JP2002166287A - Device and method for waste water treatment - Google Patents

Device and method for waste water treatment

Info

Publication number
JP2002166287A
JP2002166287A JP2000368166A JP2000368166A JP2002166287A JP 2002166287 A JP2002166287 A JP 2002166287A JP 2000368166 A JP2000368166 A JP 2000368166A JP 2000368166 A JP2000368166 A JP 2000368166A JP 2002166287 A JP2002166287 A JP 2002166287A
Authority
JP
Japan
Prior art keywords
filter
separation
biological reaction
wastewater treatment
reaction tank
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
JP2000368166A
Other languages
Japanese (ja)
Inventor
Itaru Sakai
至 坂井
Kenichiro Mizuno
健一郎 水野
Shohei Fukada
尚平 深田
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 JP2000368166A priority Critical patent/JP2002166287A/en
Publication of JP2002166287A publication Critical patent/JP2002166287A/en
Pending 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

  • Activated Sludge Processes (AREA)
  • Filtration Of Liquid (AREA)

Abstract

PROBLEM TO BE SOLVED: To efficiently solid-liquid separate and treat a biologically reacted solution which is biologically treated in a reaction tank. SOLUTION: A separation tank 19, in which at least one vertical type filtration body 9 comprising a material formed by vertically combining hollow and flat plates 9A provided with a filter cloth in a multistage state is dipped for setting, is provided on the side of the outlet of a biological reaction tank 6, the biologically reacted solution 15 from the biological reaction tank 6 is solid- liquid separated by the filtration body 9 making use of the water head difference in the separation tank 19, and then the treated water 13 after the separation is exhausted to the outside of the filtration body 9.

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、廃水処理方法お
よび装置、特に、下水を生物処理する際に、反応槽で生
物処理された生物反応液を効率的に固液分離して処理す
ることが可能な廃水処理方法および装置に関するもので
ある。
[0001] The present invention relates to a method and an apparatus for treating wastewater, and more particularly to a method and an apparatus for efficiently performing solid-liquid separation on a biological reaction solution which has been biologically treated in a reaction tank when biologically treating sewage. A possible wastewater treatment method and apparatus.

【0002】[0002]

【従来の技術】下水処理場における従来の処理方法を、
図面を参照しながら説明する。
2. Description of the Related Art Conventional treatment methods in sewage treatment plants
This will be described with reference to the drawings.

【0003】図2は、下水処理場における従来の廃液処
理装置を示す概略構成図である。
FIG. 2 is a schematic configuration diagram showing a conventional waste liquid treatment apparatus in a sewage treatment plant.

【0004】図2に示すように、流入下水1は、最初沈
澱池2において、重力沈降処理によって固液分離され
る。沈降した固形物は、汚泥掻き寄せ機3によって掻き
集められ、最初沈澱池引き抜き汚泥4として濃縮工程に
送られる。一方、沈降処理後の上澄水である最初沈澱池
越流水5は、反応槽6に供給される。反応槽6内には散
気装置7が設置されており、ブロワ8より供給される空
気によって爆気され、生物反応による活性汚泥処理が施
される。
As shown in FIG. 2, inflow sewage 1 is first solid-liquid separated in a sedimentation basin 2 by gravity sedimentation treatment. The settled solids are collected by the sludge scraper 3 and sent to the concentration step as sludge 4 from the settling basin. On the other hand, the first settling pond overflow water 5 which is the supernatant water after the sedimentation treatment is supplied to the reaction tank 6. An air diffuser 7 is installed in the reaction tank 6, and is exploded by air supplied from a blower 8 to perform an activated sludge treatment by a biological reaction.

【0005】このようにして活性汚泥処理された生物反
応液15は、最終沈澱池16に供給され、ここで再び、
重力沈降処理によって固液分離される。このようにして
最終沈澱池16で得られた上澄水は砂濾過設備17に供
給される。そして、更に濁質分が取り除かれた後、滅菌
設備18に供給され、ここで滅菌処理される。そして、
このように滅菌処理された下水の処理水13は、河川、
湖沼あるいは海域に放流されるか、または、再利用され
る。最終沈澱池16内からの引き抜き汚泥12は、反応
槽6に戻される。
[0005] The biological reaction solution 15 thus treated with the activated sludge is supplied to a final sedimentation basin 16 where it is again subjected to
Solid-liquid separation is performed by gravity sedimentation. The supernatant water thus obtained in the final settling basin 16 is supplied to the sand filtration facility 17. Then, after the turbid matter is further removed, the turbid matter is supplied to a sterilization facility 18 where it is sterilized. And
The sewage treated water 13 sterilized in this way is used for rivers,
Released into lakes or waters or reused. The sludge 12 drawn from the final settling basin 16 is returned to the reaction tank 6.

【0006】一方、公共用水域の富栄養化防止を図るた
めに、積極的な採用が検討されている窒素・リン除去等
の高度処理方法においては、反応速度をより大きくする
ために、反応槽は、標準活性汚泥法の場合より固形物濃
度の高い状態で運転されるケ一スが多い。従って、反応
槽から流出する高濃度の汚泥混合液を固液分離処理する
ことが必要となる。
On the other hand, in advanced treatment methods, such as nitrogen and phosphorus removal, which are being actively employed to prevent eutrophication of public water bodies, a reaction tank is required to increase the reaction rate. In many cases, the system is operated at a higher solid matter concentration than in the case of the standard activated sludge method. Therefore, it is necessary to subject the high-concentration sludge mixture flowing out of the reaction tank to a solid-liquid separation treatment.

【0007】特に、大都市においては、既に標準活性汚
泥法に対応した最終沈澱池が数多く稼動中であるので、
高度処理を採用するためには、図2の最終沈澱池16を
代替できるか、あるいは、これを補完することができる
新たな廃液処理手段の開発が強く望まれている。
[0007] In particular, in large cities, many final sedimentation basins compatible with the standard activated sludge method are already in operation.
In order to adopt the advanced treatment, it is strongly desired to develop a new waste liquid treatment means which can replace the final settling basin 16 of FIG. 2 or complement it.

【0008】[0008]

【発明が解決しようとする課題】このように、生物反応
により水中の有機物等を分解処理する活性汚泥等の生物
処理装置では、一般に、この生物汚泥を固液分離するた
めに、沈降分離手段による沈澱池が設けられている。し
かしながら、生物反応槽の後段に沈澱池を設けた従来の
生物処理装置では次のような問題がある。
As described above, in a biological treatment apparatus for activated sludge or the like which decomposes organic matter in water by a biological reaction, generally, the biological sludge is separated into solid and liquid by a sedimentation separation means. A sedimentation basin is provided. However, the conventional biological treatment apparatus provided with a sedimentation pond at the latter stage of the biological reaction tank has the following problems.

【0009】 比重差により汚泥を沈降分離する沈澱
処理では、汚泥の分離性能にも限界があり、流入負荷の
変動時や、バルキング発生時には処理水質が悪化する。
このため、高度な処理水質が要求される場合には、沈澱
池の後段に更に急速濾過機やストレーナ等の設備が必要
となる。
In the sedimentation treatment for sedimentation and separation of sludge due to a difference in specific gravity, there is a limit in sludge separation performance, and the quality of treated water deteriorates when the inflow load changes or when bulking occurs.
For this reason, when a high treatment water quality is required, equipment such as a rapid filter and a strainer is required at the subsequent stage of the sedimentation basin.

【0010】 最終沈澱池でスカムが発生したり、汚
泥が浮上したりする等のトラブルが発生し、水質が悪化
する場合が多い。
[0010] In many cases, troubles such as generation of scum and floating of sludge occur in the final sedimentation basin, and water quality often deteriorates.

【0011】 沈澱池は大きな設置スペースを必要と
する。
[0011] The settling basin requires a large installation space.

【0012】一方、沈降分離の代わりに生物汚泥を限外
濾過膜や精密濾過膜により膜分離する方法も提案されて
いる。この膜分離処理によれば、沈澱池のような大きな
スペースを必要とすることなく、濁質分が高度に除去さ
れた処理水を得ることができる。
On the other hand, a method has been proposed in which biological sludge is separated by a membrane using an ultrafiltration membrane or a microfiltration membrane instead of the sedimentation separation. According to this membrane separation treatment, it is possible to obtain treated water from which suspended matter is highly removed without requiring a large space such as a sedimentation pond.

【0013】しかしながら、限外濾過膜や精密濾過膜に
よる膜分離処理では、稼動エネルギーが大きい上に、膜
で処理した物質により膜が汚染され、膜孔の閉塞によっ
て濾過性能が低下するために定期的な薬液洗浄が必須で
あるという欠点がある。
[0013] However, in the membrane separation treatment using an ultrafiltration membrane or a microfiltration membrane, the operating energy is large, the membrane is contaminated by the substance treated with the membrane, and the filtration performance is reduced due to blockage of the membrane pores. There is a drawback that a proper chemical cleaning is essential.

【0014】従って、この発明の目的は、上述した従来
の生物処理における問題点を解決し、安定且つ効率的な
固液分離処理を可能とする廃水処理方法および装置を提
供することにある。
[0014] Accordingly, an object of the present invention is to provide a wastewater treatment method and apparatus capable of solving the above-mentioned problems in the conventional biological treatment and enabling stable and efficient solid-liquid separation treatment.

【0015】[0015]

【課題を解決するための手段】請求項1記載の発明は、
濾布を設けた複数枚の中空平板を上下多段に組み合わせ
たものからなる少なくとも1つの縦型濾過体が浸漬配置
された分離槽を、生物反応槽の出側に設け、前記分離槽
内において前記濾過体により水頭差を利用して、前記生
物反応槽からの生物反応液を固液分離し、分離後の処理
水を前記濾過体から排出することに特徴を有するもので
ある。
According to the first aspect of the present invention,
A separation tank in which at least one vertical filter body formed by combining a plurality of hollow flat plates provided with a filter cloth in upper and lower stages is immersed and arranged, provided on the outlet side of the biological reaction tank, and the separation tank is provided in the separation tank. It is characterized in that the biological reaction solution from the biological reaction tank is separated into solid and liquid by utilizing the head difference by the filter, and the separated treated water is discharged from the filter.

【0016】請求項2記載の発明は、前記濾布の表面に
付着した固形物を剥離除去しながら固液分離を行なうこ
とに特徴を有するものである。
A second aspect of the present invention is characterized in that solid-liquid separation is performed while peeling and removing solid matter adhered to the surface of the filter cloth.

【0017】請求項3記載の発明は、前記固形物を剥離
除去するために、流体を前記濾布面に吹き付けるか、ま
たは、流体を前記中空平板の内部に圧入することに特徴
を有するものである。
The invention according to claim 3 is characterized in that a fluid is sprayed on the surface of the filter cloth or a fluid is pressed into the inside of the hollow flat plate in order to peel and remove the solid matter. is there.

【0018】請求項4記載の発明は、前記固形物を剥離
除去するために、スクレーパを用いることに特徴を有す
るものである。
The invention according to claim 4 is characterized in that a scraper is used to peel off and remove the solid matter.

【0019】請求項5記載の発明は、前記処理水を砂濾
過手段を用いて処理することに特徴を有するものであ
る。
The invention according to claim 5 is characterized in that the treated water is treated using sand filtering means.

【0020】請求項6記載の発明は、生物反応槽と、前
記生物反応槽の出側に設けられた分離槽と、前記分離槽
内に浸漬配置された少なくとも1つの縦型濾過体とを備
え、前記濾過体は、濾布を設けた複数枚の中空平板を上
下多段に組み合わせたものからなることに特徴を有する
ものである。
According to a sixth aspect of the present invention, there is provided a biological reaction tank, a separation tank provided on an outlet side of the biological reaction tank, and at least one vertical filter body immersed and disposed in the separation tank. The filter is characterized in that the filter is composed of a plurality of hollow flat plates provided with filter cloths combined in upper and lower stages.

【0021】請求項7記載の発明は、前記濾布の表面に
付着した固形物の剥離手段が設けられていることに特徴
を有するものである。
[0021] The invention according to claim 7 is characterized in that a means for removing solid matter attached to the surface of the filter cloth is provided.

【0022】請求項8記載の発明は、前記濾過体からの
処理水を更に処理する砂濾過設備が設けられていること
に特徴を有するものである。
[0022] The invention according to claim 8 is characterized in that a sand filtration facility for further treating the treated water from the filter is provided.

【0023】[0023]

【発明の実施の形態】次に、この発明の廃水処理装置の
一実施態様を、図面を参照しながら説明する。
Next, an embodiment of a wastewater treatment apparatus according to the present invention will be described with reference to the drawings.

【0024】図1は、この発明の廃水処理装置を示す概
略構成図である。
FIG. 1 is a schematic diagram showing a wastewater treatment apparatus according to the present invention.

【0025】図1に示すように、流入下水1は、最初沈
澱池2において重力沈降によって固液分離される。沈降
した固形分は、汚泥掻き寄せ機3によって掻き寄せら
れ、最初沈澱池引き抜き汚泥4として最初沈澱池2から
排出される。一方、上澄水である最初沈澱池越流水5
は、反応槽6に供給され、ここでブロア8により供給さ
れる空気が散気装置7から供給されて曝気処理され、生
物反応が行なわれる。
As shown in FIG. 1, inflow sewage 1 is first separated into solid and liquid by gravity sedimentation in a sedimentation basin 2. The settled solids are scraped by the sludge scraper 3 and first discharged from the settling basin 2 as the settling basin drawn sludge 4. On the other hand, the first sedimentation pond
Is supplied to a reaction tank 6, where air supplied by a blower 8 is supplied from an air diffuser 7 to be aerated, and a biological reaction is performed.

【0026】このようにして得られた生物反応液15
は、分離槽19に供給され、ここで固液分離処理され
る。分離槽19内には、濾布を設けた複数個の中空平板
9Aを上下多段に組み合わせたものからなる縦型濾過体
9が浸漬配置されている。分離槽19内に供給された生
物反応液15は、縦型濾過体9の各中空平板9Aの濾布
により濾過されて固液分離される。濾過の駆動は、分離
槽19内の液位と固液分離手段9内の処理水の水位との
差である水頭差によって行われる。水頭差の変更は、濾
過体9内の処理水13を引き抜くためのポンプ14によ
る引き抜き量を変更することによって調節可能であり、
通常、0.1mから3mの範囲内とすることが好まし
い。
The biological reaction solution 15 thus obtained is
Is supplied to a separation tank 19, where it is subjected to a solid-liquid separation treatment. In the separation tank 19, a vertical filter body 9 formed by combining a plurality of hollow flat plates 9A provided with filter cloths in upper and lower stages is immersed. The biological reaction liquid 15 supplied into the separation tank 19 is filtered by the filter cloth of each hollow flat plate 9A of the vertical filter body 9 to be separated into solid and liquid. The filtration is driven by a head difference which is a difference between the liquid level in the separation tank 19 and the treated water level in the solid-liquid separation means 9. The change of the head difference can be adjusted by changing the withdrawal amount of the pump 14 for withdrawing the treated water 13 in the filter body 9,
Usually, it is preferable to be within the range of 0.1 m to 3 m.

【0027】縦型濾過体9の各中空平板9Aの上面およ
び下面には、開口部が設けてあり、この開口部は、濾布
により被覆されている。開口部の形状は、特に、限定さ
れないが、水頭圧によって付設されている濾布が撓まな
い形状とすることが好ましい。中空平板9Aが円盤形状
の場合、円盤径の径は、特に制限はないが、径が大きす
ぎると、濾布の表面に付着した固形物の除去が困難とな
るため、500mmから3000mm程度の範囲内が好
ましい。濾過体9の鉛直方向の長さについては、分離槽
19内に浸漬設置が可能な長さであれば、特に制限がな
いが、500mmから4000mm程度の範囲内が適当
である。中空平板9Aの材質としては、特に制限はな
く、ステンレス等の金属やFRP等の樹脂を用いること
ができる。
Openings are provided on the upper and lower surfaces of each hollow flat plate 9A of the vertical filter body 9, and these openings are covered with a filter cloth. The shape of the opening is not particularly limited, but is preferably a shape that does not allow the attached filter cloth to bend due to the head pressure. When the hollow flat plate 9A has a disk shape, the diameter of the disk diameter is not particularly limited. However, if the diameter is too large, it becomes difficult to remove solid substances attached to the surface of the filter cloth. Is preferred. The length of the filter body 9 in the vertical direction is not particularly limited as long as the filter body 9 can be immersed and installed in the separation tank 19, but is suitably in a range of about 500 mm to 4000 mm. The material of the hollow flat plate 9A is not particularly limited, and a metal such as stainless steel or a resin such as FRP can be used.

【0028】濾過の進行に伴って濾過体9の濾布表面に
は、固形物が付着して濾過速度が低下する。このため、
固形物剥離手段10によって、連続的もしくは間欠的に
濾過体9の濾布表面に付着した固形物を剥離除去する。
固形物剥離手段10としては、濾布に向けて水を墳射さ
せて濾布に付着した固形物を除去する構造の、水による
洗浄手段、濾布に向けて空気を噴射させて濾布に付着し
た固形物を除去する構造の、空気による洗浄手段、スク
レーパによって濾布に付着した固形物を掻き取る構造
の、スクレーパによる掻き取り手段および機械的もしく
は超音波によって濾布を振動させ、これによって濾布に
付着した固形物を除去する構造の、振動による洗浄手段
等を用いることができるが、剥離手段に要する駆動動力
が小さいといった点から、スクレーパによる掻き取り手
段が最も好ましい。
As the filtration proceeds, solids adhere to the surface of the filter cloth of the filter body 9 and the filtration speed decreases. For this reason,
The solids adhering to the filter cloth surface of the filter body 9 are continuously or intermittently peeled off by the solids peeling means 10.
The solid material peeling means 10 has a structure in which water is sprayed on the filter cloth to remove the solid matter attached to the filter cloth. The filter cloth is vibrated by means of a structure for removing adhered solid matter, a washing means by air, a structure for scraping solid matter adhered to the filter cloth by a scraper, a scraper by a scraper and mechanically or ultrasonically, Although a cleaning means by vibration or the like having a structure for removing solid matter attached to the filter cloth can be used, a scraping means using a scraper is most preferable because the driving power required for the peeling means is small.

【0029】この場合のスクレーパ形状としては、直線
形、渦巻形の何れも用いることができる。スクレーパの
材質としては、特に限定されることはなく、ステンレ
ス、合成樹脂等を用いることができるが、摩耗による耐
性が高いといった点、剥離した汚泥がスクレーパに付着
しにくいといった点、軽量であるといった点から、超高
分子量ポリエチレンが特に有効てある。
In this case, as the scraper shape, any of a linear shape and a spiral shape can be used. The material of the scraper is not particularly limited, and stainless steel, synthetic resin, or the like can be used. However, the scraper has high resistance to abrasion, the sludge that is not easily adhered to the scraper, and the light weight. In view of this, ultrahigh molecular weight polyethylene is particularly effective.

【0030】なお、水または空気等の流体を中空平板9
A内に圧入して、濾布に付着した固形物を逆洗すること
も可能である。
A fluid such as water or air is applied to the hollow flat plate 9.
It is also possible to press-fit into A and backwash the solid matter attached to the filter cloth.

【0031】固形物剥離手段10は、駆動モータ11に
よって縦型濾過体9の濾布表面を任意の回転速度で回転
しながら濾過体9の濾布表面に付着した固形物を剥離除
去する。固形物剥離手段10を固定し、濾過体9を駆動
モータ11によって回転させつつ濾布表面に付着した固
形物を剥離除去しても良い。
The solid material peeling means 10 peels and removes solid matter adhering to the filter cloth surface of the filter body 9 while rotating the filter cloth surface of the vertical filter body 9 at an arbitrary rotation speed by the drive motor 11. The solid material peeling means 10 may be fixed, and the solid matter adhering to the filter cloth surface may be peeled and removed while the filter body 9 is rotated by the drive motor 11.

【0032】縦型濾過体9の各中空平板9A内の処理水
は、処理水引き抜きポンプ14によって引き抜かれる。
The treated water in each hollow flat plate 9A of the vertical filter 9 is drawn by a treated water drawing pump 14.

【0033】図示されていないが、図1に示した砂濾過
設備を用いて処理水13を処理すれば、更に清澄な処理
水を得ることができる。
Although not shown, if the treated water 13 is treated using the sand filtration equipment shown in FIG. 1, clearer treated water can be obtained.

【0034】分離槽19内の濃縮生物反応液は、連続的
もしくは間欠的に分離槽引き抜き汚泥12として分離槽
19から引き抜かれ、その一部は、反応槽6内に返送汚
泥として供給される。
The concentrated biological reaction solution in the separation tank 19 is continuously or intermittently withdrawn from the separation tank 19 as the separation tank withdrawal sludge 12, and a part thereof is supplied into the reaction tank 6 as return sludge.

【0035】[0035]

【発明の効果】以上説明したように、この発明によれ
ば、濾布を設けた複数枚の中空平板を上下多段に組み合
わせたものからなる少なくとも1つの縦型濾過体が浸漬
配置された分離槽を、生物反応槽の出側に設け、前記分
離槽内において前記濾過体により水頭差を利用して、前
記生物反応槽からの生物反応液を固液分離することによ
って、生物反応液の固液分離を、大きな設置スペースを
必要とする沈澱池や大きな稼動動力と膜の薬液洗浄を必
要とする膜分離手段を用いることなく、低動力で安定か
つ確実に行なうことができることができ、また、高度処
理に対応した反応槽のMLSS増大、更には高濃度活性
汚泥法等の生物処理にも適用が可能であり、その効果は
非常に大きい。
As described above, according to the present invention, a separation tank in which at least one vertical filter body formed by combining a plurality of hollow flat plates provided with filter cloths in upper and lower stages is immersed. Is provided on the outlet side of the biological reaction tank, and a solid-liquid separation of the biological reaction liquid from the biological reaction tank is performed by utilizing the head difference by the filter in the separation tank. Separation can be performed stably and reliably with low power without using a sedimentation tank that requires a large installation space or membrane separation means that requires a large amount of operating power and chemical cleaning of the membrane. The present invention can be applied to an increase in the MLSS of a reaction tank corresponding to the treatment, and further to a biological treatment such as a high-concentration activated sludge method, and the effect is extremely large.

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

【図1】この発明の廃水処理装置を示す概略構成図であ
る。
FIG. 1 is a schematic configuration diagram showing a wastewater treatment device of the present invention.

【図2】下水処理場における従来の廃液処理装置を示す
概略構成図である。
FIG. 2 is a schematic configuration diagram showing a conventional waste liquid treatment device in a sewage treatment plant.

【符号の説明】[Explanation of symbols]

1:下水 2:最初沈澱池 3:汚泥掻き寄せ機 4:最初沈澱池引き抜き汚泥 5:最初沈澱池越流水 6:反応槽 7:散気装置 8:ブロワ 9:縦型濾過体 9A:中空平板 10:固形物剥離手段 11:駆動モータ 12:分離槽引き抜き汚泥 13:処理水 14:ポンプ 15:生物反応液 16:最終沈澱池 17:砂濾過設備 18:滅菌設備 19:分離槽 1: Sewage 2: First settling basin 3: Sludge scraper 4: Sludge withdrawn from first settling basin 5: First settling basin overflow 6: Reaction tank 7: Air diffuser 8: Blower 9: Vertical filter 9A: Hollow flat plate 10: Solid substance peeling means 11: Drive motor 12: Separation tank drawing sludge 13: Treated water 14: Pump 15: Biological reaction liquid 16: Final sedimentation basin 17: Sand filtration equipment 18: Sterilization equipment 19: Separation tank

───────────────────────────────────────────────────── 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) B01D 36/04 B01D 29/04 520A 520B 520D 530A 29/08 520A 540A 29/38 510A 530A 530Z 550B (72)発明者 深田 尚平 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) 4D028 BC17 BD17 4D066 AA05 AA07 AB06 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification code FI Theme coat ゛ (Reference) B01D 36/04 B01D 29/04 520A 520B 520D 530A 29/08 520A 540A 29/38 510A 530A 530Z 550B (72) Inventor Shohei Fukada 1-2-1 Marunouchi, Chiyoda-ku, Tokyo F-term (reference) 4D028 BC17 BD17 4D066 AA05 AA07 AB06

Claims (8)

【特許請求の範囲】[Claims] 【請求項1】 濾布を設けた複数枚の中空平板を上下多
段に組み合わせたものからなる少なくとも1つの縦型濾
過体が浸漬配置された分離槽を、生物反応槽の出側に設
け、前記分離槽内において前記濾過体により水頭差を利
用して、前記生物反応槽からの生物反応液を固液分離
し、分離後の処理水を前記濾過体から排出することを特
徴とする廃水処理方法。
1. A separation tank in which at least one vertical filter body formed by combining a plurality of hollow flat plates provided with a filter cloth in upper and lower multistages is provided on the outlet side of a biological reaction tank, A wastewater treatment method comprising: separating a biological reaction solution from the biological reaction tank from the biological reaction tank by solid-liquid separation by utilizing a head difference by the filter in the separation tank; and discharging treated water after separation from the filter. .
【請求項2】 前記濾布の表面に付着した固形物を剥離
除去しながら固液分離を行なうことを特徴とする、請求
項1記載の廃水処理方法。
2. The wastewater treatment method according to claim 1, wherein solid-liquid separation is performed while removing solid substances adhered to the surface of the filter cloth.
【請求項3】 前記固形物を剥離除去するために、流体
を前記濾布面に吹き付けるか、または、流体を前記中空
平板の内部に圧入することを特徴とする、請求項2記載
の廃水処理方法。
3. The wastewater treatment according to claim 2, wherein a fluid is sprayed on the surface of the filter cloth or a fluid is pressed into the hollow flat plate to remove the solid matter. Method.
【請求項4】 前記固形物を剥離除去するために、スク
レーパを用いることを特徴とする、請求項2記載の廃水
処理方法。
4. The wastewater treatment method according to claim 2, wherein a scraper is used to peel and remove said solid matter.
【請求項5】 前記処理水を砂濾過設備を用いて処理す
ることを特徴とする、請求項1から4の内の何れか1つ
に記載の廃水処理方法。
5. The wastewater treatment method according to claim 1, wherein the treated water is treated using a sand filtration facility.
【請求項6】 生物反応槽と、前記生物反応槽の出側に
設けられた分離槽と、前記分離槽内に浸漬配置された少
なくとも1つの縦型濾過体とを備え、前記濾過体は、濾
布を設けた複数枚の中空平板を上下多段に組み合わせた
ものからなることを特徴とする廃水処理装置。
6. A biological reaction tank, comprising: a separation tank provided on an outlet side of the biological reaction tank; and at least one vertical filter immersed and disposed in the separation tank. A wastewater treatment apparatus comprising a plurality of hollow flat plates provided with filter cloths combined in upper and lower stages.
【請求項7】 前記濾布の表面に付着した固形物の剥離
手段が設けられていることを特徴とする、請求項6記載
の廃水処理装置。
7. The wastewater treatment apparatus according to claim 6, further comprising means for removing solid matter attached to the surface of the filter cloth.
【請求項8】 前記濾過体からの処理水を更に処理する
砂濾過設備が設けられていることを特徴とする、請求項
6または7記載の廃水処理装置。
8. The wastewater treatment apparatus according to claim 6, further comprising a sand filtration facility for further treating the treated water from the filter.
JP2000368166A 2000-12-04 2000-12-04 Device and method for waste water treatment Pending JP2002166287A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000368166A JP2002166287A (en) 2000-12-04 2000-12-04 Device and method for waste water treatment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000368166A JP2002166287A (en) 2000-12-04 2000-12-04 Device and method for waste water treatment

Publications (1)

Publication Number Publication Date
JP2002166287A true JP2002166287A (en) 2002-06-11

Family

ID=18838467

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2000368166A Pending JP2002166287A (en) 2000-12-04 2000-12-04 Device and method for waste water treatment

Country Status (1)

Country Link
JP (1) JP2002166287A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112755621A (en) * 2020-12-17 2021-05-07 深圳市星源空间环境技术有限公司 Vibrations formula is convenient for separate sewage treatment mechanism of sewage debris
CN113526794A (en) * 2021-07-27 2021-10-22 广东东篱环境股份有限公司 Domestic wastewater treatment control system

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112755621A (en) * 2020-12-17 2021-05-07 深圳市星源空间环境技术有限公司 Vibrations formula is convenient for separate sewage treatment mechanism of sewage debris
CN113526794A (en) * 2021-07-27 2021-10-22 广东东篱环境股份有限公司 Domestic wastewater treatment control system

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