JP2000042357A - Low temperature recycle type treatment of waste gas - Google Patents
Low temperature recycle type treatment of waste gasInfo
- Publication number
- JP2000042357A JP2000042357A JP10211242A JP21124298A JP2000042357A JP 2000042357 A JP2000042357 A JP 2000042357A JP 10211242 A JP10211242 A JP 10211242A JP 21124298 A JP21124298 A JP 21124298A JP 2000042357 A JP2000042357 A JP 2000042357A
- Authority
- JP
- Japan
- Prior art keywords
- exhaust gas
- dioxin
- slaked lime
- waste gas
- bag filter
- 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
Links
Landscapes
- Treating Waste Gases (AREA)
- Filtering Of Dispersed Particles In Gases (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、都市ごみおよび産
業廃棄物の焼却処理により発生する排ガス処理方法に関
する。The present invention relates to a method for treating exhaust gas generated by incineration of municipal waste and industrial waste.
【0002】[0002]
【従来の技術】廃棄物の焼却処理により発生する排ガス
は、HCl、SOx、ダイオキシン等の有害物質を含
む。従来の技術では、図3に示すように、HCl、SO
xの酸性成分は排ガス中に吸収剤として消石灰を吹き込
み、またダイオキシンは排ガス中に吸着剤として活性炭
を吹き込み、これらをバグフィルターで飛灰と共に捕集
することにより排ガスから除去される。バグフィルター
で捕集された飛灰は、ダイオキシンを加熱分解した後、
重金属固定薬剤で処理され、ついで埋め立て処分され
る。2. Description of the Related Art Exhaust gas generated by incineration of waste contains harmful substances such as HCl, SOx and dioxin. In the prior art, as shown in FIG.
The acidic component of x is blown with slaked lime as an absorbent into the exhaust gas, and dioxin is blown with activated carbon as an adsorbent into the exhaust gas, and these are removed from the exhaust gas by collecting them together with fly ash with a bag filter. Fly ash collected by the bag filter heats and decomposes dioxin,
Treated with heavy metal fixatives and then landfilled.
【0003】[0003]
【発明が解決しようとする課題】排ガス処理では、上述
の如く、消石灰(Ca(OH)2 )の粒状物を排ガス煙
道内に吹き込むことによって、次式の如く排ガス中のH
Cl、SOxと反応させて排ガスを浄化するのが一般的
である。In the treatment of exhaust gas, as described above, particles of slaked lime (Ca (OH) 2 ) are blown into the flue gas of the exhaust gas, whereby H in the exhaust gas is expressed by the following formula.
Generally, exhaust gas is purified by reacting with Cl and SOx.
【0004】 2HCl + Ca(OH)2 → CaCl2 + 2H2 O SOx + Ca(OH)2 → CaSOx+1 + H2 O[0004] 2HCl + Ca (OH) 2 → CaCl 2 + 2H 2 O SOx + Ca (OH) 2 → CaSO x + 1 + H 2 O
【0005】この方法では、HCl、SOx除去率は当
量比1でHCl:70%、SOx:30%程度である。
これは、上記反応により、消石灰の粒子表面が反応生成
物(CaCl2 、CaSOx+1)からなる殻で覆われ、
それ以上の反応の進行が阻止されてしまうためである。
つまり、粒子内部には未反応消石灰が残っていても、そ
の表面が反応生成物で覆われるために、排ガスは未反応
消石灰部分に接触しにくくなり反応が停止したようにな
る。In this method, the HCl and SOx removal rates are about 70% HCl and 30% SOx at an equivalent ratio of 1.
This is because the surface of the slaked lime particles is covered with a shell made of a reaction product (CaCl 2 , CaSO x + 1 ) by the above reaction,
This is because further progress of the reaction is prevented.
That is, even if unreacted slaked lime remains inside the particles, the surface is covered with the reaction product, so that the exhaust gas hardly comes into contact with the unreacted slaked lime portion, and the reaction stops.
【0006】本発明の目的は、上記未反応消石灰をリサ
イクル再使用して排ガス処理のコスト節減を果たすこと
にある。An object of the present invention is to reduce the cost of exhaust gas treatment by recycling the unreacted slaked lime.
【0007】[0007]
【課題を解決するための手段】本発明による低温リサイ
クル式排ガス処理方法は、排ガスに酸性成分吸収剤粒子
およびダイオキシン吸着剤を吹き込み、バグフィルター
でこれらを飛灰と共に捕集し、捕集物を加熱してダイオ
キシンを熱分解除去する排ガス処理方法において、上記
捕集物を加熱すると共に、酸性成分の吸収により生じた
吸収剤粒子殻を破壊し、吸収剤の破壊物およびダイオキ
シン分解後の吸着剤を含む捕集物を冷却した後、バグフ
ィルター上流の排ガスに吹き込むことを特徴とする方法
である。The low-temperature recycling type exhaust gas treatment method according to the present invention is characterized in that acidic component absorbent particles and dioxin adsorbent are blown into exhaust gas, and these are collected together with fly ash by a bag filter, and the collected matter is collected. In an exhaust gas treatment method for thermally decomposing and removing dioxin, the collected matter is heated and the absorbent particle shell generated by the absorption of the acidic component is destroyed. And then blowing the exhaust gas on the upstream side of the bag filter after cooling the collected matter containing the.
【0008】[0008]
【発明の実施の形態】図1において、焼却炉(1) から出
た排ガスに酸性成分吸収剤として消石灰を吹き込み、ま
たダイオキシン吸着剤として活性炭を吹き込み、これら
をバグフィルター(2) で飛灰と共に捕集する。消石灰お
よび活性炭の各吹き込み量は入口ダイオキシン濃度に応
じて調整し、連続吹き込みを行う。吹き込み用のブロア
は1台として供給配管を共用させる。消石灰の粒子表面
は反応生成物(CaCl2 、CaSOx+1)からなる殻
で覆われる。一般的に活性炭の吹き込み量は50〜50
0mg/Nm3 程度である。バグフィルター(2) による
捕集物を加熱装置(3) で加熱してダイオキシンを熱分解
除去する。DESCRIPTION OF THE PREFERRED EMBODIMENTS In FIG. 1, slaked lime is blown into an exhaust gas discharged from an incinerator (1) as an acidic component absorbent and activated carbon is blown as a dioxin adsorbent, and these are blown together with fly ash by a bag filter (2). Collect. The blowing amount of slaked lime and activated carbon is adjusted according to the concentration of dioxin at the inlet, and continuous blowing is performed. One blower is used to share the supply pipe. The surface of the slaked lime particles is covered with a shell made of a reaction product (CaCl 2 , CaSO x + 1 ). Generally, the blowing amount of activated carbon is 50-50.
It is about 0 mg / Nm 3 . The collected matter by the bag filter (2) is heated by the heating device (3) to thermally decompose and remove dioxin.
【0009】加熱装置(3) は加熱と共に撹拌を行うもの
であり、図2に示すように、ケーシング(4) の内面に設
けられた電気ヒータ(7) と、ケーシング(4) 内に長さ方
向に配たれた回転軸(5) と、これに設けられた多数の撹
拌翼(6) とから主として構成されている。また、加熱装
置(3) の内部は、活性炭の分解を起こさないように、無
酸素状態ないしは酸素稀薄状態になされている。The heating device (3) performs stirring together with heating. As shown in FIG. 2, an electric heater (7) provided on the inner surface of the casing (4) and a length inside the casing (4) are provided. It mainly comprises a rotating shaft (5) arranged in the direction and a number of stirring blades (6) provided on the rotating shaft (5). The interior of the heating device (3) is in an oxygen-free state or an oxygen-lean state so as not to decompose the activated carbon.
【0010】上記捕集物を加熱装置(3) によって350
℃程度に加熱すると共に撹拌することによって消石灰の
粒子殻を破壊する。消石灰の破壊物およびダイオキシン
分解後の活性炭を含む捕集物をついで60℃程度に冷却
する。この冷却によって、消石灰による排ガス中の酸性
成分、特にSOxの吸収効率が向上する。[0010] The collected matter is passed through a heating device (3) for 350 hours.
The particles shell of slaked lime is broken by heating to about ° C and stirring. The collected matter containing the slaked lime debris and the activated carbon after dioxin decomposition is then cooled to about 60 ° C. By this cooling, the absorption efficiency of acidic components, particularly SOx, in the exhaust gas by slaked lime is improved.
【0011】冷却後の消石灰の破壊物および活性炭を含
む捕集物の一部をバグフィルター(2) 上流の排ガスにリ
サイクルして吹き込む。捕集物のリサイクル量も調整可
能とする。この結果、消石灰および活性炭の各使用量は
半分に低減される。A part of the collected matter containing the slaked lime debris after cooling and the activated carbon is recycled and blown into the exhaust gas upstream of the bag filter (2). The amount of collected material can be adjusted. As a result, the usage amounts of slaked lime and activated carbon are reduced by half.
【0012】バグフィルター(2) による捕集物は、特別
管理廃棄物に指定されているので、上記捕集物の残部は
重金属固定薬剤処理した後、埋め立て処分する。この結
果、飛灰量は2/3に低減され、飛灰処理装置の容量は
2/3に軽減される。Since the collected matter by the bag filter (2) is designated as specially managed waste, the remaining part of the collected matter is treated with a heavy metal fixing agent and then disposed of in a landfill. As a result, the fly ash amount is reduced to 2/3, and the capacity of the fly ash processing device is reduced to 2/3.
【0013】[0013]
【発明の効果】本発明による低温リサイクル式排ガス処
理方法では、バグフィルター捕集物を加熱すると共に吸
収剤粒子殻を破壊し、吸収剤の破壊物およびダイオキシ
ン分解後の吸着剤を含む捕集物を冷却した後、バグフィ
ルター上流の排ガスに吹き込むので、消石灰および活性
炭の吹き込み量を低減することができ、酸性成分および
ダイオキシンの除去効率を向上させることができ、ま
た、飛灰処理装置の容量のコンパクト化を果たすことが
できる。こうして、排ガス処理のコスト節減を果たすこ
とができる。According to the low-temperature recycle type exhaust gas treatment method of the present invention, the collected matter containing the broken matter of the absorbent and the adsorbent after dioxin decomposition is destroyed by heating the collected matter of the bag filter and destroying the absorbent particle shell. After cooling, the gas is blown into the exhaust gas upstream of the bag filter, so that the amount of slaked lime and activated carbon blown can be reduced, the efficiency of removing acidic components and dioxins can be improved, and the capacity of the fly ash treatment device can be reduced. Compactness can be achieved. Thus, cost reduction of exhaust gas treatment can be achieved.
【図1】 本発明による低温リサイクル式排ガス処理方
法の例を示すフローシートである。FIG. 1 is a flow sheet showing an example of a low-temperature recycling type exhaust gas treatment method according to the present invention.
【図2】 従来の排ガス処理方法の例を示すフローシー
トである。FIG. 2 is a flow sheet showing an example of a conventional exhaust gas treatment method.
【図3】 加熱装置の例を示す一部切欠き斜視図であ
る。FIG. 3 is a partially cutaway perspective view showing an example of a heating device.
1:焼却炉 2:バグフィルター 3:加熱装置 1: incinerator 2: bag filter 3: heating device
───────────────────────────────────────────────────── 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 53/70 B01D 53/34 134A 53/68 (72)発明者 小畑 博一 大阪市住之江区南港北1丁目7番89号 日 立造船株式会社内 Fターム(参考) 4D002 AA02 AA19 AA21 AC04 BA03 BA04 BA12 BA14 DA05 DA12 DA41 EA02 EA08 EA13 EA20 GA01 GA03 GB03 GB06 HA01 4D058 JA04 RA19 SA20 TA02 TA04 UA01 UA03 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) B01D 53/70 B01D 53/34 134A 53/68 (72) Inventor Hirokazu Obata 1 Minami Kohoku, Suminoe-ku, Osaka-shi No. 7-89 Citachi Shipbuilding Co., Ltd. F-term (reference) 4D002 AA02 AA19 AA21 AC04 BA03 BA04 BA12 BA14 DA05 DA12 DA41 EA02 EA08 EA13 EA20 GA01 GA03 GB03 GB06 HA01 4D058 JA04 RA19 SA20 TA02 TA04 UA01 UA03
Claims (1)
オキシン吸着剤を吹き込み、バグフィルターでこれらを
飛灰と共に捕集し、捕集物を加熱してダイオキシンを熱
分解除去する排ガス処理方法において、上記捕集物を加
熱すると共に、酸性成分の吸収により生じた吸収剤粒子
殻を破壊し、吸収剤の破壊物およびダイオキシン分解後
の吸着剤を含む捕集物を冷却した後、バグフィルター上
流の排ガスに吹き込むことを特徴とする低温リサイクル
式排ガス処理方法。1. An exhaust gas treatment method in which an acidic component absorbent particle and a dioxin adsorbent are blown into exhaust gas, and these are collected together with fly ash by a bag filter, and the collected matter is heated to thermally decompose and remove dioxin. After heating the collected matter, breaking the absorbent particle shell generated by the absorption of the acidic component, and cooling the collected matter containing the broken matter of the absorbent and the adsorbent after dioxin decomposition, exhaust gas upstream of the bag filter A low-temperature recycling type exhaust gas treatment method characterized by injecting air into a wastewater.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP21124298A JP3486765B2 (en) | 1998-07-27 | 1998-07-27 | Low-temperature recycling type exhaust gas treatment method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP21124298A JP3486765B2 (en) | 1998-07-27 | 1998-07-27 | Low-temperature recycling type exhaust gas treatment method |
Publications (2)
Publication Number | Publication Date |
---|---|
JP2000042357A true JP2000042357A (en) | 2000-02-15 |
JP3486765B2 JP3486765B2 (en) | 2004-01-13 |
Family
ID=16602653
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP21124298A Expired - Fee Related JP3486765B2 (en) | 1998-07-27 | 1998-07-27 | Low-temperature recycling type exhaust gas treatment method |
Country Status (1)
Country | Link |
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JP (1) | JP3486765B2 (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2001305119A (en) * | 2000-04-21 | 2001-10-31 | Kanto Chem Co Inc | Filler containing activated charcoal for analyzing dioxins |
JP2008030010A (en) * | 2006-07-27 | 2008-02-14 | Shinroku Nishiyama | Deodorizing method employing bag filter type dust collector and deodorizing device for bag filter type dust collector |
CN103127795A (en) * | 2013-02-07 | 2013-06-05 | 中国恩菲工程技术有限公司 | Smoke processing method and smoke processing system |
CN109603286A (en) * | 2019-01-11 | 2019-04-12 | 天津市闻达石油钻采工程装备有限公司 | The processing method of solidliquid mixture |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH0389916A (en) * | 1989-09-01 | 1991-04-15 | Hitachi Zosen Corp | In-furnace desulfurization process |
JPH0731847A (en) * | 1993-07-20 | 1995-02-03 | Kobe Steel Ltd | Removal of harmful substance from waste gas |
JPH08243341A (en) * | 1995-03-13 | 1996-09-24 | Ebara Corp | Treatment of waste gas |
-
1998
- 1998-07-27 JP JP21124298A patent/JP3486765B2/en not_active Expired - Fee Related
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH0389916A (en) * | 1989-09-01 | 1991-04-15 | Hitachi Zosen Corp | In-furnace desulfurization process |
JPH0731847A (en) * | 1993-07-20 | 1995-02-03 | Kobe Steel Ltd | Removal of harmful substance from waste gas |
JPH08243341A (en) * | 1995-03-13 | 1996-09-24 | Ebara Corp | Treatment of waste gas |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2001305119A (en) * | 2000-04-21 | 2001-10-31 | Kanto Chem Co Inc | Filler containing activated charcoal for analyzing dioxins |
JP2008030010A (en) * | 2006-07-27 | 2008-02-14 | Shinroku Nishiyama | Deodorizing method employing bag filter type dust collector and deodorizing device for bag filter type dust collector |
CN103127795A (en) * | 2013-02-07 | 2013-06-05 | 中国恩菲工程技术有限公司 | Smoke processing method and smoke processing system |
CN103127795B (en) * | 2013-02-07 | 2015-03-18 | 中国恩菲工程技术有限公司 | Smoke processing method and smoke processing system |
CN109603286A (en) * | 2019-01-11 | 2019-04-12 | 天津市闻达石油钻采工程装备有限公司 | The processing method of solidliquid mixture |
CN109603286B (en) * | 2019-01-11 | 2019-07-30 | 天津市闻达石油钻采工程装备有限公司 | The processing method of solidliquid mixture |
Also Published As
Publication number | Publication date |
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