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CN114713294B - A treatment system and method for waste antimony pentachloride catalyst - Google Patents

A treatment system and method for waste antimony pentachloride catalyst Download PDF

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CN114713294B
CN114713294B CN202110012627.9A CN202110012627A CN114713294B CN 114713294 B CN114713294 B CN 114713294B CN 202110012627 A CN202110012627 A CN 202110012627A CN 114713294 B CN114713294 B CN 114713294B
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hydrolysis
inlet
waste
antimony pentachloride
catalyst
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CN114713294A (en
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刘钱
谢小刚
白鑫
曾本忠
陈炯
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Zhonghao Chenguang Research Institute of Chemical Industry Co Ltd
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Zhonghao Chenguang Research Institute of Chemical Industry Co Ltd
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J38/00Regeneration or reactivation of catalysts, in general
    • B01J38/48Liquid treating or treating in liquid phase, e.g. dissolved or suspended
    • B01J38/64Liquid treating or treating in liquid phase, e.g. dissolved or suspended using alkaline material; using salts
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J38/00Regeneration or reactivation of catalysts, in general
    • B01J38/48Liquid treating or treating in liquid phase, e.g. dissolved or suspended
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/584Recycling of catalysts

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Catalysts (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

本发明涉及废催化剂回收技术领域,具体涉及一种废五氯化锑催化剂的处理系统及处理方法。所述处理系统包括水解装置、离心装置、干燥装置;所述水解装置内设有搅拌装置,其顶部设有废催化剂进口、碱液进口、氧化剂进口和进水口,侧壁设有清液出口,底部设有浆液出口;所述水解装置的浆液出口与离心装置的入口相连;所述离心装置的固相出口与干燥装置的入口相连。该处理系统工艺流程简单,降低目前废催化剂处理的能耗成本,并且在碱性条件下水解反应,水解釜的材质无需耐酸,大大降低设备投资,同时具有密闭性、安全性、自动化程度高的优点,废水、废气均严格处理,达标排放,可在二氟一氯甲烷生产中得到广泛应用。

The present invention relates to the technical field of waste catalyst recovery, and specifically to a treatment system and method for waste antimony pentachloride catalyst. The treatment system comprises a hydrolysis device, a centrifugal device, and a drying device; the hydrolysis device is provided with a stirring device, and the top is provided with a waste catalyst inlet, an alkali liquid inlet, an oxidant inlet, and a water inlet, the side wall is provided with a clear liquid outlet, and the bottom is provided with a slurry outlet; the slurry outlet of the hydrolysis device is connected to the inlet of the centrifugal device; the solid phase outlet of the centrifugal device is connected to the inlet of the drying device. The treatment system has a simple process flow, reduces the energy consumption cost of the current waste catalyst treatment, and the hydrolysis reaction is carried out under alkaline conditions, and the material of the hydrolysis kettle does not need to be acid-resistant, which greatly reduces the equipment investment. At the same time, it has the advantages of airtightness, safety, and high degree of automation. Wastewater and waste gas are strictly treated and discharged up to the standard, and can be widely used in the production of difluoromonochloromethane.

Description

Treatment system and treatment method for waste antimony pentachloride catalyst
Technical Field
The invention relates to the technical field of waste catalyst recovery, in particular to a treatment system and a treatment method of a waste antimony pentachloride catalyst.
Background
The activity of the catalyst antimony pentachloride used in the production of the difluoro-chloromethane gradually decreases after a period of reaction until part of the catalyst loses activity to become antimony pentafluoride, so that part of the catalyst in the reaction kettle needs to be replaced after a period of reaction.
The waste antimony pentachloride catalyst contains chloroform, antimony pentachloride, antimony trichloride, antimony pentafluoride and other organic high-boiling substances, belongs to highly harmful substances, and generates a large amount of toxic and harmful gases in the hydrolysis process, and the existing treatment method has the disadvantages of long process flow, high energy consumption and high separation difficulty, and cannot meet the increasingly high requirements of society on automation, safety, environmental protection, energy conservation of chemical industry, environmental protection devices and the like.
Disclosure of Invention
Aiming at the problems, the invention provides a treatment system and a treatment method for waste antimony pentachloride catalyst in the production process of difluoromethane.
Specifically, the invention provides the following technical scheme:
a treatment system of waste antimony pentachloride catalyst comprises a hydrolysis device, a centrifugal device and a drying device;
The hydrolysis device is internally provided with a stirring device, the top of the hydrolysis device is provided with a spent catalyst inlet, an alkali liquor inlet, an oxidant inlet and a water inlet, the side wall of the hydrolysis device is provided with a clear liquid outlet, and the bottom of the hydrolysis device is provided with a slurry outlet;
The slurry outlet of the hydrolysis device is connected with the inlet of the centrifugal device;
the solid phase outlet of the centrifugal device is connected with the inlet of the drying device.
Preferably, in the above treatment system, the hydrolysis device is further provided with an exhaust port, the exhaust port of the hydrolysis device is connected with a water caustic washing system, and the water caustic washing system is used for treating acid gas by water caustic washing and collecting the acid gas.
Preferably, in the above treatment system, the clear liquid outlet of the hydrolysis device is connected to a spent caustic tank.
Preferably, in the above processing system, the centrifugal device is a horizontal scraper discharge centrifugal machine, and the drying device is a double-cone rotary vacuum dryer. After hydrolysis, a horizontal scraper discharge centrifuge and a double-cone rotary vacuum dryer are adopted for post treatment, the whole system is not easy to be blocked (sodium fluoride, sodium chloride and the like are easy to crystallize), and the drying efficiency is high.
Preferably, the treatment system further comprises a plasma pyrolysis device, and the liquid phase outlet of the centrifugal device is connected with the plasma pyrolysis device.
Preferably, in the above processing system, the drying device is provided with an exhaust port, and the exhaust port of the drying device is connected with the plasma pyrolysis device.
The invention also provides a treatment method of the waste antimony pentachloride catalyst, which comprises the following steps:
(1) Adding industrial water into a hydrolysis device, and further adding sodium hydroxide solution to adjust the pH value to be more than 10;
(2) Continuously adding a waste antimony pentachloride catalyst and hydrogen peroxide into the hydrolysis device respectively, keeping a certain temperature and stirring speed for hydrolysis reaction, and enabling acid gas generated in the reaction to enter a water alkali washing system for water alkali washing treatment;
(3) Standing the feed liquid after the hydrolysis reaction, separating clear liquid from slurry, allowing the clear liquid to enter a waste alkali tank, allowing the slurry to enter a centrifugal machine for solid-liquid separation, allowing the separated liquid phase to enter a plasma cracking device, and allowing the separated solid phase to enter a dryer for drying treatment;
wherein, in the hydrolysis reaction, the pH value of the reaction system is kept above 10 by adding sodium hydroxide solution.
Preferably, in the above treatment method, the temperature of the hydrolysis reaction is 50 to 60 ℃.
Preferably, in the above treatment method, the mass ratio of the total addition amount of the waste antimony pentachloride catalyst to the industrial water is 1-5:10;
and/or the molar flow ratio of Sb 3+ in the continuously added waste antimony pentachloride catalyst to the hydrogen peroxide is 1.8-2.2:3, preferably 2:3.
The beneficial effects obtained by the invention are as follows:
The treatment system of the waste antimony pentachloride catalyst provided by the invention has the advantages of simple process flow, reduced energy consumption cost of the existing waste catalyst treatment, no acid resistance of materials of a hydrolysis kettle, greatly reduced equipment investment, improved economic benefit and environmental benefit of enterprises, high tightness, safety and high degree of automation, and strict treatment of waste water and waste gas, standard emission, and wide application in difluoromethane production.
Drawings
FIG. 1 is a schematic diagram of the apparatus described in example 1, wherein 1, a hydrolysis kettle, 2, a horizontal scraper discharge centrifuge, 3, a double-cone rotary vacuum dryer, 4, a water alkali washing system, 5, a waste alkali tank, 6, a fluorine-containing wastewater treatment device, 7, and a plasma pyrolysis device.
Detailed Description
The following examples are illustrative of the invention and are not intended to limit the scope of the invention. The specific techniques or conditions are not identified in the examples and are described in the literature in this field or are carried out in accordance with the product specifications.
In the description of the present invention, unless otherwise indicated, the terms "upper," "lower," and the like refer to an orientation or state relationship based on that shown in the drawings, for convenience of description and simplicity of description, and do not indicate or imply that the devices or elements referred to must have a particular orientation, be constructed and operated in a particular orientation, and thus should not be construed as limiting the invention.
In the following examples, the equipment and the like used were conventional products available for purchase by a regular channel manufacturer, without specifying the manufacturer. The methods are conventional methods unless otherwise specified, and the starting materials are commercially available from the public sources unless otherwise specified.
In the following examples, the waste antimony pentachloride used was derived from an F22 reactor, about 30% of the waste antimony pentachloride (the proportion of Sb3+ in the waste antimony pentachloride was about 20%), 60% of chloroform, 1% of hydrogen chloride, 4% of hydrogen fluoride, the balance F21 and the like.
Example 1
As shown in fig. 1, embodiment 1 provides a treatment system of waste antimony pentachloride catalyst in a difluoromethane production process, which comprises a hydrolysis kettle 1, a horizontal scraper discharge centrifuge 2, a double-cone rotary vacuum dryer 3, a water alkali washing system 4, a waste alkali tank 5, a fluorine-containing wastewater treatment device 6 and a plasma cracking device 7;
the hydrolysis kettle 1 is internally provided with a stirring device, the top of the hydrolysis kettle is provided with a waste antimony pentachloride catalyst inlet, a sodium hydroxide solution inlet, a hydrogen peroxide solution inlet and an industrial water inlet, the side wall of the hydrolysis kettle is provided with a clear liquid outlet, and the bottom of the hydrolysis kettle is provided with a slurry outlet;
The hydrolysis kettle 1 is also provided with an exhaust port, and the exhaust port of the hydrolysis kettle 1 is connected with a water alkali washing system 4;
the clear liquid outlet of the hydrolysis kettle 1 is sequentially connected with a waste alkali tank 5 and a fluorine-containing wastewater treatment device 6;
The slurry outlet of the hydrolysis kettle 1 is connected with the inlet of a horizontal scraper discharge centrifuge 2;
The horizontal scraper discharging centrifugal machine 2 is provided with a solid phase outlet and a liquid phase outlet, the solid phase outlet is connected with the double-cone rotary vacuum dryer 3, and the liquid phase outlet is connected with the plasma pyrolysis device 7;
The bipyramid gyration vacuum dryer 3 is equipped with the gas vent, and this gas vent is connected with the plasma pyrolysis device 7.
Example 2
The method for treating the waste antimony pentachloride catalyst by using the treatment system in the embodiment 1 comprises the following specific steps:
2000kg of industrial water is added into a hydrolysis kettle 1 (made of carbon steel, V=5m 3), 15r/min stirring is started, about 400kg of 15% sodium hydroxide aqueous solution is prepared and added into the hydrolysis kettle 1, cooling circulating water in a jacket on the side wall of the hydrolysis kettle 1 is opened, 600kg of waste antimony pentachloride catalyst is slowly added into the hydrolysis kettle at a rate of 300kg/h through a level difference, hydrogen peroxide is added at a rate of 1m 3/h while the waste antimony pentachloride catalyst is added, the pH value is automatically monitored, and if the pH value is reduced to 10, 0.1m 3 of 15% sodium hydroxide aqueous solution is automatically added, so that the solution in the hydrolysis kettle is always alkaline. After the addition, the stirring is closed, the mixture is cooled to normal temperature, and acid gases such as HF, HCl and the like generated in the hydrolysis process enter a water alkali washing system 4 for treatment and then are discharged after reaching standards.
The upper inorganic clear liquid in the hydrolysis kettle 1 is discharged into a waste alkali tank 5 and then is conveyed to a fluorine-containing wastewater treatment device 6 through a pump, the rest of pasty substances, organic phases and a small amount of inorganic phases enter a horizontal scraper discharge centrifuge 2, the pasty substances are separated out at the rotating speed of 3500-5000 r/min, the organic phases and the small amount of inorganic phases are conveyed to a plasma cracking device 7 for treatment, the pasty substances are conveyed to a double-cone rotary vacuum dryer 3 for micro-negative pressure and drying at 120-150 ℃ to obtain a finished product (about 60kg, and the antimony pentoxide content is about 60-70%), and the dried waste gas is conveyed to the ion cracking device 7 for treatment.
While the invention has been described in detail in the foregoing general description, embodiments and experiments, it will be apparent to those skilled in the art that modifications and improvements can be made thereto. Accordingly, such modifications or improvements may be made without departing from the spirit of the invention and are intended to be within the scope of the invention as claimed.

Claims (10)

1.一种二氟一氯甲烷生产中使用的废五氯化锑催化剂的处理系统,其特征在于,包括水解装置、离心装置、干燥装置;1. A system for treating waste antimony pentachloride catalyst used in the production of difluoromonochloromethane, characterized by comprising a hydrolysis device, a centrifugal device, and a drying device; 所述水解装置内设有搅拌装置,其顶部设有废催化剂进口、碱液进口、氧化剂进口和进水口,侧壁设有清液出口,底部设有浆液出口;The hydrolysis device is provided with a stirring device, a waste catalyst inlet, an alkali solution inlet, an oxidant inlet and a water inlet are provided on the top, a clear liquid outlet is provided on the side wall, and a slurry outlet is provided on the bottom; 所述水解装置的浆液出口与离心装置的入口相连;The slurry outlet of the hydrolysis device is connected to the inlet of the centrifugal device; 所述离心装置的固相出口与干燥装置的入口相连;The solid phase outlet of the centrifugal device is connected to the inlet of the drying device; 所述水解装置的材质无需耐酸。The material of the hydrolysis device does not need to be acid-resistant. 2.根据权利要求1所述的处理系统,其特征在于,所述水解装置还设有排气口,所述水解装置的排气口与水碱洗系统相连,所述水碱洗系统用于水碱洗处理酸性气体并收集。2. The treatment system according to claim 1 is characterized in that the hydrolysis device is also provided with an exhaust port, and the exhaust port of the hydrolysis device is connected to a water alkali washing system, and the water alkali washing system is used for water alkali washing to treat and collect acidic gases. 3.根据权利要求1所述的处理系统,其特征在于,所述水解装置的清液出口与废碱槽相连。3. The treatment system according to claim 1 is characterized in that the clear liquid outlet of the hydrolysis device is connected to the spent alkali tank. 4.根据权利要求1所述的处理系统,其特征在于,所述离心装置为卧式刮刀卸料离心机。4. The processing system according to claim 1, characterized in that the centrifugal device is a horizontal scraper discharge centrifuge. 5.根据权利要求1所述的处理系统,其特征在于,所述干燥装置为双锥回转真空干燥器。5. The processing system according to claim 1, characterized in that the drying device is a double-cone rotary vacuum dryer. 6.根据权利要求1所述的处理系统,其特征在于,还包括等离子裂解装置,所述离心装置的液相出口与所述等离子裂解装置相连。6. The processing system according to claim 1, further comprising a plasma cracking device, wherein the liquid phase outlet of the centrifugal device is connected to the plasma cracking device. 7.根据权利要求6所述的处理系统,其特征在于,所述干燥装置设有排气口,所述干燥装置的排气口与所述等离子裂解装置相连。7 . The processing system according to claim 6 , wherein the drying device is provided with an exhaust port, and the exhaust port of the drying device is connected to the plasma cracking device. 8.一种废五氯化锑催化剂的处理方法,其特征在于,采用如权利要求1所述的处理系统并包括以下步骤:8. A method for treating a spent antimony pentachloride catalyst, characterized in that the treatment system according to claim 1 is used and the method comprises the following steps: (1)将工业水加入水解装置中,并进一步加入氢氧化钠溶液调节pH值为10以上;(1) Adding industrial water to the hydrolysis device, and further adding sodium hydroxide solution to adjust the pH value to above 10; (2)将废五氯化锑催化剂和双氧水分别连续加入所述水解装置,保持一定的温度和搅拌速度进行水解反应,反应中产生的酸性气体进入水碱洗系统进行水碱洗处理;(2) adding the waste antimony pentachloride catalyst and hydrogen peroxide to the hydrolysis device respectively and continuously, maintaining a certain temperature and stirring speed for hydrolysis reaction, and the acidic gas generated in the reaction enters the water alkali washing system for water alkali washing treatment; (3)水解反应后的料液静置,进行清液和浆液的分离,清液进入废碱罐,浆液进入离心机固液分离,分离出的液相进入等离子裂解装置,分离出的固相进入干燥器进行干燥处理;(3) The liquid after the hydrolysis reaction is allowed to stand to separate the clear liquid and the slurry. The clear liquid enters the waste alkali tank, and the slurry enters the centrifuge for solid-liquid separation. The separated liquid phase enters the plasma cracking device, and the separated solid phase enters the dryer for drying. 其中,水解反应中,通过补加氢氧化钠溶液,使反应体系的pH值保持在10以上。During the hydrolysis reaction, the pH value of the reaction system is maintained above 10 by adding sodium hydroxide solution. 9.根据权利要求8所述的处理方法,其特征在于,所述水解反应的温度为50~60℃。9. The treatment method according to claim 8, characterized in that the temperature of the hydrolysis reaction is 50-60°C. 10.根据权利要求8或9所述的处理方法,其特征在于,所述废五氯化锑催化剂的总加入量与所述工业水的质量比为1~5:10;10. The treatment method according to claim 8 or 9, characterized in that the mass ratio of the total amount of the waste antimony pentachloride catalyst added to the industrial water is 1-5:10; 和/或,连续加入的所述废五氯化锑催化剂中的Sb3+与所述双氧水的摩尔流量比为1.8~2.2:3。And/or, the molar flow ratio of Sb 3+ in the continuously added waste antimony pentachloride catalyst to the hydrogen peroxide is 1.8-2.2:3.
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Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102784611A (en) * 2012-08-03 2012-11-21 云南驰宏锌锗股份有限公司 Germanium tetrachloride fully-closed hydrolysis device
CN212425659U (en) * 2020-03-30 2021-01-29 乳源东阳光氟有限公司 Processing apparatus of abandonment antimony pentachloride
CN214974063U (en) * 2021-01-06 2021-12-03 中昊晨光化工研究院有限公司 Processing system of useless antimony pentachloride catalyst

Family Cites Families (15)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5945422B2 (en) * 1978-12-05 1984-11-06 日東化学工業株式会社 Method for regenerating antimony-containing oxide catalyst
US4411874A (en) * 1982-04-29 1983-10-25 Sca Services, Inc. Detoxification of spent antimony halide catalyst and recovery of antimony values
JPH0694372B2 (en) * 1987-01-28 1994-11-24 三菱マテリアル株式会社 Method for producing high-purity antimony pentoxide powder
DE3929263A1 (en) * 1989-09-02 1991-03-07 Kali Chemie Ag METHOD FOR PROCESSING ANTIMONE HALOGENIDE CATALYST SOLUTIONS
WO1991004955A1 (en) * 1989-10-04 1991-04-18 E.I. Du Pont De Nemours And Company Fluorocarbon purification process
JPH0532418A (en) * 1991-07-31 1993-02-09 Nippon Light Metal Co Ltd Method for producing crystalline antimony pentoxide hydrate
CN1031397C (en) * 1992-01-28 1996-03-27 锡矿山矿务局 Preparation of colloidal antimony pentoxide by chlorination hydrolysis method
DE10223112A1 (en) * 2002-05-21 2003-12-24 Ufz Leipzighalle Gmbh Removal of organic halogen compounds from water, especially ground water, involves hydrolysis of hardly volatile compounds to more volatile, partly dehydrohalogenated compounds in activated charcoal bed before stripping with gas
CN103114203B (en) * 2013-01-30 2014-12-03 巨化集团技术中心 Method for preparing sodium pyroantimonate by using waste antimony pentachloride as raw material
CN103408163B (en) * 2013-08-28 2014-11-26 山东东岳化工有限公司 Treatment method of waste liquid in production of organic fluoride
CN103820645B (en) * 2014-03-21 2015-06-17 山东腾跃化学危险废物研究处理有限公司 Antimony pentachloride waste liquid treatment system
US20200115809A1 (en) * 2017-09-19 2020-04-16 Calera Corporation Systems and methods using lanthanide halide
CN108458344B (en) * 2018-06-28 2023-09-26 中化蓝天霍尼韦尔新材料有限公司 Pretreatment equipment and treatment method of antimony pentachloride waste catalyst
CN110906335A (en) * 2018-09-18 2020-03-24 中昊晨光化工研究院有限公司 Method and device for treating waste catalyst in difluoroethane production
CN110902719A (en) * 2019-10-11 2020-03-24 江苏梅兰化工有限公司 Method for recovering antimony trioxide from difluorochloromethane reaction residual liquid

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102784611A (en) * 2012-08-03 2012-11-21 云南驰宏锌锗股份有限公司 Germanium tetrachloride fully-closed hydrolysis device
CN212425659U (en) * 2020-03-30 2021-01-29 乳源东阳光氟有限公司 Processing apparatus of abandonment antimony pentachloride
CN214974063U (en) * 2021-01-06 2021-12-03 中昊晨光化工研究院有限公司 Processing system of useless antimony pentachloride catalyst

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
废氟化催化剂五氯化锑资源化处理;杨仲苗;王树华;;化工生产与技术;20130825(04);第19-20页第3节 *
杨仲苗 ; 王树华 ; .废氟化催化剂五氯化锑资源化处理.化工生产与技术.2013,(04),第19-20页第3节,. *

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