JP2002292363A - Method for treating dioxins in wastewater from waste disposer and disposer therefor - Google Patents

Method for treating dioxins in wastewater from waste disposer and disposer therefor

Info

Publication number
JP2002292363A
JP2002292363A JP2001110743A JP2001110743A JP2002292363A JP 2002292363 A JP2002292363 A JP 2002292363A JP 2001110743 A JP2001110743 A JP 2001110743A JP 2001110743 A JP2001110743 A JP 2001110743A JP 2002292363 A JP2002292363 A JP 2002292363A
Authority
JP
Japan
Prior art keywords
wastewater
waste
treatment
dioxin
treatment step
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
JP2001110743A
Other languages
Japanese (ja)
Inventor
Shigeo Kondo
重雄 近藤
Yukinori Matsuura
幸宣 松浦
Junichi Ito
純一 伊藤
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.)
JFE Engineering Corp
Original Assignee
NKK Corp
Nippon Kokan Ltd
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 NKK Corp, Nippon Kokan Ltd filed Critical NKK Corp
Priority to JP2001110743A priority Critical patent/JP2002292363A/en
Publication of JP2002292363A publication Critical patent/JP2002292363A/en
Pending legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To provide a method for treating dioxins(DXN) in wastewater from a waste disposer, whereby the discharged water will fulfie severer regulations on a dioxin concentration in future which, and the costs of an installation, a maintenance, an exchange, and an operation is reduced, and to provide the disposer therefor. SOLUTION: A DXN-containing wastewater disposer 20 is a combination of (i) a DXN-containing wastewater system M that collects DXN-containing wastewater arising from the bringing into contact with a product of waste incineration in each treatment step and from the washing of substances with which it is brought into contact, (ii) a water collection tank 28 that receives the collected wastewater, and (iii) a waste water return means N that returns the wastewater from the tank 28 to the waste incineration step. By means of a selector 35, the wastewater is returned to a waste pit 22 or an furnace incinerator 23 to be used in a incineration step or is returned to a temperature- lowering tower 25 to be treated in a cooling step and is detoxified in a waste gas treatment step. Alternatively, the wastewater is simultaneously returned to the pit 22, incinerator 23, and the tower 25 and is treated and detoxified.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は産業廃棄物(可燃
物)、一般廃棄物を処理するストーカ、流動床、キルン
等の焼却処理施設、ガス化溶融処理施設等の廃棄物処理
設備による排水中のダイオキシン類処理方法及びその装
置に関する。
The present invention relates to wastewater discharged from waste treatment facilities such as stokers for treating industrial waste (combustibles) and general waste, fluidized beds, kilns, and other incineration facilities, and gasification and melting treatment facilities. And a method for treating dioxins.

【0002】[0002]

【従来の技術】従来、廃棄物処理設備の廃棄物処理工程
即ち燃焼処理工程、ガス冷却処理工程、排ガス処理工程
で発生する排水処理は一般的に凝集沈殿法で処理され、
その処理水を更に砂濾過処理法で処理している。
2. Description of the Related Art Conventionally, wastewater treatment processes in waste treatment facilities, that is, wastewater treatment generated in a combustion treatment process, a gas cooling treatment process, and an exhaust gas treatment process are generally treated by a coagulation sedimentation method.
The treated water is further processed by a sand filtration method.

【0003】図2は上記排水処理を行うための排水処理
設備の一例を示す概略図である。排水処理設備1は凝集
沈殿槽2と下流側に中和槽3を介して砂濾過塔4を配置
している。
FIG. 2 is a schematic diagram showing an example of a wastewater treatment facility for performing the above wastewater treatment. The wastewater treatment equipment 1 has a sand filtration tower 4 disposed via a coagulation sedimentation tank 2 and a neutralization tank 3 on the downstream side.

【0004】排水処理の対象は一般にプラットホーム洗
浄水、洗車排水、灰溶融設備排水、純水装置排水、灰汚
水槽排水等である。
The objects of wastewater treatment are generally platform washing water, car washing drainage, ash melting facility drainage, pure water drainage, ash sewage tank drainage, and the like.

【0005】プラットホーム洗浄水、洗車排水は有機排
水槽5に送られ、そこでポンプP1により有機系調整槽
6に圧送され、有機系調整槽6を経て生物処理槽7で曝
気されて無機排水槽8に送られる。
[0005] The platform washing water and the car wash drainage are sent to an organic drainage tank 5, where they are pumped to an organic control tank 6 by a pump P1 and are aerated in a biological treatment tank 7 through the organic control tank 6 and an inorganic drain tank 8 is provided. Sent to

【0006】一方灰溶融設備9、純水装置10、灰汚水
槽11の各排水は無機排水槽8に送られる。また、ゴミ
ピットに設けたドレンピット12のドレン、汚泥濃縮槽
17の処理水も無機排水槽8に送られる。P2はドレン
を無機排水槽8に圧送するためのポンプである。
On the other hand, each wastewater from the ash melting facility 9, the pure water apparatus 10, and the ash sewage tank 11 is sent to the inorganic drainage tank 8. The drain of the drain pit 12 provided in the garbage pit and the treated water of the sludge concentration tank 17 are also sent to the inorganic drain tank 8. P2 is a pump for pumping the drain to the inorganic drain tank 8 under pressure.

【0007】これらの排水は無機排水槽8からポンプP
3により無機系調整槽13に圧送され、無機系調整槽1
3を経て反応槽14で苛性ソーダによる中和処理,凝集
槽15で凝集剤による凝集処理が施される。
[0007] These wastewaters are supplied from an inorganic drainage tank 8 to a pump P.
3 to the inorganic adjustment tank 13 and the inorganic adjustment tank 1
After 3, a neutralization treatment with caustic soda is performed in a reaction tank 14, and a coagulation treatment with a coagulant is performed in a coagulation tank 15.

【0008】中和処理、凝集処理が施された排水は凝集
沈殿槽2に送られる。該排水は撹拌機16で攪拌された
後、凝集された汚泥がポンプP4により汚泥濃縮槽17
に圧送される。汚泥濃縮槽17で濃縮された汚泥はゴミ
ピット等に圧送される。
The wastewater subjected to the neutralization treatment and the coagulation treatment is sent to the coagulation sedimentation tank 2. After the waste water is stirred by the stirrer 16, the aggregated sludge is removed by the pump P 4 in the sludge concentration tank 17.
To be pumped. The sludge concentrated in the sludge concentration tank 17 is pumped to a garbage pit or the like.

【0009】一方、凝集沈殿槽2で凝集汚泥を分離した
処理液は濾過水槽18に送られ、ポンプP5により砂濾
過塔4に圧送され、砂濾過塔4を通された後、放流槽に
蓄えられ、必要に応じて系外へ放流されるか、または再
利用に共される。
On the other hand, the treated liquid from which the coagulated sludge is separated in the coagulation sedimentation tank 2 is sent to a filtration water tank 18, pumped to a sand filtration tower 4 by a pump P 5, passed through the sand filtration tower 4, and stored in a discharge tank. And discharged to the outside of the system as needed, or used for reuse.

【0010】図2による排水処理設備1では元来排水中
の重金属と有機物の除去を目的としているが、浮遊物質
に吸着しているダイオキシン類も同時に除去される。
Although the purpose of the wastewater treatment equipment 1 shown in FIG. 2 is to originally remove heavy metals and organic substances in wastewater, dioxins adsorbed on suspended substances are also removed.

【0011】ダイオキシン類の除去はダイオキシン類特
別処置法により排出基準が定められたことで、排水処理
設備1についても見直しが行われ、凝集沈殿槽と砂濾過
塔の後段に高度処理装置として紫外線照射、オゾン、水
酸化イオン等による促進酸化処理設備、膜分離設備を設
置することも提案されている。
As for the removal of dioxins, the wastewater treatment equipment 1 was reviewed as emission standards were determined by the Dioxins Special Treatment Law, and ultraviolet irradiation was performed as an advanced treatment device after the coagulation sedimentation tank and sand filtration tower. It is also proposed to install a facility for accelerated oxidation treatment using ozone, hydroxide ions and the like, and a membrane separation facility.

【0012】[0012]

【発明が解決する課題】図2による排水処理設備1は、
凝集沈殿と砂濾過処理により高いダイオキシン類の除去
率が得られる。排水処理設備1で扱う排水は前述したよ
うにプラットホーム洗浄水、洗車排水、灰溶融設備排
水、純水装置排水、灰汚水等である。
The wastewater treatment equipment 1 according to FIG.
A high dioxin removal rate can be obtained by coagulation sedimentation and sand filtration. The effluents treated by the effluent treatment equipment 1 are platform washing water, car washing effluent, ash melting equipment effluent, pure water effluent, ash sewage and the like, as described above.

【0013】しかしながら、凝集沈殿と砂濾過処理によ
るダイオキシン類の除去は既に限界に達しており、現在
以上の除去率向上は期待できないことから、規制強化に
よって更に厳しい排出基準が定められた場合には対応で
きない。また、前述の排水処理設備で扱う排水の内、プ
ラットホーム洗浄水、洗車排水、灰溶融設備排水、純水
装置排水はダイオキシン類を含有しないので、従来の凝
集沈殿と砂濾過処理及びその後段に設置される高度処理
はダイオキシン類除去設備としては希釈による濃度低下
で負荷を下げる一方で処理量を肥大化させている。
However, removal of dioxins by coagulation sedimentation and sand filtration has already reached its limit, and it is not possible to expect a further increase in the removal rate. Therefore, if stricter emission standards are set by tightening regulations, I can not cope. Of the wastewater handled by the wastewater treatment equipment mentioned above, platform washing water, car washing wastewater, ash melting equipment wastewater, and pure water equipment wastewater do not contain dioxins, so they are installed in the conventional coagulation sedimentation and sand filtration treatments, and installed in the subsequent stage. The advanced treatment used for dioxin removal equipment reduces the load due to the decrease in concentration due to dilution, while increasing the treatment amount.

【0014】一方、凝集沈殿槽と砂濾過処理塔の後段に
紫外線照射、酸素、オゾン供給設備、循環ポンプ等を有
する促進酸化処理設備、膜分離設備を設置する提案の場
合は、今後予想される規制強化等によるより厳しい水質
基準に対応できると考えられるが、従来の排水処理設備
に加えて促進酸化処理設備、膜分離設備の設置面積を必
要とし、また、特殊な機器、装置を用いるために設置費
用、維持・交換費用等の負担が大きい。
On the other hand, a proposal to install an accelerated oxidation treatment facility having a UV irradiation, an oxygen and ozone supply facility, a circulation pump, etc., and a membrane separation facility at a stage subsequent to the coagulation sedimentation tank and the sand filtration tower is expected in the future. It is thought that it can respond to stricter water quality standards due to stricter regulations, but requires installation areas for accelerated oxidation treatment equipment and membrane separation equipment in addition to conventional wastewater treatment equipment, and requires the use of special equipment and equipment. Large burden of installation cost, maintenance and replacement cost, etc.

【0015】特に、促進酸化処理設備は、紫外線照射、
酸素、オゾン供給設備、循環ポンプ等の電力消費が大き
いので、運転費用の負担も大きい。
[0015] In particular, the accelerated oxidation treatment equipment is provided with ultraviolet irradiation,
Since the power consumption of oxygen, ozone supply equipment, circulation pumps, and the like is large, the burden of operating costs is also large.

【0016】本発明は上記のような問題点の解決を図っ
たものであり、今後の規制強化に対応できる放流水濃度
が確保でき、設置費用、維持・交換費用、運転費用等の
負担を低減できる廃棄物処理設備の排水中のダイオキシ
ン類処理方法及びその装置を提供することを目的とす
る。
The present invention has been made to solve the above-mentioned problems, and can secure the concentration of effluent water that can cope with the tightening of regulations in the future, and reduce the burden of installation costs, maintenance and replacement costs, operation costs, and the like. It is an object of the present invention to provide a method and an apparatus for treating dioxins in wastewater of a waste treatment facility.

【0017】[0017]

【課題を解決するための手段】本発明者等は上述した排
水処理設備の課題を解決するために各課題を整理し、検
討を行った。まず、目標としてダイオキシン類に対し
て高い分解・除去能力をもつこと、または排水処理設備
にダイオキシン類含有排水を流入させないこと、小型
で安価なダイオキシン類処理装置とすることを掲げ、
の対策としてダイオキシン類含有排水のみを独立した系
統とする。の対策として主灰、飛灰、排ガスと接触す
る物体を洗浄した排水を独立した系統とする。それによ
って下記のような発明に到達したものである。
Means for Solving the Problems The present inventors have organized and examined the respective problems in order to solve the above-mentioned problems of the wastewater treatment equipment. First, the goal was to have a high decomposition / removal capacity for dioxins, or to prevent dioxin-containing wastewater from flowing into wastewater treatment equipment, and to use a small and inexpensive dioxin treatment device.
As a countermeasure, only the dioxin-containing wastewater will be an independent system. As a countermeasure against waste, separate drainage from objects that come into contact with main ash, fly ash, and exhaust gas will be used. As a result, the following invention has been achieved.

【0018】請求項1に係る発明は、廃棄物処理設備に
よる廃棄物の燃焼処理、排ガスの冷却処理、排ガス処理
の工程からなる廃棄物処理工程により廃棄物を処理する
際に、該廃棄物処理物と接触して及び/または接触した
物体を洗浄して生じるダイオキシン類含有排水を集め、
該ダイオキシン類含有排水を前記処理工程に戻して処理
し無害化することを特徴とする廃棄物処理設備の排水中
のダイオキシン類処理方法である。
According to the first aspect of the present invention, when the waste is treated in a waste treatment process including a waste treatment process, a waste gas cooling process, and an exhaust gas treatment process by a waste treatment facility, the waste treatment is performed. Collecting dioxin-containing wastewater produced by contacting and / or washing the contacted object,
A method for treating dioxins in wastewater from a waste treatment facility, wherein the dioxin-containing wastewater is returned to the treatment step for treatment and detoxification.

【0019】請求項2に係る発明は、請求項1に係る発
明において、ダイオキシン類含有排水を廃棄物に含有さ
せて燃焼処理工程で処理し、排ガス処理工程で無害化す
ることを特徴とする。
The invention according to claim 2 is characterized in that, in the invention according to claim 1, dioxin-containing wastewater is contained in waste and treated in a combustion treatment step, and detoxified in an exhaust gas treatment step.

【0020】請求項3に係る発明は、請求項1又は請求
項2に係る発明において、ダイオキシン類含有排水を燃
焼処理工程に設置された炉の内部に噴霧して該燃焼処理
工程で処理し、排ガス処理工程で無害化することを特徴
とする。
According to a third aspect of the present invention, in the first or second aspect of the invention, dioxin-containing wastewater is sprayed into a furnace installed in the combustion treatment step and treated in the combustion treatment step. It is detoxified in an exhaust gas treatment process.

【0021】請求項4に係る発明は、請求項1、請求項
2又は請求項3に係る発明において、ダイオキシン類含
有排水を冷却処理工程に設置された減温塔に戻して冷却
処理工程で蒸発させ、排ガス処理工程で無害化すること
を特徴とする。
According to a fourth aspect of the present invention, in the first, second or third aspect of the present invention, the dioxin-containing wastewater is returned to the temperature reducing tower provided in the cooling step and evaporated in the cooling step. And detoxification in the exhaust gas treatment process.

【0022】請求項5に係る発明は、廃棄物供給手段を
有する廃棄物処理設備の燃焼処理、冷却処理、排ガス処
理の工程からなる廃棄物処理工程で発生する排水中のダ
イオキシン類を処理する処理装置であって、前記廃棄物
処理工程で発生するダイオキシン類含有排水を集めるダ
イオキシン類含有排水系統と、集めた該排水を受け入れ
る集水槽と、該集水槽から前記廃棄物処理工程に該排水
を戻す排水戻し手段とを組合わせて設置したことを特徴
とする廃棄物処理設備の排水中のダイオキシン類処理装
置である。
According to a fifth aspect of the present invention, there is provided a process for treating dioxins in waste water generated in a waste treatment process including a combustion treatment, a cooling treatment, and an exhaust gas treatment in a waste treatment facility having a waste supply means. An apparatus, comprising: a dioxin-containing wastewater system for collecting dioxin-containing wastewater generated in the waste treatment step; a water collecting tank for receiving the collected wastewater; and returning the wastewater from the water collection tank to the waste treatment step. An apparatus for treating dioxins in wastewater of a waste treatment facility, wherein the dioxin is disposed in combination with wastewater return means.

【0023】請求項6に係る発明は、請求項5に係る発
明において、ダイオキシン類含有排水を廃棄物供給施設
に戻すための排水戻し手段を設置したことを特徴とす
る。
The invention according to claim 6 is characterized in that, in the invention according to claim 5, a wastewater return means for returning dioxin-containing wastewater to a waste supply facility is provided.

【0024】請求項7に係る発明は、請求項5又は請求
項6に係る発明において、ダイオキシン類含有排水を燃
焼処理工程に設置された炉の内部に戻す排水戻し手段を
設置したことを特徴とする。
The invention according to claim 7 is characterized in that, in the invention according to claim 5 or 6, a waste water return means for returning dioxin-containing waste water to the inside of a furnace installed in the combustion treatment step is provided. I do.

【0025】請求項8に係る発明は、請求項5、請求項
6又は請求項7に係る発明において、ダイオキシン類含
有排水を冷却処理工程に設置された減温塔に戻す排水戻
し手段を設置したことを特徴とする。
The invention according to claim 8 is the invention according to claim 5, 6, or 7, further comprising a wastewater return means for returning the dioxin-containing wastewater to the cooling tower installed in the cooling process. It is characterized by the following.

【0026】本発明で対象とする廃棄物はゴミ等の一般
廃棄物、可燃物による産業廃棄物であり、それを処理す
る廃棄物処理設備はストーカ、流動床、キルン等の焼却
処理施設、ガス化溶融処理施設等を含むものである。
The wastes to be treated in the present invention are general wastes such as garbage and industrial wastes due to combustibles. Waste treatment facilities for treating the wastes include stokers, fluidized beds, incineration facilities such as kilns, and gas. It includes a chemical fusion treatment facility and the like.

【0027】また、一般に廃棄物処理設備は廃棄物を例
えばゴミをゴミ焼却炉に供給するホッパー、シユート等
の供給手段を有するが、その場合ゴミをホッパーに円滑
に供給するために、敷地内にゴミを仮置するゴミ置場
(ピツト)が設けられている。
In general, waste treatment equipment has a supply means such as a hopper or a short supply for supplying waste to a refuse incinerator, for example. A garbage storage area (pits) for temporarily storing garbage is provided.

【0028】しかし、廃棄物処理設備が小規模等の場合
には直接運搬してきた廃棄物が廃棄物置場(ピツト)を
使用しないでホッパー等に供給される場合があるので、
請求項6では廃棄物ピットを含めた廃棄物供給手段を規
定した。
However, when the waste treatment equipment is small, the directly transported waste may be supplied to a hopper or the like without using a waste storage area (pit).
Claim 6 defines a waste supply means including a waste pit.

【0029】本発明によれば、ダイオキシン類含有排水
を集めて受け入れる集水槽と該集水槽からダイオキシン
類含有排水のみを廃棄物処理工程に戻す手段とを設置す
ることにより、廃棄物焼却物と接触して及び/または接
触した物体を洗浄して生じるダイオキシン類含有排水の
みを集めて、それを前記処理工程に戻して処理し、排ガ
ス処理工程で無害化することができる。従って、ダイオ
キシン類含有排水は通常と同じく廃棄物処理工程で処理
され、排ガス処理工程で無害化される。
According to the present invention, by installing a water collecting tank for collecting and receiving dioxin-containing wastewater and a means for returning only dioxin-containing wastewater from the water collection tank to the waste treatment step, contact with waste incineration can be achieved. Then, only the dioxin-containing wastewater generated by washing and / or washing the contacted object is collected, returned to the above-mentioned treatment step, treated, and detoxified in the exhaust gas treatment step. Therefore, the dioxin-containing wastewater is treated in the waste treatment process as usual, and is rendered harmless in the exhaust gas treatment process.

【0030】[0030]

【発明の実施の形態】以下に、本発明による廃棄物処理
設備の実施形態の一例としてゴミ焼却設備を図によって
詳述する。図1は本発明による実施形態の一例のゴミ焼
却設備を示す概略図である。ゴミ焼却設備21はゴミ焼
却処理工程を燃焼処理工程、ガス冷却処理工程、排ガス
処理工程に大別し、下記に述べるように各処理工程に設
置される装置等の代表例を示す。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Hereinafter, a waste incineration facility will be described in detail with reference to the drawings as an example of an embodiment of a waste disposal facility according to the present invention. FIG. 1 is a schematic diagram showing an example of a refuse incinerator according to an embodiment of the present invention. The refuse incineration equipment 21 roughly divides the refuse incineration treatment process into a combustion treatment process, a gas cooling treatment process, and an exhaust gas treatment process, and shows typical examples of devices installed in each treatment process as described below.

【0031】燃焼処理工程にはゴミ投入ホッパに付設さ
れたゴミピット22、火格子等を設けた燃焼室とボイラ
等を備えた焼却炉23が設置され、ガス冷却処理工程に
はエコノマイザ24と減温塔25が設置されて、そして
排ガス処理工程にはバグフィルタ等の集じん機26、煙
突27が設置されている。
A refuse pit 22 attached to a refuse input hopper, a combustion chamber provided with a grate and the like and an incinerator 23 provided with a boiler and the like are installed in the combustion processing step, and an economizer 24 and a temperature reducing apparatus are provided in the gas cooling processing step. A tower 25 is installed, and a dust collector 26 such as a bag filter and a chimney 27 are installed in the exhaust gas treatment process.

【0032】上記ゴミ焼却処理工程によれば、ゴミはゴ
ミピット22で受けて、そこからゴミ投入ホッパに投入
されて焼却炉23で燃焼され燃焼ガスと主灰に分離され
る。燃焼ガスは800℃以上(好ましくは850℃以
上)に維持されて完全燃焼されて次工程に排ガスとして
排出される。排ガスはエコノマイザ24と減温塔25で
200℃以下に冷却されて集じん機(バグフイルタ)2
6で集塵され、浄化された排ガスは誘引通風機を介して
煙突27から大気中に放散される。
According to the above-described refuse incineration process, refuse is received by the refuse pit 22 and is then introduced into a refuse input hopper, where it is burned in the incinerator 23 and separated into combustion gas and main ash. The combustion gas is maintained at 800 ° C. or higher (preferably 850 ° C. or higher), is completely burned, and is discharged as exhaust gas in the next step. The exhaust gas is cooled to 200 ° C. or lower in an economizer 24 and a cooling tower 25 and is collected by a dust filter (bag filter) 2.
The exhaust gas that has been collected and purified in step 6 is released from the chimney 27 into the atmosphere via an induction ventilator.

【0033】本発明ではダイオキシン類含有排水処理装
置20として上記各処理工程でゴミ焼却物と接触して及
び/又は接触した物体を洗浄して生じるダイオキシン類
含有排水を集めるダイオキシン類含有排水系統Mと、集
めたダイオキシン類含有排水を受け入れる集水槽28
と、該集水槽28から前記ゴミ焼却処理工程に該排水を
戻す排水戻し手段Nとを組合わせて設置した装置であ
る。
In the present invention, the dioxin-containing wastewater treatment apparatus 20 includes a dioxin-containing wastewater system M that collects dioxin-containing wastewater generated by contacting and / or washing the incinerated material in each of the above-described treatment steps. , Receiving the collected dioxin-containing wastewater
And a waste water return means N for returning the waste water from the water collecting tank 28 to the refuse incineration treatment step.

【0034】ゴミ焼却物は主灰、飛灰、排ガスであり、
接触した物体は各工程に設置され該ゴミ焼却物と接触し
た装置と、主灰、飛灰を処理し系外に積み出すまでの工
程で主灰、飛灰と接触した搬送コンベヤ、混練機、処理
物バンカ、それらの設置された床面等の全てを対象とす
る。ダイオキシン類含有排水を全て集めるためである。
The waste incineration is main ash, fly ash and exhaust gas.
The contacted object is installed in each process and the equipment that comes in contact with the garbage incineration material, the main ash in the process of processing the fly ash and loading it out of the system, the conveyor that comes in contact with the fly ash, the kneader, Targets include all processed bunkers and their installed floors. This is for collecting all dioxin-containing wastewater.

【0035】図1の実施形態ではダイオキシン類含有排
水系統M(以下DXN含有排水系統Mと云う)は大別し
て焼却炉23で分離された主灰に接触して及び/又は接
触した物体を洗浄して生じるDXN含有排水系統M1、
M2とエコノマイザ24と減温塔25と集じん機(バグ
フイルタ)26で捕集された飛灰に接触して及び/又は
接触した物体を洗浄して生じるDXN含有排水系統M
3、M4で構成している。
In the embodiment shown in FIG. 1, the dioxin-containing drainage system M (hereinafter referred to as DXN-containing drainage system M) is roughly classified into contact with main ash separated in the incinerator 23 and / or cleaning of the contacted objects. DXN-containing drainage system M1
DXN-containing drainage system M generated by contacting fly ash collected by M 2, economizer 24, cooling tower 25, and dust collector (bag filter) 26 and / or washing the contacted object
3, M4.

【0036】上記主灰は一般に灰溶融装置32で120
0〜1600℃でスラグ化して、ダイオキシン類濃度の
削減と減容化が図られている。しかしその一部は灰沈殿
槽33で沈静され、灰沈殿物は系外に積み出される。灰
沈殿槽33での処理水(便宜上灰泥水と云う)はDXN
含有排水系統M1で集水槽28に送られる。また、灰沈
殿槽33から灰沈殿物を積み出す際に生じるDXN含有
洗浄水(便宜上床洗浄水と云う)はDXN含有排水系統
M2で集水槽28に送られる。
The main ash is generally supplied to the ash melting device 32 at 120
The slag is formed at 0 to 1600 ° C. to reduce the concentration and volume of dioxins. However, a part thereof is calmed down in the ash sedimentation tank 33, and the ash sediment is unloaded outside the system. The treated water (ash mud for convenience) in the ash sedimentation tank 33 is DXN
It is sent to the water collecting tank 28 in the contained drainage system M1. Further, DXN-containing washing water (referred to as floor washing water for convenience) generated when unloading the ash sediment from the ash sedimentation tank 33 is sent to the water collecting tank 28 in the DXN-containing drainage system M2.

【0037】一方、飛灰は捕集された後、埋立地等への
利用のために、減容化、含有重金属の流出防止等の処理
をするために飛灰処理装置34に送られ、そこで溶融固
化、セメント固化、薬剤処理、酸及びその他の溶媒によ
る安定化処理等が施される。
On the other hand, after the fly ash is collected, the fly ash is sent to a fly ash treatment device 34 to reduce the volume and prevent the outflow of heavy metals contained therein for use in a landfill or the like. Melt solidification, cement solidification, chemical treatment, stabilization treatment with acids and other solvents and the like are performed.

【0038】その際に飛灰と接触した搬送コンベヤ、混
練機、処理物バンカ、それらの設置された床面等のDX
N含有洗浄水(便宜上床洗浄水と云う)はDXN含有排
水系統M3、M4で集水槽28に送られる。
At this time, the DX such as a conveyor, a kneader, a processed bunker, and a floor on which the conveyor is in contact with the fly ash.
The N-containing washing water (referred to as floor washing water for convenience) is sent to the water collecting tank 28 in the DXN-containing drainage systems M3 and M4.

【0039】集水槽28は従来の灰汚水槽と異なり、集
水槽28からゴミ焼却設備に隣接した排水処理設備への
排水系統を無くし、DXN含有排水系統Mから集められ
たDXN含有排水を受け入れて、そこからゴミ焼却処理
工程にDXN含有排水を戻す拠点としたものである。又
前述の通り、DXN含有排水はゴミ焼却物と接触して及
び/又は接触した物体を洗浄して生じることから、主灰
及び飛灰の処理・搬出設備の床洗浄水、床沈殿槽のオー
バーフロー水等として現れ、発生量が時間的に大きく変
化する性質を持つ。従って、集水槽28は流量変動を吸
収するバッファタンクとして、処理工程の安定化に貢献
する。集水槽28は一個に限定されるものではなく、必
要に応じて適宜設けることができる。従って、従来の灰
汚水槽も一部改良して本発明の集水槽28として利用す
ることもできる。
Unlike the conventional ash wastewater tank, the water collecting tank 28 eliminates the drainage system from the water collecting tank 28 to the wastewater treatment facility adjacent to the refuse incineration facility, and receives the DXN-containing wastewater collected from the DXN-containing wastewater system M. This is a base from which DXN-containing wastewater is returned to the garbage incineration process. Also, as described above, DXN-containing wastewater is generated by contacting and / or cleaning objects in contact with garbage incineration, so that floor rinsing water of the main ash and fly ash treatment / export equipment and overflow of the floor sedimentation tank. It appears as water and the like, and has the property that the amount of generation greatly changes over time. Therefore, the water collecting tank 28 contributes to the stabilization of the processing step as a buffer tank absorbing the fluctuation of the flow rate. The number of the water collecting tanks 28 is not limited to one, and can be appropriately provided as needed. Therefore, the conventional ash sewage tank can be partially modified and used as the water collecting tank 28 of the present invention.

【0040】集水槽28からゴミ焼却処理工程に戻す排
水戻し手段Nは、排水供給系統29と供給装置30と吹
込み装置31から構成され、一般には排水供給系統29
に排水管、供給装置30にポンプP、吹込み装置31に
ノズルが用いられている。排水戻し手段Nは排水供給系
統29に切替装置35を設けて、好ましい例としてゴミ
ピット22と焼却炉23と減温塔25に分岐排水供給系
統29a、29b、29cを設けている。
The drainage return means N for returning the wastewater from the water collecting tank 28 to the refuse incineration process comprises a drainage supply system 29, a supply device 30, and a blowing device 31.
, A pump P for the supply device 30, and a nozzle for the blowing device 31. The drainage return means N is provided with a switching device 35 in the drainage supply system 29, and as preferable examples, branch wastewater supply systems 29 a, 29 b, and 29 c are provided in the garbage pit 22, the incinerator 23, and the cooling tower 25.

【0041】切替装置35によってDXN含有排水をゴ
ミピット22に戻して燃焼処理工程で処理し、DXN含
有排水を焼却炉23に戻して燃焼処理工程で処理し、ま
た、DXN含有排水を減温塔に戻して冷却工程で蒸発さ
せ、無害化を排ガス処理工程で行うことができ、更には
それらを互いに組み合わせて例えばDXN含有排水をゴ
ミピット22と焼却炉23と減温塔25に同時に戻して
ゴミ焼却処理工程の各処理工程で処理し、排ガス処理工
程で無害化することができる。
The DXN-containing wastewater is returned to the garbage pit 22 by the switching device 35 and treated in the combustion treatment step, the DXN-containing wastewater is returned to the incinerator 23 and treated in the combustion treatment step, and the DXN-containing wastewater is returned to the cooling tower. It can be returned and evaporated in a cooling step, and detoxification can be performed in an exhaust gas treatment step. Further, they are combined with each other and, for example, DXN-containing wastewater is simultaneously returned to the garbage pit 22, the incinerator 23, and the temperature reducing tower 25 to incinerate the garbage. It can be treated in each processing step of the process, and can be rendered harmless in the exhaust gas treatment step.

【0042】図1による実施形態で廃棄物処理設備の一
例としてゴミ焼却設備を取り上げ、ゴミピット22と焼
却炉23と減温塔25について説明したが、返送先はこ
れに限定されるものではなく上記した廃棄物処理工程内
に設置された装置等において、DXN含有排水を戻すこ
とのできる箇所にDXN含有排水を例えば吹き込むこと
ができる。
In the embodiment shown in FIG. 1, a garbage incineration facility is taken up as an example of a waste treatment facility, and the garbage pit 22, the incinerator 23, and the cooling tower 25 have been described. However, the return destination is not limited to this. DXN-containing wastewater can be blown into a place where the DXN-containing wastewater can be returned, for example, in a device or the like installed in the waste treatment process.

【0043】図1のDXN含有排水処理装置20によれ
ば、ゴミ焼却設備21による燃焼処理、冷却処理、排ガ
ス処理の工程からなるゴミ焼却処理工程によりゴミ焼却
物を処理する際に、該ゴミ焼却物と接触して及び/また
は接触した物体を洗浄して生じるDXN含有排水を集
め、該DXN含有排水を各焼却処理工程の少なくとも一
つの処理工程に戻して焼却処理工程内において処理し無
害化することができる。
According to the DXN-containing wastewater treatment apparatus 20 shown in FIG. 1, the waste incineration process is performed in the waste incineration process including the combustion process, the cooling process, and the exhaust gas process by the waste incineration facility 21. DXN-containing waste water generated by contacting and / or washing the contacted object is collected, and the DXN-containing waste water is returned to at least one treatment step of each incineration treatment step to be treated and rendered harmless in the incineration treatment step. be able to.

【0044】特に好ましい例では切替装置35によって
ダイオキシン類含有排水をゴミピット22に戻して燃焼
処理工程で処理し、ダイオキシン類含有排水を焼却炉2
3に戻して燃焼処理工程で処理し、DXN含有排水を減
温塔に戻して冷却工程で蒸発させ、無害化を排ガス処理
工程で行う。更にはそれら互いに組み合わせて同時にダ
イオキシン類含有排水をゴミ焼却処理工程の各処理工程
で処理して、排ガス処理工程で無害化することができ
る。
In a particularly preferred example, the dioxin-containing waste water is returned to the garbage pit 22 by the switching device 35 and treated in the combustion treatment step.
3 and treated in the combustion treatment step, and the DXN-containing wastewater is returned to the cooling tower and evaporated in the cooling step, and detoxification is performed in the exhaust gas treatment step. Furthermore, the dioxin-containing wastewater can be treated in each treatment step of the garbage incineration treatment step in combination with each other to be rendered harmless in the exhaust gas treatment step.

【0045】以上のように、図1による実施形態ではゴ
ミ焼却設備によるゴミ焼却処理工程で発生するDXN含
有排水は隣接する排水処理設備に送らないので、排水処
理設備で扱う排水のダイオキシン類の濃度を低減するこ
とができる。従って、規制強化等によって更に排出基準
が改正された場合でも対応できる。また、排水処理設備
はDXN含有排水の処理を含まないので、その分だけコ
ンパクトにできる。
As described above, in the embodiment shown in FIG. 1, the DXN-containing wastewater generated in the garbage incineration process by the garbage incineration facility is not sent to the adjacent wastewater treatment facility. Can be reduced. Therefore, it is possible to cope with the case where the emission standard is further revised due to the strengthening of regulations. Further, since the wastewater treatment equipment does not include the treatment of the DXN-containing wastewater, it can be made more compact accordingly.

【0046】また、凝集沈殿槽と砂濾過塔の後段に高度
処理装置として紫外線照射等による促進酸化処理設備、
膜分離設備を設置しなくてもダイオキシン類の濃度を低
減することができる。
Further, an advanced oxidation treatment equipment such as ultraviolet irradiation as an advanced treatment equipment is provided downstream of the coagulation sedimentation tank and the sand filtration tower.
The concentration of dioxins can be reduced without installing a membrane separation facility.

【0047】なお、本発明では前記ゴミ焼却処理工程に
戻すダイオキシン類含有排水量はゴミ焼却設備における
焼却炉の各処理工程で扱う単位当たりのゴミ焼却処理能
力により定まる投入水量より下回るようにする。一例と
してゴミ焼却設備では一般にゴミ焼却設備での廃熱ボイ
ラ等の効率を満足させるためにゴミカロリー計算による
処理可能な排水量を規定される。検討例として焼却能力
100t/日、ゴミカロリー2400kcal/kg、
ゴミカロリー低下の許容範囲を1000kcal/kg
とすると、一般に知られている三成分値によるゴミカロ
リー推定式による処理可能な排水量は14.3t/日で
ある。
In the present invention, the amount of dioxin-containing wastewater returned to the refuse incineration treatment step is set to be smaller than the input water amount determined by the refuse incineration treatment capacity per unit handled in each treatment step of the incinerator in the refuse incineration equipment. As an example, in waste incineration facilities, generally, the amount of wastewater that can be treated by garbage calorie calculation is defined in order to satisfy the efficiency of a waste heat boiler or the like in the waste incineration facilities. As an example of study, incineration capacity 100t / day, garbage calories 2400kcal / kg,
Allowable range of reduction of garbage calories is 1000kcal / kg
Then, the amount of wastewater that can be treated using the generally known garbage calorie estimation formula based on three component values is 14.3 t / day.

【0048】現在、殆どのゴミ焼却設備では上記したダ
イオキシン類含有排水量は数t/kgであり、それらを
本発明により全量処理してもゴミ焼却設備での排水処理
能力を上回ることはない。
At present, in most garbage incineration facilities, the above-mentioned dioxin-containing wastewater amount is several t / kg, and even if they are completely treated according to the present invention, they do not exceed the wastewater treatment capacity of the garbage incineration facility.

【0049】以上は実施形態の一例としてゴミ焼却処理
設備について述べたが、ゴミ以外の廃棄物例えば可燃物
の産業廃棄物についても同様な効果が得られることはい
うまでもない。また、ゴミ焼却処理設備にストーカー焼
却炉を用いたがこれに限定されるものではなく、流動
床、キルン等の焼却処理施設、ガス化溶融処理施設等も
用いることができる。
Although the waste incineration equipment has been described above as an example of the embodiment, it goes without saying that similar effects can be obtained for waste other than waste, for example, industrial waste of combustible materials. In addition, a stoker incinerator is used as the garbage incineration equipment, but the invention is not limited to this, and an incineration facility such as a fluidized bed or a kiln, a gasification and melting facility, or the like can also be used.

【0050】[0050]

【発明の効果】以上のように、本発明は廃棄物処理工程
で発生するダイオキシン類含有排水を集めるダイオキシ
ン類含有排水系統と、集めた該排水を受け入れる集水槽
と、該集水槽から前記廃棄物処理工程に該排水を戻す排
水戻し手段とを組合わせて設置した簡単な排水中のダイ
オキシン類処理装置によって、今後の規制強化に対応で
きる放流水濃度が確保でき、設置費用、維持・交換費
用、運転費用等の負担を軽くできる。
As described above, the present invention provides a dioxin-containing wastewater system for collecting dioxin-containing wastewater generated in a waste treatment process, a water collecting tank for receiving the collected wastewater, and a method for collecting the wastewater from the water collecting tank. A simple treatment device for dioxins in wastewater installed in combination with wastewater return means that returns the wastewater to the treatment process can ensure the concentration of effluent water that can respond to stricter regulations in the future, installation costs, maintenance and replacement costs, The burden of operating costs can be reduced.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明による実施形態の一例を示す概略図であ
る。
FIG. 1 is a schematic diagram showing an example of an embodiment according to the present invention.

【図2】従来のゴミ焼却設備における排水中のダイオキ
シン類処理設備の一例を示す図である。
FIG. 2 is a diagram showing an example of a facility for treating dioxins in wastewater in a conventional garbage incineration facility.

【符号の説明】[Explanation of symbols]

20 ダイオキシン類含有排水処理装置 21 ゴミ焼却設備 22 ゴミピット 23 焼却炉 24 エコノマイザ 25 減温塔 26 集じん機 27 煙突 28 集水槽 29 排水供給系統 29a、29b、29c 分岐排水供給系統 30 供給装置 31 吹込み装置 32 灰溶融装置 33 灰沈殿槽 34 飛灰処理装置 35 切替装置 M、M1、M2、M3、M4 ダイオキシン類含有排水
系統 N 排水戻し手段
Reference Signs List 20 Dioxin-containing wastewater treatment apparatus 21 Garbage incineration equipment 22 Garbage pit 23 Incinerator 24 Economizer 25 Cooling tower 26 Dust collector 27 Chimney 28 Water collecting tank 29 Drainage supply system 29a, 29b, 29c Branch drainage supply system 30 Supply device 31 Injection Device 32 Ash melting device 33 Ash precipitation tank 34 Fly ash treatment device 35 Switching device M, M1, M2, M3, M4 Dioxin-containing wastewater system N Wastewater return means

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C07B 35/06 F23G 7/04 601Z 37/06 B01D 53/34 134E C07D 319/24 B09B 3/00 303J F23G 7/04 601 ZAB (72)発明者 伊藤 純一 東京都千代田区丸の内一丁目1番2号 日 本鋼管株式会社内 Fターム(参考) 3B201 AA46 BB21 BB82 BB88 BC00 CC00 4D002 AA21 AC04 BA05 BA12 BA13 CA01 EA02 4D004 AA46 AB07 CA24 CC03 DA02 DA06 4D034 AA26 CA04 CA13 CA19 DA05 4H006 AA05 AC13 AC26 BD41 BD52 BD84 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) C07B 35/06 F23G 7/04 601Z 37/06 B01D 53/34 134E C07D 319/24 B09B 3/00 303J F23G 7/04 601 ZAB (72) Inventor Junichi Ito 1-2-1 Marunouchi, Chiyoda-ku, Tokyo F-term in Nihon Kokan Co., Ltd. (Reference) 3B201 AA46 BB21 BB82 BB88 BC00 CC00 4D002 AA21 AC04 BA05 BA12 BA13 CA01 EA02 4D004 AA46 AB07 CA24 CC03 DA02 DA06 4D034 AA26 CA04 CA13 CA19 DA05 4H006 AA05 AC13 AC26 BD41 BD52 BD84

Claims (8)

【特許請求の範囲】[Claims] 【請求項1】 廃棄物処理設備による廃棄物の燃焼処
理、排ガスの冷却処理、排ガス処理の工程からなる廃棄
物処理工程により廃棄物を処理する際に、該廃棄物処理
物と接触して及び/または接触した物体を洗浄して生じ
るダイオキシン類含有排水を集め、該ダイオキシン類含
有排水を前記処理工程に戻して処理し無害化することを
特徴とする廃棄物処理設備の排水中のダイオキシン類処
理方法。
When a waste is treated in a waste treatment process including a waste treatment process, a waste gas cooling process, and an exhaust gas treatment process by a waste treatment facility, the waste material is brought into contact with the waste treated material. And / or collecting dioxin-containing wastewater generated by washing a contacted object, returning the dioxin-containing wastewater to the above-mentioned treatment step, and treating and detoxifying the dioxin-containing wastewater. Method.
【請求項2】 ダイオキシン類含有排水を廃棄物に含有
させて燃焼処理工程で処理し、排ガス処理工程で無害化
することを特徴とする請求項1記載による廃棄物処理設
備の排水中のダイオキシン類処理方法。
2. The dioxins in wastewater of a waste treatment facility according to claim 1, wherein the wastewater containing dioxins is contained in the waste, treated in a combustion treatment step, and detoxified in an exhaust gas treatment step. Processing method.
【請求項3】 ダイオキシン類含有排水を燃焼処理工程
に設置された炉の内部に噴霧して該燃焼処理工程で処理
し、排ガス処理工程で無害化することを特徴とする請求
項1又は請求項2記載による廃棄物処理設備の排水中の
ダイオキシン類処理方法。
3. The method according to claim 1, wherein the wastewater containing dioxins is sprayed into a furnace installed in the combustion treatment step, treated in the combustion treatment step, and detoxified in the exhaust gas treatment step. 2. A method for treating dioxins in wastewater of a waste treatment facility according to item 2.
【請求項4】 ダイオキシン類含有排水を冷却処理工程
に設置された減温塔に戻して冷却処理工程で蒸発させ、
排ガス処理工程で無害化することを特徴とする請求項
1、請求項2または請求項3記載による廃棄物処理設備
の排水中のダイオキシン類処理方法。
4. The dioxin-containing wastewater is returned to a cooling tower provided in a cooling treatment step, and evaporated in the cooling treatment step.
4. The method for treating dioxins in wastewater of a waste treatment facility according to claim 1, wherein the detoxification is performed in an exhaust gas treatment step.
【請求項5】 廃棄物供給施設を有する廃棄物処理設備
の燃焼処理、冷却処理、排ガス処理の工程からなる廃棄
物処理工程で発生する排水中のダイオキシン類を処理す
る処理装置であって、前記廃棄物処理工程で発生するダ
イオキシン類含有排水を集めるダイオキシン類含有排水
系統と、集めた該排水を受け入れる集水槽と、該集水槽
から前記廃棄物処理工程に該排水を戻す排水戻し手段と
を組合わせて設置したことを特徴とする廃棄物処理設備
の排水中のダイオキシン類処理装置。
5. A treatment apparatus for treating dioxins in waste water generated in a waste treatment step including a combustion treatment, a cooling treatment, and an exhaust gas treatment in a waste treatment facility having a waste supply facility, A dioxin-containing drainage system for collecting dioxin-containing wastewater generated in the waste treatment process, a water collecting tank for receiving the collected wastewater, and a wastewater return means for returning the wastewater from the water collection tank to the waste treatment process are assembled. A device for treating dioxins in wastewater of a waste treatment facility, which is installed together.
【請求項6】 ダイオキシン類含有排水を廃棄物供給施
設に戻すための排水戻し手段を設置したことを特徴とす
る請求項5記載による廃棄物処理設備の排水中のダイオ
キシン類処理装置。
6. An apparatus for treating dioxins in wastewater of a waste treatment facility according to claim 5, further comprising means for returning wastewater containing dioxin-containing wastewater to a waste supply facility.
【請求項7】 ダイオキシン類含有排水を燃焼処理工程
に設置された炉の内部に戻す排水戻し手段を設置したこ
とを特徴とする請求項5又は請求項6記載による廃棄物
処理設備の排水中のダイオキシン類処理装置。
7. A wastewater treatment facility according to claim 5, further comprising a wastewater return means for returning the dioxin-containing wastewater to the inside of a furnace installed in the combustion treatment step. Dioxin processing equipment.
【請求項8】 ダイオキシン類含有排水を冷却処理工程
に設置された減温塔に戻す排水戻し手段を設置したこと
を特徴とする請求項5、請求項6又は請求項7記載によ
る廃棄物処理設備の排水中のダイオキシン類処理装置。
8. A waste treatment facility according to claim 5, wherein waste water return means for returning dioxin-containing waste water to a cooling tower installed in a cooling treatment step is provided. For treating dioxins in wastewater.
JP2001110743A 2001-01-26 2001-04-10 Method for treating dioxins in wastewater from waste disposer and disposer therefor Pending JP2002292363A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
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Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
JP2001-17781 2001-01-26
JP2001017781 2001-01-26
JP2001110743A JP2002292363A (en) 2001-01-26 2001-04-10 Method for treating dioxins in wastewater from waste disposer and disposer therefor

Publications (1)

Publication Number Publication Date
JP2002292363A true JP2002292363A (en) 2002-10-08

Family

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Country Link
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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104084417A (en) * 2014-07-16 2014-10-08 浙江华川实业集团有限公司 Waste incineration and sewage treatment integrated process for paper mill
JP2016190223A (en) * 2015-03-31 2016-11-10 栗田工業株式会社 Wastewater treatment method for incineration plant
JP2018079445A (en) * 2016-11-18 2018-05-24 川崎重工業株式会社 Waste water treatment device

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104084417A (en) * 2014-07-16 2014-10-08 浙江华川实业集团有限公司 Waste incineration and sewage treatment integrated process for paper mill
CN104084417B (en) * 2014-07-16 2016-04-06 浙江华川实业集团有限公司 A kind of paper mill waste incineration and sewage disposal integral process
JP2016190223A (en) * 2015-03-31 2016-11-10 栗田工業株式会社 Wastewater treatment method for incineration plant
JP2018079445A (en) * 2016-11-18 2018-05-24 川崎重工業株式会社 Waste water treatment device

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