CN105709743A - Catalytic wet oxidation catalyst and preparation method thereof. - Google Patents
Catalytic wet oxidation catalyst and preparation method thereof. Download PDFInfo
- Publication number
- CN105709743A CN105709743A CN201410706805.8A CN201410706805A CN105709743A CN 105709743 A CN105709743 A CN 105709743A CN 201410706805 A CN201410706805 A CN 201410706805A CN 105709743 A CN105709743 A CN 105709743A
- Authority
- CN
- China
- Prior art keywords
- catalyst
- activated carbon
- alumina
- aluminium oxide
- roasting
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
Landscapes
- Catalysts (AREA)
Abstract
The invention discloses a catalytic wet oxidation catalyst and a preparation method thereof. The catalyst comprises the following core-shell structure components, the core-shell structure components take active carbon loaded with transition metal as a core, and take alumina containing rare earth metal or amorphous silicon-aluminum as a shell. The method is characterized in that during a gel forming process of alumina or amorphous silicon-aluminum and a rare earth metal compound, an active carbon slurry loaded with transition metal is introduced, and after the gel forming process, the catalyst can be obtained through an aging process. The catalyst has high reaction activity and usage stability.
Description
Technical field
The present invention relates to a kind of catalytic wet oxidation catalyst and preparation method thereof, particularly containing catalytic wet oxidation catalyst of activated carbon and aluminium oxide or amorphous silica-alumina and preparation method thereof.
Background technology
Increasingly stringent along with global environmental regulation, the Con trolling index of sewage qualified discharge requires more and more higher, under this form, waste water treatment by catalytic oxidation increasingly obtains attention and the employing of people, such as the CWO of high-concentration sewage, catalytic and oxidative electrolysis technology, photochemical catalytic oxidation, advanced oxidation etc..In waste water catalytic oxidation process, for obtaining desirable treatment effect and by reducing reaction temperature, reaction pressure to keep relatively low wastewater treatment expense, preparation have high-activity component, high intensity, high stability cheap catalyst become the key of waste water catalytic oxidation technologies application undoubtedly.
The catalyst of waste water catalytic oxidation is broadly divided into homogeneous catalyst and heterogeneous solid catalyst two class.
Homogeneous catalyst mainly includes producing the Fenton reagent of oxygen radical, Fe3+、Cu2+, the metal ion such as cobalt and manganese, effect by means of these homogeneous catalysts, organic component in waste water, sulfide, ammonia nitrogen etc. are oxidized into low molecular acid (low mass molecule alcohol or carbon dioxide), sulfate or thiosulfate, nitrogen etc. by oxide isolations such as air, oxygen, ozone, hydrogen peroxide, make waste water reach the processing intent of decarburization, desulfurization and denitrogenation.Homogeneous oxidation catalyst preparation and use procedure are relatively simple, generally can directly select the slaines such as ferrum, copper, cobalt, manganese be made into aqueous solution or be directly thrown in handled waste water, and by the water outlet after processing being discharged or regeneration Posterior circle use.Adopt homogeneous catalytic oxidation, owing to metal active constituent can fully dissolve and disperse in waste water, generally can reach relatively stable water treatment effect, but also exist that reagent consumption is big, operating cost is high, the serious problems such as metal loss and secondary pollution, cause its application to be subject to bigger restriction.
Heterogeneous solid catalyst, mainly with activated carbon, molecular sieve, amorphous alumina, titanium dioxide etc. for carrier, makees, with one or more in alkali metal, alkaline-earth metal, transition metal or Pt, Pd noble metal, the catalyst that active component is constituted.Black, hole that activated carbon is made up of carbonaceous material are flourishing, specific surface area is big, a class microcrystalline carbon of high adsorption capacity.Activated carbon property is stable, acidproof, alkaline-resisting, heat-resisting, and water insoluble or organic solvent easily regenerates, is a kind of environmentally friendly adsorbent, is widely used in the fields such as Industrial " three Waste " improvement, food, medicine, carrier, quasiconductor, battery and power storage.The heterogeneous solid catalyst being currently used for wastewater treatment selects activated carbon as carrier mostly, but select catalyst anti-wear performance prepared by activated carbon supported metal poor, mechanical strength is not high, and the metal of load is easy to run off so that the application effect of activated-carbon catalyst is made a discount.Amorphous alumina is because having good chemical stability, pore volume is big, the advantage such as there is certain acidity, pore size distribution$ is concentrated, mechanical strength is big, corrosion-resistant, it is widely used at catalytic field, but amorphous alumina exists the shortcoming that specific surface is little, organic absorption and conversion capability is relatively small.
CN201110225789.7 discloses a kind of method utilizing discarded active amorphous alumina preparation benzene adsorption material, it be by cleaned for useless active amorphous aluminium oxide, filter, dried, adopt a kind of active amorphous aluminium oxide/absorbent charcoal composite material of cryogenic seal heat treatment mode preparation, benzene is had good adsorption effect.The method is by the organic matter carbonizing within amorphous alumina, and activated carbon is mainly distributed in the duct of amorphous alumina, so not only can block the duct of aluminium oxide, and such generated activated carbon skewness in aluminium oxide.
The preparation method that CN201110255525.6 discloses a kind of active amorphous aluminium oxide/absorbent charcoal composite material, be by waste aluminum sludge, activated carbon, binding agent through mixing, pelletize, old, molding, dry, sinter, rinse, drying and other steps makes active amorphous aluminium oxide/absorbent charcoal composite material.It is uneven that the method belongs to salic species and activated carbon physical mixing processes, aluminium oxide and activated carbon dispersion；And the mud impurity content height used, the amorphous alumina character of gained is unstable, it is impossible to repeat, and structure is complicated.
The preparation method that CN201010267074.3 discloses a kind of activated alumina composite reactive Carbon Materials, with aluminium hydroxide, activated carbon and binding agent for raw material, through mixing, pelletize, old, molding, dry, sinter, rinse, drying and other steps, the composite so obtained is still the physical mixture of aluminium oxide and activated carbon, aluminium oxide is uneven with activated carbon dispersion, and its combination property also needs further raising.
Summary of the invention
For the deficiencies in the prior art, the invention provides one and have that catalytic performance is good, mechanical strength is high, catalytic wet oxidation catalyst that anti-wear performance is strong, stability in use is good and preparation method thereof.
The catalytic wet oxidation catalyst of the present invention, including following nucleocapsid structure component, this nucleocapsid structure component is with the activated carbon of carrying transition metal for core, with the aluminium oxide containing rare earth metal or the amorphous silica-alumina containing rare earth metal for shell, with activated carbon and aluminium oxide or activated carbon and amorphous silica-alumina weight for benchmark, activated carbon accounts for 10% ~ 70%, it is preferred to 30% ~ 70%, aluminium oxide or amorphous silica-alumina account for 30% ~ 90%, it is preferred to 30% ~ 70%.
In catalyst of the present invention, described transition metal is one or more in the base metal in the 4th and 5 cycles in the periodic table of elements, and the granularity of described activated carbon is 150 order ~ 300 orders.
In catalyst of the present invention, transition metal is selected from one or more in vanadium, chromium, manganese, ferrum, cobalt, copper and titanium.In catalyst of the present invention, described rare earth metal is one or more in lanthanum, cerium.
In catalyst of the present invention, with the weight of catalyst for benchmark, the content of transition metal oxide is 1% ~ 15%, it is preferably 1% ~ 10%, the content of rare-earth oxide is 1% ~ 15%, being preferably 1% ~ 10%, the content of activated carbon and aluminium oxide or activated carbon and amorphous silica-alumina is 70% ~ 98%, it is preferred to 80% ~ 98%.
In the described amorphous silica-alumina containing rare earth metal, with the weight of amorphous silica-alumina for benchmark, the weight content of silicon oxide is 10% ~ 90%, it is preferred to 30% ~ 70%.
The catalyst of the present invention can be the powder catalyst not needing molding, it is also possible to be preformed catalyst.The granularity of powder catalyst is generally 0.05 ~ 0.20mm.Preformed catalyst can determine the size of granularity as required, is generally 0.5 ~ 8.0mm.
The character of preformed catalyst of the present invention is as follows: specific surface area is 200 ~ 1000m2/ g, pore volume is 0.3 ~ 1.8cm3/ g, < 3wt%, side pressure strength is 100 ~ 250N/cm to rate of wear.
Containing auxiliary agent in heretofore described aluminium oxide or amorphous silica-alumina, auxiliary agent can be selected from titanium, zirconium, magnesium, zinc etc. one or more, in the weight content of element below 10%, it is preferred to 1% ~ 5%.
The preparation process of catalytic wet oxidation catalyst of the present invention, including:
(1) activated carbon of carrying transition metal is pulled an oar；
(2) coprecipitation is being adopted to prepare the serosity that in the plastic process of aluminium oxide or amorphous silica-alumina and rare-earth metal complex, introducing step (1) obtains；
(3) material after the plastic that step (2) obtains carry out aging, filter, washing, dry；
(4) material of step (3) gained is made catalyst, it is preferable that at least adopt one of following method:
A, by the material of step (3) gained, roasting under inert gas shielding, obtain catalyst；
B, by the material forming of step (3) gained, after drying, roasting under inert gas shielding, obtain catalyst；
C, by material roasting under inert gas shielding of step (3) gained, then then through molding, after drying, roasting under inert gas shielding, obtain catalyst.
Step of the present invention (1) described activated carbon can be selected for the Powdered Activated Carbon commodity of routine, such as all kinds of wood activated charcoals, active fruit shell carbon, active carbon from coal；Can also select with wooden material, mineral material, plastics and garbage, such as the various activated carbon products that timber, wood flour, Linesless charcoal, coconut husk, pit, shell, coal, gangue, petroleum coke, asphalt, polrvinyl chloride, polypropylene, organic resin, damaged tire, excess sludge etc. obtain through traditional preparation methods.The activated carbon used in the present invention is powdered active carbon, granularity 150 ~ 300 order, specific surface area 500 ~ 3000m2/ g, pore volume 0.5 ~ 1.8cm3/ g, average pore radius 1 ~ 10nm.
In the inventive method, the making beating of the activated carbon of the carrying transition metal described in step (1) adopts conventional method to carry out, be generally adopted add water, one or more in low-carbon alcohols are pulled an oar, wherein low-carbon alcohols is carbon number is one or more in the monohydric alcohol of 1 ~ 5.In step (1), the activated carbon of carrying transition metal adopts conventional method load, such as infusion process.Specific as follows: to be configured to impregnation liquid with transition metal salt, then activated carbon granule is dipped in above-mentioned impregnation liquid, then drying and roasting, obtains the activated carbon of carrying transition metal, therein can adopt single-steeping, it would however also be possible to employ multiple maceration.Transition metal salt wherein used during preparation impregnation liquid can adopt soluble-salt, and such as nitrate, chloride etc., those skilled in the art can determine according to practical situation.
In the inventive method, the activated carbon of step (1) preferably carrying transition metal first adopts saccharide to process, and then pulls an oar.Described saccharide is one or more in monosaccharide and disaccharide, polysaccharide, preferred carbon number is one or more in the saccharide of 3 ~ 20, such as: one or more in triose, tetrose, pentose, hexose, maltose, glucose, sucrose, more preferably one or more in glucose, sucrose.Described saccharide consumption accounts for the 2% ~ 50% of activated carbon weight, it is preferred to 5% ~ 20%.Saccharide processes activated carbon and can directly be mixed with activated carbon by saccharide, it is also possible to being dissolved in solvent by saccharide and add activated carbon, solvent therein is one or more in water, low-carbon alcohols (namely carbon number is the monohydric alcohol of 1 ~ 5).When saccharide processes activated carbon, its liquid-solid volume ratio is below 10, it is preferable that 1 ~ 5.After saccharide processes activated carbon, excessive liquid phase is preferably filtered to remove, and then pulls an oar again.Making beating can adopt conventional method to carry out, be generally adopted add water, one or more in low-carbon alcohols are pulled an oar, wherein low-carbon alcohols is carbon number is one or more in the monohydric alcohol of 1 ~ 5.
In step of the present invention (2), adopt coprecipitation to prepare aluminium oxide or amorphous silica-alumina and rare earth metal composite oxide can be undertaken by process well known to those skilled in the art.It is usually the neutralization plastic process of acid material and alkaline material.Plastic process can adopt the mode of the continuous acid-base titration of soda acid, it would however also be possible to employ two kinds of materials also flow the mode of neutralization.
In step of the present invention (2), adopt coprecipitation prepare aluminium oxide and rare earth metal composite oxide be in aluminum source, rare earth metal source reacts with precipitant and carries out plastic, aluminum source is one or more in aluminum chloride, aluminum sulfate, aluminum nitrate, and precipitant used is usually one or several in sodium carbonate, sodium bicarbonate, sodium hydroxide, potassium hydroxide, ammonia etc..Rare earth metal source wherein used is generally adopted soluble metallic salt (such as nitrate, chloride etc.), can according to the Acidity of Aikalinity of metal salt solution used, it is mixed for co-precipitation with corresponding acid material or alkaline material, plastic cans can also be initially charged, then acid material carries out plastic with alkaline material, and above content those skilled in the art are known by coprecipitation.
In step of the present invention (2), adopting coprecipitation to prepare amorphous silica-alumina and rare earth metal composite oxide is that aluminum source, silicon source, rare earth metal source are reacted with precipitant and carried out plastic.Plastic material generally comprises aluminum source (Al2(SO4)3、AlCl3、Al(NO3)3And NaAlO2Deng in one or more), silicon source (one or more in waterglass, Ludox and organic silicon-containing compound etc.), precipitant (NaOH, NH4OH or CO2Deng), using according to the different choice of plastic process, conventional mode of operation mainly has: (1) acid aluminium salt (Al2(SO4)3、AlCl3、Al(NO3)3) and basic aluminium salt (NaAlO2) or alkaline precipitating agent (NaOH, NH4OH) plastic, (2) basic aluminium salt (NaAlO are neutralized2) and acidic precipitation agent (CO2) neutralize plastic.Silicon source is typically in plastic process introducing plastic cans, it is also possible to neutralize plastic after aluminum source or precipitant mix again, add such as waterglass in basic aluminium salt or alkaline precipitating agent and be neutralized plastic, Ludox adds in acid aluminium salt and is neutralized plastic etc..Silicon source can also add after the precipitation of aluminum source in material.Two or more combination of aforesaid way can also be used.Rare earth metal source wherein used is generally adopted soluble metallic salt (such as nitrate, chloride etc.), can according to the Acidity of Aikalinity of metal salt solution used, it is mixed for co-precipitation with corresponding acid material or alkaline material, plastic cans can also be initially charged, then acid material carries out plastic with alkaline material, and above content is that those skilled in the art are known by coprecipitation.
Described coprecipitation, plastic process is typically at room temperature ~ 85 DEG C to carry out, be relatively suitably for 40 ~ 80 DEG C, it is preferred to 50 ~ 70 DEG C.Described plastic process is typically under certain pH value condition to carry out, and typical pH is 6.0 ~ 10.0, is relatively suitably for 7.0 ~ 9.5, it is preferred to 7.5 ~ 9.0.Aging described in step (3), condition is as follows: pH is 6.0 ~ 10.0, it is preferred to 7.0 ~ 9.5, and ageing time 0.25 ~ 8.0 hour is relatively adapted at 0.5 ~ 5.0 hour, it is preferred to 1.0 ~ 3.0 hours, and aging temperature is room temperature ~ 85 DEG C, it is preferred to 40 ~ 80 DEG C.Temperature and pH when temperature time aging and pH and neutralization are preferably identical.
In the present invention, step (2) aluminium oxide or amorphous silica-alumina and in rare earth metal co-precipitation plastic process, it is also possible to add the adjuvant component that carrier is conventional, one or more in such as titanium, zirconium, magnesium, zinc etc..
In step of the present invention (2), the incorporation way of the serosity of step (1) gained adopts the one or more combination of following manner: this serosity, in plastic process, is continuously added in plastic cans by (1)；(2) this serosity is charged first in plastic cans, then carries out plastic reaction；(3) this serosity is mixed with one or more of plastic material, then carry out plastic reaction.
In step of the present invention (3), the mode of washing of described material is known in those skilled in the art, can selecting to add the mode such as water washing, lower alcohols washing when making beating washing, filtration, the temperature of washing should in the temperature range of room temperature ~ 90 DEG C, it is preferable that 50 ~ 70 DEG C.The washing of described material is typically in the scope that pH is 1.0 ~ 9.0 to carry out, it is preferable that pH is 4.0 ~ 8.5.Material described in step of the present invention (3) washing, filter after should without or containing minimal amount of heteroion, heteroion includes Na+、Cl-、SO4 2-、NO3 -、K+Deng in one or more.
In step of the present invention (3), described material is after washing, filtering, filter cake is dried, and drying mode can adopt natural drying, oven drying, spray drying, microwave drying or infrared drying, and the drying condition being generally adopted is as follows: dry 1 ~ 15 hour at 50 ~ 150 DEG C.
In step of the present invention (4), method A obtains powder catalyst without molding roasting direct.Roasting condition described in method A is as follows: sintering temperature is 450 ~ 700 DEG C, and roasting time is 1 ~ 10 hour.
In step of the present invention (4), method B and the molding described in method C can carry out as required, are generally strip, cylindric, spherical, irregular strip, special-shaped ball etc., and granularity can be determined as required, is generally 0.5 ~ 8.0mm.In described forming process, it is possible to one or more in addition shaping assistant such as binding agent, peptization acid, extrusion aid etc. as required.
In step of the present invention (4), the drying condition described in method B is generally at 80 ~ 200 DEG C, and dry 1 ~ 15 hour, sintering temperature was generally 450 ~ 700 DEG C, and roasting time is generally 1 ~ 10 hour.
In step of the present invention (4), in method C, by material roasting under inert gas shielding of step (3) gained, described roasting condition is as follows: sintering temperature is 450 ~ 700 DEG C, and roasting time is 1 ~ 10 hour.Then then through molding, after drying, roasting under inert gas shielding, obtain catalyst, the drying condition after molding is as follows: at 80 ~ 200 DEG C, and dry 1 ~ 15 hour, roasting condition was as follows: sintering temperature is generally 450 ~ 700 DEG C, and roasting time is generally 1 ~ 10 hour.
In the present invention, carrying out roasting under inert gas shielding, selected noble gas is generally nitrogen or argon.
Catalyst of the present invention adopt nucleocapsid structure component be with the activated carbon of carrying transition metal be core, with the aluminium oxide (or amorphous silica-alumina) containing rare earth metal for shell, so make reactant elder generation and as after aluminium oxide (or amorphous silica-alumina) haptoreaction of shell, contact with the activated carbon as stratum nucleare again and react, making full use of the feature that aluminium oxide (or amorphous silica-alumina) aperture is big, pore volume is high, mechanical strength is good, the combination of the same aluminium oxide of rare earth metal auxiliary agent (or amorphous silica-alumina) can effectively improve the heat stability of aluminium oxide (or amorphous silica-alumina)；Make full use of the feature that activated carbon specific surface area is big, high adsorption capacity, reactivity are high simultaneously, activated carbon can better utilize the surface nature of activated carbon and the catalysis activity of transition metal with the combination of transition metal, makes catalyst have higher reactivity and stability in use.This catalyst is particularly useful as catalytic wet oxidation catalyst, especially the catalytic wet oxidation catalyst of Love psychology, the stability of activity and use to improve catalyst.
In the preparation process of catalyst of the present invention, pull an oar again process the activated carbon of carrying transition metal in particular by saccharide after, then introduce in preparing the aluminium oxide (or amorphous silica-alumina) the plastic process with rare-earth metal complex, saccharide is adsorbed on the surfaces externally and internally of activated carbon uniformly, make to be mixed in the carbohydrate breakdown carbonization in the middle of aluminium oxide (or amorphous silica-alumina) and activated carbon by follow-up roasting process, the activated carbon being newly formed connects aluminium oxide (or amorphous silica-alumina) and activated carbon, the combination making activated carbon and aluminium oxide (or amorphous silica-alumina) is tightr, furthermore owing to the adhesion of activated carbon Yu active metal is more weak, activated carbon elder generation supported active metals, carry out after adsorbing saccharide again in follow-up roasting process, preferential and active metal attachment the activated carbon of newly-generated activated carbon is combined, it is coated on around active metal, active metal is in free and half free state in aqueous phase, the loss of active metal is not be provided providing sufficiently active while, and add the adsorption activity position of activated carbon inner surface.Therefore, preferably increase saccharide and process activated carbon, aluminium oxide (or amorphous silica-alumina) closely coating active charcoal can be promoted, be conducive to improving mechanical strength and the abrasion resisting performance of catalyst, decrease the loss of active metal on activated carbon simultaneously, and improve the utilization rate of the inner surface of activated carbon, be conducive to improving activity and the stability of catalyst.
Catalyst preparation process of the present invention is simple, convenient, it is easy to operation, is suitable for commercial production.
The catalyst of the present invention is applicable to CWO course of reaction, adopt air, oxygen-enriched air, ozone or peroxide as oxidant, continuous way or batch (-type) process high concentrated organic wastewater, are particularly well-suited to the CWO process improving temperature and reaction pressure.Using catalyst treatment waste water of the present invention can effectively reduce COD, that improves waste water can biochemical values.
Detailed description of the invention
The specific surface area of product of the present invention and pore volume are to adopt low temperature liquid nitrogen physisorphtion to measure.Rate of wear is to adopt drum-type abrasion instrument to measure (to be specifically shown in " catalyst support preparation and application technology " (petroleum industry publishing house, in May, 2002, Zhu Hongfa writes, and 4.5.4 saves).Grained catalyst granularity adopts laser particle size analyzer to measure；Preformed catalyst granularity adopts sieve method to record.In the present invention, wt% is mass fraction.
Below in conjunction with the preparation method that specific embodiment further illustrates the present invention, but the scope of the present invention is not limited solely to the scope of these embodiments.
The character of commercially available powdery coconut husk charcoal used in the present invention is as follows: specific surface area 928m2/ g, pore volume 1.0cm3/ g, average pore radius 1.1nm, iodine sorption value 700mg/g, granularity 200 order.
Embodiment 1
Joining in distilled water by solid aluminum chloride, cerous nitrate, heating simultaneously is also stirred to dissolving, and obtains solution (a).Strong aqua ammonia is added appropriate distilled water diluting into about 10wt% weak ammonia (b).Powdery coconut husk charcoal uses the impregnation liquid containing Cu to impregnate, and 120 DEG C dry 240 minutes, and the lower 550 DEG C of roastings of nitrogen protection 4 hours add mix homogeneously in D/W, and liquid-solid volume ratio is 3:1, and then add water making beating, obtains serosity (c).After plastic cans adding (a) and being heated with stirring to 60 DEG C, open the valve of the container having (b), within controlling 10 minutes, system in tank is added drop-wise to pH=4.0, now in tank, add (c), continue dropping (b), in controlling 30 minutes, system in tank is added drop-wise to pH=8.0.Keeping temperature is 60 DEG C; pH=8.0; aging 1 hour; being filtered by material in tank, washing is to without chloride ion, filtering; filter cake is dried 10 hours at 110 DEG C; obtain catalyst material A-1, then roasting 5 hours under 550 DEG C of conditions under nitrogen protection, pulverize and sieve and obtain powder catalyst J-1.The amount of plastic agents useful for same is listed in table 1.
Take powder catalyst J-1100 gram, contact with the peptization liquid containing nitric acid and form paste, extruded moulding, then at 110 DEG C dry 10 hours, under nitrogen protection under 550 DEG C of conditions roasting 5 hours, obtain catalyst A, its composition is in Table 2.
Embodiment 2
Joining in distilled water by Solid aluminum sulfate, cerous nitrate, heating simultaneously is also stirred to dissolving, and obtains solution (a).Strong aqua ammonia is added appropriate distilled water diluting into about 10wt% weak ammonia (b).Powdery coconut husk charcoal uses the impregnation liquid containing Cu to impregnate, and 120 DEG C dry 240 minutes, and the lower 550 DEG C of roastings of nitrogen protection 4 hours add mix homogeneously in D/W, and liquid-solid volume ratio is 5:1, and then add water making beating, obtains activated carbon serosity (c).Take a plastic cans, after tank adding (a) and being heated with stirring to 60 DEG C, open the valve of the container having (b), within controlling 10 minutes, system in tank is added drop-wise to pH=4.0, open the valve of (c) container, continue dropping (b), in controlling 30 minutes, system in tank is added drop-wise to pH=8.0, control the valve of the container of (c), it is ensured that be now added dropwise to complete.Keeping temperature is 60 DEG C; pH=8.0; aging 1 hour; material in tank is filtered, washs to sulfate radical-free ion, filter; filter cake is dried 10 hours at 110 DEG C; obtain catalyst material A-2, then roasting 5 hours under 550 DEG C of conditions under nitrogen protection, pulverize and sieve and obtain powder catalyst J-2.The amount of plastic agents useful for same is listed in table 1.
Take catalyst material A-2100 gram, contact with the peptization liquid containing nitric acid and form paste, extruded moulding, then at 110 DEG C dry 10 hours, under nitrogen protection under 550 DEG C of conditions roasting 5 hours, obtain catalyst B, its composition is in Table 2.
Embodiment 3
Joining in distilled water by Solid aluminum sulfate, cerous nitrate, heating simultaneously is also stirred to dissolving, and obtains solution (a).It is 250gAl that solid sodium metaaluminate is configured to concentration2O3/ L sodium aluminate solution (b).Using the impregnation liquid containing Fe to impregnate powdery coconut husk charcoal, 120 DEG C dry 240 minutes, and the lower 550 DEG C of roastings of nitrogen protection 4 hours add mix homogeneously in aqueous sucrose solution, and liquid-solid volume ratio is 3:1, and then add water making beating, obtains serosity (c).Waterglass according to 1:2 dilution proportion in deionized water, be configured to solution (d).Take a plastic cans, insert the heating of 2L deionized water and stirring and add serosity (c) after 60 DEG C, open the valve of the container having (a), (b) simultaneously, control the pH=8.0 of system, in controlling 45 minutes, (a) is dripped off, close valve.Keeping temperature is 65 DEG C, pH=8.0, after stopping 20 minutes, adds solution (d) in system, calculates according to the content 55wt% of silicon dioxide in amorphous silica-alumina and added in 10 minutes.Then aging 1 hour, material in tank is filtered, washs to sulfate radical-free ion; filter, filter cake is dried 10 hours at 110 DEG C, obtains catalyst material A-3; then roasting 5 hours under 550 DEG C of conditions under nitrogen protection, pulverize and sieve and obtain powder catalyst J-3.The amount of plastic agents useful for same is listed in table 1.
Take catalyst material A-3100 gram, contact with the peptization liquid containing nitric acid and form paste, extruded moulding, then at 110 DEG C dry 10 hours, under nitrogen protection under 550 DEG C of conditions roasting 5 hours, obtain catalyst C, its composition is in Table 2.
Embodiment 4
Joining in distilled water by solid aluminum chloride, cerous nitrate, heating simultaneously is also stirred to dissolving, and obtains solution (a).Strong aqua ammonia is added appropriate distilled water diluting into about 10wt% weak ammonia (b).Powdery coconut husk charcoal uses the impregnation liquid containing Mn to impregnate, and 120 DEG C dry 240 minutes, and the lower 550 DEG C of roastings of nitrogen protection 4 hours add mix homogeneously in D/W, and liquid-solid volume ratio is 3:1, and then add water making beating, obtains activated carbon serosity (c).After plastic cans adding (a) and being heated with stirring to 60 DEG C, open the valve of the container having (b), within controlling 10 minutes, system in tank is added drop-wise to pH=4.0, now in tank, add (c), continue dropping (b), in controlling 30 minutes, system in tank is added drop-wise to pH=8.0.Keeping temperature is 60 DEG C; pH=8.0; aging 1 hour; being filtered by material in tank, washing is to without chloride ion, filtering; filter cake is dried 10 hours at 110 DEG C; obtain catalyst material A-4, then roasting 5 hours under 550 DEG C of conditions under nitrogen protection, pulverize and sieve and obtain powder catalyst J-4.The amount of plastic agents useful for same is listed in table 1.
Take catalyst material A-4100 gram, contact with the peptization liquid containing nitric acid and form paste, extruded moulding, then at 110 DEG C dry 10 hours, under nitrogen protection under 550 DEG C of conditions roasting 5 hours, obtain catalyst D, its composition is in Table 2.
Embodiment 5
Joining in distilled water by Solid aluminum sulfate, Lanthanum (III) nitrate, heating simultaneously is also stirred to dissolving, and obtains solution (a).Strong aqua ammonia is added appropriate distilled water diluting into about 10wt% weak ammonia (b).Powdery coconut husk charcoal uses the impregnation liquid containing Cu to impregnate, and 120 DEG C dry 240 minutes, and the lower 550 DEG C of roastings of nitrogen protection 4 hours add mix homogeneously in D/W, and liquid-solid volume ratio is 3:1, and then add water making beating, obtains activated carbon serosity (c).Take a plastic cans, after tank adding (a) and being heated with stirring to 60 DEG C, open the valve of the container having (b), within controlling 10 minutes, system in tank is added drop-wise to pH=4.0, open the valve of (c) container, continue dropping (b), in controlling 30 minutes, system in tank is added drop-wise to pH=8.0, control the valve of the container of (c), it is ensured that be now added dropwise to complete.Keeping temperature is 60 DEG C; pH=8.0; aging 1 hour; material in tank is filtered, washs to sulfate radical-free ion, filter; filter cake is dried 10 hours at 110 DEG C; obtain catalyst material A-5, then roasting 5 hours under 550 DEG C of conditions under nitrogen protection, pulverize and sieve and obtain powder catalyst J-5.The amount of plastic agents useful for same is listed in table 1.
Take catalyst material A-5100 gram, contact with the peptization liquid containing nitric acid and form paste, extruded moulding, then at 110 DEG C dry 10 hours, under nitrogen protection under 550 DEG C of conditions roasting 5 hours, obtain catalyst E, its composition is in Table 2.
Embodiment 6
Repeat the synthesis of embodiment 2, without saccharide in plastic process, prepare catalyst material A-6 and powder catalyst J-6.
Preformed catalyst is prepared with embodiment 2, obtains catalyst F, and its composition is in Table 2.
Embodiment 7
Repeat the synthesis of embodiment 3, without saccharide in plastic process, prepare catalyst material A-7 and powder catalyst J-7.
Preformed catalyst is prepared with embodiment 3, obtains catalyst G, and its composition is in Table 2.
Comparative example 1
Repeat the synthesis of embodiment 2, without activated carbon, transition metal and saccharide in plastic process, prepare comparative catalyst material PA-1 and powder catalyst DF-1, its appearance white.
Take catalyst material PA-1100 gram, contact with the peptization liquid containing nitric acid and form paste, extruded moulding, then dry 10 hours at 110 DEG C, roasting 5 hours under 550 DEG C of conditions, impregnate with the impregnation liquid containing Cu, then dry 10 hours at 110 DEG C, roasting 5 hours under 550 DEG C of conditions, obtain catalyst DA, and its composition is in Table 2.
Comparative example 2
Activated carbon 100g used in embodiment 2 is contacted with the peptization liquid containing nitric acid and forms paste, extruded moulding, then at 110 DEG C dry 10 hours, under nitrogen protection under 550 DEG C of conditions after roasting 5 hours, obtain carrier, its outward appearance is black.Impregnate with the impregnation liquid containing Ce-Cu, then at 110 DEG C dry 10 hours, under nitrogen protection under 550 DEG C of conditions roasting 5 hours, obtain catalyst DB, its composition is in Table 2.
Comparative example 3
By activated carbon used in embodiment 2 with carrier material PA-1 physical mixed; contact with the peptization liquid containing nitric acid and form paste; extruded moulding; then dry 10 hours at 110 DEG C; under nitrogen protection under 550 DEG C of conditions after roasting 5 hours; obtaining catalyst carrier DZ-C, wherein activated carbon is identical with embodiment 2 with alumina content, its outward appearance black.Impregnate with the impregnation liquid containing Cu, then at 110 DEG C dry 10 hours, under nitrogen protection under 550 DEG C of conditions roasting 5 hours, obtain catalyst DC, its composition is in Table 2.
Table 1 plastic reagent quality
| Bearer number | J-1 | J-2 | J-3 | J-4 | J-5 | J-6 | J-7 |
| Aluminium salt, g | 1559 | 1029 | 201 | 1210 | 578 | 1029 | 201 |
| Sugar, g | 13 | 39 | 225 | 10 | 78 | - | - |
| Activated carbon, g | 256 | 307 | 1242 | 198 | 402 | 322 | 1337 |
| Cerous nitrate, g | 90 | 77 | 181 | 73 | - | 77 | 181 |
| Lanthanum (III) nitrate, g | - | - | - | - | 60 | - | - |
The composition of table 2 catalyst and character
| Catalyst is numbered | A | B | C | D | E | F | G | DA | DB | DC |
| CeO2, wt% | 3.55 | 3.83 | 2.89 | 3.70 | - | 3.80 | 2.85 | 3.86 | 3.84 | 3.86 |
| CuO, wt% | 3.52 | 3.84 | - | - | 2.97 | 3.86 | - | 3.85 | 3.86 | 3.86 |
| Fe2O3, wt% | - | - | 2.76 | - | - | - | 2.80 | - | - | - |
| MnO2, wt% | - | - | - | 3.59 | - | - | - | - | - | - |
| La2O3, wt% | - | - | - | - | 2.87 | - | - | - | - | - |
| Specific surface area, m2/g | 386 | 437 | 469 | 386 | 393 | 415 | 444 | 251 | 774 | 394 |
| Pore volume, mL/g | 0.47 | 0.38 | 0.33 | 0.47 | 0.28 | 0.36 | 0.31 | 0.63 | 0.46 | 0.34 |
| Side pressure strength, N/cm | 225 | 193 | 173 | 234 | 176 | 179 | 143 | 232 | 52 | 169 |
| Abrasion, wt% | 0.51 | 0.62 | 0.80 | 0.65 | 0.71 | 0.79 | 0.80 | 0.32 | 4.88 | 0.94 |
By catalyst property in table 2 it can be seen that adopt the catalyst that saccharide obtains after processing activated carbon compared with the catalyst obtained without saccharide, bulk property is improved.
It is canescence by the outward appearance of the catalyst material of embodiment of the present invention gained and catalyst, without obvious black, illustrates that activated carbon becomes the core of catalyst.
In the present invention, adopt X-ray photoelectron spectroscopy (XPS) that the element of embodiment 2 and comparative example 1 gained catalyst material surface is analyzed.From analyzing result, the elementary composition and PA-1 composition on embodiment 2 gained catalyst material A2 surface is essentially identical, all has the elemental carbon of trace.This further illustrates, and the catalyst material of the present invention is with the activated carbon of carrying transition metal for core, with the aluminium oxide containing rare earth metal or amorphous silica-alumina for shell.
Catalyst prepared by the invention described above embodiment and comparative example is evaluated.Catalyst packing is in fixed bed reactors, with air for oxide isolation, certain oil plant phenol wastewater is carried out continuous way process.
Major pollutants COD:20000mg/L in waste water, free phenol: 0.7wt%.
Treatment conditions: volume space velocity 1.5h when temperature 200 DEG C, pressure 6.0MPa, gas-liquid volume ratio 150, liquid-1.Catalyst uses the result of handled waste water after 10 hours to be listed in table 3.
Table 3 evaluation result
| Catalyst is numbered | B | C | F | G | DA | DB | DC |
| COD, mg/L | 455 | 457 | 547 | 564 | 685 | 394 | 582 |
| Free phenol, mg/L | 0.58 | 0.59 | 0.68 | 0.57 | 2.54 | 0.49 | 1.24 |
| BOD/COD | 0.62 | 0.53 | 0.52 | 0.50 | 0.41 | 0.64 | 0.48 |
From table 3 evaluation result it can be seen that adopt catalyst prepared by the inventive method, in waste water, COD reduces amplitude relatively greatly, and BOD/COD substantially increases.
Adopting the catalyst that the embodiment of the present invention is prepared with comparative example to process above-mentioned waste water under identical process conditions, after using 1000 hours, evaluation result is listed in table 4.
Table 4 estimation of stability result
| Catalyst is numbered | B | C | F | G | DA | DB | DC |
| COD, mg/L | 525 | 548 | 670 | 705 | 887 | 1536 | 868 |
| Free phenol, mg/L | 0.54 | 0.71 | 1.35 | 1.66 | 8.37 | 20.64 | 2.10 |
| BOD/COD | 0.67 | 0.54 | 0.53 | 0.50 | 0.40 | 0.23 | 0.41 |
| CeO in catalyst2, wt% | 3.78 | 2.64 | 3.74 | 2.61 | 3.81 | 2.02 | 2.89 |
| CuO in catalyst2, wt% | 3.82 | - | 3.78 | - | 3.77 | 2.14 | 2.98 |
| Fe in catalyst2O3, wt% | - | 2.53 | - | 2.42 | - | - | - |
By table 4 result it can be seen that use the catalyst prepared of the inventive method to have good stability, and in catalyst the loss of active metal be improved significantly.
Claims (22)
1. a catalytic wet oxidation catalyst, including following nucleocapsid structure component, this nucleocapsid structure component is with the activated carbon of carrying transition metal for core, with the aluminium oxide containing rare earth metal or the amorphous silica-alumina containing rare earth metal for shell, with the weight of activated carbon and aluminium oxide or activated carbon and amorphous silica-alumina for benchmark, activated carbon accounts for 10% ~ 70%, and aluminium oxide or amorphous silica-alumina account for 30% ~ 90%.
2. the catalyst described in claim 1, it is characterised in that: with the weight of activated carbon and aluminium oxide or activated carbon and amorphous silica-alumina for benchmark, activated carbon accounts for 30% ~ 70%, and aluminium oxide or amorphous silica-alumina account for 30% ~ 70%.
3. the catalyst described in claim 1, it is characterised in that: described transition metal is one or more in the base metal in the 4th and 5 cycles in the periodic table of elements, and the granularity of described activated carbon is 150 order ~ 300 orders.
4. the catalyst described in claim 1, it is characterised in that: described transition metal is selected from one or more in vanadium, chromium, manganese, ferrum, cobalt, copper and titanium；Described rare earth metal is one or more in lanthanum, cerium.
5. the catalyst described in claim 1, it is characterised in that: with the weight of catalyst for benchmark, the content of transition metal oxide is 1% ~ 15%, the content 1% ~ 15% of rare-earth oxide, and the content of activated carbon and aluminium oxide or amorphous silica-alumina is 70% ~ 98%.
6. the catalyst described in claim 1, it is characterised in that: with the weight of amorphous silica-alumina for benchmark, the weight content of silicon oxide is 10% ~ 90%, it is preferred to 30% ~ 70%.
7. the catalyst described in claim 1, it is characterised in that: described catalyst is the powder catalyst not needing molding, or preformed catalyst, and the granularity of powder catalyst is 0.05 ~ 0.20mm, and preformed catalyst granularity is 0.5 ~ 8.0mm.
8. the catalyst described in claim 1, it is characterised in that: the character of described preformed catalyst is as follows: specific surface area is 200 ~ 1000m2/ g, pore volume is 0.3 ~ 1.8cm3/ g, < 3wt%, side pressure strength is 100 ~ 250N/cm to rate of wear.
9. the catalyst described in claim 1, it is characterised in that: containing adjuvant component in described aluminium oxide or amorphous silica-alumina, described auxiliary agent is one or more in titanium, zirconium, magnesium, zinc, and the weight content counted with element is for less than 10%.
10. the preparation method of the arbitrary described catalyst of claim 1 ~ 8, including:
(1) activated carbon of carrying transition metal is pulled an oar；
(2) prepare in coprecipitation and the plastic process of aluminium oxide and rare-earth metal complex introduces the serosity that step (1) obtains；
(3) material after the plastic that step (2) obtains carry out aging, filter, washing, dry；
(4) material of step (3) gained is made catalyst.
11. in accordance with the method for claim 10, it is characterised in that: the material of step (3) gained is made catalyst and is at least adopted one of following method by step (4):
A, by the material of step (3) gained, roasting under inert gas shielding, obtain catalyst；
B, by the material forming of step (3) gained, after drying, roasting under inert gas shielding, obtain catalyst；
C, by material roasting under inert gas shielding of step (3) gained, then then through molding, after drying, roasting under inert gas shielding, obtain catalyst.
12. according to the method that claim 10 is stated, it is characterised in that: the character of step (1) described activated carbon is as follows: specific surface area 500 ~ 3000m2/ g, pore volume 0.5 ~ 1.8cm3/ g, average pore radius 1 ~ 10nm, granularity is 150 order ~ 300 orders.
13. in accordance with the method for claim 10, it is characterised in that the making beating of activated carbon described in step (1) adopt add water, one or more in low-carbon alcohols are pulled an oar, wherein low-carbon alcohols is carbon number is one or more in the monohydric alcohol of 1 ~ 5.
14. in accordance with the method for claim 10, it is characterised in that the activated carbon of the carrying transition metal described in step (1) first adopts saccharide to process, and then pulls an oar, described saccharide is carbon number is one or more in the saccharide of 3 ~ 20.
15. in accordance with the method for claim 14, it is characterised in that described saccharide consumption accounts for the 2% ~ 50% of activated carbon weight, it is preferred to 5% ~ 20%.
16. in accordance with the method for claim 14, it is characterised in that described saccharide is one or more in triose, tetrose, pentose, hexose, maltose, glucose, sucrose, it is preferred to one or more in glucose, sucrose.
17. in accordance with the method for claim 14, it is characterized in that: it is directly mixed with activated carbon by saccharide that saccharide processes activated carbon, or saccharide is dissolved in solvent and adds activated carbon, solvent therein is water, carbon number be 1 ~ 5 monohydric alcohol in one or more；When saccharide processes activated carbon, its liquid-solid volume ratio is below 10.
18. in accordance with the method for claim 10, it is characterised in that: the complex plastic process of the aluminium oxide described in step (2) or amorphous silica-alumina and rare earth metal adopts the mode of the continuous acid-base titration of soda acid, or adopts two kinds of materials and flow the mode of neutralization.
19. in accordance with the method for claim 10, it is characterised in that: in the complex plastic process of the aluminium oxide described in step (2) or amorphous silica-alumina and rare earth metal, introduce adjuvant component, namely titanium, zirconium, magnesium, one or more in zinc.
20. in accordance with the method for claim 10, it is characterised in that: in step (2), the incorporation way of the serosity of step (1) gained adopts the one or more combination of following manner: this serosity, in plastic process, is continuously added in plastic cans by (1)；(2) this serosity is charged first in plastic cans, then carries out plastic reaction；(3) this serosity is mixed with one or more of plastic material, then carry out plastic reaction.
21. in accordance with the method for claim 10, it is characterised in that: in step (3), described drying condition is as follows: dry 1 ~ 15 hour at 50 ~ 150 DEG C.
22. in accordance with the method for claim 11, it is characterized in that: in step (4), roasting condition described in method A is as follows: sintering temperature is 450 ~ 700 DEG C, roasting time is 1 ~ 10 hour, drying condition described in method B is at 80 ~ 200 DEG C, dry 1 ~ 15 hour, sintering temperature was 450 ~ 700 DEG C, and roasting time is 1 ~ 10 hour；In method C; by material roasting under inert gas shielding of step (3) gained, described roasting condition is as follows: sintering temperature is 450 ~ 700 DEG C, and roasting time is 1 ~ 10 hour; then then through molding; after drying, roasting under inert gas shielding, obtain catalyst; drying condition after molding is as follows: at 80 ~ 200 DEG C; dry 1 ~ 15 hour, roasting condition was as follows: sintering temperature is 450 ~ 700 DEG C, and roasting time is 1 ~ 10 hour.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201410706805.8A CN105709743B (en) | 2014-12-01 | 2014-12-01 | A kind of catalytic wet oxidation catalyst and its preparation method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201410706805.8A CN105709743B (en) | 2014-12-01 | 2014-12-01 | A kind of catalytic wet oxidation catalyst and its preparation method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN105709743A true CN105709743A (en) | 2016-06-29 |
| CN105709743B CN105709743B (en) | 2018-05-11 |
Family
ID=56145784
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201410706805.8A Active CN105709743B (en) | 2014-12-01 | 2014-12-01 | A kind of catalytic wet oxidation catalyst and its preparation method |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN105709743B (en) |
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108014806A (en) * | 2017-12-28 | 2018-05-11 | 广东粤能净环保科技有限公司 | A kind of method using waste acetic acid catalytic wet oxidation catalyst |
| CN108114726A (en) * | 2017-12-28 | 2018-06-05 | 广东粤能净环保科技有限公司 | The method that catalytic wet oxidation catalyst is prepared using waste acetic acid |
| CN108114728A (en) * | 2017-12-28 | 2018-06-05 | 广东粤能净环保科技有限公司 | A kind of method that catalytic wet oxidation catalyst is prepared with waste acetic acid |
| WO2019192179A1 (en) * | 2018-04-04 | 2019-10-10 | 清华大学 | Double-carrier ozone catalyst and modular catalytic oxidation wastewater treatment device |
| CN110433871A (en) * | 2019-08-09 | 2019-11-12 | 宜兴国际环保城科技发展有限公司 | A kind of disintegration-type tubular type free-radical oxidation method for preparing catalyst |
| WO2021218176A1 (en) * | 2020-04-28 | 2021-11-04 | 浙江卫星能源有限公司 | Yolk-shell sio2-al2o3 noble metal propane dehydrogenation catalyst and preparation method therefor |
Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1292304A (en) * | 2000-10-20 | 2001-04-25 | 清华大学 | Non-noble metal catalyst for catalytic wet oxidation and its preparation method |
| CN101185887A (en) * | 2007-12-20 | 2008-05-28 | 上海交通大学 | Catalyst for wet oxidation technique and preparation method thereof |
| CN101862684A (en) * | 2010-05-07 | 2010-10-20 | 大连理工大学 | Aluminum oxide-activated carbon composite carrier, preparation method and prepared catalyst |
| CN101890333A (en) * | 2010-07-06 | 2010-11-24 | 浙江大学 | Alumina membrane coated activated carbon and preparation method thereof |
| CN102125842A (en) * | 2010-01-19 | 2011-07-20 | 华东理工大学 | Multiphase wet oxidation catalyst and preparation method thereof |
| CN103041818A (en) * | 2011-10-17 | 2013-04-17 | 中国石油化工股份有限公司 | Preparation method of catalytic wet oxidation catalyst and treatment method of organic wastewater |
-
2014
- 2014-12-01 CN CN201410706805.8A patent/CN105709743B/en active Active
Patent Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1292304A (en) * | 2000-10-20 | 2001-04-25 | 清华大学 | Non-noble metal catalyst for catalytic wet oxidation and its preparation method |
| CN101185887A (en) * | 2007-12-20 | 2008-05-28 | 上海交通大学 | Catalyst for wet oxidation technique and preparation method thereof |
| CN102125842A (en) * | 2010-01-19 | 2011-07-20 | 华东理工大学 | Multiphase wet oxidation catalyst and preparation method thereof |
| CN101862684A (en) * | 2010-05-07 | 2010-10-20 | 大连理工大学 | Aluminum oxide-activated carbon composite carrier, preparation method and prepared catalyst |
| CN101890333A (en) * | 2010-07-06 | 2010-11-24 | 浙江大学 | Alumina membrane coated activated carbon and preparation method thereof |
| CN103041818A (en) * | 2011-10-17 | 2013-04-17 | 中国石油化工股份有限公司 | Preparation method of catalytic wet oxidation catalyst and treatment method of organic wastewater |
Cited By (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108014806A (en) * | 2017-12-28 | 2018-05-11 | 广东粤能净环保科技有限公司 | A kind of method using waste acetic acid catalytic wet oxidation catalyst |
| CN108114726A (en) * | 2017-12-28 | 2018-06-05 | 广东粤能净环保科技有限公司 | The method that catalytic wet oxidation catalyst is prepared using waste acetic acid |
| CN108114728A (en) * | 2017-12-28 | 2018-06-05 | 广东粤能净环保科技有限公司 | A kind of method that catalytic wet oxidation catalyst is prepared with waste acetic acid |
| CN108014806B (en) * | 2017-12-28 | 2020-10-30 | 广东粤能净环保科技有限公司 | Method for preparing wet catalytic oxidation catalyst by using waste catalytic cracking catalyst |
| CN108114728B (en) * | 2017-12-28 | 2020-10-30 | 广东粤能净环保科技有限公司 | Method for preparing wet catalytic oxidation catalyst by using waste catalytic cracking catalyst |
| CN108114726B (en) * | 2017-12-28 | 2020-10-30 | 广东粤能净环保科技有限公司 | Method for preparing wet catalytic oxidation catalyst by using waste catalytic cracking catalyst |
| WO2019192179A1 (en) * | 2018-04-04 | 2019-10-10 | 清华大学 | Double-carrier ozone catalyst and modular catalytic oxidation wastewater treatment device |
| CN110433871A (en) * | 2019-08-09 | 2019-11-12 | 宜兴国际环保城科技发展有限公司 | A kind of disintegration-type tubular type free-radical oxidation method for preparing catalyst |
| WO2021218176A1 (en) * | 2020-04-28 | 2021-11-04 | 浙江卫星能源有限公司 | Yolk-shell sio2-al2o3 noble metal propane dehydrogenation catalyst and preparation method therefor |
Also Published As
| Publication number | Publication date |
|---|---|
| CN105709743B (en) | 2018-05-11 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN105618066A (en) | Catalytic wet oxidation catalyst and preparation method thereof | |
| CN104667916A (en) | Method for preparing catalytic wet oxidation catalyst | |
| CN105712466A (en) | Ozone catalytic wet oxidation method for phenol-containing waste water | |
| CN105709743A (en) | Catalytic wet oxidation catalyst and preparation method thereof. | |
| CN104667935B (en) | Catalytic wet oxidation catalyst and preparation method thereof | |
| CN104667985B (en) | A kind of catalytic wet oxidation catalyst and preparation method thereof | |
| CN105709737A (en) | Catalytic wet oxidation catalyst and preparation method thereof | |
| CN104667936B (en) | Method for preparing catalytic wet oxidation catalyst | |
| CN105709744A (en) | Method for preparing catalytic wet oxidation catalyst | |
| CN105712460A (en) | Catalytic wet oxidation method for phenol-containing wastewater | |
| CN104667922A (en) | Method for preparing noble metal catalyst for catalytic wet oxidation | |
| CN105709746A (en) | Catalytic wet oxidation catalyst and preparation method thereof | |
| CN105709732A (en) | Noble metal catalyst for catalytic wet oxidation and preparation method thereof | |
| CN104667933B (en) | Method for preparing wet oxidation catalyst | |
| CN105709730A (en) | Precious metal catalyst used for catalytic wet oxidation and preparation method thereof | |
| CN105618040A (en) | Preparation method of precious metal catalyst used for catalytic wet oxidation | |
| CN105709776A (en) | Method for preparing catalytic wet oxidation catalyst | |
| CN105618067A (en) | Preparation method of catalytic wet oxidation catalyst | |
| CN104667988B (en) | Catalyst carrier material, catalyst carrier and preparation method thereof | |
| CN104667994B (en) | Method for preparing catalytic wet oxidation catalyst carrier | |
| CN105709733A (en) | Noble metal catalyst for catalytic wet oxidation and preparation method thereof | |
| CN105618041A (en) | Preparation method of precious metal catalyst used for catalytic wet oxidation | |
| CN104667986A (en) | Method for preparing catalytic wet oxidation catalyst carrier | |
| CN104667993B (en) | catalyst carrier material, catalyst carrier and preparation method thereof | |
| CN104667934A (en) | Method for preparing catalytic wet oxidation catalyst |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| CB02 | Change of applicant information |
Address after: No. 1, Tieshan Street innovation road, Lushun mouth District, Dalian, Liaoning Applicant after: Dalian Frip science and Technology Co., Ltd. Address before: The eastern section of Dandong road 113001 in Liaoning province Fushun City Wanghua District No. 31 Applicant before: FUSHUN HUANKE PETROCHEMICAL TECHNOLOGY DEVELOPMENT CO., LTD. |
|
| CB02 | Change of applicant information | ||
| GR01 | Patent grant | ||
| GR01 | Patent grant |