WO2012124380A1 - Device and method for processing chlorine bypass exhaust gas - Google Patents

Device and method for processing chlorine bypass exhaust gas Download PDF

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WO2012124380A1
WO2012124380A1 PCT/JP2012/051520 JP2012051520W WO2012124380A1 WO 2012124380 A1 WO2012124380 A1 WO 2012124380A1 JP 2012051520 W JP2012051520 W JP 2012051520W WO 2012124380 A1 WO2012124380 A1 WO 2012124380A1
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gas
exhaust gas
chlorine bypass
extracted
kiln
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PCT/JP2012/051520
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French (fr)
Japanese (ja)
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淳一 寺崎
貴寛 林田
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太平洋セメント株式会社
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    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B7/00Hydraulic cements
    • C04B7/36Manufacture of hydraulic cements in general
    • C04B7/60Methods for eliminating alkali metals or compounds thereof, e.g. from the raw materials or during the burning process; methods for eliminating other harmful components
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D45/00Separating dispersed particles from gases or vapours by gravity, inertia, or centrifugal forces
    • B01D45/04Separating dispersed particles from gases or vapours by gravity, inertia, or centrifugal forces by utilising inertia
    • B01D45/08Separating dispersed particles from gases or vapours by gravity, inertia, or centrifugal forces by utilising inertia by impingement against baffle separators
    • B01D45/10Separating dispersed particles from gases or vapours by gravity, inertia, or centrifugal forces by utilising inertia by impingement against baffle separators which are wetted
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03CMAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03C3/00Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
    • B03C3/017Combinations of electrostatic separation with other processes, not otherwise provided for
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03CMAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03C3/00Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
    • B03C3/02Plant or installations having external electricity supply
    • B03C3/04Plant or installations having external electricity supply dry type
    • B03C3/09Plant or installations having external electricity supply dry type characterised by presence of stationary flat electrodes arranged with their flat surfaces at right angles to the gas stream
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/20Halogens or halogen compounds
    • B01D2257/202Single element halogens
    • B01D2257/2025Chlorine
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • B01D2258/0233Other waste gases from cement factories
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03CMAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03C2201/00Details of magnetic or electrostatic separation
    • B03C2201/24Details of magnetic or electrostatic separation for measuring or calculating parameters, efficiency, etc.
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03CMAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03C2201/00Details of magnetic or electrostatic separation
    • B03C2201/32Checking the quality of the result or the well-functioning of the device

Definitions

  • the present invention relates to an apparatus and a method for treating gas discharged from a chlorine bypass facility for extracting chlorine from a kiln exhaust gas passage from a kiln bottom of a cement kiln to a lowermost cyclone to remove chlorine.
  • a chlorine bypass facility for extracting chlorine from a kiln exhaust gas passage from a kiln bottom of a cement kiln to a lowermost cyclone to remove chlorine.
  • a chlorine bypass facility for extracting a part of combustion gas and removing chlorine is used.
  • the chlorine bypass facility includes a probe 83 for extracting a part of combustion gas from a kiln exhaust gas passage from a kiln bottom of a cement kiln 82 to a lowermost cyclone (not shown), and a probe 83.
  • a cooling fan 84 that cools the extraction gas G1 by supplying cold air therein, a cyclone 85 as a classifier that separates the coarse dust D1 contained in the extraction gas G1, and fine powder D2 discharged from the cyclone 85 are included.
  • a cooler 86 that cools the extracted gas G2
  • a cooling fan 87 that supplies cool air to the cooler 86
  • a bag filter 88 that collects the dust dust D2 in the extracted gas G2 cooled by the cooler 86
  • cooling A dust tank 89 that collects the fine powder D2 discharged from the vessel 86 and the bag filter 88.
  • the cold air from the cooling fan 84 is extracted.
  • fine crystals of chlorine compounds are produced. Since the fine crystals of the chlorine compound are unevenly distributed on the fine powder side of the dust contained in the extraction gas G1, the coarse powder D1 classified by the cyclone 85 is returned to the preheater or the like attached to the cement kiln 2 as a cement raw material.
  • the extraction gas G2 containing the fine powder D2 separated by the cyclone 85 is introduced into the cooler 86, the cooled extraction gas G2 is introduced into the bag filter 88, and the dust D2 contained in the extraction gas G2 in the bag filter 88 is removed. to recover.
  • the dust D2 recovered by the bag filter 88 is stored in the dust tank 89 as chlorine bypass dust having a high chlorine concentration together with the dust discharged from the cooler 86, and then discharged out of the cement firing process and processed.
  • an electrostatic precipitator may be used to process a gas with a relatively low chlorine concentration, such as an alkali bypass bleed gas attached to a cement firing device. Proposed.
  • a bag filter 88 is used to collect the fine powder D2.
  • the bag filter 88 has a problem in that since the pressure loss is high, the operation cost becomes high, and the maintenance cost is increased because the filter cloth needs to be periodically replaced.
  • the cooler 86 since it is necessary to adjust the temperature of the extraction gas G2 by installing the cooler 86 before introducing the extraction gas G2 to the bag filter 88, maintenance of the cooler 86 is also required. There is also a problem that heat loss occurs due to cooling of G2.
  • the cooler 86 is unnecessary, and maintenance and management of the cooler 86 and heat loss due to cooling do not occur. Furthermore, there is a problem that the operating cost is high due to high pressure loss.
  • the present invention has been made in view of the above-described problems in the prior art, and the gas discharged from the chlorine bypass facility (chlorine bypass exhaust gas) can be kept low in operating cost including maintenance and management costs. It aims at processing while suppressing loss.
  • the present invention is a chlorine bypass exhaust gas treatment apparatus for extracting a part of combustion gas from a kiln exhaust gas passage from the bottom of a cement kiln to the bottom cyclone, It is characterized by comprising a probe for cooling the burned combustion gas with a low temperature gas, and a filtration type electrostatic precipitator for collecting dust contained in the gas extracted by the probe.
  • a classifier for separating coarse dust from the extracted gas extracted by the probe is provided, and the extracted gas containing fine powder discharged from the classifier is supplied to the solid gas separating apparatus. be able to.
  • the present invention is characterized in that the chlorine bypass exhaust gas treatment apparatus is used, and the inlet gas temperature of the filtration type electrostatic precipitator is 150 ° C. or more and 500 ° C. or less, preferably 250 ° C. or more and 450 ° C. or less. And according to the present invention, since the outlet gas temperature of the filtration type electrostatic precipitator can be kept high, heat loss can be suppressed even when the exhaust gas system of the cement kiln is returned.
  • the equipment cost of the cooler can be reduced, and the cost for maintenance management of the cooler and the bag filter can be reduced.
  • FIG. 1 shows a chlorine bypass facility provided with an embodiment of a chlorine bypass exhaust gas treatment apparatus according to the present invention.
  • This chlorine bypass facility 1 is connected from the kiln bottom of a cement kiln 2 to a lowermost cyclone (not shown). From the kiln exhaust gas flow path, the probe 3 for extracting a part of the combustion gas G1 with cooling air from the cooling fan 4 and the coarse dust D1 contained in the extraction gas G1 extracted by the probe 3 are separated.
  • a fan 7 and the like for supplying the exhaust gas system at the subsequent stage.
  • a filter type electrostatic precipitator manufactured by Furukawa Industrial Systems Co., Ltd. as described in JP 2010-115618 A can be used, as shown in FIG.
  • discharge electrodes 63 and 64 for generating corona discharge and box-shaped dust collection electrodes 65 and 66 having both a dust collection function and a filter function, and the dust D in the dust-containing gas Gd is discharged.
  • box-shaped dust collection electrodes 65 and 66 having both a dust collection function and a filter function
  • the dust D in the dust-containing gas Gd is discharged.
  • the clean gas Gc from which the dust D has been removed is discharged from the dust collector outlet 62 to the exhaust gas system of the cement kiln 2.
  • this filtration type electrostatic precipitator 6 has a high dust collection efficiency because the gas passes perpendicular to the filter, and is equivalent to a high-temperature bag filter. Has dust collection efficiency.
  • the conventional electrostatic precipitator has a problem that the collected dust is re-scattered by striking, but the filter-type electrostatic precipitator 6 is filtered by the dust collecting electrodes 65 and 66 after the dust is re-scattered. Therefore, the dust concentration at the outlet does not increase significantly.
  • the dust collection electrodes 65 and 66 are used for the dust collection electrodes 65 and 66, and it can maintain a stable performance with excellent heat resistance, so it can be expected to have a long life and has less pressure loss than a bag filter. This leads to a reduction in operating costs. Furthermore, since the dust collection efficiency is higher than that of a conventional electric dust collector, the size of the main body is small with the same air volume, and space can be saved.
  • the design temperature of the filter type electrostatic precipitator 6 is 320 ° C.
  • the pressure loss of the main body is about 50 mmAq
  • the design temperature of the conventional bag filter is 150 ° C.
  • the pressure loss of the main body is about 150 mmAq.
  • a cooling fan is used to extract a part G of the combustion gas from the kiln exhaust gas flow path from the kiln bottom of the cement kiln 2 to the lowermost cyclone with the probe 3. Cool with cold air from 4. As a result, the extraction gas is rapidly cooled to about 550 ° C. or less, and a chlorine compound microcrystal is generated. Since the fine crystals of the chlorine compound are unevenly distributed on the fine powder side of the dust contained in the extraction gas G1, the coarse powder D1 classified by the cyclone 5 is returned to the preheater attached to the cement kiln 2 as a cement raw material.
  • the extraction gas G2 which contains the fine powder D2 separated by the cyclone 5 and is about 400 ° C., is introduced into the filtration type electrostatic precipitator 6 to collect the fine powder D2.
  • the dust D2 collected by the filtration type electrostatic precipitator 6 is discharged out of the cement firing process and processed.
  • the exhaust gas G3 discharged from the filtration type electrostatic precipitator 6 and supplied downstream by the fan 7 is an exhaust gas system of the cement kiln 2, that is, an outlet side of a fan (IDF) that induces the exhaust gas of the cement kiln 2,
  • the preheater attached to the cement kiln 2 can be returned.

Abstract

[Problem] To process chlorine bypass exhaust gas by keeping operating costs including maintenance management costs low, and by inhibiting heat loss. [Solution] A device for processing chlorine bypass exhaust gas (1), etc. comprising: a probe (3) which extracts a part (G1) of a combustion gas from a kiln exhaust gas passage from the kiln bottom of a cement kiln (2) to a lowermost cyclone and which cools the extracted combustion gas with a low temperature gas; and a filter type electrostatic precipitator (6) which collects dust (D2) contained in gas (G2) extracted with the probe. This device may also comprise a classifier (5) which separates coarse grain dust (D1) from the extraction gas extracted with the probe, and supply the extraction gas containing fine particles discharged from the classifier to a solid-gas separation device. An inlet gas temperature of the filter type electrostatic precipitator can be 150°C to 500°C.

Description

塩素バイパス排ガスの処理装置及び処理方法Chlorine bypass exhaust gas treatment device and treatment method
 本発明は、セメントキルンの窯尻から最下段サイクロンに至るまでのキルン排ガス流路より、燃焼ガスの一部を抽気して塩素を除去する塩素バイパス設備から排出される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 gas discharged from a chlorine bypass facility for extracting chlorine from a kiln exhaust gas passage from a kiln bottom of a cement kiln to a lowermost cyclone to remove chlorine. About.
 従来、セメント製造設備におけるプレヒータの閉塞等の問題を引き起こす原因となる塩素、硫黄、アルカリ等の中で、塩素が特に問題となることに着目し、セメントキルンの窯尻から最下段サイクロンに至るまでのキルン排ガス流路より、燃焼ガスの一部を抽気して塩素を除去する塩素バイパス設備が用いられている。 Focusing on chlorine, sulfur, alkali, etc., which causes problems such as blockage of preheaters in cement manufacturing facilities, from the bottom of the kiln kiln to the bottom cyclone From the kiln exhaust gas flow path, a chlorine bypass facility for extracting a part of combustion gas and removing chlorine is used.
 塩素バイパス設備は、図3に示すように、セメントキルン82の窯尻から最下段サイクロン(不図示)に至るまでのキルン排ガス流路より、燃焼ガスの一部を抽気するプローブ83と、プローブ83内に冷風を供給して抽気ガスG1を急冷する冷却ファン84と、抽気ガスG1に含まれるダストの粗粉D1を分離する分級機としてのサイクロン85と、サイクロン85から排出された微粉D2を含む抽気ガスG2を冷却する冷却器86と、冷却器86に冷風を供給する冷却ファン87と、冷却器86で冷却された抽気ガスG2中のダストの微粉D2を集塵するバグフィルタ88と、冷却器86及びバグフィルタ88から排出された微粉D2を回収するダストタンク89とを備える。 As shown in FIG. 3, the chlorine bypass facility includes a probe 83 for extracting a part of combustion gas from a kiln exhaust gas passage from a kiln bottom of a cement kiln 82 to a lowermost cyclone (not shown), and a probe 83. A cooling fan 84 that cools the extraction gas G1 by supplying cold air therein, a cyclone 85 as a classifier that separates the coarse dust D1 contained in the extraction gas G1, and fine powder D2 discharged from the cyclone 85 are included. A cooler 86 that cools the extracted gas G2, a cooling fan 87 that supplies cool air to the cooler 86, a bag filter 88 that collects the dust dust D2 in the extracted gas G2 cooled by the cooler 86, and cooling A dust tank 89 that collects the fine powder D2 discharged from the vessel 86 and the bag filter 88.
 上記構成を有する塩素バイパス設備81では、セメントキルン82の窯尻から最下段サイクロンに至るまでのキルン排ガス流路からの燃焼ガスの一部G1をプローブ83によって抽気しながら、冷却ファン84からの冷風によって冷却することで塩素化合物の微結晶が生成される。この塩素化合物の微結晶は、抽気ガスG1に含まれるダストの微粉側に偏在しているため、サイクロン85で分級した粗粉D1をセメントキルン2に付設されたプレヒータ等にセメント原料として戻す。 In the chlorine bypass facility 81 having the above-described configuration, while the part of the combustion gas G1 from the kiln exhaust gas flow path from the kiln bottom of the cement kiln 82 to the lowermost cyclone is extracted by the probe 83, the cold air from the cooling fan 84 is extracted. By cooling with, fine crystals of chlorine compounds are produced. Since the fine crystals of the chlorine compound are unevenly distributed on the fine powder side of the dust contained in the extraction gas G1, the coarse powder D1 classified by the cyclone 85 is returned to the preheater or the like attached to the cement kiln 2 as a cement raw material.
 一方、サイクロン85によって分離された微粉D2を含む抽気ガスG2を冷却器86に導入し、冷却された抽気ガスG2をバグフィルタ88に導入し、バグフィルタ88において抽気ガスG2に含まれるダストD2を回収する。バグフィルタ88で回収したダストD2は、冷却器86から排出されたダストと共に、塩素濃度の高い塩素バイパスダストとしてダストタンク89に貯留した後、セメント焼成工程の系外に排出し、処理する。 On the other hand, the extraction gas G2 containing the fine powder D2 separated by the cyclone 85 is introduced into the cooler 86, the cooled extraction gas G2 is introduced into the bag filter 88, and the dust D2 contained in the extraction gas G2 in the bag filter 88 is removed. to recover. The dust D2 recovered by the bag filter 88 is stored in the dust tank 89 as chlorine bypass dust having a high chlorine concentration together with the dust discharged from the cooler 86, and then discharged out of the cement firing process and processed.
 ところで、近年、ハニカムセル化した棒状のセラミック管を複数配列し、900℃程度までの耐熱性を有する高耐熱型のバグフィルタが開発され、塩素バイパス設備に導入することが提案されている(例えば、特許文献1参照)。 By the way, in recent years, a high heat-resistant bag filter having a plurality of rod-shaped ceramic tubes formed into honeycomb cells and having heat resistance up to about 900 ° C. has been developed and proposed to be introduced into a chlorine bypass facility (for example, , See Patent Document 1).
 また、塩素濃度の高いガスを処理対象とすることはできないが、セメント焼成装置に付設されたアルカリバイパスの抽気ガスなど、塩素濃度の比較的低いガスを処理するにあたって、電気集塵機を利用することも提案されている。 In addition, gas with a high chlorine concentration cannot be treated, but an electrostatic precipitator may be used to process a gas with a relatively low chlorine concentration, such as an alkali bypass bleed gas attached to a cement firing device. Proposed.
日本特開2009-298677号公報Japanese Unexamined Patent Publication No. 2009-298777
 上記塩素バイパス設備81では、微粉D2を集塵するにあたってバグフィルタ88を用いている。しかし、バグフィルタ88は、圧力損失が高いため運転コストが高くなると共に、ろ布を定期的に交換する必要があるため保守管理費用が増加するという問題がある。これに加え、バグフィルタ88へ抽気ガスG2を導入する前に冷却器86を設置して抽気ガスG2の調温をする必要があるため、冷却器86の保守も必要になり、さらに、抽気ガスG2の冷却により熱損失が生ずるという問題もある。 In the chlorine bypass facility 81, a bag filter 88 is used to collect the fine powder D2. However, the bag filter 88 has a problem in that since the pressure loss is high, the operation cost becomes high, and the maintenance cost is increased because the filter cloth needs to be periodically replaced. In addition, since it is necessary to adjust the temperature of the extraction gas G2 by installing the cooler 86 before introducing the extraction gas G2 to the bag filter 88, maintenance of the cooler 86 is also required. There is also a problem that heat loss occurs due to cooling of G2.
 特に、間接冷却方式の冷却器86を用いると、冷却器86内で固結が発生して能力が低下したり、閉塞状態となって運転継続が困難になる虞もある。また、セメントキルンの窯尻でリサイクル燃料を使用しているため、燃焼した燃料の一部がバグフィルタ88に達し、バグフィルタ88のろ布を目詰まりさせたり、ろ布を焼損する虞もある。 In particular, when the indirect cooling type cooler 86 is used, solidification may occur in the cooler 86 and the capacity may be reduced, or the operation may be difficult due to a closed state. In addition, since recycled fuel is used in the kiln bottom of the cement kiln, part of the burned fuel reaches the bag filter 88, and there is a possibility of clogging the filter cloth of the bag filter 88 or burning the filter cloth. .
 一方、上記高耐熱型バグフィルタを用いた場合には、冷却器86が不要となり、冷却器86の保守管理や、冷却による熱損失が生ずることはないが、このバグフィルタは保守管理コストが比較的高く、さらに、圧力損失が高いため運転コストも高くなるという問題がある。 On the other hand, when the high heat-resistant bag filter is used, the cooler 86 is unnecessary, and maintenance and management of the cooler 86 and heat loss due to cooling do not occur. Furthermore, there is a problem that the operating cost is high due to high pressure loss.
 そこで、本発明は、上記従来の技術における問題点に鑑みてなされたものであって、塩素バイパス設備から排出されるガス(塩素バイパス排ガス)を、保守管理費用を含む運転コストを低く抑え、熱損失を抑制しながら処理することを目的とする。 Therefore, the present invention has been made in view of the above-described problems in the prior art, and the gas discharged from the chlorine bypass facility (chlorine bypass exhaust gas) can be kept low in operating cost including maintenance and management costs. It aims at processing while suppressing loss.
 上記目的を達成するため、本発明は、塩素バイパス排ガスの処理装置であって、セメントキルンの窯尻から最下段サイクロンに至るまでのキルン排ガス流路より燃焼ガスの一部を抽気するとともに、抽気した燃焼ガスを低温ガスにより冷却するプローブと、該プローブで抽気されたガスに含まれるダストを集塵するろ過式電気集塵装置とを備えることを特徴とする。 In order to achieve the above object, the present invention is a chlorine bypass exhaust gas treatment apparatus for extracting a part of combustion gas from a kiln exhaust gas passage from the bottom of a cement kiln to the bottom cyclone, It is characterized by comprising a probe for cooling the burned combustion gas with a low temperature gas, and a filtration type electrostatic precipitator for collecting dust contained in the gas extracted by the probe.
 そして、本発明によれば、ろ過式電気集塵装置を用いて抽気ガスに含まれるダストを集塵するため、バグフィルタのバグの保守管理等が不要となり、圧力損失も低く抑えることができるため、運転コストを低く抑えることができる。 According to the present invention, since dust contained in the extraction gas is collected using a filtration type electrostatic precipitator, maintenance of the bug of the bag filter is unnecessary, and pressure loss can be kept low. The operating cost can be kept low.
 上記塩素バイパス排ガスの処理装置において、前記プローブにより抽気された抽気ガスから粗粉ダストを分離する分級機を設け、該分級機から排出される微粉を含む抽気ガスを前記固気分離装置に供給することができる。 In the chlorine bypass exhaust gas processing apparatus, a classifier for separating coarse dust from the extracted gas extracted by the probe is provided, and the extracted gas containing fine powder discharged from the classifier is supplied to the solid gas separating apparatus. be able to.
 また、本発明は、上記塩素バイパス排ガスの処理装置を用い、前記ろ過式電気集塵装置の入口ガス温度を150℃以上、500℃以下、好ましくは250℃以上、450℃以下とすることを特徴とする。本発明によれば、ろ過式電気集塵装置の出口ガス温度を高く維持することができるため、セメントキルンの排ガス系に戻した場合でも、熱損失を抑制することができる。 Further, the present invention is characterized in that the chlorine bypass exhaust gas treatment apparatus is used, and the inlet gas temperature of the filtration type electrostatic precipitator is 150 ° C. or more and 500 ° C. or less, preferably 250 ° C. or more and 450 ° C. or less. And According to the present invention, since the outlet gas temperature of the filtration type electrostatic precipitator can be kept high, heat loss can be suppressed even when the exhaust gas system of the cement kiln is returned.
 以上のように、本発明によれば、冷却器の設備コストを削減することができ、冷却器及びバグフィルタの保守管理にかかる費用を削減することができる。また、機器点数の減少や圧力損失抑制により電力等の運転コストの削減が可能になると共に、熱損失を抑制することのできる塩素バイパス排ガスの処理装置を提供することができる。 As described above, according to the present invention, the equipment cost of the cooler can be reduced, and the cost for maintenance management of the cooler and the bag filter can be reduced. In addition, it is possible to provide a chlorine bypass exhaust gas treatment apparatus capable of reducing operating costs such as electric power by reducing the number of devices and suppressing pressure loss and suppressing heat loss.
本発明にかかる塩素バイパス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 chlorine bypass waste gas concerning this invention. 図1の塩素バイパス排ガスの処理装置に用いるろ過式電気集塵装置の構造及び動作を説明するための概略断面図である。It is a schematic sectional drawing for demonstrating the structure and operation | movement of a filtration type electrostatic dust collector used for the processing apparatus of the chlorine bypass exhaust gas of FIG. 従来の塩素バイパス設備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 conventional chlorine bypass installation.
  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説明する。 Next, embodiments for carrying out the present invention will be described with reference to the drawings.
 図1は、本発明にかかる塩素バイパス排ガスの処理装置の一実施の形態を設けた塩素バイパス設備を示し、この塩素バイパス設備1は、セメントキルン2の窯尻から最下段サイクロン(不図示)に至るまでのキルン排ガス流路より、燃焼ガスの一部G1を冷却ファン4からの冷風で冷却しながら抽気するプローブ3と、プローブ3で抽気した抽気ガスG1に含まれるダストの粗粉D1を分離する分級機としてのサイクロン5と、サイクロン5から排出された抽気ガスG2に含まれる微粉D2を集塵するろ過式電気集塵装置6と、ろ過式電気集塵装置6から排出された排ガスG3を後段の排ガス系に供給するためのファン7等で構成される。プローブ3及びサイクロン5については、従来の塩素バイパス設備に設置されているものと同様の構成を有するため、詳細説明を省略する。 FIG. 1 shows a chlorine bypass facility provided with an embodiment of a chlorine bypass exhaust gas treatment apparatus according to the present invention. This chlorine bypass facility 1 is connected from the kiln bottom of a cement kiln 2 to a lowermost cyclone (not shown). From the kiln exhaust gas flow path, the probe 3 for extracting a part of the combustion gas G1 with cooling air from the cooling fan 4 and the coarse dust D1 contained in the extraction gas G1 extracted by the probe 3 are separated. A cyclone 5 as a classifier to be collected, a filtration type electrostatic precipitator 6 for collecting fine powder D2 contained in the extraction gas G2 discharged from the cyclone 5, and an exhaust gas G3 discharged from the filtration type electrostatic precipitator 6 It comprises a fan 7 and the like for supplying the exhaust gas system at the subsequent stage. About the probe 3 and the cyclone 5, since it has the structure similar to what is installed in the conventional chlorine bypass installation, detailed description is abbreviate | omitted.
 ろ過式電気集塵装置6は、例えば、特開2010-115618号公報に記載されたような古河産機システムズ株式会社製フィルタ式電気集塵装置を使用することができ、図2に示すように、その内部61に、コロナ放電を発生させる放電電極63、64と、集塵機能とフィルタ機能を併せ持った箱型の集塵電極65、66等を備え、含塵ガスGd中のダストDは、放電電極63、64で発生したコロナ放電にて電荷を与えられ、集塵電極65、66で捕集された後、これらの集塵電極(フィルタ)を通過するときにろ過される。ダストDが除去された清浄ガスGcは、集塵機出口62からセメントキルン2の排ガス系に排出される。 As the filtration type electrostatic precipitator 6, for example, a filter type electrostatic precipitator manufactured by Furukawa Industrial Systems Co., Ltd. as described in JP 2010-115618 A can be used, as shown in FIG. In the interior 61, there are provided discharge electrodes 63 and 64 for generating corona discharge, and box-shaped dust collection electrodes 65 and 66 having both a dust collection function and a filter function, and the dust D in the dust-containing gas Gd is discharged. After being charged by corona discharge generated at the electrodes 63 and 64 and collected by the dust collecting electrodes 65 and 66, it is filtered when passing through these dust collecting electrodes (filters). The clean gas Gc from which the dust D has been removed is discharged from the dust collector outlet 62 to the exhaust gas system of the cement kiln 2.
 このろ過式電気集塵装置6は、静電気による集塵機能とフィルタによるろ過集塵機能の相乗効果に加え、フィルタに対してガスが直角に通過するため、集塵効率が高く、高温バグフィルタと同等の集塵効率を有する。 In addition to the synergistic effect of the electrostatic dust collection function and the filter filtration dust collection function, this filtration type electrostatic precipitator 6 has a high dust collection efficiency because the gas passes perpendicular to the filter, and is equivalent to a high-temperature bag filter. Has dust collection efficiency.
 また、従来の電気集塵機は、槌打により捕集ダストが再飛散する問題があったが、フィルタ式電気集塵機6は、ダストが再飛散しても、その後集塵電極65、66でろ過されるので、出口含塵濃度が著しく増加することはない。 Further, the conventional electrostatic precipitator has a problem that the collected dust is re-scattered by striking, but the filter-type electrostatic precipitator 6 is filtered by the dust collecting electrodes 65 and 66 after the dust is re-scattered. Therefore, the dust concentration at the outlet does not increase significantly.
 さらに、集塵電極65、66にはステンレス鋼を使用し、耐熱性に優れ安定した性能を維持することができるため、長寿命を期待でき、また、バグフィルタと比較して圧力損失が少ないため運転コストの低減に繋がる。さらに、従来の電気集塵機よりも高集塵効率であるため、同一風量では本体の大きさが小さく、省スペースを図ることもできる。尚、フィルタ式電気集塵機6の設計温度は320℃で、本体の圧力損失は50mmAq程度であり、従来のバグフィルタの設計温度は150℃で、本体の圧力損失は150mmAq程度である。 In addition, stainless steel is used for the dust collection electrodes 65 and 66, and it can maintain a stable performance with excellent heat resistance, so it can be expected to have a long life and has less pressure loss than a bag filter. This leads to a reduction in operating costs. Furthermore, since the dust collection efficiency is higher than that of a conventional electric dust collector, the size of the main body is small with the same air volume, and space can be saved. The design temperature of the filter type electrostatic precipitator 6 is 320 ° C., the pressure loss of the main body is about 50 mmAq, the design temperature of the conventional bag filter is 150 ° C., and the pressure loss of the main body is about 150 mmAq.
 次に、上記構成を有する塩素バイパス設備1についても、セメントキルン2の窯尻から最下段サイクロンに至るまでのキルン排ガス流路からの燃焼ガスの一部Gをプローブ3によって抽気しながら、冷却ファン4からの冷風によって冷却する。これによって、抽気ガスが550℃程度以下に急冷され、塩素化合物の微結晶が生成される。この塩素化合物の微結晶は、抽気ガスG1に含まれるダストの微粉側に偏在しているため、サイクロン5で分級した粗粉D1をセメントキルン2に付設されたプレヒータ等にセメント原料として戻す。 Next, for the chlorine bypass facility 1 having the above-described configuration, a cooling fan is used to extract a part G of the combustion gas from the kiln exhaust gas flow path from the kiln bottom of the cement kiln 2 to the lowermost cyclone with the probe 3. Cool with cold air from 4. As a result, the extraction gas is rapidly cooled to about 550 ° C. or less, and a chlorine compound microcrystal is generated. Since the fine crystals of the chlorine compound are unevenly distributed on the fine powder side of the dust contained in the extraction gas G1, the coarse powder D1 classified by the cyclone 5 is returned to the preheater attached to the cement kiln 2 as a cement raw material.
 サイクロン5によって分離された微粉D2を含み、400℃程度の抽気ガスG2をろ過式電気集塵装置6に導入し、微粉D2を回収する。ろ過式電気集塵装置6で回収したダストD2は、セメント焼成工程の系外に排出し、処理する。 The extraction gas G2, which contains the fine powder D2 separated by the cyclone 5 and is about 400 ° C., is introduced into the filtration type electrostatic precipitator 6 to collect the fine powder D2. The dust D2 collected by the filtration type electrostatic precipitator 6 is discharged out of the cement firing process and processed.
 一方、ろ過式電気集塵装置6から排出されファン7で下流側に供給された排ガスG3は、セメントキルン2の排ガス系、すなわちセメントキルン2の排ガスを誘引するファン(IDF)の出口側や、セメントキルン2に付設されるプレヒータに戻すことができる。 On the other hand, the exhaust gas G3 discharged from the filtration type electrostatic precipitator 6 and supplied downstream by the fan 7 is an exhaust gas system of the cement kiln 2, that is, an outlet side of a fan (IDF) that induces the exhaust gas of the cement kiln 2, The preheater attached to the cement kiln 2 can be returned.
1 塩素バイパス設備
2 セメントキルン
3 プローブ
4 冷却ファン
5 サイクロン
6  ろ過式電気集塵装置
7 ファン
61 (ろ過式電気集塵装置の)内部
62 (ろ過式電気集塵装置の)ガス出口
63、64 放電電極
65、66  集塵電極
DESCRIPTION OF SYMBOLS 1 Chlorine bypass facility 2 Cement kiln 3 Probe 4 Cooling fan 5 Cyclone 6 Filtration type electric dust collector 7 Fan 61 (of the filtration type electric dust collector) Interior 62 (of the filtration type electric dust collector) Gas outlet 63, 64 Discharge Electrodes 65, 66 Dust collection electrode

Claims (3)

  1.  セメントキルンの窯尻から最下段サイクロンに至るまでのキルン排ガス流路より燃焼ガスの一部を抽気するとともに、抽気した燃焼ガスを低温ガスにより冷却するプローブと、
     該プローブで抽気されたガスに含まれるダストを集塵するろ過式電気集塵装置とを備えることを特徴とする塩素バイパス排ガスの処理装置。
    A probe for extracting a part of the combustion gas from the kiln exhaust gas passage from the bottom of the kiln of the cement kiln to the lowermost cyclone, and cooling the extracted combustion gas with a low temperature gas,
    An apparatus for treating chlorine bypass exhaust gas, comprising: a filtration-type electrostatic precipitator that collects dust contained in gas extracted by the probe.
  2.  前記プローブにより抽気された抽気ガスから粗粉ダストを分離する分級機を備え、
     該分級機から排出される微粉を含む抽気ガスを前記固気分離装置に供給することを特徴とする請求項1又は2に記載の塩素バイパス排ガスの処理装置。
    A classifier for separating coarse dust from the extracted gas extracted by the probe;
    The chlorine bypass exhaust gas treatment apparatus according to claim 1 or 2, wherein a bleed gas containing fine powder discharged from the classifier is supplied to the solid gas separation device.
  3.  請求項1又は2に記載の塩素バイパス排ガスの処理装置を用い、前記ろ過式電気集塵装置の入口ガス温度を150℃以上、500℃以下とすることを特徴とする塩素バイパス排ガスの処理方法。 A chlorine bypass exhaust gas treatment method, wherein the chlorine bypass exhaust gas treatment device according to claim 1 or 2 is used, and an inlet gas temperature of the filtration electrostatic precipitator is set to 150 ° C or higher and 500 ° C or lower.
PCT/JP2012/051520 2011-03-11 2012-01-25 Device and method for processing chlorine bypass exhaust gas WO2012124380A1 (en)

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WO2009154088A1 (en) * 2008-06-17 2009-12-23 太平洋セメント株式会社 Apparatus and method for treating gas discharged from cement kiln
JP2010115618A (en) * 2008-11-14 2010-05-27 Furukawa Industrial Machinery Systems Co Ltd Electrostatic dust-collecting apparatus
JP2010207676A (en) * 2009-03-09 2010-09-24 Furukawa Industrial Machinery Systems Co Ltd Electric dust collector

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2009154088A1 (en) * 2008-06-17 2009-12-23 太平洋セメント株式会社 Apparatus and method for treating gas discharged from cement kiln
JP2010115618A (en) * 2008-11-14 2010-05-27 Furukawa Industrial Machinery Systems Co Ltd Electrostatic dust-collecting apparatus
JP2010207676A (en) * 2009-03-09 2010-09-24 Furukawa Industrial Machinery Systems Co Ltd Electric dust collector

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