JP2003334592A - Sewage treatment apparatus - Google Patents

Sewage treatment apparatus

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Publication number
JP2003334592A
JP2003334592A JP2002144776A JP2002144776A JP2003334592A JP 2003334592 A JP2003334592 A JP 2003334592A JP 2002144776 A JP2002144776 A JP 2002144776A JP 2002144776 A JP2002144776 A JP 2002144776A JP 2003334592 A JP2003334592 A JP 2003334592A
Authority
JP
Japan
Prior art keywords
tank
sludge
liquid
nitrification
reaction
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
JP2002144776A
Other languages
Japanese (ja)
Inventor
Hiroshi Kishino
宏 岸野
Satoshi Oketani
智 桶谷
Hideki Iwabe
秀樹 岩部
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.)
Kubota Corp
Original Assignee
Kubota 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 Kubota Corp filed Critical Kubota Corp
Priority to JP2002144776A priority Critical patent/JP2003334592A/en
Publication of JP2003334592A publication Critical patent/JP2003334592A/en
Pending legal-status Critical Current

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  • Separation Using Semi-Permeable Membranes (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Treatment Of Sludge (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To efficiently reduce the volume of sludge in a sedimentation tank into which sewage flows in. <P>SOLUTION: The sedimentation tank 1 into which sewage flows in, a digestion tank 10 for digesting sludge 9 drawn out of the sedimentation tank and a reaction tank 3 for biologically treating the supernatant liquid 2 in the sedimentation tank and the liquid 12 taken out of the digestion tank 10 are provided. An immersion type membrane filter device 5 for filtering the treated liquid 4 of the reaction tank 3 and an excess sludge draw-out passage 7 are provided to the reaction tank. <P>COPYRIGHT: (C)2004,JPO

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、下水処理装置に関
する。
TECHNICAL FIELD The present invention relates to a sewage treatment apparatus.

【0002】[0002]

【従来の技術】従来の下水処理装置として、例えば図2
に示すように、下水が流入する最初沈殿槽1と、最初沈
殿槽1の上澄液2を生物処理する主反応槽30と、主反
応槽30の処理水が流入する最終沈殿槽31とを設け、
最終沈殿槽31から引き抜いた余剰汚泥の一部を主反応
槽30に戻すとともに、残りの余剰汚泥を廃棄設備8に
送って廃棄処理し、最終沈殿槽31の上澄液を減菌設備
6に送って放流するように構成したものがある。
2. Description of the Related Art As a conventional sewage treatment apparatus, for example, FIG.
As shown in FIG. 1, a first settling tank 1 into which sewage flows, a main reaction tank 30 for biologically treating the supernatant 2 of the first settling tank 1, and a final settling tank 31 into which treated water of the main reaction tank 30 flows. Provided,
Part of the excess sludge extracted from the final settling tank 31 is returned to the main reaction tank 30, and the remaining excess sludge is sent to the disposal facility 8 for disposal, and the supernatant of the final settling tank 31 is sent to the sterilization facility 6. Some are configured to be sent and released.

【0003】そして、この下水処理装置では、最初沈殿
槽1で沈殿した汚泥(初沈汚泥) 9の減容化を図るため
に、最初沈殿槽1から引き抜いた汚泥中の有機物を生物
処理する副反応槽32と、副反応槽32の処理液33を
濾過する浸漬型膜濾過装置5とを設けて、膜濾過装置5
で濾過した濾液を、最初沈殿槽1の上澄液2と共に、主
反応槽30で生物処理し、副反応槽32から引き抜いた
発酵汚泥を最終沈殿槽31から引き抜いた余剰汚泥と共
に、廃棄処理するように構成している。
In this sewage treatment apparatus, in order to reduce the volume of the sludge (first settling sludge) 9 first settled in the settling tank 1, a sub-process for biologically treating organic matter in the sludge first drawn out of the settling tank 1. The membrane tank 5 is provided with the reaction tank 32 and the submerged membrane filter 5 for filtering the treatment liquid 33 in the side reaction tank 32.
The filtrate filtered in step 1 is biologically treated in the main reaction tank 30 together with the supernatant 2 of the precipitation tank 1, and the fermented sludge drawn from the sub-reaction tank 32 is discarded together with the excess sludge drawn from the final precipitation tank 31. Is configured as follows.

【0004】[0004]

【発明が解決しようとする課題】上記下水処理装置は、
最初沈殿槽1から引き抜いた汚泥9を副反応槽32にお
いて生物処理するものの、その副反応槽32内の処理液
33を膜濾過装置5で濾過して、濾液のみを主反応槽3
0において、再度、生物処理しており、副反応槽32か
ら引き抜いた発酵汚泥を最終沈殿槽31から引き抜いた
余剰汚泥と共に廃棄処理しているので、最初沈殿槽1で
沈殿させた汚泥9を効率良く減容化できない欠点があ
る。
The sewage treatment apparatus described above is
Although the sludge 9 extracted from the settling tank 1 is biologically treated in the sub-reaction tank 32, the treatment liquid 33 in the sub-reaction tank 32 is filtered by the membrane filtration device 5, and only the filtrate is filtered into the main reaction tank 3
At 0, the biological treatment is carried out again, and the fermented sludge drawn from the side reaction tank 32 is discarded together with the excess sludge drawn from the final settling tank 31. There is a drawback that the volume cannot be reduced well.

【0005】本発明は上記実情に鑑みてなされたもので
あって、下水が流入する沈殿槽の汚泥を効率良く減容化
できるようにすることを目的とする。
The present invention has been made in view of the above circumstances, and it is an object of the present invention to efficiently reduce the volume of sludge in a sedimentation tank into which sewage flows.

【0006】[0006]

【課題を解決するための手段】請求項1記載の発明の特
徴構成は、下水が流入する沈殿槽と、その沈殿槽から引
き抜いた汚泥を消化する消化槽と、前記沈殿槽の上澄液
と前記消化槽から取り出される槽内液とを生物処理する
反応槽とを設け、前記反応槽に、その処理液を濾過する
浸漬型膜濾過装置と、余剰汚泥の引き抜き路とを設けて
ある点にある。
According to a first aspect of the present invention, there is provided a settling tank into which sewage flows, a digestion tank for digesting sludge drawn from the settling tank, and a supernatant of the settling tank. A reaction tank for biologically treating the solution in the tank taken out from the digestion tank is provided, and the reaction tank is provided with a submerged membrane filtration device for filtering the treatment solution and a path for extracting excess sludge. is there.

【0007】〔作用及び効果〕下水が流入する沈殿槽か
ら引き抜いた汚泥を、消化槽において消化することによ
り、より高濃度の汚泥水として効率良く消化処理でき、
しかも、反応槽で生物処理し易い分子量がより小さい生
物分解性の高い有機物に分解し、その生物処理し易くな
った槽内液を固液分離せずに取り出して、沈殿槽の上澄
液と共に、反応槽に供給することによって、より微生物
にとって栄養分の多い状態で効率良く生物処理でき、そ
の処理液を浸漬型膜濾過装置で濾過すると共に、余剰汚
泥を引き抜き路を通して反応槽から引き抜けるようにし
てあるので、より高度な活性汚泥処理ができ、その結
果、下水が流入する沈殿槽の汚泥を反応槽における生物
処理によって効率良く減容化できる。
[Operation and effect] By digesting the sludge drawn from the settling tank into which the sewage flows, in the digestion tank, it is possible to efficiently perform digestion treatment as sludge water having a higher concentration,
Moreover, it is decomposed into highly biodegradable organic substances with smaller molecular weight that are easily bioprocessed in the reaction tank, and the in-tank liquid that has become easier to bioprocess is taken out without solid-liquid separation, together with the supernatant of the precipitation tank. By supplying it to the reaction tank, biological treatment can be efficiently carried out in a state where the microorganisms are rich in nutrients, and the treated liquid is filtered by the immersion type membrane filtration device, and excess sludge can be withdrawn from the reaction tank through the withdrawal path. Therefore, more advanced activated sludge treatment can be performed, and as a result, sludge in the sedimentation tank into which sewage flows can be efficiently reduced in volume by biological treatment in the reaction tank.

【0008】請求項2記載の発明の特徴構成は、前記反
応槽を脱窒槽と硝化槽とで構成して、前記沈殿槽の上澄
液と前記消化槽から取り出される槽内液とを、前記脱窒
槽を通して前記硝化槽に流入させるとともに、前記硝化
槽内の処理液の一部を前記脱窒槽に戻して循環させるよ
うに構成し、前記硝化槽に、前記膜濾過装置と前記引き
抜き路を設けてある点にある。
According to a second aspect of the present invention, the reaction tank is composed of a denitrification tank and a nitrification tank, and the supernatant liquid of the precipitation tank and the tank liquid taken out from the digestion tank are The nitrification tank is made to flow through the denitrification tank, and a part of the treatment liquid in the nitrification tank is returned to the denitrification tank for circulation, and the nitrification tank is provided with the membrane filtration device and the extraction path. There is a point.

【0009】〔作用及び効果〕反応槽を脱窒槽と硝化槽
とで構成して、沈殿槽の上澄液と消化槽から取り出され
る槽内液とを、脱窒槽と硝化槽とに亘って循環させて硝
化脱窒処理を行うので、下水が流入する沈殿槽の汚泥を
反応槽において最終的に効率良く分解して減容化できる
とともに、硝化槽内の処理液を浸漬型膜濾過装置で濾過
して、余剰汚泥を硝化槽から引き抜けるようにしてある
ので、硝化槽内の汚泥濃度が高くなって、活性汚泥処理
が可能となり、全体としてより小型の設備で、生物処理
ができるようになる。
[Operation and effect] The reaction tank is composed of a denitrification tank and a nitrification tank, and the supernatant liquid of the precipitation tank and the tank liquid taken out from the digestion tank are circulated between the denitrification tank and the nitrification tank. Since the nitrification denitrification process is performed by this method, the sludge in the sedimentation tank into which the sewage flows can be finally efficiently decomposed in the reaction tank to reduce the volume, and the treatment liquid in the nitrification tank is filtered by the immersion type membrane filtration device. Then, since the excess sludge is drawn out from the nitrification tank, the sludge concentration in the nitrification tank becomes high, the activated sludge treatment becomes possible, and the biological treatment can be carried out by a smaller equipment as a whole.

【0010】[0010]

【発明の実施の形態】以下に本発明の実施の形態を図面
に基づいて説明する。尚、図面において従来例と同一の
符号で表示した部分は、同一又は相当の部分を示してい
る。
BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of the present invention will be described below with reference to the drawings. In the drawings, the parts indicated by the same reference numerals as those in the conventional example indicate the same or corresponding parts.

【0011】図1は本発明による下水処理装置を示し、
下水が流入する最初沈殿槽1と、最初沈殿槽1の上澄液
2を生物処理する反応槽3と、反応槽3の処理液4を濾
過する浸漬型膜濾過装置5と、膜濾過装置5で濾過した
濾液を減菌する減菌槽6と、反応槽3から余剰汚泥を引
き抜く引き抜き路7とを設けて、最初沈殿槽1の上澄液
2に含まれる有機物を反応槽3で分解除去し、膜濾過装
置5で濾過した濾液を減菌槽6で減菌して放流するとと
もに、反応槽3から引き抜いた余剰汚泥を廃棄設備8に
送って廃棄処理するようにしてある。
FIG. 1 shows a sewage treatment apparatus according to the present invention,
A first settling tank 1 into which sewage flows, a reaction tank 3 for biologically treating a supernatant 2 of the first settling tank 1, an immersion type membrane filtration device 5 for filtering a treatment liquid 4 in the reaction tank 3, and a membrane filtration device 5 A sterilization tank 6 for sterilizing the filtrate filtered in step 1 and a withdrawal path 7 for withdrawing excess sludge from the reaction tank 3 are provided, and organic substances contained in the supernatant 2 of the precipitation tank 1 are first decomposed and removed in the reaction tank 3. Then, the filtrate filtered by the membrane filtration device 5 is sterilized in the sterilization tank 6 and discharged, and the excess sludge extracted from the reaction tank 3 is sent to the disposal facility 8 for disposal.

【0012】そして、最初沈殿槽1において沈降分離し
た初沈汚泥9を引き抜いて消化処理する消化槽10を設
けて、その消化槽10で初沈汚泥9を撹拌装置11で攪
拌しながら、反応槽3において生物処理し易い分子量が
小さい有機物に分解し、その分解液(槽内液) 12を取
り出して、最初沈殿槽1の上澄液2と共に反応槽3で生
物処理して、初沈汚泥9を減容化できるようにしてあ
る。
Then, a digestion tank 10 for extracting and digesting the first settled sludge 9 that has been settled and separated in the first settling tank 1 is provided, and while stirring the first settled sludge 9 in the digestion tank 10 with a stirring device 11, a reaction tank 3 is decomposed into an organic substance having a small molecular weight which is easily bioprocessed, and the decomposed liquid (tank liquid) 12 is taken out and biologically treated in the reaction tank 3 together with the supernatant liquid 2 of the first settling tank 1, and the first settling sludge 9 The volume can be reduced.

【0013】前記消化槽10は、初沈汚泥9を、好気的
な雰囲気下での微生物による消化作用により、反応槽3
中の微生物による分解作用を受け易い比較的低分子量の
有機物に分解できるようにしてある。
The digestion tank 10 has a reaction tank 3 in which the initial sludge 9 is digested by microorganisms in an aerobic atmosphere.
It is designed so that it can be decomposed into relatively low molecular weight organic substances that are easily decomposed by microorganisms inside.

【0014】前記反応槽3は、脱窒槽13と硝化槽14
とを設けて、最初沈殿槽1の上澄液2と消化槽10から
取り出す槽内液12とを、脱窒槽13を通して硝化槽1
4に流入させるとともに、硝化槽14内の処理液4の一
部を脱窒槽13に戻して循環させるように構成してあ
り、硝化槽14に膜濾過装置5を浸漬設置し、硝化槽1
4の底部に余剰汚泥の引き抜き路7を設けてある。
The reaction tank 3 includes a denitrification tank 13 and a nitrification tank 14.
First, the supernatant liquid 2 of the precipitation tank 1 and the in-tank liquid 12 taken out from the digestion tank 10 are passed through the denitrification tank 13 and the nitrification tank 1
4 and a part of the treatment liquid 4 in the nitrification tank 14 is returned to the denitrification tank 13 and circulated, and the membrane filtration device 5 is immersed in the nitrification tank 14 for installation.
A drainage path 7 for excess sludge is provided at the bottom of No. 4.

【0015】前記膜濾過装置5は、ケース15の内部に
複数の平板状膜カートリッジ16を装着するともに、そ
の下部に散気装置17を設けて、ブロア18から供給す
る空気を散気装置17から散気して、硝化槽14内の処
理液4を酸素富裕環境下で好気性処理するとともに、吸
引ポンプ19の駆動で硝化槽14内の処理液4を吸引濾
過して、濾過水を減菌槽6に取り出すようにしてある。
In the membrane filtration device 5, a plurality of flat plate-shaped membrane cartridges 16 are mounted in the case 15, and an air diffuser 17 is provided in the lower part thereof so that air supplied from a blower 18 is supplied from the air diffuser 17 to the air blower 18. Aeration is performed to aerobically process the treatment liquid 4 in the nitrification tank 14 in an oxygen-rich environment, and the suction pump 19 is driven to suction-filter the treatment liquid 4 in the nitrification tank 14 to sterilize the filtered water. It is taken out to the tank 6.

【0016】前記散気装置17から散気する空気は、エ
アリフト作用によって処理液4に気液混相の上向流を生
起させ、この上向流が掃流として膜カートリッジ16の
膜面に作用して、膜面への汚泥の付着を抑制できるよう
にしてある。
The air diffused from the air diffuser 17 causes an upward flow of a gas-liquid mixed phase in the treatment liquid 4 by an air lift action, and this upward flow acts as a sweep flow on the membrane surface of the membrane cartridge 16. In this way, the adhesion of sludge to the membrane surface can be suppressed.

【0017】前記引き抜き路7は、余剰汚泥を汚泥ポン
プ20で引き抜いて、汚泥脱水機や汚泥乾燥機並びに焼
却装置などを備えた廃棄設備8に送り出すようにしてあ
る。
The withdrawal path 7 is configured to withdraw excess sludge with a sludge pump 20 and send it to a disposal facility 8 equipped with a sludge dehydrator, a sludge dryer, an incinerator, and the like.

【0018】〔その他の実施形態〕 1.本発明による下水処理装置は、沈殿槽から引き抜い
た汚泥を嫌気性環境下で消化する消化槽を設けてあって
も良い。 2.本発明による下水処理装置は、沈殿槽の上澄液と消
化槽から取り出す槽内液とを、硝化処理と脱窒処理とを
交互に行うようにした反応槽で生物処理するように構成
してあっても良い。
[Other Embodiments] 1. The sewage treatment apparatus according to the present invention may be provided with a digestion tank for digesting sludge drawn out from the settling tank in an anaerobic environment. 2. The sewage treatment apparatus according to the present invention is configured such that the supernatant liquid of the precipitation tank and the in-tank liquid taken out from the digestion tank are biologically treated in a reaction tank configured to alternately perform nitrification treatment and denitrification treatment. It may be.

【0019】[0019]

【実施例】本願発明による下水処理装置で処理した場合
の汚泥発生量と、図2に示した従来の下水処理装置で処
理した場合の汚泥発生量とを比較した。汚泥発生量(k
g) は、通常、流入下水中のSS量(kg) 当たりで表
され、従来の下水処理では、方式別の汚泥発生量とし
て、[表1]のような数値が得られている(下水道施設
計画・設計指針と解説:日本下水道協会) 。
EXAMPLE The amount of sludge generated when treated by the sewage treatment apparatus according to the present invention was compared with the amount of sludge generated when treated by the conventional sewage treatment apparatus shown in FIG. Sludge generation amount (k
g) is usually expressed per SS amount (kg) in the inflowing sewage, and in the conventional sewage treatment, the value as shown in [Table 1] is obtained as the amount of sludge generated by each method (sewerage facilities (Planning and design guidelines and commentary: Japan Sewer Association).

【表1】 [Table 1]

【0020】図2に示した従来の下水処理装置で処理し
た場合は、標準活性汚泥法と同程度の汚泥発生量が報告
されており、汚泥の減容に対して有効な方法であるとは
言えない。
When treated with the conventional sewage treatment apparatus shown in FIG. 2, it has been reported that the amount of sludge generated is similar to that of the standard activated sludge method, and it is an effective method for reducing the volume of sludge. I can not say.

【0021】そこで、本願発明による下水処理装置を使
用して、実験水量50m3 /日,反応槽滞留時間6時
間,消化槽滞留時間48時間の実験条件で、消化槽を好
気条件下で運転した場合、汚泥発生量は0.5(汚泥発
生量(kg) /SS量(kg))であり、標準活性汚泥法
に比べて約50%程度の汚泥減容率が得られている。
Therefore, using the sewage treatment apparatus according to the present invention, the digestion tank is operated under aerobic conditions under the experimental conditions of an experimental water amount of 50 m 3 / day, a reaction tank residence time of 6 hours, and a digestion tank residence time of 48 hours. In this case, the sludge generation rate was 0.5 (sludge generation rate (kg) / SS amount (kg)), and a sludge volume reduction rate of about 50% was obtained compared to the standard activated sludge method.

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

【図1】下水処理装置の説明図FIG. 1 is an explanatory diagram of a sewage treatment device.

【図2】従来技術の説明図FIG. 2 is an explanatory diagram of a conventional technique.

【符号の説明】[Explanation of symbols]

1 沈殿槽 2 上澄液 3 反応槽 4 処理液 5 膜濾過装置 7 引き抜き路 9 汚泥 10 消化槽 12 槽内液 13 脱窒槽 14 硝化槽 1 settling tank 2 supernatant 3 reaction tanks 4 processing liquid 5 Membrane filtration device 7 Withdrawal path 9 sludge 10 digestive tank 12 Tank liquid 13 denitrification tank 14 Nitrification tank

───────────────────────────────────────────────────── フロントページの続き (72)発明者 岩部 秀樹 東京都中央区日本橋室町3丁目1番3号 株式会社クボタ東京本社内 Fターム(参考) 4D006 GA07 HA41 JA31Z JA71 KA01 KA31 KA44 KB22 KB23 4D040 BB54 BB57 BB65 4D059 AA04 AA05 BA01 BB01 BD00 BE00 BJ00 CA28    ─────────────────────────────────────────────────── ─── Continued front page    (72) Inventor Hideki Iwabe             3 1-3 Nihombashi Muromachi, Chuo-ku, Tokyo             Kubota Tokyo Head Office F-term (reference) 4D006 GA07 HA41 JA31Z JA71                       KA01 KA31 KA44 KB22 KB23                 4D040 BB54 BB57 BB65                 4D059 AA04 AA05 BA01 BB01 BD00                       BE00 BJ00 CA28

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 下水が流入する沈殿槽と、その沈殿槽か
ら引き抜いた汚泥を消化する消化槽と、前記沈殿槽の上
澄液と前記消化槽から取り出される槽内液とを生物処理
する反応槽とを設け、 前記反応槽に、その処理液を濾過する浸漬型膜濾過装置
と、余剰汚泥の引き抜き路とを設けてある下水処理装
置。
1. A reaction for biologically treating a sedimentation tank into which sewage flows, a digestion tank for digesting sludge drawn from the sedimentation tank, a supernatant of the sedimentation tank, and an in-tank liquid removed from the digestion tank. A sewage treatment apparatus, which is provided with a tank, and wherein the reaction tank is provided with an immersion type membrane filtration device for filtering the treatment liquid and a withdrawal path for excess sludge.
【請求項2】 前記反応槽を脱窒槽と硝化槽とで構成し
て、前記沈殿槽の上澄液と前記消化槽から取り出される
槽内液とを、前記脱窒槽を通して前記硝化槽に流入させ
るとともに、前記硝化槽内の処理液の一部を前記脱窒槽
に戻して循環させるように構成し、 前記硝化槽に、前記膜濾過装置と前記引き抜き路を設け
てある請求項1記載の下水処理装置。
2. The reaction tank is composed of a denitrification tank and a nitrification tank, and the supernatant liquid of the precipitation tank and the in-tank liquid taken out from the digestion tank are caused to flow into the nitrification tank through the denitrification tank. At the same time, a part of the treatment liquid in the nitrification tank is returned to the denitrification tank for circulation, and the nitrification tank is provided with the membrane filtration device and the extraction passage. apparatus.
JP2002144776A 2002-05-20 2002-05-20 Sewage treatment apparatus Pending JP2003334592A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007283249A (en) * 2006-04-19 2007-11-01 Takasago Thermal Eng Co Ltd Organic wastewater treatment system
KR100853077B1 (en) 2008-04-08 2008-08-19 효성에바라엔지니어링 주식회사 Submerged poly tetrafluoro ethylene membrane bioreactor and advanced wastewater treatment process using the same
CN102020400A (en) * 2010-12-22 2011-04-20 南京中电联环保股份有限公司 Medium and small town centralized domestic sewage treatment method and device

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007283249A (en) * 2006-04-19 2007-11-01 Takasago Thermal Eng Co Ltd Organic wastewater treatment system
KR100853077B1 (en) 2008-04-08 2008-08-19 효성에바라엔지니어링 주식회사 Submerged poly tetrafluoro ethylene membrane bioreactor and advanced wastewater treatment process using the same
CN102020400A (en) * 2010-12-22 2011-04-20 南京中电联环保股份有限公司 Medium and small town centralized domestic sewage treatment method and device
CN102020400B (en) * 2010-12-22 2013-10-16 南京中电环保股份有限公司 Medium and small town centralized domestic sewage treatment method and device

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