JP2002205044A - Waste treatment plant - Google Patents
Waste treatment plantInfo
- Publication number
- JP2002205044A JP2002205044A JP2001000943A JP2001000943A JP2002205044A JP 2002205044 A JP2002205044 A JP 2002205044A JP 2001000943 A JP2001000943 A JP 2001000943A JP 2001000943 A JP2001000943 A JP 2001000943A JP 2002205044 A JP2002205044 A JP 2002205044A
- Authority
- JP
- Japan
- Prior art keywords
- residue
- waste
- pyrolysis
- exhaust gas
- drum
- 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 34
- 239000010802 sludge Substances 0.000 claims abstract description 43
- 239000000428 dust Substances 0.000 claims abstract description 26
- 238000002844 melting Methods 0.000 claims abstract description 21
- 230000008018 melting Effects 0.000 claims abstract description 21
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical group [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 7
- 239000007789 gas Substances 0.000 claims description 39
- 238000000197 pyrolysis Methods 0.000 claims description 32
- 238000004140 cleaning Methods 0.000 claims description 23
- 229910001385 heavy metal Inorganic materials 0.000 claims description 21
- 238000002485 combustion reaction Methods 0.000 claims description 19
- 150000003839 salts Chemical class 0.000 claims description 13
- 238000011084 recovery Methods 0.000 claims description 8
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 8
- 230000001112 coagulating effect Effects 0.000 claims description 2
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims 2
- 239000003546 flue gas Substances 0.000 claims 2
- 239000002912 waste gas Substances 0.000 claims 1
- 238000010304 firing Methods 0.000 abstract 1
- 230000003311 flocculating effect Effects 0.000 abstract 1
- 238000005201 scrubbing Methods 0.000 abstract 1
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 18
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 9
- 239000011780 sodium chloride Substances 0.000 description 9
- 239000000126 substance Substances 0.000 description 8
- 239000002893 slag Substances 0.000 description 7
- 230000000694 effects Effects 0.000 description 6
- 238000005979 thermal decomposition reaction Methods 0.000 description 5
- 239000007864 aqueous solution Substances 0.000 description 4
- 238000006243 chemical reaction Methods 0.000 description 4
- 239000000460 chlorine Substances 0.000 description 4
- 229910052753 mercury Inorganic materials 0.000 description 4
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 4
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 3
- 229910052793 cadmium Inorganic materials 0.000 description 3
- 229910052801 chlorine Inorganic materials 0.000 description 3
- 238000002309 gasification Methods 0.000 description 3
- 229910052745 lead Inorganic materials 0.000 description 3
- 235000011121 sodium hydroxide Nutrition 0.000 description 3
- HGUFODBRKLSHSI-UHFFFAOYSA-N 2,3,7,8-tetrachloro-dibenzo-p-dioxin Chemical compound O1C2=CC(Cl)=C(Cl)C=C2OC2=C1C=C(Cl)C(Cl)=C2 HGUFODBRKLSHSI-UHFFFAOYSA-N 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 2
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- 230000002776 aggregation Effects 0.000 description 2
- 238000004220 aggregation Methods 0.000 description 2
- 229910052782 aluminium Inorganic materials 0.000 description 2
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 2
- 239000007795 chemical reaction product Substances 0.000 description 2
- 239000000571 coke Substances 0.000 description 2
- 230000018044 dehydration Effects 0.000 description 2
- 238000006297 dehydration reaction Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000010828 elution Methods 0.000 description 2
- 229910000041 hydrogen chloride Inorganic materials 0.000 description 2
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 238000010248 power generation Methods 0.000 description 2
- 239000000376 reactant Substances 0.000 description 2
- 102100033041 Carbonic anhydrase 13 Human genes 0.000 description 1
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 1
- 101000867860 Homo sapiens Carbonic anhydrase 13 Proteins 0.000 description 1
- 239000013522 chelant Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
- 239000010949 copper Substances 0.000 description 1
- TXKMVPPZCYKFAC-UHFFFAOYSA-N disulfur monoxide Inorganic materials O=S=S TXKMVPPZCYKFAC-UHFFFAOYSA-N 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 239000000155 melt Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 230000005855 radiation Effects 0.000 description 1
- 239000007921 spray Substances 0.000 description 1
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical compound S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 1
Landscapes
- Gasification And Melting Of Waste (AREA)
- Treating Waste Gases (AREA)
- Processing Of Solid Wastes (AREA)
- Treatment Of Sludge (AREA)
- Chimneys And Flues (AREA)
- Incineration Of Waste (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、廃棄物を熱分解ガ
スと熱分解残渣に熱分解する熱分解ドラムを設けるとと
もに、前記熱分解ガスと、前記熱分解残渣から選別され
たカーボン残渣とを受け入れて燃焼させる燃焼溶融炉を
設け、排ガスからHCl(塩化水素)やSOX (硫黄酸
化物)を除去する排ガス洗浄装置を設け、前記排ガス洗
浄装置からの重金属を含むダストを凝集沈殿させて脱水
汚泥にする脱水汚泥化手段を設けてある廃棄物処理プラ
ントに関する。BACKGROUND OF THE INVENTION The present invention provides a pyrolysis drum for pyrolyzing waste into a pyrolysis gas and a pyrolysis residue, and separates the pyrolysis gas from the carbon residue selected from the pyrolysis residue. A combustion melting furnace for receiving and burning is provided, and an exhaust gas cleaning device for removing HCl (hydrogen chloride) and SO x (sulfur oxide) from exhaust gas is provided. Dust containing heavy metals from the exhaust gas cleaning device is coagulated and settled to be dehydrated. The present invention relates to a waste treatment plant provided with dewatering sludge converting means for converting sludge.
【0002】[0002]
【従来の技術】上記の廃棄物処理プラントの排ガス洗浄
装置には乾式の排ガス洗浄装置と湿式の排ガス洗浄装置
とがある。2. Description of the Related Art There are two types of exhaust gas cleaning devices in the above-mentioned waste treatment plants: dry exhaust gas cleaning devices and wet exhaust gas cleaning devices.
【0003】このうち湿式の排ガス洗浄装置では、反応
剤として苛性ソーダ(NaOH)が使用され、残渣とし
て反応生成物である水溶したNaClや微量のダスト
(重金属(Pb・Cd・Hg・Cr等)を含む)が排出
される。Of these, in a wet exhaust gas cleaning apparatus, caustic soda (NaOH) is used as a reactant, and as a residue, water-soluble NaCl as a reaction product and a small amount of dust (heavy metals (Pb, Cd, Hg, Cr, etc.)) are removed. Including).
【0004】従来、上記の廃棄物処理プラントには、湿
式の排ガス洗浄装置からの重金属を含むダストを処理す
る手段としては、重金属溶出防止のための薬剤(キレー
ト)処理手段や、前記ダストを凝集・沈殿させて脱水汚
泥にする脱水汚泥化手段を設けてあるだけであった。Conventionally, in the above-mentioned waste treatment plant, means for treating dust containing heavy metals from a wet exhaust gas cleaning device include chemical (chelate) treatment means for preventing elution of heavy metals, and aggregation of the dust. -Only a means for dehydrating sludge to settle into dewatered sludge was provided.
【0005】[0005]
【発明が解決しようとする課題】上記従来の構成によれ
ば、排ガス洗浄装置からの重金属を含むダストを処理す
る手段としては、重金属溶出防止のための薬剤処理手段
や、重金属を含むダストを凝集・沈殿させて脱水汚泥に
する脱水汚泥化手段を設けてあるだけであったために、
脱水汚泥を最終処分場に埋立てなければならず、最終処
分場の確保に多くの時間と労力が必要になるという問題
や、環境保全の面で好ましくないという問題があり、改
善の余地が残されていた。According to the above-mentioned conventional construction, as means for treating dust containing heavy metals from an exhaust gas cleaning apparatus, there are chemical treatment means for preventing elution of heavy metals, and aggregation of dust containing heavy metals.・ Because only dewatering sludge conversion means to settle and make dewatered sludge was provided,
Dewatered sludge must be landfilled at the final disposal site, which requires a lot of time and labor to secure the final disposal site, and it is not desirable in terms of environmental conservation, leaving room for improvement. It had been.
【0006】本発明の目的は、廃棄物の最終処分場を不
要にすることができて、環境を保護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 which can eliminate the need for a final disposal site for waste and protect the environment.
【0007】[0007]
【課題を解決するための手段】請求項1による発明の構
成・作用・効果は次の通りである。The constitution, operation and effect of the invention according to claim 1 are as follows.
【0008】[構成]冒頭に記載した廃棄物処理プラン
トにおいて、前記排ガス洗浄装置を湿式の排ガス洗浄装
置に構成するとともに、前記脱水汚泥を前記熱分解ドラ
ムと燃焼溶融炉との少なくとも一方に供給する脱水汚泥
供給手段を設けてある。In the waste treatment plant described at the beginning, the exhaust gas cleaning device is configured as a wet exhaust gas cleaning device, and the dewatered sludge is supplied to at least one of the pyrolysis drum and a combustion melting furnace. Dewatered sludge supply means is provided.
【0009】[作用]湿式の排ガス洗浄装置からの重金
属を含むダストを脱水汚泥化手段で凝集・沈殿させて脱
水汚泥にする。[Operation] Dust containing heavy metals from a wet exhaust gas cleaning apparatus is coagulated and precipitated by dewatering sludge forming means to make dewatered sludge.
【0010】そして、脱水汚泥を脱水汚泥供給手段で熱
分解ドラムと燃焼溶融炉との少なくとも一方に供給す
る。Then, the dewatered sludge is supplied to at least one of the pyrolysis drum and the combustion melting furnace by the dewatered sludge supply means.
【0011】この種の廃棄物処理プラントでは、燃焼溶
融炉にカーボン残渣や集塵ダストが吹き込まれ、これら
が燃焼・溶融して、炉底からスラグが排出される。In this type of waste treatment plant, carbon residues and dust dust are blown into a combustion melting furnace, which burns and melts, and slag is discharged from the furnace bottom.
【0012】上記のように、脱水汚泥を熱分解ドラムと
燃焼溶融炉との少なくとも一方に供給すると、脱水汚泥
中の重金属が燃焼溶融炉内で前記スラグ中に封じ込めら
れて前記炉底から排出される。As described above, when the dewatered sludge is supplied to at least one of the pyrolysis drum and the combustion melting furnace, heavy metals in the dewatered sludge are sealed in the slag in the combustion melting furnace and discharged from the furnace bottom. You.
【0013】前記スラグは一般に道路舗装材として利用
されるから、請求項1の構成によれば、重金属が廃棄物
として出ることがない。Since the slag is generally used as a road pavement material, according to the first aspect of the present invention, no heavy metal is emitted as waste.
【0014】[効果]従って、脱水汚泥を最終処分場に
埋立てなくてもよくなって、廃棄物の最終処分場を不要
にすることができ、環境を保護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, there is no need to bury dewatered sludge in a final disposal site, and a final disposal site for waste can be made unnecessary, thereby providing a waste treatment plant capable of protecting the environment. Was completed.
【0015】請求項2による発明の構成・作用・効果は
次の通りである。The structure, operation and effect of the invention according to claim 2 are as follows.
【0016】[構成]請求項1による発明の構成におい
て、前記脱水汚泥化手段からの水溶したNaClを水か
ら回収する塩回収装置を設けてある。[Structure] In the structure according to the first aspect of the present invention, a salt recovery apparatus is provided for recovering water-soluble NaCl from the dewatering sludge forming means from water.
【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、塩回収装置で脱
水汚泥化手段からの水溶したNaCl(塩化ナトリウ
ム)を水から回収するので、NaClを工業塩として再
利用することができる。[Action] In addition to providing the same action as the action according to the first aspect, the water-soluble NaCl (sodium chloride) from the dewatering sludge forming means is recovered from the water by the salt recovery apparatus. NaCl can be reused as industrial salt.
【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、廃棄物
が出なくなって、より環境を保護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 of the configuration of the first aspect, it is possible to provide a waste treatment plant that does not generate waste and can further protect the environment. Was.
【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。Embodiments of the present invention will be described below with reference to the drawings.
【0020】図1に廃棄物処理プラントとしての熱分解
ガス化溶融プラントを示してある。この熱分解ガス化溶
融プラントは前処理設備1・熱分解反応設備2・熱分解
残渣選別設備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。FIG. 1 shows a pyrolysis gasification and melting plant as a waste treatment plant. This pyrolysis gasification and melting plant includes a pretreatment facility 1, a pyrolysis reaction facility 2, a pyrolysis residue sorting facility 3, a high-temperature combustion and melting facility 4, a boiler power generation facility 5, and an exhaust gas treatment facility 6.
【0021】[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8で150mm角以下に破砕し、破
砕廃棄物を搬送装置9で熱分解ドラム設備2に送る。[Pretreatment facility 1] The waste stored in the waste pit 7 is crushed by a crusher 8 to 150 mm square or less, and the crushed waste is sent to the pyrolysis drum facility 2 by a transport device 9.
【0022】[熱分解ドラム設備2]廃棄物ピット7か
らの廃棄物をスクリューコンベア10を介して熱分解ド
ラム12内に受け入れて、廃棄物を無酸素あるいは低酸
素雰囲気で約450°Cの熱分解ガスと熱分解残渣とに
熱分解する。[Thermal Decomposition Drum Facility 2] The waste from the waste pit 7 is received into the thermal decomposition drum 12 via the screw conveyor 10, and the waste is heated to about 450 ° C. in an oxygen-free or low-oxygen atmosphere. Decomposes into cracked gas and pyrolysis residue.
【0023】熱分解ガスは高温燃焼溶融炉13に送り、
熱分解残渣は熱分解残渣選別設備3に送る。The pyrolysis gas is sent to a high-temperature combustion melting furnace 13,
The pyrolysis residue is sent to the pyrolysis residue sorting equipment 3.
【0024】[熱分解残渣選別設備3]熱分解反応設備
2からの熱分解残渣を冷却コンベア14で冷却しながら
搬送し、スクリーン15・選別器16(磁選器やアルミ
選別器)を介して、鉄・アルミニウム・銅・ガラス等の
有価物を選別回収し、有価物以外のカーボン残渣を高温
燃焼溶融炉13に送る。[Thermal Decomposition Residue Sorting Facility 3] The pyrolysis residue from the pyrolysis reaction facility 2 is conveyed while being cooled by a cooling conveyor 14, and is passed through a screen 15 and a sorter 16 (a magnetic sorter or an aluminum sorter). Valuables such as iron, aluminum, copper, and glass are sorted and collected, and carbon residues other than the valuables are sent to the high-temperature combustion melting furnace 13.
【0025】[高温燃焼溶融設備4]熱分解ガス・カー
ボン残渣・集塵ダスト(ボイラや集塵器からのダスト)
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
連続排出される。[High-temperature combustion / melting equipment 4] Pyrolysis gas, carbon residue, dust collection dust (dust from boiler and dust collector)
Is blown into the high-temperature combustion melting furnace 13 from the furnace top side, and these are swirled and burned. The incinerated ash and dust particles are melted and continuously discharged from the furnace bottom.
【0026】熱分解ドラム設備2で廃棄物が燃料化され
るから低空気比で燃焼させることができ、低空気比燃焼
により排ガスが少なくなる。多段燃焼・排ガス再循環さ
せて低NOx化し、十分な滞留時間をとって低ダイオキ
シン化する。Since the waste is converted into fuel in the pyrolysis drum facility 2, it can be burned at a low air ratio, and the combustion at a low air ratio reduces the amount of exhaust gas. Multi-stage combustion and recirculation of exhaust gas to reduce NOx, and sufficient residence time to reduce dioxin.
【0027】[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、約6
00°Cで過熱蒸気管群に送り、エコノマイザーを通し
て約200°Cで集塵器17に送る。ボイラ18で40
ata・400°Cの蒸気を熱回収し、タービン19・
発電機20で電気として回収する。[Boiler power generation equipment 5] Exhaust gas is cooled in a boiler radiation zone and brought to a uniform temperature in an evaporating tube group.
It is sent to the superheated steam tube group at 00 ° C and sent to the dust collector 17 at about 200 ° C through an economizer. 40 at boiler 18
ata ・ 400 ° C steam and heat recovery
The electricity is collected by the generator 20.
【0028】[排ガス処理設備6]減温塔21・集塵器
17・湿式の排ガス洗浄装置22・活性コークス塔23
・脱硝装置24・煙突25等から成る。[Exhaust gas treatment equipment 6] Temperature reducing tower 21, dust collector 17, wet exhaust gas cleaning device 22, activated coke tower 23
It comprises a denitration device 24, a chimney 25, etc.
【0029】前記排ガス洗浄装置22は排ガスからHC
lやSOX を除去する装置で、反応剤として苛性ソーダ
が使用され、残渣として反応生成物である水溶したNa
Clや微量のダスト(重金属(Pb・Cd・Hg・Cr
等)を含む)が排出される。The exhaust gas cleaning device 22 removes HC from exhaust gas.
1 and SO X are removed by using caustic soda as a reactant, and as a residue, a reaction product, water-soluble Na
Cl and a small amount of dust (heavy metals (Pb, Cd, Hg, Cr
Etc.) are discharged.
【0030】前記活性コークス塔23はダイオキシンを
除去し、脱硝装置24はNOX を除去する。[0030] The activated coke tower 23 removes dioxin, NOx removal apparatus 24 for removing NO X.
【0031】前記排ガス洗浄装置22からの残渣を処理
する排ガス残渣処理部31を設けてある。次に、排ガス
残渣処理部31について説明する。An exhaust gas residue treatment section 31 for treating the residue from the exhaust gas cleaning device 22 is provided. Next, the exhaust gas residue processing section 31 will be described.
【0032】図1,図2に示すように、前記排ガス残渣
処理部31は、排ガス洗浄装置22からの残渣から重金
属(Pb・Cd・Hg・Cr等)が溶出するのを防止す
る薬剤処理手段26と、薬剤処理手段26からの重金属
を含むダストを凝集沈殿させて脱水汚泥にする脱水汚泥
化手段27と、脱水汚泥化手段27からの、NaClが
水溶した水溶液を水銀処理する水銀処理手段28と、水
銀処理手段28からの前記水溶液からNaClを回収す
る塩水蒸発機29(塩回収装置に相当)と、脱水汚泥を
熱分解ドラム12に供給する脱水汚泥供給手段30とを
設けて構成してある。As shown in FIGS. 1 and 2, the exhaust gas residue treatment section 31 is a chemical treatment means for preventing heavy metals (Pb, Cd, Hg, Cr, etc.) from being eluted from the residue from the exhaust gas cleaning device 22. 26, a dewatering sludge means 27 for coagulating and sedimenting the dust containing heavy metals from the chemical treatment means 26 into dewatered sludge, and a mercury treatment means 28 from the dewatering sludge means 27 for mercury-treating the aqueous solution of NaCl in water And a salt water evaporator 29 (corresponding to a salt recovery device) for recovering NaCl from the aqueous solution from the mercury treatment means 28, and a dewatered sludge supply means 30 for supplying dewatered sludge to the pyrolysis drum 12. is there.
【0033】図2において、No.1BFとは集塵器の
一例である第1バグフィルターの略称である。スクラバ
は周知のように排ガス洗浄装置の一例である。In FIG. 1BF is an abbreviation for a first bag filter which is an example of a dust collector. As is well known, a scrubber is an example of an exhaust gas cleaning device.
【0034】上記の構造により、湿式の排ガス洗浄装置
22からの残渣を薬剤処理手段26で薬剤処理して、残
渣から重金属が溶出するのを防止する。前記排ガス洗浄
装置22からの残渣には5%の重金属が残っており、塩
素は99%残っている。With the above structure, the residue from the wet exhaust gas cleaning device 22 is treated with the chemical treatment by the chemical treatment means 26 to prevent heavy metals from being eluted from the residue. In the residue from the exhaust gas cleaning device 22, 5% of heavy metal remains, and 99% of chlorine remains.
【0035】次に、薬剤処理手段26からの重金属を含
むダストを脱水汚泥化手段27で凝集・沈殿させて脱水
汚泥にする。Next, the dust containing the heavy metal from the chemical treatment means 26 is aggregated and settled by the dewatering sludge forming means 27 to make dewatered sludge.
【0036】そして、脱水汚泥を脱水汚泥供給手段30
で熱分解ドラム12に供給する。また、塩水蒸発機29
で水銀処理手段28からの前記水溶液からNaClを回
収する。煙突25からは1%の塩素が排出される。Then, the dewatered sludge is supplied to the dewatered sludge supply means 30.
To the thermal decomposition drum 12. Also, the salt water evaporator 29
To recover NaCl from the aqueous solution from the mercury treatment means 28. From the chimney 25, 1% of chlorine is discharged.
【0037】本廃棄物処理プラントでは、高温燃焼溶融
炉13に熱分解ガス・カーボン残渣・集塵ダストを炉頂
側から吹き込んで旋回燃焼し、焼却灰・集塵ダストを燃
焼・溶融して、炉底からスラグを排出させるが、上記の
ように、脱水汚泥を熱分解ドラム12に供給すると、脱
水汚泥中の重金属が高温燃焼溶融炉13内でスラグ中に
封じ込められて前記炉底から排出される。In this waste treatment plant, pyrolysis gas, carbon residue, and dust dust are blown into the high-temperature combustion melting furnace 13 from the furnace top and swirled to burn and melt the incinerated ash and dust dust. The slag is discharged from the furnace bottom. When the dewatered sludge is supplied to the pyrolysis drum 12 as described above, heavy metals in the dewatered sludge are contained in the slag in the high-temperature combustion melting furnace 13 and discharged from the furnace bottom. You.
【0038】これにより前記炉底から排出されるスラグ
に重金属の全て(100%の重金属)が含まれることに
なる。塩素は含まれていない(0%)。Thus, the slag discharged from the furnace bottom contains all of the heavy metals (100% of heavy metals). Contains no chlorine (0%).
【0039】前記スラグは道路舗装材として利用される
から、上記構造によれば重金属が廃棄物として出ること
がない。Since the slag is used as a road pavement material, according to the above structure, no heavy metal is emitted as waste.
【0040】しかも、塩水蒸発機29で水銀処理手段2
8からの水溶液からNaClを回収するので、NaCl
を工業塩として再利用することができる。Further, the mercury treatment means 2 is provided by the salt water evaporator 29.
NaCl is recovered from the aqueous solution from
Can be reused as an industrial salt.
【0041】これにより廃棄物がで出なくなり、廃棄物
の最終処分場を不要にすることができて、環境を保護で
きるようになる。As a result, no waste is generated, and a final disposal site for the waste can be eliminated, thereby protecting the environment.
【0042】[別実施形態]前記脱水汚泥供給手段30
は、前記脱水汚泥を高温燃焼溶融炉13に供給するよう
に構成してあってもよい。[Another Embodiment] The dewatered sludge supply means 30
May be configured to supply the dewatered sludge to the high-temperature combustion melting furnace 13.
【0043】また、前記脱水汚泥を熱分解ドラム12と
高温燃焼溶融炉13との両方に供給するよう構成してあ
ってもよい。Further, the dewatered sludge may be supplied to both the thermal decomposition drum 12 and the high-temperature combustion melting furnace 13.
【0044】前記塩水蒸発機29に換えて噴霧蒸発機を
設けてあってもよく、これらを塩回収装置と総称する。A spray evaporator may be provided instead of the salt water evaporator 29, and these are collectively referred to as a salt recovery device.
【0045】本発明は、前記塩回収装置を設けてない廃
棄物処理プラントにも適用することができる。The present invention can be applied to a waste treatment plant not provided with the salt recovery device.
【図1】熱分解ガス化溶融プラントの概略図FIG. 1 is a schematic diagram of a pyrolysis gasification and melting plant.
【図2】排ガス残渣処理部等を示す図FIG. 2 is a diagram showing an exhaust gas residue processing unit and the like.
【符号の説明】 12 熱分解ドラム 13 燃焼溶融炉 22 排ガス洗浄装置 26 薬剤処理手段 27 脱水汚泥化手段 29 塩回収装置 30 脱水汚泥供給手段[Description of Signs] 12 Pyrolysis drum 13 Combustion / melting furnace 22 Exhaust gas cleaning device 26 Chemical treatment device 27 Dehydration sludge conversion device 29 Salt recovery device 30 Dehydration sludge supply device
───────────────────────────────────────────────────── 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) C02F 11/00 F23G 5/16 ZABE 4D059 F23G 5/00 ZAB 7/00 ZAB 115 102B 5/027 ZAB B01D 53/34 125C 5/16 ZAB 134B 7/00 ZAB 136Z 102 F23J 15/00 C F23J 15/02 Fターム(参考) 3K061 AA07 AA16 AB02 AC02 BA05 3K070 DA03 DA05 DA21 DA23 3K078 AA05 AA06 BA26 CA02 4D002 AA02 AA19 AA28 AC04 BA02 BA14 BA20 CA01 CA13 DA02 DA12 DA35 EA02 EA05 FA04 4D004 AA01 AA36 AB07 AC05 BA02 BA03 CA04 CA09 CA24 CA26 CA27 CA28 CA32 CA40 CB04 CB13 CB34 CB42 CB43 CB45 CC03 CC12 4D059 AA11 BB03 BB04 CB01 CC04──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) C02F 11/00 F23G 5/16 ZABE 4D059 F23G 5/00 ZAB 7/00 ZAB 115 102B 5/027 ZAB B01D 53 / 34 125C 5/16 ZAB 134B 7/00 ZAB 136Z 102 F23J 15/00 C F23J 15/02 F term (reference) 3K061 AA07 AA16 AB02 AC02 BA05 3K070 DA03 DA05 DA21 DA23 3K078 AA05 AA06 BA26 CA02 4A002 AA02 AA02AA02A19A BA14 BA20 CA01 CA13 DA02 DA12 DA35 EA02 EA05 FA04 4D004 AA01 AA36 AB07 AC05 BA02 BA03 CA04 CA09 CA24 CA26 CA27 CA28 CA32 CA40 CB04 CB13 CB34 CB42 CB43 CB45 CC03 CC12 4D059 AA11 BB03 BB04 CB01 CC04
Claims (2)
解する熱分解ドラムを設けるとともに、前記熱分解ガス
と、前記熱分解残渣から選別されたカーボン残渣とを受
け入れて燃焼させる燃焼溶融炉を設け、排ガスからHC
lやSOX を除去する排ガス洗浄装置を設け、前記排ガ
ス洗浄装置からの重金属を含むダストを凝集沈殿させて
脱水汚泥にする脱水汚泥化手段を設けてある廃棄物処理
プラントであって、 前記排ガス洗浄装置を湿式の排ガス洗浄装置に構成する
とともに、前記脱水汚泥を前記熱分解ドラムと燃焼溶融
炉との少なくとも一方に供給する脱水汚泥供給手段を設
けてある廃棄物処理プラント。1. A pyrolysis drum for pyrolyzing waste into a pyrolysis gas and a pyrolysis residue and receiving and burning the pyrolysis gas and a carbon residue selected from the pyrolysis residue. Furnace is installed, and HC is
a waste gas treatment plant provided with a flue gas cleaning device for removing l and SO X , and provided with a dewatering sludge forming means for coagulating and sedimenting dust containing heavy metals from the flue gas cleaning device into dewatered sludge. A waste treatment plant comprising a cleaning device configured as a wet exhaust gas cleaning device and a dewatered sludge supply means for supplying the dewatered sludge to at least one of the pyrolysis drum and a combustion melting furnace.
Clを水から回収する塩回収装置を設けてある請求項1
記載の廃棄物処理プラント。2. The water-soluble Na from the dewatering sludge forming means.
2. A salt recovery device for recovering Cl from water is provided.
Waste treatment plant as described.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2001000943A JP2002205044A (en) | 2001-01-09 | 2001-01-09 | Waste treatment plant |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2001000943A JP2002205044A (en) | 2001-01-09 | 2001-01-09 | Waste treatment plant |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JP2002205044A true JP2002205044A (en) | 2002-07-23 |
Family
ID=18869638
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2001000943A Pending JP2002205044A (en) | 2001-01-09 | 2001-01-09 | Waste treatment plant |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP2002205044A (en) |
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2007029869A (en) * | 2005-07-27 | 2007-02-08 | Mettsu Corporation:Kk | Organic waste disposal methods |
| WO2008038992A1 (en) * | 2006-09-26 | 2008-04-03 | Gil Hyun Ahn | A deposited industrial waste thermodecomposition apparatus and decomposition method using thereof |
| WO2008081598A1 (en) * | 2006-12-28 | 2008-07-10 | N.M.G Environmental Development Co., Ltd. | Method for disposal of organic waste material and apparatus for the method |
| JP2013511386A (en) * | 2009-11-24 | 2013-04-04 | 株式会社北斗興業 | Waste to energy conversion by hydrothermal decomposition and resource regeneration methods. |
| CN103185343A (en) * | 2013-03-23 | 2013-07-03 | 安徽金鼎锅炉股份有限公司 | Hearth structure of incineration boiler |
-
2001
- 2001-01-09 JP JP2001000943A patent/JP2002205044A/en active Pending
Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2007029869A (en) * | 2005-07-27 | 2007-02-08 | Mettsu Corporation:Kk | Organic waste disposal methods |
| WO2008038992A1 (en) * | 2006-09-26 | 2008-04-03 | Gil Hyun Ahn | A deposited industrial waste thermodecomposition apparatus and decomposition method using thereof |
| WO2008081598A1 (en) * | 2006-12-28 | 2008-07-10 | N.M.G Environmental Development Co., Ltd. | Method for disposal of organic waste material and apparatus for the method |
| US8377264B2 (en) | 2006-12-28 | 2013-02-19 | N.M.G. Environmental Development Co., Ltd | Method for disposal of organic waste material and apparatus for the method |
| EP2111931B1 (en) * | 2006-12-28 | 2013-06-12 | N.M.G Environmental Development Co., Ltd. | Method for disposal of organic waste material and apparatus for the method |
| JP2013511386A (en) * | 2009-11-24 | 2013-04-04 | 株式会社北斗興業 | Waste to energy conversion by hydrothermal decomposition and resource regeneration methods. |
| CN103185343A (en) * | 2013-03-23 | 2013-07-03 | 安徽金鼎锅炉股份有限公司 | Hearth structure of incineration boiler |
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