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JP2656879B2 - Automatic combustion control method for incinerator - Google Patents
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JP2656879B2 - Automatic combustion control method for incinerator - Google Patents

Automatic combustion control method for incinerator

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Publication number
JP2656879B2
JP2656879B2 JP26622392A JP26622392A JP2656879B2 JP 2656879 B2 JP2656879 B2 JP 2656879B2 JP 26622392 A JP26622392 A JP 26622392A JP 26622392 A JP26622392 A JP 26622392A JP 2656879 B2 JP2656879 B2 JP 2656879B2
Authority
JP
Japan
Prior art keywords
amount
control
furnace
waste
combustion
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 - Lifetime
Application number
JP26622392A
Other languages
Japanese (ja)
Other versions
JPH06117618A (en
Inventor
利光 浜松
敏治 中村
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.)
Kobe Steel Ltd
Original Assignee
Kobe Steel 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 Kobe Steel Ltd filed Critical Kobe Steel Ltd
Priority to JP26622392A priority Critical patent/JP2656879B2/en
Publication of JPH06117618A publication Critical patent/JPH06117618A/en
Application granted granted Critical
Publication of JP2656879B2 publication Critical patent/JP2656879B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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  • Incineration Of Waste (AREA)

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本発明は、特に、都市ごみ焼却処
理に使用する流動床焼却炉を自動運転制御するための自
動燃焼制御方法に関する。
The present invention particularly relates to an automatic combustion control method for automatically controlling a fluidized bed incinerator used for municipal solid waste incineration.

【0002】[0002]

【従来の技術】従来の流動床式ごみ焼却炉では、自動燃
焼制御を行わせる場合、炉の出口における排出ガスの
温度を設定温度範囲内に制御する、流動砂層の温度を
設定温度範囲内に制御する、炉内圧力を適正な負圧に
保持する、主として燃焼処理量の定量供給制御による
ごみ供給量の制御、電気集じん器などの反応塔の入口
排ガス温度を設定温度範囲内に制御する、排ガスO2
濃度を検出して排ガスNOX を低減するよう二次空気の
吸い込み量制御が含まれる燃焼空気量の制御を行う、の
六つの制御がそれぞれ独立した単ループ自動制御として
組み込まれているものが多く、それらは操作者(オペレ
ータ)の経験と勘とによって、ごみ質を考慮しながら各
設定値を調整して運転制御していた。
2. Description of the Related Art In a conventional fluidized bed refuse incinerator, when automatic combustion control is performed, the temperature of the exhaust gas at the outlet of the furnace is controlled within a set temperature range. Control, keep the furnace pressure at an appropriate negative pressure, mainly control the amount of refuse supplied by quantitative supply control of the amount of combustion treatment, control the exhaust gas temperature at the inlet of the reaction tower such as an electric dust collector within the set temperature range , Exhaust gas O 2
Many things that are built as detecting and controlling the amount of combustion air that contains the suction amount control of the secondary air to reduce the exhaust gas NO X, single-loop automatic control six control is independent of the concentration In addition, they are operated and controlled by adjusting each set value in consideration of the waste quality, based on the experience and intuition of the operator (operator).

【0003】これとは別に、運転中の排ガス流量を演算
して、この値と冷却塔出入口温度とごみ供給量を用いて
ごみ発熱量を演算し、このごみ発熱量に応じてごみ、空
気供給量を自動設定する燃焼制御方法が特公平2−26
130号公報によって開示されている。
Separately from this, the flow rate of exhaust gas during operation is calculated, and the calorific value of the waste is calculated using this value, the temperature at the entrance and exit of the cooling tower, and the amount of waste supplied. Combustion control method for automatically setting the amount
No. 130 discloses this.

【0004】[0004]

【発明が解決しようとする課題】上記の各従来技術で
は、変動が激しいごみの質、供給量に対応させて、ごみ
を確実に安定して燃焼させることは難しく、その結果、
計画ごみ処理量に対して焼却処理を適応させることがで
きなく、また、排ガスNOX 濃度を下げられなくて公害
防止が果たせないし、最適経済燃焼が行えなくて燃焼処
理コストが高くつくなどの種々の問題がある。
In each of the prior arts described above, it is difficult to reliably and stably burn refuse in accordance with the quality and supply amount of refuse that fluctuates greatly.
Can not adapt the incineration process on planning waste throughput, also not reduced in the exhaust gas NO X concentration to pollution prevention can not fulfill various such combustion process costs can not be performed optimally economic combustion expensive There is a problem.

【0005】本発明は、このような問題点の解消を図る
ために成されたものであり、本発明の目的は、ごみ処理
量管理の合理化、公害の排除ならびに運転経済性,省力
化の推進を果たすことが可能な総合自動燃焼制御システ
ムを提供することにある。
The present invention has been made in order to solve such problems, and an object of the present invention is to rationalize waste management, eliminate pollution, promote operation economy, and save labor. It is an object of the present invention to provide a total automatic combustion control system capable of fulfilling the requirements.

【0006】[0006]

【課題を解決するための手段】本発明は、上記の目的を
達成するため以下に述べる構成としたものである。即
ち、本発明は、流動床焼却炉でごみを連続焼却するに際
し、炉出口ガス温度制御、砂層温度制御、炉内圧力制
御、ごみ供給量制御、反応塔入口排ガス温度制御、二次
空気の排ガスO2 濃度による自動制御を含む燃焼空気量
制御を、それぞれ単系統毎に自動制御する一方、ごみ発
熱量と燃焼用一次空気量との間に1次関数関係が成立す
ることから、ごみ発熱量の演算結果に基づき所要一次空
気量を算出して、所定時間経過する毎に一次空気量の目
標値を設定変更し、さらに、ガス冷却室排ガスO2
度、炉出口ガス温度、ガス冷却室噴射水量、炉内清水噴
霧水量、ごみ発熱量、目標焼却率の各データから各々補
正係数を演算により設定し、この補正係数に基づいてご
み供給量を増減させる補正制御をx秒/y分の時限で行
わせることを特徴とする焼却炉の自動燃焼制御方法であ
る。
The present invention has the following configuration to achieve the above object. That is, in the present invention, when continuously incinerating waste in a fluidized bed incinerator, furnace outlet gas temperature control, sand layer temperature control, furnace pressure control, waste supply control, reaction tower inlet exhaust gas temperature control, secondary air exhaust gas The combustion air amount control including the automatic control based on the O 2 concentration is automatically controlled for each single system. On the other hand, since a linear function relation is established between the waste heat amount and the primary air amount for combustion, the waste heat amount calculates a required primary air quantity based on the calculation result of the target value of the primary air amount for each of predetermined time and change settings, further gas cooling chamber exhaust O 2 concentration, the furnace exit gas temperature, the gas cooling chamber injection A correction coefficient is set by calculation from each data of the water amount, the fresh water spray water amount in the furnace, the waste heat value, and the target incineration rate, and the correction control for increasing / decreasing the waste supply amount based on the correction coefficient is performed for a time limit of x seconds / y. Characterized in that This is an automatic combustion control method for an incinerator.

【0007】[0007]

【作用】本発明によれば、現時点のごみ発熱量に適応し
た量の一次空気が演算されて、所定時間例えば20分程
度の1時間に満たない時間を経過する毎に一次空気供給
量が修正されることから、より安定した燃焼運転状況が
保たれ、しかも、この修正を行うことが決して外乱要素
とならないので、排ガスの温度、NOX 濃度の管理が徹
底される。さらに、演算により求めた補正係数に基づい
てごみ供給量を増減させる補正制御をx秒/y分、例え
ば1分毎に1秒の短周期、短時限で行わせることによっ
て、ごみ発熱量の変動に対して迅速に対応することがで
き、経済的な運転条件が確立されるとともに、運転員の
手動操作度数が従来に比して極端に少なくなる。
According to the present invention, the amount of primary air corresponding to the current amount of waste heat is calculated, and the primary air supply amount is corrected every time a predetermined time, for example, less than one hour such as about 20 minutes elapses. from being a more stable combustion operation status is maintained, moreover, since by performing this modification never become disturbance element, the temperature of the exhaust gas, the management of the nO X concentration is thorough. Further, by causing a correction control to increase or decrease the amount of waste supplied based on the correction coefficient obtained by the calculation in x seconds / y minutes, for example, in a short cycle and a short time period of 1 second every minute, the fluctuation of the amount of heat generated by the waste is changed. , And economical operating conditions are established, and the number of manual operations by the operator is extremely reduced as compared with the related art.

【0008】[0008]

【実施例】以下、本発明の実施例について添付図面を参
照しながら説明する。図1は、本発明方法の実施例に係
る流動床焼却炉の制御系統図である。流動床焼却炉(以
下、焼却炉と言う)1は、下部から給気部2、不活性砂
粒が浮遊状態に保たれる砂層部3、フリーボード部4を
内部に備える。給気部2には、押込送風機5を有する一
次空気供給管が接続され、一次空気が供給量の調節可能
に給気部2内に圧入される。押込送風機5は、空気量設
定器8の初期設定値と空気量検出器9が検出した空気量
とを入力要素としたフィードバック制御を行う制御手段
7によって駆動されるインバータ6により回転制御さ
れ、所要量の一次空気を給気部2内に供給する。この押
込送風機5の回転制御に応じて、砂層厚みの変化や空気
予熱器バイパス量の変化があっても、良好な流動状態を
維持し、最適燃焼状態を保つように一次空気量が制御さ
れる。
Embodiments of the present invention will be described below with reference to the accompanying drawings. FIG. 1 is a control system diagram of a fluidized bed incinerator according to an embodiment of the present invention. A fluidized bed incinerator (hereinafter, referred to as an incinerator) 1 includes an air supply unit 2, a sand layer unit 3 where inert sand particles are kept in a floating state, and a free board unit 4 from the bottom. A primary air supply pipe having a pushing blower 5 is connected to the air supply unit 2, and the primary air is press-fitted into the air supply unit 2 so that the supply amount can be adjusted. The rotation of the push-in blower 5 is controlled by an inverter 6 driven by a control unit 7 that performs feedback control using an initial setting value of an air amount setting device 8 and an air amount detected by an air amount detector 9 as input elements. An amount of primary air is supplied into the air supply 2. According to the rotation control of the push-in blower 5, even if there is a change in the thickness of the sand layer or a change in the bypass amount of the air preheater, the primary air amount is controlled so as to maintain a good flow state and maintain an optimum combustion state. .

【0009】一方、フリーボード部4の燃焼室には、二
次押込送風機10を有する二次空気供給管が接続され、
二次空気が供給量の調節可能に燃焼室内に圧入される。
二次押込送風機10は、排ガス02 濃度検出器13が検
出した排ガス02 濃度に基づいて、適正空気過剰率及び
排ガスNOX 値を低減するような二次空気量を算出する
演算手段14の出力と二次空気量検出器15が検出した
空気量とを入力要素としたフィードバック制御を行う制
御手段12によって駆動されるインバータ11により回
転制御され、所要量の二次空気を燃焼室内に供給する。
この押込送風機10の回転制御に応じて、最適空気比で
燃焼が行われ、常に、一定02 %が確保出来るよう二次
空気量の自動調整制御が成される。
On the other hand, a secondary air supply pipe having a secondary push blower 10 is connected to the combustion chamber of the free board section 4,
Secondary air is press-fitted into the combustion chamber with a controllable supply.
Secondary forced draft fan 10, based on exhaust gas 0 2 concentration exhaust gas 0 2 concentration detector 13 has detected, the calculating means 14 for calculating the quantity of secondary air so as to reduce the proper excess air ratio and exhaust gas NO X value The rotation is controlled by an inverter 11 driven by a control unit 12 that performs feedback control using the output and the air amount detected by the secondary air amount detector 15 as input elements, and supplies a required amount of secondary air into the combustion chamber. .
Combustion is performed at the optimum air ratio in accordance with the rotation control of the forced air blower 10, and automatic adjustment control of the secondary air amount is always performed so that a constant 0 2 % can be secured.

【0010】フリーボード部4のごみ供給口には、ごみ
供給機(給じん機)16が接続される。給じん機16
は、ごみ供給口に送られる給じん量が給じん量制御手段
17によって自動制御される。給じん量制御手段17
は、後述する炉出口ガス温度制御手段20を通じて出さ
れる炉出口ガス温度と、焼却量設定器18からの目標焼
却量と、クレーン投入量37と、後述するごみ発熱量推
定値とから求められる給じん量に応じた出力を給じん機
16に与えて、燃焼処理量の定量供給制御方式を基本と
する給じん量の自動制御を行う。
A waste supply unit (dusting machine) 16 is connected to a waste supply port of the free board unit 4. Dust feeding machine 16
The amount of dust fed to the waste supply port is automatically controlled by the dust amount control means 17. Dust supply control means 17
Is calculated from a furnace outlet gas temperature output through a furnace outlet gas temperature control means 20 described later, a target incineration amount from the incineration amount setting device 18, a crane charging amount 37, and a waste heat generation amount estimation value described later. An output corresponding to the amount of dust is given to the duster 16 to perform automatic control of the amount of dust based on a quantitative supply control method for the amount of combustion treatment.

【0011】フリーボード部4内上部には、冷却水ノズ
ル27が設けられ、流量制御弁33を有する冷却水管か
ら冷却水が供給される。流量制御弁33は、炉出口ガス
温度検出器19が検出する炉出口ガス温度に基づいて弁
開度出力を出す炉出口ガス温度制御手段20によって弁
開度が調節され、冷却水ノズル27から噴霧する炉内清
水噴霧水量を制御する。この噴霧水量の制御により、炉
出口温度は通常運転において常時、例えば、800〜9
00℃の範囲に入るよう自動制御される。
A cooling water nozzle 27 is provided in the upper part of the free board section 4, and cooling water is supplied from a cooling water pipe having a flow control valve 33. The flow control valve 33 has a valve opening controlled by a furnace outlet gas temperature control means 20 that outputs a valve opening output based on a furnace outlet gas temperature detected by a furnace outlet gas temperature detector 19, and is sprayed from a cooling water nozzle 27. To control the amount of fresh water spray in the furnace. By controlling the amount of sprayed water, the furnace outlet temperature can be constantly set, for example, from 800 to 9 in normal operation.
It is automatically controlled to enter the range of 00 ° C.

【0012】一方、砂層部3には、流量制御弁34を有
する燃焼空気管を介してバーナ26が接続される。流量
制御弁34は、砂層温度検出器36が検出する砂層温度
に基づいて弁開度出力を出す砂層温度制御手段35によ
って弁開度が調節され、燃焼空気管から送り込む燃焼空
気量(加熱量)を制御する。この加熱量の制御により、
砂層温度は通常運転において常時、例えば、650〜8
00℃の範囲に入るよう自動制御される。
On the other hand, a burner 26 is connected to the sand layer 3 via a combustion air pipe having a flow control valve 34. The flow rate control valve 34 has its valve opening adjusted by a sand layer temperature control means 35 that outputs a valve opening degree based on the sand layer temperature detected by the sand layer temperature detector 36, and the amount of combustion air (heating amount) sent from the combustion air pipe. Control. By controlling the amount of heating,
The sand layer temperature is usually 650 to 8 in normal operation.
It is automatically controlled to enter the range of 00 ° C.

【0013】フリーボード部4の最上部に設けられる排
ガス出口には、ガス冷却室21と電気集じん器22を備
える反応塔、誘引送風機23、煙突24が接続される。
ガス冷却室21には、冷却水ノズル28が設けられ、流
量制御弁32を有する冷却水管から冷却水が供給され
る。流量制御弁32は、検出された集じん器入口ガス温
度に基づいて弁開度出力を出す集じん器入口ガス温度制
御手段31によって弁開度が調節され、冷却水ノズル2
8から噴射するガス冷却室噴射水量を制御する。この噴
射水量の制御により、集じん器入口の排ガス温度は、通
常運転において常時例えば250〜300℃の温度範囲
に入るよう自動制御される。
A reaction tower having a gas cooling chamber 21 and an electric precipitator 22, an induction blower 23, and a chimney 24 are connected to an exhaust gas outlet provided at the uppermost part of the free board section 4.
A cooling water nozzle 28 is provided in the gas cooling chamber 21, and cooling water is supplied from a cooling water pipe having a flow control valve 32. The flow control valve 32 has a valve opening controlled by a dust collector inlet gas temperature control means 31 that outputs a valve opening based on the detected dust collector inlet gas temperature, and the cooling water nozzle 2
8 controls the amount of water injected from the gas cooling chamber. By controlling the injection water amount, the exhaust gas temperature at the inlet of the dust collector is automatically controlled so as to always fall within a temperature range of, for example, 250 to 300 ° C. in the normal operation.

【0014】前記排ガス出口に接続される排ガス管路に
は炉内圧力を検出する炉内圧検出器29が設けられ、検
出した炉内圧力は炉内圧制御手段30に出力される。炉
内圧制御手段30は、炉内圧力信号を受けると、インバ
ータ25に制御出力を与え、誘引送風機23の回転がイ
ンバータ25によって調節される。このように誘引送風
機23の回転を調節することによって、炉内圧力は一定
になるよう自動制御され、炉内を適正な負圧に保つこと
が可能である。
A furnace pressure detector 29 for detecting a furnace pressure is provided in an exhaust gas pipe connected to the exhaust gas outlet, and the detected furnace pressure is output to a furnace pressure control means 30. Upon receiving the furnace pressure signal, the furnace pressure control means 30 gives a control output to the inverter 25, and the rotation of the induction blower 23 is adjusted by the inverter 25. By adjusting the rotation of the induction blower 23 in this way, the pressure inside the furnace is automatically controlled to be constant, and the inside of the furnace can be maintained at an appropriate negative pressure.

【0015】図1に示される実施例の焼却炉1は、以上
説明した7つの自動制御系統を制御装置38によってコ
ントロールさせている。該制御装置38は、インプット
ポート,中央処理部(CPU),ディスプレイ部,アウ
トプットポートから形成されていて、前記各自動制御系
統の個別制御を行う他に、さらに、それらを総合し、デ
ータ処理装置の演算機能を活用して総合的なチェック・
調整を行うための自動燃焼制御システムを含んでいる。
この自動燃焼制御システムは、空気量検出器9が検出し
た一次空気量と、排ガス02 濃度検出器13が検出した
ガス冷却室排ガス02 濃度と、炉出口ガス温度検出器1
9が検出する炉出口ガス温度と、集じん器入口ガス温度
制御手段31に基づいて算出されたガス冷却室噴射水量
と、炉出口ガス温度制御手段20に基づいて算出された
炉内清水噴霧水量と、焼却量設定器18によって設定さ
れる目標焼却率(焼却量)とを、インプットポートに対
しデータとして入力させ、CPUでは、排ガス量および
エンタルピーからごみ発熱量を演算させるとともに、ガ
ス冷却室排ガス02 濃度、炉出口ガス温度、ガス冷却室
噴射水量、炉内清水噴霧水量、ごみ発熱量、目標焼却率
の各データから各々補正係数を演算させる。そして、ア
ウトプットポートからは、一次空気量の目標値およびご
み供給量の補正値を出力させる。
In the incinerator 1 of the embodiment shown in FIG. 1, the above-described seven automatic control systems are controlled by the control device 38. The control device 38 includes an input port, a central processing unit (CPU), a display unit, and an output port. In addition to individually controlling each of the automatic control systems, the control unit 38 further integrates them to perform data processing. Comprehensive check using the calculation function of the device
Includes an automatic combustion control system for making adjustments.
The automatic combustion control system includes a primary air volume of the air amount detector 9 detects a gas cooling chamber exhaust 0 2 concentration exhaust gas 0 2 concentration detector 13 has detected, the furnace exit gas temperature detector 1
9, the furnace outlet gas temperature, the gas cooling chamber injection water amount calculated based on the dust collector inlet gas temperature control means 31, and the furnace fresh water spray water amount calculated based on the furnace outlet gas temperature control means 20. And the target incineration rate (incineration amount) set by the incineration amount setting unit 18 as data into the input port, and the CPU calculates the amount of heat generated from the exhaust gas amount and the enthalpy. 0 2 concentration, the furnace exit gas temperature, the gas cooling chamber injection water, the furnace Shimizu spray water, waste heating value, thereby calculating each correction coefficient from the data of the target incineration rate. Then, the output port outputs a target value of the primary air amount and a correction value of the waste supply amount.

【0016】上記自動燃焼制御システムを設けたことに
よって、計画ごみ処理量に対する自動制御、最適空気量
の自動制御、最適経済燃焼制御が可能である。即ち、ご
み発熱量は、排ガス量およびそのエンタルピー演算によ
って求められ、このごみ発熱量と一次空気量との間には
1次関数関係が成立することから、必要な一次空気量を
算出して一定時間毎に一次空気量制御手段7に入力する
一次空気量の設定値を変化させる。また、ガス冷却室排
ガス02 濃度、炉出口ガス温度、ガス冷却室噴射水量、
炉内清水噴霧水量の各プロセス値およびごみ発熱量、目
標焼却率の各データを演算処理させて、各々の給じん量
に対する補正制御を1分当たり数秒の時限で行わせる。
次いで、ごみ供給量を補正しながら運転する場合の具体
的な制御手段の一例を下記に挙げる。先ず、補正タイプ
が異なる1系と2系とに対して、そのプロセス値及び補
正幅が示される下記の〔表1〕と〔表2〕とに基づいて
プロセス設定値(A〜D)と補正係数(E,F)をキー
ボード入力する。
By providing the above automatic combustion control system, it is possible to perform automatic control of the planned waste disposal amount, automatic control of the optimal air amount, and optimal economic combustion control. That is, the calorific value of the waste is obtained by calculating the exhaust gas amount and its enthalpy, and since a linear function relationship is established between the calorific value of the waste and the primary air amount, the necessary primary air amount is calculated and fixed. The set value of the primary air amount input to the primary air amount control means 7 is changed every time. The gas cooling chamber exhaust 0 2 concentration, the furnace exit gas temperature, the gas cooling chamber injection water,
Each process value of the in-furnace fresh water spray water amount, each heat generation amount of the waste, and each data of the target incineration rate are arithmetically processed, and the correction control for each dust amount is performed in a time limit of several seconds per minute.
Next, an example of specific control means in the case of operating while correcting the waste supply amount will be described below. First, the process set values (A to D) and the correction are set for the first and second systems having different correction types based on the following [Table 1] and [Table 2] showing the process values and the correction widths. The coefficient (E, F) is input by keyboard.

【0017】[0017]

【表1】 [Table 1]

【0018】[0018]

【表2】 [Table 2]

【0019】上記の〔表1〕及び〔表2〕において、各
上枠内の線図は、横軸にプロセス値(PV)、縦軸にご
み供給速度(SV)補正%を取ったごみ供給量補正用線
図で あって、この場合のPVとしては、各下枠内に表示
されているガス冷却室排ガス0 2 濃度(ガス冷0 2 )、
炉出口排ガス温度、炉内清水噴霧水量、ガス冷却室噴射
水量(ガス冷噴射水量)、ごみ発熱量、目標焼却率及び
ごみ投入量の7項目の各プロセス値が選ばれる。従っ
て、〔表1〕及び〔表2〕は、各プロセス値によってど
れだけの補正値を出力するかを表したものである。
In Tables 1 and 2 above, each
In the diagram in the upper frame, the process value (PV) is plotted on the horizontal axis and the plot is plotted on the vertical axis.
Waste supply amount correction line with the waste supply speed (SV) correction%
It is a figure and is displayed in each lower frame as PV in this case .
Has been that gas cooling chamber exhaust 0 2 concentration (Gasuhiya 0 2),
Furnace outlet exhaust gas temperature, furnace spray water flow, gas cooling chamber injection
Water volume (gas-cooled injection water volume), waste heat value, target incineration rate and
Each of the seven process values of the waste input is selected. Follow
Tables 1 and 2 depend on each process value.
This indicates whether only such correction values are output.

【0020】7項目のプロセス値について、そのうちの
一つの「炉出口排ガス温度」について補正の態様を説明
する。例えば、910℃(B)〜930℃(C)の範囲
であれば、SV補正出力は0であり、910℃未満
〔(B)〜(A)〕になると〔表2〕の補正タイプ2.
に基づいてプラス側に最大でも10%の補正出力(ごみ
供給量を増やす)を出し、930℃超過〔(C)〜
(D)〕になるとマイナス側に最大でも10%の補正出
力(ごみ供給量を増やす)を出すようにする。「ガス冷
2 濃度」、「ガス冷噴射水量」についても同要領で最
大で20%、15%の補正出力を出させる。
Regarding the seven process values,
Explanation of the mode of correction for one "furnace outlet exhaust gas temperature"
I do. For example, a range of 910 ° C (B) to 930 ° C (C)
If, the SV correction output is 0, which is less than 910 ° C.
When [(B)-(A)] is reached, the correction type 2.
Output of up to 10% on the plus side based on
Increase the supply amount) and exceed 930 ° C [(C) ~
(D)], a maximum of 10% correction is output to the minus side.
Give power (increase garbage supply). "Gas cooling
0 2 concentration ", the most in the same way also for the" gas cold injection amount of water. "
A correction output of at most 20% and 15% is output.

【0021】すなわち、各プロセス値がB〜C間は補正
出力は0で、B未満では最大E、C超過では最大Fの補
正係数がかかり、また、プロセス項目ごとにE及びFが
プラス値であったり、マイナス値であったりして、プロ
セス値が下がることによってごみ供給量を増大させ、ま
たは減少させるのを〔表1〕及び〔表2〕の画面におい
て設定する。〔表1〕〔表2〕は基本的に同じ画面であ
り、前述したように、「ガス冷0 2 濃度」が〔表1〕の
補正タイプ1.を、「炉出口排ガス温度」及び「ガス冷
噴射水量」が〔表2〕の補正タイプ2.をそれぞれ採用
している。
That is, each process value is corrected between B and C.
The output is 0, the maximum E below B and the maximum F above C.
A positive coefficient is applied, and E and F are
Positive value, negative value, professional
The waste value will increase and the waste supply will increase,
Or decrease it in the screen of [Table 1] and [Table 2].
To set. [Table 1] and [Table 2] are basically the same screen.
As described above, the “gas-cooled O 2 concentration” is as shown in [Table 1].
Correction type 1. To the "furnace outlet exhaust gas temperature"
Correction type 2. Each adopted
doing.

【0022】ここで、ごみ発熱量の設定値は〔表3〕
に、一次押込空気流量,二次押込空気流量の設定値は、
〔表4〕と〔表5〕に、また、炉内圧力増加分,目標焼
却量及びごみ投入量の各設定値については、〔表6〕に
それぞれ示される通りである。
Here, the set value of the calorific value is shown in [Table 3].
In addition, the set values of the primary pushing air flow rate and the secondary pushing air flow rate are
[Table 4] and [Table 5], and the set values of the furnace pressure increase, the target incineration amount, and the waste input amount are as shown in [Table 6], respectively.

【0023】[0023]

【表3】 [Table 3]

【0024】[0024]

【表4】 [Table 4]

【0025】[0025]

【表5】 [Table 5]

【0026】[0026]

【表6】 [Table 6]

【0027】その結果が、下記〔表7〕に示すように、
ごみ供給速度目標値(SV値 )に対する補正値にな
り、ガス冷却室排ガスO2 濃度からごみ投入量までの各
項目 V補正値は、「ガス冷0 2 濃度」はPV=2.
3%(表1の3.0%未満)であるから設定値Eの−2
0%、「炉出口排ガス温度」は930℃であるから0
%、「炉内清水噴霧水量」はこの場合補正出力無しの0
%、「ガス冷噴射水量」はPV=7976(表2の75
00超過)であるから設定値Fの−15%、「ごみ発熱
量」、「目標焼却率」及び「ごみ投入量」はこの場合い
ずれも補正出力無しの0%で、順番に−20,−0,
0,−15,0,0,0%になる。このSV補正値の合
計値35%を前回のごみ供給速度目標値(SV値)に対
して増減させる。そして、そのSV値が、PV値に対し
て±10%を超えると、ごみ供給量を増減させるように
する。〔表7〕ではSV値はPV値の70%から前記合
計値の35%を差し引いた35%となり、この値は「S
L=PV−10%」より低いことから、この場合、MV
=増減の出力は「減」になり、即ち、ごみ供給量を減ら
す方向で制御することになる。
The results are shown in Table 7 below.
Becomes a correction value for the dust feed speed target value (SV value), S V correction value of each item from the gas cooling chamber exhaust O 2 concentration to refuse loading volumes, "Gasuhiya 0 2 concentration" PV = 2.
Since it is 3% (less than 3.0% in Table 1), -2 of the set value E is used.
0%, since the “furnace outlet exhaust gas temperature” is 930 ° C.
%, "Reactor fresh water spray amount" is 0 in this case without correction output
%, And “gas cold injection water amount” is PV = 7976 (75 in Table 2).
00 excess), -15% of the set value F, and
In this case, "amount", "target incineration rate" and "waste input"
The deviation is also 0% without correction output, and in the order of -20, -0,
0, -15, 0, 0, 0%. The total value 35% of the SV correction value is increased or decreased from the previous waste supply speed target value (SV value). Then, when the SV value exceeds ± 10% with respect to the PV value, the amount of waste supplied is increased or decreased. In Table 7, the SV value is 70% of the PV value,
This is 35%, which is obtained by subtracting 35% of the total value.
L = PV−10% ”. In this case, MV
= The output of increase / decrease is “decrease”, that is, the amount of waste supplied is reduced.
Control in the following direction.

【0028】[0028]

【表7】 [Table 7]

【0029】このようにすることにより、従来方式で
は、ごみ発熱量等の演算結果から1回の計算ループが終
了する毎に直ちに短時間の間隔で一次空気等の各設定値
を修正していたが、この場合、その変更そのものが外乱
因子となることがあったのに対して、本実施例では、こ
の修正作業を一定の間隔時間例えば20分間毎に行うこ
とにより、乱調がなく、安定した運転状況が得られる。
この自動燃焼制御運転を行った場合の炉出口温度、炉出
口02 濃度(ごみ投入量4.71TON/H,焼却率1
00%)の実測値が図2に示される。この図より明らか
なように、温度、濃度の変化は非常に少なくて、熱収支
バランスが最適、かつ安定的にとられていることが判
る。これに対して、従来の手動操作による同条件下の運
転状態は図3に示されるとおりであって、温度、濃度共
に変動が大きいことを表している。
By doing so, in the conventional method, each set value of the primary air and the like is corrected at short intervals immediately after one calculation loop is completed from the calculation result of the heat generation amount of the refuse. However, in this case, the change itself may become a disturbance factor, but in the present embodiment, this correction work is performed at a fixed interval time, for example, every 20 minutes, so that there is no disturbance and stable. The driving situation is obtained.
Furnace outlet temperature in the case of performing the automatic combustion control operation, the furnace outlet 0 2 concentration (waste input amount 4.71TON / H, incineration of 1
(00%) is shown in FIG. As is apparent from this figure, the changes in temperature and concentration are very small, and it is understood that the heat balance is optimally and stably achieved. On the other hand, the operation state under the same conditions by the conventional manual operation is as shown in FIG. 3, which indicates that both the temperature and the concentration have large fluctuations.

【0030】[0030]

【発明の効果】以上述べたとおり、本発明によれば、ご
み発熱量の変動を素早く確認して、必要一次空気量を供
給する制御が成されることにより、最適空気量で燃焼が
続けられ、常に、排ガス02 濃度を一定に確保できるの
で、公害防止が図れるとともに、経済的に最適な燃焼制
御が可能となる。また、制御プロセスの各種変動を常時
計器監視し、必要なごみ供給量の補正を自動化した結
果、より変動幅が少ない安定した運転ができ、焼却炉を
公害が発生しないようにして最大限有効に利用でき、し
かも運転員の手動操作頻度を著しく減少することも可能
である。
As described above, according to the present invention, the control of supplying the required primary air amount is performed by quickly confirming the change in the heat generation amount of the waste, so that the combustion is continued at the optimum air amount. always so it can ensure a flue gas 0 2 concentration constant, with pollution prevention can be achieved, it is possible to economically optimal combustion control. In addition, monitoring of various fluctuations in the control process with a constant timepiece and automating the correction of the required amount of waste, as a result, stable operation with less fluctuation can be achieved, and incinerators are used without pollution to maximize efficiency. It is also possible to significantly reduce the frequency of manual operations by the operator.

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

【図1】本発明方法の実施例に係る流動床焼却炉の制御
系統図である。
FIG. 1 is a control system diagram of a fluidized bed incinerator according to an embodiment of the method of the present invention.

【図2】流動床焼却炉における本発明方法の実施に係る
自動運転時の炉出口排ガス02濃度,炉出口温度の経時
線図である。
[2] the furnace exit exhaust gas 0 2 concentration during automatic operation according to an embodiment of the present invention a method in a fluidized bed incinerator, a time diagram of the furnace outlet temperature.

【図3】図2に対応する従来の手動運転時の炉出口排ガ
ス02 濃度,炉出口温度の経時線図である。
[3] the furnace exit exhaust gas 0 2 concentration at the time of a conventional manual operation corresponding to FIG. 2 is a time diagram of the furnace outlet temperature.

【符号の説明】[Explanation of symbols]

1…流動床焼却炉、 2…給気部、 3…砂層部、 4…フリーボード部、 12…二次空気量制御手段、 17…給じん量制御手段、 18…焼却量制御手段、 20…炉出口ガス温度制御手段、 30…炉内圧制御手段、 31…集じん器入口ガス温度制御手段、 35…砂層温度制御手段、 38…制御装置。 DESCRIPTION OF SYMBOLS 1 ... Fluid bed incinerator, 2 ... Air supply part, 3 ... Sand layer part, 4 ... Free board part, 12 ... Secondary air amount control means, 17 ... Dust amount control means, 18 ... Incineration amount control means, 20 ... Furnace outlet gas temperature control means, 30: furnace internal pressure control means, 31: dust collector inlet gas temperature control means, 35: sand layer temperature control means, 38: control device.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 F23G 5/50 ZAB F23G 5/50 ZABR ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 6 Identification code Agency reference number FI Technical display location F23G 5/50 ZAB F23G 5/50 ZABR

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 流動床焼却炉でごみを連続焼却するに際
し、炉出口ガス温度制御、砂層温度制御、炉内圧力制
御、ごみ供給量制御、反応塔入口排ガス温度制御、二次
空気の排ガスO2 濃度による自動制御を含む燃焼空気量
制御を、それぞれ単系統毎に自動制御する一方、ごみ発
熱量と燃焼用一次空気量との間に1次関数関係が成立す
ることから、ごみ発熱量の演算結果に基づき所要一次空
気量を算出して、所定時間経過する毎に一次空気量の目
標値を設定変更し、さらに、ガス冷却室排ガスO2
度、炉出口ガス温度、ガス冷却室噴射水量、炉内清水噴
霧水量、ごみ発熱量、目標焼却率の各データから各々補
正係数を演算により設定し、この補正係数に基づいてご
み供給量を増減させる補正制御をx秒/y分の時限で行
わせることを特徴とする焼却炉の自動燃焼制御方法。
1. In continuous incineration of refuse in a fluidized bed incinerator, furnace outlet gas temperature control, sand layer temperature control, furnace pressure control, refuse supply control, reaction tower inlet exhaust gas temperature control, secondary air exhaust gas O (2) While the combustion air amount control including the automatic control based on the concentration is automatically controlled for each single system, a linear function relationship is established between the waste heat value and the primary air amount for combustion. calculates a required primary air quantity based on the calculation result, changes the setting of the target value of the primary air amount for each of predetermined time, furthermore, the gas cooling chamber exhaust O 2 concentration, the furnace exit gas temperature, the gas cooling chamber injection water , A correction coefficient is set by calculation from each data of the furnace clean water spray water amount, the waste heat generation amount, and the target incineration rate, and the correction control for increasing / decreasing the waste supply amount based on the correction coefficient is performed in a time limit of x seconds / y minutes. Characterized by Automatic combustion control method of 却炉.
JP26622392A 1992-10-05 1992-10-05 Automatic combustion control method for incinerator Expired - Lifetime JP2656879B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP26622392A JP2656879B2 (en) 1992-10-05 1992-10-05 Automatic combustion control method for incinerator

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP26622392A JP2656879B2 (en) 1992-10-05 1992-10-05 Automatic combustion control method for incinerator

Publications (2)

Publication Number Publication Date
JPH06117618A JPH06117618A (en) 1994-04-28
JP2656879B2 true JP2656879B2 (en) 1997-09-24

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3619940B2 (en) * 1994-12-05 2005-02-16 バブコック日立株式会社 Fluidized bed incinerator and its combustion method
US6499412B2 (en) * 2000-09-15 2002-12-31 Rohm And Haas Company Method of firebox temperature control for achieving carbon monoxide emission compliance in industrial furnaces with minimal energy consumption
KR100434650B1 (en) * 2000-12-22 2004-06-07 현대중공업 주식회사 Automatic Combustion Control System for Stoker Type Refuse Incinerator
JP6232539B2 (en) * 2016-03-30 2017-11-22 和雄 宮谷 Solid fuel combustion apparatus, solid fuel combustion method, gas heating apparatus, liquid heating apparatus, power generation system, and cooling system
CN111271714B (en) * 2020-03-24 2025-04-18 中国恩菲工程技术有限公司 Method, device, equipment and readable storage medium for controlling flue gas oxygen concentration
JP6951789B2 (en) * 2020-03-27 2021-10-20 株式会社プランテック Waste treatment amount adjustment method for vertical waste incinerators and vertical waste incinerators

Also Published As

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