JP2017057122A - Apparatus and method for treating cement kiln exhaust gas - Google Patents

Apparatus and method for treating cement kiln exhaust gas Download PDF

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JP2017057122A
JP2017057122A JP2015184801A JP2015184801A JP2017057122A JP 2017057122 A JP2017057122 A JP 2017057122A JP 2015184801 A JP2015184801 A JP 2015184801A JP 2015184801 A JP2015184801 A JP 2015184801A JP 2017057122 A JP2017057122 A JP 2017057122A
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exhaust gas
dust collector
cement kiln
activated carbon
calcium
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裕己 千葉
Hiromi Chiba
裕己 千葉
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Taiheiyo Cement Corp
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  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
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Abstract

PROBLEM TO BE SOLVED: To efficiently treat cement kiln exhaust gas at a low cost while effectively utilizing the thermal energy of eco-cement kiln exhaust gas.SOLUTION: A cement kiln exhaust gas treatment apparatus 1 comprises: a heat recovery device (boiler) 4 for recovering heat from exhaust gas G1 of an eco-cement kiln 2; a high-temperature dust collector (high-temperature bag filter) 6 that collects exhaust gas G2 of the heat recovery device 4 and has heat resistance of at least 350°C or higher; a catalyst device 7 for removing harmful substances in exhaust gas G4 of the high-temperature dust collector 6; a calcium-based agent adding device 8 for adding a calcium-based agent to exhaust gas G5 of the catalyst device 7; and a dust collector (high-temperature bag filter) 9 for collecting exhaust gas G6 to which the calcium-based agent has been added. The cement kiln exhaust gas treatment apparatus 1 may include an activated carbon adding device 11 for adding activated carbon AC to exhaust gas G8 of the dust collector 9, and a second dust collector (wet type scrubber) 12 for collecting exhaust gas G9 to which the activated carbon AC has been added.SELECTED DRAWING: Figure 1

Description

本発明は、エコセメントを製造するエコセメントキルンの排ガスを処理する装置及び方法に関する。   The present invention relates to an apparatus and a method for treating exhaust gas from an ecocement kiln for producing ecocement.

エコセメントは、都市ごみや下水汚泥の焼却灰と、従来のセメント原料とを用いて製造される。このエコセメントの焼成装置は、図2に示すように、セメントキルン2と、セメントキルン2で製造されたセメントクリンカを冷却するクリンカクーラ3とを備えるが、ダイオキシン類の再合成を抑制するため、セメントキルン2の排ガスG11の全量を排ガス冷却設備22で冷却する。   Ecocement is manufactured using incineration ash from municipal waste and sewage sludge and conventional cement raw materials. As shown in FIG. 2, the ecocement firing apparatus includes a cement kiln 2 and a clinker cooler 3 that cools the cement clinker manufactured by the cement kiln 2. However, in order to suppress resynthesis of dioxins, The entire amount of the exhaust gas G11 of the cement kiln 2 is cooled by the exhaust gas cooling facility 22.

また、排ガス冷却設備22の排ガスG12から塩素分や、焼却灰に含まれる重金属類等に由来する有害物質を除去するため、排ガスG12をサイクロン5で粗粉Cと、微粉を含む排ガスG13とに分離し、ろ過式集塵装置23で排ガスG13から微粉Fを除去し、微粉Fを除去した排ガスG14に消石灰添加装置24によって消石灰を添加し、ろ過式集塵装置25で塩素分、SOx等の酸性成分Aを除去し、酸性成分Aを除去した排ガスG15からSOx、NOx、水銀、ダイオキシン類等を活性コークス塔26で除去し、活性コークス塔26の排ガスG16を煙突13から大気に放出する。   Further, in order to remove harmful substances derived from chlorine and heavy metals contained in incineration ash from the exhaust gas G12 of the exhaust gas cooling facility 22, the exhaust gas G12 is converted into coarse powder C and exhaust gas G13 containing fine powder by the cyclone 5. Separating and removing fine powder F from the exhaust gas G13 with the filtration dust collector 23, adding slaked lime with the slaked lime addition device 24 to the exhaust gas G14 from which the fine powder F has been removed, and using the filtration dust collector 25 with chlorine, SOx, The acidic component A is removed, SOx, NOx, mercury, dioxins and the like are removed from the exhaust gas G15 from which the acidic component A has been removed by the active coke tower 26, and the exhaust gas G16 of the active coke tower 26 is released from the chimney 13 to the atmosphere.

しかし、上記排ガス処理装置21では、セメントキルン2の排ガスG11の全量を冷却しているため、多量の熱エネルギーの損失になる。また、消石灰の添加による脱硫は効率的ではなく、活性コークス塔26においても脱硫を行っていた。さらに、活性コークス塔26における活性コークスの運転コストが高く、活性コークスの再生により生じた粉塵が煙突13から排出されたり、粉塵爆発の可能性もないとは言えず、改善の余地があった。   However, since the exhaust gas treatment device 21 cools the entire amount of the exhaust gas G11 of the cement kiln 2, a large amount of heat energy is lost. Further, desulfurization by addition of slaked lime is not efficient, and desulfurization is also performed in the activated coke tower 26. Further, the operating cost of the activated coke in the activated coke tower 26 is high, and it cannot be said that dust generated by the regeneration of activated coke is discharged from the chimney 13 or dust explosion is possible, and there is room for improvement.

そこで、本発明は、上記従来技術における問題点に鑑みてなされたものであって、エコセメントキルン排ガスの熱エネルギーを有効利用しながら、効率よく低コストでセメントキルン排ガスを処理することを目的とする。   Therefore, the present invention has been made in view of the above problems in the prior art, and aims to treat cement kiln exhaust gas efficiently and at low cost while effectively using the thermal energy of the eco cement kiln exhaust gas. To do.

上記目的を達成するため、本発明は、エコセメントキルンの排ガスから熱回収する熱回収装置と、該熱回収装置の排ガスを集塵し、少なくとも350℃以上の耐熱性を有する高温集塵装置と、該高温集塵装置の排ガス中の有害物質を除去する触媒装置と、該触媒装置の排ガスにカルシウム系薬剤を添加するカルシウム系薬剤添加装置と、該カルシウム系薬剤が添加された排ガスを集塵する集塵装置とを備えることを特徴とする。   To achieve the above object, the present invention provides a heat recovery device that recovers heat from exhaust gas from an eco-cement kiln, a high-temperature dust collector that collects the exhaust gas from the heat recovery device, and has heat resistance of at least 350 ° C. A catalyst device for removing harmful substances in the exhaust gas of the high-temperature dust collector, a calcium-based drug addition device for adding a calcium-based chemical to the exhaust gas of the catalyst device, and collecting the exhaust gas to which the calcium-based chemical is added And a dust collecting device.

本発明によれば、触媒装置で排ガス中のNOx、ダイオキシン類等の有害物質を除去すると共に、排ガス中の水銀と塩化水素とによる塩化水銀の生成反応を促進させ、触媒装置の排ガスにカルシウム系薬剤を添加して塩化水銀をカルシウム系薬剤に吸着させると共に、排ガス中のSOxとカルシウム系薬剤とを反応させて石膏にし、カルシウム系薬剤と石膏とを集塵装置で回収することで、効率よく低コストでセメントキルン排ガスを処理することができる。   According to the present invention, the catalytic device removes harmful substances such as NOx and dioxins in the exhaust gas, promotes the formation reaction of mercury chloride by mercury and hydrogen chloride in the exhaust gas, Adding chemicals to adsorb mercury chloride to calcium chemicals, reacting SOx in exhaust gas with calcium chemicals to make gypsum, and collecting calcium chemicals and gypsum with a dust collector efficiently Cement kiln exhaust gas can be treated at low cost.

また、触媒装置の前段に350℃以上の耐熱性を有する高温集塵装置を備えることで、熱回収装置で回収した熱等で排ガスを再加熱せずに高温の排ガスを触媒装置に導入し、触媒装置の触媒を活性させると共に、集塵装置において回収するダスト中のカルシウム系薬剤と石膏の濃度を高めることができる。   In addition, by providing a high temperature dust collector having heat resistance of 350 ° C. or higher in the front stage of the catalyst device, high temperature exhaust gas is introduced into the catalyst device without reheating the exhaust gas with heat recovered by the heat recovery device, It is possible to activate the catalyst of the catalyst device and increase the concentration of the calcium-based drug and gypsum in the dust collected in the dust collector.

上記セメントキルン排ガス処理装置は、前記集塵装置の排ガスに活性炭を添加する活性炭添加装置と、該活性炭が添加された排ガスを集塵する第2の集塵装置とを備えることができる。これにより、排ガス中の水銀やダイオキシン類等の有害物質をより確実に除去することができる。尚、活性炭には、未使用のものの他に使用済みのものを用いることができる。   The cement kiln exhaust gas treatment device can include an activated carbon addition device that adds activated carbon to the exhaust gas of the dust collector, and a second dust collector that collects the exhaust gas to which the activated carbon is added. Thereby, harmful substances such as mercury and dioxins in the exhaust gas can be more reliably removed. The activated carbon can be used as well as unused.

さらに、前記第2の集塵装置は湿式集塵装置であって、該湿式集塵装置から排出されたスラリーを固液分離する固液分離装置を備えることができる。これにより、有害物質を吸着した活性炭が湿式集塵装置内で洗浄されて有害物質を脱着し、有害物質脱着後の活性炭が固液分離装置で固体側に排出されるため、排出された活性炭を活性炭添加装置やその他の装置で再利用することができる。   Furthermore, the second dust collector is a wet dust collector, and can include a solid-liquid separator that solid-liquid separates the slurry discharged from the wet dust collector. As a result, the activated carbon that has adsorbed the toxic substances is washed in the wet dust collector to desorb the toxic substances, and the activated carbon after desorption of the toxic substances is discharged to the solid side by the solid-liquid separator. It can be reused in activated carbon addition equipment and other equipment.

また、前記熱回収装置の排ガスを粗粉と、微粉を含むガスとに分離し、該微粉を含むガスを前記高温集塵装置に供給する分級装置を備えることができる。   Moreover, the classification | category apparatus which isolate | separates the waste gas of the said heat | fever recovery apparatus into coarse powder and the gas containing fine powder, and supplies the gas containing this fine powder to the said high temperature dust collector can be provided.

さらに、本発明は、セメントキルン排ガス処理方法であって、エコセメントキルンの排ガスから熱回収し、該熱回収した350℃以上の排ガスを集塵し、該集塵後の排ガス中の有害物質を触媒を用いて除去し、該有害物質を除去した排ガスにカルシウム系薬剤を添加し、該カルシウム系薬剤を添加した排ガスを集塵することを特徴とする。   Furthermore, the present invention is a cement kiln exhaust gas treatment method, wherein heat is recovered from exhaust gas from an eco-cement kiln, the exhaust gas at 350 ° C. or higher collected by heat recovery is collected, and harmful substances in the exhaust gas after the dust collection are collected. It is characterized by adding a calcium-based chemical to exhaust gas from which the harmful substances have been removed by using a catalyst, and collecting the exhaust gas to which the calcium-based chemical has been added.

本発明によれば、上記発明と同様に、触媒によって排ガス中のNOx、ダイオキシン類等の有害物質を除去すると共に、排ガス中の水銀と塩化水素とによる塩化水銀の生成反応を促進させ、触媒処理後の排ガスにカルシウム系薬剤を添加して塩化水銀をカルシウム系薬剤に吸着させると共に、排ガス中のSOxとカルシウム系薬剤とを反応させて石膏にし、カルシウム系薬剤と石膏とを集塵によって回収することで、効率よく低コストでセメントキルン排ガスを処理することができる。   According to the present invention, similarly to the above-described invention, the catalyst removes harmful substances such as NOx and dioxins in the exhaust gas, and promotes the formation reaction of mercury chloride by mercury and hydrogen chloride in the exhaust gas, thereby performing catalyst treatment. Add calcium-based chemical to later exhaust gas to adsorb mercury chloride to calcium-based chemical, react SOx in exhaust gas with calcium-based chemical to form gypsum, and collect calcium-based chemical and gypsum by collecting dust Thus, the cement kiln exhaust gas can be treated efficiently and at low cost.

また、350℃以上の排ガスを集塵することで、回収した熱等で排ガスを再加熱せずに高温の排ガスを触媒処理し、触媒を活性させると共に、カルシウム系薬剤を添加した排ガスを集塵して得られたダスト中のカルシウム系薬剤と石膏との濃度を向上させることができる。   In addition, by collecting the exhaust gas at 350 ° C or higher, the exhaust gas is not heated again by the recovered heat, etc., and the high temperature exhaust gas is catalyzed to activate the catalyst and collect the exhaust gas to which the calcium chemical is added. Thus, the concentration of the calcium-based drug and gypsum in the dust obtained can be improved.

以上のように、本発明によれば、エコセメントキルン排ガスの熱エネルギーを有効利用しながら、効率よく低コストでセメントキルン排ガスを処理することができる。   As described above, according to the present invention, the cement kiln exhaust gas can be processed efficiently and at low cost while effectively using the thermal energy of the eco cement kiln exhaust gas.

本発明に係るセメントキルン排ガスの処理装置の一実施の形態を示す全体構成図である。BRIEF DESCRIPTION OF THE DRAWINGS It is a whole block diagram which shows one Embodiment of the processing apparatus of the cement kiln exhaust gas which concerns on this invention. 従来のセメントキルン排ガスの処理装置の一例を示す全体構成図である。It is a whole block diagram which shows an example of the processing apparatus of the conventional cement kiln exhaust gas.

次に、本発明を実施するための形態について、図面を参照しながら詳細に説明する。   Next, an embodiment for carrying out the present invention will be described in detail with reference to the drawings.

図1は、本発明に係るセメントキルン排ガス処理装置の一実施の形態を示し、この処理装置1は、セメントキルン2及びクリンカクーラ3等を備えるエコセメント製造装置に付設され、セメントキルン2の排ガスG1から熱回収するボイラ4と、ボイラ4の排ガスG2を粗粉Cと、微粉を含む排ガスG3とに分離するサイクロン5と、サイクロン5の排ガスG3を集塵する高温バグフィルタ6と、高温バグフィルタ6の排ガスG4から有害物質を除去する触媒装置7と、触媒装置7の排ガスG5にカルシウム系薬剤(以下「Ca系薬剤」という。)を添加するCa系薬剤添加装置8と、Ca系薬剤添加装置8からCa系薬剤が添加された排ガスG6を集塵する高温バグフィルタ9とを備える。   FIG. 1 shows an embodiment of a cement kiln exhaust gas treatment apparatus according to the present invention. This treatment apparatus 1 is attached to an eco-cement manufacturing apparatus including a cement kiln 2, a clinker cooler 3, and the like, and exhaust gas from the cement kiln 2 is shown. Boiler 4 that recovers heat from G1, cyclone 5 that separates exhaust gas G2 from boiler 4 into coarse powder C and exhaust gas G3 that contains fine powder, high-temperature bag filter 6 that collects exhaust gas G3 from cyclone 5, and high-temperature bug A catalyst device 7 for removing harmful substances from the exhaust gas G4 of the filter 6, a Ca-based drug addition device 8 for adding a calcium-based drug (hereinafter referred to as "Ca-based drug") to the exhaust gas G5 of the catalyst device 7, and a Ca-based drug A high-temperature bag filter 9 for collecting the exhaust gas G6 to which the Ca-based chemical is added from the addition device 8;

また、処理装置1は、高温バグフィルタ9の排ガスG7から熱回収する熱回収装置10と、熱回収装置10の排ガスG8に活性炭ACを添加する活性炭添加装置11と、活性炭ACが添加された排ガスG9を湿式集塵する湿式スクラバ12と、湿式スクラバ12の排ガスG10を大気に放出する煙突13と、湿式スクラバ12から排出されたスラリーSをケーキCAとろ液Lとに分離する固液分離装置14と、ろ液Lを排水処理する排水処理装置15とを備える。   The processing apparatus 1 includes a heat recovery device 10 that recovers heat from the exhaust gas G7 of the high-temperature bag filter 9, an activated carbon addition device 11 that adds activated carbon AC to the exhaust gas G8 of the heat recovery device 10, and an exhaust gas to which activated carbon AC is added. A wet scrubber 12 that wet-collects G9, a chimney 13 that discharges exhaust gas G10 of the wet scrubber 12 to the atmosphere, and a solid-liquid separator 14 that separates the slurry S discharged from the wet scrubber 12 into cake CA and filtrate L And a waste water treatment device 15 for waste water treatment of the filtrate L.

ボイラ4は、セメントキルン2の排ガスG1から熱回収するために設けられる。このボイラ4は、800℃程度の排ガスG1を400℃以下に急冷する能力を有する。発生した蒸気は、エコセメント製造装置や他の装置で利用することができる。   The boiler 4 is provided to recover heat from the exhaust gas G1 of the cement kiln 2. The boiler 4 has an ability to rapidly cool the exhaust gas G1 at about 800 ° C. to 400 ° C. or less. The generated steam can be used in eco-cement manufacturing equipment and other equipment.

サイクロン5は、ボイラ4の排ガスG2を比較的塩素濃度の低い粗粉Cと、塩素濃度の高い微粉を含む排ガスG3とに分離するために備えられ、サイクロン以外の分級装置を用いることもできる。   The cyclone 5 is provided for separating the exhaust gas G2 of the boiler 4 into a coarse powder C having a relatively low chlorine concentration and an exhaust gas G3 containing a fine powder having a high chlorine concentration, and a classification device other than the cyclone can also be used.

高温バグフィルタ6は、排ガスG3中の微粉Fを回収するために備えられる。この高温バグフィルタ6には、900℃程度までの耐熱性を有し、複数の棒状のセラミック管からなるフィルタを備えるものなどを用いることができる。また、少なくとも350℃の耐熱性を有する高温集塵装置であれば、高温バグフィルタ以外の装置を用いることができる。   The high temperature bag filter 6 is provided for collecting the fine powder F in the exhaust gas G3. As this high-temperature bag filter 6, one having a heat resistance up to about 900 ° C. and including a filter made of a plurality of rod-shaped ceramic tubes can be used. In addition, a device other than the high-temperature bag filter can be used as long as it is a high-temperature dust collector having heat resistance of at least 350 ° C.

触媒装置7は、高温バグフィルタ6の排ガスG4に含まれるNOx、ダイオキシン類等の有害物質を除去すると共に、排ガスG4中の水銀と塩化水素とによる塩化水銀の生成反応を促進させるために備えられ、チタン・バナジウム系の脱硝触媒等を用いることができる。   The catalyst device 7 is provided for removing harmful substances such as NOx and dioxins contained in the exhaust gas G4 of the high-temperature bag filter 6 and for promoting the production reaction of mercury chloride by mercury and hydrogen chloride in the exhaust gas G4. Further, a titanium / vanadium-based denitration catalyst or the like can be used.

Ca系薬剤添加装置8は、触媒装置7の排ガスG5にCa系薬剤を添加し、排ガスG5中の塩化水銀を吸着させると共に、排ガスG5に含まれるSOxをCa系薬剤と反応させて石膏(CaSO4)にするために備えられる。 The Ca-based chemical addition device 8 adds a Ca-based chemical to the exhaust gas G5 of the catalyst device 7, adsorbs mercury chloride in the exhaust gas G5, and reacts SOx contained in the exhaust gas G5 with the Ca-based chemical to produce gypsum (CaSO 4 ) Provided to be in.

高温バグフィルタ9は、Ca系薬剤が添加された排ガスG6を集塵して石膏と、塩化水銀を吸着したCa系薬剤とを回収するために備えられる。尚、高温バグフィルタ9以外の高温集塵装置を用いることもでき、高温集塵装置以外の集塵装置を用いることもできる。   The high-temperature bag filter 9 is provided for collecting the gypsum and the Ca-based chemical adsorbing mercury chloride by collecting the exhaust gas G6 to which the Ca-based chemical is added. Note that a high-temperature dust collector other than the high-temperature bag filter 9 can be used, and a dust collector other than the high-temperature dust collector can also be used.

熱回収装置10は、高温バグフィルタ9の排ガスG7から熱回収し、排ガスG7の温度を湿式スクラバ12に導入するのに適した温度まで低下させるために備えられる。熱回収装置10は、排ガスG7と排ガスG10との熱交換を行うガスガスヒータとすることができるが、排ガスG7と排ガスG10以外の箇所との熱交換を行うものでもよい。また、ガスガスヒータ以外の熱交換器を用いてもよい。さらに、熱回収装置10に代えて排ガスG7を冷却する冷却装置を用いることもできる。   The heat recovery device 10 is provided for recovering heat from the exhaust gas G7 of the high-temperature bag filter 9 and reducing the temperature of the exhaust gas G7 to a temperature suitable for introduction into the wet scrubber 12. The heat recovery apparatus 10 can be a gas gas heater that performs heat exchange between the exhaust gas G7 and the exhaust gas G10, but may also perform heat exchange between a location other than the exhaust gas G7 and the exhaust gas G10. Moreover, you may use heat exchangers other than a gas gas heater. Further, a cooling device for cooling the exhaust gas G7 can be used instead of the heat recovery device 10.

活性炭添加装置11は、熱回収装置10の排ガスG8に活性炭ACを添加し、触媒装置7や高温バグフィルタ9で除去しきれなかった水銀やダイオキシン類等の有害物質を吸着させるために備えられる。活性炭ACは、ハロゲン族元素を含有するか否かに関わらず用いることができるが、含有するものを用いることで水銀の吸着効率を向上させることができる。また、活性炭ACの添加量は、活性炭原単位で10〜40mg/Nm3とすることが好ましく、これにより効果的にダイオキシン類及び水銀を吸着除去することができる。 The activated carbon addition device 11 is provided for adding activated carbon AC to the exhaust gas G8 of the heat recovery device 10 and adsorbing harmful substances such as mercury and dioxins that could not be removed by the catalyst device 7 and the high-temperature bag filter 9. Activated carbon AC can be used regardless of whether or not it contains a halogen group element. However, by using the activated carbon AC, the mercury adsorption efficiency can be improved. Moreover, it is preferable that the addition amount of activated carbon AC shall be 10-40 mg / Nm < 3 > in an activated carbon basic unit, and thereby dioxins and mercury can be adsorbed and removed effectively.

湿式スクラバ12は、活性炭ACが添加された排ガスG9を湿式集塵して排ガスG10とスラリーSとに分離して排出するために備えられる。尚、湿式スクラバ以外の湿式集塵装置を用いることもでき、湿式集塵装置以外の集塵装置を用いることもできる。   The wet scrubber 12 is provided to wet-collect the exhaust gas G9 to which the activated carbon AC is added, separate it into the exhaust gas G10 and the slurry S, and discharge it. A wet dust collector other than the wet scrubber can be used, and a dust collector other than the wet dust collector can also be used.

固液分離装置14は、湿式スクラバ12から排出されたスラリーSを固液分離するために備えられ、フィルタプレス、ベルトフィルタ等を用いることができる。また、排水処理装置15は、ろ液Lに硫化剤やキレート剤等を添加して排水処理をするために備えられる。   The solid-liquid separator 14 is provided for solid-liquid separation of the slurry S discharged from the wet scrubber 12, and a filter press, a belt filter, or the like can be used. Further, the waste water treatment device 15 is provided for performing waste water treatment by adding a sulfiding agent or a chelating agent to the filtrate L.

次に、上記構成を有する処理装置1を用いたセメントキルン排ガス処理方法について、図1を参照しながら説明する。   Next, a cement kiln exhaust gas treatment method using the treatment apparatus 1 having the above configuration will be described with reference to FIG.

セメントキルン2の窯尻に、都市ごみや下水汚泥の焼却灰と、セメント原料とを供給してセメントクリンカを焼成する。焼成したセメントクリンカをクリンカクーラ3で冷却し、得られたエコセメントクリンカを仕上ミル(不図示)で石膏等と共に粉砕してエコセメントを製造する。   Cement clinker is fired by supplying incineration ash of municipal waste and sewage sludge and cement raw material to the kiln bottom of cement kiln 2. The fired cement clinker is cooled by a clinker cooler 3, and the obtained eco cement clinker is pulverized with gypsum and the like in a finishing mill (not shown) to produce eco cement.

一方、セメントキルン2の排ガスG1をボイラ4に供給し、ボイラ4の排ガスG2の温度が350℃〜400℃になるように排ガスG1から熱回収する。   On the other hand, the exhaust gas G1 of the cement kiln 2 is supplied to the boiler 4, and heat is recovered from the exhaust gas G1 so that the temperature of the exhaust gas G2 of the boiler 4 is 350 ° C to 400 ° C.

排ガスG2をサイクロン5で分級して粗粉Cを分離し、セメントキルン2に戻してセメント原料とする。サイクロン5で分離された微粉を含む排ガスG3を高温バグフィルタ6に導入して微粉Fを回収する。350℃程度の高温バグフィルタ6の排ガスG4を触媒装置7に導入し、排ガスG4中のNOx、ダイオキシン類等の有害物質を除去すると共に、排ガスG4中の水銀と塩化水素とによる塩化水銀の生成反応を促進させる。   The exhaust gas G2 is classified by the cyclone 5 to separate the coarse powder C and returned to the cement kiln 2 to be used as a cement raw material. The exhaust gas G3 containing fine powder separated by the cyclone 5 is introduced into the high-temperature bag filter 6 to collect the fine powder F. The exhaust gas G4 of the high-temperature bag filter 6 at about 350 ° C. is introduced into the catalyst device 7 to remove harmful substances such as NOx and dioxins in the exhaust gas G4, and mercury chloride is generated by mercury and hydrogen chloride in the exhaust gas G4. Promote the reaction.

触媒装置7の排ガスG5にCa系薬剤添加装置8から消石灰等を含むCa系薬剤を添加し、Ca系薬剤と排ガスG5中のSOxとを反応させて石膏を生成させると共に、Ca系薬剤に排ガスG5中の塩化水銀を吸着させる。ここで、塩化水銀はCa系薬剤に吸着しやすい性質を有するため、効率的に水銀を吸着させることができる。   A Ca-based chemical containing slaked lime or the like is added from the Ca-based chemical addition device 8 to the exhaust gas G5 of the catalyst device 7 to cause the Ca-based chemical and SOx in the exhaust gas G5 to react to generate gypsum. Adsorb mercury chloride in G5. Here, since mercury chloride has the property of being easily adsorbed to Ca-based drugs, it can adsorb mercury efficiently.

また、Ca系薬剤は、排ガスG5中のSOxに対してCa系薬剤に含まれるCaがモル比で4.0以下、好ましくは1.5〜2.0とする。これにより、Ca系薬剤と排ガスG5中のSOxとを効率よく反応させることができる。   Further, the Ca-based chemical is such that Ca contained in the Ca-based chemical with respect to SOx in the exhaust gas G5 is 4.0 or less, preferably 1.5 to 2.0 in molar ratio. Thereby, Ca type | system | group chemical | medical agent and SOx in waste gas G5 can be made to react efficiently.

Ca系薬剤を添加した排ガスG6を高温バグフィルタ9に導入し、塩化水銀を吸着したCa系薬剤と石膏とをダストDとして回収する。高温バグフィルタ9の排ガスG7を熱回収装置10に導入して熱回収し、熱回収後の排ガスG8に活性炭添加装置11から活性炭ACを添加し、排ガスG8に残留する水銀やダイオキシン類等の有害物質を活性炭ACに吸着させる。   Exhaust gas G6 to which a Ca-based chemical is added is introduced into the high-temperature bag filter 9, and the Ca-based chemical adsorbed with mercury chloride and gypsum are collected as dust D. The exhaust gas G7 of the high-temperature bag filter 9 is introduced into the heat recovery device 10 to recover heat, and activated carbon AC is added from the activated carbon addition device 11 to the exhaust gas G8 after the heat recovery, and harmful substances such as mercury and dioxins remaining in the exhaust gas G8 The substance is adsorbed on activated carbon AC.

有害物質を吸着した活性炭を含む排ガスG9を湿式スクラバ12に導入し、湿式集塵によって排ガスG10とスラリーSとに分離する。活性炭を除去した排ガス10を煙突13から大気に放出し、活性炭を含むスラリーSを固液分離装置14でケーキCAとろ液Lとに固液分離する。ここで、活性炭に吸着した有害物質は湿式スクラバ12において活性炭から脱着するため、ケーキCAから得られる活性炭には有害物質が吸着されておらず、ケーキCAから得られる活性炭を活性炭添加装置11やその他の場所で再利用することができる。また、ろ液Lを排水処理装置15に供給して排水処理する。   The exhaust gas G9 containing activated carbon adsorbing harmful substances is introduced into the wet scrubber 12, and separated into the exhaust gas G10 and the slurry S by wet dust collection. The exhaust gas 10 from which the activated carbon has been removed is discharged from the chimney 13 to the atmosphere, and the slurry S containing the activated carbon is solid-liquid separated into the cake CA and the filtrate L by the solid-liquid separator 14. Here, since the harmful substance adsorbed on the activated carbon is desorbed from the activated carbon in the wet scrubber 12, the activated carbon obtained from the cake CA is not adsorbed, and the activated carbon obtained from the cake CA is used as the activated carbon addition device 11 and others. Can be reused at any place. Further, the filtrate L is supplied to the waste water treatment device 15 for waste water treatment.

以上のように、本実施の形態によれば、触媒装置7で排ガスG4中のNOx、ダイオキシン類等の有害物質を除去すると共に、排ガスG4中の水銀と塩化水素とによる塩化水銀の生成反応を促進させ、触媒装置7の排ガスG5にCa系薬剤を添加し、塩化水銀をCa系薬剤に吸着させると共に、排ガスG5中のSOxとCa系薬剤とを反応させて石膏にし、Ca系薬剤と石膏とを高温バグフィルタ9で回収することで、効率よく低コストでセメントキルン排ガスを処理することができる。   As described above, according to the present embodiment, the catalytic device 7 removes harmful substances such as NOx and dioxins in the exhaust gas G4, and also generates mercury chloride by the mercury and hydrogen chloride in the exhaust gas G4. The Ca-based chemical is added to the exhaust gas G5 of the catalyst device 7 to adsorb mercury chloride to the Ca-based chemical, and SOx in the exhaust gas G5 reacts with the Ca-based chemical to form gypsum. Is recovered by the high-temperature bag filter 9, so that the cement kiln exhaust gas can be treated efficiently and at low cost.

また、触媒装置7の前段に350℃以上の耐熱性を有する高温バグフィルタ6を備えることで、ボイラ4で回収した熱等で排ガスG4を再加熱せずに高温の排ガスG4を触媒装置7に導入し、触媒装置7の触媒を活性させると共に、高温バグフィルタ9において回収するダストD中のCa系薬剤と石膏との濃度を向上させることができる。   Moreover, by providing the high temperature bag filter 6 having a heat resistance of 350 ° C. or more in the front stage of the catalyst device 7, the high temperature exhaust gas G 4 is supplied to the catalyst device 7 without reheating the exhaust gas G 4 with heat recovered by the boiler 4. It can introduce and activate the catalyst of the catalyst apparatus 7, and can improve the density | concentration of Ca type | system | group chemical | medical agent and gypsum in the dust D collect | recovered in the high temperature bag filter 9. FIG.

尚、本実施の形態では、熱回収装置としてボイラ4を用いたが、その他の装置を用いて熱回収してもよく、サイクロン5を用いて排ガスG2から微粉を回収することなく排ガスG2を処理することもできる。   In this embodiment, the boiler 4 is used as the heat recovery device. However, heat recovery may be performed using another device, and the exhaust gas G2 is processed without using the cyclone 5 to recover fine powder from the exhaust gas G2. You can also

1 セメントキルン排ガス処理装置
2 セメントキルン
3 クリンカクーラ
4 ボイラ
5 サイクロン
6 高温バグフィルタ
7 触媒装置
8 Ca系薬剤添加装置
9 高温バグフィルタ
10 熱回収装置
11 活性炭添加装置
12 湿式スクラバ
13 煙突
14 固液分離装置
15 排水処理装置
AC 活性炭
C 粗粉
Ca Ca系薬剤
CA ケーキ
D ダスト
F 微粉
G1〜G10 排ガス
L ろ液
S スラリー
DESCRIPTION OF SYMBOLS 1 Cement kiln exhaust gas treatment apparatus 2 Cement kiln 3 Clinker cooler 4 Boiler 5 Cyclone 6 High temperature bag filter 7 Catalytic device 8 Ca system chemical | medical agent addition apparatus 9 High temperature bag filter 10 Heat recovery apparatus 11 Activated carbon addition apparatus 12 Wet scrubber 13 Chimney 14 Solid-liquid separation Device 15 Wastewater treatment device AC Activated carbon C Coarse powder Ca Ca-based chemical CA Cake D Dust F Fine powder G1 to G10 Exhaust gas L Filtrate S Slurry

Claims (5)

エコセメントキルンの排ガスから熱回収する熱回収装置と、
該熱回収装置の排ガスを集塵し、少なくとも350℃以上の耐熱性を有する高温集塵装置と、
該高温集塵装置の排ガス中の有害物質を除去する触媒装置と、
該触媒装置の排ガスにカルシウム系薬剤を添加するカルシウム系薬剤添加装置と、
該カルシウム系薬剤が添加された排ガスを集塵する集塵装置とを備えることを特徴とするセメントキルン排ガス処理装置。
A heat recovery device that recovers heat from the exhaust gas of the eco-cement kiln;
A high-temperature dust collector that collects the exhaust gas of the heat recovery device and has heat resistance of at least 350 ° C.,
A catalyst device for removing harmful substances in the exhaust gas of the high-temperature dust collector;
A calcium-based drug addition device for adding a calcium-based drug to the exhaust gas of the catalyst device;
A cement kiln exhaust gas treatment apparatus comprising: a dust collector that collects the exhaust gas to which the calcium-based chemical is added.
前記集塵装置の排ガスに活性炭を添加する活性炭添加装置と、
該活性炭が添加された排ガスを集塵する第2の集塵装置とを備えることを特徴とする請求項1に記載のセメントキルン排ガス処理装置。
An activated carbon addition device for adding activated carbon to the exhaust gas of the dust collector;
The cement kiln exhaust gas treatment device according to claim 1, further comprising a second dust collector that collects the exhaust gas to which the activated carbon is added.
前記第2の集塵装置は湿式集塵装置であって、該湿式集塵装置から排出されたスラリーを固液分離する固液分離装置を備えることを特徴とする請求項1又は2に記載のセメントキルン排ガス処理装置。   The said 2nd dust collector is a wet dust collector, Comprising: The solid-liquid separator which solid-liquid-separates the slurry discharged | emitted from this wet dust collector is characterized by the above-mentioned. Cement kiln exhaust gas treatment equipment. 前記熱回収装置の排ガスを粗粉と、微粉を含むガスとに分離し、該微粉を含むガスを前記高温集塵装置に供給する分級装置を備えることを特徴とする請求項1、2又は3に記載のセメントキルン排ガス処理装置。   The exhaust gas of the said heat recovery apparatus is isolate | separated into coarse powder and the gas containing fine powder, and the classification apparatus which supplies the gas containing this fine powder to the said high temperature dust collector is provided. The cement kiln exhaust gas treatment apparatus described in 1. エコセメントキルンの排ガスから熱回収し、
該熱回収した350℃以上の排ガスを集塵し、
該集塵後の排ガス中の有害物質を触媒を用いて除去し、
該有害物質を除去した排ガスにカルシウム系薬剤を添加し、
該カルシウム系薬剤を添加した排ガスを集塵することを特徴とするセメントキルン排ガス処理方法。
Heat recovery from the exhaust gas from the eco-cement kiln,
Collecting the heat-recovered exhaust gas of 350 ° C. or higher,
Use a catalyst to remove harmful substances in the exhaust gas after the dust collection,
Add calcium-based chemicals to the exhaust gas from which the harmful substances have been removed,
A cement kiln exhaust gas treatment method, wherein the exhaust gas to which the calcium-based chemical is added is collected.
JP2015184801A 2015-09-18 2015-09-18 Apparatus and method for treating cement kiln exhaust gas Pending JP2017057122A (en)

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