CN107470317B - Method for debrominating and lightening pyrolysis oil of waste circuit board - Google Patents

Method for debrominating and lightening pyrolysis oil of waste circuit board Download PDF

Info

Publication number
CN107470317B
CN107470317B CN201710453326.3A CN201710453326A CN107470317B CN 107470317 B CN107470317 B CN 107470317B CN 201710453326 A CN201710453326 A CN 201710453326A CN 107470317 B CN107470317 B CN 107470317B
Authority
CN
China
Prior art keywords
pyrolysis
circuit board
pyrolysis oil
composite additive
metal powder
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.)
Active
Application number
CN201710453326.3A
Other languages
Chinese (zh)
Other versions
CN107470317A (en
Inventor
杨帆
孙水裕
叶子玮
林伟雄
陈楠纬
李保庆
任随周
蔡焕然
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.)
Guangdong Vocational College of Environmental Protection Engineering
Original Assignee
Guangdong Vocational College of Environmental Protection Engineering
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 Guangdong Vocational College of Environmental Protection Engineering filed Critical Guangdong Vocational College of Environmental Protection Engineering
Priority to CN201710453326.3A priority Critical patent/CN107470317B/en
Publication of CN107470317A publication Critical patent/CN107470317A/en
Application granted granted Critical
Publication of CN107470317B publication Critical patent/CN107470317B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • B09B3/40Destroying solid waste or transforming solid waste into something useful or harmless involving thermal treatment, e.g. evaporation
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08JWORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
    • C08J11/00Recovery or working-up of waste materials
    • C08J11/04Recovery or working-up of waste materials of polymers
    • C08J11/10Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation
    • C08J11/16Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation by treatment with inorganic material
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10GCRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
    • C10G1/00Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10GCRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
    • C10G2300/00Aspects relating to hydrocarbon processing covered by groups C10G1/00 - C10G99/00
    • C10G2300/10Feedstock materials
    • C10G2300/1003Waste materials
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/62Plastics recycling; Rubber recycling
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/82Recycling of waste of electrical or electronic equipment [WEEE]

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Organic Chemistry (AREA)
  • Sustainable Development (AREA)
  • General Chemical & Material Sciences (AREA)
  • Wood Science & Technology (AREA)
  • Health & Medical Sciences (AREA)
  • Medicinal Chemistry (AREA)
  • Polymers & Plastics (AREA)
  • Physics & Mathematics (AREA)
  • Thermal Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention discloses a method for debrominating and lightening pyrolysis oil of a waste circuit board, which comprises the following steps: s1, crushing a waste circuit board, extracting non-metal powder, putting the non-metal powder into a pyrolysis furnace, and adding a composite additive; s2, heating the materials to 400-500 ℃, keeping for 1-2 hours until complete pyrolysis is achieved, and collecting pyrolysis oil; the composite additive comprises the following components in parts by weight: 10-90 parts of molecular sieve, CaCO310-90 parts. The method can simultaneously realize dehalogenation and lightening of the pyrolysis oil of the waste circuit board, can be widely applied to treatment or recycling of the waste circuit board, and has good application prospect.

Description

Method for debrominating and lightening pyrolysis oil of waste circuit board
Technical Field
The invention belongs to the technical field of waste circuit board recovery, and particularly relates to a method for debrominating and lightening pyrolysis oil of a waste circuit board.
Background
Printed Circuit Boards (PCBs for short) are thermosetting composite materials, which are used as core components of electronic products and are widely used in various industrial fields such as electronic components and electric control. With the development of science and technology, the frequency of upgrading and eliminating electronic products is accelerated, so that the waste amount of PCBs is increased. According to the national university estimate, the electronic waste in the eu countries reaches 910 ten thousand tons in 2005 and increases at a rate of 2.5% to 2.7% per year. The printed wiring board yield in china in 2008 is up to 26% of the world's total volume, occupying the first place in the world. Meanwhile, the waste circuit board contains various toxic and harmful substances, and the waste circuit board can pollute the environment, threaten the health of human beings and stably develop the society without being treated. Therefore, how to perform effective and harmless treatment on Waste circuit Boards (WPCBs) which are increasing rapidly becomes a common problem in the world.
The waste circuit board, which is called as "urban mine" or "secondary metal rich mine", is mainly characterized in that it contains various valuable metals (such as gold, silver, iron, aluminum, copper, etc.), and the remaining non-metal part is mainly glass fiber and epoxy resin containing halogen. The traditional WPCBs treatment method mainly comprises mechanical physical method, chemical method, pyrometallurgical smelting and the like, aims to recover valuable metals, does not fully utilize the residual non-metallic part, and is easy to generate a large amount of waste gas, waste liquid and waste residue to cause secondary pollution to the environment. In recent years, attention and research are paid to and particularly vacuum pyrolysis treatment technology, however, WPCBs contain halogen-containing flame retardants, so that pyrolysis oil contains a large amount of bromine-containing substances, and further utilization of pyrolysis oil is seriously hindered.
As for the pyrolysis dehalogenation of WPCBs, a great deal of research work is done by scholars at home and abroad. Respectively adding NaOH and Na into Blazs Lou M (Blazs Lou M, et al, 2002)2CO3The CaO, ZnO, 5A molecular sieve, 13X molecular sieve and WPCBs powder are subjected to co-pyrolysis, and Py-GC/MS and Py-GC detection show that the additive can effectively reduce the yield of bromophenol and brominated styrene. Investigation of 12 additives (Al) in Zhanzhihua et Al (2011)2O3、SnO4、CuO、ZnO、Fe2O3Cu, Fe, Al, artificial zeolite, natural zeolite, activated carbon and MCM-41) and waste epoxy circuit boards are subjected to vacuum pyrolysis, and the metal Fe and oxides thereof are found to be capable of effectively reducing the bromide content in the pyrolysis oil. Liuxin et al (2012) co-pyrolyzed with waste circuit board powder using urea, p-diaminodiphenylmethane, hexamethylenetetramine as additives, and the results show that bromine in the bromine-containing flame retardant is mainly removed in the form of HBr, methyl bromide and ethyl bromide. Addition of Fe system (Fe) to Wujiaqi et al (2014)2O3、Fe3O4FeOOH), Ca series (CaO, Ca (OH)2、CaCO3) And Al system (Al)2O3Active Al2O3Molecular sieve) oxide and waste circuit board are subjected to co-pyrolysis debromination experiment, and research shows that Fe3O4And CaCO3The debromination effect is optimal and the bromine content in the pyrolysis oil is reduced from 72.10% (without additives) to 8.91% and 7.69%. Li Shenyong et al (2015) study on Fe, FeOOH and Fe3O4Active Al2O3Performing co-pyrolysis on (the particle size is 3-5 mm, the particles) and diatomite (the silicon content is 88%) and the circuit board powder, wherein Fe3O4The diatomite and the FeOOH can obviously reduce the total bromine content of the liquid product.
Disclosure of Invention
The invention aims to provide a method for debrominating and lightening waste circuit board pyrolysis oil aiming at the defects in the prior art, wherein the debromination rate in the pyrolysis oil can exceed 80 percent, so that the recovery rate of the waste circuit board is obviously improved.
The purpose of the invention is realized by the following technical scheme:
a method for debrominating and lightening pyrolysis oil of a waste circuit board comprises the following steps:
s1, crushing a waste circuit board, extracting non-metal powder, putting the non-metal powder into a pyrolysis furnace, and adding a composite additive;
s2, heating the materials to 400-500 ℃, keeping for 1-2 hours until complete pyrolysis is achieved, and collecting pyrolysis oil;
the composite additive comprises the following components in parts by weight: 10-90 parts of molecular sieve, CaCO310-90 parts.
The method utilizes sodium ions and aluminum ions dissociated from the molecular sieve 5A in the reaction, and simultaneously utilizes the advantages of large specific surface area, high porosity and the like of the molecular sieve 5A to adsorb halogen in the pyrolysis oil, thereby achieving the removal of the halogen. Secondly, CaCO3Dissociated CO3 2-Exchange with bromide ion, and has excellent debromination effect. And Al in 5A molecular sieve2O3Has good catalytic effect on the lightening of pyrolysis oil, CaCO3The content of heavy components in the pyrolysis oil can be reduced to a certain extent. The invention uses the two additives in a composite way and adjusts the two additivesThe proportion reduces the content of heavy components in the pyrolysis oil while reducing the content of bromine in the pyrolysis oil.
Preferably, the composite additive consists of the following components in parts by weight: 30-70 parts of molecular sieve 5A and CaCO330-70 parts.
The weight ratio of the non-metal powder to the composite additive is 1-3: 3-1.
Preferably, the weight ratio of the non-metal powder to the composite additive is 1-2: 2-1.
The adding manner of the composite additive in step S1 includes but is not limited to: uniformly mixing the composite additive, adding the non-metal powder and mixing; adding non-metal powder into the molecular sieve 5A, uniformly mixing, and then adding CaCO3;CaCO3Adding the nonmetal powder, mixing uniformly, and adding the molecular sieve 5A.
Compared with the prior art, the invention has the following beneficial effects:
aiming at the two problems of high bromine content and heavy component content in the waste circuit board pyrolysis oil in the resource recovery process, the invention reduces the bromine content in the pyrolysis oil and simultaneously reduces the heavy component content in the pyrolysis oil by adding the composite modifier in the waste circuit board pyrolysis process. The method utilizes sodium ions and aluminum ions dissociated from the molecular sieve 5A in the reaction, and simultaneously utilizes the advantages of large specific surface area, high porosity and the like of the molecular sieve 5A to adsorb halogen in the pyrolysis oil, thereby achieving the removal of the halogen. Secondly, CaCO3Dissociated CO3 2-Exchange with bromide ion can also remove halogen. And Al in 5A molecular sieve2O3Has good catalytic effect on the lightening of pyrolysis oil, CaCO3The content of heavy components in the pyrolysis oil can be reduced to a certain extent. The invention uses the two additives in a compounding way and adjusts the proportion of the two additives, so that the debromination rate in the obtained pyrolysis oil can exceed 80 percent; the pyrolysis oil contains more than 45% of components at the temperature of less than 200 ℃ and more than 90% of components at the temperature of less than 350 ℃.
Detailed Description
The present invention is further explained with reference to specific embodiments, which are described in detail and specific, but not to be construed as limiting the scope of the invention, and all technical solutions obtained by equivalents or equivalent changes should be included in the scope of the claims of the present invention.
In the following examples and comparative examples, all the raw materials used were commercially available products.
Example 1
The composite additive consists of molecular sieve 5A in 30 weight portions and CaCO in 70 weight portions3And (4) forming.
A method for debrominating and lightening pyrolysis oil of a waste circuit board comprises the following steps:
s1, crushing a circuit board with electronic components removed, extracting non-metal powder, putting the non-metal powder into a pyrolysis furnace, and adding a composite additive, wherein the non-metal powder is added and fully mixed after the composite additive is uniformly mixed;
s2, after the feeding is finished, heating the pyrolysis furnace to 400 ℃, keeping for 2 hours until complete pyrolysis is achieved, and collecting pyrolysis oil generated after pyrolysis;
the weight ratio of the non-metal powder to the composite additive is 1: 1.
Example 2
The composite additive consists of molecular sieve 5A in 50 weight portions and CaCO in 50 weight portions3And (4) forming.
A method for debrominating and lightening pyrolysis oil of a waste circuit board comprises the following steps:
s1, crushing a circuit board with electronic components removed, extracting non-metal powder, putting the non-metal powder into a pyrolysis furnace, adding a composite additive, adding a molecular sieve 5A, uniformly mixing with the non-metal powder, and adding CaCO3,CaCO3Not mixed with non-metal powder;
s2, after the feeding is finished, heating the pyrolysis furnace to 450 ℃, keeping the temperature for 1.5 hours until the pyrolysis is completed, and collecting pyrolysis oil generated after the pyrolysis;
the weight ratio of the non-metal powder to the composite additive is 1: 2.
Example 3
The composite additive consists of molecular sieve 5A in 80 weight portions and CaCO in 20 weight portions3And (4) forming.
A method for debrominating and lightening pyrolysis oil of a waste circuit board comprises the following steps:
s1, crushing a circuit board with electronic components removed, extracting non-golden powder, putting the powder into a pyrolysis furnace, and adding a composite additive, wherein CaCO3Firstly, adding the non-golden powder, uniformly mixing, then adding the molecular sieve 5A, wherein the molecular sieve 5A is not mixed with the non-golden powder;
s2, after the feeding is finished, heating the pyrolysis furnace to 500 ℃, keeping for 1 hour until complete pyrolysis is achieved, and collecting pyrolysis oil generated after pyrolysis;
the weight ratio of the non-metal powder to the composite additive is 2: 1.
Example 4
The composite additive consists of molecular sieve 5A in 10 weight portions and CaCO in 90 weight portions3And (4) forming.
A method for debrominating and lightening pyrolysis oil of a waste circuit board comprises the following steps:
s1, crushing a circuit board with electronic components removed, extracting non-golden powder, putting the non-golden powder into a pyrolysis furnace, and adding a composite additive, wherein the non-golden powder is added and fully mixed after the composite additive is uniformly mixed;
s2, after the feeding is finished, heating the pyrolysis furnace to 400 ℃, keeping for 2 hours until complete pyrolysis is achieved, and collecting pyrolysis oil generated after pyrolysis;
the weight ratio of the non-metal powder to the composite additive is 1: 1.
Example 5
The composite additive consists of molecular sieve 5A in 90 weight portions and CaCO in 10 weight portions3And (4) forming.
A method for debrominating and lightening pyrolysis oil of a waste circuit board comprises the following steps:
s1, crushing a circuit board with electronic components removed, extracting non-golden powder, putting the non-golden powder into a pyrolysis furnace, and adding a composite additive, wherein the non-golden powder is added and fully mixed after the composite additive is uniformly mixed;
s2, after the feeding is finished, heating the pyrolysis furnace to 400 ℃, keeping for 2 hours until complete pyrolysis is achieved, and collecting pyrolysis oil generated after pyrolysis;
the weight ratio of the non-metal powder to the composite additive is 1: 1.
Example 6
The composite additive consists of molecular sieve 5A in 40 weight portions and CaCO in 60 weight portions3And (4) forming.
A method for debrominating and lightening pyrolysis oil of a waste circuit board comprises the following steps:
s1, crushing a circuit board with electronic components removed, extracting non-golden powder, putting the non-golden powder into a pyrolysis furnace, and adding a composite additive, wherein the non-golden powder is added and fully mixed after the composite additive is uniformly mixed;
s2, after the feeding is finished, heating the pyrolysis furnace to 400 ℃, keeping the temperature for 1.5 hours until the pyrolysis is completed, and collecting pyrolysis oil generated after the pyrolysis;
the weight ratio of the non-metal powder to the composite additive is 1: 3.
Example 7
A composite additive is prepared from molecular sieve (5A) 35 wt% and CaCO 65 wt%3And (4) forming.
A method for debrominating and lightening pyrolysis oil of a waste circuit board comprises the following steps:
s1, crushing a circuit board with electronic components removed, extracting non-golden powder, putting the non-golden powder into a pyrolysis furnace, and adding a composite additive, wherein the non-golden powder is added and fully mixed after the composite additive is uniformly mixed;
s2, after the feeding is finished, heating the pyrolysis furnace to 400 ℃, keeping for 2 hours until complete pyrolysis is achieved, and collecting pyrolysis oil generated after pyrolysis;
the weight ratio of the non-metal powder to the composite additive is 3: 1.
Example 8
The composite additive consists of molecular sieve 5A in 60 weight portions and CaCO in 40 weight portions3And (4) forming.
A method for debrominating and lightening pyrolysis oil of a waste circuit board comprises the following steps:
s1, crushing a circuit board with electronic components removed, extracting non-golden powder, putting the non-golden powder into a pyrolysis furnace, and adding a composite additive, wherein the non-golden powder is added and fully mixed after the composite additive is uniformly mixed;
s2, after the feeding is finished, heating the pyrolysis furnace to 400 ℃, keeping for 2 hours until complete pyrolysis is achieved, and collecting pyrolysis oil generated after pyrolysis;
the weight ratio of the non-metal powder to the composite additive is 1.5: 1.
Comparative example 1
A method for debrominating and lightening pyrolysis oil of a waste circuit board comprises the following steps:
s1, crushing a circuit board with electronic components removed, extracting non-metal powder and putting the non-metal powder into a pyrolysis furnace;
s2, heating the pyrolysis furnace to 400 ℃, keeping for 2 hours until complete pyrolysis is achieved, and collecting pyrolysis oil generated after pyrolysis.
Comparative example 2
An additive, which consists of 100 parts by weight of 5A.
A method for debrominating and lightening pyrolysis oil of a waste circuit board comprises the following steps:
s1, crushing a circuit board with electronic components removed, extracting non-metal powder, putting the non-metal powder into a pyrolysis furnace, and adding an additive molecular sieve 5A, wherein the additive and the non-gold powder are fully mixed;
s2, after the feeding is finished, heating the pyrolysis furnace to 400 ℃, keeping for 2 hours until complete pyrolysis is achieved, and collecting pyrolysis oil generated after pyrolysis;
the weight ratio of the non-metal powder to the additive is 1: 1.
Comparative example 3
A composite additive, which consists of 100 parts by weight of CaCO3And (4) forming.
A method for debrominating and lightening pyrolysis oil of a waste circuit board comprises the following steps:
s1, crushing a circuit board with electronic components removed, extracting non-metal powder, putting the non-metal powder into a pyrolysis furnace, and adding an additive CaCO3Wherein, the additive is fully mixed with the non-metal powder and the non-golden powder;
s2, after the feeding is finished, heating the pyrolysis furnace to 400 ℃, keeping for 2 hours until complete pyrolysis is achieved, and collecting pyrolysis oil generated after pyrolysis;
the weight ratio of the non-metal powder to the additive is 1: 1.
Application example 1
The pyrolysis oils collected after the complete pyrolysis of examples 1 to 5 and comparative examples 1 to 3 were subjected to performance tests including a debromination rate test and a pyrolysis oil composition analysis, and the results are shown in tables 1 and 2. And (3) testing the debromination rate: bromine content was determined by a combination of bomb combustion and ion chromatography.
TABLE 1 Debrominating Rate test results
Debromination rate Example 1 Example 2 Example 3 Example 4 Example 5 Example 6 Example 7 Example 8
% 82 91 87 84 81 84 86 88
Debromination rate Comparative example 1 Comparative example 2 Comparative example 3
% 0 27 31
TABLE 2 analysis results of pyrolysis oil composition
Pyrolysis oil component Example 1 Example 2 Example 3 Example 4 Example 5 Example 6 Example 7 Example 8
>360℃ 25 21 18 20 23 25 21 23
240-360℃ 19 20 25 23 20 21 21 22
120-240℃ 48 49 48 50 47 45 47 47
<120℃ 8 10 9 7 10 9 11 8
Pyrolysis oil component Comparative example 1 Comparative example 2 Comparative example 3
>360℃ 35 17 32
240-360℃ 9 31 10
120-240℃ 48 50 49
<120℃ 8 2 9
The above description is only for the purpose of illustrating the preferred embodiments of the present invention and is not to be construed as limiting the invention, and any modifications, equivalents, improvements and the like that are within the spirit and principle of the present invention are intended to be included therein.

Claims (4)

1. A method for debrominating and lightening pyrolysis oil of a waste circuit board is characterized by comprising the following steps:
s1, crushing a waste circuit board, extracting non-metal powder, putting the non-metal powder into a pyrolysis furnace, and adding a composite additive;
s2, heating the materials to 400-500 ℃, keeping for 1-2 hours until complete pyrolysis is achieved, and collecting pyrolysis oil;
the composite additive comprises the following components in parts by weight: 10-90 parts of molecular sieve, CaCO310-90 parts.
2. The method according to claim 1, wherein the composite additive is composed of the following components in parts by weight: 5A 30-70 parts of molecular sieve, CaCO330-70 parts.
3. The method according to claim 1, wherein the weight ratio of the non-metal powder to the composite additive is 1-3: 3-1.
4. The method according to claim 1, wherein the weight ratio of the non-metal powder to the composite additive is 1-2: 2-1.
CN201710453326.3A 2017-06-15 2017-06-15 Method for debrominating and lightening pyrolysis oil of waste circuit board Active CN107470317B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710453326.3A CN107470317B (en) 2017-06-15 2017-06-15 Method for debrominating and lightening pyrolysis oil of waste circuit board

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710453326.3A CN107470317B (en) 2017-06-15 2017-06-15 Method for debrominating and lightening pyrolysis oil of waste circuit board

Publications (2)

Publication Number Publication Date
CN107470317A CN107470317A (en) 2017-12-15
CN107470317B true CN107470317B (en) 2020-01-14

Family

ID=60594769

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710453326.3A Active CN107470317B (en) 2017-06-15 2017-06-15 Method for debrominating and lightening pyrolysis oil of waste circuit board

Country Status (1)

Country Link
CN (1) CN107470317B (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108500032B (en) * 2018-03-22 2021-09-28 安徽浩悦环境科技有限责任公司 Treatment method of bromine-containing waste
CN111635502B (en) * 2020-06-10 2022-04-22 万华化学集团股份有限公司 Polyisocyanate composition and preparation method and application thereof

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH04163005A (en) * 1990-10-23 1992-06-08 Matsushita Electric Works Ltd Base material for prepreg
JPH06859A (en) * 1992-06-22 1994-01-11 Diafoil Co Ltd Production of laminated film
CN103831287A (en) * 2014-03-13 2014-06-04 北京神雾环境能源科技集团股份有限公司 Method for treating circuit board
CN103846272A (en) * 2014-02-27 2014-06-11 广东工业大学 Two-step debromination method for waste printed circuit board
CN104624611A (en) * 2015-01-23 2015-05-20 长沙紫宸科技开发有限公司 Energy-regeneration pollution-free disposal method for waste electrical appliance circuit board

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH04163005A (en) * 1990-10-23 1992-06-08 Matsushita Electric Works Ltd Base material for prepreg
JPH06859A (en) * 1992-06-22 1994-01-11 Diafoil Co Ltd Production of laminated film
CN103846272A (en) * 2014-02-27 2014-06-11 广东工业大学 Two-step debromination method for waste printed circuit board
CN103831287A (en) * 2014-03-13 2014-06-04 北京神雾环境能源科技集团股份有限公司 Method for treating circuit board
CN104624611A (en) * 2015-01-23 2015-05-20 长沙紫宸科技开发有限公司 Energy-regeneration pollution-free disposal method for waste electrical appliance circuit board

Also Published As

Publication number Publication date
CN107470317A (en) 2017-12-15

Similar Documents

Publication Publication Date Title
US12054673B2 (en) Green resource-generating method based on thermal mass synergy of waste integrated circuit board
CN109020231B (en) Method for preparing alloy iron and microcrystalline glass
CN107282591B (en) Method for simultaneously debrominating and lightening waste circuit board pyrolysis oil through two-stage catalytic pyrolysis
CN103464101A (en) Resource utilization method of plant bamboo reed after restoring heavy metal contaminated soil
CN105861845B (en) A kind of method of Combined Treatment copper ashes and slag
CN102895952B (en) Porous carbon material capable of selectively absorbing gold ions, preparation method and application of porous carbon material
CN107470317B (en) Method for debrominating and lightening pyrolysis oil of waste circuit board
CN205109374U (en) Old and useless circuit board exhaust treatment device
US9650693B2 (en) Method for recovering lead from lead-containing discarded electronic waste cathode ray tube glass
CN103831080B (en) For reclaiming nickel slag sorbing material and the preparation thereof of heavy metal ions in wastewater
CN103949461B (en) A kind of method that uses near-critical water to separate and reclaim the each component material of waste and old circuit board
CN103537181A (en) Tail gas treatment device and tail gas treatment method in process of recycling waste printed circuit boards
CN104591183A (en) Method for preparing waste circuit board activated carbon by vapor process
CN106166473B (en) Method for preparing adsorbent by using non-metal separators in waste circuit boards
CN113215394B (en) Treatment method of stone coal
CN107243496B (en) Al (aluminum)2O3And Fe3O4Method for composite catalytic pyrolysis of waste circuit board nonmetal powder
CN100506407C (en) Combined type processing method for waste printed wiring board
CN105177321B (en) A kind of gallium germanium adsorbent, its preparation method and application and the method that gallium germanium is enriched with from zinc hydrometallurgy leachate
CN107399928B (en) Glass fiber ball bundle and preparation method thereof
CN107377577B (en) Based on 5A molecular sieve and Fe3O4Catalytic pyrolysis method for waste circuit board of composite additive
CN115228905B (en) Method for treating nonmetallic materials in waste circuit boards
CN109126411B (en) Excess sludge loaded iron tailing modified adsorbent and preparation method thereof
CN104438285B (en) Method for innocent treatment of waste mercury catalyst by mechanical ball milling with sulfur as additive
CN111921499A (en) Ball-milling modified composite biochar and preparation method and application thereof
CN104312955A (en) Delftia Sp. and application thereof

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