JPH03267611A - Fluidized-bed combustion method for waste - Google Patents

Fluidized-bed combustion method for waste

Info

Publication number
JPH03267611A
JPH03267611A JP6602590A JP6602590A JPH03267611A JP H03267611 A JPH03267611 A JP H03267611A JP 6602590 A JP6602590 A JP 6602590A JP 6602590 A JP6602590 A JP 6602590A JP H03267611 A JPH03267611 A JP H03267611A
Authority
JP
Japan
Prior art keywords
damper
air
waste
fluidized bed
opened
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.)
Granted
Application number
JP6602590A
Other languages
Japanese (ja)
Other versions
JP2801942B2 (en
Inventor
Hiroaki Harada
裕昭 原田
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.)
Mitsui Engineering and Shipbuilding Co Ltd
Original Assignee
Mitsui Engineering and Shipbuilding 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 Mitsui Engineering and Shipbuilding Co Ltd filed Critical Mitsui Engineering and Shipbuilding Co Ltd
Priority to JP2066025A priority Critical patent/JP2801942B2/en
Priority to CA002036747A priority patent/CA2036747C/en
Priority to US07/657,848 priority patent/US5105748A/en
Priority to DE69101858T priority patent/DE69101858T2/en
Priority to ES91301381T priority patent/ES2056572T3/en
Priority to EP91301381A priority patent/EP0443850B1/en
Priority to AT9191301381T priority patent/ATE105397T1/en
Publication of JPH03267611A publication Critical patent/JPH03267611A/en
Application granted granted Critical
Publication of JP2801942B2 publication Critical patent/JP2801942B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Abstract

PURPOSE:To allow wastes to completely burn, prevent CO gas etc., from being discharged from a furnace and improve recovery ratio of steam in the case of a boiler etc., by providing an air feed rate control means including a damper in each diffuser pipe and by opening and closing each of the dampers at specific intervals in such a manner that the ratio of air flow rate to minimum fluidization air rate falls within a specific range when the damper is opened or closed. CONSTITUTION:A damper is provided in each diffuser pipe 5 for feeding primary air for combustion. The dampers are opened and closed in such a manner that the ratio Uo/Umf, wherein flow rate of primary air is Uo and minimum air rate for fluidization Umf, falls in the range of 1.4-4 when the damper is opened and 0.5-2 when closed at intervals of 1-10 seconds and 10-100 seconds respectively. In the device, air flow rate is controlled in such a manner that at first a valve 13 is opened to feed minimum quantity of air required for combustion to each of the diffuser pipes from a line 9A, in which primary air corresponding to a ratio above the lower limit of Uo/Umf at the closing of damper is supplied and further damper control valve 7 for each diffuser pipe 5 is adjusted so that Uo/Umf comes in the range aboded by oblique lines when the damper is opened or closed. As a result, in the case of a boiler etc., steam is stably produced.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、廃棄物の流動層燃焼方法に関し、特に都市ご
み等のように経時的に量および質が異なる可燃物を流動
層の形成下に燃焼させる燃焼方法に関する。
[Detailed Description of the Invention] [Industrial Application Field] The present invention relates to a method for fluidized bed combustion of waste, and in particular, the present invention relates to a fluidized bed combustion method for waste, and in particular, a method for burning combustible materials such as municipal waste, which varies in quantity and quality over time, under the formation of a fluidized bed. This relates to a combustion method for burning.

〔従来の技術] 従来、都市ごみ等を焼却する流動層燃焼炉の問題点の一
つとして、供給されるごみの量および質の時間変動に伴
って排ガス中に未燃分が残り、黒煙または一酸化炭素等
の有害ガスを生成するという問題がある。これは炉の規
模が小さくなる程、ごみの大小の影響が大きく、大きな
問題となる。
[Prior art] One of the problems with conventional fluidized bed combustion furnaces for incinerating municipal waste, etc. is that unburned matter remains in the exhaust gas due to time fluctuations in the quantity and quality of the supplied waste, resulting in black smoke. Alternatively, there is a problem in that harmful gases such as carbon monoxide are generated. This becomes a bigger problem as the size of the furnace becomes smaller, as the influence of the size of the waste becomes greater.

これを解決するために、供給されるごみの量および賞に
応じて予め空気量その他を先行制御する方法や、ごみを
細かく破砕して定量的に炉内へ投入する方法が提案され
ているが、設計上の制約が多(、実用化は困難であった
In order to solve this problem, methods have been proposed in which the amount of air and other factors are controlled in advance according to the amount of waste to be supplied and the award, and methods in which the waste is crushed into small pieces and quantitatively fed into the furnace. , there were many design constraints (and it was difficult to put it into practical use).

上記流動層焼却における未燃分の発生は、流動層炉にお
いては燃焼速度がきわめて速いために起こる問題であり
、また古(から用いられているストーカ−炉などの機械
炉においては、コンベア等によりごみがゆっくりと火炉
内に供給されるので、未燃分の発生は比較的少なかった
The generation of unburned matter in the fluidized bed incineration is a problem that occurs because the combustion rate is extremely high in fluidized bed furnaces, and in mechanical furnaces such as stoker furnaces that have been used since ancient times. Since the waste was slowly fed into the furnace, the generation of unburned material was relatively small.

〔発明が解決しようとする課題〕[Problem to be solved by the invention]

本発明の目的は、上記流動層燃焼装置に特有の問題を解
決し、流動層炉内に投入する廃棄物の量、質の時間的変
動があっても、これに左右されずに緩慢な燃焼速度で廃
棄物を完全に燃焼させ、炉外へのCOガス等の排出を防
止し、またボイラ等に用いた場合の蒸気回収率も向上さ
せることができる流動層燃焼方法を提供することにある
The purpose of the present invention is to solve the problems specific to the fluidized bed combustion apparatus described above, and to achieve slow combustion regardless of temporal fluctuations in the quantity and quality of waste input into the fluidized bed furnace. The purpose of the present invention is to provide a fluidized bed combustion method that can completely burn waste at a high speed, prevent CO gas, etc. from being discharged outside the furnace, and improve the steam recovery rate when used in a boiler, etc. .

〔課題を解決するための手段〕[Means to solve the problem]

本発明は、流動層部に1次空気の供給ノズルを多数有す
る散気管を多数配列した流動層炉を用い、該散気管から
1次空気を供給して廃棄物を燃焼させ、さらに空塔部で
2次空気の供給下に燃焼ガス中の未燃分を燃焼させる廃
棄物の流動層燃焼方法において、前記各散気管に開閉ダ
ンパを含む空気供給量調節手段を設け、空気流量U0と
流動化最少空気量U+efとの比U、/U、、がダンパ
開時に1゜4〜4、ダンパ閉時に0.5〜2の範囲にな
るように、それぞれ1〜10秒および10〜100秒の
間隔でダーンパ開閉を行うことを特徴とする。
The present invention uses a fluidized bed furnace in which a large number of aeration tubes each having a large number of primary air supply nozzles are arranged in a fluidized bed section, supplies primary air from the aeration tubes to combust waste, and furthermore, the empty column section In the fluidized bed combustion method for waste in which unburned content in the combustion gas is combusted under the supply of secondary air, each diffuser pipe is provided with an air supply amount adjusting means including an opening/closing damper, and the air flow rate U0 and fluidization are adjusted. At intervals of 1 to 10 seconds and 10 to 100 seconds, respectively, so that the ratio U, /U, with the minimum air amount U + ef is in the range of 1°4 to 4 when the damper is open and 0.5 to 2 when the damper is closed. It is characterized by opening and closing the damper.

本発明において、燃焼される可燃物は、都市ごみ等のよ
うに経時的に量および質が異なるもので、嵩密度、水分
量、発熱量等が経時的に変化するものが好適である。都
市ごみの他にこのように看および質が異なる可燃物であ
ればいずれも本発明を通用することができ、これらの例
としては汚泥、鉱石等が挙げられる。
In the present invention, the combustible material to be burned is one whose quantity and quality change over time, such as municipal waste, and preferably one whose bulk density, moisture content, calorific value, etc. change over time. In addition to municipal waste, the present invention can be applied to any combustible material having different appearance and quality, examples of which include sludge, ore, and the like.

本発明においては、燃焼用1次空気を供給する散気管に
開閉ダンパを設け、1次空気の流量U0と流動化最少空
気量Umfとの比Uo−/U+erがダンパ開時に1.
4〜4、ダンパ閉時に0.5〜2の範囲になるように、
それぞれ1〜10秒および10〜100秒の間隔でダン
パ開閉を行うものであるが、上記ダンパ開の時間が1秒
未満では流動化用空気による攪拌が不充分であり、また
ダンパ開の時間が10秒を越えると、燃焼に寄与する空
気が過剰になり、CO低減効果が得られなくなる。また
ダンパ開時のUO/U、、が4を越えると流動化用空気
を過剰に供給することになり、運転コストが上昇し、ま
た燃焼ガスに灰が同伴され易くなる。
In the present invention, an opening/closing damper is provided in the diffuser pipe that supplies primary air for combustion, and the ratio Uo-/U+er between the flow rate U0 of the primary air and the minimum fluidizing air amount Umf is 1.0 when the damper is open.
4 to 4, so that it is in the range of 0.5 to 2 when the damper is closed.
The damper is opened and closed at intervals of 1 to 10 seconds and 10 to 100 seconds, respectively. However, if the damper is opened for less than 1 second, stirring by the fluidizing air is insufficient, and the damper is opened for less than 1 second. If it exceeds 10 seconds, there will be too much air contributing to combustion, and the CO reduction effect will no longer be obtained. Moreover, if UO/U when the damper is open exceeds 4, an excessive amount of fluidizing air will be supplied, increasing operating costs and making it easier for ash to be entrained in the combustion gas.

方、ダンパ開時のu0/Umfが1.4未満の場合は流
動層の攪拌効果が充分ではなくなる。さらにダンパ閉の
場合、その閉止時間が10秒未満ではCO低減効果が充
分でなく、また100秒を越えると、流動層内に温度む
らを生じ、局部的な過熱が進んでクリンカ等を生じる。
On the other hand, if u0/Umf when the damper is open is less than 1.4, the stirring effect of the fluidized bed will not be sufficient. Further, when the damper is closed, if the damper is closed for less than 10 seconds, the CO reduction effect will not be sufficient, and if it exceeds 100 seconds, temperature unevenness will occur in the fluidized bed, and local overheating will progress, resulting in clinker and the like.

さらにダンパ閉時のU、/U、、が2を越えるとCO低
減効果がなくなり、また0、 5未満では廃棄物の燃焼
に必要な空気量を確保できなくなる。上述のダンパ開閉
時間とUs /Umf17)好マシイ範囲は、U、/v
、t2.o 〜3.0でダンパ開3〜7秒、U、/U、
、が0.5〜1゜5でダンパ閉30〜60秒である。
Furthermore, if U, /U, when the damper is closed exceeds 2, the CO reduction effect will be lost, and if it is less than 0.5, it will not be possible to secure the amount of air necessary for combustion of waste. The above damper opening/closing time and Us /Umf17) The preferred range is U, /v
, t2. o ~3.0, damper open 3~7 seconds, U, /U,
, is 0.5 to 1°5 and the damper is closed for 30 to 60 seconds.

以下、本発明を図面によりさらに詳細に説明する。Hereinafter, the present invention will be explained in more detail with reference to the drawings.

〔実施例] 第1図は、本発明を実施するための流動層燃焼装置の一
例を示す平面断面図、第2図はその正面断面図である。
[Example] FIG. 1 is a plan sectional view showing an example of a fluidized bed combustion apparatus for carrying out the present invention, and FIG. 2 is a front sectional view thereof.

この装置は、流動層燃焼装置の炉本体1と、該炉本体l
内に1次空気を送入するためのブロア15と、該ブロア
15により送入される1次空気を管8.9、バルブ11
および7を介して炉1内に導入する散気管5を有してお
り、該散気管5には、それぞれ管8がら分岐された、バ
ルブ13を通してオフ時の空気を導入するためのバイパ
ス管9Aが付設されている。散気管5のオン−オフ制御
はバルブ7(制御弁)により所定のパターンに従ってオ
ン−オフを繰返し、一方管9Aにはバルブ13を介して
上記オン−オフにががわらず、常に一定量の空気が供給
される。なおオフ時の空気の供給は、第1図に示すよう
なバイパス管9Aを用いずに、第3図に示すようにロー
リミツター付きの制御弁7Aを管9にそれぞれ設け、第
1図と同様に制御してもよい。この場合制御弁7Aのオ
フ時には、ローリミツターがはたらき、常に一定量の空
気が流れることになる。
This device includes a furnace body 1 of a fluidized bed combustion apparatus, and a furnace body l.
A blower 15 for feeding primary air into the interior, and a pipe 8.9 and a valve 11 for the primary air fed by the blower 15.
and a bypass pipe 5 for introducing air into the furnace 1 through a valve 13 and a bypass pipe 9A branched from the pipe 8, respectively, for introducing air during off-time through a valve 13. is attached. The on-off control of the aeration pipe 5 is performed by repeatedly turning on and off according to a predetermined pattern using a valve 7 (control valve), while a constant amount of air is always supplied to the pipe 9A via a valve 13 regardless of the above-mentioned on-off operation. is supplied. Note that the air supply during the off-state is carried out in the same manner as in Fig. 1 by providing control valves 7A with low limiters in each pipe 9 as shown in Fig. 3, instead of using the bypass pipe 9A as shown in Fig. 1. May be controlled. In this case, when the control valve 7A is turned off, the low limiter works and a constant amount of air always flows.

第1図の装置における空気量制御は、まず弁13を開け
てライン9Aより各散気管5に燃焼に最低限必要な空気
量、すなわち第4図に示すダンパ閉時のUn /U−r
の下限より上に相当する1次空気を供給しておき、さら
に各散気管5のダンパ制開弁7を調節し、ダンパ開時お
よびダンパ閉時にU o / U−tが第4図に示す斜
線の範囲内に入るように調整する。なお、第4図中の黒
丸プロットはこのようにして実施したデータの一例であ
る。
The air amount control in the device shown in FIG. 1 is performed by first opening the valve 13 and sending the line 9A to each diffuser pipe 5 with the minimum amount of air required for combustion, that is, Un /U-r when the damper is closed as shown in FIG. 4.
The primary air corresponding to above the lower limit of is supplied, and the damper control valve 7 of each diffuser pipe 5 is adjusted so that Uo/Ut is as shown in Fig. 4 when the damper is open and when the damper is closed. Adjust so that it falls within the shaded range. Note that the black circle plot in FIG. 4 is an example of data obtained in this manner.

その他の流動層の条件としては、流動媒体である砂の平
均径は小さい方が好ましいが、一般には1.5〜0.3
鵬、好ましくは0.3〜0.8−である。
As for other conditions for the fluidized bed, it is preferable that the average diameter of the sand that is the fluidizing medium is small, but it is generally 1.5 to 0.3.
0.3 to 0.8, preferably 0.3 to 0.8.

なお流動化用1次空気には適当な割合で燃焼排ガスを混
入してもよい。
Incidentally, the primary air for fluidization may be mixed with combustion exhaust gas in an appropriate proportion.

本発明においては、廃棄物の流動層燃焼方法に用いられ
る種々の手段、方法を併用することができる。例えば流
動層炉の空塔部に2次空気との混合促進手段、例えば格
子状物、管列等を設けたり、流動層温度を検知して1次
空気の供給量を制御したり、また炉内圧、火炎、炉出口
酸素量を検知して廃棄物の供給量を制御する等の方法を
併用することができる。
In the present invention, various means and methods used in fluidized bed combustion methods for waste can be used in combination. For example, means for promoting mixing with secondary air, such as grids or tube rows, may be provided in the cavity of a fluidized bed furnace, or the supply amount of primary air may be controlled by detecting the temperature of the fluidized bed, or Methods such as controlling the amount of waste supplied by detecting internal pressure, flame, and the amount of oxygen at the furnace outlet can be used in combination.

[発明の効果〕 本発明によれば、簡単なオン−オフ制御方式により流動
層炉を用いて廃棄物をマイルド燃焼させることができる
。このため、小規模の燃焼炉でも、燃焼ガス中に未燃分
がほとんど含まれず、黒煙等の発生がなく、安定した条
件で運転することができ、ボイラ等の場合には蒸気発生
量が安定化する。
[Effects of the Invention] According to the present invention, waste can be mildly combusted using a fluidized bed furnace with a simple on-off control system. For this reason, even small-scale combustion furnaces can be operated under stable conditions with almost no unburned matter in the combustion gas and no black smoke, and in the case of boilers, etc., the amount of steam generated is small. Stabilize.

また空気比が通常の流動層燃焼装置よりも低めに設定す
ることができ・るので、排ガス量が少なくなる。さらに
可燃物の量、譬によらずに安定した燃焼を行うことがで
きるので、都市ごみ等の流動層焼却の場合に通常前置さ
れる破砕機等の予備処理装置は不要になる。また機械炉
の場合に生じるようなヒートスポット、溶着等の問題も
燃焼条件を選択することによって容易に回避することが
でき、運転の許容範囲も広いことから、可燃物に対する
燃焼条件の選択の範囲も大幅に拡大され、大、中、小い
ずれの規模の流動層燃焼炉においても適用することがで
きる。
Additionally, since the air ratio can be set lower than in a normal fluidized bed combustion apparatus, the amount of exhaust gas is reduced. Furthermore, since stable combustion can be performed regardless of the amount of combustible material, a pretreatment device such as a crusher, which is normally installed in the case of fluidized bed incineration of municipal waste, becomes unnecessary. In addition, problems such as heat spots and welding that occur in mechanical furnaces can be easily avoided by selecting combustion conditions, and the permissible operating range is wide, so there is a wide range of combustion conditions to choose from for combustible materials. It has also been greatly expanded and can be applied to large, medium, and small scale fluidized bed combustion furnaces.

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

第1図は、本発明を実施するための流動層燃焼装置の一
例を示す平面断面図、第2図は、その正面断面図、第3
図は、本発明の他の実施例を示す流動層燃焼装置の平面
断面図、第4図は、本発明の燃焼方法における数値範囲
を示す図である。 1・・・炉本体、2・・・燃焼室、3・・・流動層、4
・・・散気板、5・・・散気管、6・・・風箱、7・・
・バルブ(制御弁)、7A・・・制御弁、8.9.9A
・・・管、10・・・隔壁、11.13・・・パルプ、
15・・・1次空気ブロア。 第1図
FIG. 1 is a plan sectional view showing an example of a fluidized bed combustion apparatus for carrying out the present invention, FIG. 2 is a front sectional view thereof, and FIG.
This figure is a plan sectional view of a fluidized bed combustion apparatus showing another embodiment of the present invention, and FIG. 4 is a diagram showing numerical ranges in the combustion method of the present invention. 1... Furnace body, 2... Combustion chamber, 3... Fluidized bed, 4
... air diffuser plate, 5... air diffuser pipe, 6... wind box, 7...
・Valve (control valve), 7A...Control valve, 8.9.9A
... tube, 10 ... partition wall, 11.13 ... pulp,
15...Primary air blower. Figure 1

Claims (1)

【特許請求の範囲】[Claims] (1)流動層部に1次空気の供給ノズルを多数有する散
気管を多数配列した流動層炉を用い、該散気管から1次
空気を供給して廃棄物を燃焼させ、さらに空塔部で2次
空気の供給下に燃焼ガス中の未燃分を燃焼させる廃棄物
の流動層燃焼方法において、前記各散気管に開閉ダンパ
を含む空気供給量調節手段を設け、空気流量U_oと最
少流動化空気量U_m_fとの比U_o/U_m_fが
ダンパ開時に1.4〜4、ダンパ閉時に0.5〜2の範
囲になるように、それぞれ1〜10秒および10〜10
0秒の間隔でダンパ開閉を行うことを特徴とする廃棄物
の流動層燃焼方法。
(1) Using a fluidized bed furnace in which a large number of diffuser tubes each having a large number of supply nozzles for primary air are arranged in the fluidized bed section, the primary air is supplied from the diffuser tubes to burn the waste, and then the waste is combusted in the empty tower section. In a waste fluidized bed combustion method in which unburned content in combustion gas is combusted under the supply of secondary air, each diffuser pipe is provided with an air supply amount adjusting means including an opening/closing damper to adjust the air flow rate U_o and the minimum fluidization. 1 to 10 seconds and 10 to 10 seconds, respectively, so that the ratio U_o/U_m_f with the air amount U_m_f is in the range of 1.4 to 4 when the damper is open and 0.5 to 2 when the damper is closed.
A fluidized bed combustion method for waste, characterized by opening and closing a damper at intervals of 0 seconds.
JP2066025A 1990-02-22 1990-03-16 Fluidized bed combustion of waste Expired - Lifetime JP2801942B2 (en)

Priority Applications (7)

Application Number Priority Date Filing Date Title
JP2066025A JP2801942B2 (en) 1990-03-16 1990-03-16 Fluidized bed combustion of waste
US07/657,848 US5105748A (en) 1990-02-22 1991-02-20 Fluidized bed combustion method for burning wastes
CA002036747A CA2036747C (en) 1990-02-22 1991-02-20 Fluidized bed combustion method for burning wastes
ES91301381T ES2056572T3 (en) 1990-02-22 1991-02-21 COMBUSTION METHOD AND APPARATUS IN FLUIDIZED BED TO BURN WASTE.
DE69101858T DE69101858T2 (en) 1990-02-22 1991-02-21 Apparatus for burning waste in a fluidized bed.
EP91301381A EP0443850B1 (en) 1990-02-22 1991-02-21 Fluidized bed combustion apparatus for burning wastes
AT9191301381T ATE105397T1 (en) 1990-02-22 1991-02-21 APPARATUS FOR INCINERATING WASTE IN A FLUIDIZED BED.

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2066025A JP2801942B2 (en) 1990-03-16 1990-03-16 Fluidized bed combustion of waste

Publications (2)

Publication Number Publication Date
JPH03267611A true JPH03267611A (en) 1991-11-28
JP2801942B2 JP2801942B2 (en) 1998-09-21

Family

ID=13303969

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2066025A Expired - Lifetime JP2801942B2 (en) 1990-02-22 1990-03-16 Fluidized bed combustion of waste

Country Status (1)

Country Link
JP (1) JP2801942B2 (en)

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62182515A (en) * 1986-02-05 1987-08-10 Ishikawajima Harima Heavy Ind Co Ltd Stable burning method for fluidized bed furnace

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62182515A (en) * 1986-02-05 1987-08-10 Ishikawajima Harima Heavy Ind Co Ltd Stable burning method for fluidized bed furnace

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