JP2003010814A - Ash treatment method - Google Patents

Ash treatment method

Info

Publication number
JP2003010814A
JP2003010814A JP2001203080A JP2001203080A JP2003010814A JP 2003010814 A JP2003010814 A JP 2003010814A JP 2001203080 A JP2001203080 A JP 2001203080A JP 2001203080 A JP2001203080 A JP 2001203080A JP 2003010814 A JP2003010814 A JP 2003010814A
Authority
JP
Japan
Prior art keywords
melting furnace
ash
solid content
fly ash
solid
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
JP2001203080A
Other languages
Japanese (ja)
Other versions
JP3627923B2 (en
Inventor
Shinsaku Maruyama
眞策 丸山
Takaharu Uchida
隆治 内田
Seiichi Tsuda
精一 津田
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.)
Ebara Corp
Original Assignee
Ebara Corp
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 Ebara Corp filed Critical Ebara Corp
Priority to JP2001203080A priority Critical patent/JP3627923B2/en
Publication of JP2003010814A publication Critical patent/JP2003010814A/en
Application granted granted Critical
Publication of JP3627923B2 publication Critical patent/JP3627923B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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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
    • Y02P10/25Process efficiency

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Extraction Or Liquid Replacement (AREA)
  • Waste-Gas Treatment And Other Accessory Devices For Furnaces (AREA)
  • Gasification And Melting Of Waste (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a method for obtaining a recyclable solid content by concentrating a heavy metal and by lowering the chloride ion concentration in the solid content of an exhaust gas generating from a melting furnace of fly ash. SOLUTION: The fly ash from an incineration furnace and/or the fly ash (a) from the melting furnace are continuously cleaned by washing the ashes with water, mechanically rubbing the surfaces of the ash a each other into slurry 1, and then subjecting the slurry 1 the solid/liquid separation process (2) to transfer salts to the water side (d) and remove the salts. The solid content (c) is melted at the melting furnace 4 into a molten solid content (g). The dust scattered in the exhaust gas (f) from the furnace 4 is captured 5 and mixed with water so that the dust is cleaned and makes into slurry 8. After that, the slurry (8) is subjected to the solid/liquid separation process 9 and the salts are transferred to the water side (m) and removed. Thus the solid content (p) enriched with the heavy metal is obtained and the exhaust gas (f) is captured by a dust collector after adding a neutralizing agent to the exhaust gas (f). The solid content is melted at the melting furnace 4, preferably in a reductive atmosphere.

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、飛灰の処理方法に
係り、特に、一般廃棄物や産業廃棄物の焼却炉から発生
する飛灰、又は該飛灰を溶融する灰溶融炉、ガス化溶融
炉から発生する溶融飛灰を処理する灰の処理方法に関す
る。
TECHNICAL FIELD The present invention relates to a method for treating fly ash, and more particularly, to fly ash generated from an incinerator for general waste or industrial waste, or an ash melting furnace for melting the fly ash, and gasification. The present invention relates to a method for treating ash for treating molten fly ash generated from a melting furnace.

【0002】[0002]

【従来の技術】一般に、都市ごみ、産業廃棄物は焼却処
理され、それにより容積が焼却前に比べて1/20〜1
/30に減容できるが、焼却処理で発生する飛灰は、重
金属(特に、亜鉛、鉛、銅)を多く含む。そのため、そ
の無害化対策として、溶融固化、焼成処理、セメ
ント固化、薬剤処理、酸、その他の溶媒抽出による
方法、で処理することが法規制されている。これらの処
理のうち、溶融固化は、概ね1200℃以上の高温条件
下で焼却灰、飛灰を溶融固化するため、ダイオキシン類
の分解と灰の状態から更に1/2程度の減容が図られ、
溶融固化物はスラグとして建設資材等に有効利用でき、
循環型社会形成に向けて適した技術といえる。しかし、
溶融時に発生する溶融飛灰中の重金属は、更に濃縮さ
せ、無害化処理が必要となる。現在、焼却炉で発生する
飛灰と溶融炉で発生する溶融飛灰は、無害化処理後はほ
とんどのケースは、最終処分場で処分されている。前記
飛灰及び溶融飛灰へは重金属は比較的多く移行するが、
これを非鉄製練会社で山元還元を行うには濃度が低い。
2. Description of the Related Art Generally, municipal waste and industrial waste are incinerated so that the volume thereof is 1/20 to 1 as compared with that before incineration.
Although the volume can be reduced to / 30, the fly ash generated by incineration contains a large amount of heavy metals (particularly zinc, lead and copper). Therefore, as a detoxification measure, it is legally regulated to perform treatment by melt solidification, baking treatment, cement solidification, chemical treatment, acid, or other solvent extraction method. Of these treatments, the melting and solidification melts and solidifies the incineration ash and fly ash under high temperature conditions of 1200 ° C or higher, so the volume of dioxins is decomposed and the volume of ash is further reduced by about 1/2. ,
The molten solidified material can be effectively used as construction materials such as slag,
It can be said that this technology is suitable for creating a recycling-based society. But,
The heavy metal in the molten fly ash generated during melting needs to be further concentrated and detoxified. Currently, fly ash generated in the incinerator and molten fly ash generated in the melting furnace are disposed of at the final disposal site in most cases after detoxification treatment. Although relatively large amounts of heavy metals migrate to the fly ash and molten fly ash,
The concentration of this is low for Yamamoto reduction in a non-ferrous kneading company.

【0003】表1に、一般廃棄物焼却炉の主灰と飛灰の
成分組成の一例を示す。
Table 1 shows an example of the composition of the main ash and fly ash of a general waste incinerator.

【表1】 [Table 1]

【0004】また、溶融飛灰についての組成分布の一例
を表2に示す。
Table 2 shows an example of the composition distribution of molten fly ash.

【表2】 山元還元のためには、重金属濃度が数十%程度あること
が望ましいし、灰中の塩化物イオン濃度を下げないと、
山元還元側の設備の腐蝕等の問題が生じる恐れがある。
[Table 2] For the reduction of Yamamoto, it is desirable that the concentration of heavy metals be about several tens of percent, and unless the concentration of chloride ions in ash is reduced.
There may be problems such as corrosion of equipment on the Yamamoto reduction side.

【0005】[0005]

【発明が解決しようとする課題】本発明は、上記従来技
術に鑑み、飛灰を溶融する溶融炉から排出する排ガス中
の固形分の塩化物イオン濃度を下げ、重金属濃度を上げ
て非鉄製練会社で山元還元して回収できる灰の処理方法
を提供することを課題とする。
DISCLOSURE OF THE INVENTION In view of the above-mentioned prior art, the present invention reduces the concentration of chloride ions in the solid content of the exhaust gas discharged from the melting furnace for melting fly ash and increases the concentration of heavy metals to achieve non-ferrous kneading. It is an object to provide a method for treating ash that can be returned by Yamamoto at the company and collected.

【0006】[0006]

【課題を解決するための手段】上記課題を解決するため
に、本発明では、焼却炉から発生する飛灰及び/又は溶
融炉から発生する溶融飛灰を、水と混合して機械的に灰
表面をこすり合わせて連続洗浄、スラリー化した後、固
液分離して塩類を水側に移行して除去し、固形分は溶融
炉で溶融して溶融固形物とし、該溶融炉の排ガス中に飛
散するダストは捕集して、水と混合して前記と同様に洗
浄、スラリー化した後、固液分離して塩類を水側に移行
して除去すると共に、重金属分の富化した固形分を得る
ことを特徴とする灰の処理方法としたものである。この
ときの洗浄は、単なる撹拌では十分塩類が水側に溶解せ
ず、十分溶解させるには大量の水と多くの撹拌時間を要
する。このため、本発明ではスラリー化したものを機械
的に灰表面をこすり合わせ、連続処理することで洗浄時
間の短縮と水の節約をはかった。
In order to solve the above problems, in the present invention, fly ash generated from an incinerator and / or molten fly ash generated from a melting furnace is mixed with water to mechanically remove ash. After continuous cleaning by rubbing the surface and making it into a slurry, solid-liquid separation is performed to remove salts by moving to the water side, and the solid content is melted in a melting furnace into a molten solid, which is then added to the exhaust gas of the melting furnace. The scattered dust is collected, mixed with water, washed and slurried in the same manner as described above, and then solid-liquid separated to move salts to the water side for removal, and solid contents enriched with heavy metals. The method of treating ash is characterized in that The washing at this time does not sufficiently dissolve the salts on the water side by simple stirring, and a large amount of water and a long stirring time are required for sufficient dissolution. Therefore, in the present invention, the slurry was mechanically rubbed against the ash surface and continuously treated to shorten the cleaning time and save water.

【0007】また、本発明では、焼却炉から発生する飛
灰及び/又は溶融炉から発生する溶融飛灰を、水と混合
して機械的に灰表面をこすり合わせて連続洗浄、スラリ
ー化した後、固液分離して塩類を水側に移行して除去
し、固形分は溶融炉で溶融して溶融固形物とし、該溶融
炉から発生する排ガス中のばいじんをバグフィルタで捕
捉して重金属分の富化した固形分を得ると共に、該バグ
フィルタからの排ガスに中和剤(消石灰等)を加えて集
じん装置(バグフィルタ等)で捕捉することを特徴とす
る灰の処理方法としたものである。前記灰の処理方法に
おいて、固形物の溶融炉での溶融は、還元雰囲気で行う
のがよく、前記飛灰又は溶融飛灰は、焼却炉又は溶融炉
から発生する排ガス中のばいじんをバグフィルタで捕捉
したものであり、該バグフィルタから排出する排ガス
は、中和剤を加えてさらに集じん装置で浄化することが
できる。
In the present invention, the fly ash generated from the incinerator and / or the molten fly ash generated from the melting furnace is mixed with water, and the ash surface is mechanically rubbed to continuously wash and slurry. , Solid-liquid separation to remove salts by moving to the water side, the solid content is melted in a melting furnace to a molten solid matter, and the dust in the exhaust gas generated from the melting furnace is captured by a bag filter to remove heavy metal content. A method for treating ash characterized by obtaining a solid content enriched with, and adding a neutralizing agent (slaked lime etc.) to the exhaust gas from the bag filter and capturing it with a dust collector (bug filter etc.) Is. In the method for treating ash, melting of solid matter in a melting furnace is preferably performed in a reducing atmosphere, and the fly ash or molten fly ash is a bag filter for dust in exhaust gas generated from an incinerator or a melting furnace. The exhaust gas that is captured and discharged from the bag filter can be further purified by a dust collector by adding a neutralizing agent.

【0008】[0008]

【発明の実施の形態】次に、本発明を詳細に説明する。
本発明では、焼却炉から発生する飛灰及び/又は溶融炉
から発生する溶融飛灰を、水と混合して洗浄、スラリー
化した後、固液分離を行って塩類を水側に移行させ、残
った固形分のみを溶融の対象としている。これにより、
灰中の高濃度成分である塩化物イオン、アルカリ金属
(ナトリウム、カリウム)を水に溶出すると共に、相対
的に重金属濃度を上げることができる。塩化物イオン濃
度の減少は、溶融炉での溶融時の発生塩類によるダスト
の閉塞防止の点でも効果がある。アルカリ金属濃度の低
減は、固形分を溶融する溶融炉の型式が電気抵抗炉の場
合、溶融処理中にアルカリ金属塩が炉内の上部に形成さ
れ、これが電気伝導性が良いために安定運転に支障があ
るが、そのためにも好都合である。
BEST MODE FOR CARRYING OUT THE INVENTION Next, the present invention will be described in detail.
In the present invention, the fly ash generated from the incinerator and / or the molten fly ash generated from the melting furnace is mixed with water to be washed and slurried, and then solid-liquid separation is performed to move salts to the water side, Only the remaining solid content is targeted for melting. This allows
Chloride ions and alkali metals (sodium and potassium), which are high-concentration components in ash, can be eluted into water and the concentration of heavy metals can be relatively increased. The reduction of chloride ion concentration is also effective in preventing dust clogging due to salts generated during melting in the melting furnace. When the type of the melting furnace that melts solids is an electric resistance furnace, the alkali metal concentration is reduced by forming an alkali metal salt in the upper part of the furnace during the melting process. There are obstacles, but it is convenient for that.

【0009】次に、固液分離して残った固形分を溶融炉
で溶融するが、溶融炉は、炭素源の投入や、炉内の溶融
スラグ層の上に灰のカバリング層を形成させて、炉内を
還元雰囲気として溶融するのが好ましい。還元雰囲気で
は、高温に加熱すると還元され易くて、比較的沸点の低
い亜鉛、鉛、カドミウム等は金属蒸気に変化して炉内に
揮散し、炉を出た段階で酸化される。これはウェルツ法
(ウェルツ法では還元剤としてコークスを用いている)
にみられる還元揮発法として実績のある技術である。特
に、スラリー洗浄によって塩化物イオンが多く除かれて
いるため、固形分中の重金属が、塩化物になりにくくな
り、塩素化による揮散推進という点ではスラリー洗浄で
は不利になるが、この還元雰囲気による重金属飛散はこ
の不利を補填するものである。また、溶融炉は、構造上
物理的飛散物量が少ない構造とし、溶融物は極力スラグ
化することが好ましい。
Next, the solid content remaining after the solid-liquid separation is melted in a melting furnace. In the melting furnace, a carbon source is charged and an ash covering layer is formed on the molten slag layer in the furnace. It is preferable to melt in a furnace as a reducing atmosphere. In a reducing atmosphere, when heated to a high temperature, it is easily reduced, and zinc, lead, cadmium, etc., which have a relatively low boiling point, are converted into metal vapor and volatilized in the furnace, and are oxidized at the stage of leaving the furnace. This is the Welts method (in the Welts method, coke is used as a reducing agent)
It is a technology that has a proven track record as a reduction volatilization method found in. In particular, since a large amount of chloride ions are removed by slurry cleaning, heavy metals in the solid content are less likely to become chloride, which is disadvantageous in slurry cleaning in terms of promotion of volatilization by chlorination. Heavy metal scattering compensates for this disadvantage. Further, it is preferable that the melting furnace has a structure in which the amount of physically scattered matter is small, and the molten matter is slagged as much as possible.

【0010】溶融炉から発生するダストは、捕集してさ
らに水に混合して洗浄、スラリー化した後、固液分離し
て塩類を水側に移行させる。これにより、灰中の塩化物
イオン濃度をさらに低減させ、相対的に重金属濃度を上
昇させることができる。溶融方式や灰の性状により、バ
グフィルタ1段でかつ中和剤(消石灰等)の添加なしで
も、バグフィルタ処理後の排ガス中の酸性物質(HCl
等)濃度を低くおさえられる場合に適している。例え
ば、溶融炉が電気抵抗炉の場合、バグフィルタでばいじ
んを捕捉以降の排ガス中の酸性物質濃度がおさえられる
傾向があり、こうした設備では本方式を採用し易い。消
石灰添加をしてしまうと、未反応分は水に溶解しにく
く、洗浄しても固形分側に残ってしまう。製錬会社側で
は鉛を分離する場合に、硫酸鉛で固形分として分離する
ケースが多く、未反応消石灰のカルシウムも硫酸カルシ
ウムを形成するので、硫酸鉛との分離が難しくなり、好
ましくない。
Dust generated from the melting furnace is collected, further mixed with water, washed and slurried, and then solid-liquid separated to move salts to the water side. Thereby, the chloride ion concentration in the ash can be further reduced, and the heavy metal concentration can be relatively increased. Depending on the melting method and the properties of ash, acidic substances (HCl
Etc.) Suitable when the concentration can be kept low. For example, when the melting furnace is an electric resistance furnace, the concentration of acidic substances in the exhaust gas after trapping soot and dust with a bag filter tends to be suppressed, and this system is easily adopted in such equipment. If slaked lime is added, the unreacted component is difficult to dissolve in water and remains on the solid content side even if washed. On the smelting company side, when lead is separated, it is often the case that lead sulfate separates it as a solid content, and calcium in unreacted slaked lime also forms calcium sulfate, which is difficult to separate from lead sulfate, which is not preferable.

【0011】これらの一連の操作により、灰中の塩化物
イオン濃度を低減できると共に、重金属濃度を数十%ま
で上昇でき、非鉄製練会社へ山元還元できる固形物を得
ることができる。また、灰を水を加えて洗浄、スラリー
化するのは、塩類除去が目的であるため、固形分を溶融
する際、溶融炉から発生する排ガス中のばいじんを1段
目のバグフィルタで捕捉し、さらに、排出するガスに中
和剤を加えて中和して集じん装置、例えば2段目のバグ
フィルタで浄化することで、灰のスラリー化洗浄の代用
とすることができる。
By a series of these operations, the concentration of chloride ions in the ash can be reduced, the concentration of heavy metals can be increased to several tens of percent, and a solid product that can be reduced to a non-ferrous smelting company can be obtained. Also, the purpose of washing and slurrying ash by adding water is to remove salts, so when melting solids, the soot and dust in the exhaust gas generated from the melting furnace is captured by the first-stage bag filter. Further, by adding a neutralizing agent to the discharged gas and neutralizing it to purify it with a dust collecting device, for example, a second stage bag filter, it is possible to substitute for ash slurry cleaning.

【0012】次に、本発明を、図1及び図2に示す本発
明のフロー構成図を用いて説明する。図1において、焼
却灰や溶融炉で発生した灰aは、洗浄装置1で洗浄す
る。洗浄装置1の構造は、ロータ表面の突起物の回転と
それと逆方向にシェルを回転させることによって灰の表
面付着物を除去し、塩類の水側への溶出を促す構造のも
のである。この洗浄装置1で灰と水とが混ってスラリー
bとなり、脱水装置2に導入される。脱水装置2は、遠
心分離機が一般的であり、固形分cと分離水dに分けら
れる。分離水dは、水処理装置6で凝集洗殿法等で浄化
され、浄化後放流eされる。固形分cは、乾燥装置3で
乾燥後、溶融炉4で溶融される。溶融炉4から発生する
排ガスfは、集じん装置5にてばいじんjを捕捉する。
浄化した排ガスは、大気iに放出する。
Next, the present invention will be described with reference to flow charts of the present invention shown in FIGS. In FIG. 1, the incineration ash and the ash a generated in the melting furnace are cleaned by the cleaning device 1. The structure of the cleaning device 1 is such that the protrusions on the rotor surface are rotated and the shell is rotated in the opposite direction to remove surface deposits of ash and promote elution of salts to the water side. Ash and water are mixed in the cleaning device 1 to form a slurry b, which is introduced into the dehydrator 2. The dehydrator 2 is generally a centrifugal separator and is divided into a solid content c and separated water d. The separated water d is purified by the coagulation washing method or the like in the water treatment device 6, and is discharged after purification. The solid content c is dried in the drying device 3 and then melted in the melting furnace 4. The exhaust gas f generated from the melting furnace 4 captures the soot and dust j in the dust collector 5.
The purified exhaust gas is released to the atmosphere i.

【0013】ばいじんjは、洗浄装置8でスラリーk化
し、水に溶け易い塩類は、脱水装置9で分離水m側に移
行される。固形分pは、重金属が濃縮されており、製練
会社で山元還元を行う。なお、製練会社に洗浄装置8、
脱水装置9を設置し、ばいじんjの状態で引渡すことも
できる。図2は、本発明の処理方法の別のフロー構成図
であり、図2では、図1の集じん装置5が、1段目のバ
グフィルタ10と、2段目のバグフィルタ11からな
り、1段目のバグフィルタで捕捉されるばいじんjは、
酸性物質及びその除去のための消石灰を含まず、そのま
ま製練会社で山元還元を行うことができる。2段目のバ
グフィルタからは中和灰Rが発生する。
Soot and dust j is made into a slurry k in the cleaning device 8, and salts easily soluble in water are transferred to the separated water m side by the dehydrating device 9. Heavy metal is concentrated in the solid content p, and Yamamoto reduction is performed by a kneading company. In addition, the smelting company has a cleaning device 8,
It is also possible to install the dehydrator 9 and deliver it in the state of dust j. FIG. 2 is another flow configuration diagram of the processing method of the present invention. In FIG. 2, the dust collecting apparatus 5 of FIG. 1 includes a first stage bag filter 10 and a second stage bag filter 11. The soot and dust j captured by the first stage bug filter is
Yamamoto reduction can be carried out as it is at a smelting company without containing acidic substances and slaked lime for removing them. Neutralized ash R is generated from the second-stage bag filter.

【0014】[0014]

【実施例】以下、本発明を実施例により具体的に説明す
る。 実施例1 図1のフロー構成図に従って、ストーカ炉の飛灰を処理
した飛灰処理試験結果を表3に示す。この処理試験にお
ける水の使用量は、図1の洗浄装置1と脱水装置2で飛
灰質量の5倍、洗浄装置8と脱水装置9で飛灰質量の5
倍の水を使用した。溶融炉4は電気抵抗炉である。
EXAMPLES The present invention will be specifically described below with reference to examples. Example 1 Table 3 shows the fly ash treatment test results obtained by treating the fly ash of the stoker furnace according to the flow diagram of FIG. The amount of water used in this treatment test was 5 times the fly ash mass in the cleaning device 1 and the dehydrating device 2 in FIG. 1, and 5 times the fly ash mass in the cleaning device 8 and the dehydrating device 9.
Double water was used. The melting furnace 4 is an electric resistance furnace.

【0015】[0015]

【表3】 表3により、重金属(特にZn)濃度が高く、また、山
元還元の阻害となる塩化物イオン濃度が、大幅に減少し
ていることが確認できた。
[Table 3] From Table 3, it was confirmed that the concentration of heavy metals (particularly Zn) was high, and that the concentration of chloride ions, which hindered the Yamamoto reduction, was significantly reduced.

【0016】[0016]

【発明の効果】本発明によれば、焼却炉から発生する飛
灰と溶融炉から発生する溶融飛灰を最終処理場に処理す
ることなく、含有する有用な重金属類を濃縮して回収
し、資源化することができた。
According to the present invention, useful heavy metals contained therein are concentrated and recovered without treating fly ash generated from an incinerator and molten fly ash generated from a melting furnace in a final treatment plant, It was possible to recycle it.

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

【図1】本発明の灰の処理方法の一例を示すフロー構成
図。
FIG. 1 is a flow configuration diagram showing an example of a method for treating ash according to the present invention.

【図2】本発明の灰の処理方法の別の例を示すフロー構
成図。
FIG. 2 is a flow configuration diagram showing another example of the method for treating ash according to the present invention.

【符号の説明】[Explanation of symbols]

1:洗浄装置、2:脱水装置、3:乾燥装置、4:溶融
炉、5:集じん装置、6:水処理装置、7:スラグ製造
装置、8:洗浄装置、9:脱水装置、10:1段目バグ
フィルタ、11:2段目バグフィルタ、
1: Washing device, 2: Dehydrating device, 3: Drying device, 4: Melting furnace, 5: Dust collector, 6: Water treatment device, 7: Slag manufacturing device, 8: Washing device, 9: Dehydrating device, 10: 1st stage bug filter, 11: 2nd stage bug filter,

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) F27D 17/00 105 B09B 3/00 303L 5/00 N (72)発明者 津田 精一 東京都大田区羽田旭町11番1号 株式会社 荏原製作所内 Fターム(参考) 3K061 ND03 4D004 AA37 BA05 CA29 CA34 CA40 CC03 4D056 AB07 AC22 BA03 CA18 4K056 AA00 AA05 CA20 DB07 DB26 DB27 ─────────────────────────────────────────────────── ─── Continuation of front page (51) Int.Cl. 7 Identification code FI theme code (reference) F27D 17/00 105 B09B 3/00 303L 5/00 N (72) Inventor Seiichi Tsuda Haneda, Ota-ku, Tokyo 11-1-1 Asahimachi F-term in EBARA CORPORATION (reference) 3K061 ND03 4D004 AA37 BA05 CA29 CA34 CA40 CC03 4D056 AB07 AC22 BA03 CA18 4K056 AA00 AA05 CA20 DB07 DB26 DB27

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 焼却炉から発生する飛灰及び/又は溶融
炉から発生する溶融飛灰を、水と混合して機械的に灰表
面をこすり合わせて連続洗浄、スラリー化した後、固液
分離して塩類を水側に移行して除去し、固形分は溶融炉
で溶融して溶融固形物とし、該溶融炉の排ガス中に飛散
するダストは捕集して、水と混合して機械的に灰表面を
こすり合わせて連続洗浄、スラリー化した後、固液分離
して塩類を水側に移行して除去すると共に、重金属分の
富化した固形分を得ることを特徴とする灰の処理方法。
1. Fly ash generated from an incinerator and / or molten fly ash generated from a melting furnace is mixed with water and mechanically rubbed on the ash surface to continuously wash and form a slurry, and then solid-liquid separation. Then, the salts are transferred to the water side to be removed, and the solid content is melted in a melting furnace to form a molten solid matter, and the dust scattered in the exhaust gas of the melting furnace is collected and mixed with water to mechanically Rubbing the ash surface continuously to make it into a slurry, and after making it into a slurry, solid-liquid separation is performed to remove salts by moving them to the water side, and ash treatment characterized by obtaining a solid content enriched in heavy metals. Method.
【請求項2】 焼却炉から発生する飛灰及び/又は溶融
炉から発生する溶融飛灰を、水と混合して機械的に灰表
面をこすり合わせて連続洗浄、スラリー化した後、固液
分離して塩類を水側に移行して除去し、固形分は溶融炉
で溶融して溶融固形物とし、該溶融炉から発生する排ガ
ス中のばいじんをバグフィルタで捕捉して重金属分の富
化した固形分を得ると共に、該バグフィルタからの排ガ
スに中和剤を加えて集じん装置で捕捉することを特徴と
する灰の処理方法。
2. Fly ash generated from an incinerator and / or molten fly ash generated from a melting furnace are mixed with water and mechanically rubbed on the ash surface to continuously wash and form a slurry, and then solid-liquid separation. Then, the salts are transferred to the water side and removed, and the solid content is melted in a melting furnace to form a molten solid matter, and the dust in the exhaust gas generated from the melting furnace is captured by a bag filter to enrich the heavy metal content. A method for treating ash, which comprises obtaining a solid content and adding a neutralizing agent to the exhaust gas from the bag filter to capture the solid content with a dust collector.
【請求項3】 前記固形物の溶融炉での溶融は、還元雰
囲気で行うことを特徴とする請求項1又は2記載の灰の
処理方法。
3. The method for treating ash according to claim 1, wherein the solid material is melted in a melting furnace in a reducing atmosphere.
【請求項4】 前記飛灰又は溶融飛灰は、焼却炉又は溶
融炉から発生する排ガスに中和剤を添加する前に集じん
装置で捕集し、該捕集物を溶融処理することを特徴とす
る請求項1、2又は3記載の灰の処理方法。
4. The fly ash or the molten fly ash is collected by a dust collector before the neutralizing agent is added to the exhaust gas generated from the incinerator or the melting furnace, and the collected matter is melt-treated. 4. The method for treating ash according to claim 1, 2 or 3.
JP2001203080A 2001-07-04 2001-07-04 Ash processing method Expired - Fee Related JP3627923B2 (en)

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Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
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JP3627923B2 JP3627923B2 (en) 2005-03-09

Family

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Country Link
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2017148720A (en) * 2016-02-24 2017-08-31 太平洋セメント株式会社 Processing device and processing method for chlorine-containing dust

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2017148720A (en) * 2016-02-24 2017-08-31 太平洋セメント株式会社 Processing device and processing method for chlorine-containing dust

Also Published As

Publication number Publication date
JP3627923B2 (en) 2005-03-09

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