JP2000346329A - Method and apparatus for treating waste - Google Patents

Method and apparatus for treating waste

Info

Publication number
JP2000346329A
JP2000346329A JP11153688A JP15368899A JP2000346329A JP 2000346329 A JP2000346329 A JP 2000346329A JP 11153688 A JP11153688 A JP 11153688A JP 15368899 A JP15368899 A JP 15368899A JP 2000346329 A JP2000346329 A JP 2000346329A
Authority
JP
Japan
Prior art keywords
temperature
exhaust gas
dust collector
waste
sludge
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
JP11153688A
Other languages
Japanese (ja)
Inventor
Akira Nakamura
章 中村
Takashi Noto
隆 能登
Yoshinari Fujisawa
能成 藤沢
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.)
JFE Engineering Corp
Original Assignee
NKK Corp
Nippon Kokan Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by NKK Corp, Nippon Kokan Ltd filed Critical NKK Corp
Priority to JP11153688A priority Critical patent/JP2000346329A/en
Priority to GB0304004A priority patent/GB2381572B/en
Priority to PCT/JP1999/006481 priority patent/WO2000031470A1/en
Priority to GB0304005A priority patent/GB2381573B/en
Priority to KR1020007007418A priority patent/KR20010033858A/en
Priority to GB0015728A priority patent/GB2348270B/en
Publication of JP2000346329A publication Critical patent/JP2000346329A/en
Pending legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To reduce a concentration of dioxins in an incinerating furnace and to suppress generation of dioxins or the like even in an electric dust collector by multi-fuel burning a sludge in the case of incinerating a waste, and operating the collector at a specific temperature or below. SOLUTION: Not only a waste supply hopper 1a but also a sludge supply hopper 1b are newly provided in an incinerating furnace 1. A temperature sensor 7 for detecting an exhaust gas temperature is installed at an inlet of an electric dust collector 4. Further, a dust collector inlet temperature controller 8 for controlling to operate the collector 4 at 230 deg.C or below by controlling a temperature lowering facility 2 to increase a temperature lowering degree of a high temperature exhaust gas when a detected value of the sensor 7 exceeds 230 deg.C or when a temperature rise is abrupt even at the stage that the value of the sensor 7 does not exceed 230 deg.C is provided. The facility 2 has a temperature lowering tower of the type for passing here the high temperature exhaust gas through a water spraying atmosphere to thereby lower the gas temperature.

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、ごみを焼却炉にて
焼却し、発生する排ガスを処理してから大気へ放出させ
る廃棄物処理システムにおいて、ダイオキシン類を効率
よく低減させ得る廃棄物処理方法および装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a waste treatment method for efficiently reducing dioxins in a waste treatment system in which waste is incinerated in an incinerator, and the generated exhaust gas is treated and released to the atmosphere. And equipment.

【0002】[0002]

【従来の技術】都市ごみ、排プラスチック等の廃棄物
(以下、これらを単に廃棄物という)を焼却処理する焼
却炉設備の代表的なもののシステム構成を図3に示す。
図において、1は廃棄物供給ホッパ1aを有する焼却
炉、2は例えば減温塔、ボイラ、熱交換器などからなる
減温設備、3は減温設備2にて減温された排ガスからH
ClやSOx などの酸性ガスを除去する排ガス処理設
備、4は電気集塵機、5は誘引ファン、6は煙突であ
り、これらは煙道を介して直列に接続されている。
2. Description of the Related Art FIG. 3 shows a typical system configuration of an incinerator facility for incinerating waste such as municipal waste and plastic waste (hereinafter, these are simply referred to as waste).
In the figure, reference numeral 1 denotes an incinerator having a waste supply hopper 1a, 2 denotes a temperature-reducing facility composed of, for example, a temperature-reducing tower, a boiler, a heat exchanger, and the like.
Exhaust gas treatment equipment for removing acidic gases such as Cl and SOx, 4 is an electric dust collector, 5 is an induction fan, 6 is a chimney, and these are connected in series via a flue.

【0003】このようなものにおいて、ごみピットから
クレーンで焼却炉に投入された棄物は、焼却炉1で乾燥
されて燃焼し、未燃分が完全に燃焼する。焼却後、燃焼
排ガスは炉外へと排出され、減温設備2、排ガス処理設
備3、電気集塵機4を経て、煙突6から外に放出され
る。
[0003] In such a case, the waste put into the incinerator by the crane from the waste pit is dried and burned in the incinerator 1, and the unburned matter is completely burned. After the incineration, the combustion exhaust gas is discharged out of the furnace, and is discharged from the chimney 6 through the temperature reduction equipment 2, the exhaust gas treatment equipment 3, and the electric dust collector 4.

【0004】[0004]

【発明が解決しようとする課題】ところで、電気集塵機
4は、周知のようにガスやダストの性状による影響に左
右されず微細な粒子の捕集が可能であるという特徴を持
つ。しかし、このような廃棄物処理システムの場合、焼
却炉1の炉出口から排出された排ガスは、減温設備2や
排ガス処理設備3を経由し、およそ300℃程度で電気集
塵機4に導入され、集塵が行われていることが多い。こ
の300℃前後の温度は、ダイオキシンが生成され易い温
度であり、燃焼排ガスをこの300℃前後の温度で電気集
塵機4を通過させてしまうと、ダイオキシン濃度が高く
なり、煙突6から排出されてしまうという問題がある。
As is well known, the electrostatic precipitator 4 is characterized by being able to collect fine particles without being affected by the properties of gas or dust. However, in the case of such a waste treatment system, the exhaust gas discharged from the furnace outlet of the incinerator 1 is introduced into the electric precipitator 4 at about 300 ° C. through the temperature reduction equipment 2 and the exhaust gas treatment equipment 3, Dust collection is often performed. The temperature of about 300 ° C. is a temperature at which dioxin is easily generated. If the flue gas is passed through the electric dust collector 4 at the temperature of about 300 ° C., the dioxin concentration becomes high and the dioxin is discharged from the chimney 6. There is a problem.

【0005】本発明の技術的課題は、比較的簡単な装置
の導入により、焼却炉内の燃焼状態を一定に維持して、
焼却炉におけるダイオキシン類濃度を低減させ、かつ電
気集塵機部においてもダイオキシンの生成を抑えること
ができるようにすることにある。
The technical problem of the present invention is to maintain a constant combustion state in an incinerator by introducing a relatively simple apparatus,
It is an object of the present invention to reduce the concentration of dioxins in an incinerator and to suppress the generation of dioxins in an electric dust collector.

【0006】[0006]

【課題を解決するための手段】本発明に係る廃棄物処理
方法は、焼却炉、減温設備、排ガス処理設備、電気集塵
機、誘引ファン、及び煙突を、煙道を介して直列に接続
してなる廃棄物処理システムにおいて、廃棄物を焼却す
る際に、汚泥を混焼させるとともに、電気集塵機を230
℃以下で運転することを特徴としている。
According to the present invention, there is provided a waste disposal method comprising connecting an incinerator, a temperature reduction facility, an exhaust gas treatment facility, an electric dust collector, an induction fan, and a chimney in series via a flue. In the waste treatment system, when incinerating the waste, the sludge is mixed and the electric dust collector is set to 230.
It is characterized in that it is operated at a temperature of not more than ℃.

【0007】また、この方法に用いられる装置は、焼却
炉、減温設備、排ガス処理設備、電気集塵機、誘引ファ
ン、及び煙突を、煙道を介して直列に接続してなる廃棄
物処理システムにおいて、焼却炉に、廃棄物供給ホッパ
と汚泥供給ホッパを設けるとともに、電気集塵機が230
℃以下で運転されるように制御する集塵機入口温度制御
装置を設けたものである。
[0007] The apparatus used in this method is a waste treatment system in which an incinerator, a temperature reduction facility, an exhaust gas treatment facility, an electric dust collector, an induction fan, and a chimney are connected in series via a flue. The incinerator is equipped with a waste supply hopper and a sludge supply hopper, and the
It is provided with a dust collector inlet temperature control device for controlling operation at a temperature of not more than ° C.

【0008】また、本発明に係る廃棄物処理方法は、排
ガスの電気集塵機入口部での温度が230℃以下となるよ
うに減温設備を制御することを特徴としている。
Further, the waste disposal method according to the present invention is characterized in that the temperature reducing equipment is controlled so that the temperature of the exhaust gas at the inlet of the electric dust collector is 230 ° C. or less.

【0009】また、この方法に用いられる装置は、電気
集塵機入口部に排ガス温度を検出する温度センサを設置
し、集塵機入口温度制御装置は、この温度センサの検出
値をもとに電気集塵機入口部の温度が230℃以下となる
ように減温設備を制御する構成としたものである。
In the apparatus used in this method, a temperature sensor for detecting the temperature of exhaust gas is installed at the entrance of the electric precipitator, and the temperature control device at the entrance of the precipitator is based on the detected value of the temperature sensor. The structure is such that the temperature reducing equipment is controlled so that the temperature is 230 ° C. or less.

【0010】[0010]

【発明の実施の形態】以下、本発明の実施形態に係る廃
棄物処理方法およびこの方法に用いられる装置を図1に
基づき説明する。図1は本実施形態に係る廃棄物処理装
置のシステム構成を示す図であり、図中、前述の従来例
(図3)と同一部分には同一符号を付してある。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Hereinafter, a waste disposal method according to an embodiment of the present invention and an apparatus used in the method will be described with reference to FIG. FIG. 1 is a diagram showing a system configuration of a waste disposal apparatus according to the present embodiment. In the figure, the same parts as those in the above-described conventional example (FIG. 3) are denoted by the same reference numerals.

【0011】本実施形態の廃棄物処理装置は、焼却炉1
に、廃棄物供給ホッパ1aだけでなく、汚泥供給ホッパ
1bを新たに設けるとともに、電気集塵機4の入口部に
排ガス温度を検出する温度センサ7を設置し、さらに温
度センサ7の検出値が230℃を超えた時、あるいは温度
センサ7の検出値が230℃を超えない段階でも上昇が急
激であれば、減温設備2を制御して高温排ガスの減温度
合いを大きくさせることで、電気集塵機4が230℃以下
で運転されるように制御する集塵機入口温度制御装置8
を設けている。
The waste treatment apparatus according to the present embodiment includes an incinerator 1
In addition to the waste supply hopper 1a, a sludge supply hopper 1b is newly provided, and a temperature sensor 7 for detecting the temperature of the exhaust gas is installed at the entrance of the electric precipitator 4, and the detected value of the temperature sensor 7 is 230 ° C. If the temperature rises rapidly even when the temperature exceeds the temperature, or even when the detected value of the temperature sensor 7 does not exceed 230 ° C., the temperature reduction equipment 2 is controlled to increase the degree of temperature reduction of the high-temperature exhaust gas. Dust collector inlet temperature control device 8 that controls so that it operates at 230 ° C or less
Is provided.

【0012】減温設備2は、ここでは高温排ガスを水噴
霧雰囲気中を通過させることでそのガス温度を下げる方
式の減温塔からなり、集塵機入口温度制御装置8から水
噴霧量増加指令があると、その水噴霧量を多くするよう
構成されている。
The temperature reducing equipment 2 here comprises a temperature reducing tower of a type in which a high-temperature exhaust gas is passed through a water spray atmosphere to lower the gas temperature, and a dust spray inlet temperature control device 8 issues a water spray amount increase command. The water spray amount is increased.

【0013】なお、ここで用いる汚泥は、下水処理に伴
って発生する下水汚泥、し尿汚泥、有機性排水を活性汚
泥処理した際に発生する汚泥、有機物を含む排水を固液
分離したときに発生する汚泥、河川しゅんせつ時等に閉
鎖性水域で発生する汚泥、その他下水処理の過程で発生
する汚泥等、どのような種類の汚泥でも構わない。
The sludge used here is generated when solid-liquid separation is performed on sewage sludge, night soil sludge generated with sewage treatment, sludge generated when organic wastewater is treated with activated sludge, and wastewater containing organic substances. Any type of sludge may be used, such as sludge generated in closed water bodies during river dredging, and sludge generated in the course of sewage treatment.

【0014】次に、これをさらに詳述しながら本実施形
態装置を用いて廃棄物を処理する方法について説明す
る。まず、ごみピットからクレーンで廃棄物を搬送して
供給ホッパ1aより焼却炉1内に投入するとともに、汚
泥供給ホッパ1bより例えば下水処理工程等で発生した
有機性汚泥を投入する。焼却炉1内に投入された汚泥と
廃棄物は、炉内で乾燥され、着火して混焼し、排ガスは
炉出口から下流に送られる。これにより、廃棄物のみを
焼却させる場合と比較してダイオキシン濃度が低くな
る。これは以下の理由による。
Next, a method of treating waste using the apparatus according to the present embodiment will be described in further detail. First, waste is conveyed from a refuse pit by a crane, and is put into the incinerator 1 from the supply hopper 1a, and organic sludge generated in, for example, a sewage treatment process is thrown from the sludge supply hopper 1b. The sludge and waste put into the incinerator 1 are dried in the furnace, ignited and co-fired, and the exhaust gas is sent downstream from the furnace outlet. As a result, the dioxin concentration is lower than in the case where only waste is incinerated. This is for the following reason.

【0015】すなわち、汚泥中のS分は、燃焼過程にお
いてH2S、CS2、COS、SO2、SO3として焼却炉
1内に存在する。これらの物質は、ダイオキシン類生成
の触媒となる銅やその類似物質に対する被毒効果を持
ち、炉内高温燃焼場から炉出口以降の排ガスラインで効
果的にダイオキシン類を抑制させる。
That is, the S component in the sludge is present in the incinerator 1 as H2S, CS2, COS, SO2, and SO3 during the combustion process. These substances have a poisoning effect on copper or a similar substance serving as a catalyst for the production of dioxins, and effectively suppress dioxins in an exhaust gas line from the high temperature combustion field in the furnace to the exhaust gas after the furnace outlet.

【0016】また、汚泥中のN分は、燃焼過程、特に一
次燃焼領域の還元雰囲気においてアンモニアを生成し、
これが塩素化合物と反応することにより、ダイオキシン
類生成過程にあるClのダイオキシン生成反応を抑制す
る。
Further, N in sludge generates ammonia in the combustion process, particularly in a reducing atmosphere in the primary combustion zone,
This reacts with the chlorine compound to suppress the dioxin production reaction of Cl in the process of producing dioxins.

【0017】さらにまた、汚泥中の水分は、可燃物の燃
焼反応速度を抑制し、すすの発生を低減させる。すすの
発生量が抑制されれば、それに起因する芳香族系の有機
化合物濃度が低くなり、結果として不完全燃焼生成物で
あるダイオキシン類物質濃度も低減される。
Further, the moisture in the sludge suppresses the combustion reaction rate of combustibles and reduces the generation of soot. If the amount of soot generation is suppressed, the concentration of aromatic organic compounds resulting therefrom decreases, and as a result, the concentration of dioxin-like substances, which are incomplete combustion products, is also reduced.

【0018】以上の理由により、廃棄物と汚泥を混焼す
ることによってダイオキシン濃度が低減されるが、更に
本発明者らは鋭意検討を重ねた結果、廃棄物と汚泥を混
焼させる際、電気集塵機4を使用し、その運転温度を下
げれば、ダイオキシン類濃度が低下することを発見し
た。これは、ダイオキシン類が生成しやすい300℃近辺
の領域をさけて低温で運転することにより、ダイオキシ
ンの生成が抑えられるためと考えられる。本発明者らの
実験研究により得られたこの知見を示したのが図2のグ
ラフである。これは、電気集塵機4の運転温度と、電気
集塵機4の入口と出口間におけるダイオキシンの増加率
の関係を示したグラフであり、縦軸にダイオキシン増加
率、横軸に電気集塵機入口温度をとっている。
For the above reasons, the dioxin concentration is reduced by co-firing waste and sludge. However, as a result of extensive studies, the present inventors have found that when co-firing waste and sludge, an electric precipitator 4 is used. It has been found that dioxin concentration decreases when the operating temperature is lowered by using a gas. This is considered to be because the generation of dioxins is suppressed by operating at a low temperature in a region around 300 ° C. where dioxins are easily generated. FIG. 2 is a graph showing this finding obtained by the experimental study of the present inventors. This is a graph showing the relationship between the operating temperature of the electric precipitator 4 and the rate of increase of dioxin between the inlet and the outlet of the electric precipitator 4, where the vertical axis indicates the dioxin increase rate and the horizontal axis indicates the electric precipitator inlet temperature. I have.

【0019】この結果から、電気集塵機温度を230℃以
下、好ましくは210℃以下にすれば電気集塵機4内でダ
イオキシン類濃度が増加せず、効率よくダイオキシン類
濃度を低減できることがわかる。
From these results, it can be seen that if the temperature of the electric dust collector is 230 ° C. or less, preferably 210 ° C. or less, the concentration of dioxins in the electric dust collector 4 does not increase, and the concentration of dioxins can be reduced efficiently.

【0020】したがって、電気集塵機入口に設置した温
度センサ7と集塵機入口温度制御装置8により、排ガス
温度を監視し、温度センサ7の検出値が230℃を超えた
時、あるいは温度センサ7の検出値が230℃を超えない
段階でも上昇が急激であれば、集塵機入口温度制御装置
8より減温設備2に対して水噴霧量増加指令を出力さ
せ、減温設備2の水噴霧量を多くさせて、高温排ガスの
減温度合いを大きくさせ、これによって電気集塵機4の
運転時の温度を230℃以下となるように管理すること
で、ダイオキシン類濃度を低減でき、この効果と汚泥の
供給によるダイオキシン類物質濃度低減効果との相乗効
果により一層効率的にダイオキシン類濃度を低減させる
ことができる。
Therefore, the temperature of the exhaust gas is monitored by the temperature sensor 7 installed at the entrance of the electric precipitator and the temperature control device 8 at the entrance of the precipitator, and when the detected value of the temperature sensor 7 exceeds 230 ° C. If the temperature does not exceed 230 ° C. and the temperature rises sharply, the dust collector inlet temperature control device 8 outputs a water spray amount increase command to the temperature reduction device 2 to increase the water spray amount of the temperature reduction device 2. By increasing the temperature reduction of the high-temperature exhaust gas and thereby controlling the temperature of the electric precipitator 4 during operation to 230 ° C. or less, the concentration of dioxins can be reduced. The synergistic effect with the substance concentration reducing effect allows the dioxin concentration to be reduced more efficiently.

【0021】なお、システム全体を自動制御している場
合、温度センサ7の検出値を運転パラメータの一つとし
て組み込めばよい。
When the entire system is automatically controlled, the detection value of the temperature sensor 7 may be incorporated as one of the operation parameters.

【0022】電気集塵機4により微細な粒子が捕集除去
されて、クリーンとなった空気は煙突6から大気へ放出
される。
The fine particles are collected and removed by the electric precipitator 4 and the clean air is discharged from the chimney 6 to the atmosphere.

【0023】本発明の効果を検証するために、都市ごみ
と汚泥を火格子式焼却炉で焼却を行い、減温塔で排ガス
を210℃まで減温してから電気集塵機で集塵を行った場
合におけるダイオキシン類濃度と、都市ごみのみを焼却
して電気集塵機を270℃で運転した場合におけるダイオ
キシン類濃度とを比較してみたところ、本発明による前
者のものが後者のものよりもダイオキシン類濃度が約9
割低減されていることが確認された。
In order to verify the effects of the present invention, municipal solid waste and sludge were incinerated in a grate incinerator, and the temperature of the exhaust gas was reduced to 210 ° C. in a cooling tower, and then collected by an electric dust collector. When the dioxin concentration in the case and the dioxin concentration in the case where only the municipal waste was incinerated and the electric dust collector was operated at 270 ° C. were compared, the former one according to the present invention had a higher dioxin concentration than the latter. Is about 9
It was confirmed that it was reduced relatively.

【0024】[0024]

【発明の効果】以上述べたように、本発明によれば、焼
却炉、減温設備、排ガス処理設備、電気集塵機、誘引フ
ァン、及び煙突を、煙道を介して直列に接続してなる廃
棄物処理システムにおいて、廃棄物を焼却する際に、汚
泥を混焼させるとともに、電気集塵機が230℃以下で運
転されるようにしたので、効率よくダイオキシン類の発
生を低減させることができた。
As described above, according to the present invention, a disposal system in which an incinerator, a temperature reducing facility, an exhaust gas treatment facility, an electric dust collector, an induction fan, and a chimney are connected in series via a flue. In the waste disposal system, when incinerating waste, the sludge was mixed and the electric precipitator was operated at 230 ° C or lower, so that the generation of dioxins could be reduced efficiently.

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

【図1】本発明の実施形態に係る廃棄物処理装置のシス
テム構成図である。
FIG. 1 is a system configuration diagram of a waste disposal apparatus according to an embodiment of the present invention.

【図2】電気集塵機の運転温度とダイオキシンの増加率
の関係を示すグラフである。
FIG. 2 is a graph showing the relationship between the operating temperature of an electrostatic precipitator and the rate of increase in dioxin.

【図3】従来の廃棄物処理装置のシステム構成図であ
る。
FIG. 3 is a system configuration diagram of a conventional waste disposal apparatus.

【符号の説明】[Explanation of symbols]

1 焼却炉 1a 廃棄物供給ホッパ 1b 汚泥供給ホッパ 2 減温設備 3 排ガス処理設備 4 電気集塵機 5 誘引ファン 6 煙突 7 温度センサ 8 集塵機入口温度制御装置 DESCRIPTION OF SYMBOLS 1 Incinerator 1a Waste supply hopper 1b Sludge supply hopper 2 Temperature reduction equipment 3 Exhaust gas treatment equipment 4 Electric dust collector 5 Induction fan 6 Chimney 7 Temperature sensor 8 Dust collector inlet temperature control device

───────────────────────────────────────────────────── フロントページの続き (72)発明者 藤沢 能成 東京都千代田区丸の内一丁目1番2号 日 本鋼管株式会社内 Fターム(参考) 3K061 AA24 AB01 AC02 BA05 BA08 DA18  ────────────────────────────────────────────────── ─── Continuing on the front page (72) Inventor Yoshinari Fujisawa 1-2-1 Marunouchi, Chiyoda-ku, Tokyo F-term (reference) 3K061 AA24 AB01 AC02 BA05 BA08 DA18

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 焼却炉、減温設備、排ガス処理設備、電
気集塵機、誘引ファン、及び煙突を、煙道を介して直列
に接続してなる廃棄物処理システムにおいて、 廃棄物を焼却する際に、汚泥を混焼させるとともに、電
気集塵機を230℃以下で運転することを特徴とする廃棄
物処理方法。
1. A waste treatment system in which an incinerator, a temperature reducing facility, an exhaust gas treatment facility, an electric dust collector, an induction fan, and a chimney are connected in series via a flue, when incinerating waste. A waste treatment method comprising co-firing sludge and operating an electric dust collector at 230 ° C or lower.
【請求項2】 排ガスの電気集塵機入口部での温度が23
0℃以下となるように減温設備を制御することを特徴と
する請求項1記載の廃棄物処理方法。
2. The temperature of the exhaust gas at the inlet of the electrostatic precipitator is 23.
The waste treatment method according to claim 1, wherein the temperature reducing equipment is controlled so as to be 0 ° C or less.
【請求項3】 焼却炉、減温設備、排ガス処理設備、電
気集塵機、誘引ファン、及び煙突を、煙道を介して直列
に接続してなる廃棄物処理システムにおいて、 前記焼却炉に、廃棄物供給ホッパと汚泥供給ホッパを設
けるとともに、 電気集塵機が230℃以下で運転されるように制御する集
塵機入口温度制御装置を設けたことを特徴とする廃棄物
処理装置。
3. A waste treatment system in which an incinerator, a temperature-reducing facility, an exhaust gas treatment facility, an electric dust collector, an induction fan, and a chimney are connected in series via a flue, A waste treatment apparatus comprising a supply hopper and a sludge supply hopper, and a dust collector inlet temperature control device for controlling the electric dust collector to operate at 230 ° C. or lower.
【請求項4】 電気集塵機入口部に排ガス温度を検出す
る温度センサを設置し、集塵機入口温度制御装置は、該
温度センサの検出値をもとに電気集塵機入口部の温度が
230℃以下となるように減温設備を制御する構成とした
ことを特徴とする請求項3記載の廃棄物処理装置。
4. A temperature sensor for detecting exhaust gas temperature is installed at an entrance of the electric precipitator, and a temperature control device at the entrance of the precipitator detects a temperature of the entrance of the electric precipitator based on a detection value of the temperature sensor.
4. The waste treatment apparatus according to claim 3, wherein the temperature reduction equipment is controlled so as to be 230 ° C. or less.
JP11153688A 1998-11-24 1999-06-01 Method and apparatus for treating waste Pending JP2000346329A (en)

Priority Applications (6)

Application Number Priority Date Filing Date Title
JP11153688A JP2000346329A (en) 1999-06-01 1999-06-01 Method and apparatus for treating waste
GB0304004A GB2381572B (en) 1998-11-24 1999-11-19 Waste disposal incineration method
PCT/JP1999/006481 WO2000031470A1 (en) 1998-11-24 1999-11-19 Waste incineration method and device therefor
GB0304005A GB2381573B (en) 1998-11-24 1999-11-19 Waste disposal incineration method and apparatus
KR1020007007418A KR20010033858A (en) 1998-11-24 1999-11-19 Waste incineration method and device therefor
GB0015728A GB2348270B (en) 1998-11-24 1999-11-19 Waste incineration method and device therefor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11153688A JP2000346329A (en) 1999-06-01 1999-06-01 Method and apparatus for treating waste

Publications (1)

Publication Number Publication Date
JP2000346329A true JP2000346329A (en) 2000-12-15

Family

ID=15567977

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11153688A Pending JP2000346329A (en) 1998-11-24 1999-06-01 Method and apparatus for treating waste

Country Status (1)

Country Link
JP (1) JP2000346329A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102297435A (en) * 2011-02-09 2011-12-28 张玉新 Horizontal active sludge incinerator and process realizing temperature adjustment and secondary exhaust gas combustion
CN107655008A (en) * 2017-09-01 2018-02-02 佛山市南海绿电再生能源有限公司 A kind of flue gas processing method and system for reducing waste incineration Zhong content of dioxin

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102297435A (en) * 2011-02-09 2011-12-28 张玉新 Horizontal active sludge incinerator and process realizing temperature adjustment and secondary exhaust gas combustion
CN107655008A (en) * 2017-09-01 2018-02-02 佛山市南海绿电再生能源有限公司 A kind of flue gas processing method and system for reducing waste incineration Zhong content of dioxin

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