WO2012048462A1 - Method for recovering valuable resource from waste gfrp and waste circuit board - Google Patents

Method for recovering valuable resource from waste gfrp and waste circuit board Download PDF

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Publication number
WO2012048462A1
WO2012048462A1 PCT/CN2010/077697 CN2010077697W WO2012048462A1 WO 2012048462 A1 WO2012048462 A1 WO 2012048462A1 CN 2010077697 W CN2010077697 W CN 2010077697W WO 2012048462 A1 WO2012048462 A1 WO 2012048462A1
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Prior art keywords
waste
circuit boards
circuit board
recovering valuable
waste circuit
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PCT/CN2010/077697
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French (fr)
Chinese (zh)
Inventor
宋金有
Original Assignee
Song Jinyou
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Priority to PCT/CN2010/077697 priority Critical patent/WO2012048462A1/en
Publication of WO2012048462A1 publication Critical patent/WO2012048462A1/en

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    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B53/00Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form
    • C10B53/07Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form of solid raw materials consisting of synthetic polymeric materials, e.g. tyres
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B19/00Heating of coke ovens by electrical means
    • 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
    • C10G1/10Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal from rubber or rubber waste
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/003Incinerators or other apparatus for consuming industrial waste, e.g. chemicals for used articles
    • 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
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2201/00Pretreatment
    • F23G2201/30Pyrolysing
    • F23G2201/301Treating pyrogases
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2201/00Pretreatment
    • F23G2201/30Pyrolysing
    • F23G2201/304Burning pyrosolids
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2201/00Pretreatment
    • F23G2201/80Shredding
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2204/00Supplementary heating arrangements
    • F23G2204/20Supplementary heating arrangements using electric energy
    • F23G2204/203Microwave
    • 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
    • Y02P20/141Feedstock
    • Y02P20/143Feedstock the feedstock being recycled material, e.g. plastics

Abstract

A method for recovering valuable resources from waste GFRP (glass-fiber-reinforced plastic) and waste circuit boards includes the following steps: (1) microwave heat cracking: placing the waste GFRP and waste circuit boards in a high frequency microwave oven, switching on the high frequency microwave oven, and heating the material to a high temperature of 500-600℃ under microwave action to decompose and crack the thermoset high polymer materials to obtain a heat cracked gas and a solid residue; (2) condensing: collecting the heat cracked gas in the oven from step (1) and condensing to obtain an aromatic hydrocarbon mixed organic matter; (3) residue smelting: collecting the solid residue from step (1), smelting at a high temperature in a smelting furnace, and separating to obtain non-ferrous metals and a carbonaceous residue. The method has simple treating process, no pollution, low cost and high recovering efficiency.

Description

废弃玻璃钢和废弃电路板有价资源的回收方法  Recycling method for valuable resources of discarded FRP and waste circuit boards
技术领域 Technical field
本发明涉及废弃电子电器产品和工业废弃物回收利用技术领域, 具体涉及 从废弃玻璃钢和废弃电子线说路板中用微波热裂解回收有价资源的方法。 背景技术  The invention relates to the technical field of waste electrical and electronic products and industrial waste recycling, and particularly relates to a method for recovering valuable resources by microwave thermal cracking from waste glass steel and waste electronic wires. Background technique
随着经济和电子信息产业的迅速发展, 电子电器产品更新换代日益加剧, 产品使用年限缩短, 导致大量的电子产品被废弃。 废弃印刷电路板是电子废弃 物的重大组成部分, 它的回收处理已成为亟需解决的全球性问题。 废弃电路板 不同于一般的固体垃圾, 它除了含有贵金属和其它书有价金属外, 还含有铅、 镉、 水银、 六价铬、 聚氯乙烯及含面阻燃剂, 处理不当将给环境造成严重污染。 目 前, 回收废弃电路板最常用的技术有机械破碎、 湿法冶金、 火法冶金或几种技 术相结合, 但没有一种无污染、 高效率、 低成本的技术对废弃电路板资源化回 收处理。  With the rapid development of the economic and electronic information industry, the upgrading of electronic and electrical products has intensified, and the service life of products has been shortened, resulting in the abandonment of a large number of electronic products. Disposable printed circuit boards are a major component of electronic waste, and its recycling has become a global problem that needs to be addressed. Abandoned circuit board is different from ordinary solid waste. In addition to precious metals and other valuable metals, it also contains lead, cadmium, mercury, hexavalent chromium, polyvinyl chloride and surface-containing flame retardants. Improper handling will cause environmental damage. Serious pollution. At present, the most commonly used technologies for recycling waste circuit boards are mechanical crushing, hydrometallurgy, pyrometallurgy or a combination of several technologies, but there is no pollution-free, high-efficiency, low-cost technology for the recycling of waste circuit boards. .
国内, 申请号为 98101834.3公开了一种用熔融态锡金属回收处理印刷电路 板的方法及其装置。 该发明首先将废弃印刷电路板投入锡液处理炉内, 通过设 置于锡液处理炉内的燃烧机、 多组破碎搅拌装置, 浮渣刮除装置和铜箔分离装 置将其进行碳化和破碎搅拌分离, 利用印刷电路板中的铜箔、 热固性塑胶和玻 璃纤维的比重不同, 分别进行分离和收集, 达到将废弃电路板回收处理的目的。 该方法釆用昂贵的锡金属作为加热介质处理电路板, 成本较高; 锡在处理过程 易氧化, 且熔融锡粘附性强, 使废弃电路板组分分离困难; 金属锡可与金、 银、 铂和钯生成金属化合物, 因此该法容易造成这些贵金属回收困难和损失; 此外, 处理过程中产生的气体经燃烧后仍会污染环境。  Domestically, Application No. 98101834.3 discloses a method and apparatus for recycling a printed circuit board with molten tin metal. The invention firstly puts the waste printed circuit board into a tin liquid treatment furnace, and carbonizes and crushes and stirs it by a burner installed in the tin liquid treatment furnace, a plurality of sets of crushing and stirring devices, a scum scraping device and a copper foil separating device. Separation, using the copper foil, thermosetting plastic and glass fiber in the printed circuit board, the specific gravity is different, separately separated and collected, to achieve the purpose of recycling the waste circuit board. The method uses expensive tin metal as a heating medium to process the circuit board, and the cost is high; tin is easily oxidized during the treatment process, and the molten tin has strong adhesion, which makes separation of components of the waste circuit board difficult; metal tin can be combined with gold and silver , platinum and palladium form metal compounds, so this method is easy to cause difficulties and loss of recovery of these precious metals; in addition, the gas generated during the treatment will still pollute the environment after burning.
申请号为 99119731.3 公开了一种以熔融态无机盐类处理印刷电路板的方 法。 首先将废弃电路板投入熔融的无机盐内, 经破碎搅拌, 是铜箔自印刷电路 板上剥离。 同时是热固性塑胶热解, 从而分离其中的玻璃纤维及其他物质, 产 生的其他经燃烧后排出。 这种方法以熔融态无机盐作为热媒, 废弃电路板在处 理过程中由于密度相对小浮在熔液上部, 给下一步搅拌破碎带来困难。 因此, 种方法处理废弃电路板率很低, 且没有解决气体污染环境的问题。 Application No. 99119731.3 discloses a method of treating a printed circuit board with molten inorganic salts. First, the waste circuit board is put into the molten inorganic salt, and after being crushed and stirred, it is a copper foil self-printing circuit. Peel off the board. At the same time, the thermosetting plastic is pyrolyzed, thereby separating the glass fiber and other substances therein, and the other generated is discharged after being burned. In this method, the molten inorganic salt is used as the heat medium, and the waste circuit board floats on the upper portion of the molten metal due to the relatively small density during the treatment, which makes it difficult to stir and crush in the next step. Therefore, the method of dealing with waste circuit boards is very low, and the problem of gas pollution environment is not solved.
申请号为 99102862.7公开了一种废印刷电路板的粉碎分离回收工艺及其所 用设备。 该发明首先将印刷电路板粉碎成碎料, 再进一步细粉碎, 在细粉碎的 同时, 粉末状出料通过风选, 把非金属先分离出, 再把剩下的金属与非金属粉 末由空气分离器进行分离, 粗粉则返回细粉碎机继续粉碎。 这种采用机械粉碎 的方法步骤多、 流程长、 设备投资大, 回收过程需要消耗很大的能量, 回收成 本高, 且在破碎和磨碎过程不但金属物质粘附严重, 而且容易产生有毒气体, 污染环境。  Application No. 99102862.7 discloses a pulverization separation and recovery process for waste printed circuit boards and equipment therefor. The invention first pulverizes the printed circuit board into scraps and further finely pulverizes them. At the same time of fine pulverization, the powdery discharge is separated by air separation, and the non-metal is separated first, and then the remaining metal and non-metal powder are separated from the air. The separator is separated, and the coarse powder is returned to the fine pulverizer to continue pulverization. This method of mechanical pulverization has many steps, long process, and large equipment investment. The recycling process requires a large amount of energy, high recovery cost, and not only the metal substance adheres seriously during the crushing and grinding process, but also toxic gas is easily generated. polluted environment.
申请号为 200310103403.0公开了一种回收废旧印刷电路板中有价资源的方 法。 该方法首先将废弃电路板元件拆除, 分别进行粗碎细碎, 然后采用干法磁 选机选出铁磁性物质, 高频振动气力分选机, 分选出金属物质、 非金属物质, 采用湿法磁选机出铁磁性物质, 用浮选柱对选出的铁磁性物质的物料进行分 选, 最终产出铁磁性物质, 铜、 合金, 以及塑料和树脂。 这种方法在拆除元件 步骤中多半采用手工拆卸, 耗时且效率低。 采用粉碎的方法也具有流程长、 能 耗高、 成本高等缺点, 而且粉碎过程中也有有毒气体产生。  Application No. 200310103403.0 discloses a method of recycling valuable resources in a waste printed circuit board. The method firstly dismantles the components of the waste circuit board, separately performs coarse crushing, and then uses a dry magnetic separator to select a ferromagnetic substance, a high frequency vibrating pneumatic sorting machine, and sorts metal materials and non-metal materials, and adopts a wet method. The magnetic separator extracts the ferromagnetic material, and the selected ferromagnetic material is sorted by a flotation column to finally produce ferromagnetic materials, copper, alloys, and plastics and resins. This method is mostly manual disassembly in the step of removing components, which is time consuming and inefficient. The pulverization method also has the disadvantages of long process, high energy consumption, high cost, and the like, and toxic gases are also generated during the pulverization process.
申请号为 200410013482.5公开了一种废弃电路板中金属富集体的物理回收 工艺。 该工艺整个流程全部采用机械和物理分选的方法, 将废弃电路板经双齿 辊剪切机、 高效离心分选机, 依次进行剪切、 破碎、 筛分、 分选, 最终分离多 种成分的金属富集体和非金属富集体。 这种机械破碎的方法处理电路板也具有 能耗高、 成本高、 存在环境污染等缺点, 且该工艺未全面考虑非金属的回收问 题。  Application No. 200410013482.5 discloses a physical recovery process for a metal rich group in a waste circuit board. The whole process of the process adopts mechanical and physical sorting methods. The waste circuit board is subjected to shearing, crushing, sieving and sorting by double-tooth roll shearing machine and high-efficiency centrifugal sorting machine to finally separate various components. The metal rich and non-metallic rich collective. This mechanical crushing method also has disadvantages such as high energy consumption, high cost, and environmental pollution, and the process does not fully consider the problem of non-metal recycling.
申请号为 200510084196.8公开了一种废旧印刷电路板资源回收的方法。 首 物料在氮气中通过常压热解系统进行热解, 热解后固体采用剪切细碎机进行细 碎, 使金属与非金属分离: 用磁选机从细碎产物中选出铁磁性物质: 对磁选后 剩余物釆用高频气力分选机按密度分离金属与非金属。 进行机械破碎后再热解 进一步粉碎分离, 处理过程能耗较高: 氮气气氛下热解电路板易发生二次裂解, 产生大量含卤气体, 现场环境条件差, 前期粗碎时也会产生有毒气体污染环境。 Application No. 200510084196.8 discloses a method for recycling waste printed circuit board resources. The first material is pyrolyzed by a normal pressure pyrolysis system in nitrogen, and the solid is finely divided by a shearing and crushing machine after pyrolysis. Broken, separating metal from non-metal: Selecting ferromagnetic material from finely divided product by magnetic separator: For magnetic residue, use high-frequency pneumatic separator to separate metal and non-metal by density. After mechanical crushing, it is further pyrolyzed and further pulverized and separated. The energy consumption in the treatment process is high: The pyrolysis circuit board is prone to secondary cracking under nitrogen atmosphere, and a large amount of halogen-containing gas is generated. The environmental conditions on the site are poor, and toxic during the early coarse crushing. Gas pollutes the environment.
申请号为 200610002019.5公开了一种回收废弃印刷电路板的方法。 该发明 首先加热废弃电路板, 拆除所用电子组件: 用真空吸锡装置将表层的焊锡去除, 然后用硝酸剥锡液浸泡已去除表层焊锡的废弃电路板, 以回收电路板内层的焊 锡: 然后用强酸溶解电路板, 使电路板上的铜箔溶解在该熔液中: 将处理后的 废弃电路板投入熔融态硝酸钠熔液进行热裂解, 使得玻璃纤维与有机物质及其 他组分分离。 这种方法处理电路板流程长, 成本高。 处理过程中产生大量的有 害气体和废酸, 对环境造成二次污染。  Application No. 200610002019.5 discloses a method of recycling a waste printed circuit board. The invention first heats the waste circuit board and removes the electronic components used: the surface solder is removed by a vacuum suction device, and then the waste circuit board from which the surface solder has been removed is soaked with a nitric acid stripping solution to recover the solder of the inner layer of the circuit board: Dissolving the circuit board with a strong acid to dissolve the copper foil on the circuit board in the molten metal: The treated waste circuit board is put into a molten state of sodium nitrate melt for thermal cracking to separate the glass fiber from the organic matter and other components. This method handles the long process flow of the board and is costly. A large amount of harmful gases and waste acid are generated during the treatment, causing secondary pollution to the environment.
德国 Daimler-Benz Ulm Research Centre公司开发了四段式处理工艺: 欲破 碎、 液氮冷冻再粉碎, 分, 静电分选后使得金属与非金属分离。 该公司研制 的电分选设备可以分离尺寸小于 0.1mm的颗粒。 用低温破碎的方法减少了有害 气体的产生并使得废弃电路板更易破碎, 解决了传统的机械破碎产生有毒气体 的问题, 但这种工艺流程长, 并且对设备要求极高, 制冷过程消耗能量大, 成 本高。  Germany Daimler-Benz Ulm Research Centre has developed a four-stage process: to break, to freeze and then pulverize liquid nitrogen, to separate the metal from the non-metal after electrostatic separation. The company's electric sorting equipment can separate particles smaller than 0.1mm in size. The low-temperature crushing method reduces the generation of harmful gases and makes the waste circuit board more fragile, and solves the problem of the traditional mechanical crushing to generate toxic gas, but the process flow is long, and the equipment is extremely demanding, and the refrigeration process consumes a large amount of energy. , high cost.
德国 Kamet Recycling Gmbh公司采用的处理工艺是通过破碎、 重选、 磁选、 涡流分离的方法获得铁、 铝、 贵金属和有机物等几个组分。 德国 Trischler und Partner Gmbh公司的处理昂奋与之基本相同。 这两种方法是目前最常用的机械 处理工艺, 一般经过这样的处理后, 废电路板中 90%的金属和塑料得以回收, 10%左右的剩余物质(包括很难进一步处理的细粒物料、 粉尘等)则根据成分的 性质填埋或焚烧, 造成环境污染。  The processing technology used by Kamet Recycling Gmbh in Germany is to obtain several components such as iron, aluminum, precious metals and organic matter by means of crushing, re-election, magnetic separation and vortex separation. The treatment of Trischler und Partner Gmbh in Germany is basically the same. These two methods are the most commonly used mechanical treatment processes. After such treatment, 90% of the metal and plastic in the waste circuit board can be recycled, and about 10% of the remaining materials (including fine materials that are difficult to further process, Dust, etc.) is landfilled or incinerated depending on the nature of the ingredients, causing environmental pollution.
日本 EC公司开发了一种废弃电路板处理工艺。 该工艺首先利用红外加热 和两级去除的方式(分别利用垂直和水平方向的冲击力作用)使穿孔元件脱落, 不会造成任何损伤。 然后再结合加热、 冲击力和表面剥蚀技术, 使电路板上 96% 的焊料脱焊, 再采用两段式破碎法分离回收电路板。 分别使用剪切破碎机和特 制的具有剪断和沖击作用磨碎机, 将廈板粉碎成 0.1-0.3mm左右的碎块。 特制的 磨碎机中使用复合研磨转子, 并选用特种陶瓷作为研磨材料。 此项及技术以空 气作为加热介质去除焊锡和元件, 热利用率相对偏低, 且在空气中加热电路板 会使一些有毒元素挥发, 从而造成环境污染, 需要进行密闭处理和有毒物质的 处理: 此外通过两级破碎分离与非金属, 此过程中易产生有害气体造成环境污 染, 回收成本也高。 Japanese EC Corporation has developed a waste circuit board processing process. The process first uses infrared heating and two-stage removal (using vertical and horizontal impact forces, respectively) to detach the perforated elements without causing any damage. Then combined with heating, impact and surface ablation techniques, 96% of the solder on the board is desoldered, and the board is separated and separated by a two-stage crushing method. Use shear crusher and special The mill has a shearing and impact action, and the slab is pulverized into pieces of about 0.1-0.3 mm. A special grinding rotor is used in the special grinding machine, and special ceramics are used as the grinding material. This and the technology use air as a heating medium to remove solder and components, and the heat utilization rate is relatively low, and heating the circuit board in the air will cause some toxic elements to volatilize, thereby causing environmental pollution, requiring sealing treatment and treatment of toxic substances: In addition, through two-stage crushing separation and non-metal, in this process, harmful gases are easily generated to cause environmental pollution, and the recovery cost is also high.
瑞典的 Scandinavian Recycling AB(SR)开发了一种旋转式破碎机, 在中间 转简周围安装着一套能够自由旋转的压碎环, 依靠压碎环与设备内壁之间的剪 切作用破碎物料。 使用这种破碎机可以减小解离后金属的缠绕作用。 瑞士 Result 技术公司开发了一种在超音速下将涂层线路板等多层复合制件破碎的新设备。 它利用各种层压材料的冲击和离心特性不同, 将多层复合材料彼此分开。 不同 材料的变形情况不同, 脆性材料碎成粉末, 金属则形成多层球状物。 这两种设 备依靠剪切、 冲击和离心等方式破碎废弃电路板, 虽对破碎效率有所改善, 但 仍具有能耗高、 易造成环境污染等缺点。  Sweden's Scandinavian Recycling AB (SR) has developed a rotary crusher with a freely rotatable crush ring around the intermediate turn, which relies on the shearing action between the crush ring and the inner wall of the device to break the material. The use of such a crusher can reduce the entanglement of the metal after dissociation. Swiss Result Technologies has developed a new device for breaking multi-layer composite parts such as coated circuit boards at supersonic speeds. It utilizes the different impact and centrifugal properties of the various laminates to separate the multilayer composites from one another. The deformation of different materials is different, the brittle material is broken into powder, and the metal forms a multi-layered ball. These two devices rely on shearing, impact and centrifugation to break the waste circuit board. Although the crushing efficiency is improved, it still has the disadvantages of high energy consumption and environmental pollution.
上述方法对废弃电路板组分进行分离回收, 其回收过程具有能耗高、 易污 染环境等缺点。 废弃电路板的资源化应全面考虑金属和有机物质的无害化高效 回收, 焊锡的提前回收对其他金属的高效分离可以创造好条件, 因此, 现有技 术需要进一步完善, 以提高回收效率和回收纯度: 同时还需开发新的处理工艺 及设备, 寻找低成本的、 更有效的适合大规模的废弃电路板资源化回收方法。 发明内容  The above method separates and recycles the components of the waste circuit board, and the recycling process has the disadvantages of high energy consumption and easy pollution environment. The recycling of waste circuit boards should fully consider the harmless and efficient recovery of metals and organic materials. The early recovery of solder can create favorable conditions for the efficient separation of other metals. Therefore, the existing technology needs to be further improved to improve recovery efficiency and recovery. Purity: At the same time, new processing technologies and equipment need to be developed to find a low-cost, more efficient resource recycling method for large-scale waste circuit boards. Summary of the invention
本发明的目的在于克服现有技术不足而提供一种根据废弃玻璃钢、 废弃电 路板的无污染微波辐射裂解, 并从裂解中回收芳烃类有机成分的回收方法。 该 回收方法处理过程简单, 无污染, 成本低, 回收效率高。  SUMMARY OF THE INVENTION It is an object of the present invention to provide a method for recovering aromatic hydrocarbon-based organic components from cracking of non-contaminated microwave radiation from waste glass steel and waste circuit boards by overcoming the deficiencies of the prior art. The recycling method has simple processing, no pollution, low cost and high recycling efficiency.
本发明的目的可以通过以下技术措施实现: 一种废弃玻璃钢和废弃电路板 有价资源的回收方法, 所述方法包括以下步骤:  The object of the present invention can be achieved by the following technical measures: A method for recovering valuable resources from waste glass steel and waste circuit boards, the method comprising the following steps:
( 1 )微波热裂解: 将废弃玻璃钢和废弃电路板置于高频微波炉中, 开启高 频微波炉, 物料在微波的作用下产生 500 °C-600°C的高温, 使热固性高分子材料 分解裂化, 得到热裂解气和固体残渣; (1) Microwave thermal cracking: Put waste glass steel and waste circuit board in high frequency microwave oven, open high Frequency microwave oven, the material generates high temperature of 500 °C-600 °C under the action of microwave, and the thermosetting polymer material is decomposed and cracked to obtain thermal cracking gas and solid residue;
( 2 ) 收集冷凝: 收集步骤 (1 ) 炉内的热裂解气, 经冷凝后得到芳烃类混 合有机物;  (2) Collecting condensation: Collection step (1) The pyrolysis gas in the furnace is condensed to obtain an aromatic hydrocarbon mixed organic matter;
( 3 ) 残渣冶炼: 收集步骤 (1 ) 的固体残渣, 再经冶化炉高温冶炼, 分离 获得有色金属和碳渣。 作为本发明废弃玻璃钢和废弃电路板有价资源的回收方法的优选实施方 式, 所述的步骤 (1 ) 中采用 lwt%~2wt%的氧化铝作为裂解催化剂。 作为本发明废弃玻璃钢和废弃电路板有价资源的回收方法的优选实施方 式, 在步骤 (1 )微波热裂解前, 还包括步骤 (la ): 将废弃玻璃钢和废弃电路 板投入粉碎机中磨粉成 30〜60目的细 ' j、粉末。 作为本发明废弃玻璃钢和废弃电路板有价资源的回收方法的优选实施方 式, 所述的步骤 ( 2 ) 中的冷凝温度为 10〜30 °C。 作为本发明废弃玻璃钢和废弃电路板有价资源的回收方法的优选实施方 式, 所述的回收方法还包括  (3) Residue smelting: The solid residue of step (1) is collected, and then smelted by high temperature in a smelting furnace to separate non-ferrous metals and carbon residue. As a preferred embodiment of the method for recovering valuable resources of the waste glass reinforced plastic and the waste circuit board of the present invention, in the step (1), 1 wt% to 2 wt% of alumina is used as the cracking catalyst. As a preferred embodiment of the method for recovering valuable resources of waste glass fiber reinforced plastics and waste circuit boards of the present invention, before step (1) microwave thermal cracking, step (la) is further included: the waste glass reinforced plastic and the waste circuit board are put into the pulverizer for milling. Made into 30~60 mesh fine 'j, powder. As a preferred embodiment of the method for recovering valuable resources of the waste glass reinforced plastic and the waste circuit board of the present invention, the condensation temperature in the step (2) is 10 to 30 °C. As a preferred embodiment of the method for recovering valuable resources of the waste glass reinforced plastic and the waste circuit board of the present invention, the recovery method further includes
步骤 (4 )碳渣再利用: 将步骤 (3 )得到的碳渣作为水泥厂的水泥烧结材 料使用。 本发明用微波高温裂解废弃电路板及废弃玻璃钢, 从中回收有价资源的方 法, 其优点如下:  Step (4) Carbon residue reuse: The carbon residue obtained in the step (3) is used as a cement sintered material of a cement plant. The invention uses microwave high-temperature pyrolysis waste circuit board and waste glass steel to recover valuable resources therefrom, and the advantages thereof are as follows:
1、 用微波技术高温裂解废弃电路及废弃玻璃钢能够消除用煤炭焚烧造成 的环境污染问题。 由于用微波高频辐射使其炉内的温度在几十秒内就可达到裂 解要求。 使用微波后再配合适量的催化剂使裂化温度稳定、 易于操作控制, 易 挥发物馏程较低, 干馏出的有机物多为有回收价值的芳烃类有机物。 1. High-temperature cracking of waste circuits and waste glass steel by microwave technology can eliminate environmental pollution caused by coal incineration. The cracking requirement can be achieved by using microwave high-frequency radiation to bring the temperature in the furnace within several tens of seconds. The use of microwaves with a suitable amount of catalyst to stabilize the cracking temperature, easy to operate and control, easy The volatile matter distillation range is low, and the dry distillation organic matter is mostly aromatic hydrocarbon organic matter with recovery value.
2、 废弃电子线路板及玻璃钢废弃物经过微波高频辐射后再进入冶炼炉, 可使得有色金属在各相的熔点中分离出较纯金属物, 这是过去用其它物理分离 所不能做到的。  2. Waste electronic circuit boards and FRP wastes enter the smelting furnace after microwave high-frequency radiation, which can make non-ferrous metals separate relatively pure metal in the melting point of each phase, which was not possible with other physical separations in the past. .
3、由于使用微波高频裂解代替了传统的土法提取,有利于有机成分的回收, 有色金属的回收率也能显著提高, 本发明在有机成分的回收中或有色金属的回 收中都具有较高的经济效益, 每一程序所要求的设备简单、 条件易于控制, 能 明显降低回收处理成本和设备投资。  3. Due to the use of microwave high-frequency cracking instead of the traditional soil extraction, it is beneficial to the recovery of organic components, and the recovery rate of non-ferrous metals can be significantly improved. The invention has the advantages in the recovery of organic components or the recovery of non-ferrous metals. High economic efficiency, the equipment required for each procedure is simple, the conditions are easy to control, and the recycling cost and equipment investment can be significantly reduced.
4、 回收效率高, 能耗低, 适合废弃电子线路板及玻璃钢废弃物的大规模回 收。  4. High recovery efficiency and low energy consumption, suitable for large-scale recycling of waste electronic circuit boards and FRP waste.
综上所述, 本发明根据废弃电路板及废弃玻璃钢的材料特性, 用微波高频 辐射裂解, 优化了废弃热固性树脂的处理条件和工序, 在热裂解过程中方法简 单, 使得废弃电子线路板的回收成本更低, 效率更高, 更符合工业化回收处理 的要求, 适合废弃电路板及废弃玻璃钢的大规模回收处理。 具体实施方式 为使本发明更加容易理解, 下面将进一步阐述本发明的具体实施例。  In summary, the present invention optimizes the processing conditions and processes of the waste thermosetting resin according to the material characteristics of the waste circuit board and the waste glass fiber reinforced by microwave high-frequency radiation, and the method is simple in the thermal cracking process, so that the waste electronic circuit board is discarded. The recycling cost is lower, the efficiency is higher, and it is more in line with the requirements of industrial recycling treatment. It is suitable for large-scale recycling of waste circuit boards and waste glass steel. DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS In order to make the present invention easier to understand, specific embodiments of the present invention will be further described below.
实施例 1  Example 1
本实施例用微波、 碳炉综合加热裂解废弃电路板及废弃玻璃钢有价资源的 回收方法, 其步骤如下:  In this embodiment, a microwave, carbon furnace integrated heating cracking waste circuit board and a waste glass steel valuable resource recycling method are as follows:
〈1〉用微波高频辐射: 将废弃电子线路板装入微波炉裂解炉中, 并加入适 合的催化剂,将微波炉内的温度升至 500 °C~600 °C经过在微波辐射 5~6分钟进行 热裂解;  <1> Using microwave high-frequency radiation: The waste electronic circuit board is placed in a microwave cracking furnace, and a suitable catalyst is added to raise the temperature in the microwave oven to 500 ° C to 600 ° C for 5 to 6 minutes under microwave irradiation. Thermal cracking
〈2〉收集热裂解馏出产物,于 10 °C~30 °C冷凝成芳烃有机化合物(液态油); 〈3〉微波高频热裂解: 将裂解后的固态产物再进一步进行冶炼温度在 130 0 °C~1500 °C , 其作用是把有色金属从残渣中分离出来, 根据各有色金属的熔点 设定炉内的温度, 从 500 °C到 1500 °C分段提取分离; <2> Collecting the pyrolysis distillate product and condensing it into an aromatic hydrocarbon organic compound (liquid oil) at 10 °C ~ 30 °C; <3> Microwave high-frequency thermal cracking: further smelting the solid product after cracking at 130 0 °C ~ 1500 °C, its role is to separate the non-ferrous metals from the residue, according to the melting point of each non-ferrous metal Set the temperature in the furnace, and extract and separate it from 500 °C to 1500 °C;
〈 4 >收集完残渣中的金属成分再把剩余的玻璃纤维无机物作为水泥厂的水 泥烧结材料使用。  < 4 > The metal component in the residue is collected and the remaining glass fiber inorganic material is used as a cement sintered material of the cement plant.
该方法可以完全解决废弃电子线路板及废弃玻璃钢污染的问题。 实施例 2  The method can completely solve the problem of waste electronic circuit board and waste glass steel pollution. Example 2
本实施例废弃玻璃钢和废弃电路板有价资源的回收方法, 包括如下过程: 微波高频裂解: 将废弃电路板及废弃玻璃钢经破碎机破碎后再经螺旋送料 器送入微波高频裂解炉中升至 500 °C~600 °C, 在裂解过程中炉内添加 1%~2%的 氧化铝用作催化剂 (使用催化剂的目的是提高芳烃有机物的产出率, 减化反应 过程, 减低能耗节约成本);  The recycling method for the valuable resources of the waste glass steel and the waste circuit board in the present embodiment includes the following processes: Microwave high-frequency cracking: the waste circuit board and the waste glass fiber reinforced plastic are crushed by the crusher and then sent to the microwave high-frequency cracking furnace through the screw feeder. Increased to 500 °C ~ 600 °C, adding 1%~2% alumina in the furnace as a catalyst during the cracking process. The purpose of using the catalyst is to increase the yield of aromatic organic compounds, reduce the reaction process, and reduce energy consumption. save costs);
当温度上升至 250°C时, 炉内的热固性材料就开始解聚, 有部分低馏分的挥 发物被干馏出来, 当继续提温度时, 反应产物的产出量急剧增加; 当温度上升 到 500:〜 600°C时, 收集热裂解气并冷凝获得芳烃有机化合物; 炉内的廈弃电子 线路板及废弃玻璃钢也已变成含金属的残渣, 再经高温冶炼炉升温冶炼, 直至 各种有色金属完全分离出来。  When the temperature rises to 250 ° C, the thermosetting material in the furnace begins to depolymerize, and some of the low-fraction volatiles are retorted. When the temperature is continuously increased, the output of the reaction product increases sharply; when the temperature rises to 500 : ~ 600 ° C, collecting thermal cracking gas and condensation to obtain aromatic organic compounds; the furnace abandoned electronic circuit board and waste glass steel has also become a metal-containing residue, and then heated and smelted in a high-temperature smelting furnace until various colored The metal is completely separated.
收集最终的碳渣, 可作工业原料用在水泥厂作为烧水泥的原料使用。 实施例 3  The final carbon residue is collected and used as an industrial raw material in cement plants as a raw material for burning cement. Example 3
-破砰后冉经过螺旋施 送料器, 进入高频微波炉中, 炉中要加入 1%~2%的氧化铝之类的催化剂, 升温 500 °C~600 °C时把炉内干馏出热解有机成分进行收集, 换热器的冷凝温度 20 °C~ 30°C馏出成分多为芳烃类有机物。 经过干馏后的固体物含金属 15%~20%, 残渣 80%~85%, 再经过高温冶炼炉进行分离得到各种较纯的有色金属物, 最终的碳 渣作为烧结水泥的材料使用。  - After breaking, pass through the screw feeder and enter the high-frequency microwave oven. Add 1%~2% alumina to the furnace, and heat the furnace to distill the pyrolysis at 500 °C~600 °C. The organic components are collected, and the condensation temperature of the heat exchanger is 20 ° C ~ 30 ° C. The distillate components are mostly aromatic hydrocarbons. The solid matter after dry distillation contains 15% to 20% of metal and 80% to 85% of residue, and is then separated into a variety of pure non-ferrous metals by a high-temperature smelting furnace, and the final carbon residue is used as a material of sintered cement.
结论: (1 ) 在微波炉的高频作用下炉内会产生几百度的高温, 使得热固性 树脂快速断链转化成芳烃类有机物, 干馏物占 16%左右。 ( 2 ) 回收固体残渣经高温冶炼分离出 15%~20%的金属物, 最终的碳渣可 用于水泥厂烧结材料使用。 实施例 4 沫再经高频微波炉, 微波炉为管式热解炉, 裂解方式为连续式裂解, 可不使用 催化剂, 炉内的温度也在 500 °C -600 °C内无催化干馏。 Conclusion: (1) In the microwave oven, high temperature of several hundred degrees will be generated in the furnace, which will cause the thermosetting resin to be quickly broken into aromatic hydrocarbons, and the dry distillation accounts for about 16%. (2) The recovered solid residue is separated by high temperature smelting to separate 15%~20% of metal materials, and the final carbon residue can be used for sintering materials in cement plants. Example 4 The foam was passed through a high-frequency microwave oven. The microwave oven was a tubular pyrolysis furnace. The cracking method was continuous cracking. The catalyst was not used, and the temperature in the furnace was also free of catalytic dry distillation at 500 °C - 600 °C.
结论: (1 )尽管在热裂过程中没使用催化剂, 但是废弃电子线路板及玻璃 钢废弃物的粒径 30~60目仍能有效裂解。  Conclusions: (1) Although no catalyst is used in the thermal cracking process, the particle size of waste electronic circuit board and glass steel waste can be effectively cracked by 30~60 mesh.
( 2 )由于废弃电子线路板已被破碎成细 d、微粒状,金属成分可用静电分出。 实施例 5  (2) Since the waste electronic circuit board has been broken into fine d and fine particles, the metal component can be separated by static electricity. Example 5
将废弃电子线路板及玻璃钢废弃物经破碎机打碎成块状物再配入 1%~2%的 铝粉作催化剂, 微波炉裂解温度为 500 °C~600 °C , 冷凝器水温 10°C~20°C裂解产 物为芳烃类。  The waste electronic circuit board and FRP waste are broken into pieces by the crusher and then mixed with 1%~2% aluminum powder as catalyst. The cracking temperature of the microwave oven is 500 °C~600 °C, and the condenser water temperature is 10 °C. The ~20 ° C cracking product is an aromatic hydrocarbon.
结论: (1 )在高频微波裂解中, 芳烃有机物产出率为 16.5%。  Conclusions: (1) In high frequency microwave cracking, the aromatics organic matter yield is 16.5%.
( 2 )各种有色金属可以达到完全回收而且对环境不会带来污染。  (2) Various non-ferrous metals can be completely recycled and will not pollute the environment.
( 3 )最终的固体残留物也可以回收利用, 真正达到了资源循环再利用的目 的。 最后所应当说明的是, 以上实施例仅用以说明本发明的技术方案而非对本 发明保护范围的限制, 尽管参照较佳实施例对本发明作了详细说明, 本领域的 普通技术人员应当理解, 可以对本发明的技术方案进行修改或者等同替换, 而 不脱离本发明技术方案的实质和范围。  (3) The final solid residue can also be recycled, which truly achieves the purpose of recycling resources. It should be noted that the above embodiments are only intended to illustrate the technical solutions of the present invention, and are not intended to limit the scope of the present invention. The technical solutions of the present invention may be modified or equivalently substituted without departing from the spirit and scope of the technical solutions of the present invention.

Claims

权 利 要 求 Rights request
1、 一种废弃玻璃钢和废弃电路板有价资源的回收方法, 其特征在于, 所述 方法包括以下步骤: A method for recovering valuable resources of waste fiberglass and waste circuit boards, characterized in that the method comprises the following steps:
( 1 )微波热裂解: 将废弃玻璃钢和废弃电路板置于高频微波炉中, 开启高 频微波炉, 物料在微波的作用下产生 500°C-600°C的高温, 使热固性高分子材料 分解裂化, 得到热裂解气和固体残渣;  (1) Microwave thermal cracking: The waste glass fiber reinforced plastics and waste circuit board are placed in a high-frequency microwave oven, and the high-frequency microwave oven is turned on. The material generates a high temperature of 500 ° C to 600 ° C under the action of microwave, and the thermosetting polymer material is decomposed and cracked. , obtaining pyrolysis gas and solid residue;
( 2 ) 收集冷凝: 收集步骤(1 ) 炉内的热裂解气, 经冷凝后得到芳烃类混 合有机物;  (2) Collecting condensation: Collecting step (1) The pyrolysis gas in the furnace is condensed to obtain an aromatic hydrocarbon mixed organic matter;
( 3 ) 残渣冶炼: 收集步骤(1 ) 的固体残渣, 再经冶化炉高温冶炼, 分离 获得有色金属和碳渣。  (3) Residue smelting: The solid residue of step (1) is collected, and then smelted by high temperature in a smelting furnace to separate non-ferrous metals and carbon slag.
2、 根据权利要求 1所述废弃玻璃钢和废弃电路板有价资源的回收方法, 其 特征在于, 所述的步骤(1 ) 中釆用 lwt%~2wt%的氧化铝作为裂解催化剂。 A method for recovering valuable resources of waste glass reinforced plastics and waste circuit boards according to claim 1, wherein in the step (1), lwt% to 2% by weight of alumina is used as a cracking catalyst.
3、 根据权利要求 1所述废弃玻璃钢和废弃电路板有价资源的回收方法, 其 特征在于, 在步骤( 1 )微波热裂解前, 还包括步骤(la ): 将废弃玻璃钢和废 弃电路板投入粉碎机中磨粉成 30-60目的细 'J、粉末。 3. The method for recovering valuable resources of waste fiberglass and waste circuit boards according to claim 1, characterized in that, before step (1) microwave thermal cracking, step (la) is further included: putting waste fiberglass and waste circuit boards into The powder is ground into a fine powder of 30-60 mesh in a pulverizer.
4、 根据权利要求 1所述废弃玻璃钢和废弃电路板有价资源的回收方法, 其 特征在于, 所述的步骤(2 ) 中的冷凝温度为 10~30°C。 A method of recovering valuable resources of waste fiberglass and waste circuit boards according to claim 1, wherein the condensation temperature in said step (2) is 10 to 30 °C.
5、 根据权利要求 1所述废弃玻璃钢和废弃电路板有价资源的回收方法, 其 特征在于, 所述的回收方法还包括 5. The method for recovering valuable resources of waste fiberglass and waste circuit boards according to claim 1, wherein said recycling method further comprises
步骤(4 )碳渣再利用: 将步骤(3 )得到的碳渣作为水泥厂的水泥烧结材 料使用。  Step (4) Carbon residue reuse: The carbon residue obtained in the step (3) is used as a cement sintered material of a cement plant.
PCT/CN2010/077697 2010-10-13 2010-10-13 Method for recovering valuable resource from waste gfrp and waste circuit board WO2012048462A1 (en)

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