JPS6169929A - Device for processing and resource recovery of exhausted dry battery - Google Patents

Device for processing and resource recovery of exhausted dry battery

Info

Publication number
JPS6169929A
JPS6169929A JP59193163A JP19316384A JPS6169929A JP S6169929 A JPS6169929 A JP S6169929A JP 59193163 A JP59193163 A JP 59193163A JP 19316384 A JP19316384 A JP 19316384A JP S6169929 A JPS6169929 A JP S6169929A
Authority
JP
Japan
Prior art keywords
gas
dry battery
liquid
waste
receiver
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP59193163A
Other languages
Japanese (ja)
Other versions
JPH0422975B2 (en
Inventor
Kazumasa Kikuchi
菊地 一正
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.)
KOGAI BOSHI KIKI KK
Original Assignee
KOGAI BOSHI KIKI KK
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 KOGAI BOSHI KIKI KK filed Critical KOGAI BOSHI KIKI KK
Priority to JP59193163A priority Critical patent/JPS6169929A/en
Publication of JPS6169929A publication Critical patent/JPS6169929A/en
Publication of JPH0422975B2 publication Critical patent/JPH0422975B2/ja
Granted legal-status Critical Current

Links

Classifications

    • 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
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Landscapes

  • Manufacture And Refinement Of Metals (AREA)
  • Muffle Furnaces And Rotary Kilns (AREA)

Abstract

PURPOSE:To recover the valued resource in a dry battery without pollution by processing an exhausted dry battery with the device composed of a heat decomposition device, liquid-gas processing device and a heavy metal collecting device. CONSTITUTION:A dry battery X is smashed by a smashing device 11, thrown by a conveyer 12 into a carbonization oven 1 and heated by a heater 2. After the heat decomposing the smashed dry battery X, the residual dross, such as Mn, Zn and the like is recovered from an output port 18. Hg evaporation and the other generated gasses included in the dry battery are absorbed by a vacuum pump 20 into a heat exchanger 16 of a liquid-gas processor B and a pipe 6. The heat exchanger 16 is cooled by a cooling medium from a cooler 18 and the non-coagulated gasses which is not liquid are forced to be sent to a washing machine 21 from a receiver 17. Hg coagulated in the receiver 17 and exhausted liquid are separated by the difference of gravity into an exhausted neutralization tank 23 and Hg is stored in a storage tank 22. The non-coagulated exhausted gasses are cleaned and discharged by a water treating equipment 27 after the residual heavy metals, such as Hg, Zn, Cd are recovered by a metal recovering equipment C.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、水銀含有廃棄物としての各種の使用済乾電池
、すなわち廃乾電池処理装置に係り、殊に廃乾電池の無
公害処理及び資源の再利用目的に使用して好適な廃乾電
池の処理・資源回収uZに関するものである。
Detailed Description of the Invention [Field of Industrial Application] The present invention relates to various types of used dry batteries as mercury-containing waste, that is, waste dry battery processing equipment, and particularly to pollution-free processing of waste dry batteries and resource recycling. The present invention relates to UZ for processing and resource recovery of waste dry batteries suitable for use for various purposes.

〔従来技術〕[Prior art]

毒性金属としての水銀を含有する廃乾電池は、従来、主
として埋め立て処理方式または焼却処理方式によって処
理されてきたが、近時、n1者の方式では、水銀含有量
の多いアルカリ乾電池の出現とも関連して、埋め立てに
よる土壌、排水汚染公害問題が、後者の方式では大気汚
染公害の問題がクローズアンフ゛されてきている。
Traditionally, waste batteries containing mercury, a toxic metal, have been mainly disposed of by landfill or incineration, but in recent years, the N1 method has been disposed of due to the emergence of alkaline batteries with high mercury content. As a result, the problem of soil and wastewater pollution due to land reclamation, and the problem of air pollution due to the latter method, have been brought into closer focus.

殊に、最近では、ごみ焼却場の排出ガスおよび灰の中に
発ガン性のある猛毒化学物質である「ダイオキシン」が
検出されたり、使用済みの乾電池等の水銀含有廃棄物の
埋め立て地が水銀で汚染されていることが発見されたり
して大きな大きな問題となっている。そこで、最近、こ
の種有害廃棄物の処理に、例えば、下水汚泥の処理に使
用されている多段炉と同様な構造を有する多段式培焼炉
や回転レトルト炉等が使用されるようになった。
In particular, recently, ``dioxin'', a highly toxic carcinogenic chemical, has been detected in the exhaust gas and ash of garbage incinerators, and mercury-containing waste such as used dry batteries is being disposed of in landfills. It has become a major problem as it has been discovered that it has been contaminated. Therefore, recently, for example, multi-stage incubation furnaces and rotary retort furnaces, which have a similar structure to the multi-stage furnaces used to treat sewage sludge, have been used to treat this type of hazardous waste. .

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

前述した廃棄物焼却処理方式で:丈大気汚染公害の問題
を解決することが出来ないばかりでなく、資源を育効に
再利用することも困難であり、また、前述した多段式培
焼炉や回転レトルト炉等にあっては、通をの焼却炉と比
べると公害発生防止に役立つことはこれを否定し得ない
が、なお、不充分であるばかりでなく、資源の再生ない
し再利用の上でも十分な機能を発揮し得ないほか、構造
が複雑で製造並びに運転も容易でなく、処理コストも高
価とならざるを得ないといった難点がある。
The above-mentioned waste incineration method not only cannot solve the problem of air pollution, but also makes it difficult to reuse resources for cultivation purposes. Although it cannot be denied that rotary retort furnaces and the like are more useful in preventing pollution than conventional incinerators, they are not only insufficient, but also effective in terms of recycling or reusing resources. However, they do not have sufficient functionality, have complex structures, are difficult to manufacture and operate, and have high processing costs.

本発明は、これらの問題点を解決しようとするものであ
る。
The present invention seeks to solve these problems.

〔発明の目的〕[Purpose of the invention]

従って、本発明の王たる目的は、各種廃乾電池の無公害
処理及び資源の再利用目的に使用して好適であり、構造
が藺草で製造および運転も容易であり、しかも処理コス
トを比較的低く抑えることができるようにした廃乾電池
の処理資源回収装置を提供しようとするものである。
Therefore, the primary object of the present invention is to provide a battery that is suitable for non-polluting treatment of various types of waste dry batteries and for the purpose of reusing resources, has a strawberry structure, is easy to manufacture and operate, and has a relatively low processing cost. The purpose of the present invention is to provide a waste dry battery processing resource recovery device that can reduce the amount of waste.

〔発明の構成〕[Structure of the invention]

本発明に係る廃乾電池の処理・資源回収装置は、廃電池
を熱分解させ、ガスを発生させる密閉構造の乾留釜を、
その加熱炉の内部に垂下突設してなる熱分解装置と、前
記乾留釜にガス取り出し管を介して気密に連結されたガ
ス冷却用熱交換器およびこの熱交換器に気密に連結され
ていて、この熱交換器による前記乾留釜からの供給ガス
の冷却によって分離された凝結液と不凝結ガスとを収容
する密閉構造のレシーバ−からなる液・ガス処理装置と
からなり、前記乾留釜には、開閉自在な廃乾電池投入口
と廃乾電池の熱分解後に該乾留釜の底部に残留する残渣
等を外部に取り出すための開閉自在な残渣取り出し口を
設け、前記液・ガス処理装置のレシーバ−には、前記乾
留釜に発生したガスを前記ガス取り出し管を介して前記
熱交換器に強制導入し、かつ該熱交換器内の不凝結ガス
を該レシーバーに強制導入すると共にこれに連結された
ガス洗浄機に強制送入するための真空ポンプを連結し、
また前記レシーバーには、その内部に集められた凝結液
を水銀と廃液とに分離して採取するための装置が装着な
いし連設されていることを特徴とするものである。
The waste dry battery processing/resource recovery device according to the present invention includes a carbonization tank with a closed structure that thermally decomposes waste batteries and generates gas.
A pyrolysis device hanging down and protruding inside the heating furnace, a gas cooling heat exchanger airtightly connected to the carbonization kettle via a gas extraction pipe, and an airtightly connected to the heat exchanger. , a liquid/gas processing device consisting of a receiver with a sealed structure for accommodating condensate liquid and non-condensable gas separated by cooling the gas supplied from the carbonization vessel by the heat exchanger; A receiver of the liquid/gas processing apparatus is provided with a waste battery inlet that can be opened and closed, and a residue outlet that can be opened and closed to take out the residue remaining at the bottom of the carbonization tank after thermal decomposition of the waste dry battery. The gas generated in the carbonization reactor is forcibly introduced into the heat exchanger via the gas take-off pipe, and the non-condensable gas in the heat exchanger is forcibly introduced into the receiver, and the gas connected thereto is forcibly introduced into the heat exchanger. Connect a vacuum pump to forcefully feed the washing machine,
Further, the receiver is characterized in that a device for separating and collecting the condensed liquid collected inside the receiver into mercury and waste liquid is attached to or connected to the receiver.

〔実施例〕〔Example〕

以下、本発明につきその実施例を示した添付図面を参照
して詳細に説明する。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Hereinafter, the present invention will be described in detail with reference to the accompanying drawings showing embodiments thereof.

第1図において、Aは廃乾電池Xを執分解させ、各種の
成分を含むガスを発生させる密閉構造の乾留釜1を、そ
の加熱炉2の内部に垂下突設してなる熱分Phi置であ
り、乾留釜1ば加熱炉2の上部炉壁2Aを貫通して上方
に若干突出しており、その突出部分に廃乾電池投入口I
Aが設けられ、該投入口IAは蝶着された開閉蓋IA’
によって気密に閉塞されるようになっている。
In Fig. 1, A is a heat sink Phi, which is made up of a heating furnace 2 in which a carbonization tank 1 with a closed structure for decomposing a waste dry battery X and generating gas containing various components hangs down inside the heating furnace 2. The carbonization pot 1 penetrates the upper furnace wall 2A of the heating furnace 2 and protrudes slightly upward, and the waste dry battery inlet I is located in the protruding part.
A is provided, and the input port IA is connected to a hinged opening/closing lid IA'.
It is sealed airtight.

前記乾留釜1には、さらに、その下部適所に形成された
開口から前記加熱炉2の側部炉壁2Bを貫通して外方に
突出する中空筒体からなる残渣取り出し口IBが設けら
れており、廃乾電池Xの熱分解後に乾留釜1の底部に残
留する残i’!(例えば、マンガン、亜鉛等)を、この
残渣取り出し口IBから外部に取り出すことができるよ
うになっている。この残渣取り出し口IBも蝶着されノ
こ開閉蓋IB’によって気密に閉塞されるようになって
いる。…■記加勢炉2の側部炉壁2Bの下部適所には、
その燃焼室3内において乾留釜lを外部から加熱するた
めの、重油またはガスを燃料とするガンタイプのバーナ
ー4が装備されており、また、該加熱炉2の上部炉壁2
A0)a所には、燃焼室3に連通ずる煙突5が突設され
ている。
The carbonization vessel 1 is further provided with a residue outlet IB made of a hollow cylindrical body that protrudes outward through the side furnace wall 2B of the heating furnace 2 from an opening formed at a proper position in the lower part thereof. After the thermal decomposition of the waste battery X, the residue i'! (For example, manganese, zinc, etc.) can be taken out from this residue take-out port IB. This residue outlet IB is also hinged and is airtightly closed by the saw opening/closing lid IB'. ... ■ At the appropriate lower part of the side furnace wall 2B of the boosting furnace 2,
The combustion chamber 3 is equipped with a gun-type burner 4 that uses heavy oil or gas as fuel to heat the carbonization tank 1 from the outside.
A0) At location a, a chimney 5 that communicates with the combustion chamber 3 is protruded.

前記した乾留釜には、その上方突出部分の適所に安全弁
、温度センサー及び廃乾電池の熱分解によって該乾留釜
l内に発生したガスをその冷却工程に案内給送するため
のガス取り出し管6が連結されている。しかして、7は
撹拌装置であり、これは、乾留釜lの上方突出部分の中
央部に突設された回転駆動部7Aと、この回転駆動部7
Aから乾留釜l内に垂下する回転ノヤフト7Bと、この
回転ンヤフト7Bの外周に固着された螺糸状の攪拌部材
7Cとからなっている。
The above-mentioned carbonization tank has a safety valve, a temperature sensor, and a gas extraction pipe 6 at appropriate positions on the upwardly projecting part for guiding and feeding the gas generated in the carbonization tank 1 by thermal decomposition of waste dry batteries to the cooling process. connected. 7 is a stirring device, which includes a rotary drive section 7A protruding from the center of the upwardly projecting portion of the carbonization vessel l;
It consists of a rotating shaft 7B that hangs down from A into the carbonization vessel l, and a spiral stirring member 7C fixed to the outer periphery of this rotating shaft 7B.

前記廃乾電池投入口IAの近傍には、ロータリーパルプ
8を有するホンパー9が配置され、廃乾電池Xは、選別
篩装置10によって篩い分けられ、破砕ないし切削手段
11によって破砕ないし破損された後、搬入コンベヤ1
2及び前記ホンパー9を介して前記投入口LAに投入さ
れるようになっている。また、前記残渣取り出し口IB
の近傍には、残渣ピット13に連なる搬出コンベヤ14
の搬入端に設けられた残渣搬出ホッパー15が配置され
ている。
A homper 9 having a rotary pulp 8 is disposed near the waste dry battery input port IA, and the waste dry batteries conveyor 1
2 and the pumper 9 to be input into the input port LA. In addition, the residue outlet IB
Nearby, there is an unloading conveyor 14 connected to the residue pit 13.
A residue carry-out hopper 15 is disposed at the carry-in end.

Bは前記乾留釜1に前記ガス取り出し管6を介して気密
に連結されたガス冷却用熱交換器16とこの熱交換器1
6に気密に連結されていて、該熱交換器による前記乾留
釜1からの供給ガスの冷却によって分離された凝結液と
不凝結ガスとを収容する密閉構造の共通のレシーバ−I
7とからなる液・ガス処理Viaであり、この処理袋五
Bによって廃乾電池に含まれている水銀その他の物質が
液体ないしガスの形態において再生ないし処理可能とな
るものである。
B denotes a gas cooling heat exchanger 16 airtightly connected to the carbonization tank 1 via the gas extraction pipe 6, and this heat exchanger 1.
A common receiver-I of a sealed structure, which is airtightly connected to the carbonization tank 1 and contains the condensed liquid and the non-condensed gas separated by cooling the feed gas from the carbonization tank 1 by the heat exchanger.
This processing bag 5B allows mercury and other substances contained in waste dry batteries to be regenerated or processed in the form of liquid or gas.

前記ガス冷却用熱交換器I6には、急速冷却8118が
連結されており、また、前記レシーバ−17には、吸込
管19を介して真空ポンプ20が連結されていて、この
真空ポンプ20の吸引力により乾留釜l内に発生した混
合ガスをガス取り出し管6を介してガス冷却用熱交換器
16に強制導入し、かつ該熱交換器内の不凝結ガス、す
なわち、核熱交換器を通過中に液化しなかったガスを該
レシーバー17に強制導入すると共に、ゼットサイクロ
ンからなるガス洗浄機21に強制送入するようになって
いる。しかして、この真空ポンプ20は、乾留釜1内の
ガス生成量の増減に応じて吸込圧力を調節し得る構造に
なっており、その調節は必要に応して手動制御手段の操
作または自動制御装置く図示してない)の運転によって
行うことができるようになっている。
A rapid cooling unit 8118 is connected to the gas cooling heat exchanger I6, and a vacuum pump 20 is connected to the receiver 17 via a suction pipe 19. The mixed gas generated in the carbonization tank 1 by force is forcibly introduced into the gas cooling heat exchanger 16 through the gas extraction pipe 6, and the non-condensable gas in the heat exchanger, that is, passes through the nuclear heat exchanger. The gas that has not been liquefied inside is forcibly introduced into the receiver 17, and is also forcibly fed into a gas washer 21 consisting of a jet cyclone. Therefore, this vacuum pump 20 has a structure in which the suction pressure can be adjusted according to an increase or decrease in the amount of gas produced in the carbonization vessel 1, and the adjustment can be performed by operating a manual control means or by automatic control as necessary. This can be done by operating a device (not shown).

前記レンーハーI7の下部近傍には、水銀と廃液とを各
別に貯留する水銀貯槽22と廃液中和調整槽23とがそ
れぞれ配設されている。すなわち、図示の例にあっては
、レシーバー17の倒円錐状部17’の直下には、その
最下端部に連結された水銀排出管22′を介して該レシ
ーバ−に連通ずる水銀貯槽22が、また、該倒円錐状部
17′の下部側方には、その側壁部位に連結された廃t
L排出管23′を介して該レシーバーに連通ずる廃液中
和調整槽23がそれぞれ設置されており、レシーバ−1
7内ニ?W tった水銀と廃液とは、両者の比重差によ
って一応分離され、水銀貯槽22と廃液中和ill整槽
23とにそれぞれ集液されるようになっている。
A mercury storage tank 22 and a waste liquid neutralization adjustment tank 23, which separately store mercury and waste liquid, are provided near the bottom of the Lenher I7. That is, in the illustrated example, a mercury storage tank 22 is located directly below the inverted conical portion 17' of the receiver 17 and communicates with the receiver via a mercury discharge pipe 22' connected to the lowermost end thereof. Further, on the lower side of the inverted conical portion 17', there is a waste t connected to the side wall portion thereof.
A waste liquid neutralization adjustment tank 23 is installed, which communicates with the receiver via an L discharge pipe 23'.
7 inside? Wt mercury and waste liquid are temporarily separated due to the difference in specific gravity between the two, and are collected in a mercury storage tank 22 and a waste liquid neutralization tank 23, respectively.

前記廃液中和調整槽23は、多かれ少なかれなお廃液中
に混入してεする各種の物質、例えば、水銀またはその
化合物、マンガン、亜鉛、カドミウム、またはその化合
物、鉛またはその化合物等を吸着して捕集するための重
金属捕集装置Cに連結されており、該調整槽23内の廃
液は、PH1il整後、ポンプ24で該捕集装置Cに給
送されるようになっている。
The waste liquid neutralization adjustment tank 23 adsorbs various substances that are more or less mixed into the waste liquid, such as mercury or its compounds, manganese, zinc, cadmium or its compounds, lead or its compounds, etc. It is connected to a heavy metal collector C for collection, and the waste liquid in the adjustment tank 23 is fed to the collector C by a pump 24 after adjusting the pH level.

前記金属捕集装置Cは、水銀またはその化合物を捕集す
る第1吸着塔25と、この第1吸着塔25の下流側に配
設されたマンガン、亜鉛、カドミウム等水銀以外の重金
属をl’ii集する第2吸着塔26とからなっており、
これら重金属超は、例えば、キレート樹脂吸着剤のよう
な吸着剤によって捕捉されりようになっている。しかし
て、この重金属捕集装置Cによって処理された廃液は、
第2吸着塔26の下流側に配設された三次水処理装置2
7に送られ、そこで浄化された後、排水溝に放水される
The metal collection device C includes a first adsorption tower 25 that collects mercury or its compounds, and a first adsorption tower 25 that collects heavy metals other than mercury, such as manganese, zinc, and cadmium, and is disposed downstream of the first adsorption tower 25. It consists of a second adsorption tower 26 that collects
These heavy metals can be captured by adsorbents such as chelating resin adsorbents. Therefore, the waste liquid treated by this heavy metal collection device C is
Tertiary water treatment device 2 installed downstream of the second adsorption tower 26
7, where it is purified and then discharged into drains.

前記したガス洗浄機21には、図示されているように、
廃液中和調整槽23からPH副調整れた廃液が供給され
るようになっていると共に、排ガスの除湿及び脱臭のた
めの装置りが連結されている。
As illustrated in the above-mentioned gas washer 21,
A waste liquid whose pH has been sub-adjusted is supplied from the waste liquid neutralization adjustment tank 23, and a device for dehumidifying and deodorizing exhaust gas is connected thereto.

〔発明の効果〕〔Effect of the invention〕

本発明に係る廃乾電池の処理・資源回収装置は叙上の如
き構成になり、殊にその構成要素である乾留釜、ガス取
り出し管、ガス冷却用熱交換器及びレシーバ−はそれぞ
れ外気から遮断され、互いに気密に連結された密閉構造
となっているうえ、不凝結ガスは洗浄機によって浄化さ
れた後、大気中に放出されるようになっているので、煤
塵を含んだ有害ガスが外部に漏出して公害を惹起すする
おそれがないし、また、廃乾電池は、乾留処理により水
銀及び固形状重金属の形態において再生ないし再利用す
ることが可能となるから、資源の回収に資することがで
き、しかも構造が節承で大幅に小型化することができる
と共に、製造・運転・保守も容易であるがら、実用性の
みならず普及性にも富んでおり、また、処理コストも低
く抑えることができる等々幾多の実益を発揮することが
できるものである。
The waste dry battery processing/resource recovery apparatus according to the present invention has the above-mentioned configuration, and in particular, its components, such as the carbonization tank, gas extraction pipe, gas cooling heat exchanger, and receiver, are each isolated from the outside air. , have a sealed structure that is airtightly connected to each other, and the non-condensable gas is purified by a cleaning machine before being released into the atmosphere, so noxious gases containing soot and dust leak outside. Furthermore, waste dry batteries can be recycled or reused in the form of mercury and solid heavy metals through carbonization treatment, which contributes to the recovery of resources. The structure is jointed and can be significantly miniaturized, and while it is easy to manufacture, operate, and maintain, it is not only practical but also popular, and processing costs can be kept low. It can bring many practical benefits.

殊に、上記実施例にあっては、廃乾電池は、破砕ないし
切削破損された状態で乾留釜に投入されたのち撹拌装置
によって適宜撹拌されつつ乾留処理されるので、熱分解
が促進されるという利点があり、また、廃液は、廃液中
和調整槽においてPH副調整れた後、重金属捕集装置に
よって含有する有害物質を除去され、さらに、三次水処
理装置によって浄化されたうえで排水溝に放水されるよ
うになっているので、排水に伴う公害もほぼ完全に防止
することができ、さらにまた、排ガスはガス洗浄機によ
って洗浄さたた後、脱臭装置を経由して大気中に放出さ
れるので、煤塵が放出されないばかりでなく、悪臭の放
散をも効果的に防止することができるものである。
In particular, in the above embodiment, the waste dry battery is crushed or cut and damaged and then put into the carbonization tank and then subjected to carbonization treatment while being appropriately stirred by the stirring device, so that thermal decomposition is promoted. In addition, after the waste liquid undergoes pH sub-adjustment in the waste liquid neutralization adjustment tank, harmful substances contained in the waste liquid are removed by a heavy metal collection device, and further purified by a tertiary water treatment device before being sent to the drain. Since the system is designed to spray water, pollution caused by drainage can be almost completely prevented.Furthermore, after the exhaust gas is cleaned by a gas washer, it is released into the atmosphere via a deodorizing device. Therefore, not only soot and dust are not released, but also the emission of bad odors can be effectively prevented.

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

第1図は本発明に係る廃乾電池の処理・資源回収装置の
一実施例の全体側面略図、第2図は第1図に示した実施
例のフローチャートである。 図面において、Xは廃乾電池、Aは熱分解装置、lは乾
留釜、IAは廃乾電池投入口、IBは残渣取り出し口、
2は加熱炉、3は燃焼室、6はガス取り出し管、7は撹
拌装置、Bは液・ガス処理装置、16はガス冷却用熱交
換器、17はレシーバ−120は真空ポンプ、21はガ
ス洗浄機、22は水銀貯槽、23は廃液中和調整槽、C
は重金属捕集装置、25は第1吸着塔、26は第2吸着
塔、27は三次水処理袋ffi、 Dは除湿及び脱臭装
置である。
FIG. 1 is a schematic side view of an entire embodiment of a waste dry battery processing/resource recovery apparatus according to the present invention, and FIG. 2 is a flowchart of the embodiment shown in FIG. In the drawing, X is a waste battery, A is a pyrolysis device, l is a carbonization tank, IA is a waste battery inlet, IB is a residue outlet,
2 is a heating furnace, 3 is a combustion chamber, 6 is a gas extraction pipe, 7 is a stirring device, B is a liquid/gas treatment device, 16 is a gas cooling heat exchanger, 17 is a receiver, 120 is a vacuum pump, 21 is a gas Washing machine, 22 is a mercury storage tank, 23 is a waste liquid neutralization adjustment tank, C
25 is a heavy metal trapping device, 25 is a first adsorption tower, 26 is a second adsorption tower, 27 is a tertiary water treatment bag ffi, and D is a dehumidification and deodorization device.

Claims (6)

【特許請求の範囲】[Claims] (1)廃乾電池を熱分解させ、ガスを発生させる密閉構
造の乾留釜を、その加熱炉の内部に垂下突設してなる熱
分解装置と、前記乾留釜にガス取り出し管を介して気密
に連結されたガス冷却用熱交換器及びこの熱交換器に気
密に連結されていて、この熱交換器による前記乾留釜か
らの供給ガスの冷却によって分離された凝結液と不凝結
ガスとを収容する密閉構造のレシーバーからなる液・ガ
ス処理装置とからなり、前記乾留釜には、開閉自在な廃
乾電池投入口と廃乾電池の熱分解後に該乾留釜の底部に
残留する残渣等を外部に取り出すための開閉自在な残渣
取り出し口を設け、前記液・ガス処理装置のレシーバー
には、前記乾留釜に発生かたガスを前記ガス取り出し管
を介して前記熱交換器に強制導入し、かつ該熱交換器内
の不凝結ガスを該レシーバーに強制導入すると共にこれ
に連結されたガス洗浄機に強制送入するための真空ポン
プを連結し、また、前記レシーバーには、その内部に集
めらた凝結液を水銀と廃液とに分離して採取するための
装置が装着ないし連設されていることを特徴とする廃乾
電池の処理・資源回収装置。
(1) A pyrolysis device consisting of a carbonization tank with a closed structure that pyrolyzes waste dry batteries and generates gas, which is installed hanging down inside the heating furnace, and an airtight connection to the carbonization tank via a gas extraction pipe. A connected gas cooling heat exchanger and an airtightly connected gas cooling heat exchanger for storing condensed liquid and non-condensed gas separated by cooling of the gas supplied from the carbonization tank by this heat exchanger. It consists of a liquid/gas processing device consisting of a receiver with a sealed structure, and the carbonization kettle has a waste dry cell inlet that can be opened and closed, and a means for taking out the residue etc. remaining at the bottom of the carbonization kettle after thermal decomposition of the waste dry batteries to the outside. The receiver of the liquid/gas processing apparatus is provided with a residue outlet that can be opened and closed, and the receiver of the liquid/gas processing apparatus is provided with a gas that is forcibly introduced into the heat exchanger via the gas outlet pipe, and a A vacuum pump is connected to forcibly introduce the non-condensable gas in the container into the receiver and forcefully feed it to the gas washer connected to the receiver, and the receiver is connected to A waste dry battery processing/resource recovery device, characterized in that a device for separating and collecting mercury and waste liquid is attached or connected to the device.
(2)前記乾留釜は、前記加熱炉の上方に若干突出し、
その突出部分に前記廃乾電池投入口が設けられているこ
とを特徴とする特許請求の範囲第1項に記載の廃乾電池
の処理・資源回収装置。
(2) the carbonization pot slightly protrudes above the heating furnace;
The waste dry battery processing/resource recovery device according to claim 1, wherein the waste dry battery inlet is provided in the protruding portion.
(3)前記残渣取り出し口は、前記乾留釜の下部適所に
形成された開口から前記加熱炉の炉壁を貫通して外方に
突出する中空筒体からなっていることを特徴とする特許
請求の範囲第1項または第2項に記載の廃乾電池の処理
・資源回収装置。
(3) A patent claim characterized in that the residue outlet is a hollow cylindrical body that protrudes outward from an opening formed at a proper position in the lower part of the carbonization vessel and passes through the furnace wall of the heating furnace. A waste dry battery processing/resource recovery device according to item 1 or 2.
(4)前記レシーバーの下部近傍には、水銀と廃液とを
各別に貯留する水銀貯槽と廃液中和調整槽とがそれぞれ
配設されていることを特徴とする特許請求の範囲第1項
、第2項または第3項に記載の廃乾電池の処理・資源回
収装置。
(4) A mercury storage tank for separately storing mercury and waste liquid and a waste liquid neutralization adjustment tank are respectively disposed near the lower part of the receiver. The waste dry battery processing/resource recovery device according to item 2 or 3.
(5)廃液中和調整槽は、廃液中に含まれている水銀そ
の他の重金属を吸着して捕集するための重金属捕集装置
に連結されていることを特徴とする特許請求の範囲第4
項に記載の廃乾電池の処理・資源回収装置。
(5) The waste liquid neutralization adjustment tank is connected to a heavy metal collection device for adsorbing and collecting mercury and other heavy metals contained in the waste liquid.
The waste dry battery processing/resource recovery device described in 2.
(6)重金属捕集装置は、水銀を捕集する第1吸着塔と
、亜鉛、カドミウム等のような水銀以外の重金属を捕集
する第2吸着塔とからなり、該第2吸着塔は、排水溝に
つらなる三次水処理装置に連結されていることを特徴と
する特許請求の範囲第5項に記載の廃乾電池の処理・資
源回収装置。
(6) The heavy metal collection device consists of a first adsorption tower that collects mercury and a second adsorption tower that collects heavy metals other than mercury such as zinc, cadmium, etc., and the second adsorption tower: The waste dry battery processing/resource recovery device according to claim 5, wherein the device is connected to a tertiary water treatment device connected to a drainage ditch.
JP59193163A 1984-09-14 1984-09-14 Device for processing and resource recovery of exhausted dry battery Granted JPS6169929A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59193163A JPS6169929A (en) 1984-09-14 1984-09-14 Device for processing and resource recovery of exhausted dry battery

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59193163A JPS6169929A (en) 1984-09-14 1984-09-14 Device for processing and resource recovery of exhausted dry battery

Publications (2)

Publication Number Publication Date
JPS6169929A true JPS6169929A (en) 1986-04-10
JPH0422975B2 JPH0422975B2 (en) 1992-04-21

Family

ID=16303334

Family Applications (1)

Application Number Title Priority Date Filing Date
JP59193163A Granted JPS6169929A (en) 1984-09-14 1984-09-14 Device for processing and resource recovery of exhausted dry battery

Country Status (1)

Country Link
JP (1) JPS6169929A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63197592A (en) * 1986-12-12 1988-08-16 レシテック ソシエテ アノニム Method of reutilizing battery, integrated circuit substrate and electronic part
NL1004566C2 (en) * 1996-11-19 1998-05-20 Begemann Holding Bv Apparatus and method for removing mercury from waste materials by vacuum distillation.

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63197592A (en) * 1986-12-12 1988-08-16 レシテック ソシエテ アノニム Method of reutilizing battery, integrated circuit substrate and electronic part
NL1004566C2 (en) * 1996-11-19 1998-05-20 Begemann Holding Bv Apparatus and method for removing mercury from waste materials by vacuum distillation.
WO1998022628A1 (en) * 1996-11-19 1998-05-28 Begemann Holding B.V. Installation and method for removing mercury from waste materials by vacuum distillation

Also Published As

Publication number Publication date
JPH0422975B2 (en) 1992-04-21

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