method and application thereof
CN113797961B (en) RuCe/ZSM-5 molecular sieve catalyst and preparation method and application thereof
CN111482172B (en) Composite nano material of CuO/defect titanium dioxide and application thereof
Li et al. High-yield synthesis of Ce modified Fe–Mn composite oxides benefitting from catalytic destruction of chlorobenzene
JP2012050980A (en) Catalyst, oxidation catalyst, reduction catalyst, and exhaust gas cleaning catalyst
CN113769731B (en) VO for degrading dioxin at low temperature x -MoO x /TiO 2 Method for preparing and using catalyst
CN110898835A (en) Catalyst for efficiently treating ammonia nitrogen wastewater and preparation method thereof
JP5899525B2 (en) Exhaust gas purification catalyst and catalyst body supporting the same
CN107486206A (en) A kind of Mn-based material and its production and use
JP4281061B2 (en) Active oxygen storage material and method for producing the same
CN113101923A (en) Mn-Zr-La-Ce catalyst for degrading VOCs (volatile organic compounds), preparation method and low-temperature plasma concerted catalysis application thereof
CN111001398B (en) Modified titanium dioxide catalyst with special morphology and preparation method and application thereof
Bai et al. Research on ultrafast catalytic degradation of heterocyclic compounds by the novel high entropy catalyst

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

Effective date of registration: 20191213

Address after: 611436 No.777, Xinghua 10th Road, dengshuang Town, Xinjin County, Chengdu City, Sichuan Province (Industrial Park)

Patentee after: HAO HUA (CHENGDU) TECHNOLOGY Co.,Ltd.

Address before: No. 5 high tech Zone Gaopeng road in Chengdu city of Sichuan Province in 610225

Patentee before: SOUTHWEST RESEARCH & DESIGN INSTITUTE OF CHEMICAL INDUSTRY

TR01 Transfer of patent right
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20190219

CF01 Termination of patent right due to non-payment of annual fee