JPS61263687A - Apparatus for treating dry cell containing mercury - Google Patents
Apparatus for treating dry cell containing mercuryInfo
- Publication number
- JPS61263687A JPS61263687A JP60106249A JP10624985A JPS61263687A JP S61263687 A JPS61263687 A JP S61263687A JP 60106249 A JP60106249 A JP 60106249A JP 10624985 A JP10624985 A JP 10624985A JP S61263687 A JPS61263687 A JP S61263687A
- Authority
- JP
- Japan
- Prior art keywords
- mercury
- waste gas
- tower
- spray tower
- furnace
- 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
Links
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 title claims abstract description 75
- 229910052753 mercury Inorganic materials 0.000 title claims abstract description 68
- 239000002912 waste gas Substances 0.000 claims abstract description 26
- 239000007921 spray Substances 0.000 claims abstract description 20
- 238000011084 recovery Methods 0.000 claims abstract description 11
- 239000007789 gas Substances 0.000 claims abstract description 9
- 238000010438 heat treatment Methods 0.000 claims abstract description 9
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 8
- 239000000428 dust Substances 0.000 claims abstract description 7
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims abstract description 6
- 239000000741 silica gel Substances 0.000 claims abstract description 6
- 229910002027 silica gel Inorganic materials 0.000 claims abstract description 6
- 229930195733 hydrocarbon Natural products 0.000 claims abstract description 4
- 150000002430 hydrocarbons Chemical class 0.000 claims abstract description 4
- 239000012535 impurity Substances 0.000 claims abstract description 4
- 239000000463 material Substances 0.000 claims abstract description 4
- 238000001816 cooling Methods 0.000 claims abstract 2
- 238000012545 processing Methods 0.000 claims description 19
- 238000003763 carbonization Methods 0.000 claims description 16
- 239000000872 buffer Substances 0.000 claims description 5
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 5
- 238000009835 boiling Methods 0.000 claims description 4
- 238000000197 pyrolysis Methods 0.000 abstract 1
- 238000000034 method Methods 0.000 description 8
- 238000002485 combustion reaction Methods 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 4
- 229910052979 sodium sulfide Inorganic materials 0.000 description 3
- GRVFOGOEDUUMBP-UHFFFAOYSA-N sodium sulfide (anhydrous) Chemical compound [Na+].[Na+].[S-2] GRVFOGOEDUUMBP-UHFFFAOYSA-N 0.000 description 3
- 239000002699 waste material Substances 0.000 description 3
- 229910000474 mercury oxide Inorganic materials 0.000 description 2
- UKWHYYKOEPRTIC-UHFFFAOYSA-N mercury(ii) oxide Chemical compound [Hg]=O UKWHYYKOEPRTIC-UHFFFAOYSA-N 0.000 description 2
- 239000000243 solution Substances 0.000 description 2
- 241000894006 Bacteria Species 0.000 description 1
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 description 1
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 238000013459 approach Methods 0.000 description 1
- 239000007853 buffer solution Substances 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000007667 floating Methods 0.000 description 1
- 239000004615 ingredient Substances 0.000 description 1
- 229910052748 manganese Inorganic materials 0.000 description 1
- 239000011572 manganese Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 238000002844 melting Methods 0.000 description 1
- 230000008018 melting Effects 0.000 description 1
- 150000002730 mercury Chemical class 0.000 description 1
- 238000012856 packing Methods 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 238000010298 pulverizing process Methods 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
- 229910052709 silver Inorganic materials 0.000 description 1
- 239000004332 silver Substances 0.000 description 1
- QXKXDIKCIPXUPL-UHFFFAOYSA-N sulfanylidenemercury Chemical compound [Hg]=S QXKXDIKCIPXUPL-UHFFFAOYSA-N 0.000 description 1
- 238000005979 thermal decomposition reaction Methods 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 239000002918 waste heat Substances 0.000 description 1
- 239000011701 zinc Substances 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
Landscapes
- Processing Of Solid Wastes (AREA)
Abstract
Description
【発明の詳細な説明】
〔産業上の利用分野〕
この発明は、水銀含有乾電池の処理装置に関するもので
ある。DETAILED DESCRIPTION OF THE INVENTION [Industrial Field of Application] The present invention relates to a processing device for mercury-containing dry batteries.
ボタン型水銀電池や筒形アルカリ・マンガン電池には1
個当、90.2〜1.7グラムの水銀が含まれておシ、
現在わが国では、年間消費量約20億個の廃乾電池の水
銀総量は50)ンを超えていて、使用済水銀含有乾電池
は新たな公害発生源として注目されつつあり、国および
地方自治体はその回収・処理に苦慮している。1 for button type mercury batteries and cylindrical alkaline manganese batteries.
Each piece contains 90.2 to 1.7 grams of mercury.
Currently, in Japan, the total amount of mercury in the approximately 2 billion waste dry batteries that are consumed annually exceeds 50) tons, and used mercury-containing dry batteries are attracting attention as a new source of pollution, and the national and local governments are collecting them.・I am having trouble processing it.
このような使用済水銀含有乾電池の回収方法としては、
消費量が、新しく電池を購入する際に、使用済電池を販
売店に持ち込む、電池メーカーが水銀電池取扱い店に水
銀含有乾電池専用の回収箱を設置するなどの分別回収対
策がなされ始めておシ、一方、分別回収された使用済乾
電池の処理方法としては、■ドラム缶に入れて倉庫等に
保管する;■コンクリート詰めする;■一般廃棄物と共
に埋立地等に地中投棄する;■一般廃棄物と共に焼却す
る;などの処理が行なわれている。The method for collecting used mercury-containing dry batteries is as follows:
The amount of mercury-containing batteries has been reduced as more and more measures are being taken to separate and collect them, such as bringing used batteries to stores when purchasing new batteries, and battery manufacturers installing collection boxes specifically for mercury-containing batteries at stores that sell mercury batteries. On the other hand, methods for disposing of used batteries that have been collected separately include: ■ Storing them in drums in a warehouse, etc.; ■ Packing them in concrete; ■ Dumping them underground in a landfill, etc. together with general waste; ■ With general waste. Processes such as incineration are being carried out.
しかしながら、上記のような、従来の使用済水銀含有乾
電池の処理技術では、たとえば■、■のやシ方によって
は日々増大する回収量をこなし切れず、また■の方法で
は地下水汚染の危険性があシ、■の方法では大気汚染の
恐れがあって、いずれも抜本的な使用済水銀含有電池の
処理対策というには程遠い0従って、現状のままでは環
境にばらまかれる水銀量は確実に増え続け、このように
多量の水、銀がバクテリアや熱によって猛毒の有機水銀
に変化することや、他の汚染物質との複合汚染の危険性
をも合わせ考える時、より抜本的な使用済水銀含有乾電
池の処理技術の開発が要望されていることは明白である
。さらに、上記のような従来の処理技術では、電池中の
水銀は全く回収されることなく投棄されていたが、比較
的高価な水銀を再生利用な形で回収することのできる処
理技術の確立が資源の有効利用の面からも望まれている
。However, with the conventional processing technology for used mercury-containing dry batteries as described above, depending on the method of (2) and (2), for example, the amount of collection increases day by day. There is a risk of air pollution with the method (2) and (2), and they are far from being a drastic treatment measure for used mercury-containing batteries. Therefore, if the current situation continues, the amount of mercury released into the environment will definitely continue to increase. When considering the possibility that large amounts of water and silver can be transformed into highly toxic organic mercury by bacteria and heat, and the risk of complex contamination with other pollutants, we need to take a more drastic approach to treating used mercury-containing dry batteries. It is clear that there is a need for the development of processing technology. Furthermore, with the conventional processing techniques mentioned above, the mercury in batteries was dumped without being recovered at all, but it is now possible to establish a processing technology that can recover relatively expensive mercury in a recyclable form. This is also desired from the standpoint of effective use of resources.
この発明は上記の事情に鑑みなされたもので、その目的
は、水銀の回収および再生利用が可能で水銀含有乾電池
を高速処理することのできる水銀含有乾電池の処理装置
を提供することにある。This invention was made in view of the above circumstances, and its purpose is to provide a processing device for mercury-containing dry batteries that is capable of recovering and recycling mercury and that can process mercury-containing dry batteries at high speed.
上記の問題点を解決するために、この発明は、水銀含有
乾電池を粉砕する粉砕機と、この粉砕機により粉砕され
た粉砕物を水銀の沸点より高い温度で加熱する外熱式乾
留炉と、この乾留炉から排出される乾留ガスを冷却し、
水銀蒸気を凝縮させるコンデンサと、凝縮された水銀を
回収する水銀回収槽と、この水銀回収槽から排出される
廃ガス中の微量水銀および浮遊粉塵を除去するスプレー
塔と、このスプレー塔からの廃ガスより微量の不純物な
らびに水分を分離する緩衛タンク、スプレー塔で除去で
きなかったさらに微量の残留水銀を吸着除去する活性炭
と廃ガス中の炭火水素類を吸着除去するシリカゲルを充
填した充填塔、およびこの充填塔を通過した廃ガスを大
気中に放出する廃ガス煙突よりなる最終処理部と、で構
成された水銀含有乾電池の処理装置を提供するものであ
る。In order to solve the above problems, the present invention provides a pulverizer for pulverizing mercury-containing dry batteries, an external heat carbonization furnace for heating the pulverized product pulverized by the pulverizer at a temperature higher than the boiling point of mercury, The carbonization gas discharged from this carbonization furnace is cooled,
A condenser that condenses mercury vapor, a mercury recovery tank that recovers the condensed mercury, a spray tower that removes trace amounts of mercury and suspended dust from the waste gas discharged from the mercury recovery tank, and a spray tower that removes the waste gas from the spray tower. A guard tank that separates minute amounts of impurities and moisture from gas, a packed tower filled with activated carbon that adsorbs and removes trace amounts of residual mercury that could not be removed by the spray tower, and silica gel that adsorbs and removes hydrocarbons in waste gas. The present invention provides a treatment device for a mercury-containing dry battery, comprising: and a final treatment section comprising a waste gas chimney that discharges the waste gas that has passed through the packed tower into the atmosphere.
上記の構成を有するこの発明の水銀含有乾電池の処理装
置において、回収された使用済の水銀含有乾電池は粉砕
機によって適度に粉砕され、その粉砕物は外熱式乾留炉
に投入され、加熱される。In the mercury-containing dry battery processing apparatus of the present invention having the above configuration, the collected used mercury-containing dry batteries are appropriately crushed by a crusher, and the crushed product is put into an external heating type carbonization furnace and heated. .
この温度は水銀の沸点(375℃)より相当高く、主に
酸化水銀の形で乾電池に用いられている水銀は、熱分解
されて水銀蒸気となシ、その他の成分も燃焼あるいは加
熱分解によって灰および乾留ガスとなる。灰は炉床に沈
積し、水銀蒸気を含む乾留ガスはコンデンサへ送られる
。なお、この発明のように乾電池を粉砕すると、粉砕し
ない場合に較べて乾留炉あるいは燃焼炉での処理時間が
5分の1ないし6分の1に短縮され、従って装置全体の
処理時間も同様に大幅に短縮される。This temperature is considerably higher than the boiling point of mercury (375°C), and the mercury used in dry batteries, mainly in the form of mercury oxide, is thermally decomposed into mercury vapor, and other components are also ashed by combustion or thermal decomposition. and becomes carbonized gas. The ash is deposited in the hearth and the carbonized gas containing mercury vapor is sent to the condenser. Furthermore, when dry batteries are crushed as in the present invention, the processing time in a carbonization furnace or combustion furnace is shortened to one-fifth to one-sixth compared to when the batteries are not crushed, and therefore the processing time of the entire device is also reduced. will be significantly shortened.
コンデンサにおいては、乾留ガスが冷却され、水銀蒸気
が凝縮して液化し、その大半が水銀回収槽で回収される
。水銀回収槽で処理された乾留ガス(廃ガス)はスプレ
ー塔に送られて、微量水銀および浮遊粉塵が除去され、
さらに最終処理装置の緩衝タンクで水分が分離され、充
填塔の活性炭層およびシリカゲル層を通って微量の残留
水銀および炭化水素類がそれぞれ除去された後、はぼ完
全に浄化された廃ガスとして、廃ガス煙突より大気中に
放出される。In the condenser, the carbonized gas is cooled and the mercury vapor is condensed and liquefied, most of which is recovered in the mercury recovery tank. The carbonized gas (waste gas) treated in the mercury recovery tank is sent to a spray tower to remove trace amounts of mercury and suspended dust.
Furthermore, water is separated in the buffer tank of the final treatment equipment, and trace amounts of residual mercury and hydrocarbons are removed through the activated carbon layer and silica gel layer of the packed tower, and then the waste gas is completely purified. The waste gas is released into the atmosphere from the chimney.
この発明による水銀含有乾電池の処理装置の一実施例は
、粉砕機11.外熱式乾留炉2、コンデンサ3、水銀回
収槽4、第1プロワ5、スプレー塔6、第2ブロワ7、
および最終処理部8で構成されている。An embodiment of the mercury-containing dry cell processing apparatus according to the present invention includes a crusher 11. External heat carbonization furnace 2, condenser 3, mercury recovery tank 4, first blower 5, spray tower 6, second blower 7,
and a final processing section 8.
各地の水銀電池取扱店等で回収された使用済の水銀含有
乾電池は、粉砕機1で適度に粉砕され、外熱式乾留炉2
に投入されて、ガスバーナ2)により水銀の沸点(37
5℃)より相当高温で加熱される。この加熱時、乾留炉
2には、シリカゲルを充填した空気取入口22より電磁
弁23の制御下において適量の乾燥空気が供給される。Used mercury-containing dry batteries collected from mercury battery dealers, etc. in various places are properly crushed in a crusher 1, and then transferred to an external heat carbonization furnace 2.
The boiling point of mercury (37
5°C). During this heating, an appropriate amount of dry air is supplied to the carbonization furnace 2 from an air intake port 22 filled with silica gel under the control of a solenoid valve 23.
また、乾留炉2には、燃焼廃熱を利用して温水を得るた
めの水管24が炉外壁に沿って備えられている。なお、
符号25および26はそれぞれ炉内圧針および炉内温度
計を示す。Further, the carbonization furnace 2 is equipped with a water pipe 24 along the outer wall of the furnace for obtaining hot water using combustion waste heat. In addition,
Reference numerals 25 and 26 indicate an in-furnace pressure needle and an in-furnace thermometer, respectively.
炉内に投入された粉砕物中の酸化水銀は、加熱によって
分解され、水銀蒸気を発生する。また、亜鉛等その他の
成分は溶融あるいは燃焼によって残渣または浮遊粉塵と
なる。これらの水銀蒸気および浮遊粉塵を含む乾留炉2
の乾留ガスあるいは廃ガスは、第1プロワ5に引かれて
コンデンサ3を通過する間に冷却され、凝縮し、液化水
銀となって水銀回収槽4により回収される。この水銀回
収槽4では、乾留炉2に投入された粉砕物中の水銀成分
の約75ないし80パーセントが回収され、再生利用さ
れる0
水銀回収槽4の廃ガスは、第1プロワ5を介してスプレ
ー塔6へ送り込まれる。スプレー塔6は、第2図に示す
ように、下部に硫化ナトリウム溶液の入った循環タンク
61を有し、循環ポンプ62によって硫化ナトリウム溶
液を塔部63内に多数設けられたスプレーノズル64へ
送り、上昇シテ来る廃ガスに対して吹付けて、廃ガス中
の微量の水銀を硫化ナトリウムと反応させ、硫化水銀と
して除去するようになっている。また、浮遊粉塵も大部
分がこのスプレー塔6で除去される。The mercury oxide in the crushed material introduced into the furnace is decomposed by heating and generates mercury vapor. In addition, other components such as zinc become residue or floating dust by melting or combustion. Carbonization furnace 2 containing these mercury vapors and suspended dust
The carbonized gas or waste gas is drawn by the first blower 5 and cooled while passing through the condenser 3, condenses, becomes liquefied mercury, and is recovered by the mercury recovery tank 4. In this mercury recovery tank 4, about 75 to 80 percent of the mercury components in the pulverized material fed into the carbonization furnace 2 is recovered and recycled. and sent to the spray tower 6. As shown in FIG. 2, the spray tower 6 has a circulation tank 61 containing a sodium sulfide solution at the bottom, and a circulation pump 62 sends the sodium sulfide solution to a large number of spray nozzles 64 provided in a tower section 63. It is sprayed onto the rising waste gas to cause trace amounts of mercury in the waste gas to react with sodium sulfide and remove it as mercury sulfide. Further, most of the suspended dust is also removed by this spray tower 6.
スプレー塔6で処理された廃ガスは、第2プロワ7によ
って最終処理部8へ送られる。・第2プロワ7は、第3
図に示すように、主管路71の他、処理装置全体の制御
圧のバランスを調節する。ためのバイパス管路72を有
し、その制御はバイパス用スルス弁73によって行なわ
れる。なお、符号74は主管路スルス弁を示し、75お
よび76はそれぞれプロワファンおよびその駆動モータ
を示す。The waste gas treated in the spray tower 6 is sent to the final treatment section 8 by the second blower 7.・The second blower 7 is the third
As shown in the figure, the control pressure balance of the main pipe line 71 and the entire processing apparatus is adjusted. The bypass line 72 is controlled by a bypass valve 73. Note that the reference numeral 74 indicates a main pipe flow valve, and 75 and 76 indicate a blower fan and its drive motor, respectively.
最終処理部8は、第4図に示すように、スプレー塔6の
廃ガス中の微量の不純物および水分を分離する緩衝液の
入った緩衝タンク81、スプレー除去するシリカゲル8
3が充填された充填塔84、および充填塔84で処理さ
れた廃ガスを大気中に放出する廃ガス煙突85で構成さ
れておシ、この最終処理部8で処理された廃ガスは、水
銀成分がほぼ完全に除去され、環境を汚染することがな
い程度まで十分に浄化されている。As shown in FIG. 4, the final processing section 8 includes a buffer tank 81 containing a buffer solution for separating minute amounts of impurities and moisture from the waste gas from the spray tower 6, and a silica gel 8 for spray removal.
3, and a waste gas chimney 85 that discharges the waste gas treated in the packed tower 84 into the atmosphere. The ingredients have been almost completely removed and the product has been sufficiently purified to the point that it will not pollute the environment.
この発明によれば、使用済水銀含有乾電池を高速で大量
処理する仁とができ、しかも水銀の再生利用が可能であ
る。According to this invention, it is possible to process a large amount of used mercury-containing dry batteries at high speed, and it is also possible to recycle the mercury.
第1図は、この発明による水銀含有乾電池の処理装置の
一実施例の構成図、第2図は上記実施例のスプレー塔の
概略断面図、第3図は上記実施例の第2プロワの構成図
、第4図はその最終処理部の概略断面図である。
1・・・粉砕機、2・・・外熱式乾留炉、3・・・コン
デンサ、4・・・水銀回収槽、6・・・スプレー塔、8
・・・最終処理部、81・・・緩衝タンク、84・・・
充填塔、85・・・廃ガス煙突FIG. 1 is a block diagram of an embodiment of a mercury-containing dry cell processing apparatus according to the present invention, FIG. 2 is a schematic cross-sectional view of the spray tower of the above embodiment, and FIG. 3 is a configuration of the second blower of the above embodiment. 4 are schematic cross-sectional views of the final processing section. 1... Pulverizer, 2... External heating carbonization furnace, 3... Condenser, 4... Mercury recovery tank, 6... Spray tower, 8
...Final processing section, 81...Buffer tank, 84...
Packed tower, 85...waste gas chimney
Claims (2)
により粉砕された粉砕物を水銀の沸点より高い温度で加
熱する外熱式乾留炉と、この乾留炉から排出される乾留
ガスを冷却し、水銀蒸気を凝縮させるコンデンサと、凝
縮された水銀を回収する水銀回収槽と、この水銀回収槽
から廃出される廃ガス中の微量水銀および浮遊粉塵を除
去するスプレー塔と、このスプレー塔からの廃ガスより
微量の不純物ならびに水分を分離する緩衝タンク、スプ
レー塔で除去できなかったさらに微量の残留水銀を吸着
除去する活性炭と廃ガス中の炭火水素類を吸着除去する
シリカゲルを充填した充填塔、およびこの充填塔を通過
した廃ガスを大気中に放出する廃ガス煙突よりなる最終
処理部と、で構成された水銀含有乾電池の処理装置。(1) A pulverizer that crushes mercury-containing dry batteries, an external heating carbonization furnace that heats the pulverized material by this pulverizer at a temperature higher than the boiling point of mercury, and a cooling carbonization gas discharged from this carbonization furnace. A condenser that condenses mercury vapor, a mercury recovery tank that recovers the condensed mercury, a spray tower that removes trace amounts of mercury and suspended dust from the waste gas discharged from the mercury recovery tank, and A buffer tank that separates minute amounts of impurities and water from the waste gas, a packed tower filled with activated carbon that adsorbs and removes trace amounts of residual mercury that could not be removed by the spray tower, and silica gel that adsorbs and removes hydrocarbons in the waste gas. , and a final treatment section consisting of a waste gas chimney that discharges the waste gas that has passed through the packed tower into the atmosphere.
ための乾燥空気供給装置を備え、前記スプレー塔と前記
最終処理部の緩衝タンクがスルス弁によって開閉される
バイパス管路を備えたブロワにより接続されていること
を特徴とする特許請求の範囲第1項記載の水銀含有乾電
池の処理装置。(2) The external heating type carbonization furnace is equipped with a dry air supply device for supplying dry air into the furnace, and the spray tower and the buffer tank of the final treatment section have a bypass pipe that is opened and closed by a surus valve. 2. The mercury-containing dry cell processing apparatus according to claim 1, wherein the mercury-containing dry battery processing apparatus is connected by a blower provided therein.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP60106249A JPS61263687A (en) | 1985-05-16 | 1985-05-16 | Apparatus for treating dry cell containing mercury |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP60106249A JPS61263687A (en) | 1985-05-16 | 1985-05-16 | Apparatus for treating dry cell containing mercury |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS61263687A true JPS61263687A (en) | 1986-11-21 |
Family
ID=14428826
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP60106249A Pending JPS61263687A (en) | 1985-05-16 | 1985-05-16 | Apparatus for treating dry cell containing mercury |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS61263687A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2653044A1 (en) * | 1989-10-12 | 1991-04-19 | Pec Engineering | PROCESS AND DEVICES FOR DECONTAMINATION OF SOLID PRODUCTS. |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5383031A (en) * | 1976-12-28 | 1978-07-22 | Nomura Kousan Kk | Recovery process of valuable materials in silver oxide battery |
JPS60257892A (en) * | 1984-06-04 | 1985-12-19 | Eikoku Denshi:Kk | Disposal of mercury-containing battery |
-
1985
- 1985-05-16 JP JP60106249A patent/JPS61263687A/en active Pending
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5383031A (en) * | 1976-12-28 | 1978-07-22 | Nomura Kousan Kk | Recovery process of valuable materials in silver oxide battery |
JPS60257892A (en) * | 1984-06-04 | 1985-12-19 | Eikoku Denshi:Kk | Disposal of mercury-containing battery |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2653044A1 (en) * | 1989-10-12 | 1991-04-19 | Pec Engineering | PROCESS AND DEVICES FOR DECONTAMINATION OF SOLID PRODUCTS. |
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