JPH11128966A - Apparatus for treating high concentration waste water - Google Patents

Apparatus for treating high concentration waste water

Info

Publication number
JPH11128966A
JPH11128966A JP29144697A JP29144697A JPH11128966A JP H11128966 A JPH11128966 A JP H11128966A JP 29144697 A JP29144697 A JP 29144697A JP 29144697 A JP29144697 A JP 29144697A JP H11128966 A JPH11128966 A JP H11128966A
Authority
JP
Japan
Prior art keywords
filter medium
water
treatment tank
charged
treatment
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.)
Granted
Application number
JP29144697A
Other languages
Japanese (ja)
Other versions
JP3468399B2 (en
Inventor
Susumu Mori
享 森
Shigeyuki Fujimura
重幸 藤村
Osamu Yamashita
修 山下
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.)
Ishigaki Co Ltd
Original Assignee
Ishigaki Co 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 Ishigaki Co Ltd filed Critical Ishigaki Co Ltd
Priority to JP29144697A priority Critical patent/JP3468399B2/en
Publication of JPH11128966A publication Critical patent/JPH11128966A/en
Application granted granted Critical
Publication of JP3468399B2 publication Critical patent/JP3468399B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Classifications

    • 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Biological Treatment Of Waste Water (AREA)
  • Filtration Of Liquid (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide an apparatus in which BOD and SS can be remarkably decreased, in an apparatus for treating high concn. waste water. SOLUTION: A filter medium layer is formed by charging a filter medium 2 comprising a synthetic resin fibrous material in a treating tank 1, and an air pipe for aerating the filter medium and an air pipe for agitating the filter medium are provided below the filter medium layer, and a feeding pipe for a raw water and a removing pipe for treated water are respectively provided at the bottom part and the top part of the treating tank 1, and in addition, the removing pipe for the treated water and the feeding pipe for the raw water are connected with each other through an on-off valve. As the fibrous filter medium 2 is used, it is easily cleaned while contact area with waste water is large and efficient treatment can be done and it is possible to form a consolidated precise filter medium layer by circulating the treated water.

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】この発明は、下水等の有機性
汚水の処理装置に関する。
The present invention relates to an apparatus for treating organic sewage such as sewage.

【0002】[0002]

【従来の技術】従来、有機性汚水の処理装置は公知であ
る。比重が1.0以上のアンスラサイト、セラミック等
のろ材を用いた処理装置はよく知られている。また、比
重が1に近い浮上性のろ材を用いた処理装置は多数あ
り、これらの装置に用いられているろ材の形状および寸
法は、直方体で10〜30mmの正方形に5〜25mm
の厚さをもったもの等が知られている。これらのろ材寸
法は、アンスラサイトやセラミック等のろ材に比べ大き
い。これは、ろ層の目詰まり防止のためと考えられる
が、ろ材寸法が大きすぎると、ろ過抵抗が均一ではな
く、抵抗の低い部分に被処理水が多く流れる、いわゆる
偏流現象が生じ、処理に支障を来たす結果となる。さら
に、合成繊維を束ねたり、繭状に成形した繊維ろ材と称
するろ材も多数ある。これらは、一種類の繊維からでき
たものが多く、ろ過抵抗が上昇したり、水抜き時に重力
により強く押し付けられ、変形することがある。また、
上向流式ろ過は、原水と空気が同一方向に流れるのでS
Sが処理水にもれやすい欠点がある。
2. Description of the Related Art Conventionally, apparatuses for treating organic wastewater are known. Processing apparatuses using a filter medium having a specific gravity of 1.0 or more, such as anthracite or ceramic, are well known. In addition, there are a large number of processing apparatuses using a buoyant filter medium having a specific gravity close to 1, and the shape and dimensions of the filter medium used in these apparatuses are 5 to 25 mm in a rectangular parallelepiped 10 to 30 mm square.
Are known. These filter media dimensions are larger than filter media such as anthracite and ceramic. This is considered to prevent clogging of the filter layer.However, if the filter medium size is too large, the filtration resistance is not uniform, and a large amount of water to be treated flows to a low resistance portion, so-called a drift phenomenon occurs, and the treatment is difficult. This results in trouble. Furthermore, there are many filter media called fiber filter media in which synthetic fibers are bundled or formed into a cocoon shape. Many of these are made of one type of fiber, which may cause an increase in filtration resistance or deformation due to being strongly pressed by gravity during drainage. Also,
In the upward flow filtration, raw water and air flow in the same direction,
There is a disadvantage that S easily leaks into the treated water.

【0003】[0003]

【発明が解決しようとする課題】しかしながら、比重が
1に近い浮上性のろ材を用いた高負荷処理装置では、ろ
過速度が小さいため、ろ材の圧密度が十分でなく、層内
を上昇する空気と共にSSが処理水に抜け出ることがあ
る。また比重の大きいアンスラサイトやセラミックろ
材、あるいは比重が極端に小さい発泡性のろ材等では、
空隙率が小さくSSによる目詰まりが短時間で生じ、洗
浄頻度が高くなるし、洗浄に大きな動力を必要とする。
さらに、寸法の大きいろ材では偏流現象が生じ、処理に
支障を来たす。
However, in a high-load processing apparatus using a buoyant filter medium having a specific gravity close to 1, the filtering speed is low, so that the pressure density of the filter medium is not sufficient, and air rising in the layer is not sufficient. At the same time, SS may escape into the treated water. In the case of anthracite or ceramic filter media with a large specific gravity, or foamable filter media with an extremely small specific gravity,
Porosity is small, clogging by SS occurs in a short time, cleaning frequency increases, and large power is required for cleaning.
Furthermore, a large-sized filter medium causes a drift phenomenon, which hinders processing.

【0004】[0004]

【課題を解決するための手段】この発明は、ろ材に工夫
をするとともに、ろ材層高と水層高との比率を適切にす
ること、およびろ過水の一部を循環することによって微
細なSSまでも捕捉しながら、目詰まりし難くかつ逆洗
が容易なろ材層を形成したものである。すなわち、ろ材
として素材が芯をポリプロピレン、鞘をポリエチレンと
した熱融着性複合繊維で繊度が18〜65デニールであ
る第1フィラメントと、素材がポリプロピレン繊維で繊
度が3〜10デニールである第2フィラメントと、素材
が芯をポリプロピレン、鞘をポリエチレンとした熱融着
性複合繊維で繊度が1.5〜6デニールである第3フィ
ラメントを混綿したウェッブをニードルパンチング法に
より布形化し、両面のウェッブ起毛状態を平滑化するこ
となく加熱処理し、前記ウェッブの重量が200〜80
0g/平方メートル、厚みが2〜8mmの布形化板状体
を製作し、この布形化板状体を3〜5mm角に裁断した
ものをろ材として用いたものである。また、ろ材層高と
水層高との比率を65:35〜50:50とすること
で、ろ材の洗浄を容易にし、さらに、ろ材の圧密不足に
よって空気と共にSSが処理水に抜け出る欠点を、処理
水を循環することで圧密度を高くして解決したものであ
る。
SUMMARY OF THE INVENTION The present invention provides fine filter media by adjusting the ratio of filter media layer height to water layer height and circulating a part of filtered water. A filter medium layer is formed that is hardly clogged and easily backwashed while catching up. That is, a first filament having a fineness of 18 to 65 denier which is a heat-fusible conjugate fiber having a core of polypropylene and a sheath of polyethylene as a filter medium, and a second filament having a polypropylene fiber and a fineness of 3 to 10 denier. A web formed by blending a filament and a third filament having a fineness of 1.5 to 6 denier with a heat-fusible conjugate fiber having a core of polypropylene and a sheath of polyethylene is needle-punched into a cloth, and the web on both sides is formed. A heat treatment is performed without smoothing the raised state, and the weight of the web is 200 to 80.
A cloth-shaped plate having a thickness of 0 to 8 g / m 2 and a thickness of 2 to 8 mm was produced, and the cloth-shaped plate was cut into 3 to 5 mm squares and used as a filter medium. In addition, by setting the ratio of the height of the filter medium layer to the height of the water layer to 65:35 to 50:50, the filter medium can be easily washed. This was solved by increasing the pressure density by circulating the treated water.

【0005】[0005]

【発明の実施の形態】上記布形化板状体ろ材は、不織布
であるため空隙率が大きく、微生物の付着に優れてい
る。このため、ろ層中の微生物量を大きく保つことがで
きる。また、ろ過圧力や水抜き時の重力による押しつぶ
れを防止するため、太さの異なる3種類のフィラメント
を用いている。上記布形化板状体ろ材は、密に詰まって
いるのに空隙率が大きいので、目詰まりによる圧力損失
は小さく、ろ過時間が長い。洗浄は、ろ材層高:水層高
の比を65:35〜50:50とすることで、下方から
の散気で容易に流動し、捕捉されたSSや余剰汚泥を分
離することができる。この時の空気量はアンスラサイト
やセラミックろ材の装置に比べ、少なくてすむ。また、
上向流式の欠点であるSS漏れについて、処理水を循環
することで解決し、従来より低いSSの処理水が得られ
る。さらに、循環することにより、酸素を十分に溶解し
た処理水を原水に混合するため、曝気空気量が従来装置
より少なくてよい。以下、この発明に係るろ材を用いた
汚水処理装置を図面に基づいて説明する。
BEST MODE FOR CARRYING OUT THE INVENTION The above-mentioned cloth-shaped plate-shaped filter medium is a non-woven fabric, so that it has a high porosity and is excellent in adhering microorganisms. Therefore, the amount of microorganisms in the filter layer can be kept large. In addition, three types of filaments having different thicknesses are used in order to prevent crushing due to gravity at the time of filtration pressure or drainage. The cloth-shaped plate-shaped filter medium is densely packed but has a high porosity, so that pressure loss due to clogging is small and filtration time is long. In the washing, by setting the ratio of the filter medium layer height to the water layer height to 65:35 to 50:50, it is easy to flow by diffused air from below, and the trapped SS and excess sludge can be separated. At this time, the amount of air is smaller than that of a device using anthracite or ceramic filter media. Also,
The leakage of SS, which is a drawback of the upward flow type, is solved by circulating the treated water, and the treated water having a lower SS than before can be obtained. Furthermore, since the circulating process mixes the treated water in which oxygen is sufficiently dissolved into the raw water, the amount of aerated air may be smaller than that of the conventional device. Hereinafter, a sewage treatment apparatus using a filter medium according to the present invention will be described with reference to the drawings.

【0006】[0006]

【実施例】図1および図2は、この発明に係る処理装置
を示し、図1において、符号1はその下部を逆円錐状に
形成して沈殿部1aを設けた処理槽、2は処理槽1に装
入したろ材、3はろ材層内の下部に設けた曝気用エアノ
ズル、4はドラフトチューブ5の下部に設けたろ材攪拌
用エアノズルである。次に、符号6は原水の供給管であ
り、符号7は処理水の越流トラフ、8は処理水の取り出
し管、9は循環水の取り出し管、10は沈殿物の引抜き
管、11は曝気用のブロワ、12は洗浄用のブロワ、1
3は循環用のポンプ、14はろ材の係止網である。
1 and 2 show a processing apparatus according to the present invention. In FIG. 1, reference numeral 1 denotes a processing tank having a lower portion formed in an inverted conical shape and a settling portion 1a provided, and 2 denotes a processing tank. Reference numeral 1 denotes a filter medium, reference numeral 3 denotes an air nozzle for aeration provided at a lower part in the filter medium layer, and reference numeral 4 denotes an air nozzle for agitating the filter provided at a lower part of the draft tube 5. Next, reference numeral 6 denotes a raw water supply pipe, reference numeral 7 denotes a treatment water overflow trough, reference numeral 8 denotes a treatment water extraction pipe, reference numeral 9 denotes a circulating water extraction pipe, reference numeral 10 denotes a sediment withdrawal pipe, and reference numeral 11 denotes aeration. 12 is a blower for washing, 12 is a blower for washing,
Reference numeral 3 denotes a circulation pump, and reference numeral 14 denotes a mesh for holding a filter medium.

【0007】この発明に係る装置は、上述のように構成
してあり、原水は処理水の一部である循環水と混合され
て処理槽1に供給される。そして、ろ材層中を上昇して
微細な夾雑物が捕捉除去されると同時に、ろ材2に生息
する微生物に触れることによって、有機性汚濁物が分解
され、処理槽1の上部を通り越流トラフ7、さらに処理
水の取り出し管8を経て清澄水として取り出すことがで
きる。同時に処理水の一部は循環水の取り出し管9およ
び循環用のポンプ13を経て、原水と混合して、混合液
供給管6aを経て再び処理槽1に供給される。
The apparatus according to the present invention is configured as described above. Raw water is mixed with circulating water that is a part of the treated water and supplied to the treatment tank 1. At the same time, fine contaminants are trapped and removed in the filter medium layer, and at the same time, the organic pollutants are decomposed by contacting microorganisms inhabiting the filter medium 2, and the overflow trough passes through the upper part of the treatment tank 1. 7. Further, the treated water can be taken out as clarified water through a take-out pipe 8. At the same time, a part of the treated water is mixed with the raw water through the circulating water take-out pipe 9 and the circulating pump 13, and is again supplied to the treatment tank 1 through the mixed liquid supply pipe 6a.

【0008】一方、これと同時に曝気用ブロワ11を作
動させて、曝気用エアノズル3から散気することで、ろ
材2の表面および内部に保持された微生物を活性化する
ことができ、連続して供給される原水中の有機性汚濁物
を、連続して分解処理することができる。次に、このよ
うな運転をして、ろ材層が夾雑物および有機物質の分解
時に生じた汚泥等で目詰まりしたときは、原水の供給お
よび処理水の循環を停止して、処理水取り出し弁8aを
閉じ、処理槽1の底部の沈殿物を引抜き管10から抜き
取り、ついで、洗浄用ブロワ12を作動させて、ろ材攪
拌用エアノズル4から給気を行いドラフトチューブ5を
介してろ材を5〜10分攪拌する。その後、ろ材攪拌用
エアノズル4からの給気を続けながら、洗浄水を洗浄水
管15から循環用ポンプ13を介して、混合液供給管6
aから供給する。ろ材2から剥離した夾雑物や余剰汚泥
を含む排水は、処理槽1の上部、越流トラフ7、さらに
処理水の取り出し管8を経て排水管から5〜15分間槽
外へ排出される。この時間は原水性状やろ過時間によっ
て変わるものである。洗浄完了後は洗浄用ブロワ12を
停止すると共に、循環弁9aを開、洗浄水弁15aを閉
として洗浄水の供給を停止、約5分間循環のみを行う。
その後、原水の供給と曝気用ブロワ11の運転を開始し
てろ過を行い、10〜20分間処理水を排出し、その後
処理水取り出し弁8aを開とし、処理水の取り出し管8
を経て清澄水として取り出す。
On the other hand, by simultaneously operating the aeration blower 11 and diffusing air from the aeration air nozzle 3, the microorganisms retained on the surface and inside of the filter medium 2 can be activated. The organic pollutants in the supplied raw water can be continuously decomposed. Next, when the filter medium layer is clogged with sludge generated at the time of decomposition of impurities and organic substances by such an operation, supply of raw water and circulation of the treated water are stopped, and a treated water take-off valve is provided. 8a is closed, the sediment at the bottom of the treatment tank 1 is pulled out from the drawing pipe 10, and then the cleaning blower 12 is operated to supply air from the air nozzle 4 for stirring the filter medium and to remove the filter medium 5 to 5 through the draft tube 5. Stir for 10 minutes. Thereafter, the washing water is supplied from the washing water pipe 15 through the circulation pump 13 to the mixed liquid supply pipe 6 while the air supply from the filter medium stirring air nozzle 4 is continued.
Supply from a. Drainage containing impurities and excess sludge separated from the filter medium 2 is discharged from the drainage pipe to the outside of the tank through the upper part of the treatment tank 1, the overflow trough 7, and the treated water discharge pipe 8 for 5 to 15 minutes. This time varies depending on the raw water condition and the filtration time. After the completion of the washing, the washing blower 12 is stopped, the circulation valve 9a is opened, and the washing water valve 15a is closed to stop the supply of the washing water, and only the circulation is performed for about 5 minutes.
Thereafter, the supply of raw water and the operation of the aeration blower 11 are started to perform filtration, the treated water is discharged for 10 to 20 minutes, and then the treated water take-out valve 8a is opened, and the treated water take-out pipe 8 is opened.
And remove it as clear water.

【0009】図2は図1のものに比較してドラフトチュ
ーブ5のない処理装置であって、ろ材洗浄をろ材層下方
の一部に設置した、ろ材攪拌用エアノズル4からの給気
により、ろ材の攪拌を行うもので、その他は図1の場合
と同じである。
FIG. 2 shows a processing apparatus without a draft tube 5 as compared with the processing apparatus shown in FIG. 1, and the filter medium is washed by a filter medium stirring air nozzle 4 installed at a part below the filter medium layer. The other components are the same as those in FIG.

【0010】表−1および表−2は、上述のようにこの
発明に係る処理装置を用いて試験処理をした場合の装置
の処理性能および曝気空気量とBODの関連を示すもの
である。表1に示すように、原水に比較して処理水のB
ODおよびSSは大巾に低減されており、表2に示すよ
うに、使用する曝気空気量も大巾に低減されている。
Tables 1 and 2 show the relationship between the processing performance of the apparatus and the BOD and the aeration air amount when test processing is performed using the processing apparatus according to the present invention as described above. As shown in Table 1, treated water B compared to raw water
OD and SS are greatly reduced, and as shown in Table 2, the amount of aerated air used is also significantly reduced.

【0011】[0011]

【表1】 [Table 1]

【0012】[0012]

【表2】 [Table 2]

【0013】[0013]

【発明の効果】以上のように、この発明では合成樹脂繊
維材で構成したろ材を用いた汚水の処理装置において、
処理水部と原水流入部をポンプを介して接続し、処理水
の一部を循環すること、およびろ材層高と水層高との比
率を攪拌に適切となるように装入することにより微細な
SSや有機性汚濁物質を単一槽で分離除去ができ、特に
循環によりろ層形成が安定化し、処理水の溶存酸素が再
利用できて汚水の高度処理が可能となり、また、ブロワ
動力の節減が可能となるとともに、完全なろ材の洗浄を
可能にしたものである。
As described above, according to the present invention, in a wastewater treatment apparatus using a filter medium made of synthetic resin fiber material,
The treated water section and raw water inflow section are connected via a pump to circulate a portion of the treated water, and the ratio between the height of the filter medium layer and the height of the water layer is charged so as to be appropriate for stirring. SS and organic pollutants can be separated and removed in a single tank. In particular, the formation of the filter layer is stabilized by circulation, the dissolved oxygen in the treated water can be reused, and the advanced treatment of the sewage becomes possible. In addition to savings, the filter media can be completely washed.

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

【図1】この発明に係る汚水の処理装置の縦断側面図で
ある。
FIG. 1 is a vertical side view of a wastewater treatment apparatus according to the present invention.

【図2】同じく、他の実施例の縦断側面図である。FIG. 2 is a longitudinal sectional side view of another embodiment.

【符号の説明】[Explanation of symbols]

1 処理槽 2 ろ材 3 曝気用エアノズル 4 ろ材攪拌用エアノズル DESCRIPTION OF SYMBOLS 1 Processing tank 2 Filter medium 3 Air nozzle for aeration 4 Air nozzle for filter medium stirring

フロントページの続き (51)Int.Cl.6 識別記号 FI B01D 29/38 580F Continued on the front page (51) Int.Cl. 6 Identification code FI B01D 29/38 580F

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 底部に逆円錐状の沈殿部を形成した円筒
状の処理槽1の上部にろ材流出防止材を設置して、その
下方にろ材2を装入し、そのろ材層内の下部に曝気用エ
アノズル3を、ろ材層の下方にろ材攪拌用エアノズル4
を設けるとともに、さらに処理槽1の下部に原水の供給
管と処理槽上部に処理水の流出部を、処理槽下底部に沈
殿物の取り出し口を設けて成る高濃度汚水の処理装置。
1. A filter medium outflow prevention material is installed on an upper part of a cylindrical treatment tank 1 having an inverted conical settling part formed at a bottom part, and a filter medium 2 is charged below the filter medium outflow prevention material. And an air nozzle 4 for stirring the filter medium below the filter medium layer.
And a high-concentration sewage treatment apparatus further comprising a raw water supply pipe below the treatment tank 1, an outlet for treated water above the treatment tank, and a sediment outlet at the bottom bottom of the treatment tank.
【請求項2】 上記処理槽に装入するろ材2の素材が芯
をポリプロピレン、鞘をポリエチレンとした熱融着性複
合繊維で繊度が18〜65デニールである第1フィラメ
ントと、素材がポリプロピレン繊維で繊度が3〜10デ
ニールである第2フィラメントと、素材が芯をポリプロ
ピレン、鞘をポリエチレンとした熱融着性複合繊維で繊
度が1.5〜6デニールである第3フィラメントを混綿
したウェッブをニードルパンチング法により布形化し、
両面のウェッブ起毛状態を平滑化することなく加熱処理
し、前記ウェッブの重量が200〜800g/平方メー
トル、厚みが2〜8mmの布形化板状体を製作し、この
布形化板状体を3〜5mm角に裁断したものをろ材とし
て装入している請求項1記載の高濃度汚水の処理装置。
2. A first filament having a denier of 18 to 65 denier, a heat-fusible conjugate fiber having a core of polypropylene and a sheath of polyethylene, and a polypropylene fiber as a material of the filter medium 2 to be charged into the treatment tank. A web obtained by mixing a second filament having a fineness of 3 to 10 denier and a third filament having a fineness of 1.5 to 6 denier in a heat-fusible composite fiber whose material is polypropylene as a core and polyethylene as a sheath. Fabricate by needle punching method,
A heat treatment is performed without smoothing the raised state of the web on both sides to produce a cloth-shaped plate having a weight of 200 to 800 g / m 2 and a thickness of 2 to 8 mm. The high-concentration sewage treatment apparatus according to claim 1, wherein the material cut into a 3 to 5 mm square is charged as a filter medium.
【請求項3】 上記処理槽1に装入したろ材2のろ材層
高と水層高との比率を65:35〜50:50となるよ
うに、上記布形化板状体ろ材を装入したことを特徴とす
る、請求項1および請求項2記載の高濃度汚水の処理装
置。
3. The cloth-shaped plate-shaped filter medium is charged so that the ratio of the filter medium layer height to the water layer height of the filter medium 2 charged in the treatment tank 1 is 65:35 to 50:50. The high-concentration sewage treatment apparatus according to claim 1 or 2, characterized in that:
【請求項4】 上記処理槽1の処理水部と原水流入部を
ポンプを介して接続し、処理水の一部を、線速度5〜2
0m/hで循環するようにしたことを特徴とする請求項
1から請求項3記載の高濃度汚水の処理装置。
4. A treatment water section of the treatment tank 1 and a raw water inflow section are connected via a pump, and a part of the treatment water is supplied at a linear velocity of 5 to 2
The high-concentration sewage treatment apparatus according to claim 1, wherein circulation is performed at 0 m / h.
JP29144697A 1997-10-24 1997-10-24 High-concentration wastewater treatment equipment Expired - Fee Related JP3468399B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP29144697A JP3468399B2 (en) 1997-10-24 1997-10-24 High-concentration wastewater treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP29144697A JP3468399B2 (en) 1997-10-24 1997-10-24 High-concentration wastewater treatment equipment

Publications (2)

Publication Number Publication Date
JPH11128966A true JPH11128966A (en) 1999-05-18
JP3468399B2 JP3468399B2 (en) 2003-11-17

Family

ID=17768982

Family Applications (1)

Application Number Title Priority Date Filing Date
JP29144697A Expired - Fee Related JP3468399B2 (en) 1997-10-24 1997-10-24 High-concentration wastewater treatment equipment

Country Status (1)

Country Link
JP (1) JP3468399B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114671501A (en) * 2020-12-24 2022-06-28 格林生态环境有限公司 A precipitation equipment for sewage treatment

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114671501A (en) * 2020-12-24 2022-06-28 格林生态环境有限公司 A precipitation equipment for sewage treatment
CN114671501B (en) * 2020-12-24 2023-09-01 格林生态环境有限公司 Sedimentation equipment for sewage treatment

Also Published As

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