JP2000074349A - Method for reburning exhaust gas from refuse incinerator or the like and reburning apparatus used for the method - Google Patents

Method for reburning exhaust gas from refuse incinerator or the like and reburning apparatus used for the method

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Publication number
JP2000074349A
JP2000074349A JP10283221A JP28322198A JP2000074349A JP 2000074349 A JP2000074349 A JP 2000074349A JP 10283221 A JP10283221 A JP 10283221A JP 28322198 A JP28322198 A JP 28322198A JP 2000074349 A JP2000074349 A JP 2000074349A
Authority
JP
Japan
Prior art keywords
exhaust gas
reburning
combustion chamber
refuse incinerator
incinerator
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
JP10283221A
Other languages
Japanese (ja)
Inventor
Shinroku Nishiyama
信六 西山
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP10283221A priority Critical patent/JP2000074349A/en
Publication of JP2000074349A publication Critical patent/JP2000074349A/en
Pending legal-status Critical Current

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Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E20/00Combustion technologies with mitigation potential
    • Y02E20/34Indirect CO2mitigation, i.e. by acting on non CO2directly related matters of the process, e.g. pre-heating or heat recovery

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  • Incineration Of Waste (AREA)
  • Air Supply (AREA)

Abstract

PROBLEM TO BE SOLVED: To efficiently suppress generation of a dioxin of an exhaust gas by introducing the exhaust gas into a cylindrical combustion chamber, reburning the gas at a specific temperature or higher, passing the reburned gas through a layer of ceramic particles of a small particle size, exhausting the gas and then guiding the gas to a dust collector. SOLUTION: An exhaust gas inlet 2 connected to a refuse incinerating furnace D is provided at a lower end of a longitudinally disposed combustion chamber 1 via a duct, and an exhaust port 3 connected to a cooling tower via a duct is provided at an upper end of the chamber 1. The exhaust gas exhausted from the furnace is introduced into the chamber 1. Fuel is reburned at 800 deg.C or higher by an oxygen burner 4 for burning the fuel with high concentration oxygen. The reburned gas is passed through a layer 5 of ceramic particles of a small particle size in the chamber 1, then exhausted from the port 3, and introduced into a dust collector. Thus, generation of a dioxin of the exhaust gas can be efficiently suppressed.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本発明は、都市ゴミの焼却炉、産
業廃棄物の焼却炉等、ダイオキシンの発生が著しいその
他の焼却炉の排ガスの処理を行うところのゴミ焼却炉等
からの排ガスの再燃焼方法と該方法に用いる再燃焼装置
に関する。
The present invention relates to an incinerator for municipal garbage, an incinerator for industrial waste, and other incinerators that generate a large amount of dioxin. The present invention relates to a reburn method and a reburn apparatus used for the method.

【0002】[0002]

【従来の技術】最近、都市ゴミの焼却炉、産業廃棄物の
焼却炉等から排出される有害物質、特にダイオキシンの
規制が問題となっている。ダイオキシン発生のメカニズ
ムとして、これまでに明らかになっているのは、殆どの
可燃性物質が燃焼した際に発生するものであること、そ
の燃焼が比較的低温域、例えば、600〜700°C程
度であると一層大量に生成されること、即ち、不完全燃
焼によるCOの発生量と密接な関係があること等が分か
っている。
2. Description of the Related Art In recent years, regulations on harmful substances, particularly dioxins, emitted from incinerators for municipal waste and incinerators for industrial waste have become a problem. As a mechanism of dioxin generation, it has been clarified so far that most of combustible substances are generated when burned, and the combustion is performed in a relatively low temperature range, for example, about 600 to 700 ° C. It has been found that a larger amount of CO is generated, that is, it is closely related to the amount of CO generated by incomplete combustion.

【0003】こうした状況に鑑み、新たなゴミ焼却炉の
設計或いは既設の焼却炉についても、燃焼温度を高く維
持し、所定の時間、例えば4秒以上の燃焼を維持させ、
以て、COの発生を抑制し、結果としてダイオキシンの
発生を抑制しようとする規制が採用されるようになっ
た。勿論、規制対象とならない既設の小型のゴミ焼却炉
等においては、何らかの対処手段を講じなければならな
い状況にある。
[0003] In view of such a situation, the design of a new refuse incinerator or the existing incinerator is maintained at a high combustion temperature for a predetermined time, for example, 4 seconds or more.
Accordingly, regulations for suppressing the generation of CO and consequently the generation of dioxin have been adopted. Of course, in existing small garbage incinerators that are not subject to regulation, some countermeasures must be taken.

【0004】また、規制対象となるゴミ焼却炉等(新
規、既設)については、ゴミ焼却炉等の燃焼ゾーンに連
続させて再燃焼ゾーンを敷設することによってダイオキ
シンの発生を大幅に抑制することが義務つけされたので
あるが、これまでに、再燃焼ゾーンを通過した排ガスに
ついて、未だダイオキシンの発生を検出するにつき、種
々の原因が検討され、究明されてきており、その中にお
いて、ゴミ焼却炉を出た排ガスがダクトを通して冷却塔
(或いは熱交換器)、集塵機に至る過程において、ダイ
オキシンの再合成があるものと推定されており、この再
合成のメカニズムについて解明がなされていない。
[0004] Regarding refuse incinerators and the like (new and existing) to be regulated, it is possible to greatly suppress the generation of dioxin by laying a reburn zone continuously to the combustion zone of the refuse incinerator and the like. Although it was obliged, various causes have been examined and investigated to detect the generation of dioxin in the exhaust gas that has passed through the reburning zone. It is presumed that dioxin is resynthesized in the process in which the exhaust gas exiting through the duct reaches the cooling tower (or heat exchanger) and the dust collector, and the mechanism of the resynthesis has not been elucidated.

【0005】[0005]

【発明が解決しようとする課題】本発明者は、こうした
状況に鑑み、再燃焼ゾーンを備えないゴミ焼却炉等及び
再燃焼ゾーンを備えたゴミ焼却炉等について、この排気
ダクト通過時における温度低下と、残留COが原因とな
ってダイオキシンの再合成が生じているのではないかと
推測した。
In view of these circumstances, the present inventor has found that the temperature of a refuse incinerator or the like without a reburn zone and a refuse incinerator with a reburn zone when passing through the exhaust duct are reduced. It was speculated that dioxin may be resynthesized due to residual CO.

【0006】そこで、ゴミ焼却炉等の次工程において、
別途、排ガスを再燃焼させることを考えたが、単に、再
燃焼室を敷設し、ゴミ焼却炉の再燃焼ゾーンの如く空気
を補給するだけでは、残留COの完全燃焼を達成し難い
という間題があり、また、排ガスは、集塵機のブロワに
よって引かれていて、比較的速い流速でダクトを流れて
いるので、このまま再燃焼室を通過すれば、時間的に十
分な再燃焼作用を受けることが難しいという問題もあ
る。加えて、格別に撹拌作用が付与されているわけでは
ないので、排ガスの全体に亘って再燃焼作用を十分に及
ぼすというのも難しい。
Therefore, in the next process such as a garbage incinerator,
Separately, we considered re-burning the exhaust gas, but it was difficult to achieve complete combustion of residual CO simply by laying a re-burning chamber and supplying air as in the re-burning zone of a garbage incinerator. In addition, exhaust gas is drawn by the blower of the dust collector and flows through the duct at a relatively high flow rate. There is also a problem that it is difficult. In addition, since the stirring action is not particularly provided, it is difficult to sufficiently exert the reburning action over the entire exhaust gas.

【0007】本発明は、こうした現状に鑑み、ゴミ焼却
炉等(再燃焼室の有無に関わりなく)から排出される排
ガスのダイオキシン発生を効率良く抑制する方法と、該
方法に用いる再燃焼装置を提供することを目的とする。
In view of the above situation, the present invention provides a method for efficiently suppressing the generation of dioxin in exhaust gas discharged from a refuse incinerator or the like (with or without a reburning chamber) and a reburning apparatus used in the method. The purpose is to provide.

【0008】[0008]

【課題を解決するための手段】本発明にかかるゴミ焼却
炉等からの排ガスの再燃焼方法は、上記目的を達成する
為に、ゴミ焼却炉等から排出された排ガスを冷却手段を
用いて冷却し、その後、集塵機を介して大気に放出する
ところのゴミ焼却炉等から排出される排ガスの再燃焼方
法であって、ゴミ焼却炉等から排出された排ガスを筒状
の燃焼室に導入し、燃料を高濃度酸素で燃焼させる酸素
バーナーによって800°C以上で再燃焼させ、且つ、
該燃焼室内において、この再燃焼ガスを、小径のセラミ
ック粒の層を通過させてから排気して集塵機に導く、と
いう手段を講じた。
According to the method for reburning exhaust gas from a refuse incinerator or the like according to the present invention, the exhaust gas discharged from the refuse incinerator or the like is cooled using cooling means in order to achieve the above object. Then, after that, a method of reburning exhaust gas discharged from a garbage incinerator or the like that is released to the atmosphere via a dust collector, wherein the exhaust gas discharged from the garbage incinerator or the like is introduced into a cylindrical combustion chamber, The fuel is reburned at 800 ° C. or higher by an oxygen burner that burns the fuel with high concentration oxygen, and
In the combustion chamber, a measure was taken in which the reburn gas was passed through a layer of small-diameter ceramic particles, then exhausted, and led to a dust collector.

【0009】本発明において、上記燃焼室が縦向きとさ
れ、排ガスが下方から上方に流れ、該燃焼室内での排ガ
スの再燃焼時間が4秒以上であるのが好ましい。
In the present invention, it is preferable that the combustion chamber is oriented vertically, exhaust gas flows upward from below, and the reburning time of the exhaust gas in the combustion chamber is preferably 4 seconds or more.

【0010】本発明において、上記小径のセラミック粒
が粒径、0.5ミリ乃至5ミリであるのが好ましい。
In the present invention, the small-diameter ceramic particles preferably have a particle size of 0.5 mm to 5 mm.

【0011】本発明にかかるゴミ焼却炉等からの排ガス
の再燃焼装置は、上記目的を達成する為に、ゴミ焼却炉
等から排出された排ガスを冷却手段を用いて冷却し、そ
の後、集塵機を介して大気に放出するところのゴミ焼却
炉等から排出される排ガスの再燃焼装置であって、ゴミ
焼却炉等に接続された筒状の燃焼室1の一端部に排ガス
の流入口2を設けると共にその他端に排気口3を設け、
前記燃焼室1の流入口2側に、燃料を高濃度酸素で燃焼
させて排ガスを800゜C以上で再燃焼させる酸素バー
ナー4を設け、且つ、該燃焼室1の長手方向の略中間位
置に、該燃焼室1の長手方向に直交するように小径のセ
ラミック粒の層5を設けた、という手段を講じた。
In order to achieve the above object, the apparatus for reburning exhaust gas from a refuse incinerator or the like according to the present invention cools the exhaust gas discharged from the refuse incinerator or the like by using cooling means, and then switches the dust collector. A reburning device for exhaust gas discharged from a garbage incinerator or the like which is released to the atmosphere via a refuse incinerator, wherein an exhaust gas inlet 2 is provided at one end of a cylindrical combustion chamber 1 connected to the garbage incinerator or the like. At the same time, an exhaust port 3 is provided
An oxygen burner 4 that burns fuel with high-concentration oxygen and reburns exhaust gas at 800 ° C. or higher is provided on the inflow port 2 side of the combustion chamber 1, and is provided at a substantially middle position in the longitudinal direction of the combustion chamber 1. A means was provided in which a layer 5 of small-diameter ceramic grains was provided so as to be orthogonal to the longitudinal direction of the combustion chamber 1.

【0012】本発明において、上記燃焼室1が縦向きに
配置され、前記流入口2がその下端側に位置されると共
に排気口3が上端側に位置され、該燃焼室の長さが、排
ガスの再燃焼時間が4秒以上となるように設定されてい
るのが好ましい。
In the present invention, the combustion chamber 1 is arranged vertically, the inflow port 2 is located at the lower end side, and the exhaust port 3 is located at the upper end side. Is preferably set so as to be 4 seconds or more.

【0013】本発明において、上記小径のセラミック粒
が粒径、0.5ミリ乃至5ミリであり、該セラミック粒
の層5が厚さ、300ミリ乃至600ミリであるのが好
ましい。
In the present invention, the small-diameter ceramic grains preferably have a particle size of 0.5 mm to 5 mm, and the layer 5 of the ceramic grains preferably has a thickness of 300 mm to 600 mm.

【0014】尚、本発明にいうゴミ焼却炉等とは、都市
ゴミの焼却炉、産業廃棄物の焼却炉、その他、各種の焼
却設備を対象として含む。
The garbage incinerator and the like referred to in the present invention include municipal garbage incinerators, industrial waste incinerators, and various other incinerators.

【0015】[0015]

【発明の実施の態様】本発明によれば、ゴミ焼却炉等か
ら排出された排ガスを筒状の燃焼室に導入し、燃料を高
濃度酸素で燃焼させる酸素バーナーによって800°C
以上で再燃焼させることで、単に通常の空気を付加する
焼却炉の再燃焼ゾーンに比して、高温で、且つ、十分な
酸素によって完全燃焼が期待でき、排ガス中の残留CO
を殆ど無くすることができ、これに起因するダイオキシ
ンの再合成が抑制できる。
According to the present invention, exhaust gas discharged from a refuse incinerator or the like is introduced into a cylindrical combustion chamber, and the fuel is burned at 800 ° C. by a high-concentration oxygen burner.
By performing the reburning as described above, complete combustion can be expected at a higher temperature and with sufficient oxygen compared to the reburning zone of the incinerator simply adding ordinary air, and the residual CO in the exhaust gas can be expected.
Can be almost eliminated, and the resynthesis of dioxin due to this can be suppressed.

【0016】そして、燃焼室内において、この再燃焼ガ
スを、小径のセラミック粒(0.5ミリ乃至5ミリ)の
層(300ミリ乃至600ミリ)を通過させてから排気
するのが、このセラミック粒の層が酸素バーナーによる
熱量を蓄熱し、熱効率のよい状態で再燃焼を行うことが
できる。 同時に、セラミック粒を白熱加熱しているの
で、排ガスがこのセラミック粒の層を通過する際に十分
に接触加熱されて依り一層の完全燃焼を達成できる。
Then, in the combustion chamber, the reburned gas is exhausted after passing through a layer (300 mm to 600 mm) of small-diameter ceramic particles (0.5 mm to 5 mm). This layer stores the amount of heat by the oxygen burner, and can perform reburning with good thermal efficiency. At the same time, because the ceramic particles are incandescently heated, the exhaust gas is sufficiently contact heated as it passes through this layer of ceramic particles, so that more complete combustion can be achieved.

【0017】更に、排ガスがこのセラミック粒の隙間を
紆余曲折しながら通過することによって排ガスの燃焼室
内での滞留時間を長く確保でき、燃焼室自体を長いもの
に構成しなくても、所要の燃焼時間(4秒以上)を容易
に確保できる。
Furthermore, since the exhaust gas passes through the gaps between the ceramic grains while twisting and bending, a long residence time of the exhaust gas in the combustion chamber can be ensured. Even if the combustion chamber itself is not long, the required combustion can be achieved. Time (4 seconds or more) can be easily secured.

【0018】また、燃焼室を縦型として、その下方から
排ガスを流入させ、上方から排出する場合には、前記セ
ラミック粒の層に対して下方から排ガスが吹き上げる状
態となって、支持枠(篭)に入れたセラミック粒が僅か
に持ち上がる状態で、セラミック粒の隙間を詰める(下
向き流れの場合に発生し易い)といった状態もなく、寧
ろ僅かに浮揚状態で隙間を通過させることができて、ブ
ロワの吸引負圧増大を招くことなく、上述した完全燃焼
を達成できる。
Further, when the combustion chamber is of a vertical type, and the exhaust gas flows in from below and discharges the exhaust gas from above, the exhaust gas blows up from below the ceramic particle layer, and the support frame (basket) )), The gap between the ceramic grains is not filled (it is likely to occur in the case of downward flow), and the ceramic grains can be passed through the gap in a slightly floating state. The above-described complete combustion can be achieved without increasing suction negative pressure.

【0019】しかし、この燃焼室は、勿論、上方から排
ガスを流入させ、下方から排出する形態を採用しても、
所期の目的は十分に達成できるものである。
However, this combustion chamber may, of course, adopt a configuration in which exhaust gas is introduced from above and discharged from below.
The intended purpose is fully achievable.

【0020】[0020]

【実施例】本発明のゴミ焼却炉等からの排ガスの再燃焼
方法と該方法に用いる再燃焼装置の好適実施例について
以下図面に基づいて詳述する。図1は、本発明の再燃焼
装置の敷設を示す概略説明図であり、Dは、ゴミ焼却炉
を示し、ここから排出された排ガスは、ダクトを通り、
再燃焼装置Aに導入され、ここで再燃焼作用を受けた
後、冷却塔B(ここでは水冷塔)において所定温度に冷
却され、しかる後に集塵機C(ここではバグフィルター
型)において濾過され、大気に放出される。 これら冷
却塔B、集塵機Cは公知の構成のものであるので、ここ
での詳細説明は省略する。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Preferred embodiments of a method for reburning exhaust gas from a refuse incinerator and the like and a reburning apparatus used in the method according to the present invention will be described below in detail with reference to the drawings. FIG. 1 is a schematic explanatory view showing the laying of the reburning device of the present invention, D shows a refuse incinerator, and exhaust gas discharged from the incinerator passes through a duct,
After being introduced into the reburning device A, where it is subjected to the reburning action, it is cooled to a predetermined temperature in a cooling tower B (here, a water cooling tower), and then filtered in a dust collector C (here, a bag filter type), and Will be released. Since the cooling tower B and the dust collector C have a known configuration, a detailed description thereof will be omitted.

【0021】図2は、排ガスの再燃焼装置Aの縦断面を
示し、略円形の筒状に構成されて、縦向きに配置された
燃焼室1の一端部(下端部)に、ダクトを介してゴミ焼
却炉Dに接続される排ガスの流入口2を設け、また、そ
の他端(上端部)に、ダクトを介して冷却塔Bに接続さ
れる排気口3を設けてある。 因みに、この実施例で
は、燃焼室1は、内径2.4m、流入口2の中心と排気
口3中心との間(長さ)が、約10mであり、全体とし
て、排ガスの再燃焼時間が4秒以上となるように設定さ
れている。
FIG. 2 shows a longitudinal section of the exhaust gas reburning apparatus A, which is formed in a substantially circular cylindrical shape, and is provided with a duct at one end (lower end) of a vertically arranged combustion chamber 1. An exhaust gas inlet 2 connected to the refuse incinerator D is provided, and an exhaust port 3 connected to the cooling tower B via a duct is provided at the other end (upper end). Incidentally, in this embodiment, the combustion chamber 1 has an inner diameter of 2.4 m, a distance (length) between the center of the inflow port 2 and the center of the exhaust port 3 is about 10 m, and the reburning time of the exhaust gas as a whole is It is set to be 4 seconds or more.

【0022】そして、前記燃焼室1の流入口2側に、燃
料を高濃度酸素で燃焼させて排ガスを800°C以上で
再燃焼させる酸素バーナー4を設けてある。 この燃料
は、ここではLPGを用いているが、その他の気体、液
体燃料を用いてよい。 また、酸素バーナー4の構造
は、通常の構成のものであればよい。この酸素バーナー
4は、高濃度の酸素を用いることで燃焼温度が非常に高
い(火炎は200°C前後)もので、排ガスを800°
C以上に容易に加熱できるが、通常の空気のように窒素
含有量が少ないことで、窒素酸化物の発生も少なくでき
る。
On the inlet 2 side of the combustion chamber 1, there is provided an oxygen burner 4 for burning fuel with high-concentration oxygen and reburning exhaust gas at 800 ° C. or higher. This fuel uses LPG here, but other gas or liquid fuels may be used. In addition, the structure of the oxygen burner 4 may be any ordinary structure. This oxygen burner 4 has a very high combustion temperature (flame is around 200 ° C.) by using high-concentration oxygen.
Although it can be heated more easily than C, the generation of nitrogen oxides can be reduced because the nitrogen content is low like ordinary air.

【0023】上記燃焼室1の長手方向の略中間位置に、
該燃焼室1の長手方向に直交するように小径のセラミッ
ク粒の層5を設けている。 このセラミック粒の層5
は、この実施例では、セラミック粒の粒径が、0.5ミ
リ〜1ミリのもので構成されており、該セラミック粒の
層5が厚さは、500ミリ前後である。 しかし、セラ
ミック粒の粒径としは、5ミリ程度は、勿論、これより
も大きな1cm〜2cm程度のものを用いても良く、ま
た、セラミック粒の層5の厚さも、300ミリ乃至60
0ミリ程度としても良い。勿論、こうしたサイズは、燃
焼室1の規模、流速によって適宜変わることは言うまで
もない。
At a substantially middle position in the longitudinal direction of the combustion chamber 1,
A layer 5 of small-diameter ceramic grains is provided so as to be orthogonal to the longitudinal direction of the combustion chamber 1. Layer 5 of this ceramic grain
In this embodiment, the ceramic particles have a particle size of 0.5 mm to 1 mm, and the thickness of the layer 5 of the ceramic particles is about 500 mm. However, the grain size of the ceramic grains is, for example, about 5 mm, and of course, a larger grain size of about 1 cm to 2 cm may be used, and the thickness of the ceramic grain layer 5 may be 300 mm to 60 mm.
It may be about 0 mm. Of course, it goes without saying that such a size appropriately changes depending on the scale and the flow velocity of the combustion chamber 1.

【0024】そして、このセラミック粒の層5は、グリ
ッド7に支えられた支持枠6(篭)に収容されている。
このセラミック粒の収容については、加圧状態で詰め
込むのではなく、下方からの排ガスの通過によって多少
浮揚するごとき余裕がある状態で収容されている。
The layer 5 of ceramic grains is accommodated in a support frame 6 (cage) supported by a grid 7.
The ceramic particles are not packed in a pressurized state, but are housed in a state where there is a margin such that the ceramic particles slightly float due to the passage of exhaust gas from below.

【0025】図2において、8は、夫々温度センサーを
示し、9は、ダストドレイン、10は、安全弁を示す。
In FIG. 2, 8 denotes a temperature sensor, 9 denotes a dust drain, and 10 denotes a safety valve.

【0026】従って、上記排ガスの再燃焼方法は、 ゴミ焼却炉等から排出された排ガスを筒状の燃焼室
に導入し、 燃料としてのLPGを高濃度酸素(酸素濃度50%
以上)で燃焼させる酸素バーナーによって800゜C以
上で再燃焼させ、 該燃焼室内において、この再燃焼ガスを、小径のセ
ラミック粒の層を通過させてから排気して集塵機に導
く、 というステップで実施される。
Therefore, in the above-mentioned method for reburning exhaust gas, exhaust gas discharged from a refuse incinerator or the like is introduced into a cylindrical combustion chamber, and LPG as fuel is converted into high-concentration oxygen (oxygen concentration 50%).
The reburning is performed at 800 ° C. or more by the oxygen burner burned in the above), and in the combustion chamber, the reburned gas is exhausted after passing through a layer of small-diameter ceramic particles and guided to a dust collector. Is done.

【0027】この場合、上記燃焼室が縦向きとされてお
り、排ガスが下方から上方に流れ、該燃焼室内での排ガ
スの再燃焼時間が4秒以上とされている。また、上記小
径のセラミック粒が粒径、0.5ミリ乃至5ミリであ
り、セラミック粒の層を通過して、白熱状態のセラミッ
ク粒との接触によって排ガスの全体に亘っての排ガスの
再燃焼が行われる。 また、セラミック粒がバーナーの
燃焼熱量を蓄積することができるので、熱効率の良い状
態で再燃焼を行うことができる。
In this case, the combustion chamber is oriented vertically, the exhaust gas flows upward from below, and the reburning time of the exhaust gas in the combustion chamber is set to 4 seconds or more. The small-diameter ceramic particles have a particle size of 0.5 mm to 5 mm, and pass through a layer of the ceramic particles and re-burn the exhaust gas over the entire exhaust gas by contact with the incandescent ceramic particles. Is performed. In addition, since the ceramic particles can accumulate the heat of combustion of the burner, reburning can be performed with good thermal efficiency.

【0028】上述した本発明の方法及び装置を用いた結
果、燃焼室1の出口における排ガスの残留COは、測定
の結果、その入口における排ガスの1/4〜1/5に迄
減少させることができたものであり、その結果、COを
因子とするダイオキシンの発生及び再合成が、これに比
例して大幅に減少されることになるものと推定されるの
である。
As a result of using the above-described method and apparatus of the present invention, the residual CO of the exhaust gas at the outlet of the combustion chamber 1 can be reduced to 1 / to 5 of the exhaust gas at the inlet as a result of the measurement. It is presumed that as a result, the generation and resynthesis of dioxin with CO as a factor will be significantly reduced in proportion to this.

【0029】[0029]

【発明の効果】本発明によれば、ゴミ焼却炉等からの排
ガスを高濃度酸素バーナーを用いて再燃焼させて残留C
Oを無くし、更に、再燃焼排ガスをセラミック粒の層を
通過させることで長い時間に亘って十分に接触させて完
全燃焼を一層確実なものとして、同時にセラミック粒に
蓄熱して熱効率のよい状態で再燃焼を行い、以て、再燃
焼ゾーンを備えていない焼却炉は勿論、再燃焼ゾーンが
ある場合も、この焼却炉を出た後に再合成されると見ら
れているダイオキシンの発生を大幅に抑制できる利点が
ある。本発明のその他の利点は、上述の発明の実施の態
様及び実施例に項において詳述した通りである。
According to the present invention, the exhaust gas from a garbage incinerator or the like is reburned by using a high-concentration oxygen burner to remove residual C.
O is eliminated, and furthermore, the reburning exhaust gas is passed through the layer of the ceramic particles so that the exhaust gas is sufficiently contacted for a long time to ensure complete combustion. At the same time, the heat is stored in the ceramic particles and the heat efficiency is improved. After reburning, even if there is a reburn zone as well as an incinerator without a reburn zone, the generation of dioxin, which is considered to be recombined after leaving this incinerator, is greatly reduced. There is an advantage that can be suppressed. Other advantages of the present invention are as described in detail in the above-mentioned embodiments and examples of the present invention.

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

【図1】本発明にかかる排ガスの再燃焼装置を配置した
全体の説明図である。
FIG. 1 is an overall explanatory diagram in which an exhaust gas reburning device according to the present invention is arranged.

【図2】本発明にかかる排ガスの再燃焼装置の縦断側面
図である。
FIG. 2 is a vertical side view of the exhaust gas reburning apparatus according to the present invention.

【符号の説明】[Explanation of symbols]

1 燃焼室 2 排ガスの流入口 3 排気口 4 酸素バーナー 5 セラミック粒の層 DESCRIPTION OF SYMBOLS 1 Combustion chamber 2 Exhaust gas inflow port 3 Exhaust port 4 Oxygen burner 5 Layer of ceramic particles

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】ゴミ焼却炉等から排出された排ガスを冷却
手段を用いて冷却し、その後、集塵機を介して大気に放
出するところのゴミ焼却炉等から排出される排ガスの再
燃焼方法であって、 ゴミ焼却炉等から排出された排ガスを筒状の燃焼室に導
入し、燃料を高濃度酸素で燃焼させる酸素バーナーによ
って800°C以上で再燃焼させ、 且つ、該燃焼室内において、この再燃焼ガスを、小径の
セラミック粒の層を通過させてから排気して集塵機に導
く、ゴミ焼却炉等からの排ガスの再燃焼方法。
A method for reburning exhaust gas discharged from a refuse incinerator or the like, wherein the exhaust gas discharged from a refuse incinerator or the like is cooled using cooling means and then discharged to the atmosphere via a dust collector. Then, the exhaust gas discharged from a refuse incinerator or the like is introduced into a cylindrical combustion chamber, and reburned at 800 ° C. or higher by an oxygen burner that burns the fuel with high concentration oxygen. A method for reburning exhaust gas from a garbage incinerator or the like, in which the combustion gas is exhausted after passing through a layer of small-diameter ceramic particles and guided to a dust collector.
【請求項2】上記燃焼室が縦向きとされ、排ガスが下方
から上方に流れ、該燃焼室内での排ガスの再燃焼時間が
4秒以上である、請求項1のゴミ焼却炉等からの排ガス
の再燃焼方法。
2. The exhaust gas from a refuse incinerator or the like according to claim 1, wherein said combustion chamber is oriented vertically, exhaust gas flows upward from below, and the exhaust gas reburn time in said combustion chamber is 4 seconds or more. Reburn method.
【請求項3】上記小径のセラミック粒が粒径、0.5ミ
リ乃至5ミリである請求項1又は2のゴミ焼却炉等から
の排ガスの再燃焼方法。
3. The method for reburning exhaust gas from a refuse incinerator or the like according to claim 1, wherein said small-diameter ceramic particles have a particle size of 0.5 mm to 5 mm.
【請求項4】ゴミ焼却炉等から排出された排ガスを冷却
手段を用いて冷却し、その後、集塵機を介して大気に放
出するところのゴミ焼却炉等から排出される排ガスの再
燃焼装置であって、 ゴミ焼却炉等に接続された筒状の燃焼室1の一端部に排
ガスの流入口2を設けると共にその他端に排気口3を設
け、 前記燃焼室1の流入口2側に、燃料を高濃度酸素で燃焼
させて排ガスを800゜C以上で再燃焼させる酸素バー
ナー4を設け、 且つ、該燃焼室1の長手方向の略中間位置に、該燃焼室
1の長手方向に直交するように小径のセラミック粒の層
5を設けた、ゴミ焼却炉等からの排ガスの再燃焼装置。
4. A reburning device for exhaust gas discharged from a refuse incinerator or the like, which cools the exhaust gas discharged from a refuse incinerator or the like using a cooling means and then discharges the exhaust gas to the atmosphere via a dust collector. An exhaust gas inlet 2 is provided at one end of a cylindrical combustion chamber 1 connected to a refuse incinerator or the like, and an exhaust port 3 is provided at the other end. An oxygen burner 4 that burns with high-concentration oxygen and reburns exhaust gas at 800 ° C. or higher is provided, and is provided at a substantially middle position in the longitudinal direction of the combustion chamber 1 so as to be orthogonal to the longitudinal direction of the combustion chamber 1. An apparatus for reburning exhaust gas from a garbage incinerator or the like, provided with a layer 5 of small-diameter ceramic particles.
【請求項5】上記燃焼室1が縦向きに配置され、前記流
入口2がその下端側に位置されると共に排気口3が上端
側に位置され、該燃焼室の長さが、排ガスの再燃焼時間
が4秒以上となるように設定されている、請求項4のゴ
ミ焼却炉等からの排ガスの再燃焼装置。
5. The combustion chamber 1 is arranged vertically, the inflow port 2 is located at a lower end thereof, and the exhaust port 3 is located at an upper end side. The apparatus for reburning exhaust gas from a refuse incinerator or the like according to claim 4, wherein the combustion time is set to be 4 seconds or more.
【請求項6】上記小径のセラミック粒が粒径、0.5ミ
リ乃至5ミリであり、該セラミック粒の層5が厚さ、3
00ミリ乃至600ミリである、請求項4又は5のゴミ
焼却炉等からの排ガスの再燃焼装置。
6. The ceramic particle having a small diameter is 0.5 to 5 mm in diameter, and the layer 5 of the ceramic particle has a thickness of 3 mm.
The apparatus for reburning exhaust gas from a refuse incinerator or the like according to claim 4 or 5, wherein the diameter is from 00 mm to 600 mm.
JP10283221A 1998-08-29 1998-08-29 Method for reburning exhaust gas from refuse incinerator or the like and reburning apparatus used for the method Pending JP2000074349A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10283221A JP2000074349A (en) 1998-08-29 1998-08-29 Method for reburning exhaust gas from refuse incinerator or the like and reburning apparatus used for the method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10283221A JP2000074349A (en) 1998-08-29 1998-08-29 Method for reburning exhaust gas from refuse incinerator or the like and reburning apparatus used for the method

Publications (1)

Publication Number Publication Date
JP2000074349A true JP2000074349A (en) 2000-03-14

Family

ID=17662673

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10283221A Pending JP2000074349A (en) 1998-08-29 1998-08-29 Method for reburning exhaust gas from refuse incinerator or the like and reburning apparatus used for the method

Country Status (1)

Country Link
JP (1) JP2000074349A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6785082B2 (en) 2001-10-30 2004-08-31 Seagate Technology Llc Disc drive servo track writer utilizing low-density gas

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6785082B2 (en) 2001-10-30 2004-08-31 Seagate Technology Llc Disc drive servo track writer utilizing low-density gas

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