JP3437828B2 - Fuel-fired incineration ash treatment equipment - Google Patents
Fuel-fired incineration ash treatment equipmentInfo
- Publication number
- JP3437828B2 JP3437828B2 JP2000357483A JP2000357483A JP3437828B2 JP 3437828 B2 JP3437828 B2 JP 3437828B2 JP 2000357483 A JP2000357483 A JP 2000357483A JP 2000357483 A JP2000357483 A JP 2000357483A JP 3437828 B2 JP3437828 B2 JP 3437828B2
- Authority
- JP
- Japan
- Prior art keywords
- exhaust gas
- ash
- combustion
- melting furnace
- fuel
- 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.)
- Expired - Fee Related
Links
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E20/00—Combustion technologies with mitigation potential
- Y02E20/30—Technologies for a more efficient combustion or heat usage
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/20—Waste processing or separation
Landscapes
- Chimneys And Flues (AREA)
- Gasification And Melting Of Waste (AREA)
- Processing Of Solid Wastes (AREA)
Description
【0001】[0001]
【発明の属する技術分野】本発明は、一般の家庭ゴミや
産業廃棄物などを焼却して生じる焼却灰を燃料焚きして
溶融固化する際に、灰溶融炉から発生する排ガスを処理
する装置に関するものである。TECHNICAL FIELD The present invention relates to treating exhaust gas generated from an ash melting furnace when burning incineration ash produced by incineration of general household waste, industrial waste, etc. and melting and solidifying the ash <br / > it relates to that equipment be.
【0002】[0002]
【従来の技術】近年、わが国においては、一般の家庭ゴ
ミや廃棄物は、年々増加の一途をたどり、その処理が社
会問題となり、各自治体で処理することが義務付けられ
るようになった。そして、1993年より主要都道府県
は各市町村に焼却施設をもたせることが条令で規制さ
れ、その結果大都市並びに各市町村では、一処理施設以
上の焼却施設を保有するようになったが、焼却灰を埋め
るための最終処分場の確保や、埋めた焼却灰からの二次
公害発生など、様々な問題がクローズアップされるよう
になってきた。2. Description of the Related Art In recent years, in Japan, general household wastes and wastes have been increasing year by year, and their disposal has become a social problem, and each local government is obliged to dispose of them. Since 1993, major prefectures have been regulated by ordinance to have each municipality have an incineration facility, and as a result, large cities and each municipality have more than one incineration facility. Various problems have come to be highlighted, such as securing a final disposal site for landfills and secondary pollution from the buried incineration ash.
【0003】最近では、家庭ゴミも特別管理一般廃棄物
に指定され、焼却飛灰は主灰(焼却灰)と分離し、中間
処理しないと最終処分地での埋設処分ができなくなって
いる。そのため、焼却灰に含まれる重金属などの有害物
質の溶出を防止できる焼却灰の溶融固化技術が注目され
るようになり、厚生省では、大都市県を対象に焼却灰の
溶融処理施設の建設計画を1994年から推進してい
る。Recently, household waste is also designated as specially controlled general waste, incinerated fly ash is separated from main ash (incinerated ash), and it is impossible to bury it at the final disposal site without intermediate treatment. Therefore, the incineration ash melting and solidifying technology that can prevent the elution of harmful substances such as heavy metals contained in the incineration ash has been attracting attention, and the Ministry of Health and Welfare is planning the construction of an incineration ash melting treatment facility targeting metropolitan prefectures. It has been promoted since 1994.
【0004】現在、一般家庭から排出されたゴミは、種
類別に収集され、ゴミ質に応じた処理がなされている。
例えば、可燃ゴミは、一部はコンポスト肥料の原料とし
て用いられるが、ほとんどは清掃工場において焼却炉に
より焼却処理される。この焼却処理においては、焼却炉
から排出される焼却灰と、集塵機などで捕集された微細
な飛灰とを生成する。後者の飛灰は、軽く飛びやすく、
重金属も多く含まれているので、通常コンクリートで固
形化したり、排ガス中の二酸化炭素で中和処理して、炭
酸塩として安定化させたのち、埋設処理される。一方、
焼却灰は、1400〜1500℃程度の温度で溶融、固
化処理されたのち、埋設処理又は覆土材などに有効利用
される。[0004] At present, the garbage discharged from ordinary households is collected by type and treated according to the quality of the garbage.
For example, some of combustible waste is used as a raw material for compost fertilizer, but most of it is incinerated in an incinerator in a cleaning plant. In this incineration process, incineration ash discharged from the incinerator and fine fly ash collected by a dust collector or the like are generated. The latter fly ash is light and easy to fly,
Since it also contains a large amount of heavy metals, it is usually solidified with concrete or neutralized with carbon dioxide in the exhaust gas to stabilize it as a carbonate and then buried. on the other hand,
The incinerated ash is melted and solidified at a temperature of about 1400 to 1500 ° C., and then effectively used for embedding or covering soil material.
【0005】これまで焼却灰溶融炉としては、電気溶融
炉(アーク加熱方式、プラズマ加熱方式、抵抗加熱方
式)、コークスベッド溶融炉(コークス加熱方式)、表
面溶融炉(重油バーナ加熱方式)などが知られている。Conventionally, as an incinerator ash melting furnace, an electric melting furnace (arc heating method, plasma heating method, resistance heating method), coke bed melting furnace (coke heating method), surface melting furnace (heavy oil burner heating method), etc. Are known.
【0006】そして、現在稼動している焼却灰溶融炉の
大半は、電気溶融炉、例えばプラズマ加熱溶融炉である
が、これは焼却灰トン当りの消費電力が800〜100
0kWと高いため、経済的な運営を行うには、焼却炉か
らの排ガスの熱回収による発電設備を付設し、それによ
り発電した電力を溶融炉の熱源として利用しなければな
らない。しかしながら、この発電設備の限界焼却規模は
1日当りゴミ200トンという大型になり、しかも連続
炉であるため、処理量がそれ以下の小型焼却施設として
は不適当であるし、また電気炉は炉内圧の急激な変動に
対応できにくいので、含水率の高い灰や未燃焼有機物を
含む灰を処理する場合には、あらかじめ乾燥処理をしな
ければならないという煩雑さを伴う。Most of the incinerator ash melting furnaces currently in operation are electric melting furnaces, for example, plasma heating and melting furnaces, and the power consumption per ton of incinerated ash is 800 to 100.
Since it is as high as 0 kW, in order to operate economically, it is necessary to attach a power generation facility by heat recovery of exhaust gas from the incinerator, and use the electric power generated by it as a heat source of the melting furnace. However, the maximum incineration scale of this power generation facility is as large as 200 tons of garbage per day, and since it is a continuous furnace, it is unsuitable as a small incinerator with a throughput of less than that. Since it is difficult to cope with the rapid fluctuation of the ash, it is necessary to perform a drying process in advance when treating ash having a high water content or ash containing unburned organic matter.
【0007】また、コークスベッド溶融炉は、現在では
入手困難な固体化石燃料を使用するため、コスト高にな
るのを免れない上に、焼却灰1トン当り、コークスと石
灰をそれぞれ0.3トン程度必要とするため減容率が低
いという欠点がある。したがって、最近では家庭ゴミも
特別管理一般廃棄物に指定され、焼却飛灰を主灰と分離
し、中間処理しないと最終処分地での埋設処分ができな
くなったこともあって、重油のような燃料を焚く表面溶
融炉が注目されるようになってきた。Further, since the coke bed melting furnace uses solid fossil fuel, which is currently difficult to obtain, it is unavoidable that the cost becomes high, and in addition, 0.3 ton of coke and 0.3 ton of lime are obtained per ton of incinerated ash. It has a drawback that the volume reduction rate is low because it requires a certain degree. Therefore, recently, household waste is also designated as specially controlled general waste, and incineration fly ash is separated from main ash, and it is impossible to bury it at the final disposal site without intermediate treatment. Surface melting furnaces that burn fuel have come to the fore.
【0008】ところで、このような燃料焚き表面溶融炉
では、溶融排ガスをガス冷却塔でいったん350℃付近
まで急速冷却した後で排ガス熱を回収すれば問題はない
が、回収熱量を多くしようとして、通常はガス冷却塔出
口の排ガス温度を550〜650℃に設定しており、こ
の温度は炉から揮散した金属が塩化物、酸化物、ケイ酸
塩として析出する温度と一致するため、処理装置壁面や
管路内に粘着性のダストが付着し、装置が閉塞するとい
う問題を有している。By the way, in such a fuel-fired surface melting furnace, there is no problem if the exhaust gas heat is recovered after the molten exhaust gas is once rapidly cooled to around 350 ° C. in the gas cooling tower. Normally, the exhaust gas temperature at the outlet of the gas cooling tower is set to 550 to 650 ° C, and this temperature is the same as the temperature at which the metal volatilized from the furnace precipitates as chlorides, oxides, and silicates, so the wall surface of the processing equipment There is a problem that sticky dust adheres to the inside of the pipe and the pipe and the device is blocked.
【0009】また、燃料焚き表面溶融炉においては、1
350℃以上の高温を必要とするため、その排ガス熱を
できるだけ回収して有効に利用し、経済的な熱エネルギ
ー収支を保つことが先決問題であるが、これまでこの点
を解決することができないため、実用化されていなかっ
た。In the fuel-fired surface melting furnace, 1
Since a high temperature of 350 ° C or higher is required, it is a priori problem to recover the exhaust gas heat as much as possible and effectively use it to maintain an economical thermal energy balance, but this problem cannot be solved until now. Therefore, it was not put to practical use.
【0010】[0010]
【発明が解決しようとする課題】本発明は、このような
事情のもとで、燃料焚き焼却灰処理において粘着性のダ
ストの発生を抑制して、定期的な清掃のための運転停止
による能率低下を防ぎ、かつ排ガス熱をできるだけ有効
に利用して、熱エネルギーの収支状態を経済的に改善す
るとともに、伝熱面が保護される装置を提供することを
目的としてなされたものである。Under the circumstances, the present invention suppresses the generation of sticky dust in the fuel-burning incineration ash treatment, and improves the efficiency by stopping the operation for periodic cleaning. The purpose of the present invention is to provide a device that prevents a decrease in temperature and utilizes exhaust gas heat as effectively as possible to economically improve the balance of heat energy and protect the heat transfer surface .
【0011】[0011]
【課題を解決するための手段】本発明者らは、燃料焚き
焼却灰の処理について種々研究を重ねた結果、灰溶融炉
からの排ガスを、先ず燃料燃焼用の常温空気と熱交換し
て、それを予熱し、次にある程度降温した溶融排ガスを
完全蒸発しうる条件で注水して急速冷却すれば、溶融炉
でガス化した低融点物質が粘性を帯びない固体になるこ
と、したがって排ガスの回収温度域と急冷すべき温度域
を適切に選定することにより効率的な熱エネルギーの回
収が可能であることを見出し、この知見に基づいて燃料
焚き焼却灰処理に使用する本発明装置をなすに至った。The inventors of the present invention have conducted various studies on the treatment of fuel-burning incineration ash, and as a result, exhaust gas from an ash melting furnace is first heat-exchanged with room temperature air for fuel combustion, If it is preheated and then the temperature of the molten exhaust gas, which has been cooled to some extent, is poured into the molten furnace under conditions that allow it to be completely evaporated, and then rapidly cooled, the low-melting substance gasified in the melting furnace becomes a solid without viscous properties, and therefore the exhaust gas is recovered. It found that it is possible to recover efficient heat energy by appropriately selecting the temperature range to be quenched and the temperature range, the fuel on the basis of this finding
The present invention has led to the device of the present invention used for the treatment of burning incineration ash .
【0012】すなわち、本発明は、(A)焼却灰投入口
(1)と、バーナー(2,2´)を介して燃焼用空気を
供給するための空気導入口(3,3´)と、燃焼排ガス
の排出口(4)と、生成するスラグを取り出すためのス
ラグ取出口(5)を備えた灰溶融炉、(B)燃焼用空気
を加熱するための熱交換部(6)と、耐火物でライニン
グされている受熱面(7)を付設した本体(8)と、溶
融炉で発生する燃焼排ガスの導入口(9)と、燃焼排ガ
ス中に含まれる未燃焼の可燃性ガスを混合撹拌させなが
ら燃焼させるための空気吹込ノズル(10)と、降温し
た燃焼排ガスの排出口(11)を備えた排ガス燃焼器で
あって、燃焼器内を上昇する燃焼排ガスの輻射熱を熱交
換部(6)で回収できる輻射型熱交換器の機能を備えて
いる排ガス燃焼器、及び(C)前記の降温した燃焼排ガ
スの導入口(12)と、内部で自由沈降したダストを取
り出すダスト取出口(13)と、排ガス出口(14)を
備え、内部に冷却水噴霧機構(15)を配設したガス冷
却塔を直列に配置して構成され、灰溶融炉と排ガス燃焼
器とガス冷却塔をそれぞれ連結する管路(16,17)
及び排ガス燃焼器の熱交換部(6)からの加熱された燃
焼用空気をバーナー(2,2´)を介して灰溶融炉へ供
給するための管路(18)を設けたことを特徴とする燃
料焚き焼却灰処理装置を提供するものである。That is, according to the present invention , ( A) an incineration ash charging port (1) and an air introducing port (3, 3 ') for supplying combustion air through a burner (2, 2'), An ash melting furnace equipped with a combustion exhaust gas discharge port (4) and a slag extraction port (5) for extracting the generated slag, (B) a heat exchange section (6) for heating combustion air, and a fireproofing Linin with things
While mixing and stirring the main body (8) attached with the heat receiving surface (7) that is energized, the inlet (9) for the combustion exhaust gas generated in the melting furnace, and the unburned combustible gas contained in the combustion exhaust gas. an air blowing nozzle (10) for combusting, in the exhaust gas combustor with an outlet cooling combustion exhaust gas (11)
The radiant heat of the combustion exhaust gas that rises in the combustor.
Equipped with the function of a radiant heat exchanger that can be recovered in the exchange section (6)
An exhaust gas combustor, and (C) an inlet (12) for the cooled combustion exhaust gas, a dust outlet (13) for taking out dust that freely settled inside, and an exhaust gas outlet (14), and cooling inside Pipe lines (16, 17) configured by arranging gas cooling towers in which the water spray mechanism (15) is arranged in series and connecting the ash melting furnace, the exhaust gas combustor and the gas cooling tower, respectively.
And a pipe line (18) for supplying the heated combustion air from the heat exchange section (6) of the exhaust gas combustor to the ash melting furnace via the burners (2, 2 '). The present invention provides a fuel-fired incineration ash treatment device that does.
【0013】[0013]
【発明の実施の形態】次に、添付図面に従って、本発明
をさらに詳細に説明する。図1は、本発明装置の例を示
す説明図であって、この装置は灰溶融炉A、排ガス燃焼
器B及びガス冷却塔Cから構成されている。本発明装置
を使用して焼却灰を処理する際には、処理しようとする
可燃性ゴミの焼却灰は、焼却灰投入口1から灰溶融炉A
に供給される。この焼却灰には、焼却炉の炉下に堆積す
る主灰と集塵機に捕集される飛灰があり、それぞれ組成
を異にしている。表1にこれらの組成を示す。BEST MODE FOR CARRYING OUT THE INVENTION The present invention will now be described in more detail with reference to the accompanying drawings. Figure 1 is an explanatory diagram showing an example of the onset AkiraSo location, the apparatus ash melting furnace A, and a gas combustor B and gas cooling tower C. Device of the present invention
When incineration ash is treated using the ash melting furnace A from the incineration ash input port 1
Is supplied to. There are two types of incineration ash: main ash that accumulates under the incinerator and fly ash that is collected by a dust collector. Table 1 shows these compositions.
【0014】[0014]
【表1】 [Table 1]
【0015】このように、主灰の主成分は、SiO2、
Al2O3、CaO及びFe2O3であり、飛灰の主成分は
CaOである。これらの焼却灰は、灰溶融炉A中で空気
導入口3,3´から供給され、燃料焚きバーナー2,2
´により加熱された燃焼用空気により、1350〜15
00℃、通常は約1400℃に加熱され、溶融固化され
る。この際、金属の揮散が起り、排出口4から排出され
るガス中に混入する。この金属の揮散量は、灰の塩基度
により左右される。すなわち、重金属成分は、いずれも
弱塩基性であり、アルカリ金属やアルカリ土類金属は強
塩基なので、塩基度の高いところ、すなわちCaOの多
いところでは、塩基性酸化物同士がたがいに反発し合い
揮散しやすくなり、逆に塩基性の低いところ、すなわち
SiO2が多いところでは、揮散しにくくなり、スラグ
として残留し、このスラグはスラグ取出口5から取り出
される。管路20は燃料供給管を示す。表2に溶融温度
1400℃における各金属の揮散率を示す。Thus, the main component of the main ash is SiO 2 ,
Al 2 O 3 , CaO and Fe 2 O 3 , and the main component of fly ash is CaO. These incinerated ash are supplied from the air inlets 3, 3 ′ in the ash melting furnace A, and the fuel-fired burners 2, 2
1350 to 15 depending on the combustion air heated by
It is heated to 00 ° C., usually about 1400 ° C., and melted and solidified. At this time, volatilization of the metal occurs and mixes in the gas discharged from the discharge port 4. The amount of this metal volatilized depends on the basicity of the ash. That is, since the heavy metal components are all weakly basic and the alkali metal and the alkaline earth metal are strong bases, the basic oxides repel each other in a place with high basicity, that is, in a place with a large amount of CaO. Volatilization becomes easy, and conversely, in a place with low basicity, that is, in a place where there is a large amount of SiO 2 , it becomes difficult to volatilize and remains as slag, and this slag is taken out from the slag outlet 5. The pipe line 20 represents a fuel supply pipe. Table 2 shows the volatilization rate of each metal at a melting temperature of 1400 ° C.
【0016】[0016]
【表2】 [Table 2]
【0017】これらの揮散して排ガス中に含まれる金属
は、排ガスの温度が降下するに従って、塩化物、酸化
物、ケイ酸塩を形成する。すなわち、低融点物質が溶融
中に気化し、これが温度降下とともに固化する。そし
て、これが排ガス燃焼器や熱交換器の器壁に粘性を帯び
た付着物となって付着することになる。The metal that is volatilized and contained in the exhaust gas forms chlorides, oxides, and silicates as the temperature of the exhaust gas decreases. That is, the low melting point substance is vaporized during melting, and this is solidified as the temperature drops. Then, this adheres to the wall of the exhaust gas combustor or the heat exchanger as a viscous deposit.
【0018】この灰溶融炉Aの排ガス排出口4から排出
された温度1350〜1500℃の高温ガスを、排ガス
導入口9から熱交換部6を備えた排ガス燃焼器Bに導入
し、燃焼用空気と熱交換させて低融点物質が固化を起さ
ないでガス化している温度、すなわち1500〜110
0℃、好ましくは1500℃から790℃まで降温す
る。したがって、この熱交換部6により回収できる予熱
空気の温度には制限があり、入口空気温度の条件にもよ
るが、一般には最大で450℃である。この熱交換によ
り、燃焼用空気は100〜450℃に加温され、管路1
8を通って灰溶融炉Aの空気導入口3,3´からバーナ
ー2,2´に送られる。また、所望に応じこの燃焼用空
気の一部は、分岐管路19を通って排ガス燃焼器Bに送
られる燃焼排ガスの二次燃焼空気として使用することも
できる。[0018] The ash melting furnace exhaust gas discharge port 4 temperature 1,350-1,500 ° C. of the hot gas discharged from the A of this, introduced from the exhaust gas inlet 9 to the exhaust gas combustor B having a heat exchanging section 6, a combustion The temperature at which the low-melting point substance is gasified by heat exchange with air without causing solidification, that is, 1500 to 110
The temperature is lowered to 0 ° C, preferably 1500 ° C to 790 ° C. Therefore, there is a limit to the temperature of the preheated air that can be recovered by the heat exchange section 6, and the maximum temperature is generally 450 ° C., although it depends on the condition of the inlet air temperature. By this heat exchange, the combustion air is heated to 100 to 450 ° C.
It is sent to the burners 2 and 2 ′ from the air introduction ports 3 and 3 ′ of the ash melting furnace A through 8. Further, if desired, a part of the combustion air can be used as secondary combustion air of the combustion exhaust gas sent to the exhaust gas combustor B through the branch pipe line 19.
【0019】排ガス燃焼器Bは、その燃焼排ガス導入口
付近又は導入されたガス上昇開始部近辺で燃焼用空気を
噴射させるとともに、燃焼器内を上昇する燃焼排ガスの
輻射熱を熱交換部6で回収できる1種の輻射型熱交換器
の機能を備えている。これは燃焼器Bの外側を外筒で被
覆し、燃焼器Bの外壁、すなわち受熱面7と外筒の内壁
との間の間隙を空気流路に形成することにより達成しう
る。また燃焼器Bの外壁、すなわち受熱面7と外筒の内
壁には耐火物でライニングするのが好ましい。この耐火
物の厚さは、70〜150mm、その熱伝導率は3〜1
0kcal/mh℃にするのがよい。これよりも低い熱
伝導率の耐火物を用いると熱の伝達が十分に行われない
ので熱交換器の役割を果たさないし、これよりも高い耐
火物を用いると熱伝達を十分に抑制できず伝熱面を保護
することができない。The exhaust gas combustor B injects combustion air near the combustion exhaust gas introduction port or near the introduced gas rising start portion, and recovers the radiant heat of the combustion exhaust gas rising in the combustor in the heat exchange section 6. It has the function of one type of radiant heat exchanger. This can be achieved by covering the outside of the combustor B with an outer cylinder and forming a gap between the outer wall of the combustor B, that is, the heat receiving surface 7 and the inner wall of the outer cylinder in the air flow path. The outer wall of the combustor B, that is, the heat receiving surface 7 and the inner wall of the outer cylinder are preferably lined with a refractory material. The thickness of this refractory material is 70 to 150 mm, and its thermal conductivity is 3-1.
It is recommended that the temperature be 0 kcal / mh ° C. If a refractory material with a thermal conductivity lower than this is used, heat cannot be transferred sufficiently, so it does not play the role of a heat exchanger.If a refractory material with a higher thermal conductivity is used, heat transfer cannot be sufficiently suppressed and the heat transfer cannot be performed. Cannot protect hot surface.
【0020】このようにして、790〜1100℃の降
温した燃焼排ガスは、導入管17を通って導入口12か
らガス冷却塔Cに導入される。このガス冷却塔Cの内部
には冷却水噴霧機構、例えば冷水用散水管15が配設さ
れ、上記の燃焼排ガスに冷水を注水して、これを180
〜300℃まで急冷する。これにより、排ガス中の低融
点物質が瞬時に降温するので、粘性のない粉末になり、
ダスト取出口13から取り出され、後続の集塵機により
容易に捕集することができる。一方、排ガスは排ガス出
口14から系外に排出される。In this way, the combustion exhaust gas whose temperature is lowered to 790 to 1100 ° C. is introduced into the gas cooling tower C from the inlet 12 through the inlet pipe 17. Inside the gas cooling tower C, a cooling water spraying mechanism, for example, a cold water sprinkling pipe 15 is arranged, and cold water is injected into the combustion exhaust gas to generate 180
Quench to ~ 300 ° C. As a result, the low-melting-point substance in the exhaust gas cools down instantly, resulting in a non-viscous powder,
It is taken out from the dust outlet 13 and can be easily collected by the subsequent dust collector. On the other hand, the exhaust gas is discharged from the exhaust gas outlet 14 to the outside of the system.
【0021】[0021]
【実施例】次に実施例により本発明をさらに詳細に説明
する。EXAMPLES The present invention will be described in more detail with reference to examples.
【0022】実施例
外径1068mm、内径850mm(耐火キャスタブル
内径)、長さ4000mm(有効長さ)のステンレス鋼
製円筒の外側を外径1104mm、内径1088mm、
長さ4000mm(有効長さ)の外筒で被覆し、両者の
間に生じた間隙を空気流路に形成した空気予熱器兼用排
ガス燃焼器に、含水率1質量%の灰を1400℃で溶融
固化した際に発生した燃焼排ガスを供給し、空気過剰率
10%で排ガスと空気との熱交換を行った。その結果を
表3に示す。Implementation Exceptional diameter of 1068 mm, inner diameter of 850 mm (refractory castable inner diameter), length of 4000 mm (effective length) stainless steel cylinder outside the outer diameter 1104 mm, inner diameter 1088 mm,
An ash with a water content of 1 mass% is melted at 1400 ° C in an exhaust gas combustor that also serves as an air preheater and is covered with an outer cylinder with a length of 4000 mm (effective length) and the gap created between them is formed in the air flow path. The combustion exhaust gas generated at the time of solidification was supplied, and heat exchange between the exhaust gas and air was performed at an excess air ratio of 10%. The results are shown in Table 3.
【0023】[0023]
【表3】 [Table 3]
【0024】この際の空気予熱器兼用排ガス燃焼器で予
熱する燃焼空気温度は最高450℃であるから、溶融炉
排ガスの空気予熱器兼用排ガス燃焼器出口温度も950
℃以内、すなわち炉内で揮散した低融点物質がガス状態
を保つ温度域であり、熱交換伝熱面へのダストの吸着は
認められなかった。一方、空気予熱温度を例えば550
℃まで上げると、灰溶融炉排ガス温度が空気予熱器兼用
排ガス燃焼器内で700℃程度まで下がるため、伝熱面
に粘着性付着物の生成が認められた。At this time, the temperature of the combustion air preheated by the exhaust gas combustor also serving as the air preheater is 450 ° C. at the maximum, so the outlet temperature of the exhaust gas combustor also serving as the air preheater for the melting furnace exhaust gas is also 950.
Within the temperature range, that is, in the temperature range in which the low-melting point substance volatilized in the furnace was kept in a gas state, adsorption of dust on the heat exchange heat transfer surface was not observed. On the other hand, the air preheating temperature is set to 550, for example.
When the temperature was raised to ℃, the ash melting furnace exhaust gas temperature dropped to about 700 ° C. in the air preheater / exhaust gas combustor, so that the formation of sticky deposits was observed on the heat transfer surface.
【0025】[0025]
【発明の効果】本発明装置によると、燃料焚き焼却灰処
理に起因する粘着性ダスト形成の抑制を可能にした排ガ
ス熱の回収を行うことができ、低い燃料消費率で効率よ
く焼却灰溶融処理を行うことができる。According to the invention apparatus according to the present invention, it is possible to perform the recovery of exhaust heat which enables suppression of sticky dust formation due to fuel-burning ash processing, efficient incineration ash melting treatment at a low fuel consumption rate It can be performed.
【図1】 本発明装置を説明するための概略図。FIG. 1 is a schematic diagram for explaining a device of the present invention.
A 灰溶融炉 B 排ガス燃焼器 C ガス冷却塔 1 焼却灰投入口 2,2´バーナー 5 スラグ取出口 6 熱交換部 9 排ガス導入口 13 ダスト取出口 15 冷却水噴霧機構 A ash melting furnace B Exhaust gas combustor C gas cooling tower 1 Incineration ash input port 2,2 'burner 5 Slag outlet 6 heat exchange section 9 Exhaust gas inlet 13 Dust outlet 15 Cooling water spray mechanism
───────────────────────────────────────────────────── フロントページの続き (58)調査した分野(Int.Cl.7,DB名) B09B 3/00 - 5/00 ─────────────────────────────────────────────────── ─── Continuation of the front page (58) Fields investigated (Int.Cl. 7 , DB name) B09B 3/00-5/00
Claims (3)
(2,2´)を介して燃焼用空気を供給するための空気
導入口(3,3´)と、燃焼排ガスの排出口(4)と、
生成するスラグを取り出すためのスラグ取出口(5)を
備えた灰溶融炉、(B)燃焼用空気を加熱するための熱
交換部(6)と、耐火物でライニングされている受熱面
(7)を付設した本体(8)と、溶融炉で発生する燃焼
排ガスの導入口(9)と、燃焼排ガス中に含まれる未燃
焼の可燃性ガスを混合撹拌させながら燃焼させるための
空気吹込ノズル(10)と、降温した燃焼排ガスの排出
口(11)を備えた排ガス燃焼器であって、燃焼器内を
上昇する燃焼排ガスの輻射熱を熱交換部(6)で回収で
きる輻射型熱交換器の機能を備えている排ガス燃焼器、
及び(C)前記の降温した燃焼排ガスの導入口(12)
と、内部で自由沈降したダストを取り出すダスト取出口
(13)と、排ガス出口(14)を備え、内部に冷却水
噴霧機構(15)を配設したガス冷却塔を直列に配置し
て構成され、灰溶融炉と排ガス燃焼器とガス冷却塔をそ
れぞれ連結する管路(16,17)及び排ガス燃焼器の
熱交換部(6)からの加熱された燃焼用空気をバーナー
(2,2´)を介して灰溶融炉へ供給するための管路
(18)を設けたことを特徴とする燃料焚き焼却灰処理
装置。1. (A) Incineration ash charging port (1), air introducing port (3, 3 ') for supplying combustion air through burners (2, 2'), and exhaust of combustion exhaust gas Exit (4),
An ash melting furnace provided with a slag outlet (5) for taking out the generated slag, (B) a heat exchange section (6) for heating the combustion air, and a heat receiving surface (7) lined with a refractory material. ) Attached to the main body (8), an inlet (9) for the combustion exhaust gas generated in the melting furnace, and an air injection nozzle () for burning the unburned combustible gas contained in the combustion exhaust gas while mixing and stirring the mixture. 10) and an exhaust gas combustor outlet (11) for cooling the combustion exhaust gas ,
The radiant heat of rising combustion exhaust gas can be recovered by the heat exchange section (6).
Exhaust gas combustor with the function of a radiant heat exchanger,
And (C) an inlet (12) for the cooled exhaust gas
And a gas cooling tower having a dust outlet (13) for taking out dust that freely settled inside and an exhaust gas outlet (14) and having a cooling water spraying mechanism (15) arranged therein in series. , Burners (2, 2 ') for the heated combustion air from the pipes (16, 17) connecting the ash melting furnace, the exhaust gas combustor and the gas cooling tower, respectively, and the heat exchange section (6) of the exhaust gas combustor. A fuel-fired incineration ash processing apparatus, which is provided with a pipe (18) for supplying the ash to the ash melting furnace through the pipe.
ニングされている受熱面(7)と外側を被覆した外筒の
内壁との間の間隙を空気流路に形成することにより達成
する請求項1記載の燃料焚き焼却灰処理装置。 2. The function of the radiant heat exchanger is made of refractory material.
Of the heat receiving surface (7) being trained and the outer cylinder that covers the outside
Achieved by forming a gap between the inner wall and the air passage
The fuel-fired incineration ash processing apparatus according to claim 1.
l/mh℃の耐火物の厚さ70〜150mmの層でライ
ニングされている請求項1又は2記載の燃料焚き焼却灰
処理装置。3. The heat receiving surface (7) has a thermal conductivity of 3 to 10 kca.
The fuel-fired incineration ash treatment device according to claim 1 or 2, which is lined with a layer having a thickness of 70 to 150 mm of a refractory material of 1 / mh ° C.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2000357483A JP3437828B2 (en) | 2000-11-24 | 2000-11-24 | Fuel-fired incineration ash treatment equipment |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2000357483A JP3437828B2 (en) | 2000-11-24 | 2000-11-24 | Fuel-fired incineration ash treatment equipment |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JP2002159934A JP2002159934A (en) | 2002-06-04 |
| JP3437828B2 true JP3437828B2 (en) | 2003-08-18 |
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| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2000357483A Expired - Fee Related JP3437828B2 (en) | 2000-11-24 | 2000-11-24 | Fuel-fired incineration ash treatment equipment |
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| Country | Link |
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP4972458B2 (en) * | 2007-05-15 | 2012-07-11 | 株式会社タクマ | Ash melting furnace combustion chamber |
Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2000291920A (en) | 1999-04-01 | 2000-10-20 | Nkk Plant Engineering Corp | Incineration residue melting equipment |
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2000
- 2000-11-24 JP JP2000357483A patent/JP3437828B2/en not_active Expired - Fee Related
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2000291920A (en) | 1999-04-01 | 2000-10-20 | Nkk Plant Engineering Corp | Incineration residue melting equipment |
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|---|---|
| JP2002159934A (en) | 2002-06-04 |
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