CN106673055A - Method for recycling waste mercury catalyst from polyvinyl chloride production based on calcium carbide method - Google Patents

Method for recycling waste mercury catalyst from polyvinyl chloride production based on calcium carbide method Download PDF

Info

Publication number
CN106673055A
CN106673055A CN201611149476.7A CN201611149476A CN106673055A CN 106673055 A CN106673055 A CN 106673055A CN 201611149476 A CN201611149476 A CN 201611149476A CN 106673055 A CN106673055 A CN 106673055A
Authority
CN
China
Prior art keywords
mercury catalyst
chloride
give
calcium carbide
polyvinyl chloride
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
CN201611149476.7A
Other languages
Chinese (zh)
Other versions
CN106673055B (en
Inventor
李毅
丘永桂
魏昭辉
王明建
陈群涛
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Anhui Hwasu Corp
Original Assignee
Anhui Hwasu Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Anhui Hwasu Corp filed Critical Anhui Hwasu Corp
Priority to CN201611149476.7A priority Critical patent/CN106673055B/en
Publication of CN106673055A publication Critical patent/CN106673055A/en
Application granted granted Critical
Publication of CN106673055B publication Critical patent/CN106673055B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01GCOMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
    • C01G13/00Compounds of mercury
    • C01G13/04Halides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/20Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising free carbon; comprising carbon obtained by carbonising processes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28054Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J20/28057Surface area, e.g. B.E.T specific surface area
    • B01J20/28066Surface area, e.g. B.E.T specific surface area being more than 1000 m2/g
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28054Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J20/28069Pore volume, e.g. total pore volume, mesopore volume, micropore volume
    • B01J20/28073Pore volume, e.g. total pore volume, mesopore volume, micropore volume being in the range 0.5-1.0 ml/g
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2220/00Aspects relating to sorbent materials
    • B01J2220/40Aspects relating to the composition of sorbent or filter aid materials
    • B01J2220/48Sorbents characterised by the starting material used for their preparation
    • B01J2220/4875Sorbents characterised by the starting material used for their preparation the starting material being a waste, residue or of undefined composition
    • B01J2220/4893Residues derived from used synthetic products, e.g. rubber from used tyres
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01PINDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
    • C01P2006/00Physical properties of inorganic compounds
    • C01P2006/12Surface area
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01PINDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
    • C01P2006/00Physical properties of inorganic compounds
    • C01P2006/14Pore volume
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01PINDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
    • C01P2006/00Physical properties of inorganic compounds
    • C01P2006/80Compositional purity
    • 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

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Analytical Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Inorganic Chemistry (AREA)
  • Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)
  • Catalysts (AREA)

Abstract

The invention provides a method for recycling a waste mercury catalyst from polyvinyl chloride production based on a calcium carbide method. The method comprises the following steps: smashing the waste mercury catalyst with mercuric chloride, hydrogen chloride and vinyl chloride attached to activated carbon into certain fineness; extracting with carbon disulfide and filtering, thereby acquiring filter residues; heating and then condensing the filter residues under a light-shielding condition to recycle mercuric chloride; treating the filter residues with alkali, neutralizing the absorbed hydrogen chloride, filtering, drying and recycling the activated carbon. The recycling method provided by the invention has the advantages that the heating temperature for recycling the mercuric chloride is low, the recycling of the mercuric chloride can be carried out only at 90-120 DEG C, the recovery rate reaches up to 95% and the purity reaches up to 99.5%; after the recycled activated carbon is treated, the purity is high, the recovery rate reaches up to 92%, the absorption activity is recovered, the micro-pore surface area is recovered to 1000-1200m<2>/g and the pore volume is recovered to 0.3-0.6ml/g; besides, according to the method, the operation is simple, the energy consumption is low, the environment-friendly and pollution-free effects are achieved; the organic substances, such as chloroethylene, and the hydrogen chloride acidic material can be effectively removed.

Description

The recovery method of useless mercury catalyst in a kind of generated by polyvinyl chloride by calcium carbide production
Technical field
The present invention relates to catalyst reclaims field, and in particular to give up mercury catalyst in a kind of generated by polyvinyl chloride by calcium carbide production Recovery method.
Background technology
In generated by polyvinyl chloride by calcium carbide production process, acetylene and hydrogen chloride are adopted for raw material, mercuric chloride and activated carbon are to urge Agent, carries out catalytic reaction and carrys out synthesis vinyl chloride thereof monomer, and then polymerization of vinyl choride monomer forms polrvinyl chloride.With catalytic reaction Carrying out, easily the Hg chloride content of distillation is reduced to less than 4% in activated carbon, while because having adsorbed excess in activated carbon hole Raw material hydrogen chloride gas and product vinyl chloride, catalyst gradually inactivates.With China to environmental protection requirement it is increasingly strict, it is primary State hydrargyrum resource is fewer and feweri, needs to reclaim useless mercury catalyst.The mercury catalyst that gives up in prior art is reclaimed typically will be useless The mercury catalyst first steaming and decocting together with lime water, makes mercuric chloride be converted into mercury oxide, then Jing 700-800 DEG C high temperature makes mercury oxide become single Matter hydrargyrum, this kind of method response rate is low by only 57% or so, and energy consumption is big;Also have and poisonous chlorine time is passed through in heating process Hydrargyrum and mercuric chloride are received, last gas from dry distillation tail causes mercury-containing waste water, pollutes environment again after processing;It is not right in prior art in addition The organic substance and hydrochloric acid material of activated carbon adsorption is effectively removed, and affects the quality for reclaiming material.
Therefore, these problems how to be solved, it has also become those skilled in the art's technical barrier urgently to be resolved hurrily.
The content of the invention
The present invention is directed to the deficiencies in the prior art, there is provided hydrargyrum catalysis of giving up in a kind of generated by polyvinyl chloride by calcium carbide production The recovery method of agent, solves above-mentioned technical problem.
To achieve these goals, the present invention provides following technical scheme:Give up hydrargyrum in a kind of generated by polyvinyl chloride by calcium carbide production The recovery method of catalyst, comprises the steps:
(1)First useless mercury catalyst is crushed to into certain fineness, the useless hydrargyrum catalysis system refers to and be adsorbed with activated carbon mercuric chloride, chlorination The decaying catalyst of hydrogen and vinyl chloride;
(2)Useless mercury catalyst after by above-mentioned crushing removes vinyl chloride with extraction with carbon disulfide, is filtrated to get filtering residue;
(3)Above-mentioned filtering residue is heated under the conditions of lucifuge and obtains chlorination mercuryvapour, mercuric chloride solid is reclaimed in then condensation;
(4)By remaining filtering residue alkali process after above-mentioned recovery mercuric chloride, the hydrogen chloride of absorption is neutralized, filtered, be dried, reclaimed and live Property charcoal.
As a further improvement on the present invention, step(1)Described in give up mercury catalyst in be respectively 2- containing mass fraction The vinyl chloride of 3.8% mercuric chloride, the hydrogen chloride of 0.5-1% and 0.1-0.4%.
As a further improvement on the present invention, step(1)Described in give up mercury catalyst crush after fineness be 40-80 mesh, The contact area of useless mercury catalyst and extractant Carbon bisulfide can be increased, other Organic substances such as vinyl chloride of absorption in activated carbon It is easier to be dissolved in Carbon bisulfide;More preferably 60 mesh, fineness blocks filter opening when easily causing filtration more than 80 mesh, and fineness is little In 40 mesh, Organic substance vinyl chloride is not high by extraction with carbon disulfide rate.
As a further improvement on the present invention, step(2)Described in give up mercury catalyst be with Carbon bisulfide mass volume ratio 1:1.5-3, more preferably 1:2.2, make useless mercury catalyst be easier to be infiltrated by Carbon bisulfide, and extract dosage properly, save Resource.
As a further improvement on the present invention, step(3)Described under the conditions of lucifuge heating-up temperature be 90-120 DEG C, plus The hot time is 30-120min, makes mercuric chloride rapid sublimation, reclaims rapid, and lucifuge condition can avoid mercuric chloride from being partially converted into Calomel, the response rate is up to 95%, reclaims product purity and is up to 99.5%.
As a further improvement on the present invention, step(3)Described in condensation temperature be 10-25 DEG C, condensation temperature is lower, more Be conducive to chlorination mercuryvapour to be changed into solid and separate out recovery, when temperature is higher than 25 DEG C, the mercuric chloride response rate is low, and it is at room temperature Slow distillation;When temperature is less than 10 DEG C, energy consumption increases.
As a further improvement on the present invention, step(4)Described in alkali be metal hydroxidess, metal carbonate or metal Bicarbonate, for the hydrogen chloride adsorbed in neutralization activity charcoal;The metal carbonate is preferably sodium carbonate, potassium carbonate, described Alkali metal bicarbonate salt is preferably sodium bicarbonate, potassium bicarbonate, and the metal hydroxidess are preferably sodium hydroxide, potassium hydroxide, More preferably mass fraction for 20-54% sodium hydrate aqueous solution, excessive concentration, when reaching hypersaturated state, part hydroxide Sodium granule separates out the micro channel that can be blocked in activated carbon;Sodium hydrate aqueous solution volume is larger when concentration is too low, and it is right to increased The requirement of equipment volume or batch operation increased process time.
Compared with prior art, give up in generated by polyvinyl chloride by calcium carbide of the invention production mercury catalyst recovery method have with Lower advantage:Heating-up temperature is low when reclaiming mercuric chloride, it is only necessary to carry out at 90-120 DEG C, and the response rate is up to 95%, high purity 99.5%;After treatment purity is high for the activated carbon of recovery, and the response rate is up to 92%, recovers adsorption activity, and micro pore surface area is recovered To 1000-1200m2/ g, void content returns to 0.3-0.6ml/g;In addition this method is simple to operate, energy consumption is reduced, green ring Protect pollution-free, moreover it is possible to effectively remove organic substance and the hydrochloric acid materials such as vinyl chloride.
Specific embodiment
With reference to specific embodiment, the present invention is expanded on further, it should be appreciated that these embodiments are merely to illustrate the present invention Rather than restriction the scope of the present invention;In addition, it is to be understood that after present disclosure has been read, those skilled in the art can To make various changes or modifications to the present invention, these equivalent form of values also fall within appended claims limited range.
Embodiment 1:
The recovery method of useless mercury catalyst, comprises the steps in a kind of generated by polyvinyl chloride by calcium carbide production:
(1)The useless mercury catalysts of first 100g are crushed to fineness for 40 mesh, and the useless hydrargyrum catalysis system refers to and be adsorbed with activated carbon 2% chlorination The decaying catalyst of hydrargyrum, 1% hydrogen chloride and 0.4% vinyl chloride;
(2)Useless mercury catalyst after by above-mentioned crushing removes vinyl chloride with 150ml extraction with carbon disulfide, is filtrated to get filtering residue;
(3)Above-mentioned filtering residue is heated to into 90 DEG C under the conditions of lucifuge, distillation 120min obtains chlorination mercuryvapour, then at 18 DEG C Condensation is reclaimed and obtains the mercuric chloride solid that 1.92g purity is 99.5%, and the response rate is 96%;
(4)Remaining filtering residue after above-mentioned recovery mercuric chloride is processed with the sodium hydrate aqueous solution that 120g mass fractions are 20%, mistake Filter, is dried at 80 DEG C, and recovery obtains 88.9g activated carbons, and the response rate is 92%, and its micro pore surface area returns to 1000m2/ g, hole Gap volume returns to 0.3ml/g.
Embodiment 2:
The recovery method of useless mercury catalyst, comprises the steps in a kind of generated by polyvinyl chloride by calcium carbide production:
(1)The useless mercury catalysts of first 100g are crushed to fineness for 80 mesh, and the useless hydrargyrum catalysis system refers to and be adsorbed with activated carbon 3.8% chlorine Change the decaying catalyst of hydrargyrum, 0.5% hydrogen chloride and 0.1% vinyl chloride;
(2)Useless mercury catalyst after by above-mentioned crushing removes vinyl chloride with 300ml extraction with carbon disulfide, is filtrated to get filtering residue;
(3)Above-mentioned filtering residue is heated to into 120 DEG C under the conditions of lucifuge, distillation 30min obtains chlorination mercuryvapour, then at 10 DEG C Condensation is reclaimed and obtains the mercuric chloride solid that 3.69g purity is 99.6%, and the response rate is 97%;
(4)Remaining filtering residue after above-mentioned recovery mercuric chloride is processed with the sodium hydrate aqueous solution that 80g mass fractions are 54%, mistake Filter, is dried at 80 DEG C, and recovery obtains 88.9g activated carbons, and the response rate is 93%, and its micro pore surface area returns to 1200m2/ g, hole Gap volume returns to 0.6ml/g.
Embodiment 3:
The recovery method of useless mercury catalyst, comprises the steps in a kind of generated by polyvinyl chloride by calcium carbide production:
(1)The useless mercury catalysts of first 100g are crushed to fineness for 60 mesh, and the useless hydrargyrum catalysis system refers to and be adsorbed with activated carbon 2.9% chlorine Change the decaying catalyst of hydrargyrum, 0.7% hydrogen chloride and 0.2% vinyl chloride;
(2)Useless mercury catalyst after by above-mentioned crushing removes vinyl chloride with 220ml extraction with carbon disulfide, is filtrated to get filtering residue;
(3)Above-mentioned filtering residue is heated to into 105 DEG C under the conditions of lucifuge, distillation 75min obtains chlorination mercuryvapour, then at 25 DEG C Condensation is reclaimed and obtains the mercuric chloride solid that 2.76g purity is 99.5%, and the response rate is 95%;
(4)Remaining filtering residue after above-mentioned recovery mercuric chloride is processed with the sodium hydrate aqueous solution that 105g mass fractions are 35%, mistake Filter, is dried at 80 DEG C, and recovery obtains 88.5g activated carbons, and the response rate is 92%, and its micro pore surface area returns to 1108m2/ g, hole Gap volume returns to 0.46ml/g.

Claims (10)

1. the recovery method of useless mercury catalyst during a kind of generated by polyvinyl chloride by calcium carbide is produced, it is characterised in that comprise the steps:
(1)First useless mercury catalyst is crushed to into certain fineness, the useless hydrargyrum catalysis system refers to and be adsorbed with activated carbon mercuric chloride, chlorination The decaying catalyst of hydrogen and vinyl chloride;
(2)Useless mercury catalyst after by above-mentioned crushing removes vinyl chloride with extraction with carbon disulfide, is filtrated to get filtering residue;
(3)Above-mentioned filtering residue is heated under the conditions of lucifuge and obtains chlorination mercuryvapour, mercuric chloride solid is reclaimed in then condensation;
(4)By remaining filtering residue alkali process after above-mentioned recovery mercuric chloride, the hydrogen chloride of absorption is neutralized, filtered, be dried, reclaimed and live Property charcoal.
2. give up the recovery method of mercury catalyst in a kind of generated by polyvinyl chloride by calcium carbide production according to claim 1, its feature It is:Step(1)Described in give up and be respectively the hydrogen chloride of the mercuric chloride of 2-3.8%, 0.5-1% in mercury catalyst containing mass fraction With the vinyl chloride of 0.1-0.4%.
3. give up the recovery method of mercury catalyst in a kind of generated by polyvinyl chloride by calcium carbide production according to claim 1, its feature It is:Step(1)Described in give up mercury catalyst crush after fineness be 40-80 mesh.
4. give up the recovery method of mercury catalyst in a kind of generated by polyvinyl chloride by calcium carbide production according to claim 3, its feature It is:Step(1)Described in give up mercury catalyst crush after fineness be 60 mesh.
5. give up the recovery method of mercury catalyst in a kind of generated by polyvinyl chloride by calcium carbide production according to claim 1, its feature It is:Step(2)Described in give up mercury catalyst and Carbon bisulfide mass volume ratio be 1:1.5-3.
6. give up the recovery method of mercury catalyst in a kind of generated by polyvinyl chloride by calcium carbide production according to claim 5, its feature It is:Step(2)Described in give up mercury catalyst and Carbon bisulfide mass volume ratio be 1:2.2.
7. give up the recovery method of mercury catalyst in a kind of generated by polyvinyl chloride by calcium carbide production according to claim 1, its feature It is:Step(3)Described in heating-up temperature be 90-120 DEG C, heat time heating time is 30min-120min.
8. give up the recovery method of mercury catalyst in a kind of generated by polyvinyl chloride by calcium carbide production according to claim 1, its feature It is:Step(3)Described in condensation temperature be 10-25 DEG C.
9. give up the recovery method of mercury catalyst in a kind of generated by polyvinyl chloride by calcium carbide production according to claim 1, its feature It is:Step(4)Described in alkali be metal hydroxidess, metal carbonate or alkali metal bicarbonate salt.
10. give up the recovery method of mercury catalyst in a kind of generated by polyvinyl chloride by calcium carbide production according to claim 9, its feature It is:The metal hydroxidess are the sodium hydrate aqueous solution that mass fraction is 20-54%.
CN201611149476.7A 2016-12-14 2016-12-14 The recovery method of useless mercury catalyst in a kind of generated by polyvinyl chloride by calcium carbide production Active CN106673055B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201611149476.7A CN106673055B (en) 2016-12-14 2016-12-14 The recovery method of useless mercury catalyst in a kind of generated by polyvinyl chloride by calcium carbide production

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201611149476.7A CN106673055B (en) 2016-12-14 2016-12-14 The recovery method of useless mercury catalyst in a kind of generated by polyvinyl chloride by calcium carbide production

Publications (2)

Publication Number Publication Date
CN106673055A true CN106673055A (en) 2017-05-17
CN106673055B CN106673055B (en) 2018-01-12

Family

ID=58868343

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201611149476.7A Active CN106673055B (en) 2016-12-14 2016-12-14 The recovery method of useless mercury catalyst in a kind of generated by polyvinyl chloride by calcium carbide production

Country Status (1)

Country Link
CN (1) CN106673055B (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109097583A (en) * 2018-08-22 2018-12-28 昆明理工大学 A kind of method that clean and effective recycles useless low mercury catalyst
CN114229843A (en) * 2021-12-24 2022-03-25 贵州重力科技环保有限公司 Method for activating and regenerating waste activated carbon after harmless treatment of waste mercury catalyst

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102814173A (en) * 2012-08-03 2012-12-12 长葛市九州化工有限公司 Waste active carbon mercury catalyst recovery process
CN102962033A (en) * 2012-11-23 2013-03-13 那风换 Method for synchronously recovering mercuric chloride, metal salt and active carbon in spent catalyst
CN104138767A (en) * 2013-05-07 2014-11-12 贵州省万山银河化工有限责任公司 Activating and recovering method of waste mercuric chloride catalyst
CN104451154A (en) * 2014-11-14 2015-03-25 北京化工大学 New technology for recovering mercury in mercury-containing catalyst by wet method

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102814173A (en) * 2012-08-03 2012-12-12 长葛市九州化工有限公司 Waste active carbon mercury catalyst recovery process
CN102962033A (en) * 2012-11-23 2013-03-13 那风换 Method for synchronously recovering mercuric chloride, metal salt and active carbon in spent catalyst
CN104138767A (en) * 2013-05-07 2014-11-12 贵州省万山银河化工有限责任公司 Activating and recovering method of waste mercuric chloride catalyst
CN104451154A (en) * 2014-11-14 2015-03-25 北京化工大学 New technology for recovering mercury in mercury-containing catalyst by wet method

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
YAFENG REN, ET AL.: "Leaching Behavior and Risk Control of Waste Mercury Chloride Catalyst Through Mechanochemical Reaction Using Sulfur", 《ENVIRONMENTAL ENGINEERING SCIENCE》 *
张亚雄等: "我国氯化汞触媒生产和废氯化汞触媒回收利用技术进展", 《聚氯乙烯》 *
徐永炽: "用新技术回收废氯化汞触媒汞", 《贵州环保科技》 *
石家庄科创助剂有限公司: "控氧干馏法回收废触媒中HgCl2及再生汞触媒的新工艺及设备", 《2010年全国石油和化学工业节能环保技术、设备交流会》 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109097583A (en) * 2018-08-22 2018-12-28 昆明理工大学 A kind of method that clean and effective recycles useless low mercury catalyst
CN114229843A (en) * 2021-12-24 2022-03-25 贵州重力科技环保有限公司 Method for activating and regenerating waste activated carbon after harmless treatment of waste mercury catalyst

Also Published As

Publication number Publication date
CN106673055B (en) 2018-01-12

Similar Documents

Publication Publication Date Title
CN101973545B (en) Method for purifying high-purity graphite
TWI375688B (en) Process and apparatus for purifying solid salt compositions
CN209901923U (en) Harmless treatment system for industrial waste salt
CN105170108B (en) A kind of rice husk cellulose adsorbent and its preparation method and application
CN103803638A (en) Method for recycling waste mercury catalyst
CN104294048B (en) A kind of siderophore spent automotive exhaust catalysts platinum group metal recovery method
CN109534312B (en) Method for recycling and fully utilizing sodium chloride waste slag salt by using polymerization and carbonization method
CN104878208B (en) Recovery method for palladium and ruthenium in catalytic combustion catalyst Pd-Ru/alumina
CN106673055B (en) The recovery method of useless mercury catalyst in a kind of generated by polyvinyl chloride by calcium carbide production
CN106565956A (en) Method for comprehensive recycling of by-product slurry in polyphenylene sulfide productive process
CN104986908A (en) Method for treating and recycling process waste water generated during production of 1,2-Benzisothiazolin-3-One
CN113321848A (en) Method for synchronously removing antimony and bromine from electronic waste flame-retardant plastic and recycling plastic matrix
CN103272410A (en) Circular removal process for chloride ions in manganese sulfate electrolyte and application of cuprous hydroxide as dechlorinating agent
CN113666376B (en) Recycling treatment method for silicon slag
CN113800549A (en) Method for extracting barium chloride from precipitated barium sulfate waste residue
CN106984264A (en) The method that harmless treatment prepares atlapulgite is carried out to spent FCC catalyst
CN105668597B (en) The method of flyash soda acid combined extracting aluminium base product and silica-based products
CN110668956A (en) Method for desalting and purifying water phase through water washing extraction in RT base production process
CN110605106A (en) Regeneration method of waste mercury catalyst activated carbon after harmless treatment
CN102188966B (en) Process for recovering mercury chloride in hydrochloric-acid-containing wastewater discharged in acetylene method based poly(vinyl chloride) production and circularly producing mercury chloride catalyst
CN114769293A (en) Method for cooperative treatment of industrial solid waste and resource utilization of industrial waste salt
CN111943190B (en) Method for recovering graphite from electrolytic aluminum waste cathode carbon block
CN106565581A (en) A method for comprehensive recovery and utilization of lithium containing mixed salts in a polyphenylene sulfide production process
CN109369339B (en) Method for treating waste p-toluenesulfonic acid iron n-butanol solution
CN106673067A (en) Method for preparing battery-grade manganese sulfate from alkylation waste sulfuric acid

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant