JP2003230875A - Waste treatment plant - Google Patents
Waste treatment plantInfo
- Publication number
- JP2003230875A JP2003230875A JP2002032207A JP2002032207A JP2003230875A JP 2003230875 A JP2003230875 A JP 2003230875A JP 2002032207 A JP2002032207 A JP 2002032207A JP 2002032207 A JP2002032207 A JP 2002032207A JP 2003230875 A JP2003230875 A JP 2003230875A
- Authority
- JP
- Japan
- Prior art keywords
- exhaust gas
- activator
- gas
- residue
- carbon dioxide
- 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.)
- Pending
Links
- 239000002699 waste material Substances 0.000 title claims abstract description 25
- 239000007789 gas Substances 0.000 claims abstract description 106
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical group [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 95
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 claims abstract description 74
- 239000001569 carbon dioxide Substances 0.000 claims abstract description 37
- 229910002092 carbon dioxide Inorganic materials 0.000 claims abstract description 37
- 239000012190 activator Substances 0.000 claims abstract description 29
- 230000003213 activating effect Effects 0.000 claims abstract description 20
- 238000002844 melting Methods 0.000 claims abstract description 20
- 230000008018 melting Effects 0.000 claims abstract description 20
- 238000002485 combustion reaction Methods 0.000 claims abstract description 17
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 10
- 239000001301 oxygen Substances 0.000 claims abstract description 10
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 9
- 230000004913 activation Effects 0.000 claims description 18
- 238000005979 thermal decomposition reaction Methods 0.000 claims description 10
- 238000006386 neutralization reaction Methods 0.000 claims description 4
- 230000003472 neutralizing effect Effects 0.000 claims description 4
- 238000000197 pyrolysis Methods 0.000 abstract description 32
- 150000002013 dioxins Chemical class 0.000 abstract description 12
- 239000000428 dust Substances 0.000 description 14
- UIIMBOGNXHQVGW-UHFFFAOYSA-M Sodium bicarbonate Chemical compound [Na+].OC([O-])=O UIIMBOGNXHQVGW-UHFFFAOYSA-M 0.000 description 10
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 9
- 229910002091 carbon monoxide Inorganic materials 0.000 description 9
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 6
- 230000000694 effects Effects 0.000 description 6
- 238000010438 heat treatment Methods 0.000 description 6
- 235000017557 sodium bicarbonate Nutrition 0.000 description 5
- 229910000030 sodium bicarbonate Inorganic materials 0.000 description 5
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 4
- 229910052782 aluminium Inorganic materials 0.000 description 4
- 238000005303 weighing Methods 0.000 description 4
- 229910052742 iron Inorganic materials 0.000 description 3
- 230000007246 mechanism Effects 0.000 description 3
- 230000007723 transport mechanism Effects 0.000 description 3
- 101000607626 Homo sapiens Ubiquilin-1 Proteins 0.000 description 2
- 102100039934 Ubiquilin-1 Human genes 0.000 description 2
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 2
- 239000000920 calcium hydroxide Substances 0.000 description 2
- 235000011116 calcium hydroxide Nutrition 0.000 description 2
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 238000001816 cooling Methods 0.000 description 2
- 238000002309 gasification Methods 0.000 description 2
- 238000010248 power generation Methods 0.000 description 2
- 238000011144 upstream manufacturing Methods 0.000 description 2
- 101100000419 Autographa californica nuclear polyhedrosis virus AC41 gene Proteins 0.000 description 1
- 101150000715 DA18 gene Proteins 0.000 description 1
- 101100321669 Fagopyrum esculentum FA02 gene Proteins 0.000 description 1
- 101100321670 Fagopyrum esculentum FA18 gene Proteins 0.000 description 1
- -1 but thereafter Substances 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 230000007797 corrosion Effects 0.000 description 1
- 239000010791 domestic waste Substances 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 239000004744 fabric Substances 0.000 description 1
- 239000002440 industrial waste Substances 0.000 description 1
- 239000003350 kerosene Substances 0.000 description 1
- 239000006148 magnetic separator Substances 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 238000000034 method Methods 0.000 description 1
- 230000005855 radiation Effects 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/20—Waste processing or separation
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/82—Recycling of waste of electrical or electronic equipment [WEEE]
Landscapes
- Chimneys And Flues (AREA)
- Incineration Of Waste (AREA)
- Gasification And Melting Of Waste (AREA)
- Treating Waste Gases (AREA)
- Processing Of Solid Wastes (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、廃棄物を熱分解残
渣と熱分解ガスに熱分解する熱分解反応器を設け、前記
熱分解ガスと、前記熱分解残さから選別されたカーボン
残さとを受け入れて燃焼させる燃焼溶融炉を設け、バグ
フィルタで排ガスを処理する排ガス処理部を設けてある
廃棄物処理プラントに関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention is provided with a pyrolysis reactor for pyrolyzing waste into a pyrolysis residue and a pyrolysis gas, and the pyrolysis gas and the carbon residue selected from the pyrolysis residue are provided. The present invention relates to a waste treatment plant provided with a combustion melting furnace for receiving and burning, and an exhaust gas treatment unit for treating exhaust gas with a bag filter.
【0002】[0002]
【従来の技術】従来、上記の廃棄物処理プラントでは、
排ガスからダイオキシン類を除去するのに、排ガス処理
部にバグフィルタを設けるとともに、市販の活性炭をバ
グフィルタに供給する活性炭供給部を設けて、活性炭に
ダイオキシン類を吸着させるようにしてあった。2. Description of the Related Art Conventionally, in the above waste treatment plant,
In order to remove dioxins from the exhaust gas, a bag filter is provided in the exhaust gas treatment section and an activated carbon supply section that supplies commercially available activated carbon to the bag filter is provided so that the activated carbon adsorbs dioxins.
【0003】[0003]
【発明が解決しようとする課題】しかしながら、上記従
来の構成によれば、バグフィルタに活性炭を供給してい
たために、活性炭に要するコストが高くなって運転コス
トが高くなるという問題があった。However, according to the above-mentioned conventional structure, since the activated carbon is supplied to the bag filter, there is a problem that the cost required for the activated carbon becomes high and the operating cost becomes high.
【0004】本発明の目的は、排ガスからダイオキシン
類を除去するのに要するコストを低廉化できるようにし
て運転コストを低廉化できる廃棄物処理プラントを提供
する点にある。An object of the present invention is to provide a waste treatment plant capable of reducing the operating cost by reducing the cost required for removing dioxins from exhaust gas.
【0005】[0005]
【課題を解決するための手段】請求項1の構成による発
明の構成・作用・ 効果は次の通りである。The constitution, action and effect of the invention according to the constitution of claim 1 are as follows.
【0006】[構成]冒頭に記載した廃棄物処理プラン
トにおいて、前記カーボン残さのうちの一部の残さを、
前記燃焼溶融炉側に向かわせることなく賦活器に供給
し、賦活器に供給された炭酸ガスによって前記賦活器内
で賦活する賦活手段と、賦活されたカーボン残さを前記
バグフィルタに供給する賦活カーボン残さ供給手段とを
設け、前記賦活器に炭酸ガスを供給するに、前記賦活器
から排出される排ガスを回収するとともに回収排ガスに
酸素を供給することで炭酸ガスを生成し、その炭酸ガス
を前記賦活器に戻し供給するように構成してある。[Structure] In the waste treatment plant described at the beginning, a part of the carbon residue is replaced by
Supplying to an activator without going to the combustion melting furnace side, an activating means for activating in the activator by the carbon dioxide gas supplied to the activator, and activated carbon supplying activated carbon residue to the bag filter A residue supply means is provided to supply carbon dioxide gas to the activator, recover exhaust gas discharged from the activator, and generate carbon dioxide gas by supplying oxygen to the recovered exhaust gas. It is configured to be supplied back to the activator.
【0007】[作用]賦活手段が、熱分解残さから選別
されたカーボン残さのうちの一部の残さを、燃焼溶融炉
側に向かわせることなく賦活器に供給し、賦活器に供給
された炭酸ガスによって賦活器内で賦活する。そして、
賦活カーボン残さ供給手段が、賦活されたカーボン残さ
を排ガス処理部のバグフィルタに供給する。[Action] The activating means supplies a part of the carbon residue selected from the pyrolysis residue to the activator without directing it to the combustion melting furnace side, and the carbon dioxide supplied to the activator. Activated in gas in the activator. And
The activated carbon residue supply means supplies the activated carbon residue to the bag filter of the exhaust gas treating section.
【0008】賦活されたカーボン残さは活性炭と同様に
ダイオキシン類を吸着しやすくなっており、このカーボ
ン残さをバグフィルタに供給することで、排ガス中のダ
イオキシン類を除去することができる。Like the activated carbon, the activated carbon residue is likely to adsorb dioxins. By supplying this carbon residue to the bag filter, dioxins in the exhaust gas can be removed.
【0009】例えば、活性炭をバグフィルタに供給して
活性炭に排ガス中のダイオキシン類を吸着させる技術で
は活性炭に要するコストが高くなるが、請求項1の構成
によれば、活性炭をバグフィルタに供給しなくても済
み、活性炭にコストをかけなくてもよくなる。[0009] For example, in the technique of supplying activated carbon to the bag filter to adsorb dioxins in the exhaust gas to the activated carbon, the cost required for activated carbon increases, but according to the configuration of claim 1, activated carbon is supplied to the bag filter. It doesn't have to be, and you don't have to pay for activated carbon.
【0010】また、活性炭と、炭賦活されたカーボン残
さとをバグフィルタに供給して排ガス中のダイオキシン
類を除去するようにしてもよく、このような場合、活性
炭が少量で済んで活性炭に要するコストを低廉化でき
る。Further, activated carbon and charcoal-activated carbon residue may be supplied to a bag filter to remove dioxins in the exhaust gas. In such a case, a small amount of activated carbon is required for activated carbon. Cost can be reduced.
【0011】賦活器内でカーボン残さを賦活する場合、
運転当初は炭酸ガスをガスタンク等の炭酸ガス貯留部か
ら賦活器に供給するが、その後は賦活手段によって生成
した炭酸ガスを供給する。When activating the carbon residue in the activator,
At the beginning of operation, carbon dioxide gas is supplied from a carbon dioxide gas storage part such as a gas tank to the activator, but thereafter, carbon dioxide gas generated by the activation means is supplied.
【0012】詳述すると、賦活器から排出される排ガス
の大部分は一酸化炭素(CO)と炭酸ガス(CO2 )か
ら成ることから、賦活器から排出される排ガスを回収し
て回収排ガスに酸素を供給し、排ガス中の一酸化炭素を
酸素と反応させて炭酸ガスを生成する。これにより、回
収排ガスの大部分を炭酸ガスにすることができる。そし
て、この炭酸ガスを賦活ガスとして賦活器に戻し供給す
る。More specifically, most of the exhaust gas discharged from the activator is composed of carbon monoxide (CO) and carbon dioxide gas (CO 2 ). Therefore, the exhaust gas discharged from the activator is recovered and recovered as exhaust gas. Oxygen is supplied to react carbon monoxide in the exhaust gas with oxygen to generate carbon dioxide gas. As a result, most of the recovered exhaust gas can be converted to carbon dioxide gas. Then, this carbon dioxide gas is supplied as an activating gas back to the activator.
【0013】このように、炭酸ガス貯留部からは炭酸ガ
スを賦活器内に運転当初だけ供給すればよく、炭酸ガス
に要するコストを低廉化できる。As described above, it is sufficient to supply the carbon dioxide gas from the carbon dioxide gas storage section into the activator only at the beginning of the operation, so that the cost required for the carbon dioxide gas can be reduced.
【0014】[効果]従って、排ガスからダイオキシン
類を除去するのに要するコストを低廉化できるようにし
て運転コストを低廉化できる廃棄物処理プラントを提供
することができた。[Effect] Therefore, it was possible to provide a waste treatment plant capable of reducing the operating cost by reducing the cost required for removing dioxins from exhaust gas.
【0015】請求項2の構成による発明の構成・作用・
効果は次の通りである。Structure and operation of the invention according to the structure of claim 2
The effects are as follows.
【0016】[構成]請求項1による発明の構成におい
て、前記回収排ガスを中和する中和処理部を設けてあ
る。[Structure] In the structure of the present invention according to claim 1, a neutralization processing unit for neutralizing the recovered exhaust gas is provided.
【0017】[作用]請求項1の構成による作用と同様
の作用を奏することができるのに加え、回収排ガスを中
和する中和処理部を設けてあるから、管路や賦活器の高
温腐食を防止することができる。[Operation] In addition to the same operation as the operation according to the first aspect of the present invention, a high temperature corrosion of the pipeline and the activator is provided because the neutralization processing section for neutralizing the recovered exhaust gas is provided. Can be prevented.
【0018】[効果]従って、請求項1の構成による効
果と同様の効果を奏することができるのに加え、円滑に
作動させることができてメンテナンス等の回数を少なく
することができる廃棄物処理プラントを提供することが
できた。[Effects] Therefore, in addition to the same effects as the effects according to the first aspect of the invention, the waste disposal plant can be operated smoothly and the number of maintenances can be reduced. Could be provided.
【0019】[0019]
【発明の実施の形態】以下、本発明の実施の形態を図面
に基づいて説明する。BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of the present invention will be described below with reference to the drawings.
【0020】図1に、家庭ゴミ等の一般廃棄物やカーシ
ュレッダーダスト・電化製品等の産業廃棄物の処理プラ
ントである熱分解ガス化溶融プラントを示してある。FIG. 1 shows a pyrolysis gasification and melting plant which is a processing plant for general waste such as household waste and industrial waste such as car shredder dust and electric appliances.
【0021】前記熱分解ガス化溶融プラントは前処理設
備1・熱分解設備2・熱分解残さ選別設備3・高温燃焼
溶融設備4・ボイラ発電設備5・排ガス処理設備6から
成る。次に各設備について説明する。The pyrolysis gasification and melting plant comprises a pretreatment facility 1, a pyrolysis facility 2, a pyrolysis residue sorting facility 3, a high temperature combustion melting facility 4, a boiler power generation facility 5, and an exhaust gas treatment facility 6. Next, each facility will be described.
【0022】[前処理設備1]廃棄物ピット7に貯留さ
れた廃棄物を破砕機で破砕し、破砕廃棄物を搬送装置等
で熱分解設備2に送る。[Pretreatment facility 1] The waste stored in the waste pit 7 is crushed by a crusher, and the crushed waste is sent to the thermal decomposition facility 2 by a transport device or the like.
【0023】[熱分解設備2]廃棄物ピット7からの廃
棄物を熱分解ドラム12(熱分解反応器に相当)に搬送
供給し、加熱ガス供給手段102で熱分解ドラム12に
加熱ガスを供給する。そして、この加熱ガスで廃棄物を
間接的に加熱しながら、廃棄物を無酸素あるいは低酸素
雰囲気で約450℃の熱分解ガスと熱分解残に熱分解
し、熱分解ガスを後述の高温燃焼溶融炉13に送り、熱
分解残さを熱分解残さ選別設備3に送る。[Pyrolysis facility 2] The waste from the waste pit 7 is conveyed and supplied to the pyrolysis drum 12 (corresponding to a pyrolysis reactor), and the heating gas is supplied to the pyrolysis drum 12 by the heating gas supply means 102. To do. Then, while indirectly heating the waste with this heating gas, the waste is pyrolyzed into a pyrolysis gas of about 450 ° C. and a pyrolysis residue in an oxygen-free or low-oxygen atmosphere, and the pyrolysis gas is burned at a high temperature described later. It is sent to the melting furnace 13 and the pyrolysis residue is sent to the pyrolysis residue sorting facility 3.
【0024】[熱分解残さ選別設備3]熱分解ドラム1
2からの熱分解座残さを振動フィーダ70等で熱分解残
さ選別装置99に送る。[Pyrolysis Residue Sorting Equipment 3] Pyrolysis Drum 1
The pyrolysis residue from 2 is sent to the pyrolysis residue sorting device 99 by a vibration feeder 70 or the like.
【0025】前記熱分解残さ選別装置99では、磁選機
91で選別した鉄類を鉄類ヤード96に回収するととも
に、アルミ選別機で選別したアルミをアルミヤード97
に回収する。In the thermal decomposition residue sorting device 99, the iron sorted by the magnetic separator 91 is recovered in the iron yard 96, and the aluminum sorted by the aluminum sorter is collected in the aluminum yard 97.
To collect.
【0026】そして、鉄・アルミ等が選別された後の熱
分解残さを粉砕機93で粉砕する。粉砕したもののうち
異物を異物ヤード98に回収するとともに、異物以外の
カーボン残さを第1カーボン残さ管路32を通してカー
ボン残さサイロ61に送り、カーボン残さサイロ61内
のカーボン残さを、カーボン残さブロワ48によって第
2カーボン残さ管路33を通して高温燃焼溶融設備4の
高温燃焼溶融炉13にその炉頂側から吹き込む。Then, the pyrolysis residue after the iron, aluminum, etc. are selected is crushed by a crusher 93. The foreign matters of the crushed ones are collected in the foreign matter yard 98, the carbon residues other than the foreign matters are sent to the carbon residue silo 61 through the first carbon residue pipeline 32, and the carbon residue in the carbon residue silo 61 is removed by the carbon residue blower 48. It blows into the high temperature combustion melting furnace 13 of the high temperature combustion melting equipment 4 from the furnace top side through the second carbon residue pipeline 33.
【0027】[高温燃焼溶融設備4]カーボン残さ・熱
分解ガス・ 集塵ダストを高温燃焼溶融炉13に炉頂側
から吹き込み、これらを旋回燃焼する。焼却灰・集塵ダ
ストは溶融し、炉底から連続排出する。[High Temperature Combustion and Melting Facility 4] Carbon residue, pyrolysis gas, and dust dust are blown into the high temperature combustion and melting furnace 13 from the furnace top side, and these are swirled and burned. The incinerated ash and dust collected will be melted and continuously discharged from the bottom of the furnace.
【0028】[ボイラ発電設備5]排ガスはボイラ輻射
ゾーンで冷却し、蒸発管群で均一な温度にした後、加熱
蒸気群に送る。ボイラ18で蒸気を熱回収し、タービン
94・発電機95で電気として回収する。[Boiler power generation equipment 5] Exhaust gas is cooled in the boiler radiation zone, and is brought to a uniform temperature in the evaporation tube group, and then sent to the heated steam group. The boiler 18 recovers heat from the steam, and the turbine 94 / generator 95 recovers it as electricity.
【0029】[排ガス処理設備6]ボイラ18からの排
ガスに対するガス冷却塔21と第1バグフィルタ17と
第2バグフィルタ22とを設け、これらの装置で処理し
た排ガスを排気する煙突25を設けてある。[Exhaust Gas Treatment Facility 6] A gas cooling tower 21 for the exhaust gas from the boiler 18, a first bag filter 17, and a second bag filter 22 are provided, and a chimney 25 for exhausting the exhaust gas treated by these devices is provided. is there.
【0030】そして、ボイラ18・ガス冷却塔21・第
1バグフィルタ17からの集塵ダストを収容するダスト
サイロ89を設け、ダストサイロ89内の集塵ダスト
を、ダストブロワ49でダスト管路50を通して、前述
のように高温燃焼溶融炉13に炉頂側から吹き込むよう
構成してある。Then, a dust silo 89 for accommodating the dust collecting dust from the boiler 18, the gas cooling tower 21, and the first bag filter 17 is provided, and the dust collecting dust in the dust silo 89 is passed through the dust blower 49 through the dust pipe line 50. As described above, the high temperature combustion melting furnace 13 is configured to be blown from the furnace top side.
【0031】前記第2バグフィルタ22に消石灰を供給
する消石灰供給機構56を設けてある。第2バグフィル
タ22によってHClやSOxを除去することができ
る。A slaked lime supply mechanism 56 for supplying slaked lime to the second bag filter 22 is provided. The second bag filter 22 can remove HCl and SOx.
【0032】また、前記熱分解残さ選別設備3で熱分解
残さから選別されたカーボン残さのうちの一部のカーボ
ン残さを、高温燃焼溶融炉13側に向かわせることなく
賦活器に供給するとともに、賦活炉35(賦活器に相
当)に供給された炭酸ガスによって賦活炉35内で賦活
する賦活手段30と、賦活されたカーボン残さを第1バ
グフィルタ17に供給する賦活カーボン残さ供給手段3
1とを設けてある。Further, a part of the carbon residue of the carbon residue selected from the thermal decomposition residue in the thermal decomposition residue selection equipment 3 is supplied to the activator without being directed to the high temperature combustion melting furnace 13 side, An activating means 30 for activating in the activating furnace 35 by the carbon dioxide gas supplied to the activating furnace 35 (corresponding to an activating device), and an activating carbon residue supplying means 3 for supplying the activated carbon residue to the first bag filter 17.
1 and are provided.
【0033】前記賦活手段30について説明すると、熱
分解残さ選別設備3の第1カーボン残さ管路32から第
3カーボン残さ管路34を分岐するとともに、第3カー
ボン残さ管路34に計量コンベア52を設けてある。そ
して、計量コンベア52からのカーボン残さを賦活炉3
5に受け入れるよう構成してある。Explaining the activating means 30, the first carbon residue pipe 32 and the third carbon residue pipe 34 of the thermal decomposition residue sorting facility 3 are branched, and the weighing conveyor 52 is connected to the third carbon residue pipe 34. It is provided. Then, the carbon residue from the weighing conveyor 52 is activated by the activation furnace 3
It is configured to accept 5.
【0034】前記第1カーボン残さ管路32と第3カー
ボン残さ管路34の分岐部に、カーボン残さをカーボン
残さサイロ61側に流す第1状態と、賦活炉35側に流
す第2状態とに切換え自在な切換えダンパ51を設けて
ある。また、前記賦活炉35に攪拌機36・温度測定器
37・温度調節計38・電気ヒーター39を設け、炭酸
ガスを貯留するガスタンク41(炭酸ガス貯留部に相
当)を賦活炉35内に接続してある。At the branch portion of the first carbon residue pipeline 32 and the third carbon residue pipeline 34, there are a first state in which carbon residue is flown to the carbon residue silo 61 side and a second state in which it is flown to the activation furnace 35 side. A switching damper 51 that can be switched is provided. Further, the activation furnace 35 is provided with a stirrer 36, a temperature measuring device 37, a temperature controller 38, and an electric heater 39, and a gas tank 41 (corresponding to a carbon dioxide gas storage portion) for storing carbon dioxide is connected to the inside of the activation furnace 35. is there.
【0035】前記賦活炉35からの排ガスは排気管40
を通して高温燃焼溶融炉13に供給する。さらにこの排
気管40を分岐して排ガスを回収するよう構成してあ
る。そして、回収排ガスに酸素を供給することで炭酸ガ
スを生成し、その炭酸ガスを賦活炉35に戻し供給する
よう構成してある。Exhaust gas from the activation furnace 35 is exhaust pipe 40.
Through the high temperature combustion melting furnace 13. Further, the exhaust pipe 40 is branched to collect exhaust gas. Then, carbon dioxide is generated by supplying oxygen to the recovered exhaust gas, and the carbon dioxide is returned to the activation furnace 35 and supplied.
【0036】詳しくは、排気管40から分岐した分岐管
104を賦活炉35に接続し、この分岐管104の中間
部に、回収排ガスを重曹で中和する中和処理部としての
重曹充填塔100を接続するとともに、重曹充填塔10
0よりも下流側の分岐管部分に、排ガス中の一酸化炭素
を酸素と反応させる反応塔101を接続し、反応塔10
1よりも下流側の分岐管部分にガス吸引ファン103を
設けてある。More specifically, the branch pipe 104 branched from the exhaust pipe 40 is connected to the activation furnace 35, and a sodium bicarbonate packed column 100 as a neutralization processing unit for neutralizing the recovered exhaust gas with sodium bicarbonate is provided in the middle of the branch pipe 104. And the baking soda packed tower 10
A reaction tower 101 for reacting carbon monoxide in exhaust gas with oxygen is connected to a branch pipe portion on the downstream side of 0,
A gas suction fan 103 is provided in the branch pipe portion downstream of 1.
【0037】上記の構造により、運転当初は賦活ガスと
しての炭酸ガスをガスタンク41から賦活炉35に供給
する。賦活炉35から排ガスが排出されるようになる
と、排ガスをガス吸引ファン103の駆動で分岐管10
4に回収し、重曹充填塔100を通して中和する。そし
て、反応塔101で排ガスに酸素を供給してこれらを反
応させる。賦活炉35から排出される排ガスの大部分は
一酸化炭素(CO)と炭酸ガス(CO2 )であり、それ
らのうちの一酸化炭素が酸素と反応して炭酸ガスにな
る。その結果、回収排ガスの大部分を炭酸ガスにするこ
とができる。この炭酸ガスを賦活ガスとして賦活炉35
に戻し供給する。With the structure described above, carbon dioxide gas as an activating gas is supplied from the gas tank 41 to the activating furnace 35 at the beginning of the operation. When the exhaust gas is discharged from the activation furnace 35, the exhaust gas is driven by the gas suction fan 103 to branch the pipe 10.
4 and neutralize through a baking soda packed column 100. Then, in the reaction tower 101, oxygen is supplied to the exhaust gas to react them. Most of the exhaust gas discharged from the activation furnace 35 is carbon monoxide (CO) and carbon dioxide (CO 2 ), and carbon monoxide among them reacts with oxygen to become carbon dioxide. As a result, most of the recovered exhaust gas can be carbon dioxide gas. The activation furnace 35 uses this carbon dioxide gas as the activation gas.
Supply back to.
【0038】これにより、賦活ガスとしての炭酸ガス
は、ガスタンク41から賦活炉35内に運転当初だけ供
給すればよく、炭酸ガスに要するコストを低廉化でき
る。As a result, the carbon dioxide gas as the activating gas need only be supplied from the gas tank 41 into the activating furnace 35 only at the beginning of operation, and the cost required for the carbon dioxide gas can be reduced.
【0039】前記賦活カーボン残さ供給手段31は、賦
活されたカーボン残さを搬送するコンベア42と、この
コンベア42からのカーボン残さを貯留する賦活カーボ
ン残さ貯留タンク43と、このタンク43内のカーボン
残さを、賦活カーボン残さブロワ45で賦活カーボン残
さ管路46を通して第1バグフィルタ17の上流側の排
ガス管路44に吹き込む空気輸送機構55とから成る。The activated carbon residue supply means 31 stores a conveyor 42 that conveys the activated carbon residue, an activated carbon residue storage tank 43 that stores the carbon residue from this conveyor 42, and a carbon residue in this tank 43. The air transport mechanism 55 blows the activated carbon residue blower 45 through the activated carbon residue conduit 46 into the exhaust gas conduit 44 upstream of the first bag filter 17.
【0040】前記賦活カーボン残さ貯留タンク43の底
部側に定量供給機構53を設けてあり、賦活されたカー
ボン残さを一定量づつ前記排ガス管路44に吹き込み可
能に構成してある。A fixed amount supply mechanism 53 is provided on the bottom side of the activated carbon residue storage tank 43 so that a fixed amount of activated carbon residue can be blown into the exhaust gas pipeline 44 in a fixed amount.
【0041】上記の構造により、前記切換えダンパ51
を前記第2状態側に切換えて、計量コンベア52にカー
ボン残さを供給し、計量コンベア52で計量した設定量
のカーボン残さを賦活炉35に供給する。With the above structure, the switching damper 51
Is switched to the second state side, the carbon residue is supplied to the weighing conveyor 52, and the set amount of carbon residue measured by the weighing conveyor 52 is supplied to the activation furnace 35.
【0042】次に、ガスタンク41から炭酸ガスを、散
気管を通して賦活炉35内に均等に供給する。また、攪
拌機36を攪拌作動させて炭酸ガスとカーボン残さを均
一に接触させる。カーボン残さは電気ヒータ39で加熱
する。この場合、温度測定器37・温度調節計38によ
って、炉内の温度を750〜900℃間の所定の温度上
昇率で昇温させる。Next, carbon dioxide gas is uniformly supplied from the gas tank 41 into the activation furnace 35 through the diffuser pipe. Further, the stirrer 36 is operated to stir so that the carbon dioxide gas and the carbon residue are contacted uniformly. The carbon residue is heated by the electric heater 39. In this case, the temperature measuring device 37 and the temperature controller 38 raise the temperature in the furnace at a predetermined temperature increase rate of 750 to 900 ° C.
【0043】賦活炉35内への炭酸ガスの供給について
は前述の通りであるのでその説明は省略する。カーボン
残さを賦活した後は電気ヒータ39を切ってカーボン残
さを冷却する。そして、冷却したカーボン残さを賦活カ
ーボン残さ貯留タンク43に供給し、タンク底部側の定
量供給機構53で設定量のカーボン残さを空気輸送機構
55側に供給し、この空気輸送機構55で前記設定量の
カーボン残さを第1バグフィルタ17の上流側の排ガス
管路44に供給する。Since the supply of carbon dioxide gas into the activation furnace 35 is as described above, its explanation is omitted. After activating the carbon residue, the electric heater 39 is turned off to cool the carbon residue. Then, the cooled carbon residue is supplied to the activated carbon residue storage tank 43, and the set amount of carbon residue is supplied to the air transport mechanism 55 side by the fixed amount supply mechanism 53 on the tank bottom side, and the set amount is set by the air transport mechanism 55. The carbon residue of the above is supplied to the exhaust gas pipeline 44 on the upstream side of the first bag filter 17.
【0044】賦活されたカーボン残さは、活性炭と同様
にダイオキシン類を吸着しやすくなっており、このカー
ボン残さを第1バグフィルタ17に供給することで,排
ガス中のダイオキシン類を除去することができる。ダイ
オキシン類を吸着したカーボン残さはダストとともに第
1バグフィルタ17のろ布から篩い落とし、ダストサイ
ロ89に収容して、高温燃焼溶融炉13に炉頂側から吹
き込む。Like the activated carbon, the activated carbon residue is likely to adsorb dioxins. By supplying this carbon residue to the first bag filter 17, the dioxins in the exhaust gas can be removed. . The carbon residue having adsorbed dioxins is screened together with dust from the filter cloth of the first bag filter 17, stored in the dust silo 89, and blown into the high temperature combustion melting furnace 13 from the furnace top side.
【0045】[別実施形態]前記回収排ガスを重曹以外
のもので中和するよう構成してあってもよい。[Other Embodiments] The recovered exhaust gas may be neutralized with something other than baking soda.
【0046】前記賦活炉の加熱は、電気ヒータ以上のも
の、例えば灯油やガスバーナーを使用した加熱であって
もよい。The heating of the activation furnace may be heating using an electric heater or more, for example, kerosene or a gas burner.
【0047】本発明は、前記熱分解ドラム12に換え
て、例えば廃棄物を熱分解する流動床式熱分解炉を設け
てある廃棄物処理プラントにも適用することができ、こ
れら熱分解ドラム12や流動床式熱分解炉を熱分解反応
器と総称する。The present invention can be applied to a waste treatment plant provided with a fluidized bed type pyrolysis furnace for pyrolyzing waste, instead of the pyrolysis drum 12. The fluidized bed type pyrolysis furnace is generally called a pyrolysis reactor.
【0048】上記の実施形態で挙げた数値は一例であり
別の数値であってもよい。The numerical values mentioned in the above embodiment are examples and may be different numerical values.
【図1】廃棄物処理プラントの概略図FIG. 1 Schematic of waste treatment plant
6 排ガス処理部 12 熱分解反応器 13 燃焼溶融炉 17 バグフィルタ 30 賦活手段 31 賦活カーボン残さ供給手段 35 賦活器 6 Exhaust gas treatment section 12 Pyrolysis reactor 13 Combustion melting furnace 17 Bug Filter 30 activation means 31 Activated carbon residue supply means 35 Activator
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) B01J 20/20 F23G 5/027 Z 4D004 20/30 5/16 Z 4G066 B09B 5/00 5/44 Z F23G 5/00 115 B09B 3/00 ZAB 5/027 303Z 5/16 5/00 Z 5/44 B01D 53/34 134E F23J 15/02 F23J 15/00 C Fターム(参考) 3K061 AA24 AB02 AB03 AC01 BA05 CA07 DA02 DA12 DA18 DA19 FA02 FA09 FA17 FA21 FA28 3K065 AA24 AB02 AB03 AC01 BA05 HA03 3K070 DA05 DA06 DA13 DA32 DA76 3K078 AA05 BA08 BA26 BA27 CA02 CA17 CA21 CA24 4D002 AA02 AA19 AA21 AC10 BA03 BA04 BA14 CA11 CA13 DA02 DA05 DA12 DA16 DA41 EA07 HA08 4D004 AA22 AA28 AA46 CA04 CA09 CA24 CA28 CA29 CB04 CB13 CB42 CB45 CB47 4G066 AA04B AA43D CA33 DA02 FA18 GA25 ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 7 Identification code FI theme code (reference) B01J 20/20 F23G 5/027 Z 4D004 20/30 5/16 Z 4G066 B09B 5/00 5/44 Z F23G 5/00 115 B09B 3/00 ZAB 5/027 303Z 5/16 5/00 Z 5/44 B01D 53/34 134E F23J 15/02 F23J 15/00 CF Term (reference) 3K061 AA24 AB02 AB03 AC01 BA05 CA07 DA02 DA12 DA18 DA19 FA02 FA09 FA17 FA21 FA28 3K065 AA24 AB02 AB03 AC01 BA05 HA03 3K070 DA05 DA06 DA13 DA32 DA76 3K078 AA05 BA08 BA26 BA27 CA02 CA17 CA21 CA24 4D002 AA02 AA19 AA21 AC41 BA12 DA41 A41 A41 DA41 DA41 DA41 DA02 DA05 DA05 DA05 DA05 DA05 DA06 AA46 CA04 CA09 CA24 CA28 CA29 CB04 CB13 CB42 CB45 CB47 4G066 AA04B AA43D CA33 DA02 FA18 GA25
Claims (2)
解する熱分解反応器を設け、前記熱分解ガスと、前記熱
分解残さから選別されたカーボン残さとを受け入れて燃
焼させる燃焼溶融炉を設け、バグフィルタで排ガスを処
理する排ガス処理部を設けてある廃棄物処理プラントで
あって、 前記カーボン残さのうちの一部の残さを、前記燃焼溶融
炉側に向かわせることなく賦活器に供給し、賦活器に供
給された炭酸ガスによって前記賦活器内で賦活する賦活
手段と、賦活されたカーボン残さを前記バグフィルタに
供給する賦活カーボン残さ供給手段とを設け、前記賦活
器に炭酸ガスを供給するに、前記賦活器から排出される
排ガスを回収するとともに回収排ガスに酸素を供給する
ことで炭酸ガスを生成し、その炭酸ガスを前記賦活器に
戻し供給するように構成してある廃棄物処理プラント。1. A combustion melting system in which a thermal decomposition reactor for thermally decomposing waste into thermal decomposition residue and thermal decomposition gas is provided, and the thermal decomposition gas and carbon residue selected from the thermal decomposition residue are received and burned. A waste treatment plant in which a furnace is provided and an exhaust gas treatment unit that treats exhaust gas with a bag filter is provided, and some of the carbon residues are left behind without being directed to the combustion melting furnace side. And an activation means for activating in the activator by the carbon dioxide gas supplied to the activator, and an activated carbon residue supply means for supplying the activated carbon residue to the bag filter, and carbon dioxide in the activator. When supplying the gas, the exhaust gas discharged from the activator is recovered, and carbon dioxide is generated by supplying oxygen to the recovered exhaust gas, and the carbon dioxide gas is supplied back to the activator. Waste treatment plant that is configured to so that.
設けてある請求項1に記載の廃棄物処理プラント。2. The waste treatment plant according to claim 1, further comprising a neutralization processing unit for neutralizing the recovered exhaust gas.
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JP2002032207A JP2003230875A (en) | 2002-02-08 | 2002-02-08 | Waste treatment plant |
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JP2002032207A JP2003230875A (en) | 2002-02-08 | 2002-02-08 | Waste treatment plant |
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102671909A (en) * | 2011-03-14 | 2012-09-19 | 江苏腾明环保科技有限公司 | Novel garbage incineration treatment device |
CN114806619A (en) * | 2022-04-28 | 2022-07-29 | 西安交通大学 | System and method for recycling all components of waste tire |
-
2002
- 2002-02-08 JP JP2002032207A patent/JP2003230875A/en active Pending
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102671909A (en) * | 2011-03-14 | 2012-09-19 | 江苏腾明环保科技有限公司 | Novel garbage incineration treatment device |
CN114806619A (en) * | 2022-04-28 | 2022-07-29 | 西安交通大学 | System and method for recycling all components of waste tire |
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