JPH0474581A - Method for incinerating waste with reduced carbon dioxide generation - Google Patents

Method for incinerating waste with reduced carbon dioxide generation

Info

Publication number
JPH0474581A
JPH0474581A JP2189194A JP18919490A JPH0474581A JP H0474581 A JPH0474581 A JP H0474581A JP 2189194 A JP2189194 A JP 2189194A JP 18919490 A JP18919490 A JP 18919490A JP H0474581 A JPH0474581 A JP H0474581A
Authority
JP
Japan
Prior art keywords
combustion
waste
furnace
melting
matter
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
JP2189194A
Other languages
Japanese (ja)
Inventor
Satoshi Kawachi
敏 河内
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.)
JGC Corp
Original Assignee
JGC Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by JGC Corp filed Critical JGC Corp
Priority to JP2189194A priority Critical patent/JPH0474581A/en
Publication of JPH0474581A publication Critical patent/JPH0474581A/en
Pending legal-status Critical Current

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  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (AREA)

Abstract

PURPOSE:To contrive a treatment of waste wherein generation of carbon dioxide is reduced by incompletly burning waste to leave unburnt matter and fixing the non-combustion matter in a molten body. CONSTITUTION:Waste dried if necessary, is burnt in a primary combustion furnace, that is, a partial combustion melting furnace by air whose amount is equal to or less than a theoretical air ratio but generates quantity of heat sufficient to reach temp. melting formed ash, for example, 1300 - 1450 deg.C. Subsequently, the combustion gas from the partial combustion melting furnace is burnt in a secondary combustion furnace. The secondary combustion furnace may be integrated with or separated from the primary combustion furnace. To give the instance of the incineration and melting of sewage sludge, the solid unburnt matter falling from a primary combustion chamber 1 comes into contact with a molten body (8b) of ash before it comes into contact with secondary air to be fixed therein. Gaseous unburnt (incomplete combustion matter is burnt by secondary air blown in thereafter and exhaust gas is raised in temp. to issued from an exhaust gas outlet (3).

Description

【発明の詳細な説明】[Detailed description of the invention] 【産業上の利用分野】[Industrial application field]

本発明は、廃棄物とくに下水汚泥や都市ゴミの焼却処理
に当って、炭酸ガスの発生量を減らした焼却方法に関す
る。
The present invention relates to an incineration method that reduces the amount of carbon dioxide gas generated when incinerating waste, particularly sewage sludge and municipal garbage.

【従来の技術】[Conventional technology]

下水汚泥や都市ゴミのような固体廃棄物は、大量に発生
するものであり、屹燥させれば4000〜5000 k
cal /Kyの熱量をもっていることから、焼却して
減容処理することが一般的である。 一方、炭酸ガスは地球の温暖化を促進するものとして、
産業および生活の両面において、その排出量を抑制する
ことが企てられている。 従って、廃棄物の焼却処理に
おいても、炭酸カスの発生量をできるだ(プ減らすこと
か望ましい。
Solid wastes such as sewage sludge and municipal waste are generated in large quantities, and if dried, they will weigh 4,000 to 5,000 kg.
Since it has a calorific value of cal/Ky, it is generally incinerated to reduce its volume. On the other hand, carbon dioxide gas is considered to promote global warming.
Efforts are being made to reduce emissions in both industry and daily life. Therefore, it is desirable to reduce the amount of carbon dioxide generated during waste incineration.

【発明が解決しようとする課題] 本発明の目的は、廃棄物の焼却という避けられない処理を行なうに当って、炭酸カスの発生を減らした処理を可能にすることにある。 【課題を解決するだめの手段】[Problem to be solved by the invention] An object of the present invention is to enable a process that reduces the generation of carbon dioxide when incinerating waste, which is an inevitable process. [Means to solve the problem]

本発明の廃棄物の焼却方法は、焼却により生成した灰分
が溶融体を形成する廃棄物の焼却において、廃棄物を不
完全に燃焼させて未燃焼物を残し、この未燃焼物をよ2
記の溶融体中に固定することにより炭酸ガスの発生を減
らした廃棄物の焼却方法である。 この方法で焼却できる廃棄物には、上記した下水汚泥お
よび都市ゴミのほか、床扉や産業廃水の汚泥が含まれる
。 乾燥した廃棄物の発熱量が4000 Kca、I!
 /に9以上で、1300’C以下で溶融する灰分があ
る程度含まれている廃棄物が好ましいが、いずれにせよ
、灰分溶融にとって過剰の熱量すなわら廃棄物それ白身
のもつ熱量の一部を使っただけで灰分の溶融温度に達す
るだけの発熱量があれば、本発明の対象とすることかで
きる。 一般に生汚泥はこの条件をみたすが、乾燥を必要とする
。 たとえば下水汚泥では、水分10%以下にすべきで
ある。 消化汚泥は熱量が不足して使用できない。 廃棄物を部分燃焼させるための一次空気は、要するに生
成する灰分が溶融する温度に到達するだけの発熱を確保
するという観点から決定づる。 好適な空気の量は、完全燃焼に要する空気の量を1とす
るとき、通常は0.7〜0.9程度である。 燃焼により生成する灰分が未燃焼物の固定にとって不足
する場合、またはスラグの溶融温度を低くしたり溶融粘
度を小さくしたりすることを望む場合には、溶融助剤を
添加することか好ましい。 溶融助剤は、生成する灰分の組成、とくにその塩基度に
応じてえらぶ。 一般に、(灰分中の塩基性成分) /
 (S i 02 )の比が0.5〜・1.5の範囲に
なるように溶融助剤の種類と量を選択ずれば、溶融温度
の低下に役立つ。 人手容易であって安価な溶融助剤は
、石灰やシラスである。
In the waste incineration method of the present invention, in incineration of waste in which the ash produced by incineration forms a molten body, the waste is incompletely combusted to leave unburned matter, and this unburned matter is recycled.
This is a method of incinerating waste that reduces the generation of carbon dioxide gas by fixing it in the molten material described above. Wastes that can be incinerated in this way include the sewage sludge and municipal waste mentioned above, as well as floor sludge and industrial wastewater sludge. The calorific value of the dry waste is 4000 Kca, I!
It is preferable to use waste that contains a certain amount of ash that melts at a temperature of 9 or higher and 1,300°C or lower. If it has enough heat to reach the melting temperature of ash just by using it, it can be covered by the present invention. Raw sludge generally meets this requirement, but requires drying. For example, sewage sludge should have a moisture content of 10% or less. Digested sludge cannot be used due to lack of heat. The primary air for partial combustion of waste is determined from the viewpoint of ensuring sufficient heat generation to reach a temperature at which the ash produced melts. A suitable amount of air is usually about 0.7 to 0.9, where the amount of air required for complete combustion is 1. When the ash produced by combustion is insufficient for fixing unburned materials, or when it is desired to lower the melting temperature or melt viscosity of the slag, it is preferable to add a melting aid. The melting aid is selected depending on the composition of the ash to be produced, especially its basicity. Generally, (basic component in ash) /
Selecting the type and amount of the melting aid so that the ratio of (S i 02 ) is in the range of 0.5 to .1.5 helps lower the melting temperature. Lime and shirasu are easy-to-handle and inexpensive melting aids.

【作 用】[For use]

発明者は、廃棄物の焼却処理を研究した過程で、焼却炉
への下水汚泥の供給量が過大であった場合、汚泥の粒子
径が大きかった場合、および炉に吹き込んだ空気量が不
足であった場合、に未燃焼成分が溶融灰中に固定される
ことを経験して、本発明を着想した。 本発明の方法の代表的なフローを示せば第1図のとおり
であって、必要により乾燥した廃棄物を、−次燃焼炉す
なわち部分燃焼溶融炉において、理論空気比以下ではあ
るが、生成灰分が溶融する温度たとえば1300〜14
50℃に到達するに足りる熱量を発生させるだ
In the process of researching waste incineration, the inventor found that the amount of sewage sludge supplied to the incinerator was excessive, the particle size of the sludge was large, and the amount of air blown into the incinerator was insufficient. The present invention was conceived based on the experience that unburnt components are fixed in molten ash in some cases. A typical flow of the method of the present invention is shown in Fig. 1, in which the dried waste is transferred to a secondary combustion furnace, that is, a partial combustion melting furnace, where the ash content is lower than the stoichiometric air ratio. For example, the temperature at which it melts is 1300 to 14
Generates enough heat to reach 50℃

【プの空
気量で燃焼させる。 続いて、二次燃焼炉において、部分燃焼溶融炉からの燃
焼ガスを燃焼させる。 このガス中には若干のCOが含
まれているので、排出に先立ってそれを燃焼させ、□無
害にするためである。 下水汚泥や都市ゴミのような廃
棄物の燃焼においては、燃焼が不完全に止まる量の空気
比であっても、生成したC(高分子炭素化合物を含めて
)が溶融した灰にすみやかに固定されることによって、
CとCO2との反応によるCOの生成は比較的少なくて
済むことがわかった。 二次燃焼炉は、後記する例のよ
うに一次燃焼炉と一体であっても、また別体であっても
よい。 燃焼排ガスは高温であるから、上部二種の炉に供給する
空気を予熱するのに使用するほか、乾燥機にお(プる廃
棄物の乾燥に利用するとよい。 下水汚泥の焼却溶融に例をとると、たとえば第2図に示
すような構造の炉が使用される。 立型の一次燃焼炉(
1)中で、供給口(4)から投入された廃棄物は、−次
空気人口(5)からの空気によって大部分か燃焼し、生
成した灰分(8A)が溶融体となって炉壁を流下して二
次燃焼室(2)の底にたまり、出口(7A)から排出さ
れる。 −次燃焼室で燃えきらなかった未燃焼物が二次燃焼室へ
落下してきても、その入口(図で左端)に位置する二次
空気吹込み口(6A)から供給される空気によって燃焼
する。 この種の炉を使用して本発明の方法を実施するには、第
3図に示すような若干の改造を行なう。 すなわち、灰分の溶融体の排出口(7B)を、二次燃焼
室の底部ではあるが一次燃焼室の直下に位置させるとと
もに、二次空気の供給口(6B)を、それより排ガス出
口(3)側に移す。 −次燃焼室の空気比を第2図の場
合より低くすることはもちろんである。 これにより、
−次燃焼室から落下した固形の未燃焼物は、二次空気に
接しないうちに灰分の溶融体(8B)に接触して、その
中に固定される。 ガス状の未燃焼(不完全燃焼)物は
、その後に吹き込まれた二次空気により燃焼し、排ガス
温度を高めて排ガス出口(3)から出る。 図示した例は旋回溶融炉であるが、表面溶融炉も使用で
きる。 【実施例】 乾燥した下水汚泥(乾燥重量基準で発熱量4230 k
ca!J/Ky)を、第3図に示した構造の装置を用い
て、1400℃で焼却処理した。 汚泥の供給速度は1
550Kg/hr、空気比0.8である。 結果を、従来技術に従って第2図の装置で完全燃焼する
よう焼却処理した場合と比較して示せば、つぎのとおり
である。 このように、廃棄物中の炭素分の一部をCO2にせずC
゛(高分子炭素化合物の形を含む)として固定すること
により、CO2発生量を約24%減少さけることかでき
る。
[Burn with the amount of air. Subsequently, the combustion gas from the partial combustion melting furnace is combusted in a secondary combustion furnace. This gas contains a small amount of CO, so it is burned to make it harmless before being discharged. In the combustion of waste such as sewage sludge and municipal garbage, even if the air ratio is low enough to completely stop combustion, the generated C (including polymeric carbon compounds) is quickly fixed in the molten ash. By being
It has been found that relatively little CO is produced by the reaction between C and CO2. The secondary combustion furnace may be integrated with the primary combustion furnace as in the example described later, or may be separate. Since the combustion exhaust gas has a high temperature, it can be used to preheat the air supplied to the upper two types of furnaces, as well as to dry the waste to be fed into the dryer. For example, a furnace with a structure as shown in Figure 2 is used. Vertical primary combustion furnace (
In 1), most of the waste input from the supply port (4) is combusted by the air from the second air supply (5), and the generated ash (8A) becomes a melt and burns on the furnace wall. It flows down and accumulates at the bottom of the secondary combustion chamber (2), and is discharged from the outlet (7A). - Even if unburned materials that were not completely burned in the secondary combustion chamber fall into the secondary combustion chamber, they will be combusted by the air supplied from the secondary air inlet (6A) located at the inlet (left end in the figure). . To carry out the method of the present invention using this type of furnace, some modifications are made as shown in FIG. That is, the ash melt discharge port (7B) is located at the bottom of the secondary combustion chamber, but directly below the primary combustion chamber, and the secondary air supply port (6B) is located from it to the exhaust gas outlet (3). ) side. - It goes without saying that the air ratio in the secondary combustion chamber is lower than in the case of FIG. This results in
- The solid unburnt material that has fallen from the secondary combustion chamber comes into contact with the ash melt (8B) and is fixed therein before it comes into contact with the secondary air. The gaseous unburned (incompletely burned) substances are then combusted by the blown secondary air, raising the exhaust gas temperature and exiting from the exhaust gas outlet (3). Although the illustrated example is a swirl melting furnace, surface melting furnaces can also be used. [Example] Dried sewage sludge (calorific value 4230 k on dry weight basis)
ca! J/Ky) was incinerated at 1400° C. using an apparatus having the structure shown in FIG. The sludge supply rate is 1
550Kg/hr, air ratio 0.8. The results are shown below in comparison with the case of incineration for complete combustion using the apparatus shown in FIG. 2 according to the prior art. In this way, a portion of the carbon content in waste is converted into carbon instead of turning into CO2.
By fixing carbon dioxide (including in the form of high-molecular carbon compounds), it is possible to reduce CO2 emissions by approximately 24%.

【発明の効果】【Effect of the invention】

本発明の焼却方法により廃棄物を焼却すれば、燃焼によ
り発生ずるCO2の吊を効果的に減少させることができ
、CO2排出量抑制に寄与することができる。
When waste is incinerated by the incineration method of the present invention, the amount of CO2 generated by combustion can be effectively reduced, contributing to the reduction of CO2 emissions.

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

第1図は、本発明の廃棄物焼却方法の代表的なフローを
示すチャー1〜である。 第2図および第3図は、旋回溶融炉により下水汚泥の焼
却処理を行なう装置の断面図であって、第2図は従来技
術、第3図は本発明の場合をぞれぞれ示す。 1・・・−次燃焼炉     2・・・二次燃焼炉3・
・・排ガス出口     4・・・汚泥人口5・・・−
次空気入口 6A、6B・・・二次空気人口
FIG. 1 is Chart 1 to show a typical flow of the waste incineration method of the present invention. 2 and 3 are cross-sectional views of an apparatus for incinerating sewage sludge using a rotating melting furnace, with FIG. 2 showing the prior art and FIG. 3 showing the present invention. 1... - Secondary combustion furnace 2... Secondary combustion furnace 3.
...Exhaust gas outlet 4...Sludge population 5...-
Secondary air inlets 6A, 6B...Secondary air population

Claims (3)

【特許請求の範囲】[Claims] (1)燃焼により生成した灰分が溶融体を形成する廃棄
物の焼却において、廃棄物を不完全に燃焼させて未燃焼
物を残し、この未燃焼物を上記の溶融体中に固定するこ
とにより炭酸ガスの発生を減らした廃棄物の焼却方法。
(1) When incinerating waste in which the ash produced by combustion forms a molten body, the waste is incompletely combusted to leave unburned matter, and this unburned matter is fixed in the molten body. A waste incineration method that reduces carbon dioxide emissions.
(2)溶融助剤を添加して焼却を行ない、灰分溶融体の
増量および(または)粘度の調節をする請求項1の焼却
方法。
(2) The incineration method according to claim 1, wherein the incineration is performed with the addition of a melting aid to increase the amount of molten ash and/or adjust the viscosity.
(3)廃棄物が下水汚泥または都市ゴミである請求項1
または2の焼却方法。
(3) Claim 1 where the waste is sewage sludge or municipal garbage
Or incineration method 2.
JP2189194A 1990-07-17 1990-07-17 Method for incinerating waste with reduced carbon dioxide generation Pending JPH0474581A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2189194A JPH0474581A (en) 1990-07-17 1990-07-17 Method for incinerating waste with reduced carbon dioxide generation

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2189194A JPH0474581A (en) 1990-07-17 1990-07-17 Method for incinerating waste with reduced carbon dioxide generation

Publications (1)

Publication Number Publication Date
JPH0474581A true JPH0474581A (en) 1992-03-09

Family

ID=16237094

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2189194A Pending JPH0474581A (en) 1990-07-17 1990-07-17 Method for incinerating waste with reduced carbon dioxide generation

Country Status (1)

Country Link
JP (1) JPH0474581A (en)

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