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JPH0247649B2 - ROOTARIKIRUNNIOKERUNENSHOHAIGASUOMOCHIITANENSHOSEIGYOHOHO - Google Patents
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JPH0247649B2 - ROOTARIKIRUNNIOKERUNENSHOHAIGASUOMOCHIITANENSHOSEIGYOHOHO - Google Patents

ROOTARIKIRUNNIOKERUNENSHOHAIGASUOMOCHIITANENSHOSEIGYOHOHO

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Publication number
JPH0247649B2
JPH0247649B2 JP27129384A JP27129384A JPH0247649B2 JP H0247649 B2 JPH0247649 B2 JP H0247649B2 JP 27129384 A JP27129384 A JP 27129384A JP 27129384 A JP27129384 A JP 27129384A JP H0247649 B2 JPH0247649 B2 JP H0247649B2
Authority
JP
Japan
Prior art keywords
combustion
zone
furnace wall
exhaust gas
waste
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
JP27129384A
Other languages
Japanese (ja)
Other versions
JPS61149720A (en
Inventor
Norimasa Shimomura
Mineo Fukiharu
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.)
Kanadevia Corp
Original Assignee
Hitachi Shipbuilding and Engineering Co 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 Hitachi Shipbuilding and Engineering Co Ltd filed Critical Hitachi Shipbuilding and Engineering Co Ltd
Priority to JP27129384A priority Critical patent/JPH0247649B2/en
Publication of JPS61149720A publication Critical patent/JPS61149720A/en
Publication of JPH0247649B2 publication Critical patent/JPH0247649B2/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】 産業上の利用分野 本発明はロータリキルンにおける燃焼排ガスを
用いた燃焼制御方法に関する。
DETAILED DESCRIPTION OF THE INVENTION Field of the Invention The present invention relates to a combustion control method using combustion exhaust gas in a rotary kiln.

従来の技術 ロータリキルン内に投入された廃棄物は、順
次、乾燥ゾーン、熱分解・ガス化ゾーン、発炎燃
焼ゾーン、おき燃焼ゾーンを経て燃焼を終了して
いた。
Conventional Technology Waste input into a rotary kiln passes through a drying zone, a pyrolysis/gasification zone, a flaming combustion zone, and an arbor combustion zone, and then completes its combustion.

発明が解決しようとする問題点 ところで、上記の燃焼によると、廃棄物の性状
(含水率、発熱量、着火温度等)の違いにより、
上記の過程に要する時間が大きく異なる。特に廃
棄物は、その性状変化が激しく、従つてその性状
変動に応じて、ロータリキルン内の乾燥ゾーン、
熱分解・ガス化ゾーン、発炎燃焼ゾーン、おき燃
焼ゾーンの長さが変化するが、ロータリキルンの
構造上、各ゾーンを安定して制御することは不可
能であつた。このため、着火性の良い高発熱量廃
棄物の場合、キルン内投入後の急激な発炎燃焼が
制御できず、キルン内壁の損傷や高濃度のNOx
発生といつた問題があつた。一方、着火性の悪い
低発熱量廃棄物の場合、キルン内投入後から発炎
燃焼を開始するまでの乾燥ゾーン、熱分解・ガス
化ゾーンの長さが長く、且つ不安定なため、安定
した燃焼が得られないという問題があつた。これ
らの問題はすべて、含水燃料の乾燥ゾーン、熱分
解・ガス化ゾーンに必要な熱量のほとんどが発炎
燃焼による火炎からの熱輻射に依存しているこ
と、および、この火炎輻射の強度が通常の燃焼制
御方法では制御しきれなかつたことに起因してい
る。つまり、火炎輻射強度を決定する熱分解ガス
濃度、酸素濃度、燃焼反応域の温度の炉壁内の分
布状況を人為的に制御することが可能であれば、
内の各ゾーンの制御も可能となるわけである。
Problems to be Solved by the Invention By the way, according to the above combustion, due to differences in the properties of the waste (moisture content, calorific value, ignition temperature, etc.),
The time required for the above processes varies widely. In particular, waste material changes rapidly in its properties, so depending on the property changes, the drying zone in the rotary kiln,
Although the lengths of the pyrolysis/gasification zone, flaming combustion zone, and stoking combustion zone vary, it has been impossible to stably control each zone due to the structure of the rotary kiln. For this reason, in the case of high calorific value waste with good ignitability, rapid flaming combustion cannot be controlled after being put into the kiln, causing damage to the inner wall of the kiln and high concentration of NOx.
There was a problem that occurred. On the other hand, in the case of low calorific value waste with poor ignitability, the length of the drying zone and pyrolysis/gasification zone from the time it is introduced into the kiln to the start of flaming combustion is long and unstable, so There was a problem that combustion could not be obtained. All of these problems are due to the fact that most of the heat required for the drying zone of hydrous fuel and the pyrolysis/gasification zone depends on heat radiation from the flame due to flaming combustion, and that the intensity of this flame radiation is usually This is due to the fact that the previous combustion control method was unable to control the combustion. In other words, if it is possible to artificially control the distribution of pyrolysis gas concentration, oxygen concentration, and combustion reaction zone temperature within the furnace wall, which determine the flame radiation intensity,
This also makes it possible to control each zone within the zone.

従来、この種の目的で燃焼用空気の量、送入位
置を変化させる方法がとられてきたが、空気中の
酸素濃度が約21%と高いために、空気送入後の、
熱分解ガスと送入空気の燃焼反応が制御困難であ
り、したがつて、火炎輻射強度の制御も不可能で
あつた。
Conventionally, methods have been used for this type of purpose by changing the amount of combustion air and the position at which it is introduced, but because the oxygen concentration in the air is as high as approximately 21%,
The combustion reaction between the pyrolysis gas and the incoming air was difficult to control, and therefore it was also impossible to control the flame radiation intensity.

問題を解決するための手段 上記問題を解決するため、本発明のロータリキ
ルンにおける燃焼制御方法は、円筒状炉壁を有
し、この炉壁の両開口端の一方から他方に廃棄物
が移送され、廃棄物の移送経路の順に乾燥ゾー
ン、熱分解・ガス化ゾーン、発炎燃焼ゾーン及び
おき燃焼ゾーンが形成されるロータリキルンにお
いて、上記炉壁のいずれか一方の開口端から燃焼
用一次空気を供給すると共に、炉壁中間部から燃
焼排ガスを供給し、且つこの燃焼排ガスの供給量
を炉壁内の温度により制御する方法で、炉壁内の
中間部即ち発炎燃焼ゾーンに燃焼排ガスを供給し
て、発炎燃焼ゾーンの温度上昇を防ぐと共に安定
した燃焼を得るものである。
Means for Solving the Problem In order to solve the above problem, the combustion control method in a rotary kiln of the present invention has a cylindrical furnace wall, and waste is transferred from one of the open ends of the furnace wall to the other. In a rotary kiln, in which a drying zone, a pyrolysis/gasification zone, a flaming combustion zone, and a stoking combustion zone are formed in the order of the waste transfer route, primary air for combustion is supplied from the open end of one of the furnace walls. At the same time, the flue gas is supplied from the middle part of the furnace wall, and the amount of this flue gas supplied is controlled by the temperature inside the furnace wall, and the flue gas is supplied to the middle part of the furnace wall, that is, the flaming combustion zone. This prevents temperature rise in the flaming combustion zone and provides stable combustion.

実施例 以下、本発明の一実施例を第1図に基づき説明
する。1は並流式ロータリキルンの円筒状炉壁
で、回転自在に支持されている。2はこの炉壁1
の一方の開口端側に設けられた投入用フードで、
その中間部には廃棄物の投入ホツパー3が挿入さ
れると共に、その下部には補助燃料噴出ノズル4
が設けられている。5は炉壁1の他方の開口端側
に設けられた排出用フードで、その下部には焼却
残渣の排出口6が形成されると共に上部には燃焼
ガスの排出口7が形成されている。8,9は炉壁
1の中間前後位置において且つ炉壁1外周面に沿
つて設けられた第1及び第2環状空気供給室で、
炉壁1内とはそれぞれ流量調整弁10を有する複
数個の空気取入管11を介して連通されている。
12は炉壁1内に燃焼用一次空気及び燃焼用二次
空気を供給する空気供給ラインで、送風フアン1
3に接続された空気供給主管12Aと、この空気
供給主管12Aから分岐されると共にそれぞれダ
ンパー14を有する3本の空気供給枝管12B,
12C,12Dが分岐され、且つそのうち一本1
2Bは投入用ホツパー3に接続され、また残りの
2本12C,12Dは第1、第2環状空気供給室
8,9にそれぞれ接続されている。15は燃焼排
ガスを炉壁1内に供給する排ガス供給ラインで、
排ガス供給主管15Aと、この排ガス供給主管1
5Aから分岐されると共にそれぞれダンパー16
を有し且つそれぞれ先端が上記各空気供給枝管1
2B,12C,12Dのダンパー14より下流部
に接続された3本の排ガス供給枝管15B,15
C,15Dとから構成されている。なお、燃焼排
ガスとして、このロータリキルン後方から取出さ
れる処理済みの燃焼排ガスを使用するか、又は他
の焼却炉から出た燃焼排ガスを使用してもよい。
そして、上記投入用フード2及び両環状空気供給
室8,9に供給される燃焼用空気及び燃焼排ガス
は、それぞれの場所に対応する炉壁1内温度によ
つて、その供給量が制御される。即ち、乾燥ゾー
ンA及び熱分解・ガス化ゾーンB発炎燃焼ゾーン
C及びあと燃焼ゾーンDには、第1、第2及び第
3温度検出器17,18,19が配置されると共
に、第1温度検出器17からの信号によつて投入
用フード2に接続された各枝管12B,15Bの
ダンパー14,16の開度が、また第2温度検出
器18からの信号によつて第1環状空気供給室8
に接続された各枝管12C,15Cのダンパー1
4,16の開度が、更に第3温度検出器19から
の信号によつて第2環状空気供給室9に接続され
た各枝管12D,15Dのダンパー14,16の
開度が、それぞれ調節される。
Embodiment An embodiment of the present invention will be described below with reference to FIG. Reference numeral 1 denotes a cylindrical furnace wall of a cocurrent rotary kiln, which is rotatably supported. 2 is this furnace wall 1
A loading hood installed on one open end side of the
A waste input hopper 3 is inserted in the middle part, and an auxiliary fuel injection nozzle 4 is inserted in the lower part.
is provided. Reference numeral 5 denotes an exhaust hood provided on the other open end side of the furnace wall 1, with an incineration residue exhaust port 6 formed at its lower part and a combustion gas exhaust port 7 formed at its upper part. 8 and 9 are first and second annular air supply chambers provided at intermediate longitudinal positions of the furnace wall 1 and along the outer peripheral surface of the furnace wall 1;
It communicates with the inside of the furnace wall 1 via a plurality of air intake pipes 11 each having a flow rate regulating valve 10.
12 is an air supply line that supplies primary air for combustion and secondary air for combustion into the furnace wall 1;
3, and three air supply branch pipes 12B branched from this main air supply pipe 12A and each having a damper 14.
12C and 12D are branched, and one of them is 1
2B is connected to the charging hopper 3, and the remaining two 12C and 12D are connected to the first and second annular air supply chambers 8 and 9, respectively. 15 is an exhaust gas supply line that supplies combustion exhaust gas into the furnace wall 1;
Exhaust gas supply main pipe 15A and this exhaust gas supply main pipe 1
5A and a damper 16 respectively.
each having a tip end connected to each of the air supply branch pipes 1
Three exhaust gas supply branch pipes 15B, 15 connected downstream from the damper 14 of 2B, 12C, 12D
C, 15D. As the combustion exhaust gas, treated combustion exhaust gas taken out from the rear of the rotary kiln may be used, or combustion exhaust gas discharged from another incinerator may be used.
The amount of combustion air and combustion exhaust gas supplied to the input hood 2 and both annular air supply chambers 8 and 9 is controlled depending on the internal temperature of the furnace wall 1 corresponding to each location. . That is, first, second, and third temperature detectors 17, 18, and 19 are arranged in the drying zone A, the pyrolysis/gasification zone B, the flaming combustion zone C, and the post-combustion zone D, and The opening degree of the dampers 14 and 16 of each branch pipe 12B and 15B connected to the charging hood 2 is determined by the signal from the temperature detector 17, and the opening degree of the damper 14 and 16 of each branch pipe 12B and 15B connected to the charging hood 2 is determined by the signal from the second temperature detector 18. Air supply chamber 8
Damper 1 of each branch pipe 12C, 15C connected to
Further, the opening degrees of the dampers 14 and 16 of the branch pipes 12D and 15D connected to the second annular air supply chamber 9 are adjusted by the signal from the third temperature detector 19. be done.

上記構成において、投入ホツパー3から炉壁1
内に投入された廃棄物は、まず乾燥ゾーンA及び
熱分解・ガス化ゾーンBで気化乾燥されると共に
着火温度まで昇温された後、発炎燃焼ゾーンCで
発炎燃焼され、そして廃棄物の固定炭素分がおき
燃焼ゾーンDで燃焼された後、排出用フード5の
排出口6から焼却残渣として排出される。ところ
で、燃焼用一次空気は、投入用フード2から炉壁
1内に供給され、また燃焼用二次空気は第1、第
2環状空気供給室8,9から炉壁1内に供給され
る。そして、この時、発炎燃焼ゾーンCの温度が
高い場合には、自動的に、第2温度検出器18か
らの信号により、それに対応するダンパー16が
制御され、そして燃焼排ガスが発炎燃焼ゾーンC
内に供給されて温度制御即ち燃焼制御が容易に成
される。また、同時に空気用のダンパー14も一
諸に調節されて、O2濃度も制御される。
In the above configuration, from the input hopper 3 to the furnace wall 1
The waste introduced into the interior is first vaporized and dried in the drying zone A and the pyrolysis/gasification zone B, and the temperature is raised to the ignition temperature, and then flaming combustion is carried out in the flaming combustion zone C. After the fixed carbon content is burned in the combustion zone D, it is discharged from the discharge port 6 of the discharge hood 5 as incineration residue. By the way, primary air for combustion is supplied into the furnace wall 1 from the input hood 2, and secondary air for combustion is supplied into the furnace wall 1 from the first and second annular air supply chambers 8, 9. At this time, if the temperature of the flaming combustion zone C is high, the corresponding damper 16 is automatically controlled by the signal from the second temperature detector 18, and the combustion exhaust gas is transferred to the flaming combustion zone. C
Temperature control, that is, combustion control, can be easily achieved by supplying the fuel into the fuel tank. At the same time, the air dampers 14 are also adjusted to control the O 2 concentration.

勿論、乾燥ゾーンA及び熱分解・ガス化ゾーン
B並びにおき燃焼ゾーンDの温度が高い場合に
は、第1及び第3温度検出器17,19の信号に
よつて、上記と同様に、温度制御即ち燃焼制御が
成される。このように、ロータリキルンの炉壁内
の中間部即ち発炎燃焼ゾーンに燃焼排ガスを供給
して温度を制御するので、従来の燃焼用空気を供
給して燃焼の制御を行なう場合に比べて、極めて
容易に発炎燃焼ゾーンの温度上昇を防止でき、従
つて炉壁の損傷及びNOxの発生を確実に防ぐこ
とができると共に、安定した燃焼を容易に得るこ
とができる。また、すべての燃焼ゾーンにも燃焼
用二次空気を供給することができるので、性状変
化の激しい廃棄物に対しても、各ゾーンにおける
完全燃焼を図ることができる。
Of course, if the temperatures in the drying zone A, the pyrolysis/gasification zone B, and the combustion zone D are high, the temperature is controlled in the same manner as above based on the signals from the first and third temperature detectors 17 and 19. That is, combustion control is achieved. In this way, the temperature is controlled by supplying combustion exhaust gas to the middle part of the rotary kiln wall, that is, the flaming combustion zone, so compared to the conventional case where combustion air is supplied to control combustion. It is very easy to prevent the temperature rise in the flaming combustion zone, thereby reliably preventing damage to the furnace wall and the generation of NOx, and also easily achieving stable combustion. Further, since secondary air for combustion can be supplied to all combustion zones, complete combustion can be achieved in each zone even for waste whose properties change drastically.

ところで、上記実施例においては、燃焼用空気
が廃棄物と同じ方向に送られる並流式ロータリキ
ルン(着火性が良く発熱量が大きい廃棄物に適し
ている。)について説明したが、勿論、燃焼用空
気が廃棄物と逆方向に送られる向流式ロータリキ
ルン(含水率が多くて着火性の悪い廃棄物に適し
ている。)にも適用できる。この場合、第2図に
示すように、補助燃料噴出ノズル4は排出用フー
ド5に設けられると共に燃焼用一次空気は排出用
フード5下部内に供給される。
Incidentally, in the above embodiment, a parallel flow type rotary kiln (suitable for waste with good ignitability and a large calorific value) in which combustion air is sent in the same direction as the waste was explained, but of course, the combustion air is sent in the same direction as the waste. It can also be applied to counter-current rotary kilns in which the air is sent in the opposite direction to the waste (suitable for waste with high moisture content and poor ignitability). In this case, as shown in FIG. 2, the auxiliary fuel injection nozzle 4 is provided in the exhaust hood 5, and the primary combustion air is supplied into the lower part of the exhaust hood 5.

発明の効果 以上、本発明の方法によれば、ロータリキルン
の炉壁内の中間部即ち発炎燃焼ゾーンに燃焼排ガ
スを供給して温度を制御するので、従来の燃焼用
空気を供給して燃焼の制御を行なう場合に比べ
て、極めて容易に発炎燃焼ゾーンの温度上昇を防
止でき、従つて炉壁の損傷及びNOxの発生を確
実に防ぐことができると共に、安定した燃焼を容
易に得ることができる。
Effects of the Invention As described above, according to the method of the present invention, the temperature is controlled by supplying the combustion exhaust gas to the intermediate part in the furnace wall of the rotary kiln, that is, the flaming combustion zone. Compared to the case where control is performed, the temperature rise in the flaming combustion zone can be extremely easily prevented, and therefore, damage to the furnace wall and generation of NOx can be reliably prevented, and stable combustion can be easily obtained. I can do it.

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

第1図は本発明の一実施例の縦断面図、第2図
は他の実施例の縦断面図である。 1……炉壁、8……第1環状空気供給室、9…
…第2環状空気供給室、10……流量調整弁、1
1……空気取入管、12……空気供給ライン、1
3……送風フアン、14……ダンパー、15……
排ガス供給ライン、16……ダンパー、17……
第1温度検出器、18……第2温度検出器、19
……第3温度検出器。
FIG. 1 is a longitudinal cross-sectional view of one embodiment of the present invention, and FIG. 2 is a longitudinal cross-sectional view of another embodiment. 1... Furnace wall, 8... First annular air supply chamber, 9...
...Second annular air supply chamber, 10...Flow rate adjustment valve, 1
1...Air intake pipe, 12...Air supply line, 1
3...Blower fan, 14...Damper, 15...
Exhaust gas supply line, 16... damper, 17...
First temperature detector, 18...Second temperature detector, 19
...Third temperature detector.

Claims (1)

【特許請求の範囲】[Claims] 1 円筒状炉壁を有し、この炉壁の両開口端の一
方から他方に廃棄物が移送され、廃棄物の移送経
路の順に乾燥ゾーン、熱分解・ガス化ゾーン、発
炎燃焼ゾーン及びおき燃焼ゾーンが形成されるロ
ータリキルンにおいて、上記炉壁のいずれか一方
の開口端から燃焼用一次空気を供給すると共に、
炉壁中間部から燃焼排ガスを供給し、且つこの燃
焼排ガスの供給量を炉壁内の温度により制御する
ことを特徴とするロータリキルンにおける燃焼排
ガスを用いた燃焼制御方法。
1 It has a cylindrical furnace wall, and the waste is transferred from one of both open ends of this furnace wall to the other, and the waste transfer route includes a drying zone, a pyrolysis/gasification zone, a flaming combustion zone, and an oven. In a rotary kiln in which a combustion zone is formed, primary air for combustion is supplied from the open end of either one of the furnace walls, and
A combustion control method using combustion exhaust gas in a rotary kiln, characterized in that combustion exhaust gas is supplied from an intermediate part of the furnace wall, and the amount of the combustion exhaust gas supplied is controlled by the temperature inside the furnace wall.
JP27129384A 1984-12-22 1984-12-22 ROOTARIKIRUNNIOKERUNENSHOHAIGASUOMOCHIITANENSHOSEIGYOHOHO Expired - Lifetime JPH0247649B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP27129384A JPH0247649B2 (en) 1984-12-22 1984-12-22 ROOTARIKIRUNNIOKERUNENSHOHAIGASUOMOCHIITANENSHOSEIGYOHOHO

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP27129384A JPH0247649B2 (en) 1984-12-22 1984-12-22 ROOTARIKIRUNNIOKERUNENSHOHAIGASUOMOCHIITANENSHOSEIGYOHOHO

Publications (2)

Publication Number Publication Date
JPS61149720A JPS61149720A (en) 1986-07-08
JPH0247649B2 true JPH0247649B2 (en) 1990-10-22

Family

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Country Status (1)

Country Link
JP (1) JPH0247649B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
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JPH07243629A (en) * 1994-02-28 1995-09-19 Hiroshi Iwasaki Waste incineration method and incinerator
CN102644926A (en) * 2011-02-21 2012-08-22 上海电气自动化设计研究所有限公司 Loop control method of medical garbage combustion rotary kiln based on DCS (Distributed Control System)
JP6126384B2 (en) * 2013-01-17 2017-05-10 日新製鋼株式会社 Rotary kiln
CN107806641A (en) * 2017-10-31 2018-03-16 光大环保技术研究院(南京)有限公司 Rotary kiln for waste incineration

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Publication number Priority date Publication date Assignee Title
EP4064054A1 (en) 2021-03-24 2022-09-28 Fujifilm Business Innovation Corp. Information processing device, program and information processing method

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