JP3746751B2 - Control method and control apparatus for sludge combustion furnace - Google Patents
Control method and control apparatus for sludge combustion furnace Download PDFInfo
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- JP3746751B2 JP3746751B2 JP2002292900A JP2002292900A JP3746751B2 JP 3746751 B2 JP3746751 B2 JP 3746751B2 JP 2002292900 A JP2002292900 A JP 2002292900A JP 2002292900 A JP2002292900 A JP 2002292900A JP 3746751 B2 JP3746751 B2 JP 3746751B2
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- 238000002485 combustion reaction Methods 0.000 title claims description 133
- 239000010802 sludge Substances 0.000 title claims description 71
- 238000000034 method Methods 0.000 title claims description 34
- 239000000446 fuel Substances 0.000 claims description 34
- 239000000567 combustion gas Substances 0.000 claims description 28
- 239000007789 gas Substances 0.000 claims description 25
- 239000004576 sand Substances 0.000 claims description 21
- 238000001514 detection method Methods 0.000 claims description 18
- 229910052760 oxygen Inorganic materials 0.000 claims description 16
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 15
- 239000001301 oxygen Substances 0.000 claims description 15
- 239000002245 particle Substances 0.000 claims description 15
- 230000007274 generation of a signal involved in cell-cell signaling Effects 0.000 claims description 5
- 238000002835 absorbance Methods 0.000 claims description 4
- 230000001678 irradiating effect Effects 0.000 claims 1
- 238000010586 diagram Methods 0.000 description 10
- 239000010801 sewage sludge Substances 0.000 description 7
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- GQPLMRYTRLFLPF-UHFFFAOYSA-N Nitrous Oxide Chemical compound [O-][N+]#N GQPLMRYTRLFLPF-UHFFFAOYSA-N 0.000 description 2
- 230000001276 controlling effect Effects 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 229910052757 nitrogen Inorganic materials 0.000 description 2
- 238000010792 warming Methods 0.000 description 2
- 238000010521 absorption reaction Methods 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 230000018044 dehydration Effects 0.000 description 1
- 238000006297 dehydration reaction Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 239000001272 nitrous oxide Substances 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
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Classifications
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/40—Valorisation of by-products of wastewater, sewage or sludge processing
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- Investigating Or Analysing Materials By Optical Means (AREA)
- Incineration Of Waste (AREA)
- Fluidized-Bed Combustion And Resonant Combustion (AREA)
- Treatment Of Sludge (AREA)
Description
【0001】
【発明の属する技術の分野】
本発明は、汚泥を燃焼する燃焼炉の制御方法及び制御装置に関する。更にくわしくは、汚泥を燃焼する燃焼炉の排ガス中のN2Oを低減する燃焼炉の制御方法及び制御装置に関する。
【0002】
【従来の技術】
地球温暖化ガスとして知られている一酸化二窒素(以下N2O)は、これまで排ガス規制対象となっていなかったなどの理由から、下水汚泥燃焼炉においては排出濃度計測及び排ガスN2O濃度による燃焼制御はおこなわれてこなかった。ところが、N2OはCO2の約300倍の温暖化効果を生むことが知られてきいる上に、下水汚泥は窒素成分に富んでいることからその燃焼排ガスには数百ppmもの高いN2Oを含むので、下水汚泥燃焼炉から排出するN2Oを極力少なくすることが望まれている。
【0003】
従って、下水汚泥燃焼炉における排ガスN2O濃度を制御する技術は、従来、公に知られておらず、燃焼ガス中の制御物質をリアルタイムで検出する方法においても、例えばCO濃度の検出ではその例が見られるが(例えば特許文献1段落0039参照)、N2O濃度の検出については未だ公に知られていない。
【0004】
【特許文献1】
特開平11−14027号公報(例えば、段落0039参照)
【0005】
【発明が解決しようとする課題】
本発明はかかる従来の問題点に鑑みてなされたもので、下水汚泥燃焼炉の燃焼ガス中のN2Oを直接測定して、リアルタイムに燃焼条件に反映させて、その排出濃度を低減する燃焼炉の新しい制御方法及び制御装置の提供を目的とする。
【0006】
【課題を解決するための手段】
本発明の汚泥燃焼炉の制御方法は、汚泥とともに助燃料と燃焼用空気を供給して前記汚泥を燃焼する燃焼炉の制御方法において、燃焼ガス中のN2O濃度を検出して、該検出値に基づいて、燃焼空気量、二次空気量、燃焼空気温度及び助燃料流量から選ばれる少なくとも一つの操作量の補正値を算出し、該算出値に基づいて該操作量を調節して、燃焼炉の排ガス中のN2Oを低減することを特徴とする。
【0007】
更に本発明の汚泥燃焼炉の制御方法は、汚泥とともに助燃料と燃焼用空気を供給して前記汚泥を燃焼する燃焼炉であって、砂粒を熱媒体として汚泥とともに気泡流動層を形成して燃焼する燃焼炉の制御方法において、燃焼ガス中のN2O濃度と、排ガス中の酸素濃度と、砂粒層の温度と、フリーボードの温度とを検出して、該検出値に基づいて、燃焼空気量、二次空気量、燃焼空気温度及び助燃料流量から選ばれる少なくとも一つの操作量の補正値を算出し、該算出値に基づいて該操作量を調節して、燃焼炉の排ガス中のN2Oを低減することを特徴とする。
【0008】
更に本発明の汚泥燃焼炉の制御方法は、燃焼ガス中のN2O濃度が、燃焼ガス中に、近赤外波長域の特定波長のレーザ光を照射して、該レーザ光中のN2Oが吸収する特定波長の吸光度を測定して求められることを特徴とする。
【0009】
更に本発明の汚泥燃焼炉の制御方法は、前記補正値の算出が、検出した燃焼ガス中のN2O濃度と、排ガス中の酸素濃度と、砂粒層の温度と、フリーボードの温度とを前件部とし、燃焼空気量、二次空気量、燃焼空気温度及び助燃料流量を後件部としたファジィ推論による演算に基づくことを特徴とする。
【0010】
更に本発明の汚泥燃焼炉の制御方法は、前記各操作量の調節は、所定の投入汚泥量をファンクションジェネレータに入力して生成させた当該操作量設定値に、前記補正値を加算して得た補正操作量設定値と当該操作量工程値とのPID動作によって行うことを特徴とする。
【0011】
更に本発明の汚泥燃焼炉の制御装置は、汚泥とともに助燃料と燃焼用空気を供給して前記汚泥を燃焼する燃焼炉の制御装置において、燃焼ガス中のN2O濃度を検出するN2O濃度計と、燃焼空気量、二次空気量、燃焼空気温度及び助燃料流量から選ばれる少なくとも一つの操作量を検出する操作量検出手段、及び前記N2O濃度検出値に基づいて当該操作量の補正値を算出する 補正値算出手段と、当該算出補正値に基づいて補正操作量の動作信号を生成する動作信号生成手段を有する制御部を備え、当該操作量を調節可能にして燃焼炉の排ガス中のN2Oを低減することを特徴とする。
【0012】
更に本発明の汚泥燃焼炉の制御装置は、汚泥とともに助燃料と燃焼用空気を供給して前記汚泥を燃焼する燃焼炉であって、砂粒を熱媒体として汚泥とともに気泡流動層を形成して燃焼する燃焼炉の制御装置において、燃焼ガス中のN2O濃度を検出するN2O濃度計と、排ガス中の酸素濃度を検出する酸素濃度計と、砂粒層の温度を検出する温度計と、フリーボードの温度を検出する温度計と、燃焼空気量、二次空気量、燃焼空気温度及び助燃料流量から選ばれる少なくとも一つの操作量を検出する操作量検出手段、及び前記N2O濃度検出値と、酸素濃度検出値と、砂粒層の温度検出値と、フリーボードの温度検出値とに基づいて当該操作量の補正値を算出する 補正値算出手段と、当該算出補正値に基づいて補正操作量の動作信号を生成する動作信号生成手段を有する制御部を備え、当該操作量を調節可能にして燃焼炉の排ガス中のN2Oを低減することを特徴とする。
【0013】
更に本発明の汚泥燃焼炉の制御装置は、前記N2O濃度計が、近赤外波長域の特定波長のレーザ光を発振して燃焼ガス中に、照射可能なレーザ発光部と、該照射されて燃焼ガス中を透過したレーザ光を受光する受光部と、受光したレーザ光のN2Oが吸収する前後の強度を検出し、検出結果より吸光度を求め、N2O濃度の電気信号に変換するレーザ式濃度計とを備えてなることを特徴とする。
【0014】
更に本発明の汚泥燃焼炉の制御装置は、前記補正値算出手段が、検出した燃焼ガス中のN2O濃度と、排ガス中の酸素濃度と、砂粒層の温度と、フリーボードの温度とを前件部とし、燃焼空気量、二次空気量、燃焼空気温度及び助燃料流量を後件部としたファジィ推論による演算に基づく補正値算出手段であることを特徴とする。
【0015】
更に本発明の汚泥燃焼炉の制御装置は、動作信号生成手段が、 所定の投入汚泥量を入力して操作量設定値を生成するファンクションジェネレータと、当該操作量設定値と前記補正値を加算する加算器と、該加算器が生成した補正操作量設定値と当該操作量工程値とを入力して、調節操作量の動作信号を出力するPID回路を有してなることを特徴とする。
【0016】
【発明の実施の形態】
以下に本発明の実施の形態について図面を参照して詳しく説明する。但し本実施の形態に記載された製品の寸法、形状、材質、その相対配置等は特に特定的な記載がない限りは本発明の範囲をそれのみに限定する主旨ではなく単なる説明例に過ぎない。
【0017】
図1は本発明の汚泥燃焼炉を含む、汚泥燃焼炉の制御装置の概略構成図である。本図により、先ず汚泥燃焼のプロセスを説明する。下水汚泥は不図示の脱水プロセスによって脱水され、汚泥ケーキ14として供給機15により汚泥燃焼炉1に供給される。本実施態様では、汚泥燃焼炉1は砂粒を熱媒体として汚泥とともに気泡流動層を形成して燃焼する流動床式燃焼炉である。助燃料が助燃料調節弁10を介して、燃焼炉砂層域に、また燃焼空気が温度調節器12で調節されたヒータ13で加熱され、ポンプPの吐出圧により燃焼空気流量調節弁11を介して、燃焼炉底部から導入され、燃焼する。加熱された砂層の砂粒は、燃焼空気と発生する燃焼ガスによって、供給された汚泥ケーキ14とともに流動し、汚泥ケーキ14は流動しながら燃焼する。さらに、汚泥ケーキ燃焼ガスはフリーボード中を上昇しながら、二次空気調節弁9を介して供給される二次空気で燃焼を完結する。燃焼後の排ガスは炉上部から煙道16を通って、排ガス処理設備へ排出される。
【0018】
本実施態様では、制御装置として他に、砂層域の温度を検出する砂層温度計8、フリーボードの温度を検出するフリーボード温度計7、煙道16の排ガス酸素濃度を検出する酸素濃度計6を備えている。更にフリーボド上部に燃焼ガスが通過するとき、燃焼ガスのN2O濃度を検出するN2O濃度計17を備えている。N2O濃度計17はフリーボード上部の燃焼ガス通過部の一端から特定波長のレーザ光を照射するレーザ光発光部5と燃焼ガス通過部のN2Oに吸収されたレーザ光を受光しその強度を検出するレーザ受光部4と検出信号から濃度を算出し制御部へ該信号を出力するレーザ式濃度計3とから成っている。N2Oは1.517μmの波長を吸収して、照射光を減衰させ、レーザ受光部4に到達して検出される。更にこれら制御量や燃焼条件工程値などを受け入れて、燃焼に必要な空気量、助燃料量、空気温度などを調節するに必要な動作信号を出力する制御部2を備えている。
【0019】
次に本実施態様における、N2O濃度を低減する燃焼炉の制御方法について説明する。制御部にはファジィ推論による演算に基づく補正値算出手段が備えてあり、該補正値算出手段に表1に示す8水準のファジィ推論ルールにより、前記説明で検出した各検出値(N2O、O2、Ts、Tf)のファジィ集合のグレード値を前件部として入力し、燃焼空気、二次空気、助燃料の各量及び燃焼空気温度の補正値αをその後件部から出力する。
【0020】
【表1】
【0021】
更に制御部には動作信号生成手段を有しており、前記補正値αに基づいて調節操作量を生成して、各調節弁もしくは調節器の動作信号を出力する。そのロジック図を図2〜5にそれぞれ燃焼空気、二次空気、助燃料の各量及び燃焼空気温度について示す。
【0022】
図2により燃焼空気流量調節の例で説明すると、ファジィ演算補正値αは、汚泥ケーキ量設定値(SV、セットヴァリュ)をファンクションジェネレ−タ20に入力して燃焼空気流量設定値に変換した信号と加算器21で加算され、補正燃焼空気流量設定値を得る。補正燃焼空気流量設定値と燃焼空気流量工程値(PV、プロセスヴァリュ)はPID回路22に入力され、PID動作により燃焼空気流量調節弁の操作信号を出力し、燃焼空気流量調節弁11の開度を調節する。以下二次空気、助燃料の各量及び燃焼空気温度についても図3〜5において同様である。
【0023】
図3は本発明の汚泥燃焼炉の制御における、二次空気流量調節のロジック図である。図3において、ファジィ演算補正値αは、汚泥ケーキ量設定値(SV、セットヴァリュ)をファンクションジェネレータ20に入力して二次空気流量設定値に変換した信号と加算器21で加算され、補正二次空気流量設定値を得る。補正二次空気流量設定値と二次空気流量工程値(PV、プロセスヴァリュ)はPID回路22に入力され、PID動作により二次空気流量調節弁9の開度を調節する。
【0024】
図4は本発明の汚泥燃焼炉の制御における、燃焼空気温度調節のロジック図である。図4において、ファジィ演算補正値αは、汚泥ケーキ量設定値(SV、セットヴァリュ)をファンクションジェネレータ20に入力して燃焼空気温度設定値に変換した信号と加算器21で加算され、補正燃焼空気温度設定値を得る。補正燃焼空気温度設定値と燃焼空気温度工程値(PV、プロセスヴァリュ)はPID回路22に入力され、PID動作により燃焼空気温度調節器12の操作信号を出力し、ヒータ13により燃焼空気温度を調節する。
【0025】
図5は本発明の汚泥燃焼炉の制御における、助燃料流量調節のロジック図である。図5において、ファジィ演算補正値αは、汚泥ケーキ量設定値(SV、セットヴァリュ)をファンクションジェネレータ20に入力して助燃料流量設定値に変換した信号と加算器21で加算され、補正助燃料流量設定値を得る。補正助燃料流量設定値と助燃料流量工程値(PV、プロセスヴァリュ)はPID回路22に入力され、PID動作により燃料流量調節弁11の開度を調節する。
【0026】
【発明の効果】
以上説明したように、本発明により、下水汚泥燃焼炉の燃焼ガス中のN2Oを直接測定して、リアルタイムに燃焼条件に反映させて、その排出濃度を低減する燃焼炉の新しい制御方法及び制御装置の提供が可能となった。
【図面の簡単な説明】
【図1】 本発明の汚泥燃焼炉を含む、汚泥燃焼炉の制御装置の概略構成図
【図2】 本発明の汚泥燃焼炉の制御における、燃焼空気量調節のロジック図
【図3】 本発明の汚泥燃焼炉の制御における、二次空気流量調節のロジック図
【図4】 本発明の汚泥燃焼炉の制御における、燃焼空気温度調節のロジック図
【図5】 本発明の汚泥燃焼炉の制御における、助燃料流量調節のロジック図
【符号の説明】
1 汚泥燃焼炉
2 制御部
3 レーザ式濃度計
4 レーザ受光部
5 レーザ発光部
6 酸素濃度計
7 フリーボード温度計
8 砂層温度計
9 二次空気調節弁
10 助燃料調節弁
11 燃焼空気調節弁
12 燃焼空気温度調節器
20 ファンクションジェネレータ
21 加算器
22 PID回路[0001]
[Field of the Invention]
The present invention relates to a control method and control device for a combustion furnace for burning sludge. More particularly, the present invention relates to a combustion furnace control method and control apparatus for reducing N 2 O in exhaust gas of a combustion furnace that burns sludge.
[0002]
[Prior art]
Global warming nitrous oxide known as a gas (hereinafter N 2 O) is by far the reasons such as was not a gas regulated emissions concentration measurement and an exhaust gas N 2 O in the sewage sludge combustion furnace Combustion control by concentration has not been performed. However,
[0003]
Therefore, the technology for controlling the exhaust gas N 2 O concentration in the sewage sludge combustion furnace has not been publicly known so far, and even in the method of detecting the control substance in the combustion gas in real time, for example, in the detection of the CO concentration An example can be seen (see, for example, paragraph 0039 of Patent Document 1), but the detection of the N 2 O concentration is not yet publicly known.
[0004]
[Patent Document 1]
Japanese Patent Laid-Open No. 11-14027 (see, for example, paragraph 0039)
[0005]
[Problems to be solved by the invention]
The present invention has been made in view of such conventional problems. Combustion in which N 2 O in combustion gas of a sewage sludge combustion furnace is directly measured and reflected in combustion conditions in real time to reduce its exhaust concentration. An object is to provide a new method and apparatus for controlling a furnace.
[0006]
[Means for Solving the Problems]
A control method for a sludge combustion furnace according to the present invention is a control method for a combustion furnace in which auxiliary fuel and combustion air are supplied together with sludge to burn the sludge, and the N 2 O concentration in the combustion gas is detected and detected. Based on the value, calculate a correction value of at least one operation amount selected from the combustion air amount, the secondary air amount, the combustion air temperature, and the auxiliary fuel flow rate, and adjust the operation amount based on the calculated value, It is characterized by reducing N 2 O in the exhaust gas of the combustion furnace.
[0007]
Furthermore, the control method of the sludge combustion furnace of the present invention is a combustion furnace for burning the sludge by supplying auxiliary fuel and combustion air together with the sludge, and combusting by forming a bubble fluidized bed with the sludge using sand particles as a heat medium. In the control method for a combustion furnace, the N 2 O concentration in the combustion gas, the oxygen concentration in the exhaust gas, the temperature of the sand particle layer, and the temperature of the free board are detected, and the combustion air is detected based on the detected values. A correction value of at least one manipulated variable selected from the amount, the secondary air amount, the combustion air temperature, and the auxiliary fuel flow rate is calculated, and the manipulated variable is adjusted based on the calculated value, and N in the exhaust gas of the combustion furnace is calculated. 2 O is reduced.
[0008]
Further, the control method for sludge combustion furnace of the present invention, the N 2 O concentration in the combustion gas, in the combustion gas is irradiated with laser light of a specific wavelength in the near infrared wavelength region, N 2 in the laser beam It is obtained by measuring the absorbance of a specific wavelength that O absorbs.
[0009]
Furthermore, in the control method of the sludge combustion furnace of the present invention, the calculation of the correction value includes the detected N 2 O concentration in the combustion gas, the oxygen concentration in the exhaust gas, the temperature of the sand particle layer, and the temperature of the free board. The antecedent part is based on a calculation based on fuzzy inference with the combustion air amount, the secondary air amount, the combustion air temperature, and the auxiliary fuel flow rate as the consequent part.
[0010]
Furthermore, in the control method of the sludge combustion furnace of the present invention, the adjustment of each operation amount is obtained by adding the correction value to the operation amount setting value generated by inputting a predetermined input sludge amount into the function generator. The correction operation amount setting value and the operation amount process value are performed by a PID operation.
[0011]
Further, the control unit of the sludge combustion furnace of the present invention is the control device for a combustion furnace by supplying combustion air with the aid fuel with sludge burning the sludge, N 2 O for detecting the N 2 O concentration in the combustion gas A concentration meter, an operation amount detection means for detecting at least one operation amount selected from a combustion air amount, a secondary air amount, a combustion air temperature, and an auxiliary fuel flow rate, and the operation amount based on the N 2 O concentration detection value A control unit having a correction value calculation means for calculating a correction value of the control signal and an operation signal generation means for generating an operation signal of the correction manipulated variable based on the calculated correction value. N 2 O in exhaust gas is reduced.
[0012]
Furthermore, the control device for the sludge combustion furnace of the present invention is a combustion furnace that burns the sludge by supplying auxiliary fuel and combustion air together with the sludge, and burns by forming a bubble fluidized bed with the sludge using sand particles as a heat medium. the control device of a combustion furnace for the N 2 O concentration meter for detecting the concentration of N 2 O in the combustion gas, and the oxygen concentration meter that detects the oxygen concentration in the exhaust gas, a thermometer for detecting the temperature of the sand layer, A thermometer for detecting the temperature of the free board, an operation amount detecting means for detecting at least one operation amount selected from a combustion air amount, a secondary air amount, a combustion air temperature, and an auxiliary fuel flow rate, and the N 2 O concentration detection Correction value calculating means for calculating a correction value for the manipulated variable based on the detected value, the oxygen concentration detection value, the sand particle layer temperature detection value, and the freeboard temperature detection value, and correction based on the calculation correction value Generates an operation amount operation signal And a control unit having an operation signal generating means configured to reduce the N 2 O in the exhaust gas of the combustion furnace by adjusting the operation amount.
[0013]
Furthermore, the control apparatus for the sludge combustion furnace of the present invention is characterized in that the N 2 O concentration meter oscillates a laser beam having a specific wavelength in the near-infrared wavelength region and irradiates the combustion gas, and the irradiation The light receiving unit that receives the laser light transmitted through the combustion gas and the intensity before and after the N 2 O absorption of the received laser light are detected, the absorbance is obtained from the detection result, and the N 2 O concentration electric signal is obtained. It comprises a laser densitometer for conversion.
[0014]
Furthermore, in the control apparatus for the sludge combustion furnace of the present invention, the correction value calculating means detects the detected N 2 O concentration in the combustion gas, the oxygen concentration in the exhaust gas, the temperature of the sand particle layer, and the temperature of the free board. The antecedent part is a correction value calculation means based on a calculation by fuzzy inference with the combustion air amount, the secondary air amount, the combustion air temperature and the auxiliary fuel flow rate as the consequent part.
[0015]
Furthermore, in the control apparatus for the sludge combustion furnace of the present invention, the operation signal generation means inputs a predetermined input sludge amount and generates an operation amount setting value, and adds the operation amount setting value and the correction value. An adder and a PID circuit that inputs a corrected manipulated variable set value generated by the adder and the manipulated variable step value and outputs an operation signal of an adjusted manipulated variable are provided.
[0016]
DETAILED DESCRIPTION OF THE INVENTION
Hereinafter, embodiments of the present invention will be described in detail with reference to the drawings. However, the dimensions, shapes, materials, relative arrangements, and the like of the products described in the present embodiment are merely illustrative examples, not the main purpose of limiting the scope of the present invention unless otherwise specified. .
[0017]
FIG. 1 is a schematic configuration diagram of a control apparatus for a sludge combustion furnace including the sludge combustion furnace of the present invention. First, the sludge combustion process will be described with reference to FIG. The sewage sludge is dehydrated by a dehydration process (not shown) and supplied to the sludge combustion furnace 1 as a sludge cake 14 by a
[0018]
In this embodiment, in addition to the control device, a
[0019]
Then in the present embodiment, a description will be given of a control method of the combustion furnace to reduce the
[0020]
[Table 1]
[0021]
Furthermore, the control unit has an operation signal generating means, generates an adjustment operation amount based on the correction value α, and outputs an operation signal of each control valve or regulator. The logic diagrams are shown in FIGS. 2 to 5 for the amounts of combustion air, secondary air, auxiliary fuel, and combustion air temperature, respectively.
[0022]
The fuzzy calculation correction value α is converted into a combustion air flow rate setting value by inputting the sludge cake amount setting value (SV, set value) to the
[0023]
FIG. 3 is a logic diagram of secondary air flow rate adjustment in the control of the sludge combustion furnace of the present invention. In FIG. 3, the fuzzy calculation correction value α is added by the
[0024]
FIG. 4 is a logic diagram of combustion air temperature adjustment in the control of the sludge combustion furnace of the present invention. In FIG. 4, the fuzzy calculation correction value α is added by the
[0025]
FIG. 5 is a logic diagram of the auxiliary fuel flow rate adjustment in the control of the sludge combustion furnace of the present invention. In FIG. 5, the fuzzy calculation correction value α is added by the
[0026]
【The invention's effect】
As described above, according to the present invention, a new control method for a combustion furnace that directly measures N 2 O in the combustion gas of a sewage sludge combustion furnace, reflects it in combustion conditions in real time, and reduces its exhaust concentration, and A control device can be provided.
[Brief description of the drawings]
FIG. 1 is a schematic configuration diagram of a control apparatus for a sludge combustion furnace including the sludge combustion furnace of the present invention. FIG. 2 is a logic diagram for adjusting the amount of combustion air in the control of the sludge combustion furnace of the present invention. Fig. 4 is a logic diagram for adjusting the secondary air flow rate in the control of the sludge combustion furnace of the present invention. Fig. 4 is a logic diagram for adjusting the combustion air temperature in the control of the sludge combustion furnace of the present invention. , Logic diagram of auxiliary fuel flow rate adjustment [Explanation of symbols]
DESCRIPTION OF SYMBOLS 1
Claims (10)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2002292900A JP3746751B2 (en) | 2002-10-04 | 2002-10-04 | Control method and control apparatus for sludge combustion furnace |
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| Application Number | Priority Date | Filing Date | Title |
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| JP2002292900A JP3746751B2 (en) | 2002-10-04 | 2002-10-04 | Control method and control apparatus for sludge combustion furnace |
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| JP2004125331A JP2004125331A (en) | 2004-04-22 |
| JP3746751B2 true JP3746751B2 (en) | 2006-02-15 |
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| JP2002292900A Expired - Lifetime JP3746751B2 (en) | 2002-10-04 | 2002-10-04 | Control method and control apparatus for sludge combustion furnace |
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Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2012211727A (en) * | 2011-03-31 | 2012-11-01 | Kubota Corp | Sludge incineration disposal system and sludge incineration disposal method |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP5269631B2 (en) * | 2009-01-23 | 2013-08-21 | 出光興産株式会社 | N2O emission suppression combustion apparatus and N2O emission suppression method |
| JP6804183B2 (en) * | 2015-01-30 | 2020-12-23 | 三菱重工環境・化学エンジニアリング株式会社 | Fluidized bed sludge incinerator |
| CN114811596B (en) * | 2022-04-29 | 2023-01-31 | 江苏锦明再生资源有限公司 | Dry sludge treatment cleaning incinerator |
Family Cites Families (11)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS62242712A (en) * | 1986-04-15 | 1987-10-23 | Mitsubishi Heavy Ind Ltd | Low nox combustion method in fluidized bed type furnace |
| JPS63275935A (en) * | 1987-05-07 | 1988-11-14 | Fujitsu Ltd | Gas sensor |
| JPH04155105A (en) * | 1990-10-18 | 1992-05-28 | Nippon Steel Corp | Fluidized bed boiler to suppress generation of nitrous oxide |
| JPH04222304A (en) * | 1990-12-21 | 1992-08-12 | Mitsubishi Heavy Ind Ltd | Method for operating pressurized fluidized bed boiler |
| JP2889049B2 (en) * | 1992-06-09 | 1999-05-10 | 株式会社神戸製鋼所 | Method for reducing N2O and NOx in fluidized bed combustion |
| JPH06332501A (en) * | 1993-05-24 | 1994-12-02 | Ishikawajima Harima Heavy Ind Co Ltd | Feedback control device and incinerator using the control device |
| JP3059995B2 (en) * | 1994-06-03 | 2000-07-04 | 工業技術院長 | Fluidized bed combustion method for simultaneous reduction of nitrous oxide and nitrogen oxides |
| JP3023948B2 (en) * | 1994-10-25 | 2000-03-21 | 株式会社クボタ | Sewage sludge fluidized bed incinerator |
| JPH10142147A (en) * | 1996-11-08 | 1998-05-29 | Mitsubishi Heavy Ind Ltd | Method for measuring concentration of nitrogen oxides |
| JP2971421B2 (en) * | 1997-09-25 | 1999-11-08 | 中外炉工業株式会社 | Combustion control method for fluidized bed incinerator |
| JP2001033018A (en) * | 1999-07-19 | 2001-02-09 | Mitsubishi Heavy Ind Ltd | Method and apparatus for controlling combustion of burning furnace |
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2002
- 2002-10-04 JP JP2002292900A patent/JP3746751B2/en not_active Expired - Lifetime
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2012211727A (en) * | 2011-03-31 | 2012-11-01 | Kubota Corp | Sludge incineration disposal system and sludge incineration disposal method |
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