JPH0646092B2 - Waste heat recovery type sludge incinerator - Google Patents

Waste heat recovery type sludge incinerator

Info

Publication number
JPH0646092B2
JPH0646092B2 JP33052187A JP33052187A JPH0646092B2 JP H0646092 B2 JPH0646092 B2 JP H0646092B2 JP 33052187 A JP33052187 A JP 33052187A JP 33052187 A JP33052187 A JP 33052187A JP H0646092 B2 JPH0646092 B2 JP H0646092B2
Authority
JP
Japan
Prior art keywords
sludge
waste heat
exhaust gas
incinerator
amount
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
Application number
JP33052187A
Other languages
Japanese (ja)
Other versions
JPH01174802A (en
Inventor
勲 勝俣
俊英 姉崎
正利 斎藤
修郎 猪川
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.)
Kanagawa Prefecture
Original Assignee
Kanagawa Prefecture
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 Kanagawa Prefecture filed Critical Kanagawa Prefecture
Priority to JP33052187A priority Critical patent/JPH0646092B2/en
Publication of JPH01174802A publication Critical patent/JPH01174802A/en
Publication of JPH0646092B2 publication Critical patent/JPH0646092B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Landscapes

  • Incineration Of Waste (AREA)
  • Gasification And Melting Of Waste (AREA)
  • Control Of Steam Boilers And Waste-Gas Boilers (AREA)

Description

【発明の詳細な説明】 [産業上の利用分野] この発明は、廃熱回収型汚泥焼却設備に関するものであ
る。
TECHNICAL FIELD The present invention relates to a waste heat recovery type sludge incineration facility.

[従来の技術] 下水汚泥、し尿汚泥等の汚泥焼却設備に、近年省エネル
ギ焼却を目的として汚泥乾燥機、廃熱ボイラ等を付帯さ
せる例が多い。
[Prior Art] In recent years, sludge incinerators such as sewage sludge and human waste sludge are often provided with a sludge dryer, a waste heat boiler, etc. for the purpose of energy-saving incineration.

第2図に、その1例を示す。1は汚泥の流動焼却路、2
は流動空気予熱器、3は廃熱ボイラ、4は汚泥乾燥機で
ある。焼却路1からの排ガスは、先ず空気予熱器2に入
りブロワから送給される流動用空気を予熱する。次いで
排ガスの熱は廃熱ボイラ3で回収され蒸気を発生する。
発生蒸気の1部は汚泥乾燥機4に送られ汚泥の乾燥に利
用される。熱回収後の排ガスは、処理装置5で集塵、洗
浄処理されて煙突6から排出される。
FIG. 2 shows an example thereof. 1 is a sludge fluidized incinerator, 2
Is a fluidized air preheater, 3 is a waste heat boiler, and 4 is a sludge dryer. The exhaust gas from the incinerator 1 first enters the air preheater 2 to preheat the flowing air fed from the blower. Next, the heat of the exhaust gas is recovered by the waste heat boiler 3 to generate steam.
A part of the generated steam is sent to the sludge dryer 4 and used for drying the sludge. The exhaust gas after the heat recovery is subjected to dust collection and cleaning processing in the processing device 5, and is discharged from the chimney 6.

[解決しようとする問題点] しかし、上記従来設備には、次のような問題がある。[Problems to be Solved] However, the above conventional equipment has the following problems.

被焼却物である汚泥の性状(含水率、発熱量)変動に伴
い、発生排ガス温度、風量が変動し、これらはそのまま
廃熱ボイラに持ち込まれ、発生蒸気量の変動をもたら
す。
Due to changes in the properties (moisture content, calorific value) of sludge, which is the material to be incinerated, the generated exhaust gas temperature and air volume fluctuate, and these are brought into the waste heat boiler as they are, causing fluctuations in the amount of generated steam.

一方、汚泥乾燥機で消費される蒸気量は汚泥の含水率、
汚泥投入量により、一義的に決定されるといってよく、
従って蒸気消費量は廃熱ボイラの発生蒸気量と全く別の
要因で変動する。
On the other hand, the amount of steam consumed in the sludge dryer is the water content of sludge,
It can be said that it is uniquely determined by the amount of sludge input,
Therefore, the steam consumption fluctuates due to a factor completely different from the amount of steam generated by the waste heat boiler.

これら変動は、結果的には蒸気量の過不足として顕在化
する。特に、汚泥熱量が自燃点を越えている場合は、燃
焼排ガス量も増大し、その結果廃熱ボイラでの発生蒸気
量も増加するが、汚泥乾燥機が必要とする蒸気量は逆に
減少する(汚泥熱量が高い為、乾燥度を低くせざるを得
ない)為、蒸気バランスがくずれ、プラントの安定した
運転が不可能となる。
As a result, these fluctuations become apparent as an excess or deficiency of the steam amount. In particular, when the amount of sludge heat exceeds the self-burning point, the amount of combustion exhaust gas also increases, and as a result, the amount of steam generated in the waste heat boiler also increases, but the amount of steam required by the sludge dryer decreases conversely. (Since the amount of sludge heat is high, the degree of drying must be lowered.) Therefore, the steam balance is disturbed and stable operation of the plant becomes impossible.

従って、このような場合は、焼却炉への汚泥投入量を減
らして、燃焼排ガス量を減らし、もってボイラでの発生
蒸気量を減らす方法をとらざるを得ない。しかし、この
措置は頻度、期間によっては下水処理場の汚泥処理全般
への影響も避けられず、大きな問題になっている。
Therefore, in such a case, there is no choice but to take a method of reducing the amount of sludge input to the incinerator to reduce the amount of combustion exhaust gas and thus the amount of steam generated in the boiler. However, depending on the frequency and the period, this measure will inevitably affect the overall sludge treatment at the sewage treatment plant, which is a big problem.

また、廃熱ボイラは年1回の定期検査を義務付けられて
おり、その期間中は焼却プラント全体を停止せざるを得
ず、その間の汚泥焼却処理ができないことも同システム
の問題となっている。
Moreover, the waste heat boiler is obliged to carry out a periodic inspection once a year, and the entire incineration plant must be stopped during that period, and the sludge incineration process during that period is also a problem of the system. .

この発明は、上記のような問題点を解消できるようにし
た廃熱回収型汚泥焼却設備を提供することを目的とする
ものである。
It is an object of the present invention to provide a waste heat recovery type sludge incinerator capable of solving the above problems.

[問題点を解決するための手段] この発明の廃熱回収型汚泥焼却設備は、汚泥焼却炉と、
この焼却炉の排ガスの熱を回収する廃熱ボイラとを備え
た廃熱回収型汚泥焼却設備において、処理汚泥を乾燥し
て焼却炉に送給する系に設けられた重量制御装置と、処
理汚泥を焼却炉に直投する系に設けられた重量制御装置
と、廃熱ボイラを通る排ガスの量を制御して発生蒸気圧
力を制御する圧力制御装置と、廃熱ボイラのバイパス路
に設けられた排ガスクーラと、この排ガスクーラの冷媒
量を制御して出口ガス温度を制御する温度制御装置とを
備えてなるものである。
[Means for Solving Problems] The waste heat recovery type sludge incinerator of the present invention comprises a sludge incinerator,
In a waste heat recovery type sludge incinerator equipped with a waste heat boiler that recovers the heat of the exhaust gas of this incinerator, a weight control device provided in a system for drying the treated sludge and sending it to the incinerator, and the treated sludge. Is installed in the system for directly throwing the waste heat into the incinerator, the pressure control device for controlling the generated steam pressure by controlling the amount of exhaust gas passing through the waste heat boiler, and the bypass path of the waste heat boiler. It comprises an exhaust gas cooler and a temperature control device for controlling the outlet gas temperature by controlling the refrigerant amount of the exhaust gas cooler.

[作用] 乾燥系及び直投系にそれぞれ設けられた重量制御装置に
よって、焼却炉への汚泥全投入量を計画値に保ちつつ、
汚泥性状により乾燥系と直投系との投入比率を変えるこ
とにより発生排ガス量の安定化を図る。また、圧力制御
装置により廃熱ボイラを通る排ガス量を制御することに
より、発生蒸気圧を一定に維持する。そして、この制御
に伴いバイパス流量が変動しても、後続する排ガス処理
装置に悪影響を及ぼさないように、温度制御装置により
ガスクーラ出口温度を制御する。
[Operation] While keeping the total amount of sludge into the incinerator at the planned value by the weight control devices provided in the dry system and the direct throw system,
The amount of exhaust gas generated will be stabilized by changing the input ratio between the dry system and the direct injection system depending on the sludge properties. Further, the generated steam pressure is maintained constant by controlling the amount of exhaust gas passing through the waste heat boiler by the pressure control device. Then, even if the bypass flow rate changes due to this control, the temperature control device controls the gas cooler outlet temperature so as not to adversely affect the subsequent exhaust gas treatment device.

また、ボイラ定期検査時には、排ガスを全量バイパス
し、ガスクーラに流入させることによりボイラの定期検
査を可能とし、且つガスクーラにて本来ボイラで吸熱す
べき熱量を併せて吸熱させることによって、後続する排
ガス処理装置への悪影響も防止する。
In addition, during the boiler regular inspection, the exhaust gas is bypassed entirely and is allowed to flow into the gas cooler for periodic inspection of the boiler. It also prevents adverse effects on the device.

[実施例] 以下、本発明の一実施例を第1図により説明する。ここ
で、上記第1図の従来のものと同一構成の部分は図面の
同一箇所に同一符号を付してその詳細な説明を省略す
る。
[Embodiment] An embodiment of the present invention will be described below with reference to FIG. Here, the same components as those of the conventional one shown in FIG. 1 are denoted by the same reference numerals in the drawings, and detailed description thereof will be omitted.

脱水後の汚泥ケーキが、ホッパー11から汚泥乾燥機4
を備えた乾燥系12及び直投系13を介して流動焼却炉
1に投入されるようになっている。乾燥系12及び直投
系13のそれぞれに投入汚泥量を制御する重量制御装置
14及び15が設けられている。そして、各重量制御装
置14、15の設定値は焼却炉1の炉内温度制御装置1
6により設定されるようになっている。
The sludge cake after dehydration is fed from the hopper 11 to the sludge dryer 4
It is designed to be put into the fluidized incinerator 1 through a drying system 12 and a direct throwing system 13 each equipped with. The drying system 12 and the direct throwing system 13 are respectively provided with weight control devices 14 and 15 for controlling the amount of sludge input. Then, the set values of the weight control devices 14 and 15 are set to the in-furnace temperature control device 1 of the incinerator 1.
6 is set.

廃熱ボイラ3には、ドラム3aの圧力を検出し、発生蒸
気圧力を所定の値に保つ圧力制御装置21が設けられ、
ボイラ3を通る排ガス量をボイラ出口に設けられた弁2
2により制御するようになっている。
The waste heat boiler 3 is provided with a pressure control device 21 that detects the pressure of the drum 3a and keeps the generated steam pressure at a predetermined value.
The amount of exhaust gas passing through the boiler 3 is controlled by the valve 2 provided at the boiler outlet.
It is controlled by 2.

廃熱ボイラ3にバイパス路30が設けられ、このバイパ
ス路に排ガスクーラ31が設けられている。このガスク
ーラは、ブロワ33から送給される空気を冷媒としてガ
スを冷却するようになっている。そして、ブロワ33か
らの送気量を制御して出口ガス温度を所定の値に保つ温
度制御装置32が設けられている。一方、熱交換して加
熱された空気は管路35を介して煙突6に導かれ、煙突
からでる排気の白煙を防止するようになっている。
A bypass 30 is provided in the waste heat boiler 3, and an exhaust gas cooler 31 is provided in this bypass. This gas cooler is designed to cool the gas using the air sent from the blower 33 as a refrigerant. A temperature control device 32 is provided to control the amount of air sent from the blower 33 and maintain the outlet gas temperature at a predetermined value. On the other hand, the air that has been heat-exchanged and heated is guided to the chimney 6 through the pipe 35 to prevent white smoke in the exhaust gas from the chimney.

次に、上記装置の作用について説明する。Next, the operation of the above device will be described.

脱水後の汚泥ケーキの含水率は約80%で、焼却炉1へ
の全投入量の約30%を乾燥系12から、残り70%を
直投系15から投入する。焼却炉1からの発生排ガスの
温度、風量は汚泥の性状(含水率、発熱量)により変動
する。そこで、汚泥性状変動による発生排ガスの変動を
焼却炉1の炉内温度の変動として捕え、温度制御装置1
6により投入汚泥の乾燥系12と直投系13への分配割
合いを変更する。例えば、汚泥ケーキの含水率が低下し
た場合、炉温が上昇するので、乾燥系からの投入割合い
を下げる。この場合、焼却炉に投入される固形分量はほ
ぼ一定であるので発生排ガス量は殆んど変化しない。こ
うして、焼却炉1から排ガスを安定して発生させること
ができる。
The water content of the sludge cake after dehydration is about 80%, and about 30% of the total amount of the sludge cake is put into the incinerator 1 from the drying system 12 and the remaining 70% from the direct throwing system 15. The temperature and air volume of the exhaust gas generated from the incinerator 1 vary depending on the properties of the sludge (water content, calorific value). Therefore, the fluctuation of the generated exhaust gas due to the fluctuation of the sludge property is captured as the fluctuation of the temperature inside the incinerator 1, and the temperature control device 1
By 6, the distribution ratio of the input sludge to the drying system 12 and the direct throwing system 13 is changed. For example, when the water content of the sludge cake decreases, the furnace temperature rises, so the rate of addition from the drying system is decreased. In this case, since the amount of solid content charged into the incinerator is almost constant, the amount of exhaust gas generated hardly changes. In this way, exhaust gas can be stably generated from the incinerator 1.

上記により、発生排ガス量を安定させることはできる
が、蒸気消費量の変動により、ドラム圧力が変動する。
そこで、消費先に一定した蒸気を供給するために、圧力
制御装置21によりボイラ3を通る排ガス量を制御す
る。こうして、一定圧力の蒸気を使用先に供給すること
ができる。
Although the generated exhaust gas amount can be stabilized by the above, the drum pressure changes due to the change in the steam consumption amount.
Therefore, the amount of exhaust gas passing through the boiler 3 is controlled by the pressure control device 21 in order to supply constant steam to the consumer. In this way, steam with a constant pressure can be supplied to the destination.

一方、上記操作に伴って、バイパス路30を流れる排ガ
ス量が変動する。例えば、ボイラ3を通る排ガス量を絞
った場合には、バイパス路30を流れる排ガス量が増加
する。この場合に、排ガスクーラ31出口温度が上昇し
てガス処理装置5に悪影響を及ぼさないようにするた
め、温度制御装置32により冷媒空気の量を増加して出
口ガス温度を一定に維持する。
On the other hand, the amount of exhaust gas flowing through the bypass 30 changes with the above operation. For example, when the amount of exhaust gas passing through the boiler 3 is reduced, the amount of exhaust gas flowing through the bypass passage 30 increases. In this case, in order to prevent the exhaust gas cooler 31 outlet temperature from increasing and adversely affecting the gas treatment device 5, the temperature control device 32 increases the amount of refrigerant air to maintain the outlet gas temperature constant.

また、ボイラ3の定期検査時には、弁22を全閉とし、
かつ乾燥系12、乾燥機14を停止とする直投系運転モ
ードを選び焼却運転を行う。焼却炉排ガスはバイパス路
30により全量ガスクーラ31に導入される。この時、
ガスクーラ31での必要吸熱量は、通常時の約5倍に増
加する為、冷媒空気量もそれに応じて約3倍に増加させ
てガスクーラ出口温度を後段のガス処理装置5に影響を
及ぼさない温度まで冷却する。これらは制御装置32に
て行われる。この場合、冷媒ブロア33の常用点は上記
最大値の約1/3である為、常用時での省エネルギを計
る為、ブロワ33はインバータ制御、ベーン制御等がな
されるようになっている。
Further, at the time of periodic inspection of the boiler 3, the valve 22 is fully closed,
In addition, the direct throwing system operation mode in which the drying system 12 and the dryer 14 are stopped is selected and the incineration operation is performed. The total amount of incinerator exhaust gas is introduced into the gas cooler 31 by the bypass passage 30. At this time,
Since the required amount of heat absorption in the gas cooler 31 increases about 5 times that in normal times, the amount of refrigerant air is also increased about 3 times accordingly, so that the gas cooler outlet temperature does not affect the gas processing device 5 in the subsequent stage. Cool down. These are performed by the controller 32. In this case, since the service point of the refrigerant blower 33 is about ⅓ of the maximum value, the blower 33 is subjected to inverter control, vane control, etc. in order to save energy during normal use.

なお、上記例では、排ガスクーラ出口ガス温度を検出し
て温度制御するようにしているが、冷媒空気のクーラ出
口温度を検出して温度制御しても同様の効果を得ること
ができる。また、クーラの冷媒とて水を用い、ガスを散
水冷却するようにしてもよい。また、ボイラ3を通る排
ガス量の制御弁22をボイラ出口に設けてあるが、ボイ
ラ入口に設けてもよいことは勿論である。
In the above example, the temperature of the exhaust gas cooler outlet is detected and the temperature is controlled, but the same effect can be obtained by detecting the temperature of the cooler outlet of the refrigerant air and controlling the temperature. Further, water may be used as the coolant of the cooler to cool the gas by spraying. Further, although the control valve 22 for the amount of exhaust gas passing through the boiler 3 is provided at the boiler outlet, it goes without saying that it may be provided at the boiler inlet.

次に、上記装置を組み込んだ実炉の運転実績について説
明する。但し、この実炉では上記実施例と異なり、温度
制御装置32の温度検出装置はクーラ出口空気温度とな
っている。
Next, the operation results of an actual furnace incorporating the above device will be described. However, in this actual furnace, unlike the above embodiment, the temperature detection device of the temperature control device 32 is at the cooler outlet air temperature.

公称焼却炉能力 70t/d 汚泥条件 含水率 71〜78(平均73.2)% 発熱量 730〜410kcal/Kg 処理汚泥量 直投系 平均2306(最大2540、最小2070) Kg/h 55.3t/d 乾燥系 平均926(最大1060、最小640) Kg/h 22.22/t/d 廃熱ボイラ 入口ガス温度 720〜780℃ 出口ガス温度 180℃ 発生蒸気量 2000〜900Kg/h 発生蒸気圧力 7.0±0.8atg (設定値7.0atg) クーラ出口空気温度 180±10℃ (設定値180℃) 上記のように、汚泥の含水率、発熱量の変動にも拘ら
ず、設計値を上まわる処理量で、汚泥を処理することが
でき、また一定した圧力の蒸気を発生させることがで
き、さらにガスクーラ出口温度も所定の値に制御するこ
とができた。
Nominal incinerator capacity 70t / d Sludge condition Moisture content 71 to 78 (73.2 on average)% Calorific value 730 to 410kcal / Kg Amount of treated sludge Average 2306 (max 2540, min 2070) Kg / h 55.3t / d Dry Average 926 (maximum 1060, minimum 640) Kg / h 22.22 / t / d Waste heat boiler Inlet gas temperature 720-780 ° C Outlet gas temperature 180 ° C Generated steam amount 2000-900Kg / h Generated steam pressure 7.0 ± 0.8atg (Set value 7.0atg) Cooler outlet air temperature 180 ± 10 ℃ (Set value 180 ℃) As mentioned above, treat the sludge with a treatment amount that exceeds the design value, regardless of fluctuations in the water content and calorific value of the sludge. In addition, it was possible to generate steam at a constant pressure and to control the gas cooler outlet temperature to a predetermined value.

[発明の効果] この発明の廃熱回収型汚泥焼却設備は、上記のようなも
ので、処理汚泥の性状の変動にも拘らず、目標量を処理
することができる事は勿論、排ガス処理装置の悪影響を
与えることなく、一定圧力の蒸気を発生させることがで
きる。また、廃熱ボイラの定期検査時にも汚泥焼却運転
を続けることができる。
[Effects of the Invention] The waste heat recovery type sludge incineration facility of the present invention is as described above, and of course, the target amount can be treated regardless of the change in the property of the treated sludge, and the exhaust gas treating apparatus is of course possible. It is possible to generate steam at a constant pressure without adversely affecting. Further, the sludge incineration operation can be continued even during the periodic inspection of the waste heat boiler.

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

第1図は本発明の一実施例を示す説明図、第2図は従来
の廃熱回収型汚泥焼却設備の説明図である。 1……汚泥焼却炉、3……廃熱ボイラ、4……汚泥乾燥
機、12……乾燥系、13……直投系、14、15……
重量制御装置、21……圧力制御装置、30……バイパ
ス路、31……排ガスクーラ、32……温度制御装置
FIG. 1 is an explanatory view showing an embodiment of the present invention, and FIG. 2 is an explanatory view of a conventional waste heat recovery type sludge incineration facility. 1 ... Sludge incinerator, 3 ... Waste heat boiler, 4 ... Sludge dryer, 12 ... Drying system, 13 ... Direct throwing system, 14, 15 ...
Weight control device, 21 ... Pressure control device, 30 ... Bypass passage, 31 ... Exhaust gas cooler, 32 ... Temperature control device

───────────────────────────────────────────────────── フロントページの続き (72)発明者 猪川 修郎 東京都千代田区丸の内1丁目1番2号 日 本鋼管株式会社内 (56)参考文献 特開 昭59−89921(JP,A) 特開 昭59−229105(JP,A) 実開 昭58−46902(JP,U) 実開 昭56−66604(JP,U) 実開 昭62−62123(JP,U) ─────────────────────────────────────────────────── ─── Continuation of front page (72) Inventor Shuro Inokawa 1-2-1, Marunouchi, Chiyoda-ku, Tokyo Nihon Kokan Co., Ltd. (56) References JP-A-59-89921 (JP, A) JP-A-SHO 59-229105 (JP, A) Actual opening 58-46902 (JP, U) Actual opening 56-66604 (JP, U) Actual opening 62-62123 (JP, U)

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】汚泥焼却炉と、この焼却炉の排ガスの熱を
回収する廃熱ボイラとを備えた廃熱回収型汚泥焼却設備
において、処理汚泥を乾燥して焼却炉に送給する系に設
けられた重量制御装置と、処理汚泥を焼却炉に直投する
系に設けられた重量制御装置と、廃熱ボイラを通る排ガ
スの量を制御して発生蒸気圧力を制御する圧力制御装置
と、廃熱ボイラのバイパス路に設けられた排ガスクーラ
と、この排ガスクーラの冷媒量を制御して出口ガス温度
を制御する温度制御装置とを備えてなる廃熱回収型汚泥
焼却設備。
1. A waste heat recovery type sludge incinerator equipped with a sludge incinerator and a waste heat boiler for recovering heat of exhaust gas from the incinerator, to a system for drying treated sludge and sending it to the incinerator. A weight control device provided, a weight control device provided in the system that directly throws the treated sludge to the incinerator, a pressure control device that controls the generated steam pressure by controlling the amount of exhaust gas passing through the waste heat boiler, A waste heat recovery type sludge incinerator comprising an exhaust gas cooler provided in a bypass path of a waste heat boiler and a temperature control device for controlling an amount of refrigerant in the exhaust gas cooler to control an outlet gas temperature.
JP33052187A 1987-12-26 1987-12-26 Waste heat recovery type sludge incinerator Expired - Fee Related JPH0646092B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP33052187A JPH0646092B2 (en) 1987-12-26 1987-12-26 Waste heat recovery type sludge incinerator

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP33052187A JPH0646092B2 (en) 1987-12-26 1987-12-26 Waste heat recovery type sludge incinerator

Publications (2)

Publication Number Publication Date
JPH01174802A JPH01174802A (en) 1989-07-11
JPH0646092B2 true JPH0646092B2 (en) 1994-06-15

Family

ID=18233559

Family Applications (1)

Application Number Title Priority Date Filing Date
JP33052187A Expired - Fee Related JPH0646092B2 (en) 1987-12-26 1987-12-26 Waste heat recovery type sludge incinerator

Country Status (1)

Country Link
JP (1) JPH0646092B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012242029A (en) * 2011-05-23 2012-12-10 Metawater Co Ltd Heat recovery system from exhaust gas of incinerator
JP5852252B2 (en) * 2012-09-13 2016-02-03 三菱重工業株式会社 Coal-fired boiler equipment, coal drying method in coal-fired boiler equipment

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4734769B2 (en) * 2001-06-04 2011-07-27 株式会社Ihi Cogeneration plant operation method and apparatus
JP5780806B2 (en) * 2011-03-31 2015-09-16 株式会社クボタ Sludge incineration treatment system and sludge incineration treatment method

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012242029A (en) * 2011-05-23 2012-12-10 Metawater Co Ltd Heat recovery system from exhaust gas of incinerator
JP5852252B2 (en) * 2012-09-13 2016-02-03 三菱重工業株式会社 Coal-fired boiler equipment, coal drying method in coal-fired boiler equipment

Also Published As

Publication number Publication date
JPH01174802A (en) 1989-07-11

Similar Documents

Publication Publication Date Title
CA2266770A1 (en) Process and device for incineration of particulate solids
RU2469241C2 (en) Device and methods for combustion of waste water mud in furnace
JP2006291010A (en) Drying equipment for wet raw material and drying method
JPH0646092B2 (en) Waste heat recovery type sludge incinerator
JPS59180212A (en) Combustion controller in refuse incinerator
JPS59221512A (en) Sludge treatment device
JP2807813B2 (en) Method and apparatus for controlling fluidized bed dryer
JP2712017B2 (en) Combustion system and combustion furnace
JPS6155008B2 (en)
US5006322A (en) Controlling pollutants from boilers
JPH0626629A (en) Sludge melting system
JPH0798108A (en) Combustion controller for incinerator
JPH0214603B2 (en)
JPH11218383A (en) Waste drier and oxygen concentration control method in waste drier
JPS61256180A (en) Method of controlling powdered and granular body drier
JP2729915B2 (en) Fluidized bed furnace cooling method
JP3305175B2 (en) Sand bed combustion rate adjustment method for fluidized bed furnace
JP2001272170A (en) Operating method for waste drying facility
JPH09196330A (en) Waste combustion furnace and method for controlling its combustion
Shiono et al. Stable combustion in sludge melting furnace by fuzzy logic control
JP2623404B2 (en) Operating method and apparatus of fluidized bed incinerator
JP2628038B2 (en) Fluidized bed sludge incinerator with incineration ash cooling device
JP2602612B2 (en) Fluidized bed incineration of waste powder
JPS588A (en) Temperature control method in sludge incinerator
JPS63143412A (en) Method of operating incinerator

Legal Events

Date Code Title Description
R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

LAPS Cancellation because of no payment of annual fees