JPH08117724A - Method of treating fly ash from incinerator or melting furnace - Google Patents
Method of treating fly ash from incinerator or melting furnaceInfo
- Publication number
- JPH08117724A JPH08117724A JP6286008A JP28600894A JPH08117724A JP H08117724 A JPH08117724 A JP H08117724A JP 6286008 A JP6286008 A JP 6286008A JP 28600894 A JP28600894 A JP 28600894A JP H08117724 A JPH08117724 A JP H08117724A
- Authority
- JP
- Japan
- Prior art keywords
- fly ash
- filtrate
- heavy metals
- residue
- lead
- 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
Landscapes
- Processing Of Solid Wastes (AREA)
Abstract
(57)【要約】
【目的】 焼却炉や溶融炉からの飛灰中に含まれる重金
属や有害物質を、セメント固化法あるいは溶融処理によ
ることなく、安全な形で分離できる焼却炉または溶融炉
からの飛灰の処理方法の提供。
【構成】 飛灰を水に溶解してpH3〜7に調整後、重
金属を含む残渣と可溶性塩類を含む濾液とに分別する第
1工程;残渣をリパルプしてpHを3より低く調整して
亜鉛を主体とする重金属を溶出せしめ、鉛を主体とする
残渣と濾液とに分別する第2工程;上記第1、第2工程
から得られた濾液を中和してアルカリ側に調整し、亜
鉛、銅を主体とする重金属の水酸化物、さらには硫化剤
を添加して水酸化物にならなかった残りの重金属を硫化
物として沈澱させ、得られた澱物と最終濾液とに分別す
る第3工程からなることを特徴とする。
(57) [Summary] [Purpose] From an incinerator or a melting furnace that can separate heavy metals and harmful substances contained in fly ash from an incinerator or a melting furnace in a safe form without using a cement solidification method or a melting treatment. To provide a method of treating fly ash. [Structure] First step of dissolving fly ash in water to adjust the pH to 3 to 7, and then separating the residue into a residue containing heavy metals and a filtrate containing soluble salts; repulping the residue to adjust the pH to lower than 3; A second step of eluting a heavy metal mainly composed of the above and fractionating it into a residue composed mainly of lead and a filtrate; neutralizing the filtrate obtained from the first and second steps to adjust to an alkaline side, zinc, A heavy metal hydroxide mainly composed of copper, and further, a sulfidizing agent is added to precipitate the remaining heavy metal which has not been converted into a hydroxide, and the precipitated heavy metal is separated into a final filtrate. It is characterized by comprising steps.
Description
【0001】[0001]
【産業上の利用分野】本発明は、都市ごみ焼却工場や産
業廃棄物焼却工場等における焼却炉または溶融炉から発
生する重金属含有飛灰の処理方法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating heavy metal-containing fly ash generated from an incinerator or a melting furnace in a municipal solid waste incinerator, an industrial waste incinerator, or the like.
【0002】[0002]
【従来の技術】一般に、事業場や一般家庭から排出され
るゴミ(「都市ゴミ」または「一般廃棄物」と称されて
いる)は、都市ゴミ焼却場に集められて焼却処分される
が、その際に焼却炉から発生する燃えがらや飛灰は最終
処分場に運ばれ堆積されている。2. Description of the Related Art Generally, garbage discharged from business establishments and households (referred to as "urban garbage" or "general waste") is collected at an urban refuse incinerator and incinerated. At that time, cinders and fly ash generated from the incinerator are transported to the final disposal site and accumulated.
【0003】そのまま堆積されるものの他に、飛灰に含
まれる鉛、カドミウムなどの重金属類やダイオキシンな
どの有害物質をセメントで固化して廃棄したり、燃えが
らや飛灰を溶融炉で溶融固化して埋立容積を減らすこと
も行われている。In addition to what is deposited as it is, heavy metals such as lead and cadmium contained in fly ash and harmful substances such as dioxins are solidified with cement and discarded, and cinders and fly ash are melted and solidified in a melting furnace. The landfill volume is also being reduced by using this method.
【0004】[0004]
【発明が解決しようとする課題】しかしながら、近年堆
積場確保の困難性や、堆積される飛灰に含まれている
鉛、カドミウムなどの重金属やダイオキシン類の有害性
が問題視されている。However, in recent years, problems such as difficulty in securing a deposition site and harmful effects of heavy metals such as lead and cadmium contained in deposited fly ash and dioxins have been regarded as problems.
【0005】そのため、上記有害物質の安定化を図るた
めセメント固化法や薬剤処理法が開発され実用化されて
いるが、セメント固化法では埋立容積を減らすことがで
きないため、堆積場の確保に関する問題点は未解決のま
まであった。また飛灰とセメントの混練処理により飛灰
に含まれている重金属の溶出を低下させることができる
が(環境庁告示第13号法による溶出試験)、この処理
法は完全ではなく、飛灰によっては溶出防止効率は不十
分であるうえ、酸性雨等の影響を考えた場合、セメント
と混練した飛灰中の重金属類を長時間安定化させること
は難しい。Therefore, a cement solidification method and a chemical treatment method have been developed and put into practical use in order to stabilize the above-mentioned harmful substances, but since the cement solidification method cannot reduce the landfill volume, there is a problem in securing a sedimentation site. The points remained unresolved. Although the elution of heavy metals contained in fly ash can be reduced by the kneading process of fly ash and cement (elution test according to the Environmental Agency Notification No. 13 method), this treatment method is not perfect and In addition to insufficient elution prevention efficiency, it is difficult to stabilize heavy metals in fly ash mixed with cement for a long time, considering the effect of acid rain.
【0006】一方、焼却炉からの燃えがらや飛灰を溶融
処理することにより、減容化やダイオキシン類の熱分解
による無害化を図ることができるという報告がある(永
田勝也著「都市ゴミ焼却炉におけるダイオキシン対策の
現状と動向」廃棄物学会誌第3巻第3号)。On the other hand, there is a report that it is possible to reduce the volume and to make harmless by the thermal decomposition of dioxins by melting and treating the cinders and fly ash from the incinerator (Katsuya Nagata "Urban refuse incinerator" Status and Trends of Dioxin Countermeasures in Japan ", Journal of Japan Society of Waste, Vol. 3, No. 3).
【0007】しかし、上記溶融処理によると、蒸気圧の
大きい鉛やカドミウム等の重金属は、炉内で揮発して排
ガス中に入り排ガス処理設備で凝縮して再び飛灰となっ
てしまうという問題点があった。However, according to the above-mentioned melting treatment, heavy metals such as lead and cadmium having a large vapor pressure are volatilized in the furnace, enter the exhaust gas, and are condensed in the exhaust gas treatment equipment to become fly ash again. was there.
【0008】したがって本発明の目的は、焼却炉や溶融
炉からの飛灰中に含まれる重金属や有害物質を、セメン
ト固化あるいは溶融処理することなく、安定な形で分離
できる焼却炉または溶融炉からの飛灰の処理方法を提供
することにある。Therefore, an object of the present invention is to remove heavy metals and harmful substances contained in fly ash from incinerators and melting furnaces in a stable form without solidifying or melting cement. To provide a method for treating fly ash.
【0009】[0009]
【課題を解決するための手段】本発明者らは上記目的を
達成すべく鋭意研究の結果、まず飛灰を水に溶解してp
Hを3〜7に調整して処理すれば、飛灰中の重金属分と
塩類分とを濾別でき、後工程において処理液のpHを3
よりも低くコントロールして鉛を主体とする鉛残渣、さ
らに鉛以外の重金属と塩類を含む濾液を得て、次いでこ
の濾液を中和して容易にかつ安定して亜鉛を主とする重
金属の水酸化澱物が得られ、これらの残渣および澱物は
非鉄製錬用資源として活用できるものであり、またpH
コントロール用の鉱酸あるいは中和剤の添加量が比較的
少なく、コスト的にも評価できることを見いだし本発明
に到達した。As a result of earnest research to achieve the above-mentioned object, the inventors of the present invention firstly dissolved fly ash in water to obtain p.
If H is adjusted to 3 to 7 and treated, the heavy metal component and the salt component in the fly ash can be separated by filtration, and the pH of the treatment liquid is adjusted to 3 in the subsequent step.
Control to a lower level to obtain a lead residue containing mainly lead, and a filtrate containing heavy metals and salts other than lead, and then neutralizing this filtrate easily and stably to remove water containing heavy metals mainly containing zinc. Oxidized starch is obtained, and these residues and starch can be utilized as resources for non-ferrous smelting, and pH
The inventors have found that the amount of the control mineral acid or neutralizing agent added is relatively small and can be evaluated in terms of cost.
【0010】すなわち本発明は、焼却炉または溶融炉か
ら発生する塩素、ナトリウムを主体とする塩類および亜
鉛、銅を主体とする重金属を含有する飛灰の処理方法に
おいて、上記飛灰を水に溶解してpHが3〜7の範囲に
なるように調整した後、固液分離して重金属分を含む残
渣と塩類分を含む濾液に分離する第1工程;得られた残
渣をリパルプしpHを3よりも低く調整して亜鉛を主体
とする重金属を溶出せしめ、鉛を主体とする鉛残渣と濾
液とに固液分離する第2工程;次いで第1工程並びに第
2工程で得られた濾液に中和剤を添加して、亜鉛、銅を
主体とする重金属の水酸化物を沈澱させるとともに、必
要に応じて硫化剤を添加して水酸化物にならなかった残
りの重金属を硫化物として沈澱させ、これらの澱物を濾
別する第3工程;からなることを特徴とする焼却炉また
は溶融炉からの飛灰の処理方法を提供するものである。That is, the present invention relates to a method for treating fly ash containing chlorine and sodium-based salts and zinc and copper-based heavy metals generated from an incinerator or a melting furnace, wherein the fly ash is dissolved in water. After adjusting the pH to be in the range of 3 to 7, solid-liquid separation is performed to separate a residue containing heavy metals and a filtrate containing salts from the first step; the resulting residue is repulped to pH 3 The second step in which the heavy metal containing zinc as a main component is eluted and the solid solution is separated into a lead residue containing lead as a main component and the filtrate, and the filtrate obtained in the first step and the second step Add a hydrating agent to precipitate the hydroxides of heavy metals consisting mainly of zinc and copper, and, if necessary, add a sulfiding agent to precipitate the remaining heavy metals that did not become hydroxides as sulfides. , A third step of filtering off these starches; There is provided a method of processing fly ash from incinerators or melting furnace, characterized in that Ranaru.
【0011】[0011]
【作用】本発明の第1工程では、まず飛灰を水に溶解し
てスラリーとし、このスラリーを攪拌しながら塩酸また
は硫酸等の鉱酸を添加してpHを3〜7に調整する。な
おスラリー化された飛灰のpHはその組成によって異な
るため鉱酸の添加量は飛灰に応じて調整する必要があ
る。また上記スラリーのpHが既に最適pHである場合
には鉱酸を加える必要はない。さらに上記pHを維持し
ての攪拌時間は少なくとも10分程度であれば良く、そ
の時の温度は室温でよい。次いで上記スラリーを濾過し
て重金属を含む残渣と塩類を含む濾液とに分別する。In the first step of the present invention, fly ash is first dissolved in water to form a slurry, and a mineral acid such as hydrochloric acid or sulfuric acid is added to the slurry while stirring to adjust the pH to 3 to 7. Since the pH of the fly ash slurried varies depending on its composition, it is necessary to adjust the amount of mineral acid added according to the fly ash. If the pH of the slurry is already at the optimum pH, it is not necessary to add mineral acid. Further, the stirring time while maintaining the above pH may be at least about 10 minutes, and the temperature at that time may be room temperature. Then, the slurry is filtered to separate into a residue containing heavy metals and a filtrate containing salts.
【0012】第2工程では、第1工程で得られた残渣を
リパルプして塩酸を加えpHを3.0よりも低く、好ま
しくは1.0前後に調整して鉛以外の重金属を浸出溶解
させ、鉛を主体とする残渣と、亜鉛など溶解重金属分お
よびカルシウム、塩素等の塩類を含む濾液とに分別す
る。なお上記濾別において残渣に付着する浸出液を除去
して得られる残渣を資源として活用する場合に重要であ
り、通常の水洗でもよいが、水酸化ナトリウム液で洗浄
すると不純物の少ない鉛残渣を回収できる場合があり、
鉛製錬用原料として好ましい。In the second step, the residue obtained in the first step is repulped and hydrochloric acid is added to adjust the pH to a value lower than 3.0, preferably around 1.0 so that heavy metals other than lead are leached and dissolved. , A lead-based residue and a filtrate containing dissolved heavy metal components such as zinc and salts such as calcium and chlorine. In addition, it is important to utilize the residue obtained by removing the leachate adhering to the residue in the above filtration as a resource, and normal washing with water is also possible, but washing with a sodium hydroxide solution can recover lead residues with few impurities. Sometimes,
It is preferable as a raw material for lead smelting.
【0013】第3工程では、第1、第2工程で発生した
濾液を混合した後、中和剤として水酸化ナトリウム、炭
酸ナトリウムまたは水酸化カルシウムの少なくとも一種
を添加してそのpHを7.0以上好ましくは7.5〜
8.5に調整することにより、亜鉛を主とする重金属を
水酸化物として生成させ、その液中に重金属が少量残留
している場合には、さらに硫化ナトリウム、水硫化ナト
リウムまたは硫化水素などの硫化剤を添加して残留する
重金属を硫化物として沈澱させ濾過分別して亜鉛澱物と
最終中和濾液を得る。In the third step, after mixing the filtrates generated in the first and second steps, at least one of sodium hydroxide, sodium carbonate or calcium hydroxide is added as a neutralizing agent to adjust the pH to 7.0. More preferably 7.5 to
By adjusting to 8.5, a heavy metal mainly containing zinc is generated as a hydroxide, and when a small amount of heavy metal remains in the solution, sodium sulfide, sodium hydrosulfide, hydrogen sulfide, etc. A sulfiding agent is added to precipitate the remaining heavy metal as a sulfide, which is separated by filtration to obtain a zinc starch and a final neutralized filtrate.
【0014】したがって、本発明の方法では、飛灰に含
まれる重金属を主に鉛を含有する残渣と、主に亜鉛、
銅、カドミウムあるいは水銀を含有する水酸化物および
硫化物とに分けて回収することができるため、それぞれ
非鉄製錬原料として活用できる。Therefore, according to the method of the present invention, the heavy metal contained in the fly ash is mainly a lead-containing residue, and mainly zinc.
Since it can be recovered separately from hydroxides and sulfides containing copper, cadmium or mercury, they can be used as non-ferrous smelting raw materials.
【0015】[0015]
【実施例】図1は本実施例に用いられた処理工程のフロ
ーシートであって、この図を参照して本発明をさらに詳
細に説明するが、本発明の範囲は以下の実施例により制
限されるものではない。EXAMPLE FIG. 1 is a flow sheet of the processing steps used in this example, and the present invention will be explained in more detail with reference to this figure, but the scope of the present invention is limited by the following examples. It is not something that will be done.
【0016】(1)まず、3リットルビーカーに蒸留水
2リットルを入れて攪拌しながら表1に示す組成のA焼
却工場産飛灰100gを投入してスラリーとし、10分
間攪拌したところpHは5.4であった。次いでこのス
ラリーを濾過して残渣と濾液に分別し、飛灰中の重金属
分は残渣に、ナトリウム、塩素などの可溶性塩類は濾液
に分離した(以上第1工程)。(1) First, 2 liters of distilled water was placed in a 3 liter beaker, and 100 g of fly ash from the incineration plant A having the composition shown in Table 1 was added to the slurry to make a slurry, and the mixture was stirred for 10 minutes. It was .4. Next, this slurry was filtered to separate it into a residue and a filtrate. Heavy metal components in fly ash were separated into a residue, and soluble salts such as sodium and chlorine were separated into a filtrate (the above first step).
【0017】(2)次いで残渣を蒸留水2リットルでリ
パルプしたものに塩酸を添加してpHが1.0になるよ
うにpH調整後、10分間攪拌し、得られた鉛残渣を固
液分離して鉛残渣と濾液に分離した。この鉛残渣の洗浄
手段として水を用いるよりも水酸化ナトリウム(NaO
H)溶液を用いた方が鉛以外の不純物の除去に効果的で
あることが判明した(以上第2工程)。(2) Next, hydrochloric acid is added to the residue obtained by repulping the residue with 2 liters of distilled water and adjusting the pH so that the pH becomes 1.0, followed by stirring for 10 minutes, and the obtained lead residue is subjected to solid-liquid separation. And separated into a lead residue and a filtrate. Rather than using water as a means for cleaning this lead residue, sodium hydroxide (NaO
It was found that the use of the (H) solution is more effective in removing impurities other than lead (the above is the second step).
【0018】(3)次いでこの第2工程で得られた濾液
と前記第1工程の濾液を混合した後、200g/l に濃度
調整した水酸化ナトリウム水溶液を添加してpH7.0
まで中和し、さらに10g/l に濃度調整した水硫化ナト
リウム(NaHS)液を酸化還元電位で−100mV(A
g/AgCl電極)まで添加し、亜鉛を主とする重金属
の水酸化物澱物およびその他の重金属の硫化物澱物を生
成させ、固液分離して残渣と最終濾液とに分離し、残渣
は洗浄して亜鉛澱物とした(以上第3工程)。(3) Next, after mixing the filtrate obtained in the second step and the filtrate in the first step, an aqueous sodium hydroxide solution having a concentration adjusted to 200 g / l was added to adjust the pH to 7.0.
Sodium hydrosulfide (NaHS) solution neutralized to 10 g / l and adjusted to a redox potential of -100 mV (A
g / AgCl electrode) to produce a hydroxide precipitate of heavy metal mainly containing zinc and a sulfide precipitate of other heavy metal, and solid-liquid separation is performed to separate a residue and a final filtrate. It was washed to obtain zinc starch (above third step).
【0019】上記のようにして鉛澱物から得られた鉛残
渣、亜鉛澱物、最終工程における中和濾液について、P
b、Zn、Fe、Cu、Si、Al、NaおよびClの
含有量を調べその結果を、前記飛灰の各成分含有量とと
もに表1に示した。Regarding the lead residue obtained from the lead starch as described above, the zinc starch, and the neutralized filtrate in the final step, P
The contents of b, Zn, Fe, Cu, Si, Al, Na and Cl were examined, and the results are shown in Table 1 together with the contents of the respective components of the fly ash.
【0020】[0020]
【表1】 [Table 1]
【0021】表1の結果からもわかるように、飛灰に含
まれる鉛や亜鉛などの重金属は安定な形でほぼ完全に分
離されていた。また鉛残渣中の鉛品位は31.23%、
亜鉛澱物中の亜鉛品位は34.05%であって、これら
は資源として非鉄製錬所で処理できるものであり、さら
に最終の中和濾液は排水基準を下回っており、直接河川
や海に放流可能なものであった。As can be seen from the results in Table 1, heavy metals such as lead and zinc contained in the fly ash were separated almost completely in a stable form. The lead quality in the lead residue is 31.23%,
The zinc grade in the zinc starch is 34.05%, which can be treated as a resource in a non-ferrous smelter, and the final neutralization filtrate is below the wastewater standard, so that it can be directly fed to rivers or the sea. It could be released.
【0022】[0022]
【発明の効果】以上説明したように、本発明の方法によ
れば飛灰に含まれている重金属を安定な形で分離するこ
とができ、また分離された鉛を含む残渣と亜鉛を主とす
る重金属の水産化澱物はそれぞれ鉛および亜鉛を資源と
して活用できるものであるため、有害な重金属を処分場
に埋立てることなく安全な処分を行うことができる。As described above, according to the method of the present invention, heavy metals contained in fly ash can be separated in a stable form, and the separated lead-containing residue and zinc are mainly contained. Since the heavy metal aquatic sediments that utilize lead and zinc can be used as resources, safe disposal can be performed without landfilling harmful heavy metals in the repository.
【図1】本発明の一実施例に用いられた処理工程を示す
フローシートである。FIG. 1 is a flow sheet showing processing steps used in an example of the present invention.
フロントページの続き (72)発明者 杉澤 智司 東京都千代田区丸の内1丁目8番2号 同 和鉱業株式会社内Front page continuation (72) Inventor Satoshi Sugizawa 1-8-2 Marunouchi, Chiyoda-ku, Tokyo Dowa Mining Co., Ltd.
Claims (2)
ナトリウムを主体とする塩類および亜鉛、銅、鉛を主体
とする重金属を含有する飛灰の処理方法において、上記
飛灰を水に溶解してpHが3〜7の範囲になるように調
整した後、固液分離して重金属分を含む残渣と塩類分を
含む濾液に分離する第1工程;得られた残渣をリパルプ
しpHを3よりも低く調整して亜鉛を主体とする重金属
を溶出せしめ、鉛を主体とする鉛残渣と濾液とに固液分
離する第2工程;次いで第1工程並びに第2工程で得ら
れた濾液に中和剤を添加して、亜鉛、銅を主体とする重
金属の水酸化物を沈澱させ、固液分離して澱物と濾液に
分離する第3工程;からなることを特徴とする焼却炉ま
たは溶融炉からの飛灰の処理方法。1. Chlorine generated from an incinerator or a melting furnace,
In a method for treating fly ash containing salts containing sodium as a main component and heavy metals containing zinc, copper and lead as a main component, the fly ash is dissolved in water to adjust the pH to a range of 3 to 7. First step of solid-liquid separating into a residue containing heavy metals and a filtrate containing salts; repulping the obtained residue and adjusting the pH to a value lower than 3 to elute heavy metals mainly containing zinc, Second step of solid-liquid separation into a lead residue containing lead as a main component and a filtrate; Next, a neutralizing agent is added to the filtrate obtained in the first step and the second step to remove heavy metals mainly containing zinc and copper. A method for treating fly ash from an incinerator or a melting furnace, which comprises a third step of precipitating a hydroxide, solid-liquid separating it into a precipitate and a filtrate.
ナトリウムを主体とする塩類および亜鉛、銅、鉛を主体
とする重金属を含有する飛灰の処理方法において、上記
飛灰を水に溶解してpHが3〜7の範囲になるように調
整した後、固液分離して重金属分を含む残渣と塩類分を
含む濾液に分離する第1工程;得られた残渣をリパルプ
しpHを3よりも低く調整して亜鉛を主体とする重金属
を溶出せしめ、鉛を主体とする鉛残渣と濾液とに固液分
離する第2工程;次いで第1工程並びに第2工程で得ら
れた濾液に中和剤を添加して、亜鉛、銅を主体とする重
金属の水酸化物を沈澱させるとともに、さらに硫化剤を
添加して水酸化物にならなかった残りの重金属を硫化物
として沈澱させ、これらの澱物を濾別する第3工程;か
らなることを特徴とする焼却炉または溶融炉からの飛灰
の処理方法。2. Chlorine generated from an incinerator or a melting furnace,
In a method for treating fly ash containing salts containing sodium as a main component and heavy metals containing zinc, copper and lead as a main component, the fly ash is dissolved in water to adjust the pH to a range of 3 to 7. First step of solid-liquid separating into a residue containing heavy metals and a filtrate containing salts; repulping the obtained residue and adjusting the pH to a value lower than 3 to elute heavy metals mainly containing zinc, Second step of solid-liquid separation into a lead residue containing lead as a main component and a filtrate; Next, a neutralizing agent is added to the filtrate obtained in the first step and the second step to remove heavy metals mainly containing zinc and copper. A third step of precipitating the hydroxides, further adding a sulfiding agent to precipitate the remaining heavy metals not converted into hydroxides as sulfides, and filtering these precipitates off; A method for treating fly ash from an incinerator or melting furnace.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP6286008A JPH08117724A (en) | 1994-10-26 | 1994-10-26 | Method of treating fly ash from incinerator or melting furnace |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP6286008A JPH08117724A (en) | 1994-10-26 | 1994-10-26 | Method of treating fly ash from incinerator or melting furnace |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH08117724A true JPH08117724A (en) | 1996-05-14 |
Family
ID=17698812
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP6286008A Pending JPH08117724A (en) | 1994-10-26 | 1994-10-26 | Method of treating fly ash from incinerator or melting furnace |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH08117724A (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2000000546A (en) * | 1998-06-17 | 2000-01-07 | Tsukishima Kikai Co Ltd | Heavy metal component recovery method |
| WO2005040437A1 (en) * | 2003-10-27 | 2005-05-06 | Dowa Mining Co., Ltd. | Method of wet treatment of fly ash |
| JP2005246226A (en) * | 2004-03-03 | 2005-09-15 | Dowa Mining Co Ltd | Fly ash treatment method |
-
1994
- 1994-10-26 JP JP6286008A patent/JPH08117724A/en active Pending
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2000000546A (en) * | 1998-06-17 | 2000-01-07 | Tsukishima Kikai Co Ltd | Heavy metal component recovery method |
| WO2005040437A1 (en) * | 2003-10-27 | 2005-05-06 | Dowa Mining Co., Ltd. | Method of wet treatment of fly ash |
| JP2005246226A (en) * | 2004-03-03 | 2005-09-15 | Dowa Mining Co Ltd | Fly ash treatment method |
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