JP4831309B2 - Waste treatment facility and waste treatment method - Google Patents
Waste treatment facility and waste treatment method Download PDFInfo
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- JP4831309B2 JP4831309B2 JP2005365776A JP2005365776A JP4831309B2 JP 4831309 B2 JP4831309 B2 JP 4831309B2 JP 2005365776 A JP2005365776 A JP 2005365776A JP 2005365776 A JP2005365776 A JP 2005365776A JP 4831309 B2 JP4831309 B2 JP 4831309B2
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- 239000002699 waste material Substances 0.000 title claims description 36
- 238000000034 method Methods 0.000 title claims description 20
- 239000000779 smoke Substances 0.000 claims description 27
- 238000002485 combustion reaction Methods 0.000 claims description 23
- 230000002265 prevention Effects 0.000 claims description 10
- 238000010438 heat treatment Methods 0.000 claims description 4
- 238000011144 upstream manufacturing Methods 0.000 claims description 4
- 238000007664 blowing Methods 0.000 claims description 2
- 239000007789 gas Substances 0.000 description 48
- 230000000694 effects Effects 0.000 description 8
- 230000005587 bubbling Effects 0.000 description 6
- 238000010586 diagram Methods 0.000 description 5
- 239000000446 fuel Substances 0.000 description 5
- 230000006698 induction Effects 0.000 description 4
- 239000010802 sludge Substances 0.000 description 4
- 238000004056 waste incineration Methods 0.000 description 4
- 239000007788 liquid Substances 0.000 description 3
- 230000005611 electricity Effects 0.000 description 2
- 238000010248 power generation Methods 0.000 description 2
- 239000002918 waste heat Substances 0.000 description 2
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 239000000567 combustion gas Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 239000000295 fuel oil Substances 0.000 description 1
- 239000003350 kerosene Substances 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 239000010801 sewage sludge Substances 0.000 description 1
- 239000007921 spray Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 239000002912 waste gas Substances 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
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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
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E20/00—Combustion technologies with mitigation potential
- Y02E20/34—Indirect CO2mitigation, i.e. by acting on non CO2directly related matters of the process, e.g. pre-heating or heat recovery
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- Air Supply (AREA)
- Fluidized-Bed Combustion And Resonant Combustion (AREA)
- Chimneys And Flues (AREA)
Description
本発明は、廃棄物の焼却処理技術に属し、特には、焼却炉および過給機を備えた廃棄物処理設備および過給機および焼却炉を用いた廃棄物処理方法に関する。 The present invention relates to waste incineration technology, and more particularly, to a waste treatment facility including an incinerator and a supercharger, and a waste treatment method using the supercharger and the incinerator.
図2および図3に、従来の廃棄物焼却設備のブロック図を示す。
従来の廃棄物X10の焼却処理設備101では、廃棄物X10と適宜の燃料X20との焼却処理に伴って焼却炉20から排出される排ガスX40を予熱器30に導いて、焼却炉20に供給する燃焼用圧縮空気X30’の加温に用いることが行われる。
また、廃棄物X10の焼却処理設備101では、焼却炉20からの排ガスX40を排ガス湿式処理装置70で処理することがあり、この場合、排煙筒(煙突)90から排出される排ガスの白煙防止処理が行なわれることが一般的となっている。そして、白煙防止の方法としては、排ガス湿式処理70の前段に白煙防止用の空気予熱器50を設け、この予熱器50からの加熱圧縮空気X50’を湿式処理された排ガスに混合することにより行われる。
そして、従来設備101では、これらの燃焼用圧縮空気X30’用の予熱器30や白煙防止用の予熱器50に対しては、ブロアB1,B2を用いて熱交換用の空気X30,X50を供給している。
しかし、ブロアB1,B2の運転には、多大な電力が必要であるため削減が求められる。
そこで、焼却炉の排ガスを廃熱ボイラで蒸気として回収し、発電して得られる電力の一部をブロアの動力源として利用することが試みられている。
また、特に、図3に示す加圧流動床式焼却炉20を採用する従来の廃棄物焼却設備101では、焼却炉20からの高温高圧排ガスX40を過給機40に導入して、加圧空気を発生させて燃焼用空気等に利用することによりブロアB1を用いないようにすることも試みられている。
In the conventional
In addition, in the
In the
However, since the operation of the blowers B1 and B2 requires a large amount of power, reduction is required.
Thus, it has been attempted to recover the exhaust gas from the incinerator as steam with a waste heat boiler and use a part of the electric power obtained by generating electricity as a power source for the blower.
In particular, in the conventional
しかしながら、焼却炉の排ガスを利用して発電する方法は、廃熱ボイラおよび蒸気タービン発電設備等の種々の設備が必要となり、設備面および維持管理面のコストが高いため、大規模設備ではエネルギー回収による経済的効果が得られるものの、その他の多くの中小規模設備ではかえって経済的負担が悪化するため適するものではない。
また、図3の方式は、高温高圧の排ガスX41を過給機40に導入する必要があるため、加圧式の燃焼炉20が必須要件となる。このため、常圧近傍の焼却炉には適さない。
そこで、本発明の主たる課題は、常圧式の焼却炉であると加圧式の焼却炉であるとにかかわらず適用することができ、しかも、燃焼用圧縮空気や白煙防止用圧縮空気を生成し予熱器に供給するためのブロアを必要とせず、エネルギー効率に優れる、廃棄物焼却設備および処理方法を提供することにある。
However, the method of generating electricity using the exhaust gas from the incinerator requires various facilities such as a waste heat boiler and steam turbine power generation equipment, and the cost of equipment and maintenance is high. However, many other small and medium-sized facilities are not suitable because the economic burden is worsened.
Further, in the method of FIG. 3, since it is necessary to introduce the high-temperature and high-pressure exhaust gas X41 into the supercharger 40, the pressurized
Therefore, the main problem of the present invention can be applied regardless of whether it is a normal pressure type incinerator or a pressure type incinerator, and also generates compressed air for combustion and compressed air for white smoke prevention. An object of the present invention is to provide a waste incineration facility and a processing method that do not require a blower for supplying a preheater and are excellent in energy efficiency.
上記課題を解決した本発明および作用効果は次記のとおりである。
<請求項1記載の発明>
流動床式焼却炉と、流動床式焼却炉からの排ガスとの連続的なガス−ガス熱交換により、流動床式焼却炉に供給する燃焼用圧縮空気の予熱を行う第1の予熱器と、
第1の予熱器で加熱されて流動床式焼却炉に向かう燃焼用圧縮空気によってタービンが回転させられ、この回転によってコンプレッサで前記第1の予熱器に供給する圧縮空気の生成および送風を行う、第1の過給機と、
前記第1の予熱器より上流側に設けられ運転開始時に前記タービンを回転させる第1の始動用空気供給装置とを、備える、
ことを特徴とする廃棄物処理設備。
The present invention and effects obtained by solving the above problems are as follows.
<Invention of Claim 1>
A first preheater that preheats compressed air for combustion supplied to the fluidized bed incinerator by continuous gas-gas heat exchange between the fluidized bed incinerator and the exhaust gas from the fluidized bed incinerator;
The turbine is rotated by compressed air for combustion that is heated by the first preheater and goes to the fluidized bed incinerator, and by this rotation, the compressed air supplied to the first preheater is generated and blown by the compressor. A first supercharger;
A first air supply device for starting that is provided upstream of the first preheater and rotates the turbine at the start of operation ;
Waste treatment facility characterized by that.
(作用効果)
第1予熱器に供給する圧縮空気を生成するためのブロアが不要となる。また、当該圧縮空気得るために電力不要の過給機を用いることとしたため、電力削減が達成される。
(Function and effect)
A blower for generating compressed air to be supplied to the first preheater is not necessary. Further, since a supercharger that does not require power is used to obtain the compressed air, power reduction is achieved.
<請求項2記載の発明>
流動床式焼却炉からの排ガスの湿式処理を行う排ガス湿式処理装置と、
流動床式焼却炉からの排ガスとの連続的なガス−ガス熱交換により、前記湿式処理装置で処理された排ガスに混合する圧縮空気を加熱するための第2の予熱器と、
第2の予熱器で加熱された加熱圧縮空気によってタービンが回転させられ、この回転によってコンプレッサで前記第2の予熱器に供給する圧縮空気の生成および送風を行う、第2の過給機とを備える、
請求項1記載の廃棄物処理設備。
<Invention of Claim 2>
An exhaust gas wet processing apparatus for performing wet processing of exhaust gas from a fluidized bed incinerator;
A second preheater for heating the compressed air to be mixed with the exhaust gas treated by the wet treatment device by continuous gas-gas heat exchange with the exhaust gas from the fluidized bed incinerator;
A turbine is rotated by heated compressed air heated by the second preheater, and a second supercharger that generates and blows compressed air to be supplied to the second preheater by the compressor by this rotation. Prepare
The waste treatment facility according to claim 1.
(作用効果)
白煙防止処理がなされるとともに、第2予熱器に供給する圧縮空気を生成するためのブロアが不要となる。また、当該圧縮空気得るために電力不要の過給機を用いることとしたため、電力削減が達成される。
(Function and effect)
A white smoke prevention process is performed, and a blower for generating compressed air to be supplied to the second preheater becomes unnecessary. Further, since a supercharger that does not require power is used to obtain the compressed air, power reduction is achieved.
<請求項3記載の発明>
流動床式焼却炉から排出される排ガスによる連続的なガス−ガス熱交換によって、第1の予熱器にて前記流動床式焼却炉に供給する燃焼用圧縮空気の予熱を行い、
前記第1の予熱器より上流側に設けられた第1の始動用空気供給装置により、第1のターボ過給機のタービンの回転を始動させ、
前記第1の予熱器で加熱されて流動床式焼却炉に向かう燃焼用圧縮空気を、第1のターボ過給機に供給して前記タービンを継続的に回転させるとともに、当該過給機のコンプレッサにて前記第1の予熱器に供給する圧縮空気の生成および送風を行う、
ことを特徴とする廃棄物処理方法。
<Invention of Claim 3>
Preheating the compressed air for combustion supplied to the fluidized bed incinerator by a first preheater by continuous gas-gas heat exchange with the exhaust gas discharged from the fluidized bed incinerator;
The first turbocharger turbine is started to rotate by a first start-up air supply device provided upstream of the first preheater ,
The combustion compressed air towards the fluidized bed incinerator is heated by the first preheater, causes continuously rotating the turbine is supplied to the first turbocharger, the compressor of the turbocharger Generating and blowing compressed air to be supplied to the first preheater at
A waste treatment method characterized by the above.
(作用効果)
請求項1記載の発明と同様の作用効果が得られる。
(Function and effect)
The same effect as that of the first aspect of the invention can be obtained.
<請求項4記載の発明>
前記排ガス湿式処理装置で処理された排ガスに対して加熱した圧縮空気を混合する白煙防止処理を行うにあたり、
この白煙防止処理に用いる圧縮空気の加熱を、流動床式焼却炉から排出される排ガスを熱源とする第2の予熱器を用いて連続的なガス−ガス熱交換により行ない、かつ、
前記第2の予熱器で加熱された加熱圧縮空気を第2の過給機に供給して前記タービンを継続的に回転させるとともに、当該過給機のコンプレッサにて前記第2の予熱器に供給する圧縮空気の生成および送風を行う、
請求項3記載の廃棄物処理方法。
<Invention of Claim 4>
In performing the white smoke prevention treatment of mixing heated compressed air to the exhaust gas treated by the exhaust gas wet treatment apparatus,
The compressed air used for the white smoke prevention treatment is heated by continuous gas-gas heat exchange using a second preheater using the exhaust gas discharged from the fluidized bed incinerator as a heat source, and
The heated compressed air heated by the second preheater is supplied to the second supercharger to continuously rotate the turbine, and supplied to the second preheater by the compressor of the supercharger. Generate and blow compressed air,
The waste disposal method according to claim 3.
(作用効果)
請求項2記載の発明と同様の作用効果が得られる。
(Function and effect)
The same effect as that of the invention of claim 2 can be obtained.
本発明によれば、流動床式焼却炉で発生する排ガスと熱交換を行った圧縮空気で過給機のタービンを回転させるとともにコンプレッサで圧縮空気を得る。そして、この圧縮空気を予熱器に供給する。従って、従来、当該圧縮空気の生成するためにブロアを要し、またこの運転のための電力を要していたところ、このブロア(電力)が不要となり、経済的に優れるシステムである。
また、既存の設備に過給機を設置するだけでよいため簡易に施工できる。さらには、従来の電力回収方法による省エネルギー化と異なり、発電設備などが不要で、小中規模設備においても、省エネルギーの効果を得ることができる。
According to the present invention, the turbine of the supercharger is rotated by the compressed air that has exchanged heat with the exhaust gas generated in the fluidized bed incinerator, and the compressed air is obtained by the compressor. Then, this compressed air is supplied to the preheater. Therefore, conventionally, a blower is required to generate the compressed air, and electric power for this operation is required. However, this blower (electric power) is unnecessary, and this is an economically superior system.
Moreover, since it is only necessary to install a supercharger in existing equipment, it can be easily constructed. Furthermore, unlike the energy saving by the conventional power recovery method, no power generation equipment is required, and an energy saving effect can be obtained even in small and medium scale equipment.
以下、図面を参照して、本発明に係る汚泥処理設備および方法の一実施形態について説明する。
図1は、本発明に係る廃棄物処理方法を用いる廃棄物処理設備1のブロック図である。この図において、符号2は気泡流動床炉(燃焼炉)、3は第1予熱器(熱交換器)、4は第1過給機(ターボチャージャー)、5は第2予熱器(熱交換器)、6は第2過給機(ターボチャージャー)、7は排ガス湿式処理装置、8は誘引ファン、9は排煙筒、10,11は始動用空気供給装置である。
Hereinafter, an embodiment of a sludge treatment facility and method according to the present invention will be described with reference to the drawings.
FIG. 1 is a block diagram of a waste treatment facility 1 that uses the waste treatment method according to the present invention. In this figure, reference numeral 2 is a bubble fluidized bed furnace (combustion furnace), 3 is a first preheater (heat exchanger), 4 is a first supercharger (turbocharger), and 5 is a second preheater (heat exchanger). ), 6 is a second supercharger (turbocharger), 7 is an exhaust gas wet processing device, 8 is an induction fan, 9 is a smoke stack, and 10 and 11 are air supply devices for starting.
本廃棄物処理設備1は、例えば下水処理場において水分を多量に含有する汚泥等の廃棄物X1を燃料として燃焼させることによって処理するものである。なお、本実施形態における廃棄物処理設備1の気泡流動床炉2は、一日当り20〜300t程度の廃棄物X1を処理する能力を有しており、本実施形態における廃棄物処理設備1は、このような廃棄物X1の処理能力が35t/日程度の小形流動床炉2に対してエネルギー効率が高いシステム構成を有している。 The waste treatment facility 1 treats, for example, by burning waste X1 such as sludge containing a large amount of moisture as fuel in a sewage treatment plant. In addition, the bubbling fluidized bed furnace 2 of the waste treatment facility 1 in the present embodiment has an ability to treat the waste X1 of about 20 to 300 t per day, and the waste treatment facility 1 in the present embodiment is Such a waste X1 has a system configuration with high energy efficiency for the small fluidized bed furnace 2 having a processing capacity of about 35 t / day.
気泡流動床炉2は、外部から供給された廃棄物X1及び必要に応じて供給される助燃燃料X2を燃料として燃焼を行うものである。この気泡流動床炉2は、下部から供給される圧縮空気X3’によって炉内の流動状態を維持することによって、連続的な廃棄物X1の燃焼処理を可能としたものである。 The bubbling fluidized bed furnace 2 performs combustion using the waste X1 supplied from the outside and the auxiliary combustion fuel X2 supplied as necessary. This bubbling fluidized bed furnace 2 is capable of continuously treating the waste X1 by maintaining a fluid state in the furnace with compressed air X3 'supplied from below.
なお、助燃燃料X2としては重油、灯油あるいは都市ガスや石炭等の可燃物質が挙げられるが、上記圧縮空気X3’の圧力及び温度が充分に高い場合や汚泥X1の保有エネルギーが高い場合には、助燃燃料X2を気泡流動床炉2に供給しなくとも廃棄物X1を連続的に燃焼させることが可能である。 In addition, as the auxiliary fuel X2, flammable substances such as heavy oil, kerosene, city gas, and coal can be mentioned. When the pressure and temperature of the compressed air X3 ′ are sufficiently high or when the retained energy of the sludge X1 is high, Even if the auxiliary fuel X2 is not supplied to the bubbling fluidized bed furnace 2, the waste X1 can be continuously burned.
第1予熱器3は、気泡流動床炉2の後段に設けられており、気泡流動床炉2によって生成された排ガスX4と圧縮空気X3とを間接的に熱交換することによって、圧縮空気X3を所定の温度まで加温するものである。 The first preheater 3 is provided in the subsequent stage of the bubbling fluidized bed furnace 2, and indirectly exchanges heat between the exhaust gas X4 generated by the bubbling fluidized bed furnace 2 and the compressed air X3, thereby generating compressed air X3. Heating to a predetermined temperature.
第1過給機4は第1予熱器3に連結されている。第1過給機4は、第1予熱器3を流通する排ガスX4との間接的な熱交換により加熱された圧縮空気X3’によって回転駆動されるタービン4b及び当該タービン4bの回転動力を伝達されることによって外気より圧縮空気X3を生成して第1予熱器3内に送気するコンプレッサ4aから構成されている。すなわち、第1過給機4の動力源となった圧縮空気X3’が燃焼用圧縮空気として気泡流動床炉2に供給される。ここで、本発明者らは、第1過給機4で圧縮した圧縮空気X3を第1予熱器3で予熱して得られる圧縮空気X3’によりタービン4bを回転させ、さらにこの動力源となった圧縮空気X3’を燃焼用空気として気泡流動床炉2に供給するサイクルが十分に成り立つことを知見している。なお、始動方法の一例としては、ブロワや圧縮機などの始動用空気供給装置10から燃焼用空気を供給し、バーナーの着火、炉の昇温を行う。その過程で、過給機のコンプレッサ空気と燃焼空気との流路をバルブ等で切り換える。
The first supercharger 4 is connected to the first preheater 3. The first supercharger 4 is rotated by compressed air X3 ′ heated by indirect heat exchange with the exhaust gas X4 flowing through the first preheater 3, and the rotational power of the
この第1過給機4としては、舶用のものを用いることが好ましい。これは、舶用の過給機が既に世の中に広く普及しており豊富な種類が用意されているためである。 As this 1st supercharger 4, it is preferable to use the thing for ships. This is because marine superchargers are already in widespread use and a wide variety of types are available.
第2予熱器5は、第1予熱器の後段に設置され、第1予熱器を流通した排ガスX4が流通される。この排ガスX4と第2過給機6から送気される圧縮空気X5とが間接的に熱交換されて、当該圧縮空気X5の加熱が行なわれる。 The 2nd preheater 5 is installed in the back | latter stage of a 1st preheater, and the waste gas X4 which distribute | circulated the 1st preheater is distribute | circulated. The exhaust gas X4 and the compressed air X5 sent from the second supercharger 6 are indirectly heat-exchanged to heat the compressed air X5.
第2過給機6は第2予熱器5に連結されている。第2過給機6は、第2予熱器5を流通する排ガスX4との熱交換により加熱された圧縮空気X5’によって回転駆動されるタービン6b及び当該タービン6bの回転動力を伝達されることによって外気より圧縮空気X5を生成して第2予熱器5内に送気するコンプレッサ6aから構成されている。加熱された圧縮空気X5’は、後述の白煙防止用圧縮空気として利用される。ここで、本発明者らは、第2過給機6で圧縮した圧縮空気X5を第2予熱器5で予熱して得られる圧縮空気X5’によりタービン6bを回転させ、さらにこの動力源となった圧縮空気X5’を白煙防止用の圧縮空気として利用するサイクルが十分に成り立つことを知見している。
なお、始動方法の一例として、最初にブロワや圧縮機などの始動用空気供給装置11から空気を第二予熱器5に供給する。第2過給機6からの圧縮空気X5は大気へ放風する。排ガスX4の温度が高くなった後、始動用空気供給装置11からの空気と第2過給機6からの圧縮空気X5とをバルブ等を使い切り換える。
The second supercharger 6 is connected to the second preheater 5. The second supercharger 6 is rotated by compressed air X5 ′ heated by heat exchange with the exhaust gas X4 flowing through the second preheater 5, and the rotational power of the
As an example of the starting method, first, air is supplied to the second preheater 5 from the starting
排ガス湿式処理装置7は、前記第2予熱器5の後段に設けられている。排ガス湿式処理装置は、燃焼ガスX4に、例えば水、アルカリ液などを噴射して排ガス中の硫黄成分等の有害成分等を洗浄処理するものである。散布液は、排ガス性状により適宜選択される。 The exhaust gas wet treatment device 7 is provided in the subsequent stage of the second preheater 5. The exhaust gas wet processing apparatus is for cleaning and processing harmful components such as sulfur components in exhaust gas by injecting, for example, water, an alkaline liquid or the like into the combustion gas X4. The spray liquid is appropriately selected depending on the exhaust gas properties.
排ガス湿式処理装置7の後段には、排煙筒9が設けられている。排煙筒9から処理排ガスは最終的に大気開放される。 At the subsequent stage of the exhaust gas wet processing apparatus 7, a smoke exhaust tube 9 is provided. The treated exhaust gas is finally released to the atmosphere from the smoke exhaust tube 9.
排ガス湿式処理装置7から排煙筒9に続く管路の途中には、誘引ファン8が設けられている。この誘引ファン8により、排ガス湿式処理装置7から排煙筒9に処理排ガスX6を誘導される。なお、この誘引ファンは、必要ない場合もある。 An induction fan 8 is provided in the middle of the pipe line from the exhaust gas wet processing apparatus 7 to the smoke exhaust tube 9. By this induction fan 8, the treatment exhaust gas X 6 is guided from the exhaust gas wet processing device 7 to the smoke exhaust tube 9. Note that this attracting fan may not be necessary.
誘引ファン8から排煙筒9に続く管路の途中には、前記第2過給機6のタービン6bから続く管路5Pが接続されている。排ガス湿式処理装置7では、高温の排ガスに対して液体を散布等するため、多量の蒸気が発生する。従って、処理したのちに処理済みガスをそのまま後段の排煙筒9に供給されると、排煙筒から白煙があがるが、本設備では第2過給機6の動作により得られる加熱された圧縮空気X5’が適宜、排煙筒9の前段で処理排ガスX6に対して混合されるので、処理排ガスX6が再加温されて白煙防止がなされる。なお、図示はしないが、圧縮空気X5’の混合比率等は管路5Pに設けたバルブおよびこの開閉を制御する適宜の制御装置を用いる。
In the middle of the pipeline that leads from the induction fan 8 to the smoke exhaust tube 9, a pipeline 5 </ b> P that continues from the
以上の本発明にかかる設備では、従来設備同様、燃焼用圧縮空気の生成および排ガスの白煙防止処理を行うが、いずれも電力を必要としない過給機を用いて生成する。従って、従来設備と比較して、経済的な廃棄物処理設備および廃棄物処理方法である。 In the facilities according to the present invention as described above, the compressed air for combustion and the white smoke prevention treatment of the exhaust gas are performed as in the conventional facilities, but both are generated using a supercharger that does not require electric power. Therefore, it is an economical waste treatment facility and waste treatment method compared to conventional facilities.
ここで、本設備の運転実施例を、1日あたり35t程度の下水汚泥を処理する廃棄物処理設備を例に示す。この規模の設備で第1予熱器に供給される排ガスの一般的な流量および温度から、第1過給機は0.12MPaG、流量2600m3N/hの圧縮空気を第1予熱器に供給することができ、それとともに0.032MPaG、600℃の圧縮空気X3’を得ることができる。十分に過給機の運転ができるうえに、気泡焼却炉内に燃焼用圧縮空気を供給することが可能である。 Here, an operation example of this facility will be described by way of an example of a waste treatment facility for treating sewage sludge of about 35 t per day. From the general flow rate and temperature of the exhaust gas supplied to the first preheater with this scale of equipment, the first supercharger supplies the first preheater with compressed air of 0.12 MPaG and a flow rate of 2600 m 3 N / h. Along with that, compressed air X3 ′ at 0.032 MPaG and 600 ° C. can be obtained. In addition to being able to operate the supercharger sufficiently, it is possible to supply compressed air for combustion into the bubble incinerator.
さらに、第2過給機は、0.036MPaG、4000m3N/hの圧縮空気を第2予熱器に供給することが可能であり、0.003MPaG、温度300℃の圧縮空気を得ることが可能である。十分に過給機の運転が可能であるうえに、十分な温度および量の白煙防止用圧縮空気を得ることができる。 Furthermore, the second supercharger can supply compressed air of 0.036 MPaG and 4000 m 3 N / h to the second preheater, and can obtain compressed air of 0.003 MPaG and a temperature of 300 ° C. It is. It is possible to sufficiently operate the supercharger and to obtain compressed air for preventing white smoke having a sufficient temperature and amount.
同規模の処理能力の図2に示す従来設備では、燃焼用圧縮空気を得るためのブロアで概ね90kw、白煙防止用の圧縮空気を得るブロアで18.5kwを要している。 The conventional equipment shown in FIG. 2 having the same processing capacity requires approximately 90 kW for a blower for obtaining compressed air for combustion and 18.5 kW for a blower for obtaining compressed air for preventing white smoke.
してみると、本発明にかかる設備は、加圧式ではない気泡流動床炉でも過給機の運転が可能で適用可能であり、しかも、ブロアを用いる従来設備と比較して電力を要しない分、省エネルギー化が図られている。 As a result, the equipment according to the present invention can be applied to the supercharger even in a bubble fluidized bed furnace that is not a pressurized type, and moreover it requires less power than conventional equipment using a blower. , Energy saving is achieved.
本発明は、流動床式焼却炉を用いた各種廃棄物処理に利用可能である。 The present invention can be used for various kinds of waste processing using a fluidized bed incinerator.
1…汚泥処理設備、2…気泡流動床炉、3…第1予熱器、4…第1過給機、4a…コンプレッサ、4b…タービン、5…第2予熱器、6…第2過給機、6a…コンプレッサ、6b…タービン、7…湿式排ガス処理装置、8,80…誘引ファン、9…排煙筒、20…焼却炉、30…予熱器、40…過給機、50…予熱器。 DESCRIPTION OF SYMBOLS 1 ... Sludge processing equipment, 2 ... Bubble fluidized bed furnace, 3 ... 1st preheater, 4 ... 1st supercharger, 4a ... Compressor, 4b ... Turbine, 5 ... 2nd preheater, 6 ... 2nd supercharger , 6a ... compressor, 6b ... turbine, 7 ... wet exhaust gas treatment device, 8,80 ... attraction fan, 9 ... smoke stack, 20 ... incinerator, 30 ... preheater, 40 ... supercharger, 50 ... preheater.
Claims (4)
第1の予熱器で加熱されて流動床式焼却炉に向かう燃焼用圧縮空気によってタービンが回転させられ、この回転によってコンプレッサで前記第1の予熱器に供給する圧縮空気の生成および送風を行う、第1の過給機と、
前記第1の予熱器より上流側に設けられ運転開始時に前記タービンを回転させる第1の始動用空気供給装置とを、備える、
ことを特徴とする廃棄物処理設備。 A first preheater that preheats compressed air for combustion supplied to the fluidized bed incinerator by continuous gas-gas heat exchange between the fluidized bed incinerator and the exhaust gas from the fluidized bed incinerator;
The turbine is rotated by compressed air for combustion that is heated by the first preheater and goes to the fluidized bed incinerator, and by this rotation, the compressed air supplied to the first preheater is generated and blown by the compressor. A first supercharger;
A first air supply device for starting that is provided upstream of the first preheater and rotates the turbine at the start of operation ;
Waste treatment facility characterized by that.
流動床式焼却炉からの排ガスとの連続的なガス−ガス熱交換により、前記湿式処理装置で処理された排ガスに混合する圧縮空気を加熱するための第2の予熱器と、
第2の予熱器で加熱された加熱圧縮空気によってタービンが回転させられ、この回転によってコンプレッサで前記第2の予熱器に供給する圧縮空気の生成および送風を行う、第2の過給機とを備える、
請求項1記載の廃棄物処理設備。 An exhaust gas wet processing apparatus for performing wet processing of exhaust gas from a fluidized bed incinerator;
A second preheater for heating the compressed air to be mixed with the exhaust gas treated by the wet treatment device by continuous gas-gas heat exchange with the exhaust gas from the fluidized bed incinerator;
A turbine is rotated by heated compressed air heated by the second preheater, and a second supercharger that generates and blows compressed air to be supplied to the second preheater by the compressor by this rotation. Prepare
The waste treatment facility according to claim 1.
前記第1の予熱器より上流側に設けられた第1の始動用空気供給装置により、第1のターボ過給機のタービンの回転を始動させ、
前記第1の予熱器で加熱されて流動床式焼却炉に向かう燃焼用圧縮空気を、第1のターボ過給機に供給して前記タービンを継続的に回転させるとともに、当該過給機のコンプレッサにて前記第1の予熱器に供給する圧縮空気の生成および送風を行う、
ことを特徴とする廃棄物処理方法。 Preheating the compressed air for combustion supplied to the fluidized bed incinerator by a first preheater by continuous gas-gas heat exchange with the exhaust gas discharged from the fluidized bed incinerator;
The first turbocharger turbine is started to rotate by a first start-up air supply device provided upstream of the first preheater ,
The combustion compressed air towards the fluidized bed incinerator is heated by the first preheater, causes continuously rotating the turbine is supplied to the first turbocharger, the compressor of the turbocharger Generating and blowing compressed air to be supplied to the first preheater at
A waste treatment method characterized by the above.
この白煙防止処理に用いる圧縮空気の加熱を、流動床式焼却炉から排出される排ガスを熱源とする第2の予熱器を用いて連続的なガス−ガス熱交換により行ない、かつ、
前記第2の予熱器で加熱された加熱圧縮空気を第2の過給機に供給して前記タービンを継続的に回転させるとともに、当該過給機のコンプレッサにて前記第2の予熱器に供給する圧縮空気の生成および送風を行う、
請求項3記載の廃棄物処理方法。 In performing the white smoke prevention treatment of mixing heated compressed air to the exhaust gas treated by the exhaust gas wet treatment apparatus,
The compressed air used for the white smoke prevention treatment is heated by continuous gas-gas heat exchange using a second preheater using the exhaust gas discharged from the fluidized bed incinerator as a heat source, and
The heated compressed air heated by the second preheater is supplied to the second supercharger to continuously rotate the turbine, and supplied to the second preheater by the compressor of the supercharger. Generate and blow compressed air,
The waste disposal method according to claim 3.
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