JPH11281040A - Apparatus and method for treating incineration ash - Google Patents

Apparatus and method for treating incineration ash

Info

Publication number
JPH11281040A
JPH11281040A JP10081700A JP8170098A JPH11281040A JP H11281040 A JPH11281040 A JP H11281040A JP 10081700 A JP10081700 A JP 10081700A JP 8170098 A JP8170098 A JP 8170098A JP H11281040 A JPH11281040 A JP H11281040A
Authority
JP
Japan
Prior art keywords
ash
exhaust gas
salts
heat
fly ash
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP10081700A
Other languages
Japanese (ja)
Other versions
JP3837684B2 (en
Inventor
Naoki Fujiwara
直機 藤原
Manabu Yamamoto
学 山本
Wakako Shimodaira
和佳子 下平
Hideji Mori
秀治 守
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.)
Mitsubishi Power Ltd
Original Assignee
Babcock Hitachi KK
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 Babcock Hitachi KK filed Critical Babcock Hitachi KK
Priority to JP08170098A priority Critical patent/JP3837684B2/en
Publication of JPH11281040A publication Critical patent/JPH11281040A/en
Application granted granted Critical
Publication of JP3837684B2 publication Critical patent/JP3837684B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Gasification And Melting Of Waste (AREA)

Abstract

PROBLEM TO BE SOLVED: To recover salts efficiently and economically without the necessity of a special heat source by using a compact and simple facility. SOLUTION: A refuse ash treating apparatus 1 comprises an ash melting furnace 3 for heating and melting a refuse ash (a), a heat recovering unit 8 for recovering heat of an exhaust gas G1 generated from the ash melting furnace 3 and separating a molten fly ash (b) therefrom, a dust collector 12 for collecting the molten fly ash (b) in the exhaust gas discharged from the heat recovering unit 8, a wet type detoxicating treatment device 16 for adding water (k) and a pharmaceutical agent (i) to the molten ash (b) separated and collected by the heat recovering unit 8 and the dust collector 12, respectively, for separation into heavy metals (c) and an aqueous solution (d) containing salts. The apparatus further comprises an evaporating tower 21 for evaporating and solidifying the aqueous solution (d) containing salts by blowing an exhaust gas G3 which has been obtained by heating an exhaust gas G2 discharged from the dust collector 12 with the use of a heat exchanger 9 provided at the heat recovering unit 8.

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、被焼却物を焼却し
た際に発生する重金属類及び塩類を含む焼却灰を処理す
る焼却灰処理装置及び焼却灰処理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 an incineration ash treatment apparatus and an incineration ash treatment method for treating incineration ash containing heavy metals and salts generated when incinerated materials are incinerated.

【0002】[0002]

【従来の技術】近年、被焼却物を焼却した際に発生する
重金属類及び塩類を含む焼却灰を処理する焼却灰処理装
置又は焼却灰処理方法、例えば都市ごみを焼却した際に
発生するごみ灰を処理するごみ灰処理装置又はごみ灰処
理方法において、ごみ灰の減容化による埋め立て用地の
延命及びごみ灰の無害化を目的としてごみ灰を溶融する
装置又は方法が急速に普及しつつある。
2. Description of the Related Art In recent years, an incineration ash treatment apparatus or an incineration ash treatment method for treating incineration ash containing heavy metals and salts generated when incinerated materials are incinerated, for example, refuse ash generated when municipal solid waste is incinerated. In a refuse ash treatment apparatus or refuse ash treatment method for treating ash, an apparatus or a method for melting refuse ash for the purpose of extending the life of a landfill site by reducing the volume of refuse ash and detoxifying the refuse ash is rapidly spreading.

【0003】図2は、従来技術に係るごみ灰処理装置の
例を示す系統図である。従来のごみ灰処理装置2におい
て、灰溶融炉3に供給されたごみ灰aは、同時に供給さ
れた空気f及び燃料eの燃焼熱により1,000℃以上
の温度で加熱され溶融し、減容化、無害化されたスラグ
gとして炉底より排出される。ごみ灰a中にはアルカリ
金属類の塩化物を中心とした低沸点物質が数十%も含ま
れており、これらが溶融時の高熱により揮発し気体とな
る。その他にも鉛、カドミウム等の低沸点重金属も同時
に揮発し灰溶融炉3の1,000〜1,400℃の高温
排ガスG1と共に配管30aを通じて熱回収部8に送ら
れる。
FIG. 2 is a system diagram showing an example of a conventional refuse ash treatment apparatus. In the conventional refuse ash treatment device 2, refuse ash a supplied to the ash melting furnace 3 is heated and melted at a temperature of 1,000 ° C. or more by the combustion heat of the air f and the fuel e supplied at the same time, thereby reducing the volume. It is discharged from the furnace bottom as slag g which has been converted and made harmless. The refuse ash a contains several tens% of low-boiling substances, mainly chlorides of alkali metals, which are volatilized by high heat during melting to become gas. Other lead is also sent to the heat recovery unit 8 through a pipe 30a with the high temperature exhaust gas G 1 of 1,000~1,400 ° C. Low-boiling heavy metals and volatilizes simultaneously ash melting furnace 3, such as cadmium.

【0004】灰溶融炉3から排出された高温排ガスG1
は、熱回収部8で後段の集塵器12が耐えられる程度の
温度、例えばバグフィルタであれば200〜250℃程
度に冷却される。この時、灰溶融炉3で揮発し排ガスG
1中に含まれていたガス状の塩化物及び低沸点重金属は
再び凝縮、固化し排ガス中のダストとなる。これらのガ
ス状の塩化物及び低沸点物質が凝固したダスト及び灰溶
融炉3で舞い上がり排ガスG1に同伴した微細なごみ灰
aは、所謂溶融飛灰bとして熱回収部8の下部に沈降し
たり、更に下流の集塵器12で集塵(又は捕集)され
る。これらの溶融飛灰bは配管30bを通じて溶融飛灰
ホッパ14に集められる。溶融飛灰ホッパ14に集めら
れた溶融飛灰bは湿式無害化処理装置16に送られる。
尚、符号26は、集塵器12からの排ガスを排出させる
排風機、符号28は煙突である。
The high-temperature exhaust gas G 1 discharged from the ash melting furnace 3
Is cooled to a temperature at which the heat collector 8 can withstand the dust collector 12 at the subsequent stage, for example, about 200 to 250 ° C. in the case of a bag filter. At this time, the exhaust gas G
The gaseous chlorides and low-boiling heavy metals contained in 1 are condensed and solidified again and become dust in the exhaust gas. These gaseous fine dust ash a of chloride and low boiling substance entrained in the exhaust gas G 1 flyaway in the dust and ash melting furnace 3 solidification, or settled to the bottom of the heat recovery section 8 as a so-called molten fly ash b The dust is collected (or collected) by the dust collector 12 further downstream. These molten fly ash b are collected in the molten fly hopper 14 through the pipe 30b. The molten fly ash b collected in the molten fly ash hopper 14 is sent to the wet detoxification processing device 16.
Note that reference numeral 26 denotes an exhaust fan for discharging exhaust gas from the dust collector 12, and reference numeral 28 denotes a chimney.

【0005】湿式無害化処理装置16は、溶融飛灰b中
に含まれる重金属類を無害化するための薬剤i、例えば
キレート剤等が配管30cを通じて添加される。更に、
水hが配管30dを通じて供給される。溶融飛灰b中に
含まれる塩化物はほとんどすべて水溶性物質のため配管
30dを通じて供給された水hに溶解し配管30eを通
じて水処理装置19に送られる。溶融飛灰b中に含まれ
る重金属類は配管30cを通じて供給された薬剤iによ
り無害化され固体のスラッジcとして沈殿し排出され
る。
[0005] In the wet detoxification treatment device 16, a chemical i for detoxifying heavy metals contained in the molten fly ash b, for example, a chelating agent is added through a pipe 30c. Furthermore,
Water h is supplied through the pipe 30d. Almost all the chloride contained in the molten fly ash b is dissolved in the water h supplied through the pipe 30d because it is a water-soluble substance, and is sent to the water treatment apparatus 19 through the pipe 30e. Heavy metals contained in the molten fly ash b are rendered harmless by the chemical i supplied through the pipe 30c, and are precipitated and discharged as solid sludge c.

【0006】水処理装置19としては、電気分解方式或
いは逆浸透膜方式が採用され、ここで配管30eを通じ
て送り込まれた廃水に溶解している高濃度の塩類jは分
離され固体の塩化物として排出される。塩類jを分離し
た低濃度の塩類を含む(要するに浄化された)水hは配
管30dを通じて再び湿式無害化処理装置16に送ら
れ、溶融飛灰ホッパ14から送られた溶融飛灰bを溶解
するために用いられる。又、配管30kからは補給水が
この湿式処理系に供給される。
As the water treatment device 19, an electrolysis system or a reverse osmosis membrane system is adopted. Here, high-concentration salts j dissolved in wastewater sent through a pipe 30e are separated and discharged as solid chlorides. Is done. The water h containing (in short, purified) low-concentration salts from which the salts j have been separated is sent again to the wet detoxification apparatus 16 through the pipe 30d, and dissolves the molten fly ash b sent from the molten fly ash hopper 14. Used for Also, make-up water is supplied to this wet processing system from the pipe 30k.

【0007】[0007]

【発明が解決しようとする課題】しかしながら、上記従
来のごみ灰処理装置2には、次のような問題がある。即
ち、 水処理装置19として電気分解方式を採用した場合
には大型の設備となり立地条件によっては設置出来ない
場合があり、且つ設備費、電力コスト等が高く、設備が
複雑である。
However, the conventional refuse ash treatment apparatus 2 has the following problems. That is, when the electrolysis method is adopted as the water treatment apparatus 19, the equipment becomes large and cannot be installed depending on the location conditions, and the equipment cost and the power cost are high, and the equipment is complicated.

【0008】 水処理装置19として逆浸透膜方式を
採用した場合には、設備費が高く、且つポンプ等の運転
コストも高い。
When the reverse osmosis membrane system is adopted as the water treatment device 19, the equipment cost is high, and the operating costs of the pump and the like are high.

【0009】従って、従来のごみ灰処理装置2において
は、設備が大型になり、設備費、電力コスト、運転コス
ト等が高く、設備が複雑である、と云った問題を解決す
る必要があった。
Therefore, in the conventional refuse ash treatment apparatus 2, it is necessary to solve the problem that the equipment is large, the equipment cost, the power cost, the operation cost, etc. are high, and the equipment is complicated. .

【0010】本発明の課題は、被焼却物を焼却した際に
発生する重金属類及び塩類を含む焼却灰を処理する焼却
灰処理装置及び焼却灰処理方法において、設備的に小型
で簡便であり、特別な熱源を必要とせずに効率的、経済
的に塩類を回収することが出来ることである。
An object of the present invention is to provide an incineration ash treatment apparatus and an incineration ash treatment method for treating incineration ash containing heavy metals and salts generated when incinerated objects are incinerated, which is compact and simple in terms of equipment. It is possible to efficiently and economically recover salts without requiring a special heat source.

【0011】[0011]

【課題を解決するための手段】上記課題を解決するため
本発明は、被焼却物を焼却した際に発生する重金属類及
び塩類を含む焼却灰を加熱して溶融する灰溶融炉と、該
灰溶融炉で発生した排ガスの熱を回収すると共に、前記
排ガス中の飛灰を分別する熱回収分別手段と、該熱回収
分別手段から排出された排ガス中の飛灰を集塵する飛灰
集塵手段と、前記熱回収分別手段及び飛灰集塵手段で分
別乃至集塵された飛灰に水と薬剤を加えて、重金属類と
塩類を含む水溶液とに分離する処理分離手段とを備えた
焼却灰処理装置において、前記熱回収分別手段で回収さ
れた熱を利用して前記処理分離手段で分離された塩類を
含む水溶液を蒸発固化する蒸発固化手段を設けたことで
ある。
SUMMARY OF THE INVENTION In order to solve the above-mentioned problems, the present invention provides an ash melting furnace for heating and melting incinerated ash containing heavy metals and salts generated when incinerated objects are incinerated; Heat recovery and separation means for recovering the heat of the exhaust gas generated in the melting furnace and separating fly ash in the exhaust gas, and fly ash collection for collecting fly ash in the exhaust gas discharged from the heat recovery and separation means And incineration processing and separation means for adding water and chemicals to the fly ash separated or collected by the heat recovery separation means and fly ash dust collection means to separate the fly ash into an aqueous solution containing heavy metals and salts. The ash treatment device is provided with an evaporative solidification means for evaporating and solidifying the aqueous solution containing salts separated by the treatment / separation means using the heat recovered by the heat recovery / separation means.

【0012】灰溶融炉の排ガスは千数百℃以上の高温で
排出されるので、その熱は熱回収分別手段で蒸気として
回収されても尚余りがあり、この熱を利用して高濃度の
塩類を含む水溶液(廃水)を加熱蒸発させ塩類を固体と
して回収する。熱回収分別手段で回収される熱を利用す
る蒸発固化手段を設けたことにより、設備的に小型で簡
便な塩類回収装置とすることが出来、且つ熱回収分別手
段で回収される熱を利用するので特別な熱源を必要とせ
ず、効率的、経済的に塩類を回収することが出来る。
Since the exhaust gas from the ash melting furnace is discharged at a high temperature of more than 1,000 hundreds of degrees Celsius, even if the heat is recovered as steam by the heat recovery and separation means, there is still a surplus. The aqueous solution containing salt (waste water) is heated and evaporated to recover the salt as a solid. By providing the evaporative solidification means using the heat recovered by the heat recovery and separation means, it is possible to provide a simple and simple salt recovery apparatus with equipment, and to utilize the heat recovered by the heat recovery and separation means. Therefore, no special heat source is required, and the salt can be efficiently and economically recovered.

【0013】更に、上記焼却灰処理装置において、前記
蒸発固化手段の蒸発固化は、前記飛灰集塵手段から排出
された排ガスを前記熱回収分別手段に設けた熱交換器に
通すことによって加熱される排ガスを吹き込むことによ
って行なわれることである。
Further, in the above incineration ash treatment apparatus, the evaporative solidification of the evaporative solidification means is heated by passing exhaust gas discharged from the fly ash dust collection means through a heat exchanger provided in the heat recovery and separation means. This is performed by blowing exhaust gas.

【0014】この発明の焼却灰処理装置は、上記発明の
焼却灰処理装置の作用に加え、飛灰集塵手段から排出さ
れた排ガスが、ある程度温度が高いので、この排ガスを
熱回収分別手段の熱交換器に通すことによって容易に温
度を高めることが出来、塩類を含む水溶液を速やかに蒸
発固化する。
According to the incineration ash treatment apparatus of the present invention, in addition to the operation of the incineration ash treatment apparatus of the above invention, since the exhaust gas discharged from the fly ash dust collecting means has a somewhat high temperature, this exhaust gas is used as heat recovery and separation means. The temperature can be easily raised by passing through a heat exchanger, and the aqueous solution containing salts is quickly evaporated and solidified.

【0015】又、被焼却物を焼却した際に発生する重金
属類及び塩類を含む焼却灰を加熱して溶融し、発生した
排ガス中の飛灰を分別し、該飛灰に水と薬剤を加えて重
金属類と塩類を含む水溶液とに分離し、該重金属類と塩
類をそれぞれ回収する焼却灰処理方法において、前記焼
却灰を加熱して溶融する際に発生する熱を利用して前記
塩類を含む水溶液を蒸発固化し、固体の塩類として回収
することである。
Further, the incinerated ash containing heavy metals and salts generated when the incinerated material is incinerated is heated and melted, the fly ash in the generated exhaust gas is separated, and water and a chemical are added to the fly ash. In the incineration ash treatment method of separating the heavy metals and salts by an aqueous solution containing heavy metals and salts, the heat incineration ash is heated and melted to contain the salts. To evaporate and solidify the aqueous solution and recover it as solid salts.

【0016】焼却灰を加熱して溶融する際に発生する熱
を利用して塩類を含む水溶液を蒸発固化するので、簡便
に塩類を回収することが出来、且つ特別な熱源を必要と
せずに効率的、経済的に塩類を回収することが出来る。
Since the aqueous solution containing salts is evaporated and solidified by utilizing the heat generated when the incinerated ash is heated and melted, the salts can be easily recovered, and the efficiency can be improved without requiring a special heat source. It is possible to collect salts economically and economically.

【0017】[0017]

【発明の実施の形態】以下、本発明の焼却灰処理装置及
び焼却灰処理方法の実施の形態を図1に基づいて説明す
る。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of an incineration ash treatment apparatus and an incineration ash treatment method according to the present invention will be described below with reference to FIG.

【0018】図1は、本発明に係る焼却灰処理装置の一
実施形態を示す系統図である。本発明の焼却灰処理装置
の実施形態としてのごみ灰処理装置1は、被焼却物であ
るごみを焼却した際に発生するごみ灰a(焼却灰)を加
熱して溶融する灰溶融炉3と、この灰溶融炉3で発生し
た排ガスG1の熱を回収すると共に、前記排ガスG1中の
溶融飛灰bを分別する熱回収分別手段としての熱回収部
8と、この熱回収部8から排出された排ガス中の溶融飛
灰bを集塵する飛灰集塵手段としての集塵器12と、熱
回収部8及び集塵器12で分別乃至集塵された溶融飛灰
bに水と薬剤を加えて、重金属類と塩類を含む水溶液と
に分離する処理分離手段としての湿式無害化処理装置1
6とを備えている。そして、熱回収部8で回収された熱
を利用して湿式無害化処理装置16で分離された塩類を
含む水溶液dを蒸発固化する蒸発固化手段としての蒸発
塔21を設けたことである。ここで、蒸発塔21の蒸発
固化は、集塵器12から排出される排ガスG2を熱回収
部8に設けた熱交換器9に通すことによって加熱される
排ガスG3を吹き込むことによって行なわれる。
FIG. 1 is a system diagram showing one embodiment of an incineration ash treatment apparatus according to the present invention. The refuse ash treatment device 1 as an embodiment of the incineration ash treatment device of the present invention includes an ash melting furnace 3 for heating and melting refuse ash a (incineration ash) generated when incinerating refuse as refuse. , while recovering heat exhaust gas G 1 generated by the ash melting furnace 3, the heat recovery section 8 as a heat recovery fractionation means for separating the molten fly ash b in the exhaust gas G 1, from the heat recovery unit 8 A dust collector 12 as fly ash dust collecting means for collecting the molten fly ash b in the discharged exhaust gas, and water is added to the molten fly ash b separated or collected by the heat recovery unit 8 and the dust collector 12. Wet detoxification treatment apparatus 1 as treatment separation means for adding a chemical and separating it into an aqueous solution containing heavy metals and salts
6 is provided. Then, an evaporating tower 21 is provided as evaporating and solidifying means for evaporating and solidifying the aqueous solution d containing salts separated by the wet detoxifying apparatus 16 using the heat recovered by the heat recovery unit 8. Here, the evaporation solidification of the evaporation tower 21, is carried out by blowing the exhaust gas G 3 which is heated by passing the exhaust gas G 2 discharged from the dust collector 12 to the heat exchanger 9 provided in the heat recovery section 8 .

【0019】更に、詳しく説明すると、灰溶融炉3に供
給したごみ灰aは、同時に供給した空気f及び燃料eの
燃焼熱により1,000℃以上に加熱され溶融し、減容
化、無害化されたスラグgとして炉低より排出される。
ごみ灰a中にはアルカリ金属類の塩化物を中心とした低
沸点物質が数十%も含まれており、これらが溶融時の高
熱により揮発し気体となる。その他にも鉛、カドミウム
等の低沸点重金属も同時に揮発し灰溶融炉の排ガスG
1(1,000〜1,400℃)と共に配管30aを通じ
て熱回収部8に送られる。
More specifically, the refuse ash a supplied to the ash melting furnace 3 is heated and melted to 1,000 ° C. or more by the heat of combustion of the air f and the fuel e supplied at the same time, thereby reducing the volume and detoxifying the ash. The slag g is discharged from the furnace bottom.
The refuse ash a contains several tens% of low-boiling substances, mainly chlorides of alkali metals, which are volatilized by high heat during melting to become gas. In addition, low-boiling heavy metals such as lead and cadmium volatilize at the same time and exhaust gas G from the ash melting furnace
1 (1,000 to 1,400 ° C.) and sent to the heat recovery unit 8 through the pipe 30a.

【0020】この高温排ガスG1は、熱回収部8で後段
の集塵器12が耐えられる程度の温度、例えば、後段の
集塵器12としてバグフィルタを使用する場合には20
0〜250℃程度に熱回収され冷却される。この時、灰
溶融炉3で揮発し排ガスG1中に含まれるガス状の塩化
物及び低沸点重金属は再び凝縮、凝固しダストとなる。
これらの低沸点物質が凝固したダスト及び灰溶融炉で舞
い上がり排ガスG1に同伴した微細なごみ灰aは、所謂
溶融飛灰bとして熱回収部8の下部に沈降したり、下流
の集塵器12で集塵(又は捕集)される。これらの溶融
飛灰bは配管30bを通じて溶融飛灰ホッパ14に集め
られる。溶融飛灰ホッパ14に集められた溶融飛灰bは
湿式無害化処理装置16に送られる。
The high-temperature exhaust gas G 1 is heated to a temperature at which the latter-stage dust collector 12 can withstand in the heat recovery unit 8, for example, 20 ° C. when a bag filter is used as the latter-stage dust collector 12.
Heat is recovered to about 0 to 250 ° C. and cooled. At this time, gaseous chloride contained in the exhaust gas G 1 volatilized in ash melting furnace 3 and the low-boiling heavy metals recondensed, the solidified dust.
These fine dust ash a entrained in the exhaust gas G 1 flyaway in dust and ash melting furnace in which the lower boiling point material is coagulated or settled to the bottom of the heat recovery section 8 as a so-called molten fly ash b, downstream of the dust collector 12 Dust is collected (or collected) by the. These molten fly ash b are collected in the molten fly hopper 14 through the pipe 30b. The molten fly ash b collected in the molten fly ash hopper 14 is sent to the wet detoxification processing device 16.

【0021】湿式無害化処理装置16は、溶融飛灰b中
に含まれる重金属類を無害化するための薬剤i、例えば
キレート剤などが配管30cを通じて添加される。更
に、配管30dを通じて水hが供給され、溶融飛灰b中
に含まれる塩化物は殆どすべて水溶性物質のため水hに
溶解し配管30eを通じて蒸発塔21に送られる。
In the wet detoxification processing unit 16, a chemical i for detoxifying heavy metals contained in the molten fly ash b, for example, a chelating agent is added through a pipe 30c. Further, water h is supplied through the pipe 30d, and almost all chlorides contained in the molten fly ash b are dissolved in the water h because they are water-soluble substances, and are sent to the evaporation tower 21 through the pipe 30e.

【0022】ところで、集塵器12によりダスト(溶融
飛灰b)が除去されたクリーンな排ガスG2は200〜
250℃であるので、配管30eを介して送られた塩類
を含む水溶液d(塩類含有廃水)を蒸発させる蒸発塔2
1に直接吹き込むと、排ガスの温度が140℃以下とな
り、煙道で結露したり、極端な場合には排煙に必要な浮
力が不足したりする。これを避けるため、集塵器12出
口の200〜250℃の温度の低温排ガスG2を配管3
0fを介して熱回収部8に設けた熱交換器9に通す。
By the way, the clean exhaust gas G 2 from which dust (melted fly ash b) has been removed by the dust collector 12 is 200 to 200 μm.
Since the temperature is 250 ° C., the evaporating tower 2 evaporates the aqueous solution d containing salts (salt-containing wastewater) sent through the pipe 30e.
If the gas is blown directly into the exhaust gas 1, the temperature of the exhaust gas will be 140 ° C. or less, causing dew condensation in the flue. In an extreme case, the buoyancy required for exhausting the smoke will be insufficient. To avoid this, low temperature exhaust gas G 2 the pipe 3 at a temperature of 200 to 250 ° C. of the dust collector 12 outlet
It passes through a heat exchanger 9 provided in the heat recovery unit 8 via 0f.

【0023】熱交換器9に通された排ガスG3は、40
0℃程度に加熱、昇温され、この排ガスG3を蒸発塔2
1に吹き込むことによって、湿式無害化処理装置16か
ら送られ噴霧された塩類を含む水溶液dは、蒸発塔21
で気化し、塩化物は微細な固体の塩類となる。この微細
な塩類は後流の別の集塵器24で集塵され、集塵器24
の下部から有害な重金属を含まない固体の粉体の塩類j
として回収される。又、蒸発塔21に吹き込まれた約4
00℃の排ガスG3は、塩類を含む水溶液dの気化によ
り熱を奪われ、約140℃の排ガスG4となり、集塵器
24で塩類jが回収され、排風機26により煙突28か
ら排煙される。
The exhaust gas G 3 passed through the heat exchanger 9 is 40
The exhaust gas G 3 is heated to about 0 ° C. and heated, and the
1, the aqueous solution d containing salts sprayed and sprayed from the wet detoxification apparatus 16 is discharged from the evaporating tower 21.
And the chlorides turn into fine solid salts. This fine salt is collected in another downstream dust collector 24, and is collected by the dust collector 24.
Harmful heavy metal-free solid powder salts j from the bottom
Will be collected as In addition, about 4
The exhaust gas G 3 at 00 ° C. is deprived of heat by the vaporization of the aqueous solution d containing salts, becomes exhaust gas G 4 at about 140 ° C., the salt j is collected by the dust collector 24, and the smoke is exhausted from the chimney 28 by the exhaust fan 26. Is done.

【0024】本実施形態のごみ灰処理装置1は、熱回収
部8で回収された熱を利用する蒸発塔21を設けたこと
により、設備的に小型で簡便な塩類回収装置とすること
が出来、装置の設備費、電力コスト及び運転コストの低
減が可能となる。更に、特別な熱源を必要とせずに効率
的、経済的に塩類を回収することが出来る。
The refuse ash treatment apparatus 1 of the present embodiment is provided with the evaporating tower 21 utilizing the heat recovered by the heat recovery section 8, so that the apparatus can be made compact and simple in terms of facilities. In addition, it is possible to reduce equipment costs, power costs, and operation costs of the apparatus. Further, the salt can be efficiently and economically recovered without requiring a special heat source.

【0025】更に、集塵器12から排出された排ガスG
2が、ある程度温度が高いので、この排ガスG2を熱回収
部の熱交換器9に通すことによって容易に温度を高める
ことが出来、高濃度の塩類を含んだ水溶液d(廃水)を
排ガスG3の熱を利用して気化させ、複雑で高価な設備
を使用せずに簡便で自前の廃熱を利用して速やかに蒸発
固化することが出来る。
Further, the exhaust gas G discharged from the dust collector 12
2, since a certain degree temperature is high, the exhaust gas G 2 a can be increased easily temperature by passage through heat exchanger 9 of the heat recovery unit, high including the concentration of aqueous salt solution d (wastewater) the exhaust gas G It is possible to vaporize using the heat of ( 3 ) and quickly evaporate and solidify using its own waste heat without using complicated and expensive equipment.

【0026】上記実施形態のごみ灰処理装置1において
は、熱回収部3に熱交換器9を設け、集塵器12から排
出される200〜250℃の排ガスG2をこの熱交換器
9で加熱し、約400℃の排ガスG3として蒸発塔21
に吹き込んだが、熱回収部3に熱交換器9を設けずに、
集塵器12から排出された排ガスG2を別に設けたガス
ヒータ(図示せず)によって、約400℃に加熱、昇温
させ蒸発塔21に吹き込むようにしても良い。
In the refuse ash treatment apparatus 1 of the above embodiment, a heat exchanger 9 is provided in the heat recovery section 3, and the exhaust gas G 2 at 200 to 250 ° C. discharged from the dust collector 12 is passed through the heat exchanger 9. heating, evaporation tower 21 as an exhaust gas G 3 of about 400 ° C.
But without providing the heat exchanger 9 in the heat recovery section 3,
The dust collector 12 provided separately from the gas heater has been the exhaust gas G 2 discharged from the (not shown), heated to about 400 ° C., warmed may be blown into the evaporation tower 21.

【0027】次に、本実施形態のごみ灰処理方法につい
て図1を利用して説明する。本実施形態のごみ灰処理方
法は、ごみを焼却した際に発生するごみ灰aを加熱して
溶融し、発生した排ガスG1中の溶融飛灰bを分別し、
この溶融飛灰bに水hと薬剤iを加えて重金属類を含む
スラッジcと塩類を含む水溶液dとに分離し、これらの
重金属類と塩類をそれぞれ回収するものである。更に、
ごみ灰aを加熱して溶融する際に発生する熱を利用して
塩類を含む水溶液dを蒸発固化し、固体の塩類jとして
回収する。ごみ灰aを加熱して溶融する際に発生する熱
を利用して塩類を含む水溶液dを蒸発固化するので、簡
便に固体の粉体として塩類jを回収することが出来、且
つ特別な熱源を必要とせずに効率的、経済的に塩類jを
回収することが出来る。
Next, the waste ash treatment method of the present embodiment will be described with reference to FIG. Waste ash treatment method of this embodiment, by heating the dust ash a generated when incinerated waste melt, fractionating melt fly ash b in the exhaust gas G 1 generated,
Water h and chemicals i are added to the molten fly ash b to separate them into sludge c containing heavy metals and aqueous solution d containing salts, and these heavy metals and salts are respectively recovered. Furthermore,
An aqueous solution d containing salts is evaporated and solidified by utilizing heat generated when the refuse ash a is heated and melted, and collected as solid salts j. Since the aqueous solution d containing salts is evaporated and solidified using the heat generated when the refuse ash a is heated and melted, the salts j can be easily recovered as solid powder, and a special heat source is used. The salt j can be efficiently and economically recovered without the need.

【0028】[0028]

【発明の効果】本発明の焼却灰処理装置又は焼却灰処理
方法によれば、設備的に小型で簡便であり、特別な熱源
を必要とせずに効率的、経済的に塩類を回収することが
出来る。
According to the incineration ash treatment apparatus or the incineration ash treatment method of the present invention, the equipment is compact and simple, and the salt can be efficiently and economically recovered without a special heat source. I can do it.

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

【図1】本発明に係る焼却灰処理装置の一実施形態を示
す系統図である。
FIG. 1 is a system diagram showing an embodiment of an incineration ash treatment device according to the present invention.

【図2】従来技術に係るごみ灰処理装置の例を示す系統
図である。
FIG. 2 is a system diagram showing an example of a refuse ash treatment device according to the related art.

【符号の説明】[Explanation of symbols]

1 ごみ灰処理装置(焼却灰処理装置) 3 灰溶融炉 8 熱回収部(熱回収分別手段) 9 熱交換器 12 集塵器(飛灰集塵手段) 16 湿式無害化処理装置(処理分離手段) 21 蒸発塔(蒸発固化手段) G1 灰溶融炉で発生した排ガス G2 集塵器から排出された排ガス G3 熱交換器で加熱された排ガス a ごみ灰(焼却灰) b 溶融飛灰 c 重金属類を含むスラッジ d 塩類を含む水溶液 h 水 i 薬剤 j 塩類DESCRIPTION OF REFERENCE SYMBOLS 1 Waste ash treatment device (incineration ash treatment device) 3 Ash melting furnace 8 Heat recovery unit (heat recovery separation means) 9 Heat exchanger 12 Dust collector (fly ash dust collection means) 16 Wet detoxification processing device (treatment separation means) 21) Evaporation tower (evaporation solidification means) G 1 Exhaust gas generated in ash melting furnace G 2 Exhaust gas discharged from dust collector G 3 Exhaust gas heated by heat exchanger a Waste ash (incinerated ash) b Melt fly ash c Sludge containing heavy metals d Aqueous solution containing salts h Water i Drug j Salts

───────────────────────────────────────────────────── フロントページの続き (72)発明者 守 秀治 神奈川県横浜市磯子区磯子一丁目2番10号 バブコック日立株式会社横浜エンジニア リングセンタ内 ──────────────────────────────────────────────────続 き Continued on the front page (72) Inventor Hideharu Mori 1-2-10 Isogo, Isogo-ku, Yokohama-shi, Kanagawa Prefecture Inside the Babcock Hitachi, Ltd. Yokohama Engineering Center

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 被焼却物を焼却した際に発生する重金属
類及び塩類を含む焼却灰を加熱して溶融する灰溶融炉
と、該灰溶融炉で発生した排ガスの熱を回収すると共
に、前記排ガス中の飛灰を分別する熱回収分別手段と、
該熱回収分別手段から排出された排ガス中の飛灰を集塵
する飛灰集塵手段と、前記熱回収分別手段及び飛灰集塵
手段で分別乃至集塵された飛灰に水と薬剤を加えて、重
金属類と塩類を含む水溶液とに分離する処理分離手段と
を備えた焼却灰処理装置において、前記熱回収分別手段
で回収された熱を利用して前記処理分離手段で分離され
た塩類を含む水溶液を蒸発固化する蒸発固化手段を設け
たことを特徴とする焼却灰処理装置。
1. An ash melting furnace for heating and melting incinerated ash containing heavy metals and salts generated when incinerated objects are incinerated, and recovering heat of exhaust gas generated in the ash melting furnace. Heat recovery separation means for separating fly ash in exhaust gas,
Fly ash dust collecting means for collecting fly ash in the exhaust gas discharged from the heat recovery and separating means, and water and chemicals to fly ash separated or collected by the heat recovery and separating means and fly ash dust collecting means. In addition, in an incineration ash treatment device provided with a treatment separation means for separating heavy metals and an aqueous solution containing salts, the salt separated by the treatment separation means using heat recovered by the heat recovery separation means An incineration ash treatment device comprising an evaporating and solidifying means for evaporating and solidifying an aqueous solution containing.
【請求項2】 請求項1において、前記蒸発固化手段の
蒸発固化は、前記飛灰集塵手段から排出された排ガスを
前記熱回収分別手段に設けた熱交換器に通すことによっ
て加熱される排ガスを吹き込むことによって行なわれる
ことを特徴とする焼却灰処理装置。
2. The evaporating and solidifying means according to claim 1, wherein the evaporating and solidifying means comprises an exhaust gas heated by passing an exhaust gas discharged from the fly ash dust collecting means through a heat exchanger provided in the heat recovery and separating means. The incineration ash treatment device characterized by performing by blowing air.
【請求項3】 被焼却物を焼却した際に発生する重金属
類及び塩類を含む焼却灰を加熱して溶融し、発生した排
ガス中の飛灰を分別し、該飛灰に水と薬剤を加えて重金
属類と塩類を含む水溶液とに分離し、該重金属類と塩類
をそれぞれ回収する焼却灰処理方法において、前記焼却
灰を加熱して溶融する際に発生する熱を利用して前記塩
類を含む水溶液を蒸発固化し、固体の塩類として回収す
ることを特徴とする焼却灰処理方法。
3. An incinerated ash containing heavy metals and salts generated when the incinerated material is incinerated is heated and melted, fly ash in the generated exhaust gas is separated, and water and a chemical are added to the fly ash. In the incineration ash treatment method of separating the heavy metals and salts by an aqueous solution containing heavy metals and salts, the heat incineration ash is heated and melted to contain the salts. A method for treating incineration ash, comprising evaporating and solidifying an aqueous solution and recovering it as solid salts.
JP08170098A 1998-03-27 1998-03-27 Incineration ash treatment apparatus and incineration ash treatment method Expired - Fee Related JP3837684B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP08170098A JP3837684B2 (en) 1998-03-27 1998-03-27 Incineration ash treatment apparatus and incineration ash treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP08170098A JP3837684B2 (en) 1998-03-27 1998-03-27 Incineration ash treatment apparatus and incineration ash treatment method

Publications (2)

Publication Number Publication Date
JPH11281040A true JPH11281040A (en) 1999-10-15
JP3837684B2 JP3837684B2 (en) 2006-10-25

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Country Link
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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7265254B2 (en) 2001-07-30 2007-09-04 Taiheiyo Cement Corporation Waste processing method, waste processing system, integrated waste processing method, and integrated waste processing system
JP2013160666A (en) * 2012-02-07 2013-08-19 National Institute Of Advanced Industrial & Technology Method for safely disposing burned ash containing radioactive cesium
CN113546944A (en) * 2021-07-14 2021-10-26 北京科技大学 Method for degrading dioxin in waste incineration fly ash and recycling potassium and sodium elements

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7265254B2 (en) 2001-07-30 2007-09-04 Taiheiyo Cement Corporation Waste processing method, waste processing system, integrated waste processing method, and integrated waste processing system
JP2013160666A (en) * 2012-02-07 2013-08-19 National Institute Of Advanced Industrial & Technology Method for safely disposing burned ash containing radioactive cesium
CN113546944A (en) * 2021-07-14 2021-10-26 北京科技大学 Method for degrading dioxin in waste incineration fly ash and recycling potassium and sodium elements
CN113546944B (en) * 2021-07-14 2023-02-28 北京科技大学 Method for degrading dioxin in waste incineration fly ash and recycling potassium and sodium elements

Also Published As

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