JPH1176980A - Treatment of printed board - Google Patents

Treatment of printed board

Info

Publication number
JPH1176980A
JPH1176980A JP24501597A JP24501597A JPH1176980A JP H1176980 A JPH1176980 A JP H1176980A JP 24501597 A JP24501597 A JP 24501597A JP 24501597 A JP24501597 A JP 24501597A JP H1176980 A JPH1176980 A JP H1176980A
Authority
JP
Japan
Prior art keywords
board
metal
printed circuit
gas
circuit board
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.)
Pending
Application number
JP24501597A
Other languages
Japanese (ja)
Inventor
Takeshi Yasuda
健 安田
Koji Sato
晃二 佐藤
Kazuhiko Sato
和彦 佐藤
Hisao Yamashita
寿生 山下
Shigeru Azuhata
茂 小豆畑
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.)
Hitachi Ltd
Original Assignee
Hitachi Ltd
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 Hitachi Ltd filed Critical Hitachi Ltd
Priority to JP24501597A priority Critical patent/JPH1176980A/en
Publication of JPH1176980A publication Critical patent/JPH1176980A/en
Pending legal-status Critical Current

Links

Classifications

    • HELECTRICITY
    • H05ELECTRIC TECHNIQUES NOT OTHERWISE PROVIDED FOR
    • H05KPRINTED CIRCUITS; CASINGS OR CONSTRUCTIONAL DETAILS OF ELECTRIC APPARATUS; MANUFACTURE OF ASSEMBLAGES OF ELECTRICAL COMPONENTS
    • H05K3/00Apparatus or processes for manufacturing printed circuits
    • H05K3/22Secondary treatment of printed circuits
    • 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

  • Processing Of Solid Wastes (AREA)
  • Combined Means For Separation Of Solids (AREA)
  • Disintegrating Or Milling (AREA)

Abstract

PROBLEM TO BE SOLVED: To separate and recover metals and nonmetals in a waste printed board by heating a waste printed board to generate gas from resinous materials in the board and to weaken component-integrating functions in the board, and then, mechanically crushing the resulting weakly-integrated waste printed board by applying external force to the board. SOLUTION: In this treatment, a waste printed board 1 is charged into a board heating device 2 to heat the board 1, wherein, although the board heating temp. somewhat depends on the kind of the board 1, as this temp., any temp. within the range of 270 to 450 deg.C may be adopted. In this board heating device 2, resinous materials in the board 1 are converted, and concurrently, gas is generated from the resinous materials and discharged as waste gas 7. Accordingly, in the waste printed board 1 thus heat-treated, the integration of metallic components such as gold platings, copper foils and copper wires, with nonmetallic inorganic materials such as glass wool is weakened. However, sometimes, copper through-holes formed by plating, or the like, fine copper wires, etc., and these different kinds of materials are bound to each other. Therefore, the heat-treated waste printed board 1 is further crushed by a crusher 3 to easily separate metals and nonmetallic inorganic materials from each other.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は廃プリント基板の処
理方法に係り、特に廃プリント基板中の金属及び非金属
を分離,回収する方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating a waste printed circuit board, and more particularly to a method for separating and recovering metals and nonmetals from a waste printed circuit board.

【0002】[0002]

【従来の技術】リサイクル再利用で重要なことは、リサ
イクル対象物の材料別の分離・選別である。ところが、
金属,非金属無機物質及び樹脂により構成されている廃
プリント基板は材料別の選別が難しい。従って、廃プリ
ント基板は、従来は電子部品や有害なはんだがついたま
まシュレッダ処理され、最終処分場に埋立処分されてい
るのが殆どであり、金や銅に代表される金属の回収は僅
かに行われている程度で効果的なリサイクルは殆どされ
ていない。一般的に廃プリント基板のリサイクルとして
は、以下が知られている。
2. Description of the Related Art What is important in recycling and recycling is separation and sorting of materials to be recycled by material. However,
It is difficult to sort waste printed circuit boards made of metals, non-metallic inorganic substances and resins by material. Therefore, waste printed circuit boards are conventionally shredded with electronic components and harmful solder attached, and are mostly landfilled at final disposal sites.Therefore, there is little recovery of metals such as gold and copper. There is hardly any effective recycling. Generally, the following is known as recycling of a waste printed circuit board.

【0003】その1は、特開平2−88725号公報記載のよ
うに、廃プリント基板を800℃以上から銅の溶融温度
までの温度で樹脂分が着火してカーボンになる程度の空
気の供給下で焙焼し、ついで粉砕して銅を選別,回収す
る方法である。
The first problem is that, as described in Japanese Patent Application Laid-Open No. 2-88725, a waste printed circuit board is supplied with air at a temperature from 800 ° C. or higher to the melting temperature of copper so that the resin component is ignited to carbon. And then pulverize to separate and collect copper.

【0004】その2は特開平6−228667 号公報記載のよ
うに、プリント基板を粗粉砕及び微粉砕工程で粉砕し、
得られた粉砕物を比重分離によって金属成分を多く含有
する部分と、樹脂や充填材等からなる部分に分離し、回
収する方法である。
[0004] As described in JP-A-6-228667, printed circuit boards are crushed in coarse and fine crushing steps.
This is a method in which the obtained pulverized material is separated into a portion containing a large amount of a metal component and a portion made of a resin, a filler, or the like by specific gravity separation and collected.

【0005】その3は特開平6−256863 号公報記載のよ
うに、プリント基板を還元性雰囲気下かつ450℃〜1
000℃の温度雰囲気下で乾留し、残留物を大気に接触
しても急激に酸化されない程度の温度にまで冷却し、そ
の後粉砕し、粉砕物から銅などの金属とガラス等の基材
構成物とを分別する方法である。
[0005] No. 3 is that, as described in JP-A-6-256863, the printed circuit board is placed in a reducing atmosphere at 450 ° C to 1 ° C.
Dry distillation in a temperature atmosphere of 000 ° C, cool the residue to a temperature where it is not rapidly oxidized even if it comes into contact with the atmosphere, and then pulverize. It is a method of separating

【0006】その4は特開平6−296957 号公報記載のよ
うに、部品搭載の廃プリント基板を酸素を含んだ雰囲気
中で加熱し金属成分を酸化させ、粉砕処理により粉状に
微粉砕し構造材,建材,絶縁材における充填材として利
用する方法である。
No. 4, as disclosed in Japanese Patent Application Laid-Open No. 6-296957, discloses a structure in which a waste printed board on which components are mounted is heated in an atmosphere containing oxygen to oxidize a metal component, and finely pulverized by a pulverizing process. This method is used as a filler in materials, building materials and insulating materials.

【0007】その5は特開平7−75771号公報記載のよう
に、廃銅張り積層板を切断し、除熱時に樹脂が元の状態
に戻る温度範囲で加熱保持しつつ浮遊状態で相互に衝突
させて、銅とその他の成分とに分離する方法である。
No. 5 discloses a method of cutting a waste copper-clad laminate as described in Japanese Patent Application Laid-Open No. 7-75771, and colliding with each other in a floating state while heating and holding the resin in a temperature range where the resin returns to its original state when heat is removed. Then, it is a method of separating into copper and other components.

【0008】[0008]

【発明が解決しようとする課題】しかしながら、前記各
方法はいずれも以下に示すような課題を含んでいる。
However, each of the above methods has the following problems.

【0009】その1に示した方法は、800℃以上の高
温に加熱するためエネルギー消費量が多く、また、この
温度範囲では、金や銅の金属類は基板中のガラス繊維等
の非金属強化材と反応しガラス化する。ガラス化した金
属類を再精錬することはエネルギー消費量が多く回収効
率も低くなる。
The method 1 heats to a high temperature of 800 ° C. or more, which consumes a large amount of energy. In this temperature range, metals such as gold and copper are reinforced by non-metals such as glass fibers in a substrate. Reacts with materials and vitrifies. Re-smelting vitrified metals requires high energy consumption and low recovery efficiency.

【0010】その2に示した方法は、金属やガラスウー
ルなどの非金属材料などと樹脂が密着している状態であ
るために被粉砕物の強度が強くて、基板を微粉砕するの
が大変難しい。したがって特殊な破砕機を使用する必要
があるため、処理コストが高くなる。また、金や銅等の
金属材料は樹脂やガラス繊維と強固に密着しているた
め、微粉砕しても樹脂と分離しない金属が多いため、回
収率は低く、回収後も金属と樹脂を分離する工程が必要
である。
In the method described in No. 2, since the non-metallic material such as metal or glass wool is in close contact with the resin, the strength of the object to be pulverized is high, and it is very difficult to finely pulverize the substrate. difficult. Therefore, it is necessary to use a special crusher, which increases the processing cost. In addition, since metal materials such as gold and copper are tightly adhered to resin and glass fiber, many metals do not separate from resin even when finely pulverized, so the recovery rate is low, and the metal and resin are separated even after recovery. Need to be performed.

【0011】その3に示した方法は、上記その1に示し
た方法と同様にエネルギー消費量が多く、且つ、上記温
度範囲では金属がガラスと反応しガラス化するため、回
収効率は低い。
The method of the third method consumes a large amount of energy similarly to the method of the first method, and the metal reacts with the glass in the above temperature range to vitrify, so that the recovery efficiency is low.

【0012】その4に示した方法は、金属を回収せず微
粉砕物をそのまま充填材として利用するものであり利用
分野が限られる。
The method described in No. 4 uses a finely pulverized material as it is as a filler without recovering the metal, and the field of application is limited.

【0013】その5に示した方法は、無処理のままなの
で切断が難しく、且つ浮遊状態で相互に衝突させるには
特殊なサイクロンを使用する必要がある。また、本方法
は機械的な外力を加えずに切断した基板同士の衝突のエ
ネルギーにより金属を分離しようというものである。切
断した基板は軽く、風力のみでは、切断された基板をサ
イクロン中で相互に衝突させても基板から金属を分離す
るだけのエネルギーの付与は疑問である。
The method shown in No. 5 is difficult to cut because it is left untreated, and it is necessary to use a special cyclone to collide with each other in a floating state. Further, this method is to separate metals by the energy of collision between cut substrates without applying a mechanical external force. The cut substrate is light, and with wind power alone, it is questionable that even if the cut substrates are caused to collide with each other in a cyclone, energy is applied to separate the metal from the substrate.

【0014】[0014]

【課題を解決するための手段】本発明による廃プリント
基板処理方法は、樹脂と金属及び非金属無機物質とで形
成された廃プリント基板を対象とする。廃棄物をリサイ
クル再利用するためには、構成材料それぞれを分離する
ことが好都合であるが、プリント基板では、金属をはじ
めとする各種無機物質と樹脂が物理的・化学的結合によ
り一体化されており、通常の方法では分離できない。
SUMMARY OF THE INVENTION A waste printed board processing method according to the present invention is directed to a waste printed board formed of a resin, a metal, and a nonmetallic inorganic substance. In order to recycle waste, it is convenient to separate each component material.However, on printed circuit boards, various inorganic substances including metals and resins are integrated by physical and chemical bonding. And cannot be separated by ordinary methods.

【0015】本発明では、このようなプリント基板にお
いて最も確実で効率的な構成材料の分離は、金属と非金
属に分離することであることを見出し、さらにこの考え
を実現させうる方法を見出した。
In the present invention, it has been found that the most reliable and efficient separation of constituent materials in such a printed circuit board is to separate metal and nonmetal, and furthermore, a method for realizing this idea has been found. .

【0016】廃プリント基板分離のポイントは樹脂にあ
る。樹脂はプリント基板全体を一体化させている。とこ
ろが、本発明による適切な温度の加熱により、樹脂自信
がガスを発生し不可逆的に変化する。このように樹脂が
変化した場合、樹脂の一体化作用を低減でき廃プリント
基板の分離が容易になる。同時に、樹脂中に含まれてい
る樹脂強度強化成分がガス化することにより樹脂強度も
大きく低減する。樹脂のガス化は、大気中雰囲気でも窒
素等の不活性雰囲気でも良い。加熱温度は重要である。
本発明による加熱温度は270〜450℃が好適であ
る。加熱温度が最適温度より低ければ、樹脂からガスが
発生しないため、好適でない。450℃以上ではプリン
ト基板中の銅とガラスウール等の非金属無機物質が反応
して化合物を形成し、金属と非金属無機物質の分離が極
めて難しくなるため好適ではない。なお、プリント基板
を構成している金属同志の反応及び化合物化は金属の回
収に悪い影響を与えない。
The point of waste printed circuit board separation lies in the resin. The resin integrates the entire printed circuit board. However, by heating at an appropriate temperature according to the present invention, the resin itself generates gas and changes irreversibly. When the resin changes in this manner, the action of integrating the resin can be reduced, and the separation of the waste printed circuit board becomes easy. At the same time, the resin strength enhancing component contained in the resin is gasified, thereby greatly reducing the resin strength. The gasification of the resin may be performed in an air atmosphere or an inert atmosphere such as nitrogen. The heating temperature is important.
The heating temperature according to the present invention is preferably from 270 to 450 ° C. If the heating temperature is lower than the optimum temperature, no gas is generated from the resin, which is not preferable. Above 450 ° C., copper in the printed circuit board and a nonmetallic inorganic substance such as glass wool react to form a compound, which makes separation of metal and nonmetallic inorganic substance extremely difficult, which is not preferable. It should be noted that the reaction and compounding of the metals constituting the printed circuit board do not adversely affect the recovery of the metal.

【0017】上記に説明した最適な加熱により、一体化
作用の低下した廃プリント基板に機械的に外力を加えて
破砕すると、廃プリント基板中の金属及び非金属無機物
質を効率よく分離,回収することが可能となる。プリン
ト基板内部では、スルーホールを構成する多数の小型銅
製パイプや銅細線,銅箔が存在し、それらがガラスウー
ル等の非金属無機物質と異種材料の組み合わせとして幾
何学的に複雑に絡み合っている。金属の分離には、これ
らを切断しときほぐす力が必要であり、機械的に外力を
加えた破砕がこの力となる。例えば、カッターによる破
砕をすれば大量処理もできる。加熱処理で廃プリント基
板の一体化力と強度が低減されているため、通常では大
きな動力や低い生産性を示すカッターによる破砕も本発
明ではきわめて円滑な破砕が可能である。廃プリント基
板の外から機械的な外力をあたえて破砕をしない場合に
は、分離する力が低いため、分離率が低下して好適でな
い。機械的に外力を与えて破砕するには、250℃以下
にする必要がある。250℃以上では、外力を与える破
砕機の破砕能力が十分に発揮されないため分離性能が劣
る。
When the waste printed circuit board having a reduced integration function is mechanically subjected to external force and crushed by the above-described optimal heating, metal and nonmetallic inorganic substances in the waste printed circuit board are efficiently separated and recovered. It becomes possible. Inside the printed circuit board, there are a large number of small copper pipes, copper fine wires, and copper foils that constitute through holes, and these are geometrically intricately intertwined as a combination of a nonmetallic inorganic material such as glass wool and a different material. . For separating metals, a force for cutting and loosening them is necessary, and crushing by mechanically applying external force is this force. For example, mass processing can be performed by crushing with a cutter. Since the heat treatment reduces the integration power and strength of the waste printed circuit board, crushing by a cutter which usually has a large power and low productivity can be extremely smoothly crushed in the present invention. When crushing is not performed by applying a mechanical external force from outside the waste printed circuit board, the separation force is low, and the separation rate is lowered, which is not preferable. In order to crush by applying an external force mechanically, the temperature must be 250 ° C. or less. If the temperature is higher than 250 ° C., the crushing ability of the crusher for applying an external force is not sufficiently exhibited, so that the separation performance is inferior.

【0018】廃プリント基板に機械的に外力を加えて破
砕された分離物の選別には、各種方法が採用できるが、
特に、篩い分け法及び風力選別法及び渦電流選別法の三
種類の選別法の中で少なくとも一つ以上の方法を用いる
ことが好適である。本発明による加熱処理,外力付与に
よる破砕では、金属及び非金属は、材質の延性に基づい
て延性に劣るものほど小さくなるという、破砕寸法に差
異の生じることを見出した。よって、篩い分け法は有効
な方法になる。また、本発明では、廃プリント基板の金
属と非金属が分離されているため、金属は非金属より比
重が大きいこと、金属は渦電流で選択的に分離されるこ
との性質が応用でき、風力選別法及び渦電流選別法によ
る選別が可能である。これは、金属と非金属の分離を狙
った本発明の効果である。従って、比重差を利用する風
力選別法及び渦電流選別法は本発明における重要部分で
ある。
Various methods can be used to sort the separated crushed product by mechanically applying an external force to the waste printed circuit board.
In particular, it is preferable to use at least one or more of the three types of screening methods, namely, the sieving method, the wind power screening method, and the eddy current screening method. In the crushing by the heat treatment and the application of the external force according to the present invention, it has been found that the crushing size is different, that is, the smaller the metal and the non-metal are, the less the ductility is based on the ductility of the material. Therefore, the sieving method is an effective method. Further, in the present invention, since the metal and the non-metal of the waste printed circuit board are separated, the properties that the metal has a higher specific gravity than the non-metal and that the metal is selectively separated by eddy current can be applied. Sorting by the sorting method and the eddy current sorting method is possible. This is an effect of the present invention that aims at separation of metal and nonmetal. Therefore, the wind sorting method and the eddy current sorting method using the specific gravity difference are important parts in the present invention.

【0019】加熱処理では、プリント基板を構成する樹
脂が変化してガスを発生する。ガス化成分の中には樹脂
強化成分が含まれているため樹脂は同時に軟化して以後
の破砕処理を容易にする。ガス化成分の中の臭素などを
含むハロゲン化合物系ガスは、ガス中の炭化水素成分が
殆ど分解する温度まで加熱すると、アルカリ性溶液と中
和することが可能である。
In the heat treatment, the resin constituting the printed circuit board changes to generate gas. Since the gasification component contains a resin reinforcing component, the resin is simultaneously softened to facilitate the subsequent crushing treatment. Halogen compound gas containing bromine and the like in the gasification component can be neutralized with an alkaline solution when heated to a temperature at which hydrocarbon components in the gas are almost decomposed.

【0020】上記発明をシステム化すれば、廃プリント
基板を効率よく処理することが可能となる。また、多く
の製品・部品の処理において、プリント基板のような処
理困難物を含む場合、その存在により製品・部品の処理
自体が困難になる。ところが、本発明によるシステムを
多くの製品・部品を処理する中に設ければ、多くの製品
・部品処理を効果的に実施できる。これは本発明が意図
する解決課題である。したがって、本発明によるシステ
ムが含まれる当該廃プリント基板を含む製品あるいは部
品全体を処理する処理システムも本発明に該当する。
If the above-mentioned invention is systemized, it becomes possible to efficiently treat a waste printed circuit board. Further, in the case of processing many products and parts, when a difficult-to-process object such as a printed circuit board is included, the presence thereof makes the processing of the products and parts itself difficult. However, if the system according to the present invention is provided during processing of many products and parts, many products and parts can be effectively processed. This is the solution intended by the present invention. Therefore, a processing system for processing the entire product or component including the waste printed circuit board including the system according to the present invention also corresponds to the present invention.

【0021】[0021]

【発明の実施の形態】以下、本発明を実施例に基づき説
明する。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Hereinafter, the present invention will be described based on embodiments.

【0022】図1は、本発明の一実施例である廃プリン
ト基板処理システムプロセスである。図1に示したプロ
セスの構成は、廃プリント基板1,基板加熱装置2,破
砕機3,破砕機3に併設する風力選別装置4,風力選別
装置11,ブロワー11a,回収ポット5,回収された
銅箔類5a,回収された金メッキ部5b,非金属無機物
質中心の回収ポット6,回収されたガラスウール材6
a,回収された樹脂残渣6b,排気ガス7,排気ガス加
熱装置8,中和処理装置9,中和処理槽9a,中和液回
収槽9b,中和液9c,中和液循環ポンプ9d,シャワ
ーノズル9e,排気ポンプ9f,無害排気ガス10,排
気口12より成る。
FIG. 1 shows a waste printed circuit board processing system process according to an embodiment of the present invention. The configuration of the process shown in FIG. 1 includes a waste printed circuit board 1, a substrate heating device 2, a crusher 3, a wind separator 4 attached to the crusher 3, a wind separator 11, a blower 11a, a collecting pot 5, and a collected pot. Copper foils 5a, recovered gold-plated portion 5b, recovery pot 6 centered on non-metallic inorganic material 6, recovered glass wool material 6
a, recovered resin residue 6b, exhaust gas 7, exhaust gas heating device 8, neutralization treatment device 9, neutralization treatment tank 9a, neutralization solution collection tank 9b, neutralization solution 9c, neutralization solution circulation pump 9d, It comprises a shower nozzle 9e, an exhaust pump 9f, harmless exhaust gas 10, and an exhaust port 12.

【0023】プリント基板は、図3に示すようにガラス
ウール等の非金属無機物質と、エポキシ樹脂,導体回路
となる銅箔などが複雑にからみ合って構成されており、
またスルーホールを構成する多数の銅製パイプを有す
る。
As shown in FIG. 3, the printed circuit board is composed of a non-metallic inorganic substance such as glass wool, an epoxy resin, a copper foil serving as a conductor circuit, and the like in a complicated manner.
It also has a number of copper pipes that make up through holes.

【0024】廃プリント基板1は基板加熱装置2に投入
される。ここで、基板加熱温度は基板の種類にもよる
が、270℃以上450℃以下であれば良い。270℃
より低いと、基板中の樹脂の反応,変化速度が著しく遅
く実用に供せず、また、450℃を越えると基板中の金
属とガラスウール材が反応し始め金属がガラス化し、こ
のため、金属の回収率は著しく下がるため適当でない。
この基板加熱装置2で廃プリント基板1中の樹脂分は変
化しその時にガスを発生する。これらは、排気ガス7と
して排出され、廃プリント基板1は金メッキや銅箔及び
銅線などの金属部分とガラスウールなどの非金属無機物
質の一体化は低下している。ところが、メッキ等で形成
された銅スルーホールや銅細線はこれら異種材質を結合
している場合がある。ここで廃プリント基板1を破砕機
3にかけると金属や非金属無機物質は容易に分離する。
ここで破砕機3としては、例えば図2に示すようなもの
が好適である。スルーホールが多い場合には、カッター
を用いた破砕機が便利である。基板上に電子部品が多数
搭載されている場合には、前段に粗破砕機の使用も好適
である。非金属無機物質はガラスウールが大半をしめ
る。金属部分は、金メッキされた銅線及び銅箔と、銅
箔,銅細線,銅スルーホールパイプが大半を占める。ガ
ラスウールの多くは、破砕時に発生する風力を利用した
風力選別装置4により回収ポット6に回収される。回収
ポット6で回収されない分離物を風力選別装置11にか
けることによりブロワー11aの風力により、回収ポッ
ト5に主に金属が回収され、回収ポット6に主に非金属
無機物質が回収される。また、基板加熱装置2で廃プリ
ント基板1中の樹脂分が反応,変化して生じた排気ガス
7は少なくとも炭化水素系ガスであるが、廃プリント基
板1中の難燃剤が反応してできた臭化メチル,臭化エチ
ルに代表されるハロゲン化炭化水素を含んでいるため、
これを排気ガス加熱装置8に於いて酸素を含んだ雰囲気
中で加熱して、未燃炭化水素を全て反応させ、その後中
和処理槽9aに導入する。中和処理槽9aでは中和液回
収槽9b内の中和液9cが中和液循環ポンプ9dにより
吸引され、シャワーノズル9eより噴射される。ここ
に、排気ガス加熱装置8より導入された排気ガスはシャ
ワーノズル9eから噴射された中和液により中和され、
排気ポンプ9fにより吸引され、排気口12より排出さ
れる。尚、中和液9cの種類としては、例えば水酸化ナ
トリウム,水酸化カルシウム等のアルカリ水溶液があ
る。このようにすることによりハロゲン化炭化水素はハ
ロゲン,ハロゲン化水素,二酸化炭素及び水分になる。
排気ガスの加熱には加熱炉,アフターバーナー等の使用
が考えられる。排気ガス加熱装置8からの排気ガスを中
和処理装置9に於いてハロゲンを回収しガスを無害化
し、無害排気ガス10を放出する。このようなプロセス
によりプリント基板を処理し、金属を効率よく分離,回
収できる。
The waste printed board 1 is put into a board heating device 2. Here, the substrate heating temperature may be 270 ° C. or more and 450 ° C. or less, though it depends on the type of the substrate. 270 ° C
If the temperature is lower than this, the reaction and change rate of the resin in the substrate are extremely slow, which is not practical. On the other hand, if the temperature exceeds 450 ° C., the metal in the substrate and the glass wool material start reacting, and the metal is vitrified. Is not suitable because the recovery rate is significantly reduced.
The resin content in the waste printed board 1 is changed by the board heating device 2 and gas is generated at that time. These are exhausted as exhaust gas 7, and the waste printed circuit board 1 is less integrated with metal parts such as gold plating, copper foil and copper wire and nonmetallic inorganic substances such as glass wool. However, copper through-holes and thin copper wires formed by plating or the like may combine these different materials. Here, when the waste printed circuit board 1 is subjected to the crusher 3, metals and nonmetallic inorganic substances are easily separated.
Here, as the crusher 3, for example, the one shown in FIG. 2 is preferable. When there are many through holes, a crusher using a cutter is convenient. When a large number of electronic components are mounted on the substrate, it is also preferable to use a coarse crusher in the preceding stage. Most nonmetallic inorganic substances are glass wool. The metal parts are mostly gold-plated copper wire and copper foil, copper foil, copper fine wire, and copper through-hole pipe. Most of the glass wool is collected in a collection pot 6 by a wind separation device 4 using a wind generated at the time of crushing. Separates that are not collected in the collection pot 6 are applied to the wind separation device 11, whereby the wind is blown by the blower 11 a, so that mainly the metal is collected in the collection pot 5 and the nonmetallic inorganic substance is mainly collected in the collection pot 6. Further, the exhaust gas 7 generated by the reaction and change of the resin component in the waste printed board 1 in the board heating device 2 is at least a hydrocarbon-based gas, but is formed by the reaction of the flame retardant in the waste printed board 1. Because it contains halogenated hydrocarbons such as methyl bromide and ethyl bromide,
This is heated in an atmosphere containing oxygen in the exhaust gas heating device 8 to cause all unburned hydrocarbons to react, and then introduced into the neutralization tank 9a. In the neutralizing solution tank 9a, the neutralizing solution 9c in the neutralizing solution collecting tank 9b is sucked by the neutralizing solution circulating pump 9d and jetted from the shower nozzle 9e. Here, the exhaust gas introduced from the exhaust gas heating device 8 is neutralized by the neutralizing solution injected from the shower nozzle 9e,
It is sucked by the exhaust pump 9f and discharged from the exhaust port 12. As the type of the neutralizing solution 9c, for example, there is an alkaline aqueous solution such as sodium hydroxide and calcium hydroxide. By doing so, the halogenated hydrocarbon becomes halogen, hydrogen halide, carbon dioxide and water.
For heating the exhaust gas, use of a heating furnace, an afterburner, or the like is conceivable. Exhaust gas from the exhaust gas heating device 8 is recovered in a neutralization treatment device 9 to make the gas harmless, and harmless exhaust gas 10 is released. By processing the printed circuit board by such a process, the metal can be efficiently separated and recovered.

【0025】次に、実験結果について説明する。Next, the experimental results will be described.

【0026】(1)実験1 ガラス布エポキシ樹脂プリント基板の廃材から予めはん
だ,電子部品を除去した試料を、示差熱分析で室温から
550℃まで加熱し、重量減少の割合を調べた。結果を
図4に示す。ここで重量減少は、樹脂がガス化する樹脂
量に相当する。260℃までは重量減少は認められな
い。270℃からガスが発生し、重量減少する。500
℃以上ではガスが殆ど発生しなくなり、重量減少もとま
った。
(1) Experiment 1 A sample from which solder and electronic components had been removed in advance from the waste material of a glass cloth epoxy resin printed board was heated from room temperature to 550 ° C. by differential thermal analysis, and the rate of weight loss was examined. FIG. 4 shows the results. Here, the weight loss corresponds to the amount of resin gasified by the resin. No weight loss is observed up to 260 ° C. Gas evolves from 270 ° C. and loses weight. 500
Above ℃, almost no gas was generated and the weight was reduced.

【0027】(2)実験2 3cm×3cmの大きさのガラス布エポキシ樹脂プリント基
板の廃材から予めはんだ,電子部品を除去したものを試
料として、電気炉を用いて試料を大気雰囲気中で400
℃から500℃まで10℃間隔で30分加熱し、加熱後
の各試料を注意深く分解し、金属がガラスウールと反応
している量を測定した。結果を図5に示す。450℃ま
では反応は確認できなかったが、460℃以上では金属
とガラスウールの反応が認められ、その量は温度上昇と
ともに増加していった。
(2) Experiment 2 A sample obtained by removing solder and electronic components from waste glass cloth epoxy resin printed circuit boards having a size of 3 cm × 3 cm was used as a sample.
The sample was heated from 10 ° C. to 500 ° C. at 30 ° C. intervals for 30 minutes, each sample after heating was carefully decomposed, and the amount of metal reacted with glass wool was measured. FIG. 5 shows the results. No reaction was observed up to 450 ° C., but at 460 ° C. or higher, a reaction between the metal and glass wool was observed, and the amount increased with increasing temperature.

【0028】(3)実験3 23cm×19cmの大きさのガラス布エポキシ樹脂プリン
ト基板の廃材から予めはんだ,電子部品を除去した後、
電気炉を用い基板を大気雰囲気中で各温度で30分間加
熱した。その後、カッター式破砕機により基板に機械的
に外力を加え、その後風力選別を実施し、基板を構成す
る金属が、回収ポット5に回収された割合を求めた。そ
の結果を表1に示す。加熱温度260℃では30分間加
熱しても基板中の樹脂は殆ど変化せず、カッター式破砕
機にかけても基板は切断されたが、金属と非金属無機物
質は分離しなかった。しかしながら、加熱温度を270
℃とすると樹脂は多量のガスが発生し、大きく変化し
た。加熱後にカッター式破砕機で破砕すると、一部、銅
の細線やスルーホール部とガラスウールが分離できず
に、一部の非金属無機物質が回収ポット5に回収された
が、殆どの金属は回収ポット5に回収することができ
た。300℃,400℃では、回収ポット5に回収され
る非金属無機物質の混入率が低下した。450℃では、
回収ポット5に回収される金属量がやや低下するが90
%以上の金属回収が可能である。ここで、メッキされた
金は、450℃の加熱により一部剥離してしまったため
回収率が低下した。
(3) Experiment 3 After removing solder and electronic components from waste materials of a glass cloth epoxy resin printed circuit board having a size of 23 cm × 19 cm in advance,
The substrate was heated in an air atmosphere at each temperature for 30 minutes using an electric furnace. Thereafter, an external force was mechanically applied to the substrate by a cutter type crusher, and thereafter, wind separation was performed, and the ratio of the metal constituting the substrate collected in the collection pot 5 was determined. Table 1 shows the results. At a heating temperature of 260 ° C., the resin in the substrate hardly changed even after heating for 30 minutes, and the substrate was cut by a cutter-type crusher, but the metal and the nonmetallic inorganic substance were not separated. However, if the heating temperature is 270
At ℃, the resin generated a large amount of gas and changed greatly. When crushed by a cutter-type crusher after heating, some of the nonmetallic inorganic substances were recovered in the recovery pot 5 because the copper wool and the through-hole part could not be separated from the glass wool, but most metals were recovered. It was able to be collected in the collection pot 5. At 300 ° C. and 400 ° C., the mixing ratio of the nonmetallic inorganic substance collected in the collection pot 5 was reduced. At 450 ° C,
Although the amount of metal collected in the collection pot 5 is slightly reduced, 90
% Metal recovery is possible. Here, the plated gold was partially peeled off by heating at 450 ° C., so that the recovery rate was reduced.

【0029】加熱温度がさらに高い460℃になると、
金属のガラスウールとの反応がはじまり、その反応によ
り金属がガラス化しはじめる。そのため、回収ポット6
にも金属が混入しはじめる。結果として回収ポット5に
回収される金属量が低下する。また、回収ポット5への
非金属混入率も増加する。特に金メッキ部分は剥離して
ガラスウールと一緒になり回収ポット6で回収される量
が増加する。
When the heating temperature reaches 460 ° C., which is higher,
The reaction of the metal with the glass wool begins, and the reaction starts to vitrify the metal. Therefore, the collection pot 6
Also begins to mix metal. As a result, the amount of metal collected in the collection pot 5 decreases. In addition, the non-metal mixing ratio in the collection pot 5 also increases. In particular, the gold-plated portion is peeled off and becomes together with the glass wool, and the amount collected in the collection pot 6 increases.

【0030】[0030]

【表1】 [Table 1]

【0031】(4)実験4 次に、基板加熱時に発生する排気ガスの中和に関する実
験を行った。20cm×20cmの大きさのガラス布エポキ
シ樹脂プリント基板の廃材から予めはんだ,電子部品を
除去した後、電気炉を用い大気雰囲気中で室温から35
0℃に加熱した。この加熱過程に於いて発生したガスに
大気を加えた後、種々の温度に保持した排気ガス加熱炉
に導入,加熱し、加熱後、0.1 規定の水酸化ナトリウ
ム水溶液の入った5連のガス洗浄瓶に導入し中和した。
排気ガス加熱後のガスと中和後のガス中の臭化メチル,
臭化エチル等の臭化炭化水素、及び臭素,臭化水素を定
量分析した。その結果を表2に示す。基板加熱後の排気
ガスの主成分は炭化水素系ガスであり、基板樹脂に難燃
剤として添加されている臭素も臭化メチル,臭化エチル
という臭化炭化水素として排出される。この臭化炭化水
素はアルカリ溶液中に通しても殆ど中和されることはな
い。この臭化炭化水素は完全燃焼させて、臭素,臭化水
素とすれば、アルカリ溶液により中和可能である。しか
しながら、排気ガス加熱温度が750℃,800℃では
中和前のガス中に臭化メチル,臭化エチルが残っており
これは中和されなかった。しかしながら、排気ガス加熱
温度が850℃以上では臭化メチル,臭化エチルはほぼ
完全に臭素,臭化水素となり水酸化ナトリウム水溶液に
より中和できた。
(4) Experiment 4 Next, an experiment concerning neutralization of exhaust gas generated during substrate heating was performed. After removing solder and electronic components from the waste material of the glass cloth epoxy resin printed circuit board having a size of 20 cm × 20 cm, the temperature is reduced from room temperature to 35 ° C. in an air atmosphere using an electric furnace.
Heated to 0 ° C. After air was added to the gas generated in this heating process, the gas was introduced into an exhaust gas heating furnace maintained at various temperatures, heated, and after heating, a 5-unit containing 0.1 N aqueous sodium hydroxide solution was heated. It was introduced into a gas washing bottle and neutralized.
Methyl bromide in the gas after exhaust gas heating and the gas after neutralization,
Brominated hydrocarbons such as ethyl bromide, and bromine and hydrogen bromide were quantitatively analyzed. Table 2 shows the results. The main component of the exhaust gas after the substrate is heated is a hydrocarbon-based gas, and bromine added to the substrate resin as a flame retardant is also discharged as a brominated hydrocarbon such as methyl bromide and ethyl bromide. This brominated hydrocarbon is hardly neutralized when passed through an alkaline solution. If this brominated hydrocarbon is completely burned into bromine and hydrogen bromide, it can be neutralized with an alkaline solution. However, at exhaust gas heating temperatures of 750 ° C. and 800 ° C., methyl bromide and ethyl bromide remained in the gas before neutralization, and were not neutralized. However, when the exhaust gas heating temperature was 850 ° C. or higher, methyl bromide and ethyl bromide almost completely became bromine and hydrogen bromide, and could be neutralized with an aqueous sodium hydroxide solution.

【0032】[0032]

【表2】 [Table 2]

【0033】[0033]

【発明の効果】以上のように本発明によれば、少なくと
も金属と樹脂及び非金属無機物質で形成される廃プリン
ト基板から金属及び非金属を効率よく分離,回収できる
廃プリント基板処理方法を提供することができる。
As described above, according to the present invention, there is provided a waste printed board processing method capable of efficiently separating and recovering metal and non-metal from a waste printed board formed of at least a metal, a resin, and a nonmetallic inorganic substance. can do.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明の一実施例である廃プリント基板処理シ
ステムプロセスを示す図。
FIG. 1 is a view showing a waste printed board processing system process according to an embodiment of the present invention.

【図2】本発明の処理方法に用いる破砕機の一例を示す
概略構成図。
FIG. 2 is a schematic configuration diagram showing an example of a crusher used in the processing method of the present invention.

【図3】プリント基板の一例を示す断面図。FIG. 3 is a cross-sectional view illustrating an example of a printed circuit board.

【図4】廃プリント基板の加熱温度と重量減少の関係を
示す図。
FIG. 4 is a diagram illustrating a relationship between a heating temperature of a waste printed circuit board and weight reduction.

【図5】廃プリント基板の金属とガラスウール反応量を
示す図。
FIG. 5 is a diagram showing a reaction amount of metal and glass wool on a waste printed circuit board.

【符号の説明】[Explanation of symbols]

1…廃プリント基板、2…基板加熱装置、3…破砕機、
4…風力選別装置、5,6…回収ポット、7…排気ガ
ス、8…排気ガス加熱装置、9…中和処理装置、11…
風力選別装置、11a…ブロワー。
1 ... waste printed circuit board, 2 ... substrate heating device, 3 ... crusher,
4 ... Wind sorting device, 5, 6 ... Recovery pot, 7 ... Exhaust gas, 8 ... Exhaust gas heating device, 9 ... Neutralization treatment device, 11 ...
Wind separator, 11a ... blower.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 山下 寿生 茨城県日立市大みか町七丁目1番1号 株 式会社日立製作所日立研究所内 (72)発明者 小豆畑 茂 茨城県日立市大みか町七丁目1番1号 株 式会社日立製作所日立研究所内 ──────────────────────────────────────────────────続 き Continued on the front page (72) Inventor Toshio Yamashita 7-1-1, Omika-cho, Hitachi City, Ibaraki Prefecture Inside the Hitachi Research Laboratory, Hitachi, Ltd. No. 1 Inside the Hitachi Research Laboratory, Hitachi, Ltd.

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】樹脂と金属と非金属無機物質とからなるプ
リント基板の廃品を加熱処理したのち粉砕して金属と非
金属無機物質とを分離回収する方法において、前記プリ
ント基板の加熱処理を樹脂がガスを発生し且つ金属と非
金属無機物質とが化合物を形成しない温度で行って樹脂
からガスを発生させ、その後破砕機により破砕すること
を特徴とするプリント基板の処理方法。
1. A method of heating and treating waste printed circuit boards comprising a resin, a metal and a non-metallic inorganic substance, followed by pulverization to separate and recover the metal and the non-metallic inorganic substance. A method for treating a printed circuit board, wherein the method is performed at a temperature at which a gas is generated and the metal and the nonmetallic inorganic substance do not form a compound to generate a gas from the resin, and then crushed by a crusher.
【請求項2】請求項1に記載の方法において、前記プリ
ント基板の加熱温度を270℃以上,450℃以下とす
ることを特徴とするプリント基板の処理方法。
2. The method according to claim 1, wherein the heating temperature of the printed board is set to 270 ° C. or more and 450 ° C. or less.
【請求項3】請求項1に記載の方法において、前記破砕
時に該プリント基板の温度を250℃以下まで下げてお
くことを特徴とするプリント基板の処理方法。
3. The method according to claim 1, wherein the temperature of the printed circuit board is reduced to 250 ° C. or less during the crushing.
【請求項4】請求項1に記載の方法において、前記プリ
ント基板の加熱により樹脂から発生したガスを回収し、
該ガスを酸素含有雰囲気中で加熱して該ガスに含まれて
いる炭化水素分を分解し、その後該ガス中に残留するハ
ロゲン化合物をアルカリ水溶液により中和することを特
徴とするプリント基板の処理方法。
4. The method according to claim 1, wherein a gas generated from the resin by heating the printed circuit board is recovered,
A process for heating a gas in an oxygen-containing atmosphere to decompose hydrocarbons contained in the gas, and then neutralizing a halogen compound remaining in the gas with an aqueous alkali solution. Method.
【請求項5】請求項1に記載の方法において、前記破砕
機によりプリント基板を破砕したのち、篩い分け法,風
力選別法及び渦電流選別法の内の少なくとも1つを用い
て、金属と非金属無機物質とを分離することを特徴とす
るプリント基板の処理方法。
5. The method according to claim 1, wherein after the printed circuit board is crushed by the crusher, the metal is separated from the metal by using at least one of a sieving method, a wind screening method and an eddy current screening method. A method for treating a printed circuit board, wherein the method is for separating metal and inorganic substances.
JP24501597A 1997-09-10 1997-09-10 Treatment of printed board Pending JPH1176980A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP24501597A JPH1176980A (en) 1997-09-10 1997-09-10 Treatment of printed board

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP24501597A JPH1176980A (en) 1997-09-10 1997-09-10 Treatment of printed board

Publications (1)

Publication Number Publication Date
JPH1176980A true JPH1176980A (en) 1999-03-23

Family

ID=17127315

Family Applications (1)

Application Number Title Priority Date Filing Date
JP24501597A Pending JPH1176980A (en) 1997-09-10 1997-09-10 Treatment of printed board

Country Status (1)

Country Link
JP (1) JPH1176980A (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2005084839A1 (en) * 2004-03-08 2005-09-15 Ivan Madar Method of processing multicomponent, composite and combined materials and use of so separated components
CN102029282A (en) * 2010-09-27 2011-04-27 北京航空航天大学 Device and method for treating tail gas generated during process of extracting glass fiber from waste printed circuit board (PCB)
CN103752581A (en) * 2014-01-02 2014-04-30 浙江海洋学院 Nonmetal waste processing device
CN104511473A (en) * 2014-12-16 2015-04-15 南华大学 Waste circuit board disassembling machine
US20150322545A1 (en) * 2011-12-15 2015-11-12 Advanced Technology Materials, Inc. Apparatus and method for stripping solder metals during the recycling of waste electrical and electronic equipment
CN106179691A (en) * 2016-09-28 2016-12-07 广州市联冠机械有限公司 Waste and old circuit board resource reclaim processing system
CN110451929A (en) * 2019-08-27 2019-11-15 盐城工学院 The cement base porous filter material and preparation method thereof of waste circuit board non-metal powder preparation
WO2020175350A1 (en) * 2019-02-28 2020-09-03 三菱マテリアル株式会社 Method for treating waste electronic substrate

Cited By (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2005084839A1 (en) * 2004-03-08 2005-09-15 Ivan Madar Method of processing multicomponent, composite and combined materials and use of so separated components
US7407122B2 (en) 2004-03-08 2008-08-05 Ivan Madar Method of processing multicomponent, composite and combined materials and use of so separated components
CN102029282A (en) * 2010-09-27 2011-04-27 北京航空航天大学 Device and method for treating tail gas generated during process of extracting glass fiber from waste printed circuit board (PCB)
US20150322545A1 (en) * 2011-12-15 2015-11-12 Advanced Technology Materials, Inc. Apparatus and method for stripping solder metals during the recycling of waste electrical and electronic equipment
US9649712B2 (en) * 2011-12-15 2017-05-16 Entegris, Inc. Apparatus and method for stripping solder metals during the recycling of waste electrical and electronic equipment
US9731368B2 (en) 2011-12-15 2017-08-15 Entegris, Inc. Apparatus and method for stripping solder metals during the recycling of waste electrical and electronic equipment
CN103752581A (en) * 2014-01-02 2014-04-30 浙江海洋学院 Nonmetal waste processing device
CN104511473A (en) * 2014-12-16 2015-04-15 南华大学 Waste circuit board disassembling machine
CN106179691A (en) * 2016-09-28 2016-12-07 广州市联冠机械有限公司 Waste and old circuit board resource reclaim processing system
WO2020175350A1 (en) * 2019-02-28 2020-09-03 三菱マテリアル株式会社 Method for treating waste electronic substrate
JP2020138141A (en) * 2019-02-28 2020-09-03 三菱マテリアル株式会社 Processing method of waste electronic substrate
CN110451929A (en) * 2019-08-27 2019-11-15 盐城工学院 The cement base porous filter material and preparation method thereof of waste circuit board non-metal powder preparation

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