CN1433842A - Gas-phase fluorinating method preparation for CoMo/TiQ2-Al2O3 dehydrogen desulfurization catalyst - Google Patents
Gas-phase fluorinating method preparation for CoMo/TiQ2-Al2O3 dehydrogen desulfurization catalyst Download PDFInfo
- Publication number
- CN1433842A CN1433842A CN 02101986 CN02101986A CN1433842A CN 1433842 A CN1433842 A CN 1433842A CN 02101986 CN02101986 CN 02101986 CN 02101986 A CN02101986 A CN 02101986A CN 1433842 A CN1433842 A CN 1433842A
- Authority
- CN
- China
- Prior art keywords
- catalyst
- tio
- carrier
- como
- fluoridizing
- 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 present invention discloses a preparation method for modifying hydrodesulphurization catalyst used in processing petroleum product and raising catalytic activity. Said method utilizes the freon wet air to make fluooration treatment of catalyst carrier TiO2-Al2O3, then the cobalt and molybdenum active components are loaded on the fluorated carrier so as to obtain the invented catalyst. As compared with solution impregnation method said invention adopts the freon to make gas-phase fluoration preparation or catalyst, and has the advantages of that it is easy to control, uniform, does not damage structure of catalyst and can obviously raise activity of catalyst.
Description
The present invention relates to the processing of oil product, specifically the Hydrobon catalyst that uses in the existing PETROLEUM PROCESSING is implemented modification, improve a kind of preparation method of catalytic activity.
Administering pollution, protecting environment is the significant problem that the our times various countries face jointly.In environmental pollution, the pollution of water and atmospheric environment is the most outstanding.In all pollution sources of water and atmosphere, chemical contamination is the most general.And in atmospheric environment was administered, oxysulfide was key objects because of causing acid rain, the vegeto-animal growth of destruction and corroding metal goods.Oxysulfide in the atmosphere mainly results from fuel engines institute exhaust gas discharged, but the source is an existing low amounts of organic sulfur thing in the fuel oil.Since the twentieth century, the global mobility vehicle sharply increases, and the consumption of vapour, diesel oil grows with each passing day, and the tail gas of engine emission can be on the rise to the pollution of environment, enters 21st century, and this situation can be more serious.Therefore, the basic outlet that reduces the atmospheric sulfer oxide contaminant is to remove and transform organic sulfur compound the fuel oil from the source, prepares eco-friendly clean fuel.
In recent years, developed countries such as U.S., moral, day, method all constantly propose strict restriction index to the quality, particularly sulfur content of fuel oil product in environmental legislation, require 2005 years to drop to 50ppm from present 300ppm.And also there is big gap in contrast to this in the quality of China's fuel oil product, and this is one of significant challenge that petrochemical enterprise in China is faced after the accession to WTO.Therefore, accelerate the development of China's oil chemical industry hydrotreatment technology, the quality that improves product has become the task of top priority.
It is exactly crucial process the PETROLEUM PROCESSING that the hydrotreatment process begins as the energy from oil, mainly refers to remove the various non-hydrocarbon component in the oil product, reduces the processing procedure of components such as sulfur-bearing, nitrogen in the oil product, comprises hydrodesulfurization, hydrodenitrogeneration etc.No matter hydrotreating catalyst passes by still is now heat subject in the catalyticing research always.The purpose of hydrotreatment process is to prevent the further catalyst poisoning of processing of oil product, reduces the discharging that causes air-polluting sulphur and nitrogen oxide, and the stability that improves oil product, prolongs the storage time.Along with the exhaustion of petroleum resources, the deep processing of petroleum resources and coal chemical develop rapidly and people to the improving constantly of environmental protection understanding of importance, the importance of hydrotreatment process will be more apparent outstanding in future.
Though the hydrotreating catalyst system of having reported is a lot, and some industrial process that also have been applied to, but the degree of depth of desulfurization, denitrogenation and stable aspect still unsatisfactory, so when seeking and developing new catalyst system and catalyzing, the modification or the improvement of existing catalyst is devoted in many researchs.
In hydrotreating catalyst, mix fluorine element, it is reported it is a kind of effectively method of modifying, but in all researchs in the past, what fluoridize was handled all employings is the ammonium fluoride solution infusion process, and the addition of fluorine is bigger, this once was proved and made the obvious negative effect that catalyst specific surface reduces and structure division destroys, and was difficult to reach the uniformity of fluoridizing.
Retrieval according to the interrelated data of Chinese patent shows, has not yet to see the relevant report that useful Organic fluoride chloride is handled Hydrobon catalyst.
The objective of the invention is to provide a kind of and existing Hydrobon catalyst is carried out fluorinated modified preparation method, thereby reach the purpose that improves catalyst hydrodesulfurization active with machine fluorochloride (fluorine Lyons).
The object of the present invention is achieved like this: a kind of CoMo/TiO
2-Al
2O
3The gas phase fluorination modification preparation of Hydrobon catalyst is characterized in that: by the carrier TiO of fluorine Lyons humid air to catalyst
2-Al
2O
3Carry out fluorination treatment, then on the carrier after fluoridizing again in the load cobalt and active component of cobalt make catalyst, specifically comprise:
Fluoridizing of carrier: used TiO
2/ γ-Al
2O
3Carrier contains TiO
21~100% (quality); Used fluorization agent is fluorine Lyons (CFC-12 content is 99%).Described freon is diluted to the mist that contains variable concentrations and adds a certain amount of water vapour by bubbling with air, and wherein the concentration of freon is 1~10%; The gaseous mixture of fluorinated agent is by the fixed bed of loading catalyst carrier, and the flow velocity of gaseous mixture is 10~100cm
3/ min, the temperature of fixed bed is controlled at 200~500 ℃; When fluoridizing, generally keep 0.5~3h under these conditions, best 50~70min switches to flow of dried air again after the time, treats to take out the sample drying preservation after it drops to room temperature naturally.
Preparation of catalysts: CoMo/TiO
2-Al
2O
3Active component cobalt and molybdenum are by conventional quantitatively immersion process for preparing in the catalyst.The TiO that fluoridized
2-Al
2O
3Carrier is earlier with the ammonium molybdate solution dipping, at room temperature placement 10~12h and behind 120 ℃ of oven dry 4~8h, at 450~550 ℃ of roasting 2~5h.And then the dipping cobalt nitrate that uses the same method; MoO in made each goods
3Be respectively 5~30% and 0.5~10% (weight) with CoO content.
Utilize fluorination process of the present invention also can directly carry out fluorination treatment, but its effect slightly is worse than the processing mode that first fluorinated support floods active component again to industrial catalyst.
The present invention adopts freon gas phase humid air fluoride process to replace villiaumite solution fluoridize method prepared catalyst that goes out under optimal conditions, and its BET specific area is 220~230m
2/ g; Its surface acidity is slightly than being lower than the catalyst of not fluoridizing; It is higher by 20~25% (at 310 ℃, 0.3g catalyst and 1.2cm than BY2 industrial catalyst to the hydrodesulfurization activity of thiophene
3Under/min thiophene the flow velocity).Therefore, compare, adopt fluorine Lyons that catalyst is carried out the gas phase fluorination tool and be easy to control, equal even advantages such as catalyst structure of not destroying with solution dipping method.So the present invention can reach the purpose of drafting.
Concrete preparation of the present invention and method are provided by following embodiment:
Take by weighing 8g by broken be 40~80 order particles and at the TiO of 500 ℃ of roasting 16h
2-Al
2O
3Carrier, the diameter of packing into are in the glass tube of 30mm, and (20ml/min) rose to 420 ℃ with the speed of 5 ℃/min during first air in drying flowed, and switched to the fluorine Lyons mist that contains 1% volumetric concentration then.Mist enters before the carrier and adds steam through Bubbling method, and saturator constant temperature is at 25 ℃, overall flow rate 50cm
3/ min.Switch to flow of dried air at 420 ℃ again after keeping 1h, treat that it drops to naturally to take out sample after the room temperature and put into the drier preservation;
Take by weighing the carrier after 5g fluoridizes, carry out incipient impregnation, place 24h under the room temperature, 120 ℃ of air-dry 4h, 500 ℃ of calcining 6h with the ammonia solution (1.0ml/g) of ammonium molybdate; With with quadrat method dipping cobalt nitrate (0.9ml/g), promptly obtain fluorination catalyst.
Zhi Bei catalyst and BY2 industrial catalyst like this, with a fixed-bed catalytic reactor, at loaded catalyst 0.3g, the hydrogen mixed gas flow velocity 40cm of thiophene volumetric concentration 3%
3/ min, reaction temperature is 310 ℃ to be estimated down, and the conversion ratio of thiophene is respectively 43% and 32%.
Claims (4)
1. CoMo/TiO
2-Al
2O
3The gas phase fluorination modification preparation of Hydrobon catalyst is characterized in that: by the carrier TiO of fluorine Lyons humid air to catalyst
2-Al
2O
3Carry out fluorination treatment, then on the carrier after fluoridizing again in the load cobalt and active component of cobalt make catalyst, specifically comprise:
Fluoridizing of carrier: used TiO
2/ γ-Al
2O
3Carrier contains TiO
21~100%; Used fluorization agent is fluorine Lyons; Described freon is diluted to the mist that contains variable concentrations and adds a certain amount of water vapour by bubbling with air, the gaseous mixture of fluorinated agent is by the fixed bed of loading catalyst carrier, keep 0.5~3h when fluoridizing, 50~70min switches to flow of dried air again after the time, treat that it drops to take out after the room temperature naturally to put into the drier preservation;
Preparation of catalysts: CoMo/TiO
2-Al
2O
3Active component cobalt and molybdenum are by conventional quantitatively immersion process for preparing, the TiO that fluoridized in the catalyst
2-Al
2O
3Carrier is earlier with the ammonium molybdate solution dipping, at room temperature placement 10~12h and behind 120 ℃ of oven dry 4~8h, at 450~550 ℃ of roasting 2~5h; And then the dipping cobalt nitrate that uses the same method.
2. CoMo/TiO according to claim 1
2-Al
2O
3The gaseous fluoridizing method preparation of Hydrobon catalyst, it is characterized in that: the concentration of freon is 1~10%, the flow velocity of gas is 10~100cm
3/ min;
3. CoMo/TiO according to claim 1
2-Al
2O
3The gaseous fluoridizing method preparation of Hydrobon catalyst, its feature: the temperature that is fixed bed is controlled at 200~500 ℃;
4. CoMo/TiO according to claim 1
2-Al
2O
3The gaseous fluoridizing method preparation of Hydrobon catalyst, its feature: the MoO in made each goods
3Be respectively 5~30% and 0.5~10wt% with CoO content.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CNB02101986XA CN1150989C (en) | 2002-01-23 | 2002-01-23 | Gas-phase fluorinating method preparation for CoMo/TiQ2-Al2O3 dehydrogen desulfurization catalyst |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CNB02101986XA CN1150989C (en) | 2002-01-23 | 2002-01-23 | Gas-phase fluorinating method preparation for CoMo/TiQ2-Al2O3 dehydrogen desulfurization catalyst |
Publications (2)
Publication Number | Publication Date |
---|---|
CN1433842A true CN1433842A (en) | 2003-08-06 |
CN1150989C CN1150989C (en) | 2004-05-26 |
Family
ID=27627429
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CNB02101986XA Expired - Fee Related CN1150989C (en) | 2002-01-23 | 2002-01-23 | Gas-phase fluorinating method preparation for CoMo/TiQ2-Al2O3 dehydrogen desulfurization catalyst |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN1150989C (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101590415B (en) * | 2008-05-30 | 2012-08-08 | 中国石油天然气股份有限公司 | Method for preparing load type Co or Ni and Mo or W catalyst |
CN107597152A (en) * | 2016-07-11 | 2018-01-19 | 中国石油天然气股份有限公司 | A kind of hydrogenation catalyst and preparation method thereof |
CN108137316A (en) * | 2014-10-31 | 2018-06-08 | 索尔维公司 | Catalyst including fluorinated metal oxide, production method and method for hydrogenation |
-
2002
- 2002-01-23 CN CNB02101986XA patent/CN1150989C/en not_active Expired - Fee Related
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101590415B (en) * | 2008-05-30 | 2012-08-08 | 中国石油天然气股份有限公司 | Method for preparing load type Co or Ni and Mo or W catalyst |
CN108137316A (en) * | 2014-10-31 | 2018-06-08 | 索尔维公司 | Catalyst including fluorinated metal oxide, production method and method for hydrogenation |
CN107597152A (en) * | 2016-07-11 | 2018-01-19 | 中国石油天然气股份有限公司 | A kind of hydrogenation catalyst and preparation method thereof |
Also Published As
Publication number | Publication date |
---|---|
CN1150989C (en) | 2004-05-26 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Wang et al. | Insights into co-doping effect of Sm and Fe on anti-Pb poisoning of Mn-Ce/AC catalyst for low-temperature SCR of NO with NH3 | |
WO2015149499A1 (en) | Low-temperature and highly efficient denitration catalyst and preparation method therefor | |
CN104080524B (en) | Absorption in ionic liquid for the NO and oxidation | |
JPH09103646A (en) | Method and apparatus for treating combustion exhaust gas | |
WO2012027948A1 (en) | Method for treating sulfur-containing gas and hydrogenation catalyst used in the method | |
CN105413715B (en) | Low-temperature denitration of flue gas is acidified the sulfur resistant catalyst and preparation method thereof of manganese cobalt cerium with composite carrier load type | |
CN102716753A (en) | Catalyst for low-temperature selective catalytic reduction of nitric oxide and preparation method of catalyst | |
CN103055694A (en) | Method for flue gas denitrification by organic waste gas | |
US4141959A (en) | Process for removing nitrogen oxides from combustion flue gas | |
Chen et al. | Deactivation effects of potassium on a CeMoTiO x catalyst for the selective catalytic reduction of NO x with NH3 | |
CN105521791B (en) | The preparation method of vulcanization type catalyst for selective hydrodesulfurizationof of gasoline | |
US7541010B2 (en) | Silver doped catalysts for treatment of exhaust | |
CN112973785B (en) | Catalyst for synergistically removing VOCs and NOx and preparation method thereof | |
CN104190478A (en) | Regeneration method of denitration desulfurization active carbon catalyst | |
CN110026182A (en) | Low-temperature denitration catalyst and its preparation and application in high sulfur resistive | |
CN106582740A (en) | Method for preparing heteropoly acid composite carbon material with popcorn as precursor for low-temperature removal of NOx | |
CN110026206A (en) | A kind of NH of the anti-ABS poisoning of new type low temperature3The preparation method and application of SCR catalyst | |
EP0643991B1 (en) | Nitrogen oxide decomposing catalyst and denitration method using the same | |
CN102527207B (en) | Method for removing multiple pollutants at the same time through electrostatic enhanced catalytic oxidation device used therein | |
KR101513834B1 (en) | A catalyst for selective catalytic reduction and a method for preparing the same | |
CN1150989C (en) | Gas-phase fluorinating method preparation for CoMo/TiQ2-Al2O3 dehydrogen desulfurization catalyst | |
CN110479245A (en) | A kind of molybdenum cerium support type catalyst for denitrating flue gas and its preparation method and application | |
KR100668926B1 (en) | Method of regenerating scr catalyst | |
CN110201694A (en) | A kind of regeneration method of residual hydrogenation decaying catalyst | |
JP2008272646A (en) | Hydrogenation catalyst re-activation method and manufacturing method of hydrogenation 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 | ||
C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
C19 | Lapse of patent right due to non-payment of the annual fee | ||
CF01 | Termination of patent right due to non-payment of annual fee |