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JPH0781151B2 - High efficiency NOx control method - Google Patents
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JPH0781151B2 - High efficiency NOx control method - Google Patents

High efficiency NOx control method

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Publication number
JPH0781151B2
JPH0781151B2 JP4210087A JP4210087A JPH0781151B2 JP H0781151 B2 JPH0781151 B2 JP H0781151B2 JP 4210087 A JP4210087 A JP 4210087A JP 4210087 A JP4210087 A JP 4210087A JP H0781151 B2 JPH0781151 B2 JP H0781151B2
Authority
JP
Japan
Prior art keywords
nox
control
ecoo
concentration
coal
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
JP4210087A
Other languages
Japanese (ja)
Other versions
JPS63207894A (en
Inventor
学 折本
勝 森尾
祐輔 只隈
Original Assignee
バブコツク日立株式会社
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Publication date
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Priority to JP4210087A priority Critical patent/JPH0781151B2/en
Publication of JPS63207894A publication Critical patent/JPS63207894A/en
Publication of JPH0781151B2 publication Critical patent/JPH0781151B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、微粉炭燃焼装置において、多種類の石炭を同
一火炉で燃焼させる際の排ガス中の窒素酸化物を低減す
る運転方法に係り、高効率にして低NOx化を図るに好適
な火炉の制御方法に関する。
Description: TECHNICAL FIELD The present invention relates to an operation method for reducing nitrogen oxides in exhaust gas when burning many types of coal in the same furnace in a pulverized coal combustion apparatus, The present invention relates to a furnace control method suitable for achieving high efficiency and reducing NOx.

〔従来の技術〕[Conventional technology]

燃料として、多種類の石炭を同一ボイラで微粉状で浮遊
燃焼させるボイラ等にあっては、排ガス中のNOxに関し
て以下のことが言える。燃料比(固定炭素/揮発分)
が高い程NOx発生が高くなる。すなわち石炭中に含有す
るN分は、揮発分並びに固定炭素に偏在することなく分
布しており、燃料比が低い程、揮発分放出時のN分放出
率が高くなり、燃料比が高い程多くのN分がチャー中に
残留する。そして、揮発分中のN分は、バーナ中心域で
の還元雰囲気下で短時間に放出されることからNOxへの
転換率は低くなるのに対し、チャー中に残留するN分
は、酸化雰囲気下での燃焼を余儀なくされNOxへの転換
率が高くなる(第7図参照)。燃料中のN分が高いほ
どNOxが高くなる(第2図参照)。火炉出口O2(以下E
CoO2という)によってNOx値が影響を受ける(第4図NOx
曲線参照)。同一炭種の場合は、ECoO2に対しNOx値と
灰中未燃分とが相反する特性を有し、従ってNOxを低下
させる運転法は灰中未燃分を高める特性となる(第4図
未燃分曲線参照)と云った特徴をもつ。またECoO2一定
の場合でも、微粉炭の粒度によって燃料比に対する灰中
未燃分は変化する(第3図)。
The following can be said regarding NOx in the exhaust gas in a boiler or the like in which a large number of types of coal are burned in the form of fine powder in the same boiler as the fuel. Fuel ratio (fixed carbon / volatile matter)
The higher the value, the higher the NOx generation. That is, the N content contained in the coal is distributed without being unevenly distributed in the volatile content and the fixed carbon. The lower the fuel ratio, the higher the N content release rate at the time of volatile content release, and the higher the fuel ratio, the greater the N content. N minutes of remain in the char. Then, the N content in the volatile matter is released in a short time in the reducing atmosphere in the central region of the burner, so the conversion rate to NOx is low, while the N content remaining in the char is in the oxidizing atmosphere. Combustion underneath is forced and the conversion rate to NOx becomes high (see Fig. 7). The higher the N content in the fuel, the higher the NOx (see Fig. 2). Furnace outlet O 2 (hereinafter E
NOx value is affected by CoO 2 (Fig. 4 NOx)
See curve). In the case of the same coal type, the NOx value and the unburned ash content are incompatible with ECoO 2 , and therefore the operating method that reduces NOx has the characteristic of increasing the unburned ash content (Fig. 4). (Refer to the unburned component curve). Even when ECoO 2 is constant, the unburned content in the ash with respect to the fuel ratio changes depending on the particle size of the pulverized coal (Fig. 3).

これらの燃料比や燃料中N分の異なる多種類の石炭を同
一火炉で燃焼させ、且つ環境規制値以内にNOxを抑える
制御法としては、第5図において説明するように、基本
的には(イ)低NOxバーナによるNOxレベルの低下、
(ロ)二段燃焼設備の設置と、二段燃焼比の変化、
(ハ)排煙脱硝装置の取付けと、脱硝装置用NH3注入比
率の変化と云った方法で制御されてきた。
As described in FIG. 5, basically, as a control method for burning various types of coal having different fuel ratios and N content in the fuel in the same furnace and suppressing NOx within the environmental regulation value, as shown in FIG. B) Lower NOx level due to low NOx burner,
(B) Installation of two-stage combustion equipment and changes in the two-stage combustion ratio,
(C) It has been controlled by the method of mounting the flue gas denitration device and changing the NH 3 injection ratio for the denitration device.

第5図は、従来から存在する微粉炭焚きボイラ構造例
を、第6図はそのNOx制御例を示す。第5図において、
石炭は石炭バンカ20から給炭機21を経て微粉炭機22に送
られて粉砕され微粉炭が製造される。微粉炭機22からの
微粉炭は、微粉炭管23を経由して微粉炭バーナ24によっ
て火炉1へ供給され、風箱14からの燃焼用空気とともに
火炎2を形成する。尚、風箱14内にはエアレジスタ25及
び二段燃焼用NOxポート26が存在する。
FIG. 5 shows an example of a conventional pulverized coal burning boiler structure, and FIG. 6 shows an example of NOx control. In FIG.
Coal is sent from a coal bunker 20 through a coal feeder 21 to a pulverized coal machine 22 and pulverized to produce pulverized coal. The pulverized coal from the pulverized coal machine 22 is supplied to the furnace 1 by the pulverized coal burner 24 via the pulverized coal pipe 23 and forms the flame 2 together with the combustion air from the wind box 14. An air register 25 and a two-stage combustion NOx port 26 are present in the wind box 14.

そして、燃焼用空気の調整は、給炭機21の燃料量に比例
して強圧通風機11の入口に配置された空気流量制御タン
パ12によって行われる。通圧通風機11からの空気は、分
流して、一方の流れは火炉2からの排熱ガスを利用した
空気予熱器4により予熱された後、二段燃焼用空気流量
制御ダンパ10あるいはバーナ入口空気ダンパ13を経て火
炉1内に送られる。尚、前記空気流量制御ダンパ12はEC
oO2計32によってフィードバック制御されていた。分流
した空気の他方の流れは一次通風機15を通って、さらに
分流して前記空気予熱器4によって一部が予熱され熱空
気16となり予熱されなかった冷空気17と共に温度制御ダ
ンパ18を介して混合されて温度制御された後、微粉炭機
一次風量制御ダンパ19を経て微粉炭機22内に送られる。
Then, the adjustment of the combustion air is performed by the air flow rate control tamper 12 arranged at the inlet of the strong pressure blower 11 in proportion to the fuel amount of the coal feeder 21. The air from the ventilation fan 11 is split and one flow is preheated by the air preheater 4 using the exhaust heat gas from the furnace 2, and then the two-stage combustion air flow control damper 10 or burner inlet It is sent into the furnace 1 via the air damper 13. The air flow control damper 12 is an EC
It was feedback controlled by oO 2 total 32. The other flow of the split air is passed through the primary fan 15 and further split, and is partially preheated by the air preheater 4 to become hot air 16 and cold air 17 which has not been preheated through the temperature control damper 18. After being mixed and temperature-controlled, it is fed into the pulverized coal machine 22 through the pulverized coal machine primary air flow control damper 19.

また、NOx制御については、燃焼用空気量の10〜30%に
相当する量が二段燃焼用空気として分離されて送られる
二段燃焼用空気流量制御ダンパ10の開度を制御すること
によって微粉炭バーナ24のバーナ口空気比を制御し、ま
ず火炉1出口のNOx発生量を抑える。さらに、排煙脱硝
装置(以下De−NOx装置という)3へ配管34により注入
されるNH3注入率を、排ガス中のNOxメータ31によって監
視しつつ、NH3注入量制御弁33によって、制御して煙突
7の出口NOxを制御していたものである。尚、煙道8の
途中には電気集塵機5及び誘引通風機6が設けられる。
Regarding NOx control, fine powder is obtained by controlling the opening degree of the two-stage combustion air flow rate control damper 10 in which an amount corresponding to 10 to 30% of the combustion air amount is separated and sent as the two-stage combustion air. The air ratio of the burner port of the charcoal burner 24 is controlled to suppress the NOx generation amount at the furnace 1 outlet first. Further, the NH 3 injection rate injected into the flue gas denitration device (hereinafter referred to as De-NOx device) 3 by the pipe 34 is controlled by the NH 3 injection amount control valve 33 while being monitored by the NOx meter 31 in the exhaust gas. The outlet NOx of the chimney 7 was controlled. An electric dust collector 5 and an induced draft fan 6 are provided in the middle of the flue 8.

次に第6図を説明する。Next, FIG. 6 will be described.

まず、空気流量制御ダンパ12の制御について説明する。First, the control of the air flow rate control damper 12 will be described.

ボイラ入力信号BID(101)により空気流量要求信号が作
成されるが、この空気流量要求信号は燃焼に必要な空気
流量要求信号となるように過剰空気率を加算して作成さ
れる。過剰空気率は先ず負荷に応じたECoO2設定を演算
器(104)により作成し、ECoO2測定信号(102)と減算
器(105)により減算しその偏差が積分器(106)により
積分されて過剰空気率信号となる。ボイラ入力信号(10
1)と過剰空気率信号(積分器(106)出力)は加算器
(107)で加算され空気流量要求信号となる。この空気
流量要求信号と空気流量測定信号AF(103)を減算器(1
08)で減算し、その偏差が零となるように調節計(比例
積分器)(109)により空気流量制御ダンパ(12)を調
節する。尚、H/A(空気予熱器110,113,120)は自動手動
切替器で通常は自動状態で使用し、運転員が手動調整す
るときはH/Aを手動に切替えて調整する。
An air flow rate request signal is created by the boiler input signal BID (101). This air flow rate request signal is created by adding the excess air ratio so as to be the air flow rate request signal required for combustion. The excess air ratio is calculated by setting the ECoO 2 setting according to the load by the calculator (104), subtracting it by the ECoO 2 measurement signal (102) and the subtractor (105), and integrating the deviation by the integrator (106). It becomes an excess air ratio signal. Boiler input signal (10
1) and the excess air ratio signal (output of the integrator (106)) are added by the adder (107) to form an air flow rate request signal. This air flow rate request signal and the air flow rate measurement signal AF (103) are subtracted (1
In step 08), the air flow rate control damper (12) is adjusted by a controller (proportional integrator) (109) so that the deviation becomes zero. The H / A (air preheater 110, 113, 120) is an automatic manual switching device and is normally used in an automatic state. When the operator manually adjusts, the H / A is switched to manual and adjusted.

次に、二段燃焼空気流量制御ダンパ10の制御について説
明する。これは、ボイラ燃焼空気流量に応じて制御ダン
パ開度を決定する制御で、空気流量測定信号A/F(103)
によりダンパ開度設定を演算器(112)で作成し演算器
(112)の出力信号で2段燃焼用空気流量制御ダンパ(1
0)を調整する。
Next, the control of the two-stage combustion air flow rate control damper 10 will be described. This is a control that determines the control damper opening according to the boiler combustion air flow rate. The air flow rate measurement signal A / F (103)
The damper opening setting is created by the calculator (112) by the output signal of the calculator (112) and the two-stage combustion air flow rate control damper (1
Adjust 0).

さらに、NH3注入流量制御弁(33)の制御について説明
する。
Further, the control of the NH 3 injection flow rate control valve (33) will be described.

NH3注入流量制御は排ガス中のNOx量に応じてNH3注入量
を調整することによりおこなう。NH3注入量要求信号は
燃焼空気量(排ガス量に相当)AF(103)と排ガス中のN
Ox測定信号(115)を掛算器(117)で掛算して作成す
る。NH3注入量要求信号((117)出力信号)とNH3測定
信号(116)を減算器(118)で減算しその偏差が零にな
るように調節計(比例積分器)(119)によりNH3注入流
量制御弁33を調節する。
The NH 3 injection flow rate control is performed by adjusting the NH 3 injection amount according to the NOx amount in the exhaust gas. The NH 3 injection amount request signal is the combustion air amount (corresponding to the exhaust gas amount) AF (103) and N in the exhaust gas.
It is created by multiplying the Ox measurement signal (115) by the multiplier (117). The NH 3 injection amount request signal ((117) output signal) and the NH 3 measurement signal (116) are subtracted by the subtractor (118) and the deviation is zero by the controller (proportional integrator) (119). 3 Adjust the injection flow control valve 33.

ところで、要求されるNOxレベルが年々低くなっている
為、二段燃焼用空気流量制御ダンパ10は最適化した結果
の最大の開度で使用し、NH3注入率で調整する方式が一
般的となって来た。
By the way, since the required NOx level is decreasing year by year, it is common to use the two-stage combustion air flow rate control damper 10 at the maximum opening as a result of optimization and adjust it with the NH 3 injection rate. It has become.

この方法によれば、まず基本的には、ECoO2濃度は、負
荷(燃料量)と一対に対応させたプログラム制御(第6
図104)を組んでいた。従って多種類の石炭を同一火炉
で燃焼させる場合は、NOx、灰中未燃分ともに多く生ず
る高燃料化炭をベースとして高めにECoO2設定されてい
た。
According to this method, basically, the ECoO 2 concentration is basically controlled by a program control (6th load) corresponding to a load (fuel amount).
(Figure 104) was assembled. Therefore, when burning many types of coal in the same furnace, ECoO 2 was set higher based on the highly fueled coal that produces a large amount of both NOx and unburned ash.

そして、燃料比が低い、つまり燃えやすく且つNOxも下
げやすい低燃料比炭を燃焼させる時も、効率を上げ所内
動力率を下げる為に効果的なECoO2を下げて運転するこ
とは行われないままであった。
And, even when burning a low fuel ratio coal that has a low fuel ratio, that is, it is easy to burn and also lowers NOx, it is not possible to operate by lowering the effective ECoO 2 in order to increase the efficiency and reduce the power factor in the plant. It remained.

〔発明が解決しようする問題点〕[Problems to be solved by the invention]

上記した従来技術は、多種類の石炭を同一火炉で使用し
て高効率運転しようとする観点から考えた時、未燃分が
低く且つNOxも下げやすい低揮発分炭(第4図参照)に
ついて、排ガス損失が低下でき所内率も下げられる手段
として有効なECoO2濃度を下げた運転をおこなうこと
が、出来ない。従って、これらの石炭ではECoO2濃度を
下げることによって更にNOxが低下できNH3注入率が低下
できるにもかかわらず、ECoO2濃度を下げる運転がなさ
れにくい為に、NH3も努力して下げる事がなく従って高
効率運転されてなかった。
The above-mentioned conventional technology is a low volatility coal (see FIG. 4) that has low unburned content and is easy to reduce NOx from the viewpoint of high efficiency operation by using many types of coal in the same furnace. However, it is not possible to operate with a low ECoO 2 concentration, which is effective as a means of reducing exhaust gas loss and lowering the in-house rate. Thus, despite the addition it can decrease NH 3 injection rate can decrease NOx by lowering the ECoO 2 concentration in these coal, in order to not easily made operated to lower the ECoO 2 concentration, to lower NH 3 also efforts to There was therefore no high efficiency operation.

このような運転の方法は、我国のように資源のない国で
は危険分散の点から数多くの産炭地からの石炭を輸入し
同一火炉へ燃焼させていると同時に、火炉が大容量炉と
なっており、さらに鉱物船の大きさとの関連で炭種が変
わる度合いは増しているほか、効率向上の要求は日増し
に強くなっている等から、問題があった。
This kind of operation method imports coal from a number of coal-producing areas and burns it in the same furnace from the viewpoint of risk dispersion in a country without resources such as Japan, and at the same time the furnace becomes a large-capacity furnace. In addition, the degree of change in coal type is increasing in relation to the size of the mineral ship, and the demand for improved efficiency is becoming stronger day by day.

〔問題点を解決するための手段〕[Means for solving problems]

本発明は、上記した問題点を解決する為に、まず、入荷
したバンカに入って来た石炭性状のうち燃料比と燃料中
N分を、制御上のインプット項目として電算機へ入力す
る。一方、電算機には、当該火炉または、類似炉で得ら
れたデータから、(a)N分に対するNOx(第2図参
照)補正率、(b)ECoO2濃度に対するNOxと未燃分(第
4図参照)、(c)燃料比に対するNOx(第7図参
照)、および未燃分(第3図参照)(d)NH3注入率と
脱硝率の関連(従来から既知)、を記憶させておく。煙
突出口NOx値(地元の規制値)は制御目標値として事前
に把握されているので、該NOx値の範囲内において、ECo
O2濃度に対する排ガス損失及び所内率のコスト計算、EC
oO2濃度に対し未燃分増加による損失コスト(未燃分コ
スト)計算、及び前記NOx値によって決まるNH3注入率に
対するコスト計算を計算させる。そして計算結果にもと
づいて効率が最大(損失が最小)となるECoO2濃度を見
出し、従来のECoO2濃度プログラムに、バイアス率を打
出すと共に自動時に制御信号としてアウトプットする。
以上のような制御は、たとえば、インテリジェット型NO
x制御装置によっておこなう。
In order to solve the above-mentioned problems, the present invention first inputs the fuel ratio and the N content in the fuel among the coal properties that have entered the bunker that has arrived to the computer as input items for control. On the other hand, from the data obtained in the furnace or a similar furnace, the computer calculates (a) NOx (see FIG. 2) correction factor for N content, (b) NOx and unburned content (E) for ECoO 2 concentration. (See FIG. 4), (c) NOx with respect to fuel ratio (see FIG. 7), and unburned content (see FIG. 3) (d) Relationship between NH 3 injection rate and denitrification rate (known from the past). Keep it. The smoke outlet NOx value (local regulation value) is known in advance as a control target value, so within the range of the NOx value, ECo
Cost calculation of exhaust gas loss and in-house ratio with respect to O 2 concentration, EC
Calculation of loss cost (unburned component cost) due to increase of unburned component with respect to oO 2 concentration and cost calculation for NH 3 injection rate determined by the NOx value. Then, based on the calculation results, the ECoO 2 concentration that maximizes the efficiency (minimum loss) is found, and the bias rate is added to the conventional ECoO 2 concentration program and output as a control signal automatically.
The control described above is performed, for example, with an intelligent jet type NO.
x Control unit.

〔作用〕[Action]

微粉炭燃焼炉においてECoO2濃度を変化させた時のNOx、
灰中未燃分の挙動は第4図に示されている。まず、NOx
について取り上げると、二段燃焼率を一定とするとECoO
2濃度が低くなった場合、バーナ下流において発生したN
Oxは空気不足の雰囲気下で還元作用を受け、その一部が
安定なN2に還元され、NOx値は低下する。NOx低下はDe−
NOxにおけるNH3注入率を下げる効果をもつほか空気予熱
器の酸性硫安の発生を軽減しA/H詰りを軽減させる。次
に、未燃分はECoO2濃度が低くなった場合、酸欠によっ
て燃焼率が低下し、この為、灰中未燃分中の未燃カーボ
ンにはたとえば尚8,000Kcal/kgの発熱量を有しており、
未燃損失は燃料損失で増加する。
NOx when changing the ECoO 2 concentration in a pulverized coal combustion furnace,
The behavior of unburned matter in the ash is shown in FIG. First, NOx
Let's take a look at
2 N generated in the downstream of the burner when the concentration became low
Ox undergoes a reducing action in an air-deficient atmosphere, part of which is reduced to stable N 2 , and the NOx value decreases. Decrease in NOx
It has the effect of lowering the NH 3 injection rate in NOx, and also reduces the generation of acid ammonium sulfate in the air preheater and reduces A / H clogging. Next, when the ECoO 2 concentration of the unburned matter becomes low, the combustion rate decreases due to oxygen deficiency, and therefore the unburned carbon in the unburned matter in the ash still has a calorific value of 8,000 Kcal / kg, for example. Have,
Unburned loss increases with fuel loss.

一方、空気予熱器出口ガス温度は一般的に低負荷時でも
130℃,高負荷時は145℃程度をバランスする様設計され
る為、ECoO2濃度が高いほど、排ガス量が増加し、乾き
排ガス損失の他、空気中湿分損失が増加すると共に、空
気や排ガスを移送する為の強圧通風機および誘引通風機
6の動力は、大きくなる。
On the other hand, the air preheater outlet gas temperature is generally low even under low load.
Since it is designed to balance about 130 ° C and about 145 ° C at high load, the higher the ECoO 2 concentration is, the more the exhaust gas amount increases, and in addition to the dry exhaust gas loss, the air moisture loss also increases, and The power of the high-pressure draft fan and the induction draft fan 6 for transferring the exhaust gas becomes large.

これらは、極めて複雑に多変数で関与しており、最適化
を図るには、多変数の因子を総合的に判断して行う必要
があり、多種類の石炭で且つ大容量燃焼炉で炭種が頻繁
に変化する為、たとえばインテリジェント型NOx制御装
置を使った制御をおこなえば、コスト面の最適化が図れ
る。
These are very complicatedly involved in multiple variables, and in order to achieve optimization, it is necessary to comprehensively judge the factors of the multiple variables. Since it changes frequently, cost control can be optimized if control is performed using, for example, an intelligent NOx control device.

〔実施例〕〔Example〕

具体的な実施例を第1図にもとづいて説明する。図にお
いて右側の制御回路は、従来技術と同一機能同一作用を
もつ(第6図左側参考)。図中の左側に示される様に、
ECoO2制御回路に、事前にインテリジェント型NOx制御装
置を付加させ、次に予知出来る石炭中の燃料比及びN分
をインプットする(201)。この燃料比及びN分は、連
続分析装置による結果として信号で入力してもよいし、
人手によって入力してもよい。NOx制御装置内では、例
えば、燃料比に対するNOx及び未燃分が、データファイ
ルまたは計算式(負荷静定特性)で予測される(20
2)。その後、NOxは燃料中N分によってN分補正が、か
けられる(203)。このNOx値によって、De−NOx特性を
もとにNH3注入率が決定出来る(204)。該注入率におけ
るNOx値が地元の規制値の制限内か否かが判断される(2
05)。制限内であれば、次いで、NH3注入率コスト、排
ガス損失及び所内率(206)さらに未燃分コスト(207)
がNOx制限ECoO2内で繰返し計算されて、損失ミニマム値
が選定される(208)。これをもとにして、従来技術で
採用しているO2プログラム制御設定値にバイアス率を加
算して(209)、O2濃度を求めるものである。勿論ECoO2
濃度には火炉安全上に必要なミニマム値は下限として与
えられている。
A specific embodiment will be described with reference to FIG. The control circuit on the right side of the drawing has the same function and function as those of the prior art (see the left side of FIG. 6). As shown on the left side of the figure,
An intelligent NOx controller is added to the ECoO 2 control circuit in advance, and then the predictable fuel ratio and N content in coal are input (201). This fuel ratio and N content may be input as a signal as a result of the continuous analyzer,
You may enter it manually. In the NOx controller, for example, NOx and unburned fuel content with respect to the fuel ratio are predicted by a data file or a calculation formula (load static characteristic) (20
2). After that, NOx is corrected by N minutes according to N minutes in the fuel (203). Based on this NOx value, the NH 3 injection rate can be determined based on the De-NOx characteristics (204). It is judged whether the NOx value in the injection rate is within the limit of the local regulation value (2
05). Within limits, then, NH 3 injection rate cost, the exhaust gas loss and house index (206) further unburned cost (207)
Is repeatedly calculated in the NOx-limited ECoO 2 to select the minimum loss value (208). Based on this, the bias rate is added to the O 2 program control setting value adopted in the conventional technique (209) to obtain the O 2 concentration. Of course ECoO 2
The minimum value for furnace safety is given as the lower limit for the concentration.

このようにインテリジェント型NOx制御装置を用いてNOx
制御した場合には、(NOx特性、未燃分特性に若干余裕
がないと不可能であるが)負荷に対するECoO2濃度設定
値は、燃料が異ることにより変化して、運転員にはまざ
らわしい面はあるが、ECoO2濃度のベースとなっている
高燃料比炭以外の石炭が入荷した時は、低ECoO2濃度化
が可能となり、従って排ガス損失、NH3注入率が低下し
て、高効率運転が可能となるほか、SO2→SO3への転化率
やリークNH3が減るので、De−NOx装置を設置した時の問
題として残るNH4(H)SO4(酸性硫安)によるA/Hの詰
り、すなわちドラフトロス上昇が軽減出来る。
Thus, using the intelligent NOx controller, NOx
When controlled, the ECoO 2 concentration set value for the load (although it is impossible unless there is some margin in the NOx characteristics and unburned content characteristics) changes due to different fuels, and is Although it is confusing, when coal other than the high fuel ratio coal, which is the base of the ECoO 2 concentration, arrives, it becomes possible to lower the ECoO 2 concentration, thus reducing exhaust gas loss and NH 3 injection rate. In addition to enabling high-efficiency operation, the conversion rate from SO 2 to SO 3 and the leak NH 3 are reduced, so NH 4 (H) SO 4 (acidic ammonium sulfate) remains as a problem when installing a De-NOx device. The clogging of A / H due to), that is, the rise of draft loss can be reduced.

また、ECoO2濃度低下に伴って懸念される排ガス量低下
での対流伝熱部の特性すなわち、例えば再熱蒸気温度特
性、未達の問題は、排ガスのパラレルダンパ制御、また
は/および排ガス再循環ガス量制御によっても対応が可
能となるので問題はない。
In addition, the characteristics of the convection heat transfer part when the amount of exhaust gas decreases, which is a concern with a decrease in the concentration of ECoO 2 , that is, for example, the reheat steam temperature characteristic, the problem that has not been achieved is parallel damper control of exhaust gas and / or exhaust gas recirculation. There is no problem because it can be handled by controlling the gas amount.

煙突出口にてのNOx濃度は60ppmとされて,NOxダンパはほ
ぼ全開または一定開度で運転されDe−NOxへNH3注入率が
主制御因子と考えられている現在において今後、ECoO2
でNOx制御することを提案できるのは、NRバーナと云っ
た高効率低NOxバーナが開発され、このバーナを生か
し、更に高効率化するにはどうすればよいかという間に
ある程度答えられたものである。
NOx concentration in the chimney outlet is a 60 ppm, the future at present the NOx damper NH 3 injection rate into operated at substantially full open or constant opening De-NOx is considered as the main regulator, ECoO 2
The reason why NOx control can be proposed is that the high-efficiency and low-NOx burner called NR burner was developed, and there was an answer to some extent between how to use this burner to further improve the efficiency. .

〔発明の効果〕〔The invention's effect〕

本発明によれば、 (1) 多種類の石炭のうち、ECoO2濃度(NOx、未燃
分)設定のベースとなった高燃料比炭以外の燃料が入荷
した時、低ECoO2濃度運転が可能であるので、最も効率
の高い運用が可能となる。
According to the present invention, (1) When a fuel other than the high-fuel-ratio coal, which is the base for setting the ECoO 2 concentration (NOx, unburned matter) among the various types of coal, is received, the low ECoO 2 concentration operation is performed. Since this is possible, the most efficient operation is possible.

(2) ECoO2濃度低下に伴ない、酸性硫安によるA/H詰
りが軽減出来、ランニングコストの他、メインテナンス
フィの軽減が可能となる。
(2) As the ECoO 2 concentration decreases, A / H clogging due to acidic ammonium sulfate can be reduced, and running costs as well as maintenance phi can be reduced.

(3) 多種炭に対し、ワンマンコントロールを行うに
当り最適ECoO2濃度を、制御装置内で算出出来るので、
省力化したプラントに最適である。
(3) Since the optimum ECoO 2 concentration can be calculated in the control device when performing one-man control for multiple coals,
Ideal for labor-saving plants.

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

第1図は本発明になるインテリジェント制御装置をあら
わす図、第2図はバーナ空気比、燃料比がほぼ一定で、
N分が変化した時のNOx特性図、第3図はO2一定、燃料
比変化時の未燃分特性図、第4図はO2変化時の未燃分及
びNOxの特性図、第5図は従来技術になるボイラシステ
ム例をあらわす図、第6図は従来技術になる燃焼空気量
制御システムをあらわす図、第7図は燃料中N分が、ほ
ぼ同一で、燃料比が変化した時のNOx特性図である。
FIG. 1 shows an intelligent control device according to the present invention, and FIG. 2 shows a burner air ratio and a fuel ratio which are substantially constant.
NOx characteristic diagram when N minute is changed, Fig. 3 is O 2 constant, unburned component characteristic diagram when the fuel ratio is changed, and Fig. 4 is an unburned component and NOx characteristic diagram when O 2 is changed, 5th The figure shows an example of a conventional boiler system, FIG. 6 shows a conventional combustion air amount control system, and FIG. 7 shows when the N content in the fuel is almost the same and the fuel ratio changes. 3 is a NOx characteristic diagram of FIG.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】燃料比(固定炭素/揮発分)および燃料中
のN分が異なる多種類の石炭を同一火炉において燃焼さ
せる燃焼炉において、煙道排ガス中のNOxを規制値以内
に制御する制御回路に、事前に今から使用する石炭の燃
料比および燃料中N分をインプットすることにより、負
荷静定特性にもとづいた効率計算を排ガス中のO2(ECoO
2)濃度、灰中の未燃分、NH3注入量の因子から計算さ
せ、効率が最大となるECoO2濃度を見い出してアウトプ
ットし、該濃度にもとづいて自動的に燃焼用空気量を制
御し、よってNOxを制御する制御回路を設定することを
特徴とした高効率NOx制御方法。
1. A control for controlling NOx in flue gas within a regulated value in a combustion furnace in which multiple types of coal having different fuel ratios (fixed carbon / volatile matter) and N content in fuel are burned in the same furnace. By inputting the fuel ratio of the coal to be used from now on and the N content in the fuel in advance to the circuit, the efficiency calculation based on the load static characteristic can be calculated in the exhaust gas O 2 (ECoO
2 ) Calculated from factors such as concentration, unburned content in ash, and NH 3 injection amount, find the ECoO 2 concentration that maximizes efficiency, output it, and automatically control the combustion air amount based on that concentration Therefore, a high-efficiency NOx control method characterized by setting a control circuit for controlling NOx.
JP4210087A 1987-02-25 1987-02-25 High efficiency NOx control method Expired - Fee Related JPH0781151B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4210087A JPH0781151B2 (en) 1987-02-25 1987-02-25 High efficiency NOx control method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4210087A JPH0781151B2 (en) 1987-02-25 1987-02-25 High efficiency NOx control method

Publications (2)

Publication Number Publication Date
JPS63207894A JPS63207894A (en) 1988-08-29
JPH0781151B2 true JPH0781151B2 (en) 1995-08-30

Family

ID=12626566

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4210087A Expired - Fee Related JPH0781151B2 (en) 1987-02-25 1987-02-25 High efficiency NOx control method

Country Status (1)

Country Link
JP (1) JPH0781151B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004069251A (en) * 2002-08-09 2004-03-04 Mitsubishi Heavy Ind Ltd Pulverized coal combustion system

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5162228B2 (en) * 2007-12-21 2013-03-13 バブコック日立株式会社 Boiler equipment
JP4985857B1 (en) * 2011-02-25 2012-07-25 三菱マテリアル株式会社 Control method of NOx concentration in exhaust gas in combustion equipment using pulverized coal
JP6946060B2 (en) * 2017-06-01 2021-10-06 三菱パワー株式会社 Control device for coal-fired boiler

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004069251A (en) * 2002-08-09 2004-03-04 Mitsubishi Heavy Ind Ltd Pulverized coal combustion system

Also Published As

Publication number Publication date
JPS63207894A (en) 1988-08-29

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