JPH06226238A - Treatment of fly ash - Google Patents

Treatment of fly ash

Info

Publication number
JPH06226238A
JPH06226238A JP5018652A JP1865293A JPH06226238A JP H06226238 A JPH06226238 A JP H06226238A JP 5018652 A JP5018652 A JP 5018652A JP 1865293 A JP1865293 A JP 1865293A JP H06226238 A JPH06226238 A JP H06226238A
Authority
JP
Japan
Prior art keywords
fly ash
kneader
hydrogen
kneading
scrubber
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
JP5018652A
Other languages
Japanese (ja)
Other versions
JP2969126B2 (en
Inventor
Minoru Sawachi
實 澤地
Teruaki Fujikawa
輝昭 藤川
Tadao Murakawa
忠夫 村川
Akio Hirotsune
晃男 広常
Nobuhiro Maeda
信広 前田
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.)
Hitachi Zosen Corp
Original Assignee
Hitachi Zosen 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 Hitachi Zosen Corp filed Critical Hitachi Zosen Corp
Priority to JP5018652A priority Critical patent/JP2969126B2/en
Publication of JPH06226238A publication Critical patent/JPH06226238A/en
Application granted granted Critical
Publication of JP2969126B2 publication Critical patent/JP2969126B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Abstract

PURPOSE:To eliminate the danger of explosion by hydrogen by adding water and a pH control agent at need to fly ashes contg. harmful heavy metals and adding a heavy metal fixing agent thereto under kneading, then sucking and discharging gases contg. the hydrogen generated at the time of kneading to the outside of the system through a scrubber. CONSTITUTION:The fly ashes for one batch are fed from an EP ash hopper 1 by a feeder 3 and are injected together with the humidifying water from a liquid chemical injector 6 to a vibration type kneader 5 in order to subject the smoke gases captured by a refuse incineration furnace, etc., to a batch treatment for the purpose of preventing splashing of the cry ashes. The exciting force of the kneader 5 is made smaller so as to suppress the generation of the hydrogen at this time. Ventilation operation is carried out by opening ventilation dampers 16, 17 and actuating a blower 8 for ventilation after calculation of the fly ashes. Simultaneously, the vibration frequency of the kneader 5 is increased to enhance a kneading effect. The gases contg. the hydrogen generated at this time are discharged by the blower 8 to the outside of the system through the scrubber 7. The heavy metal fixing agent and flocculating agent are successively injected from the liquid chemical injector 6 and the pH control agent is injected at need.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】この発明は、都市ごみや産業廃棄
物などの焼却プラントから排ガスとともに排出される灰
分、たとえば電気集塵機(EP)で収集された灰分であ
るEP灰や、バグフィルタで捕集された灰分など(この
明細書全体を通してこの種の灰分を「飛灰」と称する)
の処理方法に関し、より詳細には、人体に有害な重金属
を含む飛灰を無害化する方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to ash discharged together with exhaust gas from an incinerator plant such as municipal waste and industrial waste, for example, EP ash which is ash collected by an electric dust collector (EP) and a bag filter. Collected ash, etc. (This kind of ash is referred to as "fly ash" throughout this specification)
More specifically, the present invention relates to a method for rendering fly ash containing a heavy metal harmful to a human body harmless.

【0002】[0002]

【従来の技術】この種の飛灰の中には人体に有害な重金
属類の塩化物が多量に含まれており、特にカドミウム、
鉛、水銀は、「有害な産業廃棄物に係わる判定基準を定
める総理府令」に定められた溶出基準値を越える傾向に
ある。
2. Description of the Related Art This kind of fly ash contains a large amount of chlorides of heavy metals harmful to the human body, especially cadmium,
Lead and mercury tend to exceed the elution standard values stipulated by the "Prime Ministerial Ordinance that sets criteria for determining hazardous industrial waste."

【0003】このような有害重金属を含む飛灰をそのま
ま埋立処理すると、雨水などにより飛灰中の重金属が溶
出し、土壌や河川を汚染し環境問題を引き起こすおそれ
があるので、最近ではセメント固化法や酸抽出法あるい
は炭酸塩化法などによって飛灰を処理する例が多くなっ
てきた。
If fly ash containing such harmful heavy metals is directly landfilled, heavy metals in the fly ash may be eluted by rainwater and the like, which may pollute soil and rivers and cause environmental problems. Increasingly, fly ash is treated by the acid extraction method or the carbonation method.

【0004】しかしながら、これらの処理方法では、添
加するセメントや抽出した重金属類を固定するための薬
剤のコストが多大なものとなり、さらにこの処理設備の
運転維持管理がはなはだ面倒であった。
However, in these treatment methods, the cost of the added cement and the chemicals for fixing the extracted heavy metals becomes great, and the operation and maintenance of the treatment equipment is very troublesome.

【0005】こうした状況から本発明者らは先に、飛灰
に所要量の水その他を添加して飛灰を振動式混合機を用
いて加湿混練しながら、キレート化剤さらに鉄塩を添加
する、飛灰の無害化処理方法を提案した(特開昭63−
278589号公報参照)。
Under these circumstances, the present inventors first added a chelating agent and an iron salt while adding a required amount of water or the like to fly ash and moistening and kneading the fly ash using a vibrating mixer. Proposed a method for detoxifying fly ash (JP-A-63-
278589).

【0006】この発明は、上記特許出願の発明の延長上
にあるものである。
The present invention is an extension of the invention of the above patent application.

【0007】[0007]

【発明が解決しようとする課題】一般に飛灰を無害化処
理する方法においては、飛灰を水に溶解するかまたは水
で加湿する工程が必要である。この時、飛灰中に含まれ
るAl、Zn、Pbなどの両性金属がやはり飛灰中に含
まれるアルカリ成分と反応し、水素の発生を伴う。さら
に、重金属の無害化を促進するためにアルカリを添加す
ると、上記反応が促進され、水素の発生が一層助長され
る。このため、重金属を無害化する装置内および屋内に
水素が滞留し、水素濃度が上昇して爆発を招く危険があ
る(水素−空気系で水素4〜75%が爆発濃度範囲であ
る)。
Generally, in the method of detoxifying fly ash, a step of dissolving fly ash in water or moistening with water is necessary. At this time, amphoteric metals such as Al, Zn, and Pb contained in the fly ash react with the alkaline components contained in the fly ash, and hydrogen is generated. Furthermore, when an alkali is added to promote the detoxification of heavy metals, the above reaction is promoted and the generation of hydrogen is further promoted. For this reason, there is a risk that hydrogen will accumulate in the apparatus for detoxifying heavy metals and indoors, leading to an increase in hydrogen concentration and an explosion (4 to 75% of hydrogen in the hydrogen-air system is in the explosion concentration range).

【0008】したがって、装置内あるいは屋内の水素濃
度を爆発の危険範囲から避けるための処置を講じること
が必要となる。
Therefore, it is necessary to take measures to avoid the hydrogen concentration in the device or indoors from the danger range of explosion.

【0009】この発明の目的は、上記のごとき実情に鑑
み、重金属の無害化反応に伴って発生する水素による爆
発の危険性のない飛灰の処理方法を提供することにあ
る。
In view of the above situation, an object of the present invention is to provide a method for treating fly ash which is free from the danger of explosion due to hydrogen generated by the detoxification reaction of heavy metals.

【0010】[0010]

【課題を解決するための手段】この発明は、上記目的を
達成すべく工夫されたものであり、より効果的な飛灰の
無害化処理方法を追及した結果、操作を敢えてバッチ式
とし、かつ、混練機内の水素含有ガスをスクラバーを経
てブロワで吸引して系外へ排出することにより、顕著な
効果がもたらされることを見出し、完成するに至ったも
のである。
The present invention has been devised to achieve the above object, and as a result of pursuing a more effective fly ash detoxification treatment method, the operation was intentionally made into a batch type, and The inventors have found that a remarkable effect is brought about by sucking the hydrogen-containing gas in the kneader through the scrubber with a blower and discharging it out of the system, and have completed the invention.

【0011】すなわち、この発明による飛灰の処理方法
は、混練機において、有害重金属を含んだ飛灰に水と必
要に応じてpH調整剤を加えて飛灰を加湿混練しなが
ら、この混練物に重金属固定剤と必要に応じてpH調整
剤を加え、当該混練機内で発生した水素を含むガスをス
クラバーを経てブロワで吸引して系外へ排出すること、
スクラバーの使用済み洗浄液を加湿用水として上記混練
機へ送ること、および、一連の操作をバッチ式で行うこ
とを特徴とするものである。
That is, the method for treating fly ash according to the present invention is a kneading machine in which a fly ash containing harmful heavy metals is added with water and, if necessary, a pH adjusting agent to knead the fly ash with humidification. A heavy metal fixing agent and, if necessary, a pH adjusting agent, and a gas containing hydrogen generated in the kneader is sucked with a blower through a scrubber and discharged out of the system.
It is characterized in that the used cleaning liquid of the scrubber is sent to the above kneader as humidifying water, and that a series of operations is performed in a batch system.

【0012】[0012]

【実施例】つぎに、この発明の処理方法を実施例により
具体的に説明する。
EXAMPLES Next, the processing method of the present invention will be specifically described by way of examples.

【0013】1) 処理装置の概要 飛灰処理装置は、図1に示すように、下端側部にホッパ
バイブレータ(2) を備えたEP灰ホッパ(1) と、ホッパ
(1) の下に横設されたEP灰切り出し用のフィーダ(3)
と、フィーダ(3) の終端部の下にシュート(4) を介して
設置された振動式混練機(5) と、混練機(5) に配設され
た薬液注入装置(6) と、混練機(5) から屋外に配設され
た換気ダクト(15)に設けられたスクラバー(7) と、スク
ラバー(7) の後流に設けられた換気用ブロワ(8) と、ブ
ロワ(8) から出る排気ガス中の可燃性ガス濃度を検知す
る可燃性ガス検知器(9) と、混練機(5) の下に設置され
た処理灰排出コンベヤ(10)とを主たる構成要素とするも
のである。
1) Outline of processing apparatus The fly ash processing apparatus is, as shown in FIG. 1, an EP ash hopper (1) having a hopper vibrator (2) on the lower end side, and a hopper.
(1) Feeder for EP ash cutting that is installed underneath (3)
And a vibrating kneader (5) installed via a chute (4) below the end of the feeder (3), and a chemical injection device (6) installed in the kneader (5). From the scrubber (7) installed in the ventilation duct (15) installed outdoors from the machine (5), the ventilation blower (8) installed in the downstream of the scrubber (7), and the blower (8). The main components are a combustible gas detector (9) that detects the concentration of combustible gas in the exhaust gas emitted, and a treated ash discharge conveyor (10) installed below the kneading machine (5). .

【0014】振動式混練機(5) は、横倒円胴状の混練機
本体(11)がスプリング(12)を介して基台(13)上に据え付
けられ、混練機本体(11)に複数のロッド(14)が内臓さ
れ、混練機本体(11)の両側部に加振機(18)が設けられた
ものである。加振機(18)の作動により、混練機本体(11)
内で飛灰は、複数のロッド(14)に叩かれるように混練さ
れる。
In the vibration type kneader (5), a kneading machine main body (11) in the shape of a horizontal cylinder is installed on a base (13) via a spring (12), and a plurality of kneading machine main bodies (11) are installed. The rod (14) is built in, and the shaker (18) is provided on both sides of the kneading machine body (11). By the operation of the shaker (18), the kneader body (11)
Fly ash is kneaded therein by being hit by a plurality of rods (14).

【0015】換気ダクト(15)はビニルホースより成り、
飛灰が付着しても混練機(5) の振動でこれを払い落とす
ようにしてある。
The ventilation duct (15) consists of a vinyl hose,
Even if fly ash adheres, it is wiped off by the vibration of the kneading machine (5).

【0016】2) 装置の運転 ごみ焼却炉から排出されるばい塵は電気集塵器で捕捉さ
れ、搬送装置にてEP灰ホッパ(1) に一時貯留される。
乾灰の飛散防止を目的としてバッチ処理を行うため、ホ
ッパ(1) から1バッチ分の飛灰をフィーダ(3) で切り出
しシュート(4)を介して振動式混練機(5) に供給すると
同時に、薬液注入装置(6) から加湿用の水を注入する。
この水は工業用水である。この時、混練機(5) には乾灰
を投入するので、水素対策のための換気ができない。そ
のため、水素発生を極力抑えるよう混練機(5) の加震力
を小さくする。具体的には混練機(5) の振動周波数を2
0〜30Hzとする。この操作条件により混練機内の水
素濃度を爆発限界(4%)以下に抑えることができる。
また、1バッチ分の飛灰を2回に別けてホッパ(1)から
切り出し、灰の加湿状態を均一化すると共に加湿用の水
も2回に分け、その内1回の水はスクラバー(7) の下部
水槽から排気ダクト(15)を経て混練機(5) に給水し、排
気ダクトの洗浄を行い、ダクトの閉塞を防止する。灰計
量時の加湿用水は、全加湿用水の50重量%以上とし、
飛灰の温度を下げることにより水素発生を抑える。
2) Operation of the device Soot dust discharged from the refuse incinerator is captured by the electrostatic precipitator and temporarily stored in the EP ash hopper (1) by the transfer device.
In order to perform batch processing for the purpose of preventing the scattering of dry ash, one batch of fly ash is cut out from the hopper (1) by the feeder (3) and supplied to the vibration type kneader (5) through the chute (4) at the same time. , Inject water for humidification from the chemical injection device (6).
This water is industrial water. At this time, since dry ash is put into the kneading machine (5), it is not possible to ventilate for hydrogen countermeasures. Therefore, the seismic force of the kneading machine (5) should be reduced to minimize hydrogen generation. Specifically, set the vibration frequency of the kneading machine (5) to 2
0 to 30 Hz. By these operating conditions, the hydrogen concentration in the kneader can be suppressed to below the explosion limit (4%).
In addition, fly ash for one batch is divided into two parts and cut out from the hopper (1) to make the humidification condition of the ash uniform and to divide the water for humidification into two parts, one of which is the scrubber (7 Water is supplied to the kneading machine (5) from the lower water tank of () through the exhaust duct (15), and the exhaust duct is washed to prevent the duct from being blocked. Humidification water at the time of ash measurement should be 50% by weight or more of all the humidification water,
Hydrogen generation is suppressed by lowering the fly ash temperature.

【0017】飛灰の計量後、換気ダンパ(16)(17)を開と
し、換気用ブロワ(8) を作動させて換気操作を行い、同
時に混練機(5) の振動周波数を50〜60Hzに上げ、
混練機の加震力を大きくして混練効果を高める。その結
果、混練機内で発生した水素を含むガスはスクラバー
(7) を経てブロワ(8) で屋外へ排出される。換気ダクト
(15)内のガス流速は3m/秒以下とする。薬液注入装置
(6) から重金属固定剤として液体キレートまたは水硫化
ソーダなどの硫化物、次いで凝集剤を順次注入し、水素
濃度が飽和に達し下がり始めた時点でpH調整剤として
苛性ソーダを注入する。この結果、混練機内の水素濃度
を平均化することができる。ブロワ(8) から出る排気ガ
ス中の水素ガス濃度は可燃性ガス検知器(9) により検知
される。当該検知器(9) から、設定濃度にて混練機を停
止する安全装置に信号が送られる。pH調整剤の添加量
は飛灰サンプルの自動滴定により予め設定されている。
After measuring the fly ash, the ventilation dampers (16) (17) are opened, the ventilation blower (8) is operated to perform the ventilation operation, and at the same time, the vibration frequency of the kneading machine (5) is set to 50 to 60 Hz. Raise,
Enhance the kneading effect by increasing the shaking force of the kneading machine. As a result, the gas containing hydrogen generated in the kneader is scrubbered.
After going through (7), it is discharged to the outside by the blower (8). Ventilation duct
The gas flow velocity in (15) shall be 3 m / sec or less. Chemical injection device
From (6), a liquid chelate or a sulfide such as sodium hydrosulfide, and then a coagulant are sequentially injected as a heavy metal fixing agent, and caustic soda is injected as a pH adjuster when the hydrogen concentration starts to reach saturation. As a result, the hydrogen concentration in the kneader can be averaged. The hydrogen gas concentration in the exhaust gas emitted from the blower (8) is detected by the combustible gas detector (9). A signal is sent from the detector (9) to a safety device that stops the kneader at the set concentration. The addition amount of the pH adjusting agent is preset by automatic titration of the fly ash sample.

【0018】苛性ソーダ注入後、薬液配管の洗浄を兼ね
て加湿用水の量の微調整を行い、次バッチの灰計量時に
苛性ソーダの混入を少なくして水素発生を抑える。
After the caustic soda is injected, the amount of the humidifying water is finely adjusted while also cleaning the chemical liquid pipe, and the caustic soda is less mixed when the ash of the next batch is measured to suppress the generation of hydrogen.

【0019】混練は10〜20分行われる。この混練に
より重金属固定剤の添加量を少なくし、処理灰の重金属
の安定化を達成できる。混練時の処理灰のpHは3〜1
0程度である。
The kneading is carried out for 10 to 20 minutes. By this kneading, the amount of the heavy metal fixing agent added can be reduced, and the stabilization of the heavy metal in the treated ash can be achieved. The pH of the treated ash during kneading is 3 to 1
It is about 0.

【0020】混練終了後、混練機底部の排出ゲートを開
け、処理灰を排出する。この時、混練機(5) を傾斜(前
傾)することにより排出作業が効率よく行われる。処理
灰は排出コンベヤ(10)によって灰ピットなどに排出され
る。10〜20分の排出操作で混練機内の飛灰がほぼ完
全に除去される。こうして一連の操作をバッチ式で行っ
た後、最終的に得られた飛灰スラッジは15〜50重量
%の含水率を有する。
After the kneading is completed, the discharge gate at the bottom of the kneader is opened to discharge the treated ash. At this time, the kneading machine (5) is tilted (tilted forward) to efficiently perform the discharging work. The treated ash is discharged to an ash pit or the like by the discharge conveyor (10). The fly ash in the kneading machine is almost completely removed by the discharging operation for 10 to 20 minutes. After performing a series of operations in a batch manner, the fly ash sludge finally obtained has a water content of 15 to 50% by weight.

【0021】排出が終わると次のバッチ工程に入るため
混練機の排出ゲートを洗浄した後閉じる。換気操作は次
バッチの運転が行われる直前まで行う。
When the discharge is completed, the discharge gate of the kneading machine is washed and then closed to start the next batch process. Ventilate until just before the next batch operation.

【0022】添付表1に原料灰および処理灰中の重金属
などの溶出試験結果を示す。
Attached Table 1 shows the results of the elution test of heavy metals and the like in the raw ash and the treated ash.

【0023】また、図2に運転中の飛灰処理装置内の水
素濃度変化を示す。
Further, FIG. 2 shows changes in the hydrogen concentration in the fly ash processing apparatus during operation.

【0024】[0024]

【表1】 [Table 1]

【0025】[0025]

【発明の効果】この発明による飛灰の処理方法は以上の
如く構成されているので、発生する水素による爆発の危
険性を伴うことなく、飛灰中の重金属を無害化処理する
ことができる。
Since the method for treating fly ash according to the present invention is constructed as described above, it is possible to detoxify heavy metals in fly ash without the risk of explosion due to hydrogen generated.

【0026】また、一連の操作をバッチ式で行うので、
重金属固定剤などの薬剤の添加量を調整したり、添加タ
イミングを抑制したり、混練機の加振力を制御すること
ができ、さらに混練機の換気に伴う微粉体(飛灰)の排
気中への飛散を極力抑えることができる。
Further, since a series of operations are performed in a batch system,
The amount of chemicals such as heavy metal fixatives can be adjusted, the timing of addition can be controlled, the vibration force of the kneader can be controlled, and during the exhaust of fine powder (fly ash) accompanying ventilation of the kneader. Can be suppressed as much as possible.

【0027】また、スクラバーの使用済み洗浄液を加湿
用水として上記混練機へ送るので、水をクローズド系で
使用することができると共に、換気ダクトを洗浄しその
詰まりトラブルを防止することができる。
Further, since the used cleaning liquid of the scrubber is sent to the above kneader as humidifying water, the water can be used in a closed system and the ventilation duct can be cleaned to prevent clogging trouble.

【0028】さらに、この発明の方法によれば、混練効
果が良く、混練時間を調整できるため、有害重金属と薬
剤との反応が効率良く行われ、無害化に必要な薬剤量が
他の処理法に比べ1/10以下ですみ、薬剤(水溶液)
以外の添加物を使用しないため処理灰の減容化効果が大
きく、飛灰を多量の水で溶解しないため、排水処理設備
が不要である。
Further, according to the method of the present invention, since the kneading effect is good and the kneading time can be adjusted, the reaction between the harmful heavy metal and the drug is efficiently carried out, and the amount of the drug required for detoxification is different from other treatment methods. 1/10 or less compared to, chemicals (aqueous solution)
Since no other additives are used, the effect of reducing the volume of treated ash is large, and fly ash is not dissolved in a large amount of water, so no wastewater treatment facility is required.

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

【図1】この発明の実施例を示すフローシートである。FIG. 1 is a flow sheet showing an embodiment of the present invention.

【図2】運転中の飛灰処理装置内の水素濃度変化を示す
グラフである。
FIG. 2 is a graph showing a change in hydrogen concentration in a fly ash processing apparatus during operation.

【符号の説明】[Explanation of symbols]

(5) …振動式混練機 (6) …薬液注入装置 (7) …スクラバー (8) …換気用ブロワ (9) …可燃性ガス検知器 (5)… Vibration type kneader (6)… Chemical liquid injector (7)… Scrubber (8)… Ventilation blower (9)… Combustible gas detector

フロントページの続き (72)発明者 村川 忠夫 大阪市此花区西九条5丁目3番28号 日立 造船株式会社内 (72)発明者 広常 晃男 大阪市此花区西九条5丁目3番28号 日立 造船株式会社内 (72)発明者 前田 信広 大阪市此花区西九条5丁目3番28号 日立 造船株式会社内Front page continuation (72) Inventor Tadao Murakawa 5-3-28 Nishikujo, Konohana-ku, Osaka City Hitachi Shipbuilding Co., Ltd. In-house (72) Inventor Nobuhiro Maeda 5-3-8 Nishi-Kujo, Konohana-ku, Osaka City Hitachi Shipbuilding Co., Ltd.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 混練機において、有害重金属を含んだ飛
灰に水と必要に応じてpH調整剤を加えて飛灰を加湿混
練しながら、この混練物に重金属固定剤と必要に応じて
pH調整剤を加え、当該混練機内で発生した水素を含む
ガスをスクラバーを経てブロワで吸引して系外へ排出す
ること、スクラバーの使用済み洗浄液を加湿用水として
上記混練機へ送ること、および、一連の操作をバッチ式
で行うことを特徴とする飛灰の処理方法。
1. In a kneading machine, water and a pH adjusting agent are added to fly ash containing harmful heavy metals to moisten and knead the fly ash, and a heavy metal fixing agent and a pH if necessary are added to the kneaded product. A regulator is added, a gas containing hydrogen generated in the kneader is sucked out of the system by a blower through a scrubber, and the used cleaning liquid of the scrubber is sent to the above kneader as humidifying water, and a series of A method for treating fly ash, characterized in that the above operation is performed in a batch system.
JP5018652A 1993-02-05 1993-02-05 Fly ash treatment method Expired - Fee Related JP2969126B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5018652A JP2969126B2 (en) 1993-02-05 1993-02-05 Fly ash treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5018652A JP2969126B2 (en) 1993-02-05 1993-02-05 Fly ash treatment method

Publications (2)

Publication Number Publication Date
JPH06226238A true JPH06226238A (en) 1994-08-16
JP2969126B2 JP2969126B2 (en) 1999-11-02

Family

ID=11977553

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5018652A Expired - Fee Related JP2969126B2 (en) 1993-02-05 1993-02-05 Fly ash treatment method

Country Status (1)

Country Link
JP (1) JP2969126B2 (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0409172A2 (en) * 1989-07-18 1991-01-23 Mitsubishi Kasei Corporation Process for dimerizing aromatic halogen compounds
JP2006021154A (en) * 2004-07-09 2006-01-26 Oji Paper Co Ltd Method for stabilizing combustion ash, stabilized combustion ash and method for manufacturing hydrogen
JP2006281150A (en) * 2005-04-04 2006-10-19 Takuma Co Ltd Refuse incinerator equipped with incineration ash reforming apparatus
JP2011098264A (en) * 2009-11-04 2011-05-19 Daido Steel Co Ltd Method for treating dust in exhaust gas
KR20200104457A (en) * 2019-02-26 2020-09-04 한국에너지기술연구원 System and Method for generating H2 using ash

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0409172A2 (en) * 1989-07-18 1991-01-23 Mitsubishi Kasei Corporation Process for dimerizing aromatic halogen compounds
JP2006021154A (en) * 2004-07-09 2006-01-26 Oji Paper Co Ltd Method for stabilizing combustion ash, stabilized combustion ash and method for manufacturing hydrogen
JP2006281150A (en) * 2005-04-04 2006-10-19 Takuma Co Ltd Refuse incinerator equipped with incineration ash reforming apparatus
JP2011098264A (en) * 2009-11-04 2011-05-19 Daido Steel Co Ltd Method for treating dust in exhaust gas
KR20200104457A (en) * 2019-02-26 2020-09-04 한국에너지기술연구원 System and Method for generating H2 using ash

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