JP2011012875A - Method and device for suppressing generation of hydrogen chloride gas in waste gasification melting furnace - Google Patents

Method and device for suppressing generation of hydrogen chloride gas in waste gasification melting furnace Download PDF

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JP2011012875A
JP2011012875A JP2009156808A JP2009156808A JP2011012875A JP 2011012875 A JP2011012875 A JP 2011012875A JP 2009156808 A JP2009156808 A JP 2009156808A JP 2009156808 A JP2009156808 A JP 2009156808A JP 2011012875 A JP2011012875 A JP 2011012875A
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hydrogen chloride
chloride gas
melting furnace
waste gasification
gas
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Mitsumasa Todaka
光正 戸高
Toshiro Kato
敏郎 加藤
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Nippon Steel Engineering Co Ltd
Nippon Steel Plant Designing Corp
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Nittetsu Plant Designing Corp
Nippon Steel Engineering Co Ltd
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Abstract

PROBLEM TO BE SOLVED: To provide a method and device for suppressing generation of hydrogen chloride gas and sulfur oxide gas generated by burning of waste.SOLUTION: In the method and device for suppressing generation of hydrogen chloride gas in a waste gasification melting furnace, linestone fine powder of 1-30 μm is continuously blown into the flame of a combustion burner provided in a combustion chamber and burnt therein in the step of burning generated pyrolysis gas by the combustion burner in the waste gasification melting furnace.

Description

本発明は、廃棄物の燃焼によって発生する塩化水素ガスおよび硫黄酸化物ガスの発生を抑制する方法およびその装置に関するものである。   The present invention relates to a method and apparatus for suppressing the generation of hydrogen chloride gas and sulfur oxide gas generated by combustion of waste.

従来、廃棄物ガス化溶融炉においては、廃棄物中に含まれる塩素分や硫黄分はガス化溶融炉から発生する熱分解ガス中と同ガスに随伴する可燃性ダスト中に移行するが、大半はダスト中に含まれる。このダストが燃焼室に設けられた燃焼バーナで燃焼する過程で、人体に有害な硫黄酸化物ガス(SOx)や塩化水素ガス(HCl)が生成され、燃焼排ガス中に含まれる。   Conventionally, in waste gasification and melting furnaces, chlorine and sulfur contained in the waste are transferred to the pyrolysis gas generated from the gasification and melting furnace and combustible dust accompanying the gas. Is contained in dust. In the process of burning this dust with a combustion burner provided in the combustion chamber, sulfur oxide gas (SOx) and hydrogen chloride gas (HCl) harmful to the human body are generated and included in the combustion exhaust gas.

上記、有害ガスを除去するために、従来は、例えば特開2008−23484号公報(特許文献1)に開示されているように、燃焼排ガスをボイラー等で冷却後、バックフィルタ入口煙道に消石灰粉を吹込み、バックフィルタ濾布に付着した消石灰が濾布を通過する排ガス中のSOX やHClと反応することで排ガス中から除去することが一般に行われている。 In order to remove the toxic gas, conventionally, as disclosed in, for example, Japanese Patent Application Laid-Open No. 2008-23484 (Patent Document 1), the combustion exhaust gas is cooled by a boiler or the like, and then slaked lime is added to the back filter inlet flue. In general, slaked lime adhering to the back filter filter cloth is blown out and reacted with SO X and HCl in the exhaust gas passing through the filter cloth to be removed from the exhaust gas.

また、特開2006−297261号公報(特許文献2)に開示されているように、排ガスに含まれるダイオキシン類、NOx、SOxを同時に除去するために、電子ビーム照射手段の下流側に配置された第2集塵手段を設け、排ガスに含まれる煤塵を集塵する集塵手段から第2集塵手段に至るまでのガス流路途中に消石灰供給手段を設けて、第2集塵手段によって、硝酸、硫酸、塩化水素と消石灰との反応である、硝酸カルシウム、硫酸カルシウムを集塵する方法が提案されている。   Further, as disclosed in Japanese Patent Laid-Open No. 2006-297261 (Patent Document 2), in order to simultaneously remove dioxins, NOx, and SOx contained in the exhaust gas, it is disposed on the downstream side of the electron beam irradiation means. A second dust collecting means is provided, a slaked lime supply means is provided in the middle of the gas flow path from the dust collecting means for collecting the soot contained in the exhaust gas to the second dust collecting means, and the second dust collecting means A method of collecting calcium nitrate and calcium sulfate, which is a reaction between sulfuric acid, hydrogen chloride and slaked lime, has been proposed.

さらに、特開昭64−4222号公報(特許文献3)に開示されているように、被焼却物の燃焼により焼却炉から発生する排ガスを焼却炉から冷却用のガス冷却室及び有害ガス除去装置を経て集塵装置に至る排ガスの排出経路を介して排出する際に排ガス中に含まれる塩化水素を除去する方法において、塩化水素と接触反応させるための吸収剤を排出経路内の異なる場所で2段階に供給し、前段で使用する吸収剤より後段で使用する吸収剤の塩化水素吸収性能を向上させる排ガス中の塩化水素の除去方法が提案されている。
特開2008−23484号公報 特開2006−297261号公報 特開昭64−4222号公報
Furthermore, as disclosed in JP-A-64-4222 (Patent Document 3), a gas cooling chamber for cooling exhaust gas generated from the incinerator by combustion of the incineration object from the incinerator and a harmful gas removing device In the method of removing hydrogen chloride contained in the exhaust gas when discharged through the exhaust gas exhaust route leading to the dust collector, an absorbent for contact reaction with hydrogen chloride is added at different locations in the exhaust route. There has been proposed a method for removing hydrogen chloride in exhaust gas that is supplied to the stage and improves the hydrogen chloride absorption performance of the absorbent used in the subsequent stage rather than the absorbent used in the previous stage.
JP 2008-23484 A JP 2006-297261 A Japanese Unexamined Patent Publication No. 64-4222

上述した特許文献1は、燃焼排ガスをボイラー等で冷却後、バックフィルタ入口煙道に消石灰粉を吹込み、バックフィルタ濾布に付着した消石灰が濾布を通過する排ガス中のSOX やHClと反応することで排ガス中から除去するものであるが、しかし、燃焼室で発生するHClガスやSOxガスは酸性ガスであり、特にHClガスは高温で金属を強く腐食させるため、後段のボイラ伝熱管を腐食させる要因となっている。このためボイラの伝熱管の温度が制御され、蒸気温度が制御されている。このため、蒸気タービンで発電するシステムではボイラ伝熱管の腐食問題が発電効率に大きく影響している。 In Patent Document 1 described above, after cooling combustion exhaust gas with a boiler or the like, slaked lime powder is blown into the back filter inlet flue, and slaked lime adhering to the back filter filter cloth passes through the filter cloth with SO X and HCl. Although it is removed from the exhaust gas by reacting, the HCl gas and SOx gas generated in the combustion chamber are acidic gases, and since HCl gas strongly corrodes metals at high temperatures, the boiler heat transfer tube in the latter stage It is a factor that corrodes. For this reason, the temperature of the heat transfer tube of the boiler is controlled, and the steam temperature is controlled. For this reason, in a system that generates power with a steam turbine, the corrosion problem of the boiler heat transfer tube greatly affects the power generation efficiency.

また、シャフト炉式溶融炉においては、溶融スラグの塩基度調整のため、溶融炉に石灰石をごみと共に投入しているため、溶融炉発生ガスには石灰微粉が一部随伴しているため、燃焼室出口のHClは通常100〜150ppm、SOxは10ppm以下と大きく抑えられているが、ボイラ蒸気温度を高くするためには、さらに腐食環境を改善する必要があり、また、HClはごみ中の塩素分により発生するため、ごみ質により大きく変動するという特性があり、ボイラの腐食効果を得るには、さらなるこのHCl低減化や変動防止を図る必要がある。   Also, in the shaft furnace type melting furnace, limestone is put into the melting furnace together with debris to adjust the basicity of the molten slag. The HCl at the outlet of the room is usually suppressed to 100-150 ppm and SOx is below 10 ppm. However, in order to raise the boiler steam temperature, it is necessary to further improve the corrosive environment. Therefore, in order to obtain a corrosive effect of the boiler, it is necessary to further reduce the HCl and prevent the fluctuation.

さらに、引用文献2または3に示すように、排ガスに含まれる煤塵を集塵する集塵装置に至る排ガスの排出経路に消石灰を供給して排出する際に排ガス中に含まれる塩化水素を除去する方法が提案されているが、しかし、発生したHClやSOxガスはバックフィルタ入口で除去され、しかも低温でHCl、SOxと反応性が高い高価な消石灰粉が使用されるため、排ガス中のHClやSOxの2〜3倍の消石灰が必要となっているのが実状である。   Furthermore, as shown in the cited document 2 or 3, when supplying and discharging slaked lime to the exhaust gas discharge path leading to the dust collector that collects the dust contained in the exhaust gas, hydrogen chloride contained in the exhaust gas is removed. However, the generated HCl and SOx gas is removed at the back filter inlet, and expensive slaked lime powder that is highly reactive with HCl and SOx is used at a low temperature. The actual condition is that slaked lime 2 to 3 times the SOx is required.

上述のような問題や要請を解消するために、発明者らは鋭意開発を進めた結果、溶融炉で発生したガスを燃焼バーナで燃焼する過程で燃焼バーナの火炎中に石灰石微粉を吹込んで、燃焼で発生するHClやSOxを高温火炎中で反応させ、CaCl2 やCaSO4 等の塩類として捕捉すること。さらには、燃焼室出口の残存HClをレーザ式HCl計で連続計測し、ごみ質により変動するHClに対して石灰石吹込量を制御可能とした廃棄物ガス化溶融炉における塩化水素ガス発生抑制方法およびその装置を提供する。 In order to eliminate the problems and requests as described above, the inventors have intensively developed and as a result, injected limestone fine powder into the flame of the combustion burner in the process of burning the gas generated in the melting furnace with the combustion burner, HCl and SOx generated by combustion are reacted in a high-temperature flame and captured as salts such as CaCl 2 and CaSO 4 . Furthermore, a method for suppressing the generation of hydrogen chloride gas in a waste gasification and melting furnace, in which residual HCl at the combustion chamber outlet is continuously measured with a laser-type HCl meter, and the amount of limestone blown into HCl that varies depending on the waste quality can be controlled, and The device is provided.

その発明の要旨とするところは、
(1)廃棄物ガス化溶融炉において、発生した熱分解ガスを燃焼室に設けられた燃焼バーナで燃焼する過程において、該燃焼バーナの火炎中に1〜30μmの石灰石微粉を連続的に吹き込んで燃焼することを特徴とする廃棄物ガス化溶融炉における塩化水素ガス発生抑制方法。
The gist of the invention is that
(1) In the process of burning the generated pyrolysis gas in the waste gasification and melting furnace in the combustion burner provided in the combustion chamber, 1-30 μm fine limestone powder is continuously blown into the flame of the combustion burner. A method for suppressing the generation of hydrogen chloride gas in a waste gasification and melting furnace characterized by burning.

(2)前記(1)に記載の燃焼方法において、石灰石微粉の吹込位置を熱分解ガスが燃焼バーナに入る管路としたことを特徴とする廃棄物ガス化溶融炉における塩化水素ガス発生抑制方法。
(3)前記(1)に記載の燃焼方法において、燃焼室出口煙道に、レーザ光透過式塩化水素ガス分析計を用い、該塩化水素ガス分析計の分析値に基づいて石灰石の吹込量を制御することを特徴とする廃棄物ガス化溶融炉における塩化水素ガス発生抑制方法。
(2) In the combustion method as described in (1) above, a method for suppressing the generation of hydrogen chloride gas in a waste gasification and melting furnace, characterized in that the position where the limestone fine powder is blown is a conduit into which pyrolysis gas enters the combustion burner. .
(3) In the combustion method described in (1), a laser light transmission type hydrogen chloride gas analyzer is used for the combustion chamber outlet flue, and the amount of limestone blown in based on the analysis value of the hydrogen chloride gas analyzer. A method for suppressing the generation of hydrogen chloride gas in a waste gasification and melting furnace, characterized by controlling.

(4)廃棄物ガス化溶融炉において、燃焼室出口の一端にレーザ光透過式塩化水素ガス計発光器、他端にレーザ光透過式塩化水素ガス計受光器を配設し、該発光器から塩化水素ガスの吸光域の波長を持つレーザ光を発光し、他端の受光器で受光し、塩化水素ガス濃度に応じた吸光量を計測し、該塩化水素ガス濃度に応じた石灰石の切出し量を制御することを特徴とする廃棄物ガス化溶融炉における塩化水素ガス発生抑制装置にある。   (4) In a waste gasification and melting furnace, a laser light transmission type hydrogen chloride gas meter light emitter is disposed at one end of the combustion chamber outlet, and a laser light transmission type hydrogen chloride gas meter light receiver is disposed at the other end. Laser light having a wavelength in the absorption region of hydrogen chloride gas is emitted, received by a receiver at the other end, the amount of absorption according to the concentration of hydrogen chloride gas is measured, and the amount of limestone cut out according to the concentration of hydrogen chloride gas In a hydrogen chloride gas generation suppressing device in a waste gasification and melting furnace.

以下述べたように、本発明による安価な石灰石微粉を直接燃焼バーナの火炎中に連続的に吹き込んで燃焼させると同時に、燃焼室出口煙道に、レーザ光透過式塩化水素ガス分析計を用い、塩化水素ガス分析計の分析値に基づいて石灰石の吹込量を制御することにより、変動するHClに対して石灰石吹込量を制御可能することで、安価でかつHClの低減化による設備等の腐食を防止し、HClの変動防止を図り安定した操業方法および装置を提供することにある。   As described below, the low-cost limestone fine powder according to the present invention is continuously blown directly into the flame of the combustion burner and burned, and at the same time, a laser light transmission type hydrogen chloride gas analyzer is used for the combustion chamber outlet flue, By controlling the limestone injection amount based on the analysis value of the hydrogen chloride gas analyzer, the limestone injection amount can be controlled with respect to fluctuating HCl. An object of the present invention is to provide a stable operation method and apparatus by preventing the fluctuation of HCl.

以下、本発明について図面に従って詳細に説明する。
図1は、本発明に係る廃棄物ガス化溶融炉のシステム全体概略図である。この図1に示すように、ごみビットに貯留されたごみ11はごみクレーン10により溶融炉1に投入されごみの熱分解ガスは発生ガス管2を経由して燃焼室3に設置された燃焼バーナ8に送られる。一方、燃焼空気は燃焼空気ファン9より燃焼バーナ8に送られ、燃焼室3内で混合され燃焼する。燃焼ガスはボイラ4にて熱回収され、冷却されて、さらに水噴霧式ガス冷却塔5にて冷却されバックフィルタ6にて煤塵等の有害物質を除去して誘引送風機7により大気に排出される。
The present invention will be described in detail below with reference to the drawings.
FIG. 1 is an overall schematic view of a waste gasification melting furnace system according to the present invention. As shown in FIG. 1, garbage 11 stored in a garbage bit is introduced into a melting furnace 1 by a garbage crane 10, and pyrolysis gas of garbage is installed in a combustion chamber 3 via a generated gas pipe 2. 8 is sent. On the other hand, the combustion air is sent from the combustion air fan 9 to the combustion burner 8 and mixed and burned in the combustion chamber 3. The combustion gas is recovered by heat in the boiler 4, cooled, further cooled in the water spray type gas cooling tower 5, removed harmful substances such as dust by the back filter 6, and discharged to the atmosphere by the induction blower 7. .

この場合、HClやSOxの有害ガスは燃焼室3で発生すものであるが、この除去手段として、燃焼バーナの火炎中、特に燃焼バーナに入る管路に1〜30μmの石灰石微粉を連続的に吹き込んで燃焼させることにより、直接石灰石吹込装置から石灰石粉を吹込み、石灰石粉がHClまたはSOxとが反応し、下記式によりガス中から除去される。   In this case, noxious gases such as HCl and SOx are generated in the combustion chamber 3, but as a means for removing this, 1-30 μm limestone fine powder is continuously applied in the flame of the combustion burner, particularly in the pipeline entering the combustion burner. By blowing and burning, limestone powder is blown directly from the limestone blowing device, the limestone powder reacts with HCl or SOx, and is removed from the gas by the following formula.

CaCO3 → CaO+CO2 (熱分解)
CaO+H2 O → Ca(OH)2 (消石灰)
Ca(OH)2 +2HCl→ CaCl2 +2H2 O (脱塩化水素)
CaCO 3 → CaO + CO 2 (pyrolysis)
CaO + H 2 O → Ca (OH) 2 (slaked lime)
Ca (OH) 2 + 2HCl → CaCl 2 + 2H 2 O (dehydrochlorination)

図2は、本発明に係る実施例である溶融炉の断面図である。溶融炉発生ガスは発生ガス管2を経由して、燃焼バーナ8に送られ、複数のポート8aに分岐し、一方、燃焼空気は燃焼空気ファン9より燃焼バーナ8に送られ、発生ガスポートを挟むように配置された空気ポート8bを形成し、燃焼室内で液合燃焼する。石灰石微粉は石灰粉タンク14より石灰粉切出フィダー13から切出され、バーナ部の発生ガスの流路に投入され、発生ガスの気流により拡散分布してバーナガスポート8aより燃焼バーナの火炎中に入る。この火炎中で石灰石は下記式の熱分解し、反応性の高い生石灰に変化し、HClやSOxと燃焼室内で反応し、燃焼室出口のHClやSOxが抑えられる。   FIG. 2 is a sectional view of a melting furnace which is an embodiment according to the present invention. The melting furnace generated gas is sent to the combustion burner 8 via the generated gas pipe 2 and branched to a plurality of ports 8a. On the other hand, the combustion air is sent from the combustion air fan 9 to the combustion burner 8 and passes through the generated gas port. An air port 8b arranged so as to be sandwiched is formed, and liquid combustion is performed in the combustion chamber. The limestone fine powder is cut out from the lime powder cutting feeder 13 from the lime powder tank 14, is put into the flow path of the generated gas in the burner section, is diffused and distributed by the flow of the generated gas, and is burned in the flame of the combustion burner from the burner gas port 8a. to go into. In this flame, the limestone is thermally decomposed according to the following formula to change into highly reactive quicklime, reacts with HCl and SOx in the combustion chamber, and HCl and SOx at the outlet of the combustion chamber are suppressed.

また、石灰石微粉とした理由は、従来の消石灰の場合はHClとSOxとの反応性は高いが、しかし、消石灰は石灰石等を外部で熱分解する工程が必要なために石灰石に比べてかなりコスト高となるので実用的でない。また、石灰石微粉を1〜30μmとしたのは、1μm未満では作業性が悪く、30μmを超えるとHClとSOxとの反応性が悪くなることから、その範囲を1〜30μmとした。好ましくは10〜25μmとする。   The reason for making limestone fine powder is that the reactivity of HCl and SOx is high in the case of conventional slaked lime, but slaked lime is considerably more expensive than limestone because it requires a process of externally decomposing limestone. Since it becomes high, it is not practical. The reason why the limestone fine powder is 1 to 30 μm is that the workability is poor when it is less than 1 μm, and the reactivity between HCl and SOx is poor when it exceeds 30 μm, so the range is set to 1 to 30 μm. Preferably, it is 10 to 25 μm.

さらに、燃焼室出口には、レーザー式HCl計が設けられ、出口管の一端に設けた発光器15aから発光したHClガスの吸光域の波長を持つレーザ光12を発光し、受光器15bで受光し、HCl濃度に応じた吸光量を計測してHCl濃度を出力する。このHCl濃度に応じ、石灰石微粉の切出量を制御し、石灰粉切出フィダー13から切出され、燃焼室出口HCl濃度を適正な石灰石量で常に低い値に保つように制御される。さらに、吹込まれた石灰石微粉は、高温の火炎中では全量生石灰に変化するための未反応の生石灰はバックフィルタでは消石灰の代わりとして機能する。   Further, a laser type HCl meter is provided at the outlet of the combustion chamber, and laser light 12 having a wavelength in the absorption region of HCl gas emitted from the light emitter 15a provided at one end of the outlet pipe is emitted and received by the light receiver 15b. Then, the amount of absorption corresponding to the HCl concentration is measured and the HCl concentration is output. In accordance with this HCl concentration, the amount of limestone fine powder cut out is controlled and cut out from the lime powder cutout feeder 13, and the combustion chamber outlet HCl concentration is controlled to be kept at a low value with an appropriate amount of limestone. Furthermore, the limestone fine powder that has been blown is converted into quick lime in a high temperature flame, and unreacted quick lime functions as a substitute for slaked lime in the back filter.

以上のように、安価な石灰石微粉を直接燃焼バーナの火炎中に連続的に吹き込んで燃焼させると同時に、燃焼室出口煙道に、レーザ光透過式塩化水素ガス分析計を用い、塩化水素ガス分析計の分析値に基づいて石灰石の吹込量を制御することにより、変動するHClに対して石灰石吹込量を制御可能することで、安価でかつHClの低減化による設備等の腐食を防止し、かつHClの変動防止を図り安定した操業を可能とした。   As described above, low-cost limestone fine powder is directly blown into the flame of a direct combustion burner and burned, and at the same time, using a laser light transmission type hydrogen chloride gas analyzer in the combustion chamber outlet flue, hydrogen chloride gas analysis By controlling the amount of limestone blown based on the analytical value of the meter, the amount of limestone blown can be controlled with respect to fluctuating HCl, thereby preventing corrosion of equipment and the like due to reduction in HCl, and Preventing fluctuations in HCl, enabling stable operation.

本発明に係る廃棄物ガス化溶融炉のシステム全体概略図である。It is the whole system schematic diagram of the waste gasification melting furnace concerning the present invention. 本発明に係る実施例である溶融炉の断面図である。It is sectional drawing of the melting furnace which is the Example which concerns on this invention.

1 溶融炉
2 発生ガス管
3 燃焼室
4 ボイラ
5 水噴霧式ガス冷却塔
6 バックフィルタ
7 誘引送風機
8 燃焼バーナ
8a ポート
8b 空気ポート
9 燃焼空気ファン
10 ごみクレーン
11 ごみ
12 レーザ光
13 石灰粉切出フィダー
14 石灰粉タンク
15a 発光器
15b 受光器

特許出願人 新日鉄エンジニアリング株式会社 他1
代理人 弁理士 椎 名 彊 他1
DESCRIPTION OF SYMBOLS 1 Melting furnace 2 Generating gas pipe 3 Combustion chamber 4 Boiler 5 Water spray type gas cooling tower 6 Back filter 7 Induction fan 8 Combustion burner 8a Port 8b Air port 9 Combustion air fan 10 Garbage crane 11 Garbage 12 Laser light 13 Lime powder cutting Fider 14 Lime powder tank 15a Light emitter 15b Light receiver

Patent Applicant Nippon Steel Engineering Co., Ltd. 1
Attorney Attorney Shiina and others 1

Claims (4)

廃棄物ガス化溶融炉において、発生した熱分解ガスを燃焼室に設けられた燃焼バーナで燃焼する過程において、該燃焼バーナの火炎中に1〜30μmの石灰石微粉を連続的に吹き込んで燃焼することを特徴とする廃棄物ガス化溶融炉における塩化水素ガス発生抑制方法。 In the waste gasification and melting furnace, in the process of burning the generated pyrolysis gas with the combustion burner provided in the combustion chamber, 1-30 μm fine limestone powder is continuously blown into the flame of the combustion burner and burned A method for suppressing the generation of hydrogen chloride gas in a waste gasification and melting furnace. 請求項1に記載の燃焼方法において、石灰石微粉の吹込位置を熱分解ガスが燃焼バーナに入る管路としたことを特徴とする廃棄物ガス化溶融炉における塩化水素ガス発生抑制方法。 2. The method for suppressing the generation of hydrogen chloride gas in a waste gasification and melting furnace according to claim 1, wherein the limestone fine powder is blown at a position where the pyrolysis gas enters a combustion burner. 請求項1に記載の燃焼方法において、燃焼室出口に、レーザ光透過式塩化水素ガス分析計を配設し、該塩化水素ガス分析計の分析値に基づいて石灰石の吹込量を制御することを特徴とする廃棄物ガス化溶融炉における塩化水素ガス発生抑制方法。 2. The combustion method according to claim 1, wherein a laser light transmission type hydrogen chloride gas analyzer is disposed at the outlet of the combustion chamber, and the amount of limestone blown is controlled based on the analysis value of the hydrogen chloride gas analyzer. A method for suppressing generation of hydrogen chloride gas in a waste gasification and melting furnace. 廃棄物ガス化溶融炉において、燃焼室出口の一端にレーザ光透過式塩化水素ガス計発光器、他端にレーザ光透過式塩化水素ガス計受光器を配設し、該発光器から塩化水素ガスの吸光域の波長を持つレーザ光を発光し、他端の受光器で受光し、塩化水素ガス濃度に応じた吸光量を計測し、該塩化水素ガス濃度に応じた石灰石の切出し量を制御することを特徴とする廃棄物ガス化溶融炉における塩化水素ガス発生抑制装置。 In a waste gasification and melting furnace, a laser light transmission type hydrogen chloride gas meter light emitter is disposed at one end of the combustion chamber outlet, and a laser light transmission type hydrogen chloride gas meter light receiver is disposed at the other end. A laser beam having a wavelength in the light absorption region is emitted, received by a light receiver at the other end, the amount of absorption according to the hydrogen chloride gas concentration is measured, and the amount of limestone cut out according to the hydrogen chloride gas concentration is controlled. An apparatus for suppressing the generation of hydrogen chloride gas in a waste gasification melting furnace.
JP2009156808A 2009-07-01 2009-07-01 Method and device for suppressing generation of hydrogen chloride gas in waste gasification melting furnace Pending JP2011012875A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP2412432A1 (en) 2010-07-29 2012-02-01 Sony Corporation Nicotine Absorbent, Quinoline Absorbent, Benzopyrene Absorbent, Toluidine Absorbent, and Carcinogen Absorbent
JP2013053829A (en) * 2011-09-06 2013-03-21 Kawasaki Heavy Ind Ltd Boiler with corrosion inhibition apparatus and method for inhibiting corrosion of boiler
CN104401943A (en) * 2014-09-30 2015-03-11 南通星球石墨设备有限公司 Hydrogen chloride synthetic furnace control system

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS57117325A (en) * 1981-01-14 1982-07-21 Nippon Steel Corp Method of decreasing amount of noxious gas component in combustion gas discharged from refuse melting furnace
JPS61174927A (en) * 1985-01-28 1986-08-06 Hitachi Zosen Corp Dry type noxious gas removing apparatus
JPH074610A (en) * 1993-06-16 1995-01-10 Mitsubishi Heavy Ind Ltd Boiler with furnace desulphurization device
JP2006046825A (en) * 2004-08-05 2006-02-16 Takuma Co Ltd Treatment method and treatment apparatus of chlorine compound

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS57117325A (en) * 1981-01-14 1982-07-21 Nippon Steel Corp Method of decreasing amount of noxious gas component in combustion gas discharged from refuse melting furnace
JPS61174927A (en) * 1985-01-28 1986-08-06 Hitachi Zosen Corp Dry type noxious gas removing apparatus
JPH074610A (en) * 1993-06-16 1995-01-10 Mitsubishi Heavy Ind Ltd Boiler with furnace desulphurization device
JP2006046825A (en) * 2004-08-05 2006-02-16 Takuma Co Ltd Treatment method and treatment apparatus of chlorine compound

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP2412432A1 (en) 2010-07-29 2012-02-01 Sony Corporation Nicotine Absorbent, Quinoline Absorbent, Benzopyrene Absorbent, Toluidine Absorbent, and Carcinogen Absorbent
JP2013053829A (en) * 2011-09-06 2013-03-21 Kawasaki Heavy Ind Ltd Boiler with corrosion inhibition apparatus and method for inhibiting corrosion of boiler
CN104401943A (en) * 2014-09-30 2015-03-11 南通星球石墨设备有限公司 Hydrogen chloride synthetic furnace control system

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