JPH06331123A - Control of amount of combustion air for incinerator for waste - Google Patents
Control of amount of combustion air for incinerator for wasteInfo
- Publication number
- JPH06331123A JPH06331123A JP14122993A JP14122993A JPH06331123A JP H06331123 A JPH06331123 A JP H06331123A JP 14122993 A JP14122993 A JP 14122993A JP 14122993 A JP14122993 A JP 14122993A JP H06331123 A JPH06331123 A JP H06331123A
- Authority
- JP
- Japan
- Prior art keywords
- amount
- air
- combustion
- oxygen
- exhaust gas
- 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.)
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- Incineration Of Waste (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は、ごみ焼却場において安
定にごみを燃焼させるための燃焼用空気量の制御方法に
関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for controlling a combustion air amount for stably burning refuse in a refuse incinerator.
【0002】[0002]
【従来の技術】ごみ焼却炉の操業において燃焼用空気量
の制御は重要な操業要素である。燃焼用空気量を燃焼状
態に基づいて適正に制御するのはむずかしいため、実際
にはごみ発熱量により設定される燃焼用空気量をボイラ
ー付きの焼却炉の場合はボイラーの蒸発量、水噴霧式の
焼却炉の場合は噴霧水量により間接的に表わされる排ガ
スの熱量により補正し、制御されている。2. Description of the Related Art In the operation of a refuse incinerator, controlling the amount of combustion air is an important operating factor. Since it is difficult to properly control the amount of combustion air based on the combustion state, the amount of combustion air that is actually set by the amount of heat generated by waste is the amount of evaporation of the boiler or water spray type in the case of an incinerator with a boiler. In the case of the incinerator, it is corrected and controlled by the heat quantity of the exhaust gas, which is indirectly represented by the spray water quantity.
【0003】[0003]
【発明が解決しようとする課題】安定した燃焼制御を行
おうとする場合に燃焼用空気量を排ガスの熱量に基づい
て制御すると、焼却炉内のごみの燃焼状況、ごみの過不
足、2次空気による炉出口温度の変化の影響を受け、必
ずしも燃焼に必要とする空気量を設定することができな
いため、安定した燃焼が行われないという欠点があっ
た。本発明は従来の欠点を補い、適正な燃焼用空気量を
供給することにより、安定したごみの供給、すなわち規
定処理量を満足し、未燃分の発生を極力抑え、安定した
燃焼を維持することを目的とするものである。When the amount of combustion air is controlled based on the amount of heat of exhaust gas in order to perform stable combustion control, the combustion situation of dust in the incinerator, excess and deficiency of dust, and secondary air There is a drawback that stable combustion cannot be performed because the amount of air required for combustion cannot be set due to the influence of changes in the furnace outlet temperature due to. The present invention compensates for the conventional defects and supplies a proper amount of air for combustion, thereby supplying a stable amount of dust, that is, satisfying a prescribed processing amount, suppressing the generation of unburned components as much as possible, and maintaining stable combustion. That is the purpose.
【0004】[0004]
【課題を解決するための手段】本発明のごみ焼却炉の燃
焼用空気量制御方法は、上記の目的を達成するために、
供給した燃焼用空気によりごみを燃焼せしめ、発生した
排ガスに2次空気と水を供給して減温せしめ、煙道より
排出せしめるごみ焼却炉における燃焼用空気供給用風道
には空気流量計、温度計を設置し、得られた測定値より
一定時間に供給した燃焼用空気(一定温度に換算)中の
酸素量を求め、2次空気供給用風道には空気流量計、温
度計を設置し、得られた測定値より一定時間に供給した
2次空気(一定温度に換算)中の酸素量を求め、煙道に
は排ガス流量計、温度計、酸素濃度計、水分濃度計を設
置し、得られた測定値より一定時間に排出した排ガス
(一定温度、無水分に換算)中の酸素量を求め、前記燃
焼用空気中の酸素量と2次空気中の酸素量の和から排ガ
ス中の酸素量を減算して燃焼により消費した酸素量を求
め、前記燃焼用空気中の酸素量を燃焼により消費した酸
素量で除算して一次空気過剰率を演算し、これとごみの
発熱量から設定した標準空気過剰率とを比較し、その偏
差がなくなるように燃焼用空気量を制御することを特徴
とするものである。In order to achieve the above object, the method for controlling the amount of air for combustion in a refuse incinerator according to the present invention comprises:
The waste air is burnt by the supplied combustion air, the secondary air and water are supplied to the generated exhaust gas to reduce the temperature, and the exhaust air is discharged from the flue. A thermometer is installed, the amount of oxygen in the combustion air (converted to a constant temperature) supplied for a certain period of time is calculated from the measured values, and an air flow meter and thermometer are installed in the secondary air supply air duct. Then, determine the amount of oxygen in the secondary air (converted to a constant temperature) that was supplied for a fixed time from the measured values, and install an exhaust gas flow meter, thermometer, oxygen concentration meter, and moisture concentration meter in the flue. The amount of oxygen in the exhaust gas (constant temperature, converted to anhydrous content) discharged in a certain time is calculated from the obtained measured value, and the amount of oxygen in the combustion air and the amount of oxygen in the secondary air The oxygen amount consumed by combustion is calculated by subtracting the oxygen amount of The primary air excess ratio is calculated by dividing the amount of oxygen in the product by the amount of oxygen consumed by combustion, and this is compared with the standard excess air ratio set from the heat value of the waste, and the combustion air amount is used to eliminate the deviation. It is characterized by controlling.
【0005】[0005]
【作用】供給した燃焼用空気によりごみを燃焼せしめ、
発生した排ガスに2次空気と水を供給して減温せしめ、
煙道より排出せしめるごみ焼却炉において、一定時間に
供給する燃焼用空気(一定温度に換算)中の酸素量と一
定時間に供給する2次空気(一定温度に換算)中の酸素
量と一定時間に排出する排ガス(一定温度、一定水分に
換算)中の酸素量とを求める。[Operation] Burns refuse with the supplied combustion air,
Supply secondary air and water to the generated exhaust gas to reduce the temperature,
In a refuse incinerator that can be discharged from a flue, the amount of oxygen in combustion air (converted to a constant temperature) and the amount of oxygen in secondary air (converted to a constant temperature) that is supplied for a fixed time and a fixed time And the amount of oxygen in the exhaust gas (converted to constant temperature and constant moisture) discharged to.
【0006】前記燃焼用空気中の酸素量と2次空気中の
酸素量の和から排ガス中の酸素量を減算して燃焼により
消費した酸素量を求め、前記燃焼用空気中の酸素量を燃
焼により消費した酸素量で除算して一次空気過剰率を演
算し、これとごみの発熱量から設定した標準空気過剰率
とを比較し、その偏差がなくなるように燃焼用空気量を
制御するので、絶えず変化するごみの性状、燃焼状態の
複雑な関係に対応して燃焼用空気を供給できるため、安
定した燃焼状態を連続して維持できる。The amount of oxygen consumed in combustion is obtained by subtracting the amount of oxygen in exhaust gas from the sum of the amount of oxygen in the combustion air and the amount of oxygen in the secondary air, and the amount of oxygen in the combustion air is burned. Calculate the primary air excess rate by dividing by the amount of oxygen consumed by, and compare this with the standard air excess rate set from the heat generation amount of the waste, and control the combustion air amount so that the deviation disappears, Combustion air can be supplied in response to the ever-changing property of waste and the complicated relationship of combustion state, so that a stable combustion state can be continuously maintained.
【0007】[0007]
【実施例】以下、図面を参照してこの発明の一実施例に
ついて説明する。ごみ焼却炉の概略説明図である図1に
おいて、ごみ投入口1よりクレーン2にて投入されたご
み3は、燃焼室入口4を経て燃焼室5に入る。空気予熱
器6で予熱された燃焼用空気7は押込送風機8により炉
の下から供給される。燃焼室内5で、ごみは燃焼用空気
7により燃焼し灰となり、炉の出口9より灰搬出装置1
0に送り出される。燃焼によって発生した高温の排ガス
は、供給された2次空気11により混合攪拌されるとと
もに、炉出口排ガス温度計12で測定され、規定の炉出
口温度の範囲に制御され、ガス冷却装置13に送られ
る。ガス冷却装置13には冷却水噴霧ポンプ14より送
られる冷却水が噴霧ノズルより噴霧され、排ガスはさら
に減温されて空気予熱器6へ送られ、燃焼用空気7と熱
交換され、排ガス流量計15、空気予熱器出口温度計1
6を経て集じん器17を通り、誘引送風機18にて煙突
19に送られ、外部に排出される。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the present invention will be described below with reference to the drawings. In FIG. 1, which is a schematic explanatory view of a refuse incinerator, refuse 3 introduced by a crane 2 from a garbage inlet 1 enters a combustion chamber 5 through a combustion chamber inlet 4. The combustion air 7 preheated by the air preheater 6 is supplied from below the furnace by a forced air blower 8. In the combustion chamber 5, the dust is burned by the combustion air 7 to form ash, and the ash discharge device 1 from the outlet 9 of the furnace.
Sent to 0. The high-temperature exhaust gas generated by combustion is mixed and stirred by the supplied secondary air 11, measured by the furnace outlet exhaust gas thermometer 12, controlled to a specified furnace outlet temperature range, and sent to the gas cooling device 13. To be The cooling water sent from the cooling water spray pump 14 is sprayed to the gas cooling device 13 from the spray nozzle, and the exhaust gas is further reduced in temperature and sent to the air preheater 6, where it is heat-exchanged with the combustion air 7, and the exhaust gas flow meter is measured. 15, air preheater outlet thermometer 1
After passing 6 through the dust collector 17, it is sent to the chimney 19 by the induction blower 18 and discharged to the outside.
【0008】ここで、ごみ焼却炉において供給される酸
素ガス量と排出される酸素ガス量とより消費される酸素
ガス量を求め、1次空気過剰率を制御することにより、
合理的な焼却炉の自動制御を可能とする方法につき述べ
る。先ず、燃焼室5に供給される燃焼用空気量 v1 ( Nm
3 /h) は、燃焼用空気流量計(送風機出口:風道)23
にて測定されるが、この燃焼用空気温度は 燃焼用空気
温度計26にて測定されるように t1 ℃) であるため、
0℃、1気圧における燃焼用空気量 v2 ( Nm3/h )を式
(1) にしたがって演算する。 v2 = v1 ×273 / (273 + t1 ) (1)Here, the amount of oxygen gas consumed is calculated from the amount of oxygen gas supplied and the amount of oxygen gas discharged in the refuse incinerator to control the primary air excess ratio,
A method that enables rational automatic control of an incinerator will be described. First, the amount of combustion air supplied to the combustion chamber 5 v 1 (Nm
3 / h) is a combustion air flow meter (blower outlet: wind passage) 23
However, since this combustion air temperature is t 1 ℃ as measured by the combustion air thermometer 26,
Formula for the combustion air amount v 2 (Nm 3 / h) at 0 ° C and 1 atmosphere
Calculate according to (1). v 2 = v 1 × 273 / (273 + t 1 ) (1)
【0009】0℃、1気圧における燃焼用空気量 v2 (
Nm3 /h )に大気中の酸素濃度(21%)を乗じ、0℃、
1気圧における燃焼用空気中の酸素量 v3 ( Nm3 /h )を
式(2) にしたがって演算する。 v3 = v2 ×0.21 (2)The amount of combustion air v 2 (
Nm 3 / h) multiplied by atmospheric oxygen concentration (21%),
The oxygen amount v 3 (Nm 3 / h) in the combustion air at 1 atm is calculated according to equation (2). v 3 = v 2 × 0.21 (2)
【0010】次に、2次空気流量 v4 ( Nm3 /h )は風道
(送風機出口)に設けた2次空気流量計22により測定
されるが、この2次空気温度は2次用空気温度計24に
て測定されるように t2 ( ℃) であるため、0℃、1気
圧における2次空気量 v5 (Nm3 /h )を式(3) にしたが
って演算する。 v5 = v4 ×273 / (273 + t2 ) (3)Next, the secondary air flow rate v 4 (Nm 3 / h) is measured by a secondary air flow meter 22 provided at the air passage (blower outlet). The secondary air temperature is the secondary air. Since it is t 2 (° C.) as measured by the thermometer 24, the secondary air amount v 5 (Nm 3 / h) at 0 ° C. and 1 atmospheric pressure is calculated according to the equation (3). v 5 = v 4 × 273 / (273 + t 2 ) (3)
【0011】0℃、1気圧における2次空気量 v5 ( Nm
3 /h )に大気中の酸素濃度(21%)を乗じ、0℃、1
気圧における2次空気中の酸素量 v6 ( Nm3 /h )を式
(4) にしたがって演算する。 v6 = v5 × 0.21 (4)Secondary air quantity v 5 (Nm
3 / h) multiplied by atmospheric oxygen concentration (21%), 0 ℃, 1
The amount of oxygen in secondary air at atmospheric pressure v 6 (Nm 3 / h)
Calculate according to (4). v 6 = v 5 × 0.21 (4)
【0012】次に、燃焼により一定時間に発生する排ガ
スの量 v7 ( Nm3 /h) は、排ガス流量計15(集じん器
17の後方に設置することが多い)で測定されるが、こ
の排ガスには、ごみの燃焼により発生した水蒸気を含む
ほか、ガス冷却装置13で供給された噴霧水により発生
した水蒸気により増量しているため、排ガス水分濃度計
20の測定値 w( %) に基づき排ガス中の水分量を除い
た乾き排ガス量 v8 (Nm3 /h )を式(5) にしたがって演
算する。 v8 = v7 ×(100 ー w) ÷100 (5)Next, the amount v 7 (Nm 3 / h) of the exhaust gas generated in a certain time by the combustion is measured by the exhaust gas flow meter 15 (often installed behind the dust collector 17). This exhaust gas contains water vapor generated by the combustion of dust and is increased by the water vapor generated by the spray water supplied by the gas cooling device 13. Therefore, the measured value w (%) of the exhaust gas moisture concentration meter 20 becomes Based on this, the dry exhaust gas amount v 8 (Nm 3 / h) excluding the water amount in the exhaust gas is calculated according to equation (5). v 8 = v 7 × (100-w) ÷ 100 (5)
【0013】空気予熱器出口の排ガス温度計16により
測定した温度 t3 (℃) に基づき、0℃、1気圧におけ
る乾き排ガス量 v9 ( Nm3 /h )を式(6) にしたがって演
算する。 v9 = v8 × 273/ (273 + t2 ) (6)Based on the temperature t 3 (° C.) measured by the exhaust gas thermometer 16 at the outlet of the air preheater, the dry exhaust gas amount v 9 (Nm 3 / h) at 0 ° C. and 1 atm is calculated according to the equation (6). . v 9 = v 8 × 273 / (273 + t 2 ) (6)
【0014】排ガス酸素濃度計21によって測定される
酸素濃度s (%) により乾き排ガス中の酸素量 v10( Nm
3 /h )を式(7) にしたがって演算する。 v10= v9 ×s÷100 (7)Based on the oxygen concentration s (%) measured by the exhaust gas oxygen concentration meter 21, the amount of oxygen in the dry exhaust gas v 10 (Nm
3 / h) is calculated according to equation (7). v 10 = v 9 × s ÷ 100 (7)
【0015】したがって、0℃、1気圧における燃焼用
空気中の酸素量 v3 ( Nm3 /h )と0℃、1気圧における
2次空気中の酸素量 v6 ( Nm3 /h )の和から0℃、1気
圧における乾き排ガス中の酸素量 v10( Nm3 /h )を減算
して、燃焼により消費された酸素量 v11 (Nm3 /h )を求
める。 v11= v3 + v6 − v10 (8)Therefore, the sum of the oxygen content v 3 (Nm 3 / h) in the combustion air at 0 ° C. and 1 atmosphere and the oxygen content v 6 (Nm 3 / h) in the secondary air at 0 ° C. and 1 atmosphere. The oxygen amount v 10 (Nm 3 / h) in the dry exhaust gas at 0 ° C. and 1 atmosphere is subtracted from the above to obtain the oxygen amount v 11 (Nm 3 / h) consumed by the combustion. v 11 = v 3 + v 6 − v 10 (8)
【0016】上記のようにして得られた0℃、1気圧に
おける燃焼用に供給された酸素量 v3 ( Nm3 /h )を0
℃、1気圧における消費された酸素量 v11 (Nm3 /h )で
除算し、空気過剰率 K1 を算出する。 K1 =v3 ÷ v11 (9)The oxygen amount v 3 (Nm 3 / h) supplied for combustion at 0 ° C. and 1 atm obtained as described above is 0.
The excess air ratio K 1 is calculated by dividing by the amount of oxygen consumed v 11 (Nm 3 / h) at 1 ° C and 1 ° C. K 1 = v 3 ÷ v 11 (9)
【0017】この演算された空気過剰率 K1 をごみの発
熱量より設定される標準空気過剰率K2 と比べ、その偏
差を求めた。なお、標準空気過剰率 K2 は、式(10)より
求めた。 K2 =a ×Hu+b (10) ただし、Huはごみの発熱量、a,b は定数である。The calculated excess air ratio K 1 was compared with the standard excess air ratio K 2 which was set from the heat value of the waste, and the deviation was calculated. The standard excess air ratio K 2 was calculated from the equation (10). K 2 = a × Hu + b (10) where Hu is the heat value of the waste and a and b are constants.
【0018】空気過剰率 K1 と標準空気過剰率 K2 との
偏差がなくなるよう燃焼用空気量を補正し、制御したと
ころ、絶えず変化するごみの性状、燃焼状態の複雑な関
係に対応して所望の燃焼用空気を供給することができる
こととなり、安定した燃焼状態を連続して維持すること
ができた。When the amount of combustion air was corrected and controlled so that the deviation between the excess air ratio K 1 and the standard excess air ratio K 2 was eliminated, it was confirmed that the property of dust and the complicated relationship of combustion conditions would change constantly. It became possible to supply desired combustion air, and it was possible to continuously maintain a stable combustion state.
【0019】[0019]
【発明の効果】本発明は、以上説明したように、燃焼に
より消費される酸素量と燃焼用空気に含まれる酸素量に
より求められる空気過剰率を連続して算出し、燃焼中の
ごみの発熱量により設定した標準空気過剰率との偏差を
求め、これを補正するように燃焼用空気を制御するた
め、燃焼中のごみの必要とする適正な燃焼用空気を供給
するので、効率的な燃焼を行うことができ、その結果適
正な処理量を処理し、未燃の発生を防ぐことができ、合
理的な焼却炉の自動制御を可能とする。As described above, the present invention continuously calculates the excess air ratio determined by the amount of oxygen consumed by combustion and the amount of oxygen contained in combustion air to generate the heat of dust during combustion. The deviation from the standard excess air ratio set by the amount is calculated, and the combustion air is controlled so as to correct it, so the proper combustion air required for the dust during combustion is supplied, so efficient combustion is achieved. As a result, it is possible to process an appropriate amount of treatment, prevent the generation of unburned substances, and enable rational automatic control of the incinerator.
【図1】本発明の実施例を示す焼却炉の概略説明図であ
る。FIG. 1 is a schematic explanatory diagram of an incinerator showing an embodiment of the present invention.
1 ごみ投入口 2 クレーン 3 ごみ 4 燃焼室入口 5 燃焼室 6 空気予熱器 7 燃焼用空気 8 押込送風機 9 炉の出口 10 灰搬出装置 11 2次空気 12 炉出口排ガス温度
計 13 ガス冷却装置 14 冷却水噴霧ポンプ 15 排ガス流量計 16 排ガス温度計 17 集じん器 18 誘引送風機 19 煙突 20 排ガス水分濃度計 21 排ガス酸素濃度計 22 2次空気流量計 23 燃焼用空気流量計 24 2次空気温度計 26 燃焼用空気温度計1 Waste Inlet 2 Crane 3 Waste 4 Combustion Chamber Inlet 5 Combustion Chamber 6 Air Preheater 7 Combustion Air 8 Forced Blower 9 Reactor Outlet 10 Ash Removal Device 11 Secondary Air 12 Furnace Outlet Exhaust Thermometer 13 Gas Cooling Device 14 Cooling Water spray pump 15 Exhaust gas flow meter 16 Exhaust gas thermometer 17 Dust collector 18 Induction blower 19 Chimney 20 Exhaust gas moisture concentration meter 21 Exhaust gas oxygen concentration meter 22 Secondary air flow meter 23 Combustion air flow meter 24 Secondary air thermometer 26 Combustion For air thermometer
Claims (1)
しめ、発生した排ガスに2次空気と水を供給して減温せ
しめ、煙道より排出せしめるごみ焼却炉における燃焼用
空気供給用風道には空気流量計、温度計を設置し、得ら
れた測定値より一定時間に供給した燃焼用空気(一定温
度に換算)中の酸素量を求め、2次空気供給用風道には
空気流量計、温度計を設置し、得られた測定値より一定
時間に供給した2次空気(一定温度に換算)中の酸素量
を求め、煙道には排ガス流量計、温度計、酸素濃度計、
水分濃度計を設置し、得られた測定値より一定時間に排
出した排ガス(一定温度、無水分に換算)中の酸素量を
求め、前記燃焼用空気中の酸素量と2次空気中の酸素量
の和から排ガス中の酸素量を減算して燃焼により消費し
た酸素量を求め、前記燃焼用空気中の酸素量を燃焼によ
り消費した酸素量で除算して一次空気過剰率を演算し、
これとごみの発熱量から設定した標準空気過剰率とを比
較し、その偏差がなくなるように燃焼用空気量を制御す
ることを特徴とするごみ焼却炉の燃焼用空気量制御方
法。1. A ventilation air duct for combustion air in a refuse incinerator, in which waste air is burned by the supplied combustion air, secondary air and water are supplied to the generated exhaust gas to reduce the temperature, and the exhaust gas is discharged from a flue. Is equipped with an air flow meter and a thermometer, and the amount of oxygen in the combustion air (converted to a constant temperature) supplied for a certain period of time is found from the measured values, and an air flow meter is installed in the secondary air supply air duct , A thermometer was installed, and the amount of oxygen in the secondary air (converted to a constant temperature) that was supplied for a certain period of time was obtained from the measured values, and an exhaust gas flow meter, thermometer, oxygen concentration meter,
A moisture concentration meter is installed, and the amount of oxygen in the exhaust gas (constant temperature, converted to anhydrous content) discharged for a certain period of time is obtained from the obtained measured value, and the amount of oxygen in the combustion air and the oxygen in the secondary air are obtained. Obtain the amount of oxygen consumed by combustion by subtracting the amount of oxygen in the exhaust gas from the sum of the amount, to calculate the primary air excess rate by dividing the amount of oxygen in the combustion air by the amount of oxygen consumed by combustion,
A method for controlling the amount of combustion air in a refuse incinerator, which comprises comparing this with a standard excess air ratio set from the heat value of the waste and controlling the amount of combustion air so as to eliminate the deviation.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP14122993A JPH06331123A (en) | 1993-05-21 | 1993-05-21 | Control of amount of combustion air for incinerator for waste |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
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JP14122993A JPH06331123A (en) | 1993-05-21 | 1993-05-21 | Control of amount of combustion air for incinerator for waste |
Publications (1)
Publication Number | Publication Date |
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JPH06331123A true JPH06331123A (en) | 1994-11-29 |
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Application Number | Title | Priority Date | Filing Date |
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JP14122993A Pending JPH06331123A (en) | 1993-05-21 | 1993-05-21 | Control of amount of combustion air for incinerator for waste |
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JP (1) | JPH06331123A (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO1999018394A1 (en) | 1997-10-02 | 1999-04-15 | Nkk Corporation | Combustion control method for refuse incinerator |
JP5996762B1 (en) * | 2015-11-19 | 2016-09-21 | 株式会社タクマ | Waste combustion control method and combustion control apparatus to which the method is applied |
-
1993
- 1993-05-21 JP JP14122993A patent/JPH06331123A/en active Pending
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO1999018394A1 (en) | 1997-10-02 | 1999-04-15 | Nkk Corporation | Combustion control method for refuse incinerator |
EP1267122A1 (en) | 1997-10-02 | 2002-12-18 | Nkk Corporation | Combustion control method in refuse incineration furnace |
JP5996762B1 (en) * | 2015-11-19 | 2016-09-21 | 株式会社タクマ | Waste combustion control method and combustion control apparatus to which the method is applied |
WO2017085941A1 (en) * | 2015-11-19 | 2017-05-26 | 株式会社タクマ | Waste incineration control method, and incineration control apparatus using same |
JP2017096517A (en) * | 2015-11-19 | 2017-06-01 | 株式会社タクマ | Waste material combustion method and combustion control device applying the same |
EP3379147A4 (en) * | 2015-11-19 | 2018-12-05 | Takuma Co., Ltd. | Waste incineration control method, and incineration control apparatus using same |
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