JP2004148317A - Method for treating waste gas from melting furnace - Google Patents

Method for treating waste gas from melting furnace Download PDF

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JP2004148317A
JP2004148317A JP2003409049A JP2003409049A JP2004148317A JP 2004148317 A JP2004148317 A JP 2004148317A JP 2003409049 A JP2003409049 A JP 2003409049A JP 2003409049 A JP2003409049 A JP 2003409049A JP 2004148317 A JP2004148317 A JP 2004148317A
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temperature
exhaust gas
water
melting furnace
bag filter
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JP3765542B2 (en
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Toshimasa Shirai
利昌 白井
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Mitsubishi Heavy Industries Ltd
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
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  • Waste-Gas Treatment And Other Accessory Devices For Furnaces (AREA)
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Abstract

<P>PROBLEM TO BE SOLVED: To reduce the equipment cost by simplifying the structure of a wastewater treatment equipment for treating wastewater withdrawn from the wet smoke washing equipment and to prevent the bag filter from generating a low-temperature corrosion in a system for treating a waste gas from an ash melting furnace. <P>SOLUTION: The cleaning of the waste gas from the melting furnace by successively passing it through a temperature-lowering apparatus that lowers the temperature of the waste gas with a temperature-lowering water fed from a water supply tank, a bag filter, and a wet smoke washing equipment, is characterized in that water withdrawn from the wet smoke-washing equipment is introduced into the water supply tank, fed therefrom into the temperature-lowering equipment, and sprayed as the temperature-lowering water. <P>COPYRIGHT: (C)2004,JPO

Description

本発明は、プラズマ溶融炉等の灰溶融炉からの排ガスを減温装置、バグフィルタ、及び湿式洗煙設備とに順に通過させながら浄化処理するようにした溶融排ガス処理方法に関する。   The present invention relates to a method for treating a molten exhaust gas in which exhaust gas from an ash melting furnace such as a plasma melting furnace is subjected to a purification treatment while sequentially passing the exhaust gas through a temperature reducing device, a bag filter, and a wet smoke washing facility.

図3は廃棄物焼却炉に併設されたプラズマ溶融炉の排ガス処理システムの検討技術の1例を示す系統図である。
図3において1はプラズマ溶融炉、8は該溶融炉1に産業廃棄物等の燃焼処理物を投入するためのホッパ、10は該プラズマ溶融炉1からの排ガス管、17は残渣排出管である。
2は排ガス温度を低下させるための減温装置で、上記プラズマ溶融炉1に上記排ガス管10を介して接続されている。3は該ガス中の溶融炉飛灰等の除去を行なうバグフィルタで、ヒータ31及び飛灰搬送コンベア32が付設され、除去後の飛灰を不図示の飛灰処理設備へ搬送する。19は前記減温装置2とバグフィルタ3とを接続する排ガス管である。
FIG. 3 is a system diagram showing an example of a technique for studying an exhaust gas treatment system of a plasma melting furnace attached to a waste incinerator.
In FIG. 3, reference numeral 1 denotes a plasma melting furnace, 8 denotes a hopper for charging combustion products such as industrial wastes into the melting furnace 1, 10 denotes an exhaust gas pipe from the plasma melting furnace 1, and 17 denotes a residue discharge pipe. .
Reference numeral 2 denotes a temperature reducing device for lowering the exhaust gas temperature, which is connected to the plasma melting furnace 1 via the exhaust gas pipe 10. Reference numeral 3 denotes a bag filter for removing fly ash and the like from the melting furnace in the gas, which is provided with a heater 31 and a fly ash transport conveyor 32, and transports the removed fly ash to a fly ash processing facility (not shown). Reference numeral 19 denotes an exhaust gas pipe connecting the temperature reducing device 2 and the bag filter 3.

4は排ガス中の高濃度酸性ガス成分を除去する湿式洗煙塔でNaOHタンク41より添加されたアルカリ性水により高濃度酸性ガス成分と湿式接触させて塩類を析出させる。11は前記バグフィルタ3と該湿式洗煙塔4とを接続する排ガス管で、該排ガス管11には排ガス圧送用の排ガスファン7が設けられている。
18は前記湿式洗煙塔4出口に接続される排ガス管である。
また、6は排水処理装置で、前記湿式洗煙塔4からの引き抜き排水中の重金属類等の除去を行なうものである。
5は前記減温装置2へ供給する減温水が収容される給水槽、9は該給水槽5と前記減温装置2とを接続する減温水管である。
Reference numeral 4 denotes a wet smoke washing tower for removing high-concentration acidic gas components in the exhaust gas, which is brought into wet contact with the high-concentration acidic gas components by alkaline water added from the NaOH tank 41 to precipitate salts. Reference numeral 11 denotes an exhaust gas pipe for connecting the bag filter 3 and the wet-type smoke washing tower 4, and the exhaust gas pipe 11 is provided with an exhaust gas fan 7 for feeding exhaust gas under pressure.
Reference numeral 18 denotes an exhaust gas pipe connected to the outlet of the wet smoke washing tower 4.
Reference numeral 6 denotes a wastewater treatment device for removing heavy metals and the like in the wastewater drawn out from the wet-type smoke washing tower 4.
Reference numeral 5 denotes a water supply tank in which the temperature-reducing water to be supplied to the temperature-reducing device 2 is stored.

かかる溶融炉の排ガス処理システムの稼動時において、プラズマ溶融炉1から排出された排ガスは排ガス管10を通って減温装置2に導入される。
減温装置2においては、給水槽5から減温水管9を介して導入される減温水を排ガス中に噴霧して排ガス温度をバグフィルタ3の所要入口温度(150℃〜160℃程度が好適)まで降温させる。
該減温装置2を経た排ガスは排ガス管19を介してバグフィルタ3に導入され、溶融炉飛灰等が除去され、該飛灰は飛灰搬送コンベア32を介して不図示の飛灰処理設備へ搬送する。
During the operation of the exhaust gas treatment system of the melting furnace, the exhaust gas discharged from the plasma melting furnace 1 is introduced into the temperature reducing device 2 through the exhaust gas pipe 10.
In the temperature reducing device 2, the temperature-reduced water introduced from the water supply tank 5 via the temperature-reducing water pipe 9 is sprayed into the exhaust gas to adjust the exhaust gas temperature to the required inlet temperature of the bag filter 3 (preferably about 150 ° C. to 160 ° C.). Cool down to
Exhaust gas that has passed through the temperature reducing device 2 is introduced into the bag filter 3 through an exhaust gas pipe 19 to remove fly ash and the like in the melting furnace, and the fly ash is supplied to a fly ash treatment facility (not shown) via a fly ash conveyor 32. Transport to

該バグフィルタ3を経た排ガスは排ガスファン7によって排ガス管11内を通して湿式洗煙塔4に送られ、ここで高濃度の酸性ガス分が除去された後、排ガス管18を経て、焼却炉(不図示)側の排ガスと合流されるかあるいは外部に排出される。
前記湿式洗煙塔4からの引き抜き排水は排水処理装置6において重金属類が除去された後、放流、あるいは焼却炉側排水処理装置(不図示)に送られる。
The exhaust gas that has passed through the bag filter 3 is sent by an exhaust gas fan 7 through an exhaust gas pipe 11 to a wet-type smoke washing tower 4, where high-concentration acidic gas is removed. (Shown) or is discharged to the outside.
After the heavy metals are removed in the wastewater treatment device 6, the wastewater drawn out from the wet smoke washing tower 4 is discharged or sent to an incinerator-side wastewater treatment device (not shown).

尚、ゴミ焼却炉の飛灰を溶融固化する溶融固化装置にバグフィルタ及び洗滌塔を付設する技術が特許文献1に存在する。
特開平9−276651号公報
Patent Document 1 discloses a technique in which a bag filter and a washing tower are attached to a melting and solidifying apparatus for melting and solidifying fly ash of a garbage incinerator.
JP-A-9-276651

図3に示すプラズマ溶融炉の排ガス処理システムにおいて、該プラズマ溶融炉と併設されている廃棄物焼却炉(不図示)側に大型の湿式洗煙塔が設置されている場合には、バグフィルタ3にての徐塵後の溶融炉排ガスを前記焼却炉側の排ガスと混合した後、前記湿式洗煙塔4にて一括処理を行なっている。   In the exhaust gas treatment system for a plasma melting furnace shown in FIG. 3, when a large wet-type smoke washing tower is installed on the side of a waste incinerator (not shown) provided in parallel with the plasma melting furnace, the bag filter 3 is used. After mixing the flue gas of the melting furnace after the dust reduction with the flue gas of the incinerator, batch treatment is performed in the wet-type smoke washing tower 4.

しかしながら、前記焼却炉側において、乾式の排ガス処理設備のみ設置されている場合には、図3に示すようにプラズマ溶融炉1側の排ガス処理システム内に単独で湿式洗煙塔4を設けることを要する。   However, when only a dry-type exhaust gas treatment facility is installed on the incinerator side, it is necessary to provide the wet-type smoke washing tower 4 alone in the exhaust gas treatment system on the plasma melting furnace 1 side as shown in FIG. It costs.

このため、前記のようなプラズマ溶融炉1側の排ガス処理システムに湿式洗煙塔4を設けるシステムにおいては、該洗煙塔4から引き抜かれ、排水をそのまま下水道に放流可能な場合には、簡易な排水処理装置によって排水中の重金属の除去のみを行えばよいが、前記放流が不可能な場合には、湿式洗煙塔4の引き抜き排水路に複雑な保守整備を要し、広範囲の物質の除去機能を有する排水処理装置6を設けることを要し、該排水処理装置6の構造が複雑かつ大型化し、高コストとなる。   For this reason, in the system in which the wet smoke washing tower 4 is provided in the exhaust gas treatment system on the side of the plasma melting furnace 1 as described above, when the smoke washing tower 4 is withdrawn and the wastewater can be discharged to the sewer as it is, It is only necessary to remove heavy metals in the wastewater by a simple wastewater treatment device. However, when the discharge is not possible, complicated maintenance is required for the drainage drainage channel of the wet-type smoke cleaning tower 4, and a wide range of substances must be removed. It is necessary to provide the wastewater treatment device 6 having a removing function, and the structure of the wastewater treatment device 6 is complicated and large, and the cost is high.

また、かかる溶融炉の排ガス処理システムにおいては、減温装置2において、バグフィルタ3入口の所要排ガス温度まで降温(減温)するため、水が噴霧されており、これによってバグフィルタ3等の機器に酸性ガス成分による低温腐食が発生するという問題点があった。   In such an exhaust gas treatment system for a melting furnace, water is sprayed in the temperature reducing device 2 to lower (reduce) the temperature of the exhaust gas to the required exhaust gas temperature at the inlet of the bag filter 3. There is a problem that low-temperature corrosion occurs due to the acid gas component.

本発明はかかる課題に鑑み、灰溶融炉からの排ガスを、減温装置、バグフィルタ及び湿式洗煙設備を介して処理する排ガス処理システムにおいて、前記湿式洗煙設備からの引き抜き排水処理用の排水処理装置の構造を簡単化して装置コストを低減するとともに、前記バグフィルタにおける低温腐食の発生を防止することを目的とする。   In view of the foregoing, the present invention provides an exhaust gas treatment system for treating exhaust gas from an ash melting furnace through a temperature reducing device, a bag filter, and a wet smoke cleaning facility. It is an object of the present invention to simplify the structure of a processing device, reduce the cost of the device, and prevent low-temperature corrosion in the bag filter.

そこで、本発明はかかる課題を解決するため、その第1発明として、 灰溶融炉からの排ガスを、給水槽から供給される減温水により降温させる減温装置と、バグフィルタと、湿式洗煙設備とに順に通過させながら浄化処理するに際し、前記湿式洗煙設備の引き抜き排水を前記給水槽に導入し、該給水槽から前記減温装置に供給して減温水として噴霧することを特徴とする溶融排ガス処理方法を提案する。   In order to solve such problems, the present invention provides, as a first invention, a temperature-reducing device for lowering the temperature of exhaust gas from an ash melting furnace by using temperature-reducing water supplied from a water supply tank, a bag filter, and a wet-type smoke cleaning facility. When purifying while sequentially passing through, the drawn wastewater of the wet-type smoke washing facility is introduced into the water supply tank, and supplied to the temperature reducing device from the water supply tank and sprayed as temperature-reduced water. An exhaust gas treatment method is proposed.

尚、前記湿式洗煙設備は前記灰溶融炉側の排ガス管路に設置してなるのがよいが、燃焼炉側の湿式洗煙設備を兼用して用いてもよい。そこで本第2発明は、前記灰溶融炉からの排ガスを燃焼炉側の排ガスと混合して湿式洗煙塔に導入することを特徴とする。   The wet smoke cleaning equipment is preferably installed in the exhaust gas pipe on the ash melting furnace side, but may be used also as the wet smoke cleaning equipment on the combustion furnace side. Therefore, the second invention is characterized in that the exhaust gas from the ash melting furnace is mixed with the exhaust gas on the combustion furnace side and introduced into the wet smoke washing tower.

また、第3発明は、前記第1発明に係る排ガス処理装置を使用した排ガス処理方法に係り、前記減温水、具体的には給水槽にNaOH若しくはNaHCO等の塩基成分を添加してアルカリ性減温水となして前記減温装置に供給することを特徴とする。 Further, a third invention relates to an exhaust gas treatment method using the exhaust gas treatment apparatus according to the first invention, wherein alkali water is reduced by adding a base component such as NaOH or NaHCO 3 to the temperature-reduced water, specifically, a water supply tank. It is characterized in that it is supplied as hot water to the temperature reducing device.

かかる第1及び第2発明によれば、湿式洗煙設備からの引き抜き排水は、排水処理装置で重金属の除去処理が施こされた後若しくはそのまま、給水槽に導入され、該給水槽にて減温水と混合される。(閉回路を構成すれば重金属の除去処理を行なわなくてもよい。)
そして、この混合減温水は減温装置に送られて排ガス中に噴霧され、排ガス温度をバグフィルタの所要入口温度まで降温させる。
According to the first and second aspects of the present invention, the drainage drained from the wet-type smoke washing facility is introduced into the water tank after the heavy metal removal treatment is performed by the wastewater treatment apparatus or as it is, and reduced in the water tank. Mix with hot water. (If a closed circuit is configured, the heavy metal removal processing need not be performed.)
Then, the mixed desuperheated water is sent to the desuperheater and sprayed into the exhaust gas to lower the temperature of the exhaust gas to a required inlet temperature of the bag filter.

前記減温装置で噴霧された前記混合減温水には前記湿式洗煙設備でアルカリ処理されているために、引き抜き排水中の塩類が混入されているが、この塩類(析出塩類)は前記混合減温水の噴霧が混ざった排ガスとともにバグフィルタに送られ、該バグフィルタにて溶融炉飛灰とともに除去される。これにより、前記排水処理装置においては重金属の除去のみを行なえばよい。   The mixed temperature-reduced water sprayed by the temperature-reducing device has been subjected to alkali treatment in the wet-type smoke-cleaning facility, so that salts in the drawn wastewater are mixed therein. The spray of hot water is sent to the bag filter together with the mixed exhaust gas, and is removed together with the fly ash by the bag filter. Thus, the wastewater treatment device only needs to remove heavy metals.

従ってかかる発明によれば、湿式洗煙設備の引き抜き排水を減温水に混入させて減温装置に送り、この混合減温水を排ガス中に噴霧することにより、引き抜き排水中の(析出)塩類は減温装置での前記混合減温水の噴霧により排ガス中に混入されてバグフィルタに送られて該バグフィルタにて溶融炉飛灰と共に確実に除去される。   Therefore, according to this invention, the (precipitated) salts in the extracted wastewater are reduced by mixing the extracted wastewater of the wet-type smoke cleaning equipment into the deheated water and sending it to the temperature reducing device, and spraying the mixed deheated water into the exhaust gas. The mixed desuperheated water is sprayed by the warming device, mixed into the exhaust gas, sent to the bag filter, and reliably removed together with the melting furnace fly ash by the bag filter.

これにより、前記湿式洗煙設備からの引き抜き排水を処理する排水処理装置では簡易な重金属の除去のみをなせばよく、該排水処理装置は、構造が簡単、かつ小型のもので足りる。また前記引き抜き排水を循環して使用する場合は、外部に排出するときに重金属処理を行なえばよい。
また、本発明によれば、洗煙塔からの引き抜き排水中に含まれる(析出)塩類を前記処理により連続的に系外に排出させることが可能となり、排ガス処理系における塩類の濃縮を防止することができる。
As a result, the wastewater treatment device for treating the drainage water drawn from the wet-type smoke cleaning facility only needs to remove simple heavy metals. The structure of the wastewater treatment device is simple and small. When the drawn wastewater is circulated and used, a heavy metal treatment may be performed when discharging it to the outside.
Further, according to the present invention, it is possible to continuously discharge (precipitated) salts contained in the drainage drawn out from the smoke washing tower to the outside of the system by the above treatment, and to prevent the concentration of the salts in the exhaust gas treatment system. be able to.

更に第3発明によれば、減温水に適量のNaOHを添加することにより減温水はアルカリ性になって減温装置にて排ガス中に噴霧され、該アルカリ性減温水により高濃度酸性ガス成分と湿式接触させて塩類を析出させるとともに、高濃度酸性ガス成分を弱酸性化させる。
そしてこの弱酸性化された溶融炉排ガスが析出塩類とともにバグフィルタに送られて、該バグフィルタにおいて析出塩類の除去と共に排ガスによる低温腐食を抑制する。
According to the third aspect of the present invention, the temperature-reduced water is made alkaline by adding an appropriate amount of NaOH to the temperature-reduced water, and is sprayed into exhaust gas by the temperature-reducing device. In this way, salts are precipitated, and a high-concentration acidic gas component is weakly acidified.
Then, the weakly acidified melting furnace exhaust gas is sent to the bag filter together with the precipitated salts, and the bag filter removes the precipitated salts and suppresses low-temperature corrosion due to the exhaust gas.

即ち、かかる発明によれば、減温水中に適量のNaOHを添加して該減温水をアルカリ性にし、これを排ガス中に噴霧して高濃度酸性ガス成分を弱酸性化させると共に塩類を析出させてバグフィルタに流すことにより、バグフィルタに前記塩類の除去と共に該バグフィルタの酸性ガスによる低温腐食を防止することができる。   That is, according to this invention, an appropriate amount of NaOH is added to the desuperheated water to make the desuperheated water alkaline, and this is sprayed into the exhaust gas to weakly acidify the high-concentration acidic gas component and precipitate salts. By flowing the solution through the bag filter, it is possible to remove the salts from the bag filter and to prevent low-temperature corrosion of the bag filter due to acidic gas.

さらに前記減温装置にて噴霧される減温水にNaOHの代りにNaHCO(重曹)
を添加し、これをアルカリ性減温水となして前記減温装置に供給してもよい。
Further, instead of NaOH, NaHCO 3 (baking soda) was added to the temperature-reduced water sprayed by the temperature-reducing device.
May be added, and this may be supplied to the temperature reducing device as alkaline temperature-reduced water.

更にかかる発明によれば、湿式洗煙設備を焼却炉側に設置した場合において、減温水にNaHCOを適量添加して減温装置にて排ガス中に噴霧してこれをアルカリ性にし、バグフィルタに送ることにより、前記と同様に塩類の析出と共に、バグフィルタ等の酸性ガス成分による低温腐食を防止できる。
なお、NaOHやNaHCOの代りに他の塩基性成分を添加しても同様な効果を有することは自明である。
Further, according to the invention, when the wet smoke cleaning equipment is installed on the incinerator side, an appropriate amount of NaHCO 3 is added to the deheated water, and the deheated device is sprayed into the exhaust gas to make it alkaline, which is used for the bag filter. By sending, it is possible to prevent salt precipitation and low-temperature corrosion due to an acidic gas component such as a bag filter in the same manner as described above.
It is obvious that the same effect can be obtained by adding another basic component instead of NaOH or NaHCO 3 .

以下、図面を参照して本発明の好適な実施例を例示的に詳しく説明する。但しこの実施例に記載されている構成部品の寸法、材質、形状、その相対的配置等は特に特定的な記載がない限りは、この発明の範囲をそれに限定する趣旨ではなく、単なる説明例に過ぎない。   Hereinafter, preferred embodiments of the present invention will be illustratively described in detail with reference to the drawings. However, the dimensions, materials, shapes, relative arrangements, and the like of the components described in this embodiment are not intended to limit the scope of the present invention unless otherwise specified, and are merely illustrative examples. Not just.

図1は本発明の第1実施例に係るプラズマ溶融炉の溶融排ガス処理装置の系統図である。
図1において1はプラズマ溶融炉、8は該溶融炉1に産業廃棄物等の燃焼処理物を投入するためのホッパ、10は該プラズマ溶融炉1からの排ガス管、17は残渣排出管である。2は排ガス温度を低下させるための減温装置で、上記プラズマ溶融炉1に上記排ガス管10を介して接続されている。
3は排ガス中の飛灰及び析出塩類除去用のバグフィルタで、ヒータ31及び飛灰搬送コンベア32が付設され、除去後の飛灰を不図示の飛灰処理設備へ搬送する。19は前記減温装置2とバグフィルタ3とを接続する排ガス管である。
FIG. 1 is a system diagram of a molten exhaust gas treatment apparatus for a plasma melting furnace according to a first embodiment of the present invention.
In FIG. 1, reference numeral 1 denotes a plasma melting furnace, 8 denotes a hopper for charging combustion products such as industrial wastes into the melting furnace 1, 10 denotes an exhaust gas pipe from the plasma melting furnace 1, and 17 denotes a residue discharge pipe. . Reference numeral 2 denotes a temperature reducing device for lowering the exhaust gas temperature, which is connected to the plasma melting furnace 1 via the exhaust gas pipe 10.
Reference numeral 3 denotes a bag filter for removing fly ash and precipitated salts in the exhaust gas, which is provided with a heater 31 and a fly ash conveyor 32, and transports the fly ash after removal to a fly ash processing facility (not shown). Reference numeral 19 denotes an exhaust gas pipe connecting the temperature reducing device 2 and the bag filter 3.

4は排ガス中の高濃度酸性ガス成分を除去する湿式洗煙塔でNaOHタンク41より添加されたアルカリ性水により高濃度酸性ガス成分と湿式接触させて塩類を析出させる。11は前記バグフィルタ3と該湿式洗煙塔4とを接続する排ガス管で、該排ガス管11には排ガス圧送用の排ガスファン7が設けられている。
18は前記湿式洗煙塔出口に接続される排ガス管である。
5は前記減温装置2へ供給する減温水が収容される給水槽、9は該給水槽5と前記減温装置2とを接続する減温水管である。
以上の構成は図3に示す従来技術と同様である。
Reference numeral 4 denotes a wet smoke washing tower for removing high-concentration acidic gas components in the exhaust gas, which is brought into wet contact with the high-concentration acidic gas components by alkaline water added from the NaOH tank 41 to precipitate salts. Reference numeral 11 denotes an exhaust gas pipe for connecting the bag filter 3 and the wet-type smoke washing tower 4, and the exhaust gas pipe 11 is provided with an exhaust gas fan 7 for feeding exhaust gas under pressure.
Reference numeral 18 denotes an exhaust gas pipe connected to the outlet of the wet-type smoke washing tower.
Reference numeral 5 denotes a water supply tank in which the temperature-reducing water to be supplied to the temperature-reducing device 2 is stored.
The above configuration is the same as that of the prior art shown in FIG.

本発明の第1実施例においては、前記湿式洗煙塔4の引き抜き排水を処理するシステムを改良している。
即ち図1において、6は排水処理装置であり、前記湿式洗煙塔4からの引き抜き排水が導入され、該排水中の重金属を除去するものであることは前記した通りであるが、該排水処理装置6の処理排水の出口は、排水管15を介して前記給水槽5に接続されている。
また前記給水槽5には前記引き抜き排水とともにNaOHを添加して減温水をアルカリ性減温水にするように構成している。
In the first embodiment of the present invention, the system for treating the drainage of the wet smoke washing tower 4 is improved.
That is, in FIG. 1, reference numeral 6 denotes a wastewater treatment device, which draws wastewater from the wet-type smoke washing tower 4 and removes heavy metals in the wastewater as described above. The outlet of the treated wastewater of the device 6 is connected to the water supply tank 5 via a drainpipe 15.
Further, NaOH is added to the water supply tank 5 together with the drawn drainage so that the temperature-reduced water becomes alkaline temperature-reduced water.

係る構成からなるプラズマ溶融炉の排ガス処理システムの稼動時において、
湿式洗煙塔4からの引き抜き排水は排水処理装置6に送られ、ここで該排水中の重金属の除去が行なわれる。
該排水処理装置6で重金属が除去された引き抜き排水は該排水管15を経て前記給水槽5に送られて該給水槽5中の減温水と混合される。
また、前記給水槽5には、後述するように少量のNaOH(水酸化ナトリウム)も混入されて減温水をアルカリ性減温水にする。
During operation of the exhaust gas treatment system of the plasma melting furnace having the above configuration,
The drainage drained from the wet smoke washing tower 4 is sent to a drainage treatment device 6, where heavy metals in the drainage are removed.
The drawn wastewater from which heavy metals have been removed by the wastewater treatment device 6 is sent to the water supply tank 5 through the drainage pipe 15 and mixed with the temperature-reduced water in the water supply tank 5.
Further, a small amount of NaOH (sodium hydroxide) is also mixed into the water supply tank 5 as described later, so that the temperature-reduced water becomes alkaline temperature-reduced water.

そして前記給水槽5内の混合減温水、つまり前記引き抜き排水とNaOHが混入された減温水は減温水管9を通って減温装置2に送られる。
一方、プラズマ溶融炉1から排出された排ガスは排ガス管10を通って減温装置2に導入されている。
Then, the mixed temperature-reduced water in the water supply tank 5, that is, the temperature-reduced water mixed with the drawn drainage and NaOH is sent to the temperature-reducing device 2 through the temperature-reduced water pipe 9.
On the other hand, the exhaust gas discharged from the plasma melting furnace 1 is introduced into the temperature reducing device 2 through the exhaust gas pipe 10.

該減温装置2においては、前記給水槽5から減温水管9を介して導入される前記混合減温水を排ガス中に噴霧して排ガス温度をバグフィルタ3の所要入口温度(150℃〜160℃程度が好適)まで降温させるとともに、減温水はアルカリ性になって減温装置2にて排ガス中に噴霧されるため、該アルカリ性減温水により排ガスと湿式接触させて該排ガス中の高濃度酸性ガス成分を弱酸性化させて塩類を析出させる。
該減温装置2を経た排ガスは析出塩類及び飛灰と共に、排ガス管19を介してバグフィルタ3に導入され、ここで析出塩類及び飛灰が除去される。
In the temperature reducing device 2, the mixed temperature-reduced water introduced from the water supply tank 5 through the temperature-reducing water pipe 9 is sprayed into the exhaust gas, and the temperature of the exhaust gas is adjusted to the required inlet temperature of the bag filter 3 (150 ° C. to 160 ° C.). And the temperature-reduced water becomes alkaline and is sprayed into the exhaust gas by the temperature-reducing device 2. Therefore, the alkaline temperature-reduced water is brought into wet contact with the exhaust gas to form a high-concentration acidic gas component in the exhaust gas. Is slightly acidified to precipitate salts.
The exhaust gas that has passed through the temperature reducing device 2 is introduced into the bag filter 3 via the exhaust gas pipe 19 together with the precipitated salts and fly ash, where the precipitated salts and fly ash are removed.

かかるバグフィルタ3の作動時において、前記減温装置2にて排ガス中に噴霧された混合減温水には前記湿式洗煙塔4からの引き抜き排水中の塩類もアルカリ性減温水によりアルカリ溶解して再度減温装置2にて析出されて前記バグフィルタ3に送られる。
そして、該バグフィルタ3においては、前記塩類及び飛灰等の固体成分が除去され、これらは飛灰搬送コンベア32を介して飛灰処理設備へ搬送する。
During the operation of the bag filter 3, the salts in the waste water extracted from the wet-type smoke-washing tower 4 are dissolved in the mixed de-heated water sprayed into the exhaust gas by the de-heater 2 with the alkali de-heated water and dissolved again. Deposited in the temperature reducing device 2 and sent to the bag filter 3.
Then, in the bag filter 3, solid components such as the salts and fly ash are removed, and these are transported to the fly ash processing equipment via the fly ash transport conveyor 32.

従って、前記湿式洗煙塔4からの引き抜き排水を処理する排水処理装置6では簡易な重金属の除去のみを伴なえばよく、該排水処理装置6は、構造が簡単、かつ小型のもので足りる。
また、前記洗煙塔4からの引き抜き排水中に含まれる塩類及び排ガス中の高濃度酸性ガス成分を中和させて析出させた塩類を前記のような処理により連続的に系外に排出させるので、排ガス処理系における塩類の濃縮を防止することができる。
Therefore, the wastewater treatment device 6 for treating the wastewater extracted from the wet-type smoke washing tower 4 only needs to simply remove heavy metals, and the wastewater treatment device 6 has a simple structure and a small size.
Further, the salts contained in the drainage water drawn out from the smoke washing tower 4 and the salts precipitated by neutralizing the high-concentration acidic gas components in the exhaust gas are continuously discharged outside the system by the treatment as described above. In addition, concentration of salts in the exhaust gas treatment system can be prevented.

前記動作後に、該バグフィルタ3を出た排ガスは排ガスファン7によって排ガス管11内を通して湿式洗煙塔4に送られ、ここで酸性ガス分等が完全に除去された後、排ガス管18を経て、焼却炉(不図示)側の排ガスと合流されるかあるいは外部に排出される。   After the above operation, the exhaust gas exiting the bag filter 3 is sent by the exhaust gas fan 7 through the exhaust gas pipe 11 to the wet-type smoke washing tower 4 where acid gas and the like are completely removed. , And is discharged to the outside or combined with exhaust gas from an incinerator (not shown).

また、前記給水槽5内の減温水にNaOHを適量(少量)添加することにより、減温装置2内でアルカリ性減温水により排ガスと湿式接触させて該排ガス中の高濃度酸性ガス成分は弱酸性化されてバグフィルタ3に送られ、該バグフィルタ3における酸性ガスによる低温腐食を抑制する。   In addition, by adding an appropriate amount (a small amount) of NaOH to the temperature-reduced water in the water supply tank 5, the exhaust gas is brought into wet contact with the exhaust gas by the alkaline temperature-reduced water in the temperature-reducing device 2 so that the high-concentration acidic gas component in the exhaust gas becomes weakly acidic. And sent to the bag filter 3 to suppress low-temperature corrosion of the bag filter 3 due to acid gas.

尚、前記実施例において、減温装置2の噴霧用ノズルの詰まりを回避するには、前記引き抜き排水に含まれる塩分を給水槽5で供給されるNaOHの添加により一度アルカリ溶液として溶解後、減温装置2に供給し、該減温装置2にて排ガス中の高濃度酸性ガス成分を中和させて塩類を析出させるようにすることが必要であるが、該NaOHの添加による減温水のアルカリ性の度合は弱アルカリ程度にし、給水槽5内の減温水のアルカリ度を極力低く押え、給水槽5内での塩類の生成を阻止するのが好ましい。   In the above embodiment, in order to avoid clogging of the spray nozzle of the temperature reducing device 2, the salt contained in the drainage water was once dissolved as an alkaline solution by adding NaOH supplied in the water supply tank 5 and then reduced. It is necessary to supply to the warming device 2 and neutralize the high-concentration acidic gas components in the exhaust gas to precipitate salts by the temperature reducing device 2. It is preferable to make the degree of weak alkaline, to keep the alkalinity of the temperature-reduced water in the water supply tank 5 as low as possible, and to prevent the generation of salts in the water supply tank 5.

図2は本発明の第2実施例を示すプラズマ溶融炉の排ガス処理システムの系統図である。
この実施例においては、前記第1実施例における湿式洗煙塔4及びこれに付設される排水処理装置6を焼却炉(不図示)側に設置している。
FIG. 2 is a system diagram of an exhaust gas treatment system for a plasma melting furnace according to a second embodiment of the present invention.
In this embodiment, the wet-type smoke washing tower 4 of the first embodiment and the wastewater treatment device 6 attached thereto are installed on the incinerator (not shown) side.

従ってこの実施例においては、図1の装置から湿式洗煙塔4、排水処理装置6、及び該排水処理装置6と給水槽5とを接続する排水管15を除去し、バグフィルタ3及びブロワ7を経た排ガスを燃焼炉側の排ガスと混合して湿式洗煙塔40に導入している。
また、給水槽5内の減温水にはNaHCO(重曹)が適量(少量)添加されている。
上記以外の構成は図1の第1実施例と同様であり、これと同一の部材は同一の符号にて示す。
Therefore, in this embodiment, the wet-type smoke washing tower 4, the wastewater treatment device 6, and the drainage pipe 15 connecting the wastewater treatment device 6 and the water supply tank 5 are removed from the apparatus shown in FIG. The flue gas that has passed through is mixed with the flue gas on the combustion furnace side and introduced into the wet smoke washing tower 40.
Further, an appropriate amount (a small amount) of NaHCO 3 (baking soda) is added to the temperature-reduced water in the water supply tank 5.
The configuration other than the above is the same as that of the first embodiment of FIG. 1, and the same members are denoted by the same reference numerals.

この実施例においても、減温装置5への減温水にNaHCOを少量添加してアルカリ性にし、これを減温装置2にて排ガス中に噴霧することにより、バグフィルタ3等の酸性ガス成分による低温腐食を防止するとともに、減温水はアルカリ性になって減温装置2にて排ガス中に噴霧されるため、該アルカリ性減温水により排ガスと湿式接触させて該排ガス中の高濃度酸性ガス成分を弱酸性化させて塩類を析出させる。
該減温装置2を経た排ガスは析出塩類及び飛灰と共に、排ガス管19を介してバグフィルタ3に導入され、ここで析出塩類及び飛灰が除去される。
Also in this embodiment, a small amount of NaHCO 3 is added to the temperature-reduced water to the temperature-reducing device 5 to make it alkaline, and this is sprayed into the exhaust gas by the temperature-reducing device 2, whereby the acid gas component of the bag filter 3 and the like is used. In addition to preventing low-temperature corrosion, the temperature-reduced water becomes alkaline and is sprayed into the exhaust gas by the temperature-reducing device 2, so that the alkaline temperature-reduced water makes wet contact with the exhaust gas to weaken the high-concentration acidic gas component in the exhaust gas. Acidify and precipitate the salts.
The exhaust gas that has passed through the temperature reducing device 2 is introduced into the bag filter 3 via the exhaust gas pipe 19 together with the precipitated salts and fly ash, where the precipitated salts and fly ash are removed.

以上記載のごとく請求項1、2の発明によれば、湿式洗煙塔の引き抜き排水を減温水に混入させて減温装置に送り、この混合減温水を排ガス中に噴霧するように構成したので、引き抜き排水中の塩類は減温装置での前記混合減温水の噴霧により排ガス中に混入されてバグフィルタに送られて該バグフィルタにて確実に除去される。   As described above, according to the first and second aspects of the present invention, the drainage of the wet-type smoke washing tower is mixed with the deheated water and sent to the deheater, and the mixed deheated water is sprayed into the exhaust gas. The salts in the drawn waste water are mixed into the exhaust gas by spraying the mixed de-heated water in the de-heater, sent to the bag filter and surely removed by the bag filter.

これにより、前記湿式洗煙塔からの引き抜き排水を処理する排水処理装置では簡易な重金属の除去のみをなせばよく、排水処理装置の構造が簡単化、かつ小型化され装置コストが低減される。   As a result, in the wastewater treatment apparatus for treating the drainage water drawn from the wet-type smoke washing tower, it is only necessary to perform simple heavy metal removal, and the structure of the wastewater treatment apparatus is simplified, the size is reduced, and the apparatus cost is reduced.

また、洗煙塔からの引き抜き排水中に含まれる塩類を前記減温装置及びバグフィルタでの処理により連続的に系外に排出させることが可能となり、排ガス処理系における塩類の濃縮を防止することができる。   Further, it is possible to continuously discharge the salts contained in the drainage drawn out from the smoke washing tower to the outside of the system by the treatment with the temperature reducing device and the bag filter, thereby preventing the concentration of the salts in the exhaust gas treatment system. Can be.

また請求項3、4の発明によれば、減温水中に適量のNaOHやNaHCO等の塩基類を添加して該減温水をアルカリ性にし、これを排ガス中に噴霧してバグフィルタに流すことにより、バグフィルタに前記アルカリ性の噴霧が送られることとなり、これによって、該バグフィルタの酸性ガスによる低温腐食を防止することができる。 According to the third and fourth aspects of the present invention, an appropriate amount of a base such as NaOH or NaHCO 3 is added to the temperature-reduced water to make the temperature-reduced water alkaline, and this is sprayed into an exhaust gas to flow through a bag filter. As a result, the alkaline spray is sent to the bag filter, whereby the low temperature corrosion of the bag filter due to the acidic gas can be prevented.

さらに、湿式洗煙塔を焼却炉側に設置した場合においても同様に、バグフィルタ等の酸性ガス成分による低温腐食を防止できる。   Furthermore, even when the wet smoke tower is installed on the incinerator side, low-temperature corrosion due to an acidic gas component such as a bag filter can be similarly prevented.

本発明の第1実施例に係るプラズマ溶融炉の排ガス処理システムの系統図である。1 is a system diagram of an exhaust gas treatment system for a plasma melting furnace according to a first embodiment of the present invention. 本発明の第2実施例を示す図1に対応する図である。FIG. 6 is a view corresponding to FIG. 1 and illustrating a second embodiment of the present invention. 本出願人が検討した先行技術を示す図1に対応する図である。FIG. 2 is a diagram corresponding to FIG. 1 showing a prior art studied by the present applicant.

符号の説明Explanation of reference numerals

1 プラズマ溶融炉
2 減温装置
3 バグフィルタ
4 湿式洗煙塔
5 給水槽
6 排水処理装置
7 排ガスファン
9 減温水管
10、11、19 排ガス管
15 排水管
40 湿式洗煙設備(焼却炉側)
DESCRIPTION OF SYMBOLS 1 Plasma melting furnace 2 Temperature reducing device 3 Bag filter 4 Wet smoke washing tower 5 Water supply tank 6 Drainage treatment device 7 Exhaust gas fan 9 Temperature reducing water pipe 10, 11, 19 Exhaust gas pipe 15 Drain pipe 40 Wet smoke cleaning equipment (incinerator side)

Claims (4)

灰溶融炉からの排ガスを、給水槽から供給される減温水により降温させる減温装置と、バグフィルタと、湿式洗煙設備とに順に通過させながら浄化処理するに際し、前記湿式洗煙設備の引き抜き排水を前記給水槽に導入し、該給水槽から前記減温装置に供給して減温水として噴霧することを特徴とする溶融排ガス処理方法。   At the time of purifying the exhaust gas from the ash melting furnace by sequentially passing it through a temperature reducing device for lowering the temperature with the temperature reducing water supplied from the water supply tank, a bag filter, and a wet smoke cleaning device, the wet smoke cleaning device is pulled out. A method for treating molten exhaust gas, comprising introducing wastewater into the water supply tank, supplying the wastewater from the water supply tank to the temperature reducing device, and spraying the same as reduced temperature water. 前記灰溶融炉からの排ガスを燃焼炉側の排ガスと混合して湿式洗煙塔に導入することを特徴とする請求項1記載の溶融排ガス処理方法。   2. The method for treating a molten exhaust gas according to claim 1, wherein the exhaust gas from the ash melting furnace is mixed with the exhaust gas on the combustion furnace side and introduced into a wet smoke washing tower. 前記減温水にNaOH若しくはNaHCO等の塩基成分を添加してアルカリ性減温水となして前記減温装置に供給することを特徴とする請求項1若しくは2記載の溶融排ガス処理方法。 The method for treating a molten exhaust gas according to claim 1, wherein a base component such as NaOH or NaHCO 3 is added to the temperature-reduced water to make alkaline temperature-reduced water and supplied to the temperature-reducing device. 前記給水槽にNaOH若しくはNaHCO等の塩基成分を添加してアルカリ性減温水となしてから前記減温装置に減温水として供給することを特徴とする請求項1若しくは2記載の溶融排ガス処理方法。 3. The method for treating molten exhaust gas according to claim 1, wherein a basic component such as NaOH or NaHCO3 is added to the water supply tank to form alkaline desuperheated water, and then supplied to the deheater as desuperheated water.
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