JP2008279344A - Exhaust treatment device of sludge disposal facilities and exhaust treatment method - Google Patents

Exhaust treatment device of sludge disposal facilities and exhaust treatment method Download PDF

Info

Publication number
JP2008279344A
JP2008279344A JP2007124802A JP2007124802A JP2008279344A JP 2008279344 A JP2008279344 A JP 2008279344A JP 2007124802 A JP2007124802 A JP 2007124802A JP 2007124802 A JP2007124802 A JP 2007124802A JP 2008279344 A JP2008279344 A JP 2008279344A
Authority
JP
Japan
Prior art keywords
exhaust
sludge
gas
cooling
facility
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
Application number
JP2007124802A
Other languages
Japanese (ja)
Inventor
Yoshihito Izawa
良仁 伊沢
Naoki Ueno
直樹 上野
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Taiheiyo Cement Corp
Original Assignee
Taiheiyo Cement Corp
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Taiheiyo Cement Corp filed Critical Taiheiyo Cement Corp
Priority to JP2007124802A priority Critical patent/JP2008279344A/en
Publication of JP2008279344A publication Critical patent/JP2008279344A/en
Pending legal-status Critical Current

Links

Images

Abstract

<P>PROBLEM TO BE SOLVED: To efficiently treat air containing an odor exhausted from a sludge receiving chamber, a storage chamber for storing the sludge, etc. while avoiding a hike in equipment cost. <P>SOLUTION: This exhaust treatment device 1 is provided with a gas extraction part 3 and a gas treatment part 4 attached to a cement kiln 7, with a probe 8 which extracts a part of the combustion gas from a kiln exhaust gas flow path located at the lower part of a preheater for the cement kiln 7, and a cooling ductwork 9 for feeding cold air into the probe 8, a vacuum fan 6 which exhausts the air containing the odor from sludge disposal facilities 5, and a probe cooling fan 18 which introduces the exhaust A coming from the vacuum fan 6 into the cooling ductwork 9 of the gas extraction part 3. In addition, the device 1 uses the exhaust A originating from the sludge disposal facilities 5 as a cooling agent for an extracted gas G. Thus it is possible to treat a large amount of the exhaust A regardless of the consumption of a main fuel and air for combustion at the preheater. Further, the laying of the ductwork over an extensive distance is not necessary, and the exhaust A can be treated using chlorine bypass facilities. <P>COPYRIGHT: (C)2009,JPO&INPIT

Description

本発明は、汚泥処理設備の排気処理装置及び排気処理方法に関し、特に、汚泥を受け入れる汚泥受入室や、汚泥を貯蔵する貯蔵室等から排出される臭気を含む空気を処理する装置等に関する。   The present invention relates to an exhaust treatment apparatus and an exhaust treatment method for a sludge treatment facility, and more particularly to an apparatus for treating air containing odor discharged from a sludge receiving chamber for receiving sludge, a storage chamber for storing sludge, and the like.

下水道の普及や高度排水処理の実施等に伴い、下水処理施設から発生する汚泥量は、年々増加し、その処理方法が問題となっている。汚泥の大部分は埋め立て処分によって処理されるが、埋立処分場は逼迫しており、新たな処分地の確保も極めて困難な状況にある。   With the spread of sewerage and the implementation of advanced wastewater treatment, the amount of sludge generated from sewage treatment facilities has been increasing year by year, and the treatment method has become a problem. Most of the sludge is disposed of by landfill, but the landfill site is tight and it is extremely difficult to secure a new disposal site.

こうした問題の解決を図るべく、近年、下水汚泥等の含水汚泥をセメント製造工場に持ち込み、セメント原料の一部として用いる方法が採用されている。この方法では、埋め立て場所の確保が不要となるだけでなく、多量の汚泥を処理することもできるため、大いに注目を集めている。   In recent years, in order to solve these problems, a method has been adopted in which hydrous sludge such as sewage sludge is brought into a cement manufacturing factory and used as a part of cement raw material. This method not only makes it unnecessary to secure a landfill site, but also can treat a large amount of sludge, and thus has attracted a great deal of attention.

しかし、含水汚泥をセメント製造工場で処理するにあたっては、持ち込まれた汚泥を受入室等で受け入れたり、貯蔵室等に一時的に貯蔵しなければならず、その際の悪臭が問題となる。かかる問題は、室内空気を排出して受入室等を換気すれば解決することができるが、排出した臭気を含む空気を直接大気中に放出することはできず、その処理が必要となる。このため、排気を脱臭するための専用の脱臭設備が必要となり、処理コストの増大を招いている。   However, when processing hydrous sludge at a cement manufacturing plant, the introduced sludge must be received in a receiving room or temporarily stored in a storage room or the like, and the bad odor at that time becomes a problem. Such a problem can be solved by exhausting the indoor air and ventilating the receiving room or the like, but the air containing the exhausted odor cannot be directly released into the atmosphere, and it is necessary to deal with it. For this reason, a dedicated deodorizing equipment for deodorizing the exhaust is required, which increases the processing cost.

そこで、特許文献1に記載のように、汚泥処理設備からの排気をプレヒータに燃焼用空気として導入したり、クリンカクーラの2次空気回収帯に導入し、プレヒータ又はクリンカクーラの2次空気回収帯で燃焼させる方法が提案されている。この方法によれば、既存の設備を利用して排気を処理できるため、専用の脱臭設備を設けずとも、排気を処理することが可能となる。
特許第3841326号公報
Therefore, as described in Patent Document 1, the exhaust from the sludge treatment facility is introduced into the preheater as combustion air, or introduced into the secondary air recovery zone of the clinker cooler, and the secondary air recovery zone of the preheater or clinker cooler is introduced. A method of burning in is proposed. According to this method, since exhaust gas can be processed using existing equipment, exhaust gas can be processed without providing a dedicated deodorizing equipment.
Japanese Patent No. 3841326

しかし、近年、セメントキルンのプレヒータ下部や、セメントキルンに付設された仮焼炉での含水汚泥及び廃棄物等の使用量が増加する一方、プレヒータでの主燃料及び燃焼用空気の使用量が減少傾向にある。このため、排気をプレヒータに燃焼用空気として導入する方法を採用しても、汚泥処理設備からの排気の全てを使用するのは困難であり、排気を効率良く処理できない虞がある。   However, in recent years, the amount of water-containing sludge and waste in the lower part of the preheater of the cement kiln and in the calciner attached to the cement kiln has increased, while the amount of main fuel and combustion air in the preheater has decreased. There is a tendency. For this reason, even if it employ | adopts the method of introduce | transducing exhaust_gas | exhaustion as combustion air to a preheater, it is difficult to use all the exhaust_gas | exhaustion from sludge treatment equipment, and there exists a possibility that exhaust_gas | exhaustion cannot be processed efficiently.

また、汚泥処理設備からの排気をクリンカクーラの2次空気回収帯に導入する方法を採用するには、排気をクリンカクーラに導入するための管路が必要となるが、汚泥処理に際しては、含水汚泥をセメントキルンのプレヒータ下部に投入するのが一般的であることから、汚泥処理設備は、クリンカクーラから離れたプレヒータの近辺に設置されることが多いため、プレヒータの近辺からクリンカクーラまでの長距離に亘って管路を設置しなければならず、設備コストが高騰するという問題がある。   In order to adopt the method of introducing the exhaust from the sludge treatment facility into the secondary air recovery zone of the clinker cooler, a pipe line for introducing the exhaust into the clinker cooler is required. Since it is common to put sludge into the lower part of the preheater of the cement kiln, sludge treatment equipment is often installed near the preheater away from the clinker cooler, so the length from the vicinity of the preheater to the clinker cooler is long. There is a problem that pipes must be installed over a distance, and the equipment cost increases.

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、設備コストの高騰を回避しつつ、効率良く排気を処理することができる汚泥処理設備の排気処理装置等を提供することを目的とする。   Therefore, the present invention has been made in view of the problems in the above-described conventional technology, and an exhaust treatment apparatus for a sludge treatment facility that can efficiently treat exhaust while avoiding an increase in equipment cost. The purpose is to provide.

上記目的を達成するため、本発明は、汚泥処理設備から排出される臭気を含む空気を処理する汚泥処理設備の排気処理装置であって、セメントキルンのプレヒータ下部のキルン排ガス流路より、燃焼ガスの一部を抽気する抽気手段と、該抽気手段によって抽気された抽気ガスを冷却する冷却手段とを有し、前記セメントキルンに付設された塩素バイパス設備と、前記汚泥処理設備から臭気を含む空気を排出する排気手段と、前記汚泥処理設備からの排気を前記塩素バイパス設備の前記冷却手段に導入する導入手段とを備え、前記汚泥処理設備からの排気を、前記冷却手段において抽気ガスの冷却に用いることを特徴とする。   In order to achieve the above object, the present invention provides an exhaust treatment apparatus for a sludge treatment facility that treats air containing odors discharged from a sludge treatment facility, from a kiln exhaust gas flow path below a preheater of a cement kiln. And a cooling means for cooling the extraction gas extracted by the extraction means, a chlorine bypass facility attached to the cement kiln, and air containing odor from the sludge treatment facility And an introduction means for introducing the exhaust from the sludge treatment facility into the cooling means of the chlorine bypass facility, and the exhaust from the sludge treatment facility is used to cool the extraction gas in the cooling means. It is characterized by using.

そして、本発明によれば、汚泥処理設備からの排気を、塩素バイパス設備において、冷却手段で抽気ガスを冷却するための冷風として用いるため、プレヒータでの主燃料及び燃焼用空気の使用量に関わらず処理することが可能となる。また、本発明によれば、長距離に亘って管路を設置する必要がないのに加え、塩素バイパス設備を利用して排気を処理することができるため、設備コストの高騰を回避することもできる。   According to the present invention, the exhaust gas from the sludge treatment facility is used as cold air for cooling the extracted gas by the cooling means in the chlorine bypass facility, so that the amount of main fuel and combustion air used in the preheater is related. Can be processed. In addition, according to the present invention, it is not necessary to install a pipeline over a long distance, and since exhaust gas can be processed using a chlorine bypass facility, an increase in facility cost can be avoided. it can.

前記排気処理装置は、前記抽気ガスの冷却に用いた排気を、前記セメントキルンを含む焼成設備に環流させる環流手段を備えることができる。環流された排気をセメント焼成設備で処理することにより、排気処理装置に専用の脱臭装置を付設することが不要となるとともに、従来、塩素バイパス設備からの排気をセメント焼成設備に環流させていた場合と比較しても、セメント焼成設備に環流される空気量に変化がないため、環流に伴う熱損失の低下を招くこともない。   The exhaust treatment apparatus may include a circulation means for circulating the exhaust gas used for cooling the extraction gas to a firing facility including the cement kiln. By treating the exhausted exhaust air with a cement firing facility, it is not necessary to attach a dedicated deodorizing device to the exhaust treatment device, and conventionally, exhaust from the chlorine bypass facility has been recirculated to the cement firing facility. In comparison with the above, since there is no change in the amount of air circulated to the cement firing facility, there is no reduction in heat loss associated with the circulatory flow.

また、本発明は、汚泥処理設備から排出される臭気を含む空気を処理する汚泥処理設備の排気処理方法であって、前記汚泥処理設備からの臭気を含む空気を、セメントキルンに付設された塩素バイパス設備において、セメントキルンのプレヒータ下部のキルン排ガス流路より抽気した抽気ガスの冷却に用いることを特徴とする。本発明によれば、前記発明と同様に、設備コストの高騰を回避しつつ、効率良く排気を処理することが可能となる。   The present invention also relates to an exhaust treatment method for a sludge treatment facility that treats air containing odor discharged from the sludge treatment facility, wherein the chlorine containing the odor from the sludge treatment facility is attached to a cement kiln. In the bypass facility, it is used for cooling the extracted gas extracted from the kiln exhaust gas flow path below the preheater of the cement kiln. According to the present invention, similarly to the above-described invention, it is possible to treat exhaust efficiently while avoiding an increase in equipment cost.

前記汚泥処理設備の排気処理方法において、前記抽気ガスの冷却に用いた排気を、前記セメントキルンを含む焼成設備に環流させることができ、排気処理装置に専用の脱臭装置を不要とし、従来、塩素バイパス設備からの排気をセメント焼成設備に環流させていた場合と比較しても、熱損失の低下を招くこととはならない。   In the exhaust treatment method of the sludge treatment facility, the exhaust used for cooling the extraction gas can be recirculated to the firing facility including the cement kiln, and a dedicated deodorizing device is not required for the exhaust treatment device. Even if the exhaust from the bypass facility is recirculated to the cement firing facility, the heat loss will not be reduced.

以上のように、本発明によれば、設備コストの高騰を回避しつつ、効率良く汚泥処理設備からの排気を処理することが可能となる。   As described above, according to the present invention, it is possible to efficiently treat the exhaust gas from the sludge treatment facility while avoiding an increase in facility cost.

次に、本発明の実施の形態について、図面を参照しながら説明する。   Next, embodiments of the present invention will be described with reference to the drawings.

図1は、本発明にかかる汚泥処理設備の排気処理装置(以下「処理装置」という)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7に付設され、大別して、汚泥受入部2と、ガス抽気部3と、ガス処理部4とからなる。汚泥受入部2は、外部の汚泥発生設備からの汚泥を受け入れるための設備であり、ガス抽気部3及びガス処理部4は、ともに燃焼ガス中の塩素を除去する塩素バイパス設備として用いられる。   FIG. 1 shows an embodiment of an exhaust treatment device (hereinafter referred to as “treatment device”) of a sludge treatment facility according to the present invention. This treatment device 1 is attached to a cement kiln 7 and is roughly divided into sludge receiving portions. 2, a gas extraction unit 3, and a gas processing unit 4. The sludge receiving unit 2 is a facility for receiving sludge from an external sludge generation facility, and the gas extraction unit 3 and the gas processing unit 4 are both used as a chlorine bypass facility for removing chlorine in the combustion gas.

汚泥受入部2は、セメント製造工場に持ち込まれた下水汚泥等の含水汚泥Sを受け入れる汚泥受入棟5と、汚泥受入棟5の室内空気を排出して汚泥受入棟5を換気するバキュームファン6とを備える。汚泥受入棟5には、持ち込まれた含水汚泥Sを一時的に貯蔵する汚泥タンク5aと、汚泥タンク5aに貯蔵された含水汚泥Sをセメントキルン7又は乾燥機(不図示)等に搬送する供給コンベア5bとが設けられる。尚、この汚泥受入棟5は、含水汚泥Sの投入場所に近いセメントキルン7のプレヒータ近辺に設置される。   The sludge receiving unit 2 includes a sludge receiving building 5 that accepts a sewage sludge S such as sewage sludge brought into a cement manufacturing factory, and a vacuum fan 6 that vents the sludge receiving building 5 by discharging indoor air from the sludge receiving building 5. Is provided. In the sludge receiving building 5, the sludge tank 5a for temporarily storing the brought-in water-containing sludge S, and the supply for transporting the water-containing sludge S stored in the sludge tank 5a to a cement kiln 7 or a dryer (not shown), etc. A conveyor 5b is provided. The sludge receiving building 5 is installed near the preheater of the cement kiln 7 near the place where the hydrous sludge S is charged.

ガス抽気部3は、セメントキルン7のプレヒータ下部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8と、プローブ8内に冷風を供給するためのプローブ冷却ファン18と、プローブ8内に冷風を供給する冷却管路9と、プローブ8で抽気した抽気ガスGと汚泥受入棟5の排気Aとが混合された混合ガスG’に含まれるダストの粗粉を分離する分級機としてのサイクロン10とを備える。プローブ冷却ファン18の入口ダクト18aには、汚泥受入部2のバキュームファン6の出口ダクト6aから延設された管路11が接続される。   The gas extraction unit 3 includes a probe 8 for extracting a part of combustion gas from a kiln exhaust gas flow path below the preheater of the cement kiln 7, a probe cooling fan 18 for supplying cold air into the probe 8, As a classifier for separating coarse dust particles contained in a mixed gas G ′ in which a cooling pipe 9 for supplying cold air to the gas, and an extraction gas G extracted by the probe 8 and an exhaust A of the sludge receiving building 5 are mixed. The cyclone 10 is provided. A pipe line 11 extending from the outlet duct 6 a of the vacuum fan 6 of the sludge receiving unit 2 is connected to the inlet duct 18 a of the probe cooling fan 18.

ガス処理部4は、サイクロン10から排出された微粉を含む混合ガスG’を冷却する冷却器12と、冷却器12に冷風を供給する冷却ファン13と、冷却器12で冷却された混合ガスG’を集塵するバッグフィルタ14と、冷却器12及びバッグフィルタ14から排出されたダストを貯蔵するダストタンク15と、バッグフィルタ14からの排気をプレヒータのトップサイクロン17に導入する排気ファン16とを備える。   The gas processing unit 4 includes a cooler 12 that cools the mixed gas G ′ containing fine powder discharged from the cyclone 10, a cooling fan 13 that supplies cool air to the cooler 12, and the mixed gas G that is cooled by the cooler 12. A bag filter 14 for collecting the dust, a dust tank 15 for storing the dust discharged from the cooler 12 and the bag filter 14, and an exhaust fan 16 for introducing the exhaust from the bag filter 14 into the top cyclone 17 of the preheater. Prepare.

次に、処理装置1による汚泥受入棟5の排気の処理手順について図1を参照しながら説明する。   Next, the exhaust gas processing procedure of the sludge receiving building 5 by the processing apparatus 1 will be described with reference to FIG.

車両によって含水汚泥Sが汚泥受入棟5に搬入されると、含水汚泥Sを汚泥タンク5aに一時的に貯蔵した後、供給コンベア5bを介して、乾燥機、セメントキルン7のプレヒータ下部等に搬送し、セメント原料の一部として使用する。この際、汚泥受入棟5内を換気するため、バキュームファン6を運転し、臭気を含む空気を汚泥受入棟5から排出する。排気Aは、バキュームファン6の出口ダクト6aから管路11を通り、抽気ガスGを冷却するためのプローブ冷却ファン18の入口ダクト18aに供給される。排気Aは、冷却管路9を通ってプローブ8内に流れ込み、プローブ8内の抽気ガスGと接触し、抽気ガスGを冷却する。   When the water-containing sludge S is carried into the sludge receiving building 5 by the vehicle, the water-containing sludge S is temporarily stored in the sludge tank 5a, and then conveyed to the dryer, the lower part of the preheater of the cement kiln 7, etc. via the supply conveyor 5b. And used as part of the cement raw material. At this time, in order to ventilate the inside of the sludge receiving building 5, the vacuum fan 6 is operated and air containing odor is discharged from the sludge receiving building 5. The exhaust A is supplied from the outlet duct 6a of the vacuum fan 6 through the pipe line 11 to the inlet duct 18a of the probe cooling fan 18 for cooling the extracted gas G. The exhaust A flows into the probe 8 through the cooling pipe 9 and comes into contact with the extracted gas G in the probe 8 to cool the extracted gas G.

プローブ8内の排気Aは、冷却された抽気ガスGとともに、プローブ8から排出され、サイクロン10に導入される。その後、サイクロン10において、排気Aと抽気ガスGとが混合された混合ガスG’から粗粉ダストを分離する。混合ガスG’に含まれる塩素は、ダストの微粉側に偏在しているため、サイクロン10で分離された粗粉をセメントキルン系に戻し、セメント原料の一部として再利用する。   The exhaust A in the probe 8 is discharged from the probe 8 together with the cooled extraction gas G and introduced into the cyclone 10. Thereafter, in the cyclone 10, the coarse dust is separated from the mixed gas G ′ in which the exhaust A and the extracted gas G are mixed. Since chlorine contained in the mixed gas G ′ is unevenly distributed on the fine powder side of the dust, the coarse powder separated by the cyclone 10 is returned to the cement kiln system and reused as part of the cement raw material.

一方、粗粉ダストを分離した後の混合ガスG’を、サイクロン10から後段の冷却器12及びバッグフィルタ14に順次導入し、冷却器12において、混合ガスG’を所定の温度まで冷却し、バッグフィルタ14によって、混合ガスG’中の微粉ダストを回収し、塩素を除去する。微粉ダストを回収した混合ガスG’を、バッグフィルタ14からプレヒータのトップサイクロン17に導入し、後段で脱臭処理する。   On the other hand, the mixed gas G ′ after separating the coarse dust is sequentially introduced from the cyclone 10 into the cooler 12 and the bag filter 14 in the subsequent stage, and the mixed gas G ′ is cooled to a predetermined temperature in the cooler 12. The bag filter 14 collects the fine dust in the mixed gas G ′ and removes chlorine. The mixed gas G ′ obtained by collecting the fine dust is introduced from the bag filter 14 into the top cyclone 17 of the preheater, and deodorized at the subsequent stage.

以上説明したように、本実施の形態においては、セメントキルン7のプレヒータ近辺に設置した汚泥受入棟5からの排気Aを、セメントキルン7のプレヒータ下部に設置されたプローブ8の冷却管路9に導入し、抽気ガスGを冷却するための冷風として用いるため、長距離に亘って管路を設置する必要がないのに加え、塩素バイパス設備を利用して排気Aを処理することができ、設備コストの高騰を回避することが可能となる。また、本実施の形態においては、プレヒータでの主燃料及び燃焼用空気の使用量に関わらず、排気Aを多量に使用することができるため、排気Aを効率良く処理することが可能となる。   As described above, in the present embodiment, the exhaust A from the sludge receiving building 5 installed in the vicinity of the preheater of the cement kiln 7 is supplied to the cooling pipe 9 of the probe 8 installed in the lower part of the preheater of the cement kiln 7. Introduced and used as cold air for cooling the extracted gas G, it is not necessary to install a pipeline over a long distance, and exhaust A can be treated using chlorine bypass equipment, It becomes possible to avoid the cost increase. In the present embodiment, since the exhaust A can be used in a large amount regardless of the amount of main fuel and combustion air used in the preheater, the exhaust A can be processed efficiently.

また、本実施の形態においては、排気Aを含む混合ガスG’をプレヒータのトップサイクロン17に環流し、セメント焼成装置側で脱臭処理するため、処理装置1に専用の脱臭装置を付設することが不要となる。これに加え、従来、塩素バイパス設備からの排気をセメント焼成設備に環流させていた場合と比較しても、セメント焼成設備に環流される空気量に変化がなく、環流に伴う熱損失の低下を招来することもない。   In the present embodiment, the mixed gas G ′ containing the exhaust A is circulated to the top cyclone 17 of the preheater and deodorized on the cement baking apparatus side. Therefore, a dedicated deodorizing apparatus can be attached to the processing apparatus 1. It becomes unnecessary. In addition to this, the amount of air recirculated to the cement firing equipment has not changed compared to the case where the exhaust from the chlorine bypass equipment has been recirculated to the cement firing equipment. There is no invitation.

尚、上記実施の形態においては、バッグフィルタ14からの排気をプレヒータのトップサイクロンに導入するが、プレヒータ下部、仮焼炉、又はトップサイクロン後段にあるキルン排ガスを排気するためのファン出口に導入してもよい。   In the above embodiment, the exhaust from the bag filter 14 is introduced into the top cyclone of the preheater, but is introduced into the fan outlet for exhausting the kiln exhaust gas at the lower part of the preheater, the calcining furnace, or after the top cyclone. May be.

また、上記実施の形態においては、サイクロン10とバッグフィルタ14との間に冷却器12を設けるが、冷却器12を省略し、混合ガスG’を冷却することなく、プレヒータのトップサイクロン17に戻すようにしてもよい。この場合、バッグフィルタ14には、高温でも処理可能な集塵機(例えば、移動層式集塵装置)を用いる必要がある。   Moreover, in the said embodiment, although the cooler 12 is provided between the cyclone 10 and the bag filter 14, the cooler 12 is abbreviate | omitted and it returns to the top cyclone 17 of a preheater, without cooling mixed gas G '. You may do it. In this case, the bag filter 14 needs to use a dust collector (for example, a moving bed type dust collector) that can be processed even at a high temperature.

上記実施の形態においては、抽気手段と冷却手段が一体的に掲載されているプローブ8を使用している場合を例示したが、抽気手段と冷却手段が別々に設置されているセメント焼成設備も存在する。その場合でも、排気Aをプローブ8と別に設置された冷却手段に供給することで、上記実施の形態と同様の効果を得ることができる。   In the above embodiment, the case where the probe 8 in which the extraction means and the cooling means are listed is used is illustrated, but there is also a cement firing facility in which the extraction means and the cooling means are separately installed. To do. Even in such a case, the same effect as that of the above embodiment can be obtained by supplying the exhaust A to the cooling means installed separately from the probe 8.

本発明にかかる汚泥処理設備の排気処理装置の一実施の形態を示す全体構成図である。1 is an overall configuration diagram showing an embodiment of an exhaust treatment apparatus for a sludge treatment facility according to the present invention.

符号の説明Explanation of symbols

1 汚泥処理設備の排気処理装置
2 汚泥受入部
3 ガス抽気部
4 ガス処理部
5 汚泥受入棟
5a 汚泥タンク
5b 供給コンベア
6 バキュームファン
6a 出口ダクト
7 セメントキルン
8 プローブ
9 冷却管路
9a 入口ダクト
10 サイクロン
11 管路
12 冷却器
13 冷却ファン
14 バッグフィルタ
15 ダストタンク
16 排出ファン
17 トップサイクロン
18 プローブ冷却ファン
18a 入口ダクト
A (汚泥処理設備の)排気
S 含水汚泥
G 抽気ガス
G’混合ガス
DESCRIPTION OF SYMBOLS 1 Exhaust treatment apparatus of sludge treatment equipment 2 Sludge receiving part 3 Gas extraction part 4 Gas processing part 5 Sludge receiving building 5a Sludge tank 5b Supply conveyor 6 Vacuum fan 6a Outlet duct 7 Cement kiln 8 Probe 9 Cooling line 9a Inlet duct 10 Cyclone 11 pipeline 12 cooler 13 cooling fan 14 bag filter 15 dust tank 16 discharge fan 17 top cyclone 18 probe cooling fan 18a inlet duct A (sludge treatment facility) exhaust S hydrous sludge G extraction gas G 'mixed gas

Claims (4)

汚泥処理設備から排出される臭気を含む空気を処理する汚泥処理設備の排気処理装置であって、
セメントキルンのプレヒータ下部のキルン排ガス流路より、燃焼ガスの一部を抽気する抽気手段と、該抽気手段によって抽気された抽気ガスを冷却する冷却手段とを有し、前記セメントキルンに付設された塩素バイパス設備と、
前記汚泥処理設備から臭気を含む空気を排出する排気手段と、
前記汚泥処理設備からの排気を前記塩素バイパス設備の前記冷却手段に導入する導入手段とを備え、
前記汚泥処理設備からの排気を、前記冷却手段において抽気ガスの冷却に用いることを特徴とする汚泥処理設備の排気処理装置。
An exhaust treatment device for a sludge treatment facility for treating air containing odor discharged from the sludge treatment facility,
From the kiln exhaust gas flow path below the preheater of the cement kiln, it has an extraction means for extracting a part of the combustion gas, and a cooling means for cooling the extraction gas extracted by the extraction means, and is attached to the cement kiln. Chlorine bypass equipment,
Exhaust means for discharging air containing odor from the sludge treatment facility;
Introducing means for introducing exhaust from the sludge treatment facility into the cooling means of the chlorine bypass facility,
An exhaust treatment apparatus for a sludge treatment facility, wherein the exhaust from the sludge treatment facility is used for cooling the extracted gas in the cooling means.
前記抽気ガスの冷却に用いた排気を、前記セメントキルンを含む焼成設備に環流させる環流手段を備えることを特徴とする請求項1に記載の汚泥処理設備の排気処理装置。   The exhaust treatment apparatus for a sludge treatment facility according to claim 1, further comprising a circulation means for circulating the exhaust used for cooling the extraction gas to a firing facility including the cement kiln. 汚泥処理設備から排出される臭気を含む空気を処理する汚泥処理設備の排気処理方法であって、
前記汚泥処理設備からの臭気を含む空気を、セメントキルンに付設された塩素バイパス設備において、セメントキルンのプレヒータ下部のキルン排ガス流路より抽気した抽気ガスの冷却に用いることを特徴とする汚泥処理設備の排気処理方法。
An exhaust treatment method for a sludge treatment facility for treating air containing odor discharged from a sludge treatment facility,
The sludge treatment facility characterized in that air containing odor from the sludge treatment facility is used for cooling the extracted gas extracted from the kiln exhaust gas flow path below the preheater of the cement kiln in the chlorine bypass facility attached to the cement kiln. Exhaust treatment method.
前記抽気ガスの冷却に用いた排気を、前記セメントキルンを含む焼成設備に環流させることを特徴とする請求項3に記載の汚泥処理設備の排気処理方法。   The exhaust treatment method for a sludge treatment facility according to claim 3, wherein the exhaust gas used for cooling the extraction gas is recirculated to a firing facility including the cement kiln.
JP2007124802A 2007-05-09 2007-05-09 Exhaust treatment device of sludge disposal facilities and exhaust treatment method Pending JP2008279344A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2007124802A JP2008279344A (en) 2007-05-09 2007-05-09 Exhaust treatment device of sludge disposal facilities and exhaust treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2007124802A JP2008279344A (en) 2007-05-09 2007-05-09 Exhaust treatment device of sludge disposal facilities and exhaust treatment method

Publications (1)

Publication Number Publication Date
JP2008279344A true JP2008279344A (en) 2008-11-20

Family

ID=40140627

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2007124802A Pending JP2008279344A (en) 2007-05-09 2007-05-09 Exhaust treatment device of sludge disposal facilities and exhaust treatment method

Country Status (1)

Country Link
JP (1) JP2008279344A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102829641A (en) * 2012-09-19 2012-12-19 河南易能达能源科技有限公司 System for firing cement kiln head exhaust gas into primary air
US20210009455A1 (en) * 2018-04-04 2021-01-14 Taiheiyo Engineering Corporation Organic sludge treatment device and treatment method

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000226241A (en) * 1999-02-09 2000-08-15 Taiheiyo Cement Corp Reduction of sulfur oxides in chlorine bypass exhaust gas
WO2005050114A1 (en) * 2003-11-18 2005-06-02 Taiheiyo Cement Corporation Combustion gas extraction probe and combustion gas treatment method

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000226241A (en) * 1999-02-09 2000-08-15 Taiheiyo Cement Corp Reduction of sulfur oxides in chlorine bypass exhaust gas
WO2005050114A1 (en) * 2003-11-18 2005-06-02 Taiheiyo Cement Corporation Combustion gas extraction probe and combustion gas treatment method

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102829641A (en) * 2012-09-19 2012-12-19 河南易能达能源科技有限公司 System for firing cement kiln head exhaust gas into primary air
US20210009455A1 (en) * 2018-04-04 2021-01-14 Taiheiyo Engineering Corporation Organic sludge treatment device and treatment method
US11591246B2 (en) * 2018-04-04 2023-02-28 Taiheiyo Engineering Corporation Organic sludge treatment device and treatment method

Similar Documents

Publication Publication Date Title
TWI419847B (en) Treatment method for high-water content organic waste and treatment apparatus thereof
JP5088919B2 (en) Cement baking apparatus and waste treatment method
KR101823961B1 (en) Drying system of sludge by reheating method using steam circulation
JP4823596B2 (en) Method and apparatus for treating exhaust gas in cement firing facility
US8069581B2 (en) System for purifying contaminated soil
WO2008001747A1 (en) Cement burning apparatus and method of drying highly hydrous organic waste
JP4445147B2 (en) Sludge treatment method and apparatus
JP6018458B2 (en) Sludge treatment equipment and treatment method
US7972419B2 (en) Apparatus and method for reducing emissions resulting from raw meal grinding
JP4445148B2 (en) Sludge treatment method and apparatus
EP2039660B1 (en) Cement calcination apparatus and method of drying highly hydrous organic waste
JP2008279344A (en) Exhaust treatment device of sludge disposal facilities and exhaust treatment method
JP6678263B2 (en) Organic waste treatment apparatus and treatment method
JP2012140313A (en) Chlorine bypass system, and method for treatment of chlorine bypass extracted gas
JP5582554B2 (en) Cement baking equipment
JP5412711B2 (en) Method and apparatus for treating high water content inorganic waste
AU2011236010B2 (en) Direct High Temperature Sewage Energy Recuperator Transformer Module
JP2007098343A (en) Exhaust gas treatment method and treating system of cement manufacturing apparatus
JP6249703B2 (en) Cement baking apparatus and water-containing organic waste treatment method
CN110557945A (en) Organic sludge treatment device and treatment method
JP2003340496A (en) Drying and carbonization furnace and multi-kind recycled product manufacturing system provided with drying and carbonation furnace
JP2009023852A (en) Waste gas treatment system and treating method in cement production apparatus
AU2013200262A1 (en) Direct high temperature sewage energy recuperator transformer module
JP2015181988A (en) Hydrous sludge treatment apparatus
JP2005230789A (en) Carbonization method of organic matter-containing sludge

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20100126

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20110225

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20121203

A02 Decision of refusal

Free format text: JAPANESE INTERMEDIATE CODE: A02

Effective date: 20130401