JP2001311515A - Exhaust gas treatment method for ash melting furnace and system for the same - Google Patents

Exhaust gas treatment method for ash melting furnace and system for the same

Info

Publication number
JP2001311515A
JP2001311515A JP2000129513A JP2000129513A JP2001311515A JP 2001311515 A JP2001311515 A JP 2001311515A JP 2000129513 A JP2000129513 A JP 2000129513A JP 2000129513 A JP2000129513 A JP 2000129513A JP 2001311515 A JP2001311515 A JP 2001311515A
Authority
JP
Japan
Prior art keywords
exhaust gas
ash
melting furnace
incinerator
incineration
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
JP2000129513A
Other languages
Japanese (ja)
Other versions
JP3664941B2 (en
Inventor
Noriaki Senba
範明 仙波
Akira Noma
野間  彰
Susumu Nishikawa
進 西川
Yoshimasa Kawami
佳正 川見
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.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries Ltd
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Filing date
Publication date
Application filed by Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP2000129513A priority Critical patent/JP3664941B2/en
Publication of JP2001311515A publication Critical patent/JP2001311515A/en
Application granted granted Critical
Publication of JP3664941B2 publication Critical patent/JP3664941B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Abstract

PROBLEM TO BE SOLVED: To provide a treatment method for treating incinerated ash by using a melting furnace in which a large amount of harmful materials is not included in exhaust gas. SOLUTION: In the exhaust gas treatment method for the ash melting furnace and an exhaust gas treatment system, when a part of the exhaust gas burnt in an incinerator is supplied to a dust collector through a boiler and a desuperheater, slaked line is sprayed in the pre-stage of the dust collector, and then, the incinerated exhaust gas is separated from fly ash in the dust collector. The fly ash is mixed wit main ash directly exhausted from the incinerator, and then, the melting furnace is charged with the mixed ash. The exhaust gas from the melting furnace is sequentially supplied to a combustion chamber, the desuperheater and a dust remover, and then, supplied to a scrubber. After that, the exhaust gas is mixed with the incinerated exhaust gas and the mixed gas is treated by denitration catalyst.

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、灰溶融炉の排ガス
処理方法および処理システムに関し、さらに詳しくは、
下水汚泥、都市ごみ、産業廃棄物などの焼却灰及び事業
用火力発電プラント等の燃焼炉(焼却炉)から排出され
る焼却灰を、溶融炉を用いて処理する排ガス処理方法に
関するものである。
The present invention relates to an exhaust gas treatment method and a treatment system for an ash melting furnace.
The present invention relates to an exhaust gas treatment method for treating incineration ash such as sewage sludge, municipal solid waste, and industrial waste, and incineration ash discharged from a combustion furnace (incinerator) such as a thermal power plant for business use by using a melting furnace.

【0002】[0002]

【従来の技術】従来より、下水汚泥、都市ごみ及び産業
廃棄物などの焼却灰(粉体無機物)は、その資源化、減
容化及び無害化を図るために、焼却炉から排出された後
に、溶融炉によって溶融され、スラグや排ガス等として
排出されている。このような溶融炉を使用して炉本体内
で焼却灰を溶融するには、ごみ焼却炉から排出された焼
却灰を乾式灰出装置より磁選器、焼却灰サイロ及び灰供
給コンベヤ等の前処理系を経て、灰供給ホッパーから炉
本体内に投入し、投入された焼却灰を溶融する。この
際、焼却炉から排出される焼却灰(主灰)には、同様に
焼却炉から排出される飛灰を、飛灰サイロや計量器を経
て混合し、灰供給コンベアから供給する。
2. Description of the Related Art Conventionally, incinerated ash (powder inorganic material) such as sewage sludge, municipal solid waste and industrial waste has been discharged from an incinerator in order to reduce its resources, reduce its volume and render it harmless. Is melted by a melting furnace and discharged as slag, exhaust gas, and the like. In order to melt incineration ash in the furnace body using such a melting furnace, the incineration ash discharged from the refuse incinerator is pre-treated by a dry ash extraction device using a magnetic separator, incineration ash silo, ash supply conveyor, etc. After passing through the system, the ash is supplied from the ash supply hopper into the furnace body, and the supplied incineration ash is melted. At this time, fly ash similarly discharged from the incinerator is mixed with incinerated ash (main ash) discharged from the incinerator via a fly ash silo or a measuring instrument, and supplied from an ash supply conveyor.

【0003】溶融炉内で発生した溶融スラグや溶融メタ
ルは、出滓口から出滓樋を通ってスラグ出滓装置に排出
され、スラグコンベヤを介してスラグ排出系に導かれ、
種々の利用に供される。炉本体には、例えば主電極等が
配設され、炉本体の上部には窒素ガス発生装置から窒素
ガスが送給されるようになっている。ごみ焼却炉はバグ
フィルタを介して煙突に連通され、一方、溶融炉本体内
で発生した排ガスは出滓口を経て、バグフィルタ、湿式
洗煙塔および煙突等からなる排ガス処理系に導かれよう
になっている。
[0003] Molten slag and molten metal generated in the melting furnace are discharged from a slag port through a slag drain to a slag slag discharging apparatus, and guided to a slag discharge system via a slag conveyor.
Provided for various uses. For example, a main electrode and the like are provided in the furnace main body, and nitrogen gas is supplied from a nitrogen gas generator to an upper portion of the furnace main body. The refuse incinerator is connected to the chimney via a bag filter, while the exhaust gas generated in the melting furnace body is guided to an exhaust gas treatment system consisting of a bag filter, a wet smoke washing tower, a chimney, etc. through a slag port. It has become.

【0004】ところで、通常、灰溶融炉の排ガス中に
は、高濃度のダスト、塩化水素、硫黄酸化物や、一酸化
炭素、窒素酸化物、ダイオキシン類等の有害な有機塩素
化合物などが多く存在している。そして、溶融炉排ガス
の処理方法としては、特開平9−33027号には、溶
融炉において焼却炉の焼却灰と飛灰を共に処理する焼却
溶融設備、特開平9−276651号には、塩化水素等
の有害物を排ガス中から低コストで除去する焼却灰溶融
炉の排ガス処理装置が開示されている。しかしながら、
これら従来の排ガス処理装置では、ダスト除去もしくは
それに加えての酸性ガス、窒素酸化物の対策のみであ
り、上記のような多くの有害物質を総合的に処理できる
排ガス処理は未だ提案されていない。そして、従来の溶
融炉側の排ガス処理では、洗煙排水の処理が難しいとい
う問題や、特にダイオキシン類の有害物質が放出されて
しまうという大きな問題があった。
[0004] By the way, in the flue gas of an ash melting furnace, high concentrations of dust, hydrogen chloride, sulfur oxides, and harmful organic chlorine compounds such as carbon monoxide, nitrogen oxides, and dioxins are usually present. are doing. Japanese Patent Application Laid-Open No. 9-33027 discloses an incineration melting facility for processing both incineration ash and fly ash in an incinerator in a melting furnace. An exhaust gas treatment device for an incineration ash melting furnace for removing harmful substances such as harmful substances from exhaust gas at low cost is disclosed. However,
These conventional exhaust gas treatment apparatuses only take measures against dust removal or acid gas and nitrogen oxides in addition thereto, and exhaust gas treatment capable of comprehensively treating many harmful substances as described above has not yet been proposed. And, in the conventional exhaust gas treatment on the melting furnace side, there was a problem that it was difficult to treat the smoke washing wastewater, and a serious problem that harmful substances such as dioxins were released.

【0005】[0005]

【発明が解決しようとする課題】本発明者らは、上記問
題点に鑑み、灰溶融炉を含む排ガス処理システムについ
て、環境問題等を十分に踏まえた、より安全で確実なシ
ステムを構築するとともに、システム全体とした場合に
は、より効率的でエネルギー的にも有利な排ガス処理方
法を開発すべく、鋭意検討した。その結果、本発明者ら
は、ダスト除去のための集塵装置(バグフィルタ、電気
集塵器等)、酸性ガス除去のためのスクラバ、一酸化炭
素、ダイオキシン分解のための燃焼室、窒素酸化物分解
のための触媒装置(反応塔や触媒担持バグ)を総合的に
組み合わせ、溶融炉からの排ガスを処理する方法によっ
て、上記問題点が解決されることを見い出した。本発明
は、かかる見地より完成されたものである。
SUMMARY OF THE INVENTION In view of the above problems, the present inventors have constructed a safer and more reliable system for an exhaust gas treatment system including an ash melting furnace, which fully takes environmental issues into consideration. In the case of the whole system, we have studied diligently to develop a more efficient and energy-efficient exhaust gas treatment method. As a result, the present inventors have developed a dust collector (eg, a bag filter, an electric dust collector) for removing dust, a scrubber for removing acid gas, a combustion chamber for decomposing carbon monoxide and dioxin, and a nitrogen oxidizer. It has been found that the above problems can be solved by a method of treating exhaust gas from a melting furnace by comprehensively combining a catalyst device (reaction tower and catalyst carrying bug) for decomposing substances. The present invention has been completed from such a viewpoint.

【0006】[0006]

【課題を解決するための手段】すなわち、本発明は、焼
却炉で燃焼させた排ガスの一部を、ボイラおよび減温塔
を介して集塵装置に至らせる際に、該集塵装置の前段に
て消石灰を噴霧してから、該集塵装置にて焼却排ガスと
飛灰とに分離し、該飛灰を、焼却炉から直接排出される
焼却灰(主灰)と混合した後、溶融炉に投入する処理方
法であって、該溶融炉からの排ガスが燃焼室、減温塔、
除塵装置を順次経て、スクラバを介した後、該焼却排ガ
スと混合して脱硝触媒により処理されることを特徴とす
る灰溶融炉の排ガス処理方法を提供するものである。ま
た、本発明は、焼却炉で燃焼させた排ガスの一部を、ボ
イラおよび減温塔を介して集塵装置に至らせる際に、該
集塵装置の前段にて消石灰を噴霧してから、該集塵装置
にて焼却排ガスと飛灰とに分離し、該飛灰を、焼却炉か
ら直接排出される焼却灰(主灰)と混合した後、溶融炉
に投入する処理方法であって、該溶融炉からの排ガスが
燃焼室、減温塔、除塵装置を順次経た後、該焼却排ガス
と混合してからスクラバおよび脱硝触媒により処理され
ることを特徴とする灰溶融炉の排ガス処理方法を提供す
るものである。ここで、本発明の排ガス処理方法では、
前記スクラバより排出される洗煙排水を、前記減温塔の
いずれか1つへ噴霧する態様、あるいは、前記スクラバ
より排出される洗煙排水を、逆浸透膜に通してから前記
減温塔のいずれか1つへ噴霧する態様などが好適に挙げ
られる。
That is, the present invention is directed to a method in which a part of the exhaust gas burned in an incinerator is passed through a boiler and a cooling tower to a dust collecting apparatus, and is provided at a stage upstream of the dust collecting apparatus. After spraying slaked lime in the above, the exhaust gas is separated into incineration exhaust gas and fly ash by the dust collector, and the fly ash is mixed with incineration ash (main ash) discharged directly from the incinerator, and then melted. A treatment method, wherein the exhaust gas from the melting furnace is a combustion chamber, a cooling tower,
It is an object of the present invention to provide an exhaust gas treatment method for an ash melting furnace, wherein the exhaust gas is sequentially passed through a scrubber, mixed with the incineration exhaust gas, and treated by a denitration catalyst. Further, the present invention, when a part of the exhaust gas burned in the incinerator, to reach the dust collector through a boiler and a cooling tower, after spraying slaked lime in the preceding stage of the dust collector, A processing method in which the incinerator exhaust gas and fly ash are separated by the dust collector, and the fly ash is mixed with incineration ash (main ash) directly discharged from the incinerator, and then charged into a melting furnace, An exhaust gas treatment method for an ash melting furnace, wherein the exhaust gas from the melting furnace is sequentially passed through a combustion chamber, a cooling tower, and a dust removing device, mixed with the incineration exhaust gas, and then treated with a scrubber and a denitration catalyst. To provide. Here, in the exhaust gas treatment method of the present invention,
A mode in which the smoke washing wastewater discharged from the scrubber is sprayed to any one of the cooling towers, or the smoke washing wastewater discharged from the scrubber is passed through a reverse osmosis membrane, A mode of spraying to any one of them is preferably exemplified.

【0007】本発明の処理方法によれば、溶融炉の後段
の効果的な位置に燃焼室を設けること等により、ダイオ
キシン類の排出を有効に防止することができる。また燃
焼室の効果として、溶融炉内を還元雰囲気にしておくこ
とができ、これによって、炉内は低酸素ガス雰囲気とな
り重金属を外に排出し易くなる。この場合、溶融炉から
排出されるガスについては、一酸化炭素濃度が高くなっ
てしまうが、後段の燃焼室によって一酸化炭素濃度を低
く抑制することができる。さらに本発明を用いれば、焼
却炉からの排ガス処理に必要とされるランニングコスト
を、低く抑えることができる。
According to the treatment method of the present invention, the emission of dioxins can be effectively prevented by providing a combustion chamber at an effective position after the melting furnace. Further, as an effect of the combustion chamber, the inside of the melting furnace can be kept in a reducing atmosphere, whereby the inside of the furnace becomes a low oxygen gas atmosphere, and the heavy metals can be easily discharged to the outside. In this case, the concentration of carbon monoxide in the gas discharged from the melting furnace increases, but the concentration of carbon monoxide can be suppressed to a low level by the combustion chamber in the subsequent stage. Further, according to the present invention, the running cost required for treating exhaust gas from an incinerator can be kept low.

【0008】[0008]

【発明の実施の形態】以下、本発明を図示した実施の形
態に基づいて詳細に説明する。実施の形態(その1) 図1は、本発明に係る排ガス処理方法を実施するのに好
適な処理システムの一例を示す図である。本実施の形態
では、焼却炉1で燃焼させた排ガスの一部を、廃熱ボイ
ラ3および冷却用の減温塔4に導く。同じく焼却炉1か
ら排出される主灰については、そのまま溶融炉2に供給
される。上記減温塔4で冷却された排ガスは、集塵装置
であるバグフィルタ5に投入されるが、その直前にて、
消石灰が噴霧・供給される。この際、活性炭をさらに加
えることもできる。このような消石灰が噴霧された排ガ
スは、バグフィルタ5にて焼却排ガスと飛灰とに分離さ
れる。ここで、集塵装置としては、バグフィルタの他、
電気集塵器、サイクロンなどを用いることができる。そ
して、分離された飛灰成分については、焼却炉1から直
接排出される主灰と混合した後、溶融炉2に投入され
る。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Hereinafter, the present invention will be described in detail based on illustrated embodiments. Embodiment (No. 1) FIG. 1 is a diagram showing an example of a processing system suitable for performing an exhaust gas processing method according to the present invention. In the present embodiment, a part of the exhaust gas burned in the incinerator 1 is guided to the waste heat boiler 3 and the cooling temperature reducing tower 4. Similarly, the main ash discharged from the incinerator 1 is supplied to the melting furnace 2 as it is. The exhaust gas cooled in the cooling tower 4 is supplied to a bag filter 5 which is a dust collector.
Slaked lime is sprayed and supplied. At this time, activated carbon can be further added. The exhaust gas sprayed with such slaked lime is separated by the bag filter 5 into incineration exhaust gas and fly ash. Here, besides the bag filter,
An electric dust collector, a cyclone, or the like can be used. Then, the separated fly ash component is mixed with the main ash directly discharged from the incinerator 1 and then charged into the melting furnace 2.

【0009】溶融炉2では、通常の焼却炉の焼却によっ
て生じた主灰、および排ガス中に残った塵などの飛灰を
混合して、通常は灰供給ホッパから投入する。ホッパの
下部にはスクリューが設けられていて、そこから灰投入
口を経て溶融炉内に供給され、炉内は窒素雰囲気になっ
ている。炉内には、主灰と飛灰とが溶けた溶融スラグ層
があり、供給された灰もその上に堆積する。溶融スラグ
の温度は、通常約1600℃程度である。溶けた灰であ
るスラグは、出滓口から排出される。溶融炉として具体
的には、プラズマアーク式、アーク式、電気抵抗式、高
周波式等の電気式溶融炉、および、バーナ式、コークス
ベッド式等の燃料式溶融炉などが挙げられる。溶融炉
は、通常、有底円筒状に形成された炉本体を有してお
り、該炉本体下部側面には、溶融されたスラグ及び排ガ
スを抜き出す出滓口が設けられている。また、一般に溶
融炉内は内壁を定型耐火物であるレンガ等で囲ってお
り、その外側に水冷ジャケットを設けて、冷却してい
る。
In the melting furnace 2, main ash produced by incineration in a normal incinerator and fly ash such as dust remaining in exhaust gas are mixed and usually fed from an ash supply hopper. A screw is provided at the lower part of the hopper, from which it is supplied to the melting furnace through the ash inlet, and the furnace is in a nitrogen atmosphere. In the furnace, there is a molten slag layer in which main ash and fly ash are melted, and the supplied ash is also deposited thereon. The temperature of the molten slag is usually about 1600 ° C. The slag, which is the molten ash, is discharged from the slag port. Specific examples of the melting furnace include an electric melting furnace such as a plasma arc type, an arc type, an electric resistance type and a high frequency type, and a fuel type melting furnace such as a burner type and a coke bed type. The melting furnace usually has a furnace main body formed in a cylindrical shape with a bottom, and a slag port for extracting molten slag and exhaust gas is provided on a lower side surface of the furnace main body. In general, the inside of the melting furnace is surrounded by a brick or the like, which is a standard refractory, and a water cooling jacket is provided outside the inside to cool the inside.

【0010】溶融炉2からの排出される排ガスは、先ず
燃焼室6を通ってから、減温塔7に送られる。燃焼室6
には、燃焼空気ファンより空気が送給され、通常は高温
のエアーを導入する方式が用いられるが、燃焼用バーナ
が設けられていても良い。この燃焼室の作用によって、
溶融炉2から生じる排ガスのうち、一酸化炭素COや、
ダイオキシン類等の物質は燃焼分解される。そして減温
塔7では、排ガスをさらに後流に送って処理できるよう
に冷却が行われる。減温塔7(冷却塔)としては、冷却
空気の吹き込みによる空冷式、冷却水の噴霧による水冷
式などの装置を用いることができる。
The exhaust gas discharged from the melting furnace 2 first passes through a combustion chamber 6 and then is sent to a cooling tower 7. Combustion chamber 6
In this method, air is supplied from a combustion air fan and a method of introducing high-temperature air is usually used, but a combustion burner may be provided. By the action of this combustion chamber,
Among the exhaust gas generated from the melting furnace 2, carbon monoxide CO,
Substances such as dioxins are burned and decomposed. Then, in the cooling tower 7, cooling is performed so that the exhaust gas can be further sent downstream for processing. As the cooling tower 7 (cooling tower), an apparatus of an air cooling type by blowing cooling air or a water cooling type by spraying cooling water can be used.

【0011】減温塔7を経た排ガスは、除塵装置である
バグフィルタ8に導かれるが、その直前で消石灰や活性
炭が添加されても良い。バグフィルタ8ではダストが除
塵されて、排ガスと溶融飛灰とに分離され、溶融飛灰は
接続されている溶融飛灰処理装置等に送られる。除塵装
置としては、バグフィルタの他、除塵用サイクロン等を
用いることができる。
The exhaust gas that has passed through the cooling tower 7 is guided to a bag filter 8, which is a dust remover, and slaked lime or activated carbon may be added immediately before. In the bag filter 8, dust is removed and separated into exhaust gas and molten fly ash, and the molten fly ash is sent to a connected molten fly ash processing device or the like. As the dust removing device, besides the bag filter, a dust removing cyclone or the like can be used.

【0012】本実施の形態では、バグフィルタ8を経た
排ガスはスクラバ9に供給されて、酸性ガスはこのスク
ラバ9で吸収・除去され、清浄な排ガスとなる。このス
クラバ9からは浄化の際に、洗煙排水が排出される。そ
して、浄化された排ガスは、前記減温塔4の後流に配さ
れたバグフィルタ5から排出される焼却排ガスと混合す
る。混合された排ガスは、脱硝触媒10により脱硝処理
を行ってから系外に放出される。このように本実施の形
態によれば、溶融炉2から生じる排ガス中から、有害物
であるCOやダイオキシン類を極めて効果的なタイミン
グで燃焼分解させられるので、排ガスをより安全なもの
として放出することが可能となる。
In the present embodiment, the exhaust gas that has passed through the bag filter 8 is supplied to a scrubber 9, and the acid gas is absorbed and removed by the scrubber 9, resulting in a clean exhaust gas. From the scrubber 9, smoke cleaning wastewater is discharged during purification. The purified exhaust gas is mixed with the incineration exhaust gas discharged from the bag filter 5 disposed downstream of the cooling tower 4. The mixed exhaust gas is discharged out of the system after being subjected to a denitration treatment by the denitration catalyst 10. As described above, according to the present embodiment, harmful substances such as CO and dioxins can be burned and decomposed at extremely effective timing from the exhaust gas generated from the melting furnace 2, so that the exhaust gas is released as safer. It becomes possible.

【0013】実施の形態(その2) 図2は、本発明に係る排ガス処理方法を実施するのに好
適な他の処理システムの一例を示す図である。本実施の
形態では、上記実施の形態(その1)と同様に、焼却炉
1で燃焼させた排ガスの一部を、ボイラ3および減温塔
4を介して集塵装置(バグフィルタ5等)に至らせる際
に、バグフィルタ5の前段にて消石灰を噴霧する。そし
て、バグフィルタ5にて焼却排ガスと飛灰とに分離し、
この飛灰を、焼却炉1から直接排出される主灰と混合し
て、溶融炉2に投入する。溶融炉2からの排ガスは燃焼
室6、減温塔7、除塵装置(バグフィルタ8等)を順次
経る。これら装置での作用は実施の形態(その1)と同
じである。
Embodiment (No. 2) FIG. 2 is a diagram showing an example of another processing system suitable for carrying out the exhaust gas processing method according to the present invention. In the present embodiment, similarly to the above-described embodiment (part 1), a part of the exhaust gas burned in the incinerator 1 is passed through the boiler 3 and the cooling tower 4 to a dust collecting device (such as a bag filter 5). Is sprayed with slaked lime before the bag filter 5. Then, it is separated into incineration exhaust gas and fly ash by the bag filter 5,
This fly ash is mixed with the main ash discharged directly from the incinerator 1 and is put into the melting furnace 2. Exhaust gas from the melting furnace 2 sequentially passes through the combustion chamber 6, the cooling tower 7, and a dust removing device (eg, a bag filter 8). The operation of these devices is the same as that of the first embodiment.

【0014】本実施の形態では、除塵装置であるバグフ
ィルタ8からの排ガスについて、集塵装置(バグフィル
タ5)から排出される焼却排ガスと混合した後、スクラ
バ11に送られる。このスクラバ11にて、酸性ガスは
吸収・除去され、清浄な排ガスとなり、一方、浄化の際
の洗煙排水が排出される。この浄化された排ガスは、窒
素酸化物を分解するための脱硝触媒により処理される。
脱硝触媒を有する触媒装置としては、反応塔や触媒担持
バグ等を用いることができる。本実施の形態によれば、
スクラバは焼却炉からの焼却排ガス処理用のものと兼用
させることができ、効率的な処理が可能である。
In the present embodiment, the exhaust gas from the bag filter 8 which is a dust removing device is mixed with the incineration exhaust gas discharged from the dust collecting device (the bag filter 5) and then sent to the scrubber 11. In the scrubber 11, the acidic gas is absorbed and removed, and becomes a clean exhaust gas, while the smoke washing wastewater at the time of purification is discharged. This purified exhaust gas is treated by a denitration catalyst for decomposing nitrogen oxides.
As a catalyst device having a denitration catalyst, a reaction tower, a catalyst-carrying bug, or the like can be used. According to the present embodiment,
The scrubber can also be used for treating incineration exhaust gas from an incinerator, and can be treated efficiently.

【0015】実施の形態(その3) 図3および図4は、本発明に係る排ガス処理方法を実施
するのに好適な他の処理システムの例を示す図である。
図3および図4の形態においては、実施の形態(その
1)と同様に、焼却炉1で燃焼させた排ガスの一部を、
ボイラ3および減温塔4を介して集塵装置(バグフィル
タ5等)に至らせる際に、集塵装置の前段にて消石灰を
噴霧してから、集塵装置にて焼却排ガスと飛灰とに分離
し、この飛灰を、焼却炉1から直接排出される主灰と混
合した後、溶融炉に投入する。溶融炉2からの排ガスは
燃焼室6、減温塔7、除塵装置(バグフィルタ8等)を
順次経て、スクラバ9を介した後、前記焼却排ガスと混
合して脱硝触媒により処理される。ここで本実施の形態
では、スクラバ9から排出される洗煙排水を、前段の減
温塔4もしくは7へ噴霧して、冷却水として使用する。
つまり、出てくる洗煙排水を、そのまま排出するのでは
なく、例えば減温塔等で水若しくは空気を噴霧するのに
利用する。これによって、排ガス処理を実施する際に発
生する排水の量を減少させ、システムとした場合の無排
水化に近づけることができる。
Embodiment (Part 3) FIGS. 3 and 4 are diagrams showing examples of another processing system suitable for carrying out the exhaust gas processing method according to the present invention.
In the embodiment of FIGS. 3 and 4, a part of the exhaust gas burned in the incinerator 1 is similar to the first embodiment.
When the dust is collected through the boiler 3 and the cooling tower 4 to the dust collector (eg, the bag filter 5), slaked lime is sprayed before the dust collector, and then the incineration exhaust gas and fly ash are removed by the dust collector. This fly ash is mixed with the main ash discharged directly from the incinerator 1 and then put into a melting furnace. Exhaust gas from the melting furnace 2 passes through a combustion chamber 6, a cooling tower 7, a dust removing device (eg, a bag filter 8) sequentially, passes through a scrubber 9, is mixed with the incineration exhaust gas, and is treated by a denitration catalyst. Here, in the present embodiment, the smoke washing drainage discharged from the scrubber 9 is sprayed to the cooling tower 4 or 7 in the preceding stage and used as cooling water.
That is, the discharged smoke washing drainage is not used as it is, but is used for spraying water or air with a cooling tower or the like. As a result, the amount of wastewater generated when performing exhaust gas treatment can be reduced, and the system can be made to have no drainage.

【0016】一方、本実施の形態においては、系内に水
銀(Hg)が濃縮される可能性があるため、溶融炉の排
ガス処理で水銀を系外に排出する手段(活性炭噴霧、排
水からの水銀除去)が必要となる。一般に、鉛やカドミ
ウムなどと異なり、水銀はバグフィルタ等では回収でき
ずに、溶融炉内で飛散してしまう。このような水銀は沸
点が低く、溶融飛灰への吸着能が非常に低いので、例え
ば活性炭等を途中に用いなければ、実質的に回収するこ
とが困難である。よって、実施の形態(その1)のシス
テムに加えて洗煙排水を利用する場合には、運転の継続
と共に、系内部に水銀が蓄積(濃縮)してしまうことが
無いように、水銀を系外に除去することが必要である。
したがって、図3の形態のように洗煙排水を戻す場合に
は、活性炭を除塵装置(バグフィルタ8等)の前段で添
加することが必要となる。消石灰は、必要に応じて添加
することができる。
On the other hand, in this embodiment, since there is a possibility that mercury (Hg) may be concentrated in the system, means for discharging mercury to the outside of the system in the exhaust gas treatment of the melting furnace (activated charcoal spraying, Mercury removal) is required. Generally, unlike lead and cadmium, mercury cannot be collected by a bag filter or the like, but is scattered in a melting furnace. Since such mercury has a low boiling point and an extremely low adsorption ability to molten fly ash, it is difficult to substantially recover the mercury unless, for example, activated carbon or the like is used in the middle. Therefore, when using the smoke-washing wastewater in addition to the system of the first embodiment (part 1), the mercury is added to the system so that mercury does not accumulate (concentrate) inside the system as the operation continues. It is necessary to remove it outside.
Therefore, when returning the smoke washing wastewater as in the embodiment of FIG. 3, it is necessary to add the activated carbon before the dust remover (eg, the bag filter 8). Slaked lime can be added as needed.

【0017】また、図3のシステムは、洗煙排水をその
まま冷却剤として利用する態様であるが、図4のシステ
ムのように、洗煙排水を逆浸透膜12に通してから冷却
剤として利用する態様もある。図4の形態では、逆浸透
膜12によって上記水銀が系外に除去させるので、図3
の形態とは異なり、活性炭を除塵装置(バグフィルタ8
等)の前段で添加しなくとも良い。但し、必要であれば
消石灰と同様に、活性炭を添加することもできる。
The system shown in FIG. 3 uses the smoke washing wastewater as a coolant as it is. However, as in the system shown in FIG. 4, the smoke washing wastewater passes through the reverse osmosis membrane 12 and is used as a coolant. In some embodiments, In the embodiment of FIG. 4, the mercury is removed outside the system by the reverse osmosis membrane 12.
Activated carbon is different from the form of
Etc.) need not be added in the preceding stage. However, if necessary, activated carbon can be added in the same manner as slaked lime.

【0018】実施の形態(その4) 図5および図6は、本発明に係る排ガス処理方法を実施
するのに好適な他の処理システムの例を示す図である。
図5および図6の形態においては、実施の形態(その
2)と同様に、焼却炉1で燃焼させた排ガスの一部を、
集塵装置(バグフィルタ5等)の前段にて消石灰を噴霧
してから焼却排ガスと飛灰とに分離し、飛灰を焼却炉1
から直接排出される主灰と混合した後、溶融炉2に投入
する。溶融炉2からの排ガスは燃焼室6、減温塔7、除
塵装置8を順次経た後、前記焼却排ガスと混合してから
スクラバ11および脱硝触媒10により処理される。こ
こで本実施の形態では、上記実施の形態(その3)と同
じようにスクラバ11から排出される洗煙排水を、前段
の減温塔4もしくは7へ噴霧して、冷却水として使用す
る。
Embodiment (Part 4) FIGS. 5 and 6 are diagrams showing examples of another processing system suitable for carrying out the exhaust gas processing method according to the present invention.
In the embodiment of FIG. 5 and FIG. 6, as in the embodiment (2), a part of the exhaust gas burned in the incinerator 1
The slaked lime is sprayed before the dust collector (eg, the bag filter 5), and then separated into incineration exhaust gas and fly ash.
After being mixed with the main ash discharged directly from the furnace, it is charged into the melting furnace 2. The exhaust gas from the melting furnace 2 passes through the combustion chamber 6, the cooling tower 7, and the dust removing device 8 in that order, is mixed with the incineration exhaust gas, and then treated by the scrubber 11 and the denitration catalyst 10. Here, in the present embodiment, similarly to the above-described embodiment (No. 3), the smoke washing drainage discharged from the scrubber 11 is sprayed to the cooling tower 4 or 7 in the preceding stage and used as cooling water.

【0019】図5のシステムは、洗煙排水をそのまま冷
却剤として利用する態様であり、水銀除去の観点から、
溶融炉2の後段で除塵装置8の前段では、活性炭の添加
が必須である。消石灰は、必要に応じて添加される。ま
た図6のシステムのように、洗煙排水を逆浸透膜12に
通してから冷却剤として利用する態様もあり、この形態
では、逆浸透膜12によって上記水銀が系外に除去させ
るので、活性炭を除塵装置(バグフィルタ8等)の前段
で添加しなくとも良い。以上、本発明の実施の形態につ
き述べたが、本発明は既述の実施の形態に限定されるも
のではなく、本発明の要旨を逸脱しない範囲内において
種々の変形及び変更を加え得るものである。
The system shown in FIG. 5 is an embodiment in which the wastewater of smoke cleaning is used as it is as a coolant.
In a stage after the melting furnace 2 and in a stage before the dust removing device 8, addition of activated carbon is essential. Slaked lime is added as needed. In addition, as in the system shown in FIG. 6, there is also an embodiment in which the smoke washing wastewater is passed through the reverse osmosis membrane 12 and then used as a coolant. Need not be added before the dust remover (eg, the bag filter 8). Although the embodiments of the present invention have been described above, the present invention is not limited to the above-described embodiments, and various modifications and changes can be made without departing from the spirit of the present invention. is there.

【0020】[0020]

【発明の効果】本発明によれば、溶融炉後段に燃焼室を
設けること等の効果的な各装置の配置により、ダイオキ
シン類の排出を有効に防止することができる。また、溶
融炉内を還元雰囲気にしておくことができ、これによっ
て、低酸素ガス雰囲気となり重金属を外に排出し易くな
る。この場合、溶融炉から排出されるガスについては、
一酸化炭素濃度が高くなってしまうが、後段の燃焼室に
よって一酸化炭素濃度を低く抑制することができる。さ
らに本発明を用いれば、焼却炉からの排ガス処理に必要
とされるランニングコストを、低く抑えることができ
る。そして、灰溶融炉による排ガス処理を、長期間にわ
たり連続的かつ安全に実施することが可能となる。
According to the present invention, the emission of dioxins can be effectively prevented by arranging each device effectively, such as providing a combustion chamber at the latter stage of the melting furnace. Further, the inside of the melting furnace can be kept in a reducing atmosphere, whereby the atmosphere becomes a low oxygen gas atmosphere and the heavy metals can be easily discharged outside. In this case, for the gas discharged from the melting furnace,
Although the concentration of carbon monoxide increases, the concentration of carbon monoxide can be suppressed to a low level by the combustion chamber in the subsequent stage. Further, according to the present invention, the running cost required for treating exhaust gas from an incinerator can be kept low. And it becomes possible to perform the exhaust gas treatment by the ash melting furnace continuously and safely for a long period of time.

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

【図1】本発明に係る排ガス処理方法を実施するシステ
ムの一例を示した図である。
FIG. 1 is a diagram showing an example of a system for implementing an exhaust gas treatment method according to the present invention.

【図2】本発明に係る処理方法を実施する他のシステム
の一例を示した図である。
FIG. 2 is a diagram showing an example of another system for implementing the processing method according to the present invention.

【図3】本発明に係る処理方法を実施する他のシステム
の一例を示した図である。
FIG. 3 is a diagram showing an example of another system for implementing the processing method according to the present invention.

【図4】本発明に係る処理方法を実施する他のシステム
の一例を示した図である。
FIG. 4 is a diagram showing an example of another system for implementing the processing method according to the present invention.

【図5】本発明に係る処理方法を実施する他のシステム
の一例を示した図である。
FIG. 5 is a diagram showing an example of another system for implementing the processing method according to the present invention.

【図6】本発明に係る処理方法を実施する他のシステム
の一例を示した図である。
FIG. 6 is a diagram showing an example of another system for implementing the processing method according to the present invention.

【符号の説明】[Explanation of symbols]

1 焼却炉 2 溶融炉 3 廃熱ボイラ 4 減温塔 5 集塵装置(バグフィルタ) 6 燃焼室 7 減温塔 8 除塵装置(バグフィルタ) 9 スクラバ 10 脱硝触媒 11 スクラバ 12 逆浸透膜 DESCRIPTION OF SYMBOLS 1 Incinerator 2 Melting furnace 3 Waste heat boiler 4 Temperature reduction tower 5 Dust collection device (Bag filter) 6 Combustion chamber 7 Temperature reduction tower 8 Dust removal device (Bag filter) 9 Scrubber 10 Denitration catalyst 11 Scrubber 12 Reverse osmosis membrane

───────────────────────────────────────────────────── 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) B01D 53/94 F23J 15/00 E F23G 5/44 ZAB B01D 53/36 ZAB F23J 1/00 101A 15/00 F23J 15/00 H (72)発明者 西川 進 神奈川県横浜市金沢区幸浦一丁目8番地1 三菱重工業株式会社横浜研究所内 (72)発明者 川見 佳正 神奈川県横浜市中区錦町12番地 三菱重工 業株式会社横浜製作所内 Fターム(参考) 3K061 DA18 DA19 NB02 NB03 NB13 NB15 3K065 AB03 AC01 AC03 AC19 BA05 BA10 HA02 HA03 HA07 3K070 DA05 DA07 DA16 DA29 DA37 DA42 DA46 DA49 DA52 4D048 AA06 AB06 CA03 CC39 CD05 CD08 CD10 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) B01D 53/94 F23J 15/00 E F23G 5/44 ZAB B01D 53/36 ZAB F23J 1/00 101A 15/00 F23J 15/00 H (72) Inventor Susumu Nishikawa 1-8-1 Koura, Kanazawa-ku, Yokohama-shi, Kanagawa Prefecture Inside the Mitsubishi Research Institute of Mitsubishi Heavy Industries, Ltd. F-term in Yokohama, Ltd. F-term (reference)

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 焼却炉で燃焼させた排ガスの一部を、ボ
イラおよび減温塔を介して集塵装置に至らせる際に、該
集塵装置の前段にて消石灰を噴霧してから、該集塵装置
にて焼却排ガスと飛灰とに分離し、該飛灰を、焼却炉か
ら直接排出される焼却灰と混合した後、溶融炉に投入す
る処理方法であって、 該溶融炉からの排ガスが燃焼室、減温塔、除塵装置を順
次経て、スクラバを介した後、前記焼却排ガスと混合し
て脱硝触媒により処理されることを特徴とする灰溶融炉
の排ガス処理方法。
When a part of the exhaust gas burned in an incinerator is passed through a boiler and a cooling tower to a dust collecting device, slaked lime is sprayed at a preceding stage of the dust collecting device. A method of separating the incineration exhaust gas and fly ash by a dust collector, mixing the fly ash with the incineration ash discharged directly from the incinerator, and then charging the incinerator with a melting furnace. An exhaust gas treatment method for an ash melting furnace, wherein the exhaust gas passes through a combustion chamber, a cooling tower, and a dust removing device, passes through a scrubber, is mixed with the incineration exhaust gas, and is treated by a denitration catalyst.
【請求項2】 焼却炉で燃焼させた排ガスの一部を、ボ
イラおよび減温塔を介して集塵装置に至らせる際に、該
集塵装置の前段にて消石灰を噴霧してから、該集塵装置
にて焼却排ガスと飛灰とに分離し、該飛灰を、焼却炉か
ら直接排出される焼却灰と混合した後、溶融炉に投入す
る処理方法であって、 該溶融炉からの排ガスが燃焼室、減温塔、除塵装置を順
次経た後、前記焼却排ガスと混合してからスクラバおよ
び脱硝触媒により処理されることを特徴とする灰溶融炉
の排ガス処理方法。
2. When a part of the exhaust gas burned in the incinerator is passed to a dust collector via a boiler and a cooling tower, slaked lime is sprayed at a stage preceding the dust collector, and A method of separating the incineration exhaust gas and fly ash by a dust collector, mixing the fly ash with the incineration ash discharged directly from the incinerator, and then charging the incinerator with a melting furnace. An exhaust gas treatment method for an ash melting furnace, wherein the exhaust gas sequentially passes through a combustion chamber, a cooling tower, and a dust removal device, is mixed with the incineration exhaust gas, and then is treated by a scrubber and a denitration catalyst.
【請求項3】 前記スクラバより排出される洗煙排水
を、前記減温塔のいずれか1つへ噴霧することを特徴と
する請求項1又は2に記載の灰溶融炉の排ガス処理方
法。
3. The exhaust gas treatment method for an ash melting furnace according to claim 1, wherein the smoke washing wastewater discharged from the scrubber is sprayed to any one of the cooling towers.
【請求項4】 前記スクラバより排出される洗煙排水
を、逆浸透膜に通してから前記減温塔のいずれか1つへ
噴霧することを特徴とする請求項1又は2に記載の灰溶
融炉の排ガス処理方法。
4. The ash melting according to claim 1, wherein the smoke washing wastewater discharged from the scrubber is passed through a reverse osmosis membrane and then sprayed to any one of the cooling towers. Furnace exhaust gas treatment method.
【請求項5】 焼却炉で燃焼させた排ガスの一部を、ボ
イラおよび減温塔を介して集塵装置に至らせる際に、該
集塵装置の前段にて消石灰を噴霧してから、該集塵装置
にて焼却排ガスと飛灰とに分離し、該飛灰を、焼却炉か
ら直接排出される焼却灰と混合した後、溶融炉に投入す
る処理システムであって、 該溶融炉からの排ガスが燃焼室、減温塔、除塵装置を順
次経て、スクラバを介した後、前記焼却排ガスと混合し
て脱硝触媒装置により処理することを特徴とする灰溶融
炉の排ガス処理システム。
5. When a part of the exhaust gas burned in the incinerator is passed through a boiler and a cooling tower to a dust collecting device, slaked lime is sprayed at a preceding stage of the dust collecting device. A processing system in which the incineration exhaust gas and fly ash are separated by a dust collector, the fly ash is mixed with incineration ash discharged directly from the incinerator, and then charged into a melting furnace. An exhaust gas treatment system for an ash melting furnace, wherein exhaust gas passes through a combustion chamber, a cooling tower, and a dust removing device, passes through a scrubber, is mixed with the incinerated exhaust gas, and is treated by a denitration catalyst device.
【請求項6】 焼却炉で燃焼させた排ガスの一部を、ボ
イラおよび減温塔を介して集塵装置に至らせる際に、該
集塵装置の前段にて消石灰を噴霧してから、該集塵装置
にて焼却排ガスと飛灰とに分離し、該飛灰を、焼却炉か
ら直接排出される焼却灰と混合した後、溶融炉に投入す
る処理システムであって、 該溶融炉からの排ガスが燃焼室、減温塔、除塵装置を順
次経た後、前記焼却排ガスと混合してからスクラバおよ
び脱硝触媒装置により処理することを特徴とする灰溶融
炉の排ガス処理システム。
6. When a part of the exhaust gas burned in the incinerator is passed through a boiler and a cooling tower to a dust collecting device, slaked lime is sprayed at a stage preceding the dust collecting device. A processing system in which the incineration exhaust gas and fly ash are separated by a dust collector, the fly ash is mixed with incineration ash discharged directly from the incinerator, and then charged into a melting furnace. An exhaust gas treatment system for an ash melting furnace, wherein the exhaust gas sequentially passes through a combustion chamber, a cooling tower, and a dust removal device, is mixed with the incineration exhaust gas, and then is treated by a scrubber and a denitration catalyst device.
JP2000129513A 2000-04-28 2000-04-28 Exhaust gas treatment method and system for ash melting furnace Expired - Fee Related JP3664941B2 (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010115588A (en) * 2008-11-12 2010-05-27 Kubota Corp Melting treatment method of incineration ash and melting treatment equipment
CN106352363A (en) * 2016-08-31 2017-01-25 吕宜德 Industrial boiler low-nitric-oxide combustion and environment protection system and technological method
CN107970708A (en) * 2017-11-30 2018-05-01 成都易态科技有限公司 High-temperature dust removal ash afterheat utilizing system
CN113289447A (en) * 2021-07-26 2021-08-24 徐州中科振丰环境科技研究院有限公司 Waste gas treatment device for desalination pretreatment of household garbage incineration fly ash
CN113310056A (en) * 2021-05-11 2021-08-27 中广核工程有限公司 Hazardous waste incineration treatment system and method
CN113719838A (en) * 2021-08-28 2021-11-30 江苏仙盛环保科技有限公司 Smoke purification furnace and operation method thereof

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010115588A (en) * 2008-11-12 2010-05-27 Kubota Corp Melting treatment method of incineration ash and melting treatment equipment
CN106352363A (en) * 2016-08-31 2017-01-25 吕宜德 Industrial boiler low-nitric-oxide combustion and environment protection system and technological method
CN107970708A (en) * 2017-11-30 2018-05-01 成都易态科技有限公司 High-temperature dust removal ash afterheat utilizing system
CN107970708B (en) * 2017-11-30 2023-07-04 成都易态科技有限公司 High-temperature dedusting ash waste heat utilization system
CN113310056A (en) * 2021-05-11 2021-08-27 中广核工程有限公司 Hazardous waste incineration treatment system and method
CN113289447A (en) * 2021-07-26 2021-08-24 徐州中科振丰环境科技研究院有限公司 Waste gas treatment device for desalination pretreatment of household garbage incineration fly ash
CN113719838A (en) * 2021-08-28 2021-11-30 江苏仙盛环保科技有限公司 Smoke purification furnace and operation method thereof

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