CN110302796A - A kind of Mn-Fe-Cu/ γ-Al of hypergravity fluidisation spray-stain method preparation2O3Catalyst and its application - Google Patents

A kind of Mn-Fe-Cu/ γ-Al of hypergravity fluidisation spray-stain method preparation2O3Catalyst and its application Download PDF

Info

Publication number
CN110302796A
CN110302796A CN201910616351.8A CN201910616351A CN110302796A CN 110302796 A CN110302796 A CN 110302796A CN 201910616351 A CN201910616351 A CN 201910616351A CN 110302796 A CN110302796 A CN 110302796A
Authority
CN
China
Prior art keywords
catalyst
carrier
packed bed
hypergravity
bed
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
Application number
CN201910616351.8A
Other languages
Chinese (zh)
Inventor
焦纬洲
邵圣娟
刘有智
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.)
North University of China
Original Assignee
North University of China
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 North University of China filed Critical North University of China
Priority to CN201910616351.8A priority Critical patent/CN110302796A/en
Publication of CN110302796A publication Critical patent/CN110302796A/en
Pending legal-status Critical Current

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
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/76Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/84Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/889Manganese, technetium or rhenium
    • B01J23/8892Manganese
    • 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
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • 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
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/78Treatment of water, waste water, or sewage by oxidation with ozone
    • 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
    • C02F2101/38Organic compounds containing nitrogen
    • 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
    • C02F2305/02Specific form of oxidant
    • C02F2305/023Reactive oxygen species, singlet oxygen, OH radical

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Materials Engineering (AREA)
  • Catalysts (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Abstract

The invention belongs to loaded catalyst preparation and technical field of waste water processing, the problems such as generally existing active component dispersion degree of loaded catalyst is not high, load is uneven, load capacity is low, the production cycle is long is prepared for current infusion process, a kind of hypergravity fluidisation spray-stain method preparation Mn-Fe-Cu/ γ-Al is provided2O3Catalyst and its application.γ-Al2O3Carrier is filler, and manganese, iron, copper metal salt make maceration extract, and hypergravity makes maceration extract contact dipping with carrier from inside to outside with Sprayable, and reverse air blast makes carrier granular be near fluidization, and active component is in carrier surface uniform adsorption.The high loaded catalyst of active component dispersion degree height, even particle size, activity is prepared in roasting.Make filler with the catalyst, make reactor so that hypergravity adverse current is rotary packed bed, high-gravity technology, heterogeneous catalysis and ozone oxidation synergistic effect improve nitrobenzene degradation rate and ozone utilization rate, shorten process cycle, is suitble to the nitrobenzene waste water that processing is of large quantities, processing task is heavy.

Description

A kind of Mn-Fe-Cu/ γ-Al of hypergravity fluidisation spray-stain method preparation2O3Catalyst and its Using
Technical field
The invention belongs to loaded catalyst preparation and technical field of waste water processing, and in particular to a kind of hypergravity fluidisation spray Mn-Fe-Cu/ γ-the Al of stain method preparation2O3Catalyst, and heterogeneous catalysis ozone oxidation degrading nitrobenzene is coupled for hypergravity Waste water.
Background technique
Heterogeneous catalysis ozone Oxidation Treatment organic wastewater using the absorption of catalyst, is urged by introducing solid catalyst Change characteristic, catalysis ozone, which decomposes, generates more OH free radicals, and causes a series of radical chain reaction, to thoroughly drop Solve the persistent organic pollutants in waste water.Heterogeneous catalysis has high catalytic activity, mineralization of organic material rate height, without secondary dirt It contaminates, be easily recycled the advantages of processing, thus receive significant attention.It focuses primarily upon metal composite oxide at present and support type is urged The development of the solid catalysts such as agent, modified mineral.
Loaded catalyst includes the (CN 102091619 such as aluminium oxide, molecular sieve, ceramics, active carbon with porous material B, 2012.10.24;CN 101811049 B, 2013.03.27;CN 106311270 B, 2018.09.11;CN 103586026 A ,2014.02.19;CN 105289585 B, 2018.04.03) it is carrier, by Determination of multiple metal elements or metal oxide supported Thereon, in conjunction with the interaction of carrier and active component, the dissolution of metal ion is avoided, enhances its catalytic activity, and have both The good advantage of carrier large specific surface area itself, high mechanical strength and thermal stability.Metal member currently used for heterogeneous catalysis Element mainly has noble metal, transition metal and rare-earth metal series.Wherein transition metal price is relatively cheap, raw material is easy to get, is catalyzed Activity is high and is concerned.And its catalytic activity of manganese catalyst series is the most prominent, is most widely used, but its anti-SO2With it is anti- H2The ability of O is poor, needs to adulterate other components to improve its catalytic activity.Common carrying method have infusion process, the precipitation method, Mixing method, ion-exchange etc., wherein infusion process principle is when active component solution is contacted with porous carrier in capillary pressure It is penetrated into inside support voids under effect, the process with absorption is diffused in inner surface of the carrier.This method is simple, raw material is sharp It is low with rate height, economic cost, it is easy to industrial application.The patent of invention of 106311270 B of Publication No. CN with grain active carbon or Y type molecular sieve prepares ozone oxidation catalyst as active component as carrier, using the oxide of iron, molybdenum, tantalum, potassium, manganese, is used for Catalytic ozonation degradation coking wastewater and agricultural chemicals waste water, COD removal rate reach 90% or more.105289585 B of publication number CN Patent of invention using active carbon as carrier, iron and manganese oxides are as active component, and sodium hydroxide is as precipitating reagent, using leaching The stain precipitation method prepare loaded catalyst, handle dyeing waste water for O3 catalytic oxidation, can reach Treatment of Industrial Water discharge Standard.
But in above-mentioned preparation process, solute is limited by diffusion absorption and is easy in catalyst drying process migration, Lead to the problem of active component poor dispersion, load are uneven, active site is reduced.For equi-volume impregnating, activity Component dispersion degree is very poor, and granular size is different;Excessive infusion process, immersion period is long, the bad control of load capacity;And dipper precipitation Method, sedimentation cycle is long, easily formation egg-shell catalyst.Moreover, being related to gas-liquid-solid three for heterogeneous catalysis ozone oxidation system Phase, using conventional reactor, generally existing Ozone Gas Mass Transfer Efficiency is low, and ozone utilization rate is not high and filling of catalyst is fixed Problem.Therefore it provides a kind of active component dispersion degree height, Load Balanced, large specific surface area, activity are high, with short production cycle negative Supported catalyst preparation method can strengthen ozone mass transfer in combination with one kind, increase the reaction of gas, liquid, solid three-phase contact area Equipment is of great significance for the research of heterogeneous catalysis ozone oxidation.
High-gravity technology (High Gravity Technology, Higee) is strengthened as a kind of novel chemical process Technology generates super gravity field by the high speed rotation of packed bed, make air-liquid under Elevated Gravity porous media or duct in Liquid shear is very thin liquid film and small liquid mist, drop by flowing, huge shearing force, increases phase boundary specific surface area, Phase interface renewal rate is accelerated, to greatly improve mass transfer rate, the microcosmic mixing alternate for two has traditional reactor Incomparable advantage can be widely applied to the chemical processes such as absorption, rectifying, extraction, absorption.
Summary of the invention
Prepare that the generally existing active component dispersion degree of loaded catalyst is not high, load is uneven for current infusion process Even, the problems such as load capacity is low, the production cycle is long, the present invention provides a kind of Mn-Fe-Cu/ of hypergravity fluidisation spray-stain method preparation γ-Al2O3Catalyst and its application, the catalyst activity component dispersion degree height, Load Balanced, activity are high, with short production cycle, together When combination can strengthen ozone mass transfer, increase the hypergravity equipment of gas, liquid, solid three-phase contact area, which is used for hypergravity Heterogeneous catalysis ozone oxidation nitrobenzene waste water in.
Hypergravity equipment of the present invention is the rotary packed bed (CN of hypergravity adverse current having disclosed 201510093434.5), packing layer is the mixing filled layer of wire packing and carrier or loaded catalyst.
To achieve the above object, the technical solution adopted by the present invention is that: a kind of Mn- of hypergravity fluidisation spray-stain method preparation Fe-Cu/γ-Al2O3Catalyst, the Mn-Fe-Cu/ γ-Al2O3Catalyst is with γ-Al2O3Carrier as filler, Mn, Fe, Cu metal salt is maceration extract, rotary packed bed using hypergravity adverse current, adjusts air mass flow, and carrier granular is made to be in nearly fluidisation shape State makes maceration extract and air in rotary packed bed middle counter current contacting under hypergravity centrifugal action, after carrier is sufficiently impregnated, uses Hot-air stripping moisture, fixes active component, catalyst precursor is then taken out 300-700 DEG C of high-temperature roasting, i.e., For Mn-Fe-Cu/ γ-Al2O3Loaded catalyst.
Mn, Fe, Cu metal salt is the mixed solution of copper nitrate, ferric nitrate and manganese acetate, concentration of metal ions proportion For 1:1-4:1-4;In terms of Cu concentration of metal ions, the concentration of salt solution is 0.01-0.05 mol/L.
The preparation Mn-Fe-Cu/ γ-Al2O3The method of catalyst, the specific steps are as follows:
(1) impregnation: γ-Al2O3Filling even enters cross_flow rotating packed bed after Vehicle element;Mn, Fe, Cu metal salt Mixed impregnant liquor is placed in reservoir, is pumped into cross_flow rotating packed bed inner cavity through circulation, maceration extract is equal via liquid distribution trough It is even to be sprayed at carrier bed inner edge, under the effect of high speed centrifugation power, leaching is radially contacted with carrier from inside to outside with Sprayable Stain, while air is sent into through blower by bed exocoel, under inside and outside differential pressure effect, ecto-entad connects with maceration extract and carrier adverse current Touching, by adjusting gas velocity, makes carrier granular be in nearly fluidized state, with the revolution and rotation of particle, makes carrier granular and leaching Stain liquid comes into full contact with, and the liquid after dipping returns to reservoir and carries out circulation dipping;
(2) high-temperature roasting: after the completion of dipping, carrying out stripping to bed using hot-air, remove catalyst surface moisture, fixed to live Property component, take out catalyst precursor after 300-700 DEG C of high-temperature roasting.
γ-the Al2O3Carrier is the spherical gamma-Al of partial size 1-2 mm2O3, loading is 50 g/L.
γ-Al2O3Vehicle element method are as follows: 2 h are impregnated with 0.1 mol/L dust technology, deionized water is cleaned to neutrality, 12 h are dried at 105 DEG C, roast 4 h at 300 DEG C.
The rotary packed bed revolving speed is 600-1200 rpm, and fluid flow is 40-120 L/h, air mass flow 4- 10 m3/ h, circulation dip time are 30 ~ 90 min.
The air stripping method is 120 DEG C of 60 min of hot-air stripping, and tolerance is 4 m3/h。
Calcining time is 3-6 h.
Mn-Fe-Cu/ γ-the Al2O3Catalyst heterogeneous catalysis ozone oxidation nitrobenzene waste water in super gravity field In application, concrete application method are as follows: by Mn-Fe-Cu/ γ-Al2O3For catalyst as filler, filling even enters adverse current rotary filling Expect that bed, loading are 100 g;The 2 L nitrobenzene waste waters of 200 mg/L are added to reservoir, are pumped into rotary filling material through circulation Bed inner cavity, ozone are sent into rotary packed bed through rotary packed bed gas access, and controlling rotary packed bed revolving speed is 1000 rpm, Fluid flow is 85L/h, and gas flow 60L/h, gas phase ozone concentration is 60mg/L, and nitrobenzene waste water is under hypergravity along diameter It is thrown away to from rotary packed bed bed inner edge, the ozone gas counter current contacting of rotary packed bed bed, liquid is passed through with ecto-entad Body is then thrown to outer wall vertical and falls, and returns to reservoir, nitrobenzene waste water and ozone gas in rotation filler from liquid outlet Counter current contacting carries out circular response in bed.
Treated, and nitrobenzene waste water is analyzed from thief hatch direct sample, is gone according to the degradation rate of nitrobenzene waste water and TOC Except rate evaluates the catalytic activity of the catalyst.
The present invention utilizes high-gravity technology, and rotary packed bed as hypergravity equipment using adverse current, catalyst carrier is used as and fills out Material, maceration extract aerosol dispersion is made under super gravity field, is sprayed in high-speed rotating carrier surface, simultaneously with liquid mist, drop state Reverse air blast makes carrier granular be near fluidization, promotes the revolution rotation of particle, on the one hand extends the dipping residence time, improves The load capacity of active component, while promoting active component in the uniform adsorption of carrier surface, reduce dipping yin-yang face phenomenon.This Outside, is further shortened the production cycle, most using the quick stripping of hot-air for the drying process of shaping carrier in super gravity field By roasting, active component dispersion degree height, even particle size, activity height, loaded catalyst with short production cycle are prepared.
Rotary packed bed as reactor using adverse current later, above-mentioned catalyst makes nitro under super gravity field as filler Benzene waste water with ozone gas react by the counter current contacting in catalyst bed, joint high-gravity technology, heterogeneous catalysis and ozone oxygen The synergistic effect for changing three, improves the degradation rate of nitrobenzene and the utilization rate of ozone.
The present invention utilizes high-gravity technology, with carrier γ-Al2O3As filler, make maceration extract aerosol dispersion, with liquid mist, liquid Drop-wise state is sprayed in high-speed rotating carrier surface, while reverse air blast makes carrier granular be near fluidization, promotes particle Revolution rotation, on the one hand extends the dipping residence time, improves the load capacity of Mn, Fe, Cu active component, while promoting active component In the uniform adsorption of carrier surface, dipping yin-yang face phenomenon is reduced.
Life is further shortened using 120 DEG C of hot-air quick strippings for the drying process of shaping carrier in super gravity field The period is produced, while with mm grades of spherical gamma-Al2O3As carrier, the forming process in catalyst later period is eliminated, the catalysis prepared Agent have with rotary packed bed matching, active component is uniformly dispersed, large specific surface area, catalytic activity are high, with short production cycle excellent Point.
It is rotary packed bed as gas-liquid-solid phase reaction device, Mn-Fe-Cu/ γ-Al using adverse current2O3Catalyst as filler, Joint high-gravity technology, heterogeneous catalysis and ozone oxidation three synergistic effect, accelerate mass transfer and the decomposition of ozone, promote to produce Raw more OH free radicals, effectively improve the degradation rate of nitrobenzene and the utilization rate of ozone, shorten process cycle, are suitble to place Manage the nitrobenzene waste water of processing task weight of large quantities.
Detailed description of the invention
Fig. 1 is that the present invention prepares the Mn-Fe-Cu/ γ-Al2O3The process flow chart of catalyst;In figure: 1- ozone occurs Device;2- valve;3- flowmeter;4- blower;5- preheater;6- shell;7- motor;8- carrier;9- reservoir;10- pump;11- tail Aspiration receiving apparatus;
Fig. 2 is that hypergravity fluidizes spray-stain method preparation Mn-Fe-Cu/ γ-Al2O3The device master of catalyst and treatment of Nitrobenzene waste water Body figure;In figure: 6.1- liquid outlet;6.2- silk screen;6.3- gas vent;6.4- liquid inlet;6.5- liquid distribution trough;6.6- Gas access;
Fig. 3 is Mn-Fe-Cu/γ-Al in embodiment 12O3The outside drawing for roasting front and back, in figure: A is outside drawing before roasting;B For outside drawing after roasting;
Fig. 4 is Mn-Fe-Cu/γ-Al in embodiment 12O3The SEM of catalyst and carrier figure;
Fig. 5 is Mn-Fe-Cu/γ-Al in embodiment 12O3Catalyst Catalytic Ozonation nitrobenzene in super gravity field Waste water nitrobenzene degradation rate with catalyst access times trend chart.
Specific embodiment
The present invention is described in further details with reference to the accompanying drawings and detailed description.But the content of present invention not by Following embodiments are limited to.
Embodiment 1: using process flow shown in Fig. 1, with 1-2 mm spherical gamma-Al2O3For carrier, with the dilute nitre of 0.1 mol/L 2 h of acid soak, deionized water are cleaned to neutrality, dry 12 h at 105 DEG C, roast 4 h at 300 DEG C, filling even enters after cooling Rotary packed bed, loading is 50 g/L.Molar ratio 1:1:4 nitric acid is prepared by 0.05 mol/L (in terms of Cu concentration of metal ions) Copper, ferric nitrate, manganese acetate metal mixed salt solution, adjusting pH is 5.0, is placed in reservoir.By maceration extract through circulation be pumped into it is super Gravity is rotary packed bed, and fluid flow is 40 L/h, and air mass flow is 6 m3/ h, revolving speed are set as 800 rpm, make itself and carrier Dipping is come into full contact with, circulation dip time is 90 min.Then lead to 60 min of hot-air to take away catalyst surface moisture, make to live Property component is fixed.It takes out catalyst and roasts the Cu01- that 4 h are 13% to get metallic element load capacity at 500 DEG C Fe01-Mn04/γ-Al2O3Catalyst.
Prepared catalyst is through electron microscope scanning, as a result as shown in figure 4, Mn-Fe-Cu/γ-Al2O3Catalyst SEM figure it can be seen that load after carrier surface become coarse, metal oxide is with lesser even particulate dispersion in carrier Surface, active site is more, and catalytic activity is high.In combination with outside drawing 3, it can be seen that catalyst surface color is uniform, is not present Apparent yin-yang face phenomenon, shows that active component reaches uniform load in carrier surface, keeps good exterior appearance.
Embodiment 2: the process flow shown in Fig. 1, with 1-2 mm spherical gamma-Al2O3For carrier, with 0.1 mol/L dust technology 2h is impregnated, deionized water is cleaned to neutrality, dry 12 h at 105 DEG C, roasts 4 h at 300 DEG C, filling even enters rotation after cooling Packed bed, loading are 50 g/L.By 0.05 mol/L (in terms of Cu concentration of metal ions) prepare molar ratio 1:1:4 copper nitrate, Ferric nitrate, manganese acetate metal mixed salt solution, adjusting pH is 5.0, is placed in reservoir.Maceration extract is pumped into hypergravity through circulation Rotary packed bed, fluid flow is 40 L/h, and air mass flow is 4 m3/ h, revolving speed are set as 600 rpm, fill it with carrier Tap touching dipping, circulation dip time are 30 min.Then lead to 60 min of hot-air to take away catalyst surface moisture, make activity Component is fixed.It takes out catalyst and roasts the Cu01-Fe01- that 2 h are 10% to get metallic element load capacity at 500 DEG C Mn04/γ-Al2O3Catalyst.
Embodiment 3: the process flow shown in Fig. 1, with 1-2 mm spherical gamma-Al2O3For carrier, with 0.1 mol/L dust technology 2h is impregnated, deionized water is cleaned to neutrality, dry 12 h at 105 DEG C, roasts 4 h at 300 DEG C, filling even enters rotation after cooling Packed bed, loading are 75 g/L.Molar ratio 1:2:2 copper nitrate, nitre are prepared by 0.03mol/L (in terms of Cu concentration of metal ions) Sour iron, manganese acetate metal mixed salt solution, adjusting pH is 5.0, is placed in reservoir.Maceration extract is pumped into hypergravity rotation through circulation Turn packed bed, fluid flow is 120 L/h, and air mass flow is 10 m3/ h, revolving speed are set as 800 rpm, keep it abundant with carrier Contact dipping, circulation dip time are 60 min.Then lead to 60 min of hot-air to take away catalyst surface moisture, make active group Divide and is fixed.It takes out catalyst and roasts the Cu01-Fe02- that 6 h are 9% to get metallic element load capacity at 300 DEG C Mn02/γ-Al2O3Catalyst.
Embodiment 4: the process flow shown in Fig. 1, with 1-2 mm spherical gamma-Al2O3For carrier, with 0.1mol/L dust technology 2h is impregnated, deionized water is cleaned to neutrality, dry 12 h at 105 DEG C, roasts 4 h at 300 DEG C, filling even enters rotation after cooling Packed bed, loading are 100 g/L.By 0.05mol/L (in terms of Cu concentration of metal ions) prepare molar ratio 1:1:4 copper nitrate, Ferric nitrate, manganese acetate metal mixed salt solution, adjusting pH is 5.0, is placed in reservoir.Maceration extract is pumped into hypergravity through circulation Rotary packed bed, fluid flow is 80 L/h, and air mass flow is 8 m3/ h, revolving speed are set as 1200 rpm, fill it with carrier Tap touching dipping, circulation dip time are 90 min.Then lead to 60 min of hot-air to take away catalyst surface moisture, make activity Component is fixed.It takes out catalyst and roasts the Cu01-Fe01- that 4 h are 16% to get metallic element load capacity at 500 DEG C Mn04/γ-Al2O3Catalyst.
Embodiment 5: the process flow shown in Fig. 1, with 1-2 mm spherical gamma-Al2O3For carrier, with 0.1 mol/L dust technology 2h is impregnated, deionized water is cleaned to neutrality, dry 12 h at 105 DEG C, roasts 4 h at 300 DEG C, filling even enters rotation after cooling Packed bed, loading are 50 g/L.Molar ratio 1:4:2 copper nitrate, nitre are prepared by 0.05mol/L (in terms of Cu concentration of metal ions) Sour iron, manganese acetate metal mixed salt solution, adjusting pH is 5.0, is placed in reservoir.Maceration extract is pumped into hypergravity rotation through circulation Turn packed bed, fluid flow is 120 L/h, and air mass flow is 10 m3/ h, revolving speed are set as 1200 rpm, fill it with carrier Tap touching dipping, circulation dip time are 30 min.Then lead to 60 min of hot-air to take away catalyst surface moisture, make activity Component is fixed.It takes out catalyst and roasts the Cu01-Fe04- that 4 h are 17% to get metallic element load capacity at 700 DEG C Mn02/γ-Al2O3Catalyst.
Embodiment 6: using Mn-Fe-Cu/ γ-Al made from example 12O3Catalyst, O3 catalytic oxidation treatment of Nitrobenzene Waste water.Using process flow shown in Fig. 1, by Mn-Fe-Cu/ γ-Al2O3Filling even enters rotary packed bed, loading 100 g.The 2 L nitrobenzene solutions that initial concentration is 200 mg/L are prepared, adjusting pH is 6.9, is placed in reservoir.Adjust ozone generator Outlet gas phase ozone concentration be 60 mg/L, gas flow be 60 L/h, pumping fluid flow be 85 L/h, rotary packed bed turn The rpm of fast N=1000, gas-liquid two-phase counter current contacting in catalyst bed are reacted.
Mn-Fe-Cu/γ-Al2O3Catalyst catalytic ozonation degradation nitrobenzene waste water nitre in super gravity field As shown in figure 5, treated, nitrobenzene waste water is straight from thief hatch with the trend charts of catalyst access times for base benzene degradation rate Connect sampling analysis, the degradation rate of nitrobenzene up to 100%, TOC removal rate up to 87%, ozone utilization rate reaches 78%.Catalyst 20 h are used continuously, catalytic performance is without the trend that is decreased obviously, and metal ion does not occur dissolution phenomenon.
Prepared catalyst catalytic performance repeats experimental result as shown in figure 5, according to experiment is repeated as can be seen that catalysis Agent is with good stability, this is related with the more active site of catalyst surface Load Balanced, holding.
Mn-Fe-Cu/γ-Al prepared by embodiment 1- embodiment 52O3Catalyst ozonisation results of property is shown in Table 1.As can be seen from Table 1 using Mn-Fe-Cu/γ-Al of hypergravity fluidisation spray-stain method preparation2O3Catalyst loadings are high, for The degradation rate and TOC removal rate of nitrobenzene respectively reach 95%, 70% or more;Ozone utilization rate reaches 65% or more.Show this method The catalyst significant effect of preparation, while high-gravity technology, heterogeneous catalysis and ozone oxidation three being coupled, utilize association Same effect can accelerate mass transfer and the decomposition of ozone, promote to generate more OH free radicals, effectively improve the mineralization rate of nitrobenzene With the utilization rate of ozone, it is suitble to the nitrobenzene waste water that processing is of large quantities, processing task is heavy.
Table 1 is Mn-Fe-Cu/γ-Al under different preparation conditions2O3Catalyst ozonizes results of property table

Claims (9)

1. a kind of Mn-Fe-Cu/ γ-Al of hypergravity fluidisation spray-stain method preparation2O3Catalyst, it is characterised in that: the Mn-Fe- Cu/γ-Al2O3Catalyst is in hypergravity adverse current is rotary packed bed, with γ-Al2O3Carrier is filler, Mn, Fe, Cu metal Salt is maceration extract, and adjusting air mass flow makes carrier granular be in nearly fluidized state, while under hypergravity centrifugal action, making to impregnate Liquid and the air counter current contacting in carrier bed, after carrier is sufficiently impregnated, using hot-air stripping moisture, are subject to active component It is fixed, then 300-700 DEG C of high-temperature roasting, as Mn-Fe-Cu/ γ-Al are taken out from bed2O3Loaded catalyst.
2. a kind of Mn-Fe-Cu/ γ-Al of hypergravity fluidisation spray-stain method preparation according to claim 12O3Catalyst, Be characterized in that: Mn, Fe, Cu metal salt is the mixed solution of copper nitrate, ferric nitrate and manganese acetate, concentration of metal ions proportion For 1:1-4:1-4;In terms of Cu concentration of metal ions, the concentration of salt solution is 0.01-0.05 mol/L.
3. preparing Mn-Fe-Cu/ γ-Al of any of claims 1 or 22O3The method of catalyst, it is characterised in that: specific steps It is as follows:
(1) impregnation: γ-Al2O3Filling even enters cross_flow rotating packed bed after Vehicle element;Mn, Fe, Cu metal salt Mixed impregnant liquor is placed in reservoir, is pumped into cross_flow rotating packed bed inner cavity through circulation, maceration extract is equal via liquid distribution trough It is even to be sprayed at carrier bed inner edge, under the effect of high speed centrifugation power, leaching is radially contacted with carrier from inside to outside with Sprayable Stain, while air is sent into through blower by bed exocoel, under inside and outside differential pressure effect, ecto-entad connects with maceration extract and carrier adverse current Touching, by adjusting gas velocity, makes carrier granular be in nearly fluidized state, with the revolution and rotation of particle, makes carrier granular and leaching Stain liquid comes into full contact with, and the liquid after dipping returns to reservoir and carries out circulation dipping;
(2) high-temperature roasting: after the completion of dipping, carrying out stripping to bed using hot-air, remove catalyst surface moisture, fixed to live Property component, take out catalyst precursor after 300-700 DEG C of high-temperature roasting.
4. preparation Mn-Fe-Cu/ γ-Al according to claim 32O3The method of catalyst, it is characterised in that: the γ- Al2O3Carrier is the spherical gamma-Al of partial size 1-2 mm2O3, loading is 50 g/L.
5. preparation Mn-Fe-Cu/ γ-Al according to claim 32O3The method of catalyst, it is characterised in that: γ-Al2O3 Vehicle element method are as follows: 2 h are impregnated with 0.1 mol/L dust technology, deionized water is cleaned to neutrality, dry 12 h at 105 DEG C, 4 h are roasted at 300 DEG C.
6. preparation Mn-Fe-Cu/ γ-Al according to claim 32O3The method of catalyst, it is characterised in that: the rotation The revolving speed of packed bed is 600-1200 rpm, and fluid flow is 40-120 L/h, and air mass flow is 4-10 m3/ h, circulation dipping Time is 30 ~ 90 min.
7. preparation Mn-Fe-Cu/ γ-Al according to claim 32O3The method of catalyst, it is characterised in that: the heat is empty Air-blowing desorption method is 120 DEG C of 60 min of hot-air stripping, and tolerance is 4 m3/h。
8. preparation Mn-Fe-Cu/ γ-Al according to claim 32O3The method of catalyst, it is characterised in that: calcining time For 3-6 h.
9. Mn-Fe-Cu/ γ-Al of any of claims 1 or 22O3Catalyst O3 catalytic oxidation nitrobenzene in super gravity field Application in waste water, application is it is characterized by: concrete application method are as follows: by Mn-Fe-Cu/ γ-Al2O3Catalyst as filler, It is rotary packed bed that filling even enters adverse current type, loading 100g;The 2 L nitrobenzene waste waters of 200 mg/L are added to liquid storage Slot is pumped into rotary packed bed inner cavity through circulation, and ozone is sent into rotary packed bed through rotary packed bed gas access, control rotation Turning packed bed revolving speed is 1000rpm, fluid flow 85L/h, gas flow 60L/h, and gas phase ozone concentration is 60mg/L, nitre Base benzene waste water is radially thrown away from rotary packed bed bed inner edge under hypergravity, passes through rotary packed bed bed with ecto-entad Ozone gas counter current contacting, liquid is then thrown to outer wall vertical and falls, and returns to reservoir, nitrobenzene waste water from liquid outlet Circular response is carried out in rotary packed bed middle counter current contacting with ozone gas.
CN201910616351.8A 2019-07-09 2019-07-09 A kind of Mn-Fe-Cu/ γ-Al of hypergravity fluidisation spray-stain method preparation2O3Catalyst and its application Pending CN110302796A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910616351.8A CN110302796A (en) 2019-07-09 2019-07-09 A kind of Mn-Fe-Cu/ γ-Al of hypergravity fluidisation spray-stain method preparation2O3Catalyst and its application

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910616351.8A CN110302796A (en) 2019-07-09 2019-07-09 A kind of Mn-Fe-Cu/ γ-Al of hypergravity fluidisation spray-stain method preparation2O3Catalyst and its application

Publications (1)

Publication Number Publication Date
CN110302796A true CN110302796A (en) 2019-10-08

Family

ID=68079960

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910616351.8A Pending CN110302796A (en) 2019-07-09 2019-07-09 A kind of Mn-Fe-Cu/ γ-Al of hypergravity fluidisation spray-stain method preparation2O3Catalyst and its application

Country Status (1)

Country Link
CN (1) CN110302796A (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112331866A (en) * 2020-11-06 2021-02-05 中北大学 Fe/Co-N-MCF composite catalyst for fuel cell and preparation method thereof
CN112679636A (en) * 2019-10-18 2021-04-20 中国石油化工股份有限公司 Process for preparing catalyst for ethylene polymerization
CN113318747A (en) * 2021-06-11 2021-08-31 浙江中凯瑞普环境工程股份有限公司 High-salt and high-chlorine tolerant supported catalyst and preparation method and application thereof
CN113797856A (en) * 2021-09-23 2021-12-17 中北大学 Supergravity rotating fluidized field enhanced liquid-solid adsorption equipment and method
CN114471585A (en) * 2022-02-28 2022-05-13 山东华特环保科技有限公司 Ozone catalyst with acetate as precursor and preparation method and application thereof
CN114632524A (en) * 2022-05-18 2022-06-17 中国环境科学研究院 Copper-manganese/aluminum oxide catalyst for petrochemical wastewater treatment and preparation method thereof
CN114749177A (en) * 2022-05-20 2022-07-15 烟台哈尔滨工程大学研究院 Preparation method of sewage ozone oxidation catalyst
CN115010286A (en) * 2021-03-05 2022-09-06 万华化学集团股份有限公司 Catalytic dechlorination process for dilute brine at outlet of electrolytic cell

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108341478A (en) * 2018-02-06 2018-07-31 中北大学 A kind of method and device of hypergravity catalytic wet oxidation phenol wastewater
CN108854931A (en) * 2018-07-06 2018-11-23 中北大学 A kind of device and method preparing metallic catalyst
CN109647431A (en) * 2019-02-21 2019-04-19 渤海水业股份有限公司 A kind of catalyst, preparation method and the usage for catalytic ozonation processing used water difficult to degradate

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108341478A (en) * 2018-02-06 2018-07-31 中北大学 A kind of method and device of hypergravity catalytic wet oxidation phenol wastewater
CN108854931A (en) * 2018-07-06 2018-11-23 中北大学 A kind of device and method preparing metallic catalyst
CN109647431A (en) * 2019-02-21 2019-04-19 渤海水业股份有限公司 A kind of catalyst, preparation method and the usage for catalytic ozonation processing used water difficult to degradate

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
刘建周: "《工业催化工程》", 30 June 2018, 中国矿业大学出版社 *

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112679636A (en) * 2019-10-18 2021-04-20 中国石油化工股份有限公司 Process for preparing catalyst for ethylene polymerization
CN112679636B (en) * 2019-10-18 2022-12-27 中国石油化工股份有限公司 Method for preparing catalyst for ethylene polymerization
CN112331866A (en) * 2020-11-06 2021-02-05 中北大学 Fe/Co-N-MCF composite catalyst for fuel cell and preparation method thereof
CN115010286A (en) * 2021-03-05 2022-09-06 万华化学集团股份有限公司 Catalytic dechlorination process for dilute brine at outlet of electrolytic cell
CN115010286B (en) * 2021-03-05 2024-05-07 万华化学集团股份有限公司 Catalytic dechlorination process for dilute brine at outlet of electrolytic tank
CN113318747A (en) * 2021-06-11 2021-08-31 浙江中凯瑞普环境工程股份有限公司 High-salt and high-chlorine tolerant supported catalyst and preparation method and application thereof
CN113797856A (en) * 2021-09-23 2021-12-17 中北大学 Supergravity rotating fluidized field enhanced liquid-solid adsorption equipment and method
CN114471585A (en) * 2022-02-28 2022-05-13 山东华特环保科技有限公司 Ozone catalyst with acetate as precursor and preparation method and application thereof
CN114471585B (en) * 2022-02-28 2024-05-07 山东华特环保科技有限公司 Ozone catalyst with acetate as precursor and preparation method and application thereof
CN114632524A (en) * 2022-05-18 2022-06-17 中国环境科学研究院 Copper-manganese/aluminum oxide catalyst for petrochemical wastewater treatment and preparation method thereof
CN114749177A (en) * 2022-05-20 2022-07-15 烟台哈尔滨工程大学研究院 Preparation method of sewage ozone oxidation catalyst

Similar Documents

Publication Publication Date Title
CN110302796A (en) A kind of Mn-Fe-Cu/ γ-Al of hypergravity fluidisation spray-stain method preparation2O3Catalyst and its application
CN110302797A (en) A kind of bi-component manganese base supported catalyst of hypergravity spray-stain method preparation and its application
CN105457643B (en) A kind of preparation method of activated carbon supported type catalyst for Electrocatalysis Degradation organic wastewater
CN111054421A (en) Graphite-like carbon nitride doped modified microsphere catalyst and preparation method and application thereof
CN103521218B (en) Preparation method for photocatalyst used for treating volatile organic compounds
CN109647431B (en) Catalyst for catalytic oxidation treatment of refractory wastewater by ozone, preparation method and application thereof
CN107159068A (en) A kind of preparation method of graphene composite aerogel
CN111135823B (en) Wet oxidation catalyst and preparation method and application thereof
CN110152682A (en) A kind of organic wastewater ozone oxidation catalyst and its preparation method and application
CN107670680A (en) A kind of immobilized fenton catalyst and preparation method and application
CN111686731B (en) Preparation method of alpha-FeOOH/GAC catalyst and application of alpha-FeOOH/GAC catalyst in degrading nitrobenzene wastewater in hypergravity field
CN108380214A (en) A kind of preparation of modified meerschaum and the method applied to wastewater treatment
CN107876053A (en) A kind of high intensity wastewater treatment catalyst and its preparation method and application
CN109908926B (en) Preparation method of ozone catalytic oxidation catalyst
CN106345486A (en) High-efficiency solid-phase ozone oxidation catalyst, and preparation method and application thereof
CN108607569A (en) It improves electro-catalysis and restores CO2The synthetic method of the catalyst of CO selectivity in the process
CN108855084A (en) A method of high porosity ozone oxidation nbsCOD catalyst is prepared using Fenton iron cement
CN102249444B (en) Multi-stage series ozone catalytic oxidation deep treatment device and preparation method of catalyst applied to same
CN107803179A (en) Preparation method of arsenic-removing adsorption agent for water process and products thereof and application
CN106964333A (en) The method that rare earth loaded catalyst for handling sewage and its preparation method and application and catalytic ozonation handle sewage
CN110102286B (en) Doped nano manganese dioxide-graphene/Al2O3Preparation method of catalyst, catalyst and application
CN108525673A (en) One type Fenton solid catalyst and its preparation method and application
CN105344360A (en) Preparation method and application of doping type nanometer MnO<2>-CuO/Al<2>O<3> catalyst
CN108993531A (en) A kind of method of spent FCC catalyst resource utilization
CN205740573U (en) The device of hypergravity reinforced nano Zero-valent Iron Ozone advanced treating nitrobenzene waste water

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
RJ01 Rejection of invention patent application after publication

Application publication date: 20191008

RJ01 Rejection of invention patent application after publication