JP2000070663A - Exhaust gas cooling and harmful substance removing method - Google Patents

Exhaust gas cooling and harmful substance removing method

Info

Publication number
JP2000070663A
JP2000070663A JP10249738A JP24973898A JP2000070663A JP 2000070663 A JP2000070663 A JP 2000070663A JP 10249738 A JP10249738 A JP 10249738A JP 24973898 A JP24973898 A JP 24973898A JP 2000070663 A JP2000070663 A JP 2000070663A
Authority
JP
Japan
Prior art keywords
exhaust gas
cooling
activated carbon
harmful substances
harmful substance
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP10249738A
Other languages
Japanese (ja)
Inventor
Kazunori Wakiya
和紀 脇屋
Hitoshi Yamamoto
仁巳 山本
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.)
Okawara Mfg Co Ltd
Original Assignee
Okawara Mfg Co Ltd
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 Okawara Mfg Co Ltd filed Critical Okawara Mfg Co Ltd
Priority to JP10249738A priority Critical patent/JP2000070663A/en
Publication of JP2000070663A publication Critical patent/JP2000070663A/en
Pending legal-status Critical Current

Links

Landscapes

  • Treating Waste Gases (AREA)
  • Separation Of Gases By Adsorption (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide an exhaust gas cooling and harmful substance removing method capable of simultaneously performing the cooling of exhaust gas and the removal of a harmful substance by one apparatus, capable of keeping the removal ratio of the harmful substance high, also preventing the re-synthesis of dioxin, not taking an apparatus arranging space and capable of suppressing equipment cost or running cost relatively low. SOLUTION: In a method for cooling exhaust gas and removing a harmful substance in the exhaust gas, a fluidized bed treatment apparatus 1 is used and, in such a state that the fluidizing chamber 2 of this apparatus 1 is packed, for example, with granular activated carbon with a size of 0.3-4.0 mm, the exhaust gas is sent into the fluidizing chamber 2 to fluidize activated carbon and a cooling liquid is sprayed and dripped on activated carbon to remove the heat of the exhaust gas to lower the temp. thereof and the harmful substance in the exhaust gas is bonded to activated carbon to remove the harmful substance from the exhaust gas.

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】本発明はゴミ焼却炉等の排ガ
スを冷却するとともに排ガス中の有害物質を除去する方
法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for cooling exhaust gas from a garbage incinerator or the like and removing harmful substances from the exhaust gas.

【0002】[0002]

【発明の背景】ゴミ焼却炉の排ガスから発生するダイオ
キシン類等の有害物質が近年問題となっており、このダ
イオキシン類等の有害物質をいかに低減するかが技術的
課題となっている。現在のゴミ焼却炉の排ガスの処理と
しては、排ガスを冷却すること及び排ガス中の有害物質
を除去することが行われ、これによりダイオキシン類等
の有害物質の発生、放散を防ぐようにしている。
BACKGROUND OF THE INVENTION In recent years, harmful substances such as dioxins generated from exhaust gas from garbage incinerators have become a problem, and there is a technical problem how to reduce such harmful substances such as dioxins. As the treatment of exhaust gas from current garbage incinerators, the exhaust gas is cooled and harmful substances in the exhaust gas are removed, thereby preventing generation and emission of harmful substances such as dioxins.

【0003】まず排ガスの冷却方法について説明する。
排ガスを冷却(急冷)する理由は、200〜500℃の
温度領域においてダイオキシン類が再合成しやすいこと
から、排ガス温度がこの温度域に留まることがないよう
にするためであり、500〜800℃以上の排ガスを一
気に200℃以下に急冷することが行われている。この
ための従来のゴミ焼却炉の冷却方法としては、水噴霧、
スクラバー、空気希釈、熱交換器を用いる方法などがあ
る。また本出願人がすでに出願に及んでいる特願平10
−88012号に示されるような流動層処理装置を用い
る方法も発案されている。
[0003] First, a method of cooling exhaust gas will be described.
The reason why the exhaust gas is cooled (quenched) is that dioxins are easily resynthesized in a temperature range of 200 to 500 ° C., so that the exhaust gas temperature does not remain in this temperature range. The above exhaust gas is rapidly cooled to 200 ° C. or less at a stretch. Conventional refuse incinerator cooling methods for this purpose include water spray,
There are methods using a scrubber, air dilution, and a heat exchanger. In addition, the applicant has filed a patent application filed in Japanese Patent Application
A method using a fluidized bed treatment apparatus as disclosed in JP-A-88012 has also been proposed.

【0004】しかしながら、上述したような排ガスの冷
却方法には、次のような問題点がある。すなわち従来の
冷却方法では関連する補器類を要する等により装置が全
体として大きくなり、また排水処理を行う機器類等が必
要になったりする。また冷却方法のみではダイオキシン
類そのものを除去したのではなく、あくまで発生環境を
排除したに過ぎないからダイオキシン類が再合成し易い
等の問題がある。更に前述した特願平10−88012
号では、流動層処理装置の流動層内にアルミナボール等
の媒体球を流動化させ、そこにアルカリ溶液等を供給し
て排気ガスを通す実施の形態を示しており、このものは
上述したような従来装置の問題点を解決するものである
が、流動層部分の圧損が大きく、排気ファンの動力を大
きくしなければならないというコストアップ要因を有し
ていた。
However, the above-described exhaust gas cooling method has the following problems. That is, in the conventional cooling method, the size of the apparatus as a whole is increased due to the necessity of related auxiliaries and the like, and equipment for performing wastewater treatment is required. Further, there is a problem that dioxins are easily re-synthesized because dioxins themselves are not removed by the cooling method alone, but only the generation environment is eliminated. Further, the aforementioned Japanese Patent Application No. Hei 10-88012
No. 2 shows an embodiment in which a medium sphere such as an alumina ball is fluidized in a fluidized bed of a fluidized-bed processing apparatus, and an alkali solution or the like is supplied thereto and exhaust gas is passed therethrough. However, it has a high pressure loss in the fluidized bed portion and has a cost increase factor in that the power of the exhaust fan must be increased.

【0005】一方、従来の有害物質の除去方法として
は、焼却炉に生石灰を入れたり、また排ガス中に消石
灰、活性炭を吹き込みバグフィルタで採取したり、更に
は活性炭吸着塔や触媒塔に排ガスを通過させるという方
法が採られている。しかしながら、上述したような排ガ
ス中の有害物質の除去方法には、次のような問題点があ
る。すなわち従来の有害物質の除去方法では、例えばバ
グ採取ではダイオキシン類の除去率が80%程度であ
り、除去能力が充分ではない。また活性炭吸着塔や触媒
塔等の除去装置は、装置が大きく場所を取り、また別途
冷却装置が必要なことなどもあり、設備費が高くなると
いう問題点を有していた。
On the other hand, as a conventional method of removing harmful substances, quick lime is put into an incinerator, slaked lime and activated carbon are blown into exhaust gas and collected with a bag filter, and the exhaust gas is further discharged into an activated carbon adsorption tower or a catalyst tower. The method of passing is adopted. However, the method for removing harmful substances in exhaust gas as described above has the following problems. That is, in the conventional method for removing harmful substances, for example, in collecting bugs, the removal rate of dioxins is about 80%, and the removal ability is not sufficient. In addition, the removal apparatus such as the activated carbon adsorption tower and the catalyst tower has a problem that the equipment cost is large because the apparatus takes a large space and a separate cooling device is required.

【0006】[0006]

【開発を試みた技術的課題】本発明はこのような背景か
らなされたものであって、一台の装置で排ガスの冷却と
有害物質の除去を同時に行え、且つ有害物質の除去率を
高く維持できるとともに、ダイオキシン類の再合成も防
ぎ、更に装置の設置スペースを取らず、且つ設備費やラ
ンニングコストも比較的低く抑えることができる新規な
排ガスの冷却並びに有害物質除去方法の開発を試みたも
のである。
[Technical Problems Attempted to Be Developed] The present invention has been made in view of such a background, and a single device can simultaneously cool exhaust gas and remove harmful substances, and maintain a high harmful substance removal rate. A new exhaust gas cooling and harmful substance removal method that can prevent the resynthesis of dioxins, prevent the installation space of equipment, and keep the equipment cost and running cost relatively low. It is.

【0007】[0007]

【課題を解決するための手段】すなわち請求項1記載の
排ガスの冷却並びに有害物質除去方法は、排ガスを冷却
するとともに排ガス中の有害物質を除去する方法におい
て、流動層処理装置を用い、この流動室内に活性炭を入
れた状態で排ガスを流動室内に送り込み、この排ガスで
前記活性炭を流動化し、同時に流動層内に供給される冷
却液により排ガスの熱を奪って温度を降下させるととも
に、前記活性炭に前記排ガス中の有害物質を付着させる
ことにより排ガス中から有害物質を除去することを特徴
として成るものである。
According to a first aspect of the present invention, there is provided a method for cooling exhaust gas and removing harmful substances, the method comprising the steps of: The exhaust gas is sent into the fluidized chamber with the activated carbon in the chamber, and the activated carbon is fluidized by the exhaust gas, and at the same time, the temperature of the exhaust gas is lowered by removing the heat of the exhaust gas by the cooling liquid supplied into the fluidized bed, The method is characterized by removing harmful substances from exhaust gas by attaching harmful substances in the exhaust gas.

【0008】また請求項2記載の排ガスの冷却並びに有
害物質除去方法は、前記要件に加え、前記活性炭は粒状
であることを特徴として成るものである。
The method for cooling exhaust gas and removing harmful substances according to claim 2 is characterized in that, in addition to the above requirements, the activated carbon is granular.

【0009】更に請求項3記載の排ガスの冷却並びに有
害物質除去方法は、前記請求項2記載の要件に加え、前
記活性炭の粒の大きさは、0.3〜4.0mmであるこ
とを特徴として成るものである。
Further, the method for cooling exhaust gas and removing harmful substances according to claim 3 is characterized in that, in addition to the requirements described in claim 2, the size of the particles of the activated carbon is 0.3 to 4.0 mm. It consists of.

【0010】更にまた請求項4記載の排ガスの冷却並び
に有害物質除去方法は、前記請求項2または3記載の要
件に加え、前記活性炭の粒径分布を、0.5〜1.0m
mの範囲内とすることを特徴として成るものである。
According to a fourth aspect of the present invention, there is provided a method for cooling exhaust gas and removing harmful substances, wherein the activated carbon has a particle size distribution of 0.5 to 1.0 m.
m.

【0011】更にまた請求項5記載の排ガスの冷却並び
に有害物質除去方法は、前記請求項1、2、3または4
記載の要件に加え、前記排ガスは、焼却炉から排気され
た排ガスであることを特徴として成るものである。
Further, the method for cooling exhaust gas and removing harmful substances according to claim 5 is the same as that of claim 1, 2, 3, or 4.
In addition to the stated requirements, the exhaust gas is exhaust gas exhausted from an incinerator.

【0012】[0012]

【発明の実施の形態】以下本発明を図示の実施の形態に
基づき説明する。なお以下の説明にあたっては、まず本
発明の排ガスの冷却並びに有害物質除去方法に用いる装
置を説明した後、この装置の作動態様と併せて本発明の
排ガスの冷却並びに有害物質除去方法について説明す
る。なおこの実施の形態では、焼却炉の排ガス中のダイ
オキシン類等の有害物質を除去するとともに、この排ガ
スの温度を200℃以下に冷却する実施の形態を示す。
DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described below with reference to the illustrated embodiments. In the following description, first, an apparatus used for the method for cooling exhaust gas and removing harmful substances according to the present invention will be described, and then the method for cooling exhaust gas and removing harmful substances according to the present invention will be described together with the operation mode of this apparatus. In this embodiment, an embodiment is shown in which harmful substances such as dioxins in the exhaust gas of an incinerator are removed and the temperature of the exhaust gas is cooled to 200 ° C. or lower.

【0013】図1中符号1に示す装置は、流動層処理装
置であり、この装置により排ガスの冷却を行うととも
に、排ガス中の有害物質の除去を行う。流動層処理装置
1はほぼタワー状を成し、その中間段に流動室2を有
し、その下方に焼却炉からの排ガスが吹込口4aから吹
き込まれる排ガス吹込室4を有する。また流動室2の上
方には有害物質が除去された排ガスを排気するための排
気室3を有している。流動室2と、排ガス吹込室4と
は、複数の穿孔がなされた目皿板2Aにより仕切られ
る。流動室2内には、粒状の活性炭が入れられ、排ガス
によって流動状態とされる。符号7は冷却液を供給する
液体供給装置であり、冷却液としては本実施の形態では
水を使用するものであるが、その他、排ガス中の有害物
質を中和する液体、例えばアルカリ溶液を用いるように
してもよい。また流動室2内には、活性炭を攪拌するた
めの攪拌装置や、流動室2から排ガス吹込室4へ落ちる
水を再度流動室2へ循環する循環装置等を適宜設けても
よい。
An apparatus indicated by reference numeral 1 in FIG. 1 is a fluidized bed treatment apparatus, which cools exhaust gas and removes harmful substances in the exhaust gas. The fluidized bed processing apparatus 1 has a substantially tower shape, has a fluid chamber 2 at an intermediate stage, and has an exhaust gas blowing chamber 4 below which exhaust gas from an incinerator is blown from a blowing port 4a. Further, an exhaust chamber 3 for exhausting exhaust gas from which harmful substances have been removed is provided above the flow chamber 2. The flow chamber 2 and the exhaust gas blowing chamber 4 are separated by a perforated plate 2A having a plurality of perforations. Activated granular carbon is put in the fluidized chamber 2 and is made to flow by exhaust gas. Reference numeral 7 denotes a liquid supply device for supplying a cooling liquid. In this embodiment, water is used as the cooling liquid. In addition, a liquid that neutralizes harmful substances in exhaust gas, for example, an alkaline solution is used. You may do so. Further, a stirring device for stirring the activated carbon, a circulating device for circulating water falling from the flow chamber 2 to the exhaust gas blowing chamber 4 to the flow chamber 2 again, and the like may be appropriately provided in the flow chamber 2.

【0014】流動層処理装置1における排気室3には、
バグフィルタ6が接続され、ここで更に排ガス中の塵や
活性炭から出た粉等が集塵され、排気ファン8を通って
排気される。なおバグフィルタ6で集塵された異物は下
部の取出口6aから取り出される。
The exhaust chamber 3 in the fluidized bed processing apparatus 1 includes:
A bag filter 6 is connected, where dust in exhaust gas and powder from activated carbon are further collected and exhausted through an exhaust fan 8. The foreign matter collected by the bag filter 6 is taken out from a lower outlet 6a.

【0015】液体供給装置7について説明する。液体供
給装置7は、冷却液を貯留する液体タンク7Aと、弁7
Bと、液体供給ポンプ7Cとを具備して成る。液体ポン
プの底部から流動層処理装置1へ供給管が延び、流動室
2内のノズル5から冷却液が流動層へ向けて噴霧または
滴下される。
The liquid supply device 7 will be described. The liquid supply device 7 includes a liquid tank 7A for storing a cooling liquid, a valve 7
B and a liquid supply pump 7C. A supply pipe extends from the bottom of the liquid pump to the fluidized bed processing apparatus 1, and a cooling liquid is sprayed or dropped from a nozzle 5 in the fluidized chamber 2 toward the fluidized bed.

【0016】本発明の排ガスの冷却並びに有害物質除去
方法に用いる装置の具体的な形態は以上のようにして成
り、以下作動態様を説明しながら併せて本発明の排ガス
の冷却並びに有害物質除去方法について説明する。焼却
炉から排出された排ガスは流動層処理装置1の吹込口4
aから目皿板2Aを通って、流動室2内へ噴出される。
流動室2内には、活性炭が入っており、これらが前記排
ガスにより流動状態とされる。ここに冷却液が噴霧また
は滴下されて活性炭の表面に付着する。水分が付着した
活性炭は流動状態にあり、排ガスと極めて効率よく接触
するので、排ガスは200℃以下に急冷され、一方排ガ
ス中のダイオキシン類等の有害物質は、活性炭に吸着さ
れる。そして浄化された排ガスが排気室3からバグフィ
ルタ6に排出される。バグフィルタ6内では固形物質が
除去され、排気ファン8を介して排気される。排気ガス
は200℃以下に急冷され、ダイオキシン類の合成に関
わる前駆物質も除去されるため、ダイオキシン類が再合
成されるようなこともなくなる。なお活性炭は比重が小
さいため、流動媒体としてアルミナボールを使用した場
合に比べ、流動層圧損が小さく、従って排気ファン8の
動力を小さく抑えることができる。
The specific form of the apparatus used in the method for cooling exhaust gas and removing harmful substances according to the present invention is as described above, and the method for cooling exhaust gas and removing harmful substances according to the present invention will be described together with the operation mode. Will be described. Exhaust gas discharged from the incinerator is supplied to the inlet 4 of the fluidized bed treatment apparatus 1.
a is ejected into the flow chamber 2 through the perforated plate 2A.
Activated carbon is contained in the flow chamber 2, and these are made to flow by the exhaust gas. Here, the cooling liquid is sprayed or dropped and adheres to the surface of the activated carbon. Since the activated carbon to which moisture has adhered is in a fluid state and comes into contact with the exhaust gas very efficiently, the exhaust gas is quenched to 200 ° C. or less, while harmful substances such as dioxins in the exhaust gas are adsorbed by the activated carbon. Then, the purified exhaust gas is discharged from the exhaust chamber 3 to the bag filter 6. The solid matter is removed in the bag filter 6 and exhausted through the exhaust fan 8. Exhaust gas is rapidly cooled to 200 ° C. or lower, and precursors involved in the synthesis of dioxins are also removed, so that dioxins are not resynthesized. Since activated carbon has a low specific gravity, the fluidized bed pressure loss is smaller than when alumina balls are used as a fluidized medium, and therefore, the power of the exhaust fan 8 can be suppressed to a small value.

【0017】[0017]

【実施例】次に本発明の排ガスの冷却並びに有害物質除
去方法を用いた具体的な実験例についてこのとき得られ
たデータを示しながら説明する。図2に示されるのが、
本発明の実験に用いられた装置類であり、基本的に前述
した実施の形態で示した装置を用い、これに排ガスを想
定したガスを作成する装置類と、各種の測定器具を付設
して成る。
Next, specific experimental examples using the method for cooling exhaust gas and removing harmful substances according to the present invention will be described with reference to data obtained at this time. As shown in FIG.
The devices used in the experiments of the present invention are basically the same as those described in the above-described embodiment, and are provided with devices for producing gas assuming exhaust gas and various measuring instruments. Become.

【0018】前述した流動層処理装置1、バグフィルタ
6、液体供給装置7等以外の装置類について説明する。
符号9に示す機器は吹込ファンで、外気を導入するもの
である。この吹込ファン9により導入された外気はオリ
フィス10によって流量が計測される。そしてこの外気
のいくらかが直接流動層処理装置1の吹込口4aへ吹き
込まれるとともに、残りの外気は二基のヒータ11A、
11Bにより熱せられ、前記吹込口4aへ吹き込まれ
る。
Devices other than the fluidized bed processing device 1, the bag filter 6, the liquid supply device 7, and the like will be described.
The device indicated by reference numeral 9 is a blower fan for introducing outside air. The flow rate of the outside air introduced by the blowing fan 9 is measured by the orifice 10. Some of this outside air is directly blown into the blowing port 4a of the fluidized bed processing apparatus 1, and the remaining outside air is supplied to two heaters 11A,
It is heated by 11B and is blown into the blowing port 4a.

【0019】また符号12に示す機器はビュレットであ
り、ダイオキシンの代替被検体であるモノクロロベンゼ
ンがこれにより所定量が計測されながら流動層処理装置
1の吹込口4aに供給される。なおモノクロロベンゼン
はダイオキシンの前駆物質の一つでもあるのでこれが本
発明により除去されれば、ダイオキシンも減少すること
が示される。
The device denoted by reference numeral 12 is a burette, and monochlorobenzene, which is a substitute for dioxin, is supplied to the blow-in port 4a of the fluidized bed processing apparatus 1 while measuring a predetermined amount. Since monochlorobenzene is also one of the precursors of dioxin, it is shown that dioxin is reduced if it is removed according to the present invention.

【0020】また符号13で示す機器は重量計であり、
水の供給重量を計測する。また排気室3と排ガス吹込室
4にはそれぞれ温度計が設けられ、検査ガスの温度が計
測される。また符号14で示す機器は例えば水柱圧力計
等を用いた流動層圧損計測器であり、検査ガスが流動層
を経ることによる圧損を検査するためのものである。
The device denoted by reference numeral 13 is a weighing scale.
Measure the water supply weight. Further, a thermometer is provided in each of the exhaust chamber 3 and the exhaust gas blowing chamber 4 to measure the temperature of the inspection gas. The device indicated by reference numeral 14 is a fluidized-bed pressure-loss measuring device using, for example, a water column pressure gauge and the like, for inspecting a pressure loss caused by a test gas passing through a fluidized bed.

【0021】また流動層処理装置1の流動床面積は0.
05m2 であり、前記排ガス吹込室4の温度を300℃
に保ち、排気室3の温度を150℃となるように冷却液
を噴霧して検査ガスを冷却するようにした。なお実験は
流動媒体を、円柱の活性炭(上低面が直径3mmで高さ
3mm)、破砕した活性炭(粒径が0.5〜1.7mm
と、0.36〜0.85mmの二種類)、アルミナボー
ル(直径2mm)とで比較して、それぞれについて投入
量を変化させて、流動層圧損とモノクロロベンゼンの除
去率を検査した。
The fluidized bed processing apparatus 1 has a fluidized bed area of 0.1.
05 m 2 , and the temperature of the exhaust gas
And the test gas is cooled by spraying a cooling liquid so that the temperature of the exhaust chamber 3 becomes 150 ° C. In the experiment, a fluidized medium was a column of activated carbon (upper and lower surfaces having a diameter of 3 mm and a height of 3 mm) and crushed activated carbon (having a particle size of 0.5 to 1.7 mm).
And two types of 0.36 to 0.85 mm) and alumina balls (diameter: 2 mm). The fluidized bed pressure loss and the removal rate of monochlorobenzene were inspected by changing the input amounts for each.

【0022】結果は下記の表1に抜粋して示すとおりで
ある。モノクロロベンゼンの除去率の最も良かったのは
Run3の除去率99%の時であり、このときは、粒径
が0.5〜1.7mmの粒状活性炭を6.8kg投入し
て実験を行った。このときにはモノクロロベンゼンの濃
度は吹き込み時に26ppmに条件設定してあったもの
が0.3ppmに低下し、流動層材料圧損は136mm
Aqであった。
The results are as shown in Table 1 below. The best removal rate of monochlorobenzene was obtained when the removal rate of Run3 was 99%. At this time, 6.8 kg of granular activated carbon having a particle size of 0.5 to 1.7 mm was charged and the experiment was performed. . At this time, the concentration of monochlorobenzene, which had been set to 26 ppm at the time of blowing, was reduced to 0.3 ppm, and the pressure loss of the fluidized bed material was 136 mm.
Aq.

【0023】アルミナボールを流動媒体として用いた場
合、Run1に示されるようにモノクロロベンゼンの濃
度は下がらなかった。なおアルミナボールは流動層材料
圧損が大きく、更に投入量を少なくすると水の分散が悪
くなる。また上下面が直径3mmで、高さが3〜8mm
の円柱状の活性炭を用いた場合には、Run7やRun
8に示すようにモロクロロベンゼンの除去率は、破砕炭
を用いたRun2〜6のうちのそれぞれ条件の近いもの
と比べると小さかった。
When alumina balls were used as the fluid medium, the concentration of monochlorobenzene did not decrease as shown in Run 1. Alumina balls have a large pressure loss in the fluidized bed material, and if the amount is further reduced, the dispersion of water becomes worse. The upper and lower surfaces are 3 mm in diameter and 3 to 8 mm in height
In the case of using columnar activated carbon, Run7 or Run
As shown in FIG. 8, the removal rate of morochlorobenzene was smaller than that of Runs 2 to 6 using the crushed charcoal, which had similar conditions.

【0024】[0024]

【表1】 [Table 1]

【0025】[0025]

【発明の効果】請求項1記載の排ガスの冷却並びに有害
物質除去方法によれば、流動層処理装置1を用い、流動
室2内に活性炭を入れた状態で排ガスを流動室2内に送
り込んで活性炭を流動化させ、これに冷却液を噴霧また
は滴下するため、排ガスが急冷されるとともに、排ガス
中からダイオキシン類などの有害物質を活性炭に吸着さ
せることにより除去することができる。また排ガスの熱
が急速に奪われ低温度とされることと、ダイオキシン類
の合成にかかわる前駆物質(有害物質)が除去されるこ
とにより、排ガスが冷却された後にダイオキシン類が再
合成されることも防がれる。冷却機能と有害物質除去機
能を兼ね備えた装置を、従来よりもそれぞれの性能が向
上しているにもかかわらず、比較的コンパクトな装置と
して提供でき、従来の冷却装置や、活性炭の吸着塔、触
媒塔等の有害物質除去装置のように装置が大きくならな
い。
According to the method for cooling exhaust gas and removing harmful substances according to the first aspect of the present invention, the exhaust gas is fed into the fluid chamber 2 using the fluidized bed treatment apparatus 1 while the activated carbon is put in the fluid chamber 2. Since the activated carbon is fluidized and the cooling liquid is sprayed or dropped thereon, the exhaust gas is rapidly cooled and harmful substances such as dioxins can be removed from the exhaust gas by adsorbing the activated carbon. In addition, the heat of the exhaust gas is quickly taken away to lower the temperature, and the precursors (harmful substances) involved in the synthesis of dioxins are removed, so that the dioxins are resynthesized after the exhaust gas is cooled. Is also prevented. Despite the improved performance of each unit, which has both cooling and harmful substance removal functions, it can be provided as a relatively compact unit. The equipment does not become large like a toxic substance removal equipment such as a tower.

【0026】請求項2記載の排ガスの冷却並びに有害物
質除去方法によれば、活性炭が粒状であるため、流動媒
体としてアルミナボールを使用した場合に比べ、流動層
圧損を小さくでき、排気ファン8の動力を小さく抑える
ことができる。また活性炭の吸着表面積も大きく、有害
物質の除去率も大きくなる。
According to the method for cooling exhaust gas and removing harmful substances according to the second aspect, since the activated carbon is granular, the fluidized bed pressure loss can be reduced as compared with the case where alumina balls are used as the fluidized medium. The power can be kept small. Also, the adsorption surface area of activated carbon is large, and the removal rate of harmful substances is also large.

【0027】請求項3記載の排ガスの冷却並びに有害物
質除去方法によれば、活性炭の粒の大きさは、0.3〜
4.0mmであるため、活性炭の流動状態もよく、有害
物質の除去率に優れ、流動層圧損も小さくなる。
According to the method for cooling exhaust gas and removing harmful substances according to the third aspect, the size of the activated carbon particles is 0.3 to
Since it is 4.0 mm, the flow state of the activated carbon is good, the harmful substance removal rate is excellent, and the fluidized bed pressure loss is small.

【0028】請求項4記載の排ガスの冷却並びに有害物
質除去方法によれば、活性炭の粒径分布を、0.5〜
1.0mmの範囲内とするものであるため、活性炭が流
動層において均一に分散し、有害物質の除去率に更に優
れ、流動層圧損も小さくなる。
According to the method for cooling exhaust gas and removing harmful substances according to the fourth aspect, the particle size distribution of the activated carbon is adjusted to 0.5 to 0.5%.
Since it is within the range of 1.0 mm, the activated carbon is uniformly dispersed in the fluidized bed, the harmful substance removal rate is further excellent, and the fluidized bed pressure loss is reduced.

【0029】請求項5記載の排ガスの冷却並びに有害物
質除去方法によれば、ダイオキシン類の発生は、ゴミ焼
却炉からの発生がほとんどであるため、本発明を焼却炉
に用いることによりダイオキシン類の発生が大幅に防が
れる。
According to the method for cooling exhaust gas and removing harmful substances according to the fifth aspect, since dioxins are mostly generated from a garbage incinerator, the present invention is applied to an incinerator to reduce dioxins. Generation is largely prevented.

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

【図1】本発明の排ガスの冷却並びに有害物質除去方法
の実施の形態を示す説明図である。
FIG. 1 is an explanatory view showing an embodiment of a method for cooling exhaust gas and removing harmful substances according to the present invention.

【図2】本発明の排ガスの冷却並びに有害物質除去方法
の実施例を示す説明図である。
FIG. 2 is an explanatory view showing an embodiment of the method for cooling exhaust gas and removing harmful substances according to the present invention.

【符号の説明】[Explanation of symbols]

1 流動層処理装置 2 流動室 2A 目皿板 3 排気室 4 排ガス吹込室 4a 吹込口 5 ノズル 6 バグフィルタ 6a 取出口 7 液体供給装置 7A 液体タンク 7B 弁 7C 液体供給ポンプ 8 排気ファン 9 吹込ファン 10 オリフィス 11A ヒータ 11B ヒータ 12 ビュレット 13 重量計 14 流動層圧損計測器 DESCRIPTION OF SYMBOLS 1 Fluidized bed processing apparatus 2 Fluid chamber 2A Perforated plate 3 Exhaust chamber 4 Exhaust gas blowing chamber 4a Inlet 5 Nozzle 6 Bag filter 6a Outlet 7 Liquid supply device 7A Liquid tank 7B Valve 7C Liquid supply pump 8 Exhaust fan 9 Blow fan 10 Orifice 11A Heater 11B Heater 12 Bullet 13 Weight scale 14 Fluidized bed pressure loss measuring instrument

フロントページの続き Fターム(参考) 4D002 AA21 AC04 BA04 BA12 BA13 BA14 CA01 CA09 DA35 DA41 GA02 GA03 GB01 GB02 GB03 GB04 GB06 GB12 HA08 4D012 CA12 CC14 CE01 CE02 CF02 CF03 CF04 CF05 CF06 CG05 CH01 CJ05 CK01 Continued on front page F term (reference) 4D002 AA21 AC04 BA04 BA12 BA13 BA14 CA01 CA09 DA35 DA41 GA02 GA03 GB01 GB02 GB03 GB04 GB06 GB12 HA08 4D012 CA12 CC14 CE01 CE02 CF02 CF03 CF04 CF05 CF06 CG05 CH01 CJ05 CK01

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 排ガスを冷却するとともに排ガス中の有
害物質を除去する方法において、流動層処理装置を用
い、この流動室内に活性炭を入れた状態で排ガスを流動
室内に送り込み、この排ガスで前記活性炭を流動化し、
同時に流動層内に供給される冷却液により排ガスの熱を
奪って温度を降下させるとともに、前記活性炭に前記排
ガス中の有害物質を付着させることにより排ガス中から
有害物質を除去することを特徴とする排ガスの冷却並び
に有害物質除去方法。
1. A method for cooling effluent gas and removing harmful substances in the effluent gas, using a fluidized bed treatment apparatus, sending the effluent gas into the fluidized chamber with the activated carbon contained in the fluidized chamber, Fluidize,
At the same time, the temperature of the exhaust gas is lowered by depriving the heat of the exhaust gas by the cooling liquid supplied into the fluidized bed, and the harmful substance is removed from the exhaust gas by attaching the harmful substance in the exhaust gas to the activated carbon. Method of cooling exhaust gas and removing harmful substances.
【請求項2】 前記活性炭は粒状であることを特徴とす
る請求項1記載の排ガスの冷却並びに有害物質除去方
法。
2. The method for cooling exhaust gas and removing harmful substances according to claim 1, wherein said activated carbon is granular.
【請求項3】 前記活性炭の粒の大きさは、0.3〜
4.0mmであることを特徴とする請求項2記載の排ガ
スの冷却並びに有害物質除去方法。
3. The activated carbon has a grain size of 0.3 to 0.3.
3. The method for cooling exhaust gas and removing harmful substances according to claim 2, wherein the diameter is 4.0 mm.
【請求項4】 前記活性炭の粒径分布を、0.5〜1.
0mmの範囲内とすることを特徴とする請求項2または
3記載の排ガスの冷却並びに有害物質除去方法。
4. The particle size distribution of said activated carbon is 0.5 to 1.
4. The method for cooling exhaust gas and removing harmful substances according to claim 2, wherein the diameter is within a range of 0 mm.
【請求項5】 前記排ガスは、焼却炉から排気された排
ガスであることを特徴とする請求項1、2、3または4
記載の排ガスの冷却並びに有害物質除去方法。
5. The exhaust gas according to claim 1, wherein the exhaust gas is exhaust gas exhausted from an incinerator.
The method for cooling exhaust gas and removing harmful substances according to the above.
JP10249738A 1998-09-03 1998-09-03 Exhaust gas cooling and harmful substance removing method Pending JP2000070663A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10249738A JP2000070663A (en) 1998-09-03 1998-09-03 Exhaust gas cooling and harmful substance removing method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10249738A JP2000070663A (en) 1998-09-03 1998-09-03 Exhaust gas cooling and harmful substance removing method

Publications (1)

Publication Number Publication Date
JP2000070663A true JP2000070663A (en) 2000-03-07

Family

ID=17197484

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10249738A Pending JP2000070663A (en) 1998-09-03 1998-09-03 Exhaust gas cooling and harmful substance removing method

Country Status (1)

Country Link
JP (1) JP2000070663A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002079029A (en) * 2000-09-07 2002-03-19 Daido Steel Co Ltd Method for cooling exhaust gas from melting furnace

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002079029A (en) * 2000-09-07 2002-03-19 Daido Steel Co Ltd Method for cooling exhaust gas from melting furnace
JP4701485B2 (en) * 2000-09-07 2011-06-15 大同特殊鋼株式会社 Melting furnace exhaust gas cooling method

Similar Documents

Publication Publication Date Title
US6027550A (en) Apparatus and method for removing volatile organic compounds from a stream of contaminated air with use of an adsorbent material
CA1070620A (en) Apparatus for the continuous purification of exhaust gas containing solvent vapours
JP2010234335A (en) Deodorizing apparatus
US5439659A (en) Method for treating exhaust gas and an apparatus therefor
US4000993A (en) Process for scrubbing gas streams
KR20070097048A (en) Method and apparatus for treatment of exhaust gas
JP2006077225A (en) Method and apparatus for separating petroleum
JP2000070663A (en) Exhaust gas cooling and harmful substance removing method
JP2000140627A (en) Dioxin removing material, dioxin removing method and regenerating method of dioxin removing material
TW380055B (en) Exhaust gas treatment apparatus and exhaust gas treatment equipment
JP2003161586A (en) Gas cooling method and gas cooler
CN105854510B (en) A kind of VOCs processing equipment and method
JPH0139813B2 (en)
JP2003024741A (en) Combustion type semiconductor exhaust gas treatment apparatus
JP2000126550A (en) Combustion device and method for treating exhaust gas therefrom, ash cooling device therefor
JP2003089696A (en) Method for removing dioxin by catalyst ion-plasma reaction and device for removing the same
JP2003329233A (en) Exhaust gas processing device
JP2002045740A (en) Method and apparatus for removing resinous deposit occurring from coating material
US2712361A (en) Apparatus for contacting gaseous fluids with granular solids, and valve therefor
JP2002079028A (en) Exhaust gas cooling tower with dust collection part
JPH10165765A (en) Process and device for treating exhaust gas
JP2008207138A (en) Hydrocarbon removal/recovery device
JP2002066305A (en) Medium regenerating column, medium regenerating method, waste gas treating device and waste gas treating method
JPH06283186A (en) Processing of fuel exhaust gas of molten carbonate fuel cell and device therefore
JP2004344729A (en) Apparatus and method for dry treatment of hf-containing gas

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20050419

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20060428

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20080108

A02 Decision of refusal

Free format text: JAPANESE INTERMEDIATE CODE: A02

Effective date: 20080527