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JP2013000670A - Sewage treatment apparatus - Google Patents

Sewage treatment apparatus Download PDF

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JP2013000670A
JP2013000670A JP2011135187A JP2011135187A JP2013000670A JP 2013000670 A JP2013000670 A JP 2013000670A JP 2011135187 A JP2011135187 A JP 2011135187A JP 2011135187 A JP2011135187 A JP 2011135187A JP 2013000670 A JP2013000670 A JP 2013000670A
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sewage
treatment apparatus
tank
treated water
sewage treatment
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Daisuke Mikami
大助 三上
Tetsuo Namima
哲夫 浪間
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Asahi Kasei Chemicals Corp
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Asahi Kasei Chemicals Corp
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Priority to JP2011135187A priority Critical patent/JP2013000670A/en
Priority to CN2012202675845U priority patent/CN202898160U/en
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • 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

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

Abstract

PROBLEM TO BE SOLVED: To provide a sewage treatment apparatus which efficiently eliminates organic pollution material, a nitrogen compound, and a phosphorus compound by combining a biotreatment device and a membrane separation device, and which reduces a load on the membrane separation device and stably obtains high-quality reclaimed water.SOLUTION: The sewage treatment apparatus includes a purification device 3A which receives and purifies a part of sewage flowing to a trunk sewer; the biotreatment device 7 which biologically eliminates the organic pollution material, nitrogen compound, and phosphorus compound from treated water obtained by the purification device 3A; the membrane separation device 9 which separates and eliminates sludge from the biologically-treated water obtained by the biotreatment device 7 and obtains the reclaimed water. The purification device 3A includes a storage tank 11 combining an oil floating and separating unit which floats and separates oil from the sewage, a solid settling and separating unit which settles and separates solids in the sewage, and a solubilizing device which retains and solubilizes the solids settled and separated by the solid settling and separating unit.

Description

本発明は、集合住宅などから下水道幹線に向けて排出される汚水を受け入れ、汚水中の有機汚濁物、窒素化合物、及びリン化合物を生物学的に除去して再生水を得る汚水処理装置に関する。   The present invention relates to a sewage treatment apparatus that receives sewage discharged from an apartment house or the like toward a sewer main line and biologically removes organic pollutants, nitrogen compounds, and phosphorus compounds in the sewage to obtain reclaimed water.

下水道幹線に連絡する上流側の分岐管から汚水を引き入れ、その汚水を処理して再生水として市街地などに供給するサテライト処理場が知られている。例えば、特許文献1には、サテライト処理場に設置される汚水処理装置の一例が開示されている。この汚水処理装置は、浮上濾材を用いた高速濾過によって汚水の前処理を行った後、嫌気槽と好気槽とを備えた生物処理装置によって有機物等を除去することで再生水を得ている。特に、この装置では、省スペース化を実現するために、好気槽内に膜分離装置を設けている。   There is known a satellite treatment plant that draws sewage from an upstream branch pipe connected to a sewer main line, processes the sewage, and supplies it as reclaimed water to an urban area or the like. For example, Patent Document 1 discloses an example of a sewage treatment apparatus installed in a satellite treatment plant. This sewage treatment apparatus obtains reclaimed water by performing pretreatment of sewage by high-speed filtration using a floating filter medium, and then removing organic substances and the like by a biological treatment apparatus including an anaerobic tank and an aerobic tank. In particular, in this apparatus, a membrane separation apparatus is provided in the aerobic tank in order to save space.

特開2008−705号公報JP 2008-705 A

近年、再生水の利用用途の広がりに伴って再生水の高品質化が望まれてきており、再生水に含まれる窒素やリン化合物についても問題視されるようになってきた。しかしながら、従来の汚水処理装置では、嫌気槽と好気槽とを備えた生物処理装置を備えているものの、この装置では前処理として高速濾過が行われるので窒素やリン化合物の除去に必要な有機物成分が過度に除去される可能性がある。また、汚水中に溶存する有機物成分の量は、そもそも汚水の性状によって変化し、有機物成分の量が少ないと微生物の働きも抑えられ、脱窒素反応が不十分になる。また、有機物成分の量が少ないと微生物によるリン化合物の捕捉も不十分になり、膜分離装置での実質的なリン化合物の分離が難しくなって高品質の再生水を得ることが難しくなる。一方で、前処理を省略した装置構成とすると、膜分離装置への負荷が過大になり、安定して再生水を得ることが難しくなってしまう。   In recent years, with the widespread use of reclaimed water, it has been desired to improve the quality of reclaimed water, and nitrogen and phosphorus compounds contained in reclaimed water have also been regarded as problems. However, although the conventional sewage treatment apparatus includes a biological treatment apparatus including an anaerobic tank and an aerobic tank, since this apparatus performs high-speed filtration as a pretreatment, organic substances necessary for removing nitrogen and phosphorus compounds are used. Ingredients may be removed excessively. In addition, the amount of the organic component dissolved in the sewage varies depending on the nature of the sewage. If the amount of the organic component is small, the action of microorganisms is suppressed and the denitrification reaction is insufficient. Further, when the amount of the organic component is small, the phosphorus compound is not sufficiently captured by the microorganisms, and it becomes difficult to substantially separate the phosphorus compound by the membrane separation device, and it becomes difficult to obtain high-quality recycled water. On the other hand, if it is set as the apparatus structure which abbreviate | omitted the pretreatment, the load to a membrane separator will become excessive and it will become difficult to obtain reclaimed water stably.

本発明は、以上の課題を解決することを目的としており、生物処理装置と膜分離装置とを併用することで有機汚濁物、窒素化合物、及びリン化合物を効果的に除去すると共に、膜分離装置の負荷を低減して高品質の再生水を安定的に得ることができる汚水処理装置を提供することを目的とする。   The present invention aims to solve the above-mentioned problems, and effectively removes organic pollutants, nitrogen compounds, and phosphorus compounds by using a biological treatment apparatus and a membrane separation apparatus together with a membrane separation apparatus. It is an object of the present invention to provide a sewage treatment apparatus that can stably obtain high-quality reclaimed water by reducing the load of water.

本発明は、下水道幹線に向かって流れる汚水の一部を受け入れて浄化処理する浄化装置と、浄化装置で得られた処理水から、有機汚濁物、窒素化合物、及びリン化合物を生物学的に除去する生物処理装置と、生物処理装置で得られた生物処理水から濁質を分離除去して再生水を得る膜分離装置と、を備え、浄化装置は、汚水中の油分を浮上分離する油分浮上分離手段と、汚水中の固形分を沈降分離する固形分沈降分離手段と、固形分沈降分離手段で沈降分離された固形分を滞留させて可溶化する可溶化手段と、を有することを特徴とする汚水処理装置。   The present invention biologically removes organic pollutants, nitrogen compounds, and phosphorus compounds from a purification device that receives and purifies part of the sewage flowing toward the sewer main line, and the treated water obtained by the purification device. And a membrane separation device that separates and removes turbidity from the biologically treated water obtained by the biological treatment device to obtain reclaimed water, and the purification device floats and separates the oil component that floats and separates the oil component in the sewage And a solid content sedimentation and separation means for sedimenting and separating solids in sewage, and a solubilization means for retaining and solubilizing the solids sedimented and separated by the solid content sedimentation and separation means. Sewage treatment equipment.

本発明によれば、膜分離装置に過負荷を与える油分、及び固形分は、前段の浄化装置において除去される。さらに、浄化装置は、固形分沈降分離手段で沈降分離された固形分を可溶化する可溶化手段を備えており、生物処理装置において窒素化合物、及びリン化合物を生物学的に除去する上で必要となる有機物成分を固形分の可溶化によって補うことができる。その結果として、生物処理装置と膜分離装置とを併用することで有機汚濁物、窒素化合物、及びリン化合物を効果的に除去すると共に、膜分離装置の負荷を低減して高品質の再生水を安定的に得ることができる。   According to the present invention, the oil component and the solid component that give an overload to the membrane separation device are removed by the purification device in the previous stage. Furthermore, the purification device is equipped with a solubilizing means for solubilizing the solid content settled and separated by the solid content sedimentation separating means, and is necessary for biologically removing nitrogen compounds and phosphorus compounds in the biological treatment equipment. The organic component that becomes can be supplemented by solubilization of the solid content. As a result, the combined use of biological treatment equipment and membrane separation equipment effectively removes organic pollutants, nitrogen compounds, and phosphorus compounds, while reducing the load on the membrane separation equipment and stabilizing high-quality reclaimed water. Can be obtained.

また、可溶化手段での汚水の滞留時間は、1時間以上で、且つ24時間以下であると好ましく、可溶化手段での汚水の滞留時間は、2時間以上で、且つ8時間以下であると更に好ましい。   Moreover, the residence time of the sewage in the solubilization means is preferably 1 hour or more and 24 hours or less, and the residence time of the sewage in the solubilization means is 2 hours or more and 8 hours or less. Further preferred.

さらに、浄化装置で得られた処理水中の残存夾雑物を物理的に分離除去し、残存夾雑物を除去した処理水を生物処理装置に供給する固液分離装置を備えると好適である。残存夾雑物を除去することで、膜分離装置に与える負荷が更に低減される。   Furthermore, it is preferable to provide a solid-liquid separation device that physically separates and removes the remaining impurities in the treated water obtained by the purification device and supplies the treated water from which the remaining impurities have been removed to the biological treatment device. By removing the remaining contaminants, the load applied to the membrane separation device is further reduced.

さらに、浄化装置は、油分浮上分離手段、及び固形分沈降分離手段として機能する汚水の貯留槽を有し、貯留槽は、汚水を受け入れる導入部と、汚水を静置状態に保持して汚水から油分を浮上分離すると共に、汚水から固形分を沈降分離する槽本体と、油分、及び固形分が分離された処理水を槽本体から排出する排出部と、を有すると好適である。この構成によれば、汚水の貯留槽によって油分浮上分離手段、及び固形分沈降分離手段を兼用できるので、省スペース化に有利であり、さらに、比重差によって油分、固形分、及び処理水を簡易に分離できるので装置構成のシンプル化に有利である。   Further, the purification device has a sewage storage tank functioning as an oil flotation separating means and a solid sedimentation separating means, and the storage tank holds the sewage from the sewage by holding the sewage in a stationary state. It is preferable to have a tank main body that floats and separates the oil content and settles and separates the solid content from the sewage, and a discharge unit that discharges the oil and the treated water from which the solid content has been separated from the tank main body. According to this configuration, the sewage storage tank can be used for both the oil flotation separation means and the solid sedimentation separation means, which is advantageous for space saving. Further, the oil content, solid content, and treated water can be simplified by the difference in specific gravity. It is advantageous to simplify the device configuration.

さらに、槽本体は、沈降する固形分が堆積する底部と、底部の周縁に沿って立設されると共に、固形分を保持する側壁とを有し、可溶化手段は、固形分を滞留させる底部、及び側壁によって形成されると好適である。上記構成によれば、汚水から沈降分離された固形分を可溶化のために滞留させる構成を簡単に実現できる。   Further, the tank main body has a bottom portion on which the sedimented solid content is deposited, and a side wall that holds the solid content while being erected along the periphery of the bottom portion, and the solubilizing means is a bottom portion that retains the solid content. , And the side wall. According to the said structure, the structure which makes solid content settled and separated from sewage retain for solubilization is easily realizable.

さらに、貯留槽は、槽本体を区切る仕切壁と、仕切壁を挟んで隣接する貯留室同士を連通する連通孔と、を有すると好適である。貯留槽の槽本体を仕切壁で区切ることにより、汚水中の残存夾雑物の除去を期待でき、特に後段に固液分離装置を配置する場合には、固液分離装置の負荷を低減できる。   Furthermore, the storage tank preferably includes a partition wall that partitions the tank body and a communication hole that connects adjacent storage chambers with the partition wall interposed therebetween. By separating the tank main body of the storage tank with a partition wall, it is possible to expect removal of residual contaminants in the sewage, and particularly when a solid-liquid separator is arranged in the subsequent stage, the load on the solid-liquid separator can be reduced.

さらに、導入部は、仕切壁によって区切られた複数の貯留室のうち、いずれか一つの貯留室に設けられ、排出部は、複数の貯留室のうち、導入部が設けられた貯留室とは別の貯留室に設けられていると好適である。この構成によれば、導入部が設けられた貯留室とは別の貯留室に排出部が設けられているので、排出部が設けられた下流の貯留室では、導入部で導入される汚水の流れに影響され難くなり、従って、下流の貯留室では汚水を静置状態に保持し易くなる。   Furthermore, the introduction unit is provided in any one of the plurality of storage chambers partitioned by the partition wall, and the discharge unit is a storage chamber in which the introduction unit is provided among the plurality of storage chambers. It is suitable if it is provided in another storage chamber. According to this configuration, since the discharge unit is provided in a storage chamber different from the storage chamber in which the introduction unit is provided, in the downstream storage chamber in which the discharge unit is provided, the sewage introduced in the introduction unit It becomes difficult to be influenced by the flow, and therefore, it becomes easy to keep the sewage in a stationary state in the downstream storage chamber.

本発明によれば、生物処理装置と膜分離装置とを併用することで有機汚濁物、窒素化合物、及びリン化合物を効果的に除去すると共に、膜分離装置の負荷を低減して高品質の再生水を安定的に得ることができる。   According to the present invention, organic contaminants, nitrogen compounds, and phosphorus compounds are effectively removed by using a biological treatment device and a membrane separation device in combination, and the load on the membrane separation device is reduced to produce high-quality recycled water. Can be obtained stably.

本発明の実施形態に係る汚水処理装置と下水道幹線との関係を概略的に示す図である。It is a figure which shows roughly the relationship between the sewage treatment apparatus which concerns on embodiment of this invention, and a sewer main line. 本発明の実施形態に係る汚水処理装置を模式的に示す図である。It is a figure which shows typically the sewage treatment apparatus which concerns on embodiment of this invention. 本発明の第1実施形態に係る浄化装置を模式的に示す断面図である。It is sectional drawing which shows typically the purification apparatus which concerns on 1st Embodiment of this invention. 本実施形態に係る固液分離装置を模式的に示す断面図である。It is sectional drawing which shows typically the solid-liquid separation apparatus which concerns on this embodiment. 本実施形態に係る生物処理装置を模式的に示す図である。It is a figure which shows typically the biological treatment apparatus which concerns on this embodiment. 本発明の第2実施形態に係る浄化装置を模式的に示す断面図である。It is sectional drawing which shows typically the purification apparatus which concerns on 2nd Embodiment of this invention. 本発明の第3実施形態に係る浄化装置を模式的に示す断面図である。It is sectional drawing which shows typically the purification apparatus which concerns on 3rd Embodiment of this invention.

以下、本発明の好適な実施形態に係る汚水処理装置について図面を参照しながら説明する。なお、本発明は以下の実施形態に限定されるものではなく、本発明を具現化する態様が広く含まれる。   Hereinafter, a sewage treatment apparatus according to a preferred embodiment of the present invention will be described with reference to the drawings. In addition, this invention is not limited to the following embodiment, The aspect which embodies this invention is included widely.

図1に示されるように、汚水処理装置1Aは、集合住宅や工場などから下水道幹線に向けて排出される汚水を受け入れ、汚水中の有機汚濁物、窒素化合物、及びリン化合物を生物学的に除去して再生水を得る装置である。なお、汚水の受け入れは、集合住宅や工場などの施設単位で排出される汚水の一部であったり、特定エリア内に存在する複数の施設から排出される合流汚水の一部であったりしてもよい。なお、汚水処理装置1Aで受け入れる汚水を、排水量(全量)の一部とすることにより、排水量の変動の影響を受けずに、必要設備に合わせてサイズを調整でき、経済性が向上する。   As shown in FIG. 1, the sewage treatment apparatus 1A accepts sewage discharged from an apartment house or factory toward a sewer main line, and biologically removes organic pollutants, nitrogen compounds, and phosphorus compounds in the sewage. It is a device that removes to obtain reclaimed water. In addition, acceptance of sewage may be part of sewage discharged in units of facilities such as apartment houses or factories, or part of combined sewage discharged from multiple facilities in a specific area. Also good. In addition, by making the sewage received by the sewage treatment apparatus 1A a part of the drainage amount (total amount), the size can be adjusted according to the required facilities without being affected by the fluctuation of the drainage amount, and the economy is improved.

図2に示されるように、第1の実施形態に係る汚水処理装置1Aは、汚水を受け入れて浄化処理する浄化装置3Aと、浄化装置3Aで得られた処理水中の残存夾雑物(例えば、髪の毛など)を物理的に分離除去する固液分離装置5と、固液分離装置5で得られた二次的な処理水から、有機汚濁物、窒素化合物、及びリン化合物を生物学的に除去する生物処理装置7と、生物処理装置7で得られた生物処理水から濁質を分離除去して再生水を得る膜分離装置9と、を備えている。
[浄化装置]
As shown in FIG. 2, a sewage treatment apparatus 1A according to the first embodiment includes a purification apparatus 3A that receives and purifies sewage, and residual impurities (for example, hair) in treated water obtained by the purification apparatus 3A. And the like, and organic contaminants, nitrogen compounds, and phosphorus compounds are biologically removed from the solid-liquid separation device 5 that physically separates and removes, and the secondary treated water obtained by the solid-liquid separation device 5. A biological treatment device 7 and a membrane separation device 9 that separates and removes turbidity from the biological treatment water obtained by the biological treatment device 7 to obtain reclaimed water are provided.
[Purification device]

最初に、図3を参照して浄化装置3Aについて説明する。浄化装置3Aは、油分浮上分離手段、固形分沈降分離手段、及び可溶化手段を備えている。油分浮上分離手段とは、汚水中の水分Wと油脂分Fとを比重差を利用して分離する手段であり、固形分沈降分離手段とは、糞塊などの粗大固形分(固形分)Sと水分Wとの比重差を利用し、汚水から粗大固形分Sを沈降分離する手段である。また、可溶化手段は、沈降堆積した粗大固形分Sを長時間滞留させることで可溶化する手段である。   First, the purification device 3A will be described with reference to FIG. The purification apparatus 3A includes an oil content floating separation means, a solid content sedimentation separation means, and a solubilization means. The oil flotation separation means is means for separating the water W and the fats and oils F in the sewage using the difference in specific gravity, and the solid sedimentation separation means is a coarse solid content (solid content) S such as feces. Is a means for settling and separating coarse solids S from sewage using the specific gravity difference between water and water W. The solubilizing means is a means for solubilizing the sedimented and deposited coarse solids S for a long time.

本実施形態に係る浄化装置3Aでは、油分浮上分離手段、固形分沈降分離手段、及び可溶化手段として機能する汚水の貯留槽11Aを備えている。貯留槽11Aは、汚水を受け入れる導入管(導入部)13と、汚水を蓄える槽本体15Aと、槽本体15Aから処理水(以下、「一次処理水」という)を排出する排出管(排出部)17とを備えている。   The purification apparatus 3A according to the present embodiment includes a sewage storage tank 11A that functions as an oil content floating separation unit, a solid content settling separation unit, and a solubilization unit. The storage tank 11A includes an introduction pipe (introduction section) 13 that receives sewage, a tank body 15A that stores sewage, and a discharge pipe (discharge section) that discharges treated water (hereinafter referred to as “primary treated water”) from the tank body 15A. 17.

汚水を受け入れる導入管(導入部)13は、槽本体15Aの側壁25を貫通すると共に、貯留槽11A内で屈曲し、管流出口13cが貯留槽11A内の下方を向くように配置されている。管流出口13cは、流入する汚水による油脂分の層(以下、「油層」という)のかき混ぜを防止できる方が好ましいため、予定水位に生じる油層を仮定した場合に、その油層よりも下方に配置する方が好ましい。   The introduction pipe (introduction section) 13 that receives sewage passes through the side wall 25 of the tank body 15A, is bent in the storage tank 11A, and is arranged so that the pipe outlet 13c faces downward in the storage tank 11A. . The pipe outlet 13c is preferably disposed below the oil layer when it is assumed that an oil layer generated at a predetermined water level is assumed because it is preferable to prevent the oil and fat layer (hereinafter referred to as "oil layer") from being mixed with the inflowing sewage. Is preferred.

処理水を排出する排出管(排出部)17は、導入管13に対向して配置されており、槽本体15Aの側壁25を貫通すると共に、槽本体15A内で屈曲し、管流出口17cが槽本体15Aの下方に向くように配置されている。管流出口17cは、油層のかき混ぜを防止できる方が好ましいため、予定水位に生じる油層を仮定した場合に、その油層よりも下方に配置する方が好ましい。   A discharge pipe (discharge section) 17 that discharges the treated water is disposed to face the introduction pipe 13 and penetrates the side wall 25 of the tank body 15A and bends in the tank body 15A. It arrange | positions so that it may face the downward direction of 15 A of tank main bodies. Since it is preferable that the pipe outlet 17c can prevent the oil layer from being stirred, it is preferable to dispose the pipe outlet 17c below the oil layer when an oil layer generated at a predetermined water level is assumed.

また、排出管17の管流出口17cは、槽本体15A内に沈降堆積する粗大固形分Sの吸い込みを防止する必要があるため、槽本体15A内に堆積する粗大固形分Sの嵩を想定し、その嵩よりも高い位置となるように配置されている。   Further, since the pipe outlet 17c of the discharge pipe 17 needs to prevent the suction of the coarse solid content S that settles and deposits in the tank body 15A, the bulk of the coarse solid content S that accumulates in the tank body 15A is assumed. It is arranged to be at a position higher than its bulk.

汚水は、導入管13を介して槽本体15A内に導入され、槽本体15Aで静置状態に保持される。その際に、汚水中の油脂分Fは浮上分離され、また、粗大固形分Sは沈降分離される。   The sewage is introduced into the tank body 15A through the introduction pipe 13, and is kept stationary by the tank body 15A. At that time, the oil and fat F in the sewage is floated and separated, and the coarse solid S is settled and separated.

槽本体15Aは、汚水から沈降分離された粗大固形分Sが堆積する底部21と、底部21の周縁に沿って立設されると共に、粗大固形分Sを保持する側壁25とを有する。従って、汚水から沈降分離された粗大固形分Sは、底部21及び側壁25によって定位置に保持され、所定時間、槽本体15A内で滞留する。その結果、粗大固形分S中の有機物成分の一次処理水中への溶出が図られる。   15 A of tank main bodies have the bottom part 21 in which the coarse solid content S settled and separated from the sewage deposits, and the side wall 25 which hold | maintains the coarse solid content S while standing along the periphery of the bottom part 21. As shown in FIG. Accordingly, the coarse solid content S settled and separated from the sewage is held at a fixed position by the bottom 21 and the side wall 25 and stays in the tank body 15A for a predetermined time. As a result, elution of the organic component in the coarse solid content S into the primary treated water is achieved.

粗大固形分S中の有機物成分の可溶化には、1時間〜24時間が必要であり、望ましくは2時間〜8時間が必要である。従って、貯留槽11Aを可溶化手段として実現させるためには、粗大固形分Sの滞留時間が、1時間以上で、且つ24時間以下となるように設計し、さらに、望ましくは、滞留時間が、2時間以上で、且つ8時間以下となるように設計する必要がある。   The solubilization of the organic component in the coarse solid S requires 1 to 24 hours, preferably 2 to 8 hours. Therefore, in order to realize the storage tank 11A as a solubilizing means, the residence time of the coarse solid content S is designed to be 1 hour or more and 24 hours or less, and more preferably, the residence time is It is necessary to design for 2 hours or more and 8 hours or less.

なお、汚水の滞留時間は、設計上、汚水の流入流量、汚水の排出流量、及び貯留槽11Aの槽本体15Aの容積によって定めることが可能である。例えば、時間流入量15mであれば、15m〜360m(1〜24hr滞留)、望ましくは、30m〜120m(2〜8hr滞留)となる。 In addition, the residence time of sewage can be determined by design by the inflow flow rate of sewage, the discharge flow rate of sewage, and the volume of the tank body 15A of the storage tank 11A. For example, if the time inflow amount is 15 m 3 , it is 15 m 3 to 360 m 3 (1 to 24 hr retention), and preferably 30 m 3 to 120 m 3 (2 to 8 hr residence).

なお、滞留時間が長くなると有機物成分の可溶化には有利であるが、一方で、槽本体15Aの容積の増大につながるなどして設備が過大になり、処理効率やコストの面で不利になる。また、滞留時間が長くなると底部で可溶化した有機物成分が嫌気化して有機物の分解が進み可溶化効果が損なわれる。従って、貯留槽11Aは、粗大固形分Sの滞留時間が、上限値で24時間以下、望ましくは、8時間以下となるように設計される必要がある。   A long residence time is advantageous for solubilizing organic components, but on the other hand, the capacity of the tank main body 15A is increased and the equipment becomes excessive, which is disadvantageous in terms of processing efficiency and cost. . In addition, when the residence time is increased, the organic component solubilized at the bottom is anaerobic, decomposition of the organic matter proceeds, and the solubilizing effect is impaired. Accordingly, the storage tank 11A needs to be designed so that the residence time of the coarse solid content S is 24 hours or less, preferably 8 hours or less, as an upper limit.

槽本体15Aの可溶化手段としての機能により、粗大固形分S中の有機物成分が溶出された一次処理水は、排出管17から排出され、移送管を備えた一次処理水排出ライン27を通って固液分離装置5に供給される。
[固液分離装置]
Due to the function of the tank body 15A as the solubilizing means, the primary treated water from which the organic component in the coarse solid S is eluted is discharged from the discharge pipe 17 and passes through the primary treated water discharge line 27 provided with a transfer pipe. It is supplied to the solid-liquid separator 5.
[Solid-liquid separator]

図2、及び図4に示されるように、固液分離装置5は、一次処理水を受け入れる貯水部29と、貯水部29内を上流側領域(一次側領域)29aと下流側領域(二次側領域)29bとに区分けするように配置された微細夾雑物分離部31とを備えている。微細夾雑物分離部31は、ドラム型スクリーンやバースクリーンなどを適宜に適用できるが、髪の毛などの繊維状の夾雑物の除去を効果的に行うためには、メッシュ状のドラムによって固液分離を図るドラム型スクリーンの方が有利である。   As shown in FIG. 2 and FIG. 4, the solid-liquid separation device 5 includes a water storage unit 29 that receives primary treated water, an upstream region (primary region) 29 a and a downstream region (secondary region) in the water storage unit 29. And a fine contaminant separating unit 31 arranged so as to be divided into a side region 29b. As the fine contaminant separation unit 31, a drum-type screen or a bar screen can be appropriately applied. However, in order to effectively remove fibrous contaminants such as hair, solid-liquid separation is performed by a mesh-shaped drum. A drum-type screen is more advantageous.

貯水部29の一次側領域29aには一次処理水の導入部32が設けられ、二次側領域29bには微細夾雑物分離部31で微細夾雑物が除去された後の二次的な処理水(以下、「二次処理水」という)が排出される排出部33が設けられている。排出部33は、後段の生物処理装置7に連絡する移送管を備えた二次処理水移送ライン30に接続されており、二次処理水移送ライン30には、管路を自動、または手動にて開閉するバルブ30aが設けられている。また、微細夾雑物分離部31で除去された微細夾雑物は、バケツ34に受けられて排出される。
[生物処理装置、及び膜分離装置]
The primary treated water introduction part 32 is provided in the primary side area 29a of the water storage part 29, and the secondary treated water after the fine contaminants are removed by the fine contaminant separating part 31 in the secondary side area 29b. A discharge part 33 for discharging (hereinafter referred to as “secondary treated water”) is provided. The discharge unit 33 is connected to a secondary treated water transfer line 30 having a transfer pipe that communicates with the biological treatment apparatus 7 at the subsequent stage. A valve 30a that opens and closes is provided. Further, the fine contaminants removed by the fine contaminant separation unit 31 are received by the bucket 34 and discharged.
[Biological treatment apparatus and membrane separation apparatus]

図2、及び図5に示されるように、生物処理装置7、及び膜分離装置9は、活性汚泥により、二次処理水中に含まれる有機物を除去すると共に、二次処理水の窒素やリンを高度に処理する装置である。本実施形態に係る生物処理装置7は、上流側から順番に配置された嫌気槽37、無酸素槽38及び好気槽39を備えており、具体的には、嫌気−無酸素−好気法(A2O法)と称される処理方式を具現化する装置である。また、本実施形態に係る膜分離装置9は、生物処理装置7で得られた活性汚泥を含む生物処理水から汚泥などの濁質を分離除去して再生水を得る装置であり、具体的には、膜分離活性汚泥法(MBR)と称される処理方式を具現化する装置である。   As shown in FIGS. 2 and 5, the biological treatment device 7 and the membrane separation device 9 remove organic substances contained in the secondary treated water with activated sludge and remove nitrogen and phosphorus from the secondary treated water. It is a highly processing device. The biological treatment apparatus 7 according to this embodiment includes an anaerobic tank 37, an anaerobic tank 38, and an aerobic tank 39 arranged in order from the upstream side. Specifically, the anaerobic-anoxic-aerobic method. It is an apparatus that embodies a processing method called (A2O method). The membrane separation device 9 according to the present embodiment is a device that separates and removes turbidity such as sludge from biologically treated water containing activated sludge obtained by the biological treatment device 7 to obtain reclaimed water. Specifically, It is an apparatus that embodies a treatment system called a membrane separation activated sludge process (MBR).

生物処理装置7は、嫌気槽37よりも上流側に二次処理水を受け入れる調整槽40を備えており、調整槽40内に供給された二次処理水は、ポンプ41によって嫌気槽37に供給される。また、生物処理装置7には、好気槽39から前段の無酸素槽38に硝化液を送る循環配管42と、好気槽39から嫌気槽37に返送汚泥を送る返送配管43とが設けられている。また、嫌気槽37、及び無酸素槽38内には撹拌翼44が設置されており、好気槽39にはブロワ45から供給された空気を散気する散気管46が設けられている。   The biological treatment apparatus 7 includes an adjustment tank 40 that receives the secondary treatment water upstream of the anaerobic tank 37, and the secondary treatment water supplied into the adjustment tank 40 is supplied to the anaerobic tank 37 by the pump 41. Is done. In addition, the biological treatment apparatus 7 is provided with a circulation pipe 42 for sending the nitrification liquid from the aerobic tank 39 to the preceding anaerobic tank 38 and a return pipe 43 for sending the returned sludge from the aerobic tank 39 to the anaerobic tank 37. ing. Further, a stirring blade 44 is installed in the anaerobic tank 37 and the anaerobic tank 38, and an aeration tube 46 for diffusing the air supplied from the blower 45 is provided in the aerobic tank 39.

調整槽40から嫌気槽37内へ供給された二次処理水は、返送配管43によって送られてきた返送汚泥と混合される。返送汚泥に含まれるリン蓄積菌は、嫌気槽37内の処理水(以下、「生物処理水」という)中と好気槽39からの硝化液中の溶解性有機物を取り込むと同時に菌体内に蓄積したリンを放出する。   The secondary treated water supplied from the adjustment tank 40 into the anaerobic tank 37 is mixed with the return sludge sent by the return pipe 43. The phosphorus accumulating bacteria contained in the returned sludge are taken up in the microbial cells at the same time as taking in the soluble organic matter in the treated water in the anaerobic tank 37 (hereinafter referred to as “biologically treated water”) and the nitrifying liquid from the aerobic tank 39. Release phosphorus.

次に、嫌気槽37内の生物処理水は無酸素槽38に導入される。この無酸素槽38へは後段の好気槽39からの硝化液も導入されており、嫌気槽37から流出した生物処理水と硝化液とが無酸素状態で接触する。嫌気槽37からの生物処理水中の汚泥に含まれる脱窒菌が生物処理水中の有機物成分を水素供与体として脱窒を行うことにより、硝化液中の硝酸態窒素が窒素ガスに変化し、除去される。   Next, the biologically treated water in the anaerobic tank 37 is introduced into the anoxic tank 38. The anaerobic tank 38 is also introduced with a nitrifying liquid from a subsequent aerobic tank 39, and the biologically treated water flowing out of the anaerobic tank 37 and the nitrifying liquid come into contact with each other in an oxygen-free state. The denitrifying bacteria contained in the sludge in the biologically treated water from the anaerobic tank 37 denitrify the organic component in the biologically treated water as a hydrogen donor, so that the nitrate nitrogen in the nitrification solution is changed to nitrogen gas and removed. The

次に、無酸素槽38内の生物処理水は好気槽39に導入されて曝気処理され、好気状態下で汚水中の有機物が酸化分解されると共に、汚泥中の硝化細菌により有機態窒素やアンモニア態窒素が硝化される。さらに好気状態下では、生物処理水中のリン化合物は、リン蓄積菌により過剰に摂取され、このリン蓄積菌を含む汚泥を系外へ抜き出すことにより、リンが液中から除去される。   Next, the biologically treated water in the anoxic tank 38 is introduced into the aerobic tank 39 and subjected to aeration treatment, and the organic matter in the sewage is oxidatively decomposed in the aerobic state, and the organic nitrogen by the nitrifying bacteria in the sludge. And ammonia nitrogen is nitrified. Furthermore, under an aerobic condition, the phosphorus compound in the biologically treated water is excessively ingested by the phosphorus accumulating bacteria, and phosphorus is removed from the liquid by extracting the sludge containing the phosphorus accumulating bacteria out of the system.

好気槽39内の生物処理水、つまり、生物処理装置7で得られた生物処理水は膜分離装置9によって汚泥などの濁質が分離除去されて再生水となる。膜分離装置9は、中空糸膜などの膜エレメントを備えた膜モジュール9a、膜モジュール9aに接続されたヘッダ管9b、ヘッダ管9bを介して膜モジュール9aに吸引濾過を行わせるポンプ(図示省略)などを備えている。ヘッダ管9bは、再生水を移送する移送管を備えた再生水ライン51に接続されている。再生水ライン51は、集合住宅や工場、散水施設、または噴水や公園の池などの人工的な施設に連絡しており、再生水ライン51によって移送された再生水は、各施設において適宜に利用される。   The biologically treated water in the aerobic tank 39, that is, the biologically treated water obtained by the biological treatment device 7 is separated and removed by the membrane separation device 9 into sludge and the like to become reclaimed water. The membrane separation device 9 includes a membrane module 9a having a membrane element such as a hollow fiber membrane, a header pipe 9b connected to the membrane module 9a, and a pump (not shown) that performs suction filtration on the membrane module 9a via the header pipe 9b. ) Etc. The header pipe 9b is connected to a reclaimed water line 51 having a transfer pipe for transferring reclaimed water. The reclaimed water line 51 communicates with apartment buildings, factories, watering facilities, or artificial facilities such as fountains and park ponds, and the reclaimed water transferred by the reclaimed water line 51 is appropriately used in each facility.

本実施形態に係る汚水処理装置1Aによれば、膜分離装置9に過負荷を与える油脂分F、及び固形分Sは、前段の浄化装置3Aにおいて除去される。さらに、浄化装置3Aは、固形分沈降分離手段、及び可溶化手段として機能する貯留槽11Aを備えており、生物処理装置7において窒素化合物、及びリン化合物を生物学的に除去する上で必要となる有機物成分を粗大固形分Sの可溶化によって補うことができる。その結果として、生物処理装置7と膜分離装置9とを併用することで有機汚濁物、窒素化合物、及びリン化合物を効果的に除去すると共に、膜分離装置9の負荷を低減して高品質の再生水を安定的に得ることができる。   According to the sewage treatment apparatus 1A according to the present embodiment, the oil / fat F and the solid S that give an overload to the membrane separation apparatus 9 are removed by the purification apparatus 3A in the previous stage. Furthermore, the purification device 3A includes a storage tank 11A that functions as a solids sedimentation separation unit and a solubilization unit, and is necessary for biologically removing nitrogen compounds and phosphorus compounds in the biological treatment device 7. The organic component can be supplemented by solubilization of the coarse solid S. As a result, by using the biological treatment device 7 and the membrane separation device 9 together, organic pollutants, nitrogen compounds, and phosphorus compounds are effectively removed, and the load on the membrane separation device 9 is reduced, resulting in high quality. Reclaimed water can be obtained stably.

なお、参考例として、例えば、貯留槽11Aに対応する浄化装置3Aなどを設けることなく、生物処理装置の前処理工程としてスクリーンなどを設ける態様(「通常態様」と称する)も想定されるが、この通常態様では、糞塊などの有機物がスクリーンで捕捉されてしまうため、汚水処理装置1Aのごとく、有機物成分を有効利用することはできない。   As a reference example, for example, a mode in which a screen or the like is provided as a pretreatment process of a biological treatment device without providing a purification device 3A corresponding to the storage tank 11A (referred to as a “normal mode”) is also assumed. In this normal mode, since organic matter such as feces is captured by the screen, the organic matter component cannot be effectively used as in the case of the sewage treatment apparatus 1A.

さらに、本実施形態では、浄化装置3Aの貯留槽11Aによって油分浮上分離手段、及び固形分沈降分離手段を兼用できるので、省スペース化に有利であり、さらに、比重差によって油脂分F、粗大固形分S、及び一次処理水を簡易に分離できるので装置構成のシンプル化に有利である。   Furthermore, in this embodiment, since the oil content floating separation means and the solid content settling separation means can be used in combination by the storage tank 11A of the purification device 3A, it is advantageous for space saving. Since the fraction S and the primary treated water can be easily separated, it is advantageous for simplifying the apparatus configuration.

さらに、汚水処理装置1Aでは、浄化装置3Aで得られた一次処理水中の残存夾雑物を固液分離装置5によって物理的に分離除去しているので、後段の膜分離装置9に与える負荷を低減できる。   Furthermore, in the sewage treatment apparatus 1A, the residual contaminants in the primary treated water obtained by the purification apparatus 3A are physically separated and removed by the solid-liquid separation apparatus 5, thereby reducing the load applied to the membrane separation apparatus 9 at the subsequent stage. it can.

さらに、本実施形態に係る可溶化手段は、貯留槽11Aの槽本体15Aの底部21、及び側壁25によって形成されるため、沈降堆積された粗大固形分Sを可溶化のために滞留させる構成を簡単に実現できる。
(第2実施形態に係る汚水処理装置)
Furthermore, since the solubilization means according to the present embodiment is formed by the bottom portion 21 of the tank body 15A of the storage tank 11A and the side wall 25, a configuration in which the coarse solid content S that has been deposited is retained for solubilization. Easy to implement.
(Sewage treatment apparatus according to the second embodiment)

次に、図6を参照して第2実施形態に係る汚水処理装置1Bについて説明する。なお、第2実施形態に係る汚水処理装置1Bと第1実施形態に係る汚水処理装置1Aとの実質的な相違点は浄化装置3Bのみであるため、以下の説明では、第2実施形態に係る浄化装置3Bを中心に説明する。また、浄化装置3Bは、第1実施形態に係る浄化装置3Aと同様の要素、または構造を備えているため、同様の要素や構造には、同一の符号を付して詳しい説明は省略する。   Next, the sewage treatment apparatus 1B according to the second embodiment will be described with reference to FIG. In addition, since the substantial difference between the sewage treatment apparatus 1B according to the second embodiment and the sewage treatment apparatus 1A according to the first embodiment is only the purification apparatus 3B, the following description relates to the second embodiment. The purification device 3B will be mainly described. Moreover, since the purification apparatus 3B includes the same elements or structures as the purification apparatus 3A according to the first embodiment, the same elements and structures are denoted by the same reference numerals and detailed description thereof is omitted.

浄化装置3Bは、油分浮上分離手段、固形分沈降分離手段、及び可溶化手段として機能する汚水の貯留槽11Bを備えている。貯留槽11Bは、汚水を受け入れる導入管(導入部)13と、汚水を蓄える槽本体15Bと、槽本体15Bから処理水(以下、「一次処理水」という)を排出する排出管(排出部)17とを備えている。   The purification device 3B is provided with a sewage storage tank 11B that functions as an oil content floating separation means, a solid content sedimentation separation means, and a solubilization means. The storage tank 11B includes an introduction pipe (introduction section) 13 that receives sewage, a tank body 15B that stores sewage, and a discharge pipe (discharge section) that discharges treated water (hereinafter referred to as “primary treated water”) from the tank body 15B. 17.

槽本体15Bは、仕切壁19,20によって上流室15a、中間室15b、及び下流室15cの三つ(複数)の貯留室に区画されており、槽本体15の底部24は、仕切壁19,20によって上流室15a、中間室15b、及び下流室15cそれぞれの底部24a,24b,24cとして区切られている。また、上流室15aと中間室15bとを区画する第1の仕切壁19には、上流室15aと中間室15bとを連通する連通孔22が形成されている。また、中間室15bと下流室15cとを区画する第2の仕切壁20には、中間室15bと下流室15cとを連通する連通孔23が形成されている。連通孔22,23は、底部24よりも上方の位置に形成されている。   The tank main body 15B is divided into three (plural) storage chambers of the upstream chamber 15a, the intermediate chamber 15b, and the downstream chamber 15c by the partition walls 19 and 20, and the bottom 24 of the tank main body 15 includes the partition wall 19, 20 is divided into bottom portions 24a, 24b, and 24c of the upstream chamber 15a, the intermediate chamber 15b, and the downstream chamber 15c, respectively. The first partition wall 19 that divides the upstream chamber 15a and the intermediate chamber 15b is formed with a communication hole 22 that communicates the upstream chamber 15a and the intermediate chamber 15b. The second partition wall 20 that divides the intermediate chamber 15b and the downstream chamber 15c is formed with a communication hole 23 that communicates the intermediate chamber 15b and the downstream chamber 15c. The communication holes 22 and 23 are formed at positions above the bottom 24.

汚水を受け入れる導入管(導入部)13は、上流室15aに設けられている。また、処理水を排出する排出管(排出部)17は、上流室15aとは別である下流室15cに設けられている。   An introduction pipe (introduction section) 13 for receiving sewage is provided in the upstream chamber 15a. In addition, a discharge pipe (discharge unit) 17 that discharges the treated water is provided in a downstream chamber 15c that is different from the upstream chamber 15a.

汚水は、導入管13を介して槽本体15の上流室15aに導入され、連通孔22,23を抜けながら中間室15b、及び下流室15cの順番で緩やかに流れ、その過程で静置状態に保持される。その際に、汚水中の油脂分Fは上流室15a、中間室15b、及び下流室15cそれぞれで浮上分離され、また、粗大固形分Sも沈降分離される。なお、上流室15a、中間室15b、及び下流室15cそれぞれで生成される油層、及び沈降分離層は、上流室15aで最も厚くなり、下流室15cで最も薄くなる。   The sewage is introduced into the upstream chamber 15a of the tank body 15 through the introduction pipe 13, and gently flows in the order of the intermediate chamber 15b and the downstream chamber 15c while passing through the communication holes 22 and 23, and is left stationary in the process. Retained. At that time, the oil and fat F in the sewage is levitated and separated in each of the upstream chamber 15a, the intermediate chamber 15b, and the downstream chamber 15c, and the coarse solid component S is also separated by sedimentation. Note that the oil layer and the sedimentation separation layer generated in each of the upstream chamber 15a, the intermediate chamber 15b, and the downstream chamber 15c are thickest in the upstream chamber 15a and thinnest in the downstream chamber 15c.

槽本体15Bは、汚水から沈降分離された粗大固形分Sが堆積する底部24と、底部24の周縁に沿って立設されると共に、粗大固形分Sを保持する側壁25とを有する。底部24と側壁25とは可溶化手段として機能し、汚水から沈降分離された粗大固形分Sは、底部24及び側壁25によって保持され、所定時間保持される。   The tank body 15 </ b> B includes a bottom 24 on which the coarse solid S precipitated and separated from the sewage is deposited, and a side wall 25 that stands along the periphery of the bottom 24 and holds the coarse solid S. The bottom 24 and the side wall 25 function as a solubilizing means, and the coarse solid content S settled and separated from the sewage is held by the bottom 24 and the side wall 25 and held for a predetermined time.

なお、貯留槽11Bを可溶化手段として実現させるためには、粗大固形分Sの滞留時間が、1時間以上で、且つ24時間以下となるように設計し、さらに、望ましくは、滞留時間が、2時間以上で、且つ8時間以下となるように設計する必要がある。   In order to realize the storage tank 11B as a solubilizing means, the residence time of the coarse solid content S is designed to be 1 hour or more and 24 hours or less. It is necessary to design for 2 hours or more and 8 hours or less.

貯留槽11Bの特に槽本体15Bの可溶化手段としての機能により、粗大固形分S中の有機物成分が溶出された一次処理水は、排出管17から排出され、移送管を備えた一次処理水排出ライン27を通って固液分離装置5に供給される。   Due to the function of the storage tank 11B as a solubilizing means, in particular, the tank body 15B, the primary treated water from which the organic components in the coarse solids S are eluted is discharged from the discharge pipe 17, and the primary treated water discharged with the transfer pipe is discharged. It is supplied to the solid-liquid separator 5 through the line 27.

第2実施形態に係る汚水処理装置1Bによれば、第1の実施形態に係る汚水処理装置1Aと同様の効果、つまり、膜分離装置9に過負荷を与える油脂分F、及び固形分Sは、前段の浄化装置3Bにおいて除去される。さらに、浄化装置3Bは、固形分沈降分離手段、及び可溶化手段として機能する貯留槽11Cを備えており、生物処理装置7において窒素化合物、及びリン化合物を生物学的に除去する上で必要となる有機物成分を粗大固形分Sの可溶化によって補うことができる。その結果として、生物処理装置7と膜分離装置9とを併用することで有機汚濁物、窒素化合物、及びリン化合物を効果的に除去すると共に、膜分離装置9の負荷を低減して高品質の再生水を安定的に得ることができる。   According to the sewage treatment apparatus 1B according to the second embodiment, the same effect as that of the sewage treatment apparatus 1A according to the first embodiment, that is, the oil and fat F and the solid content S that give an overload to the membrane separation device 9 are It is removed in the purification device 3B in the previous stage. Furthermore, the purification device 3B includes a storage tank 11C that functions as a solid sedimentation separation unit and a solubilization unit, and is necessary for biologically removing nitrogen compounds and phosphorus compounds in the biological treatment device 7. The organic component can be supplemented by solubilization of the coarse solid S. As a result, by using the biological treatment device 7 and the membrane separation device 9 together, organic pollutants, nitrogen compounds, and phosphorus compounds are effectively removed, and the load on the membrane separation device 9 is reduced, resulting in high quality. Reclaimed water can be obtained stably.

さらに、第2実施形態に係る汚水処理装置1Bによれば、貯留槽11Bの槽本体15Bが仕切壁19,20で区切られているので、汚水W中の残存夾雑物の除去を期待でき、後段に配置している固液分離装置5への負荷を低減できる。   Furthermore, according to the sewage treatment apparatus 1B according to the second embodiment, since the tank main body 15B of the storage tank 11B is partitioned by the partition walls 19 and 20, it is possible to expect the removal of residual impurities in the sewage W, and the subsequent stage It is possible to reduce the load on the solid-liquid separation device 5 arranged in the above.

さらに、浄化装置3Bの導入管13は、排出管17が設けられた下流室15cとは別の貯留室である上流室15aに設けられているので、下流室15cでは、導入管13から導入される汚水の流れに影響され難くなり、従って、下流室15cでは汚水を静置状態に保持し易くなる。
(第3実施形態に係る汚水処理装置)
Further, since the introduction pipe 13 of the purification device 3B is provided in the upstream chamber 15a which is a storage chamber different from the downstream chamber 15c in which the discharge pipe 17 is provided, the introduction pipe 13 is introduced from the introduction pipe 13 in the downstream chamber 15c. Therefore, it becomes difficult to be influenced by the flow of sewage, and thus it is easy to keep the sewage in a stationary state in the downstream chamber 15c.
(Sewage treatment apparatus according to the third embodiment)

次に、図7を参照して第3実施形態に係る汚水処理装置1Cについて説明する。なお、第3実施形態に係る汚水処理装置1Cと第1、第2実施形態に係る汚水処理装置1A,1Bとの実質的な相違点は浄化装置3Cのみであるため、以下の説明では、第3実施形態に係る浄化装置3Cを中心に説明する。また、浄化装置3Cは、第1、第2実施形態に係る浄化装置3A,3Bと同様の要素、または構造を備えているため、同様の要素や構造には、同一の符号を付して詳しい説明は省略する。   Next, a wastewater treatment apparatus 1C according to the third embodiment will be described with reference to FIG. The substantial difference between the sewage treatment apparatus 1C according to the third embodiment and the sewage treatment apparatuses 1A and 1B according to the first and second embodiments is only the purification apparatus 3C. The purification device 3C according to the third embodiment will be mainly described. Moreover, since the purification device 3C includes the same elements or structures as the purification devices 3A and 3B according to the first and second embodiments, the same elements and structures are denoted by the same reference numerals and detailed. Description is omitted.

浄化装置3Cは、油分浮上分離手段、固形分沈降分離手段、及び可溶化手段としての機能を有する汚水の貯留槽11Cを備えている。貯留槽11Cは、汚水を受け入れる導入管(導入部)13と、汚水を蓄える槽本体15Cと、槽本体15Cから一次処理水を排出する排出管(排出部)17とを備えている。   The purification device 3C includes a sewage storage tank 11C having functions as an oil content floating separation means, a solid content sedimentation separation means, and a solubilization means. The storage tank 11C includes an introduction pipe (introduction section) 13 that receives sewage, a tank body 15C that stores sewage, and a discharge pipe (discharge section) 17 that discharges primary treated water from the tank body 15C.

槽本体15Cは、仕切壁55によって上流室15a、及び下流室15cの二つ(複数)の貯留室に区画されており、槽本体15Cの底部57は、仕切壁55によって上流室15a、及び下流室15cそれぞれの底部57a,57bとして区切られている。また、上流室15aと下流室15cとを区画する仕切壁55には、上流室15aと下流室15cとを連通する連通孔59が形成されている。   The tank body 15C is divided into two (a plurality of) storage chambers, that is, an upstream chamber 15a and a downstream chamber 15c by a partition wall 55. The bottom portion 57 of the tank body 15C is separated from the upstream chamber 15a and the downstream by the partition wall 55. The chambers 15c are divided as bottom portions 57a and 57b. The partition wall 55 that partitions the upstream chamber 15a and the downstream chamber 15c is formed with a communication hole 59 that communicates the upstream chamber 15a and the downstream chamber 15c.

貯留槽11Cの槽本体15Cでは、導入管13からの汚水が上流室15aに導入され、さらに、連通孔59を抜けながら下流室15cに向けて緩やかに流れ、その過程で静置状態に保持される。その際に、汚水中の油脂分Fは上流室15a、及び下流室15cそれぞれで浮上分離され、また、粗大固形分Sは沈降分離される。なお、上流室15a、及び下流室15cそれぞれで生成される油層、及び沈降分離層は、上流室15aで最も厚くなり、下流室15cで最も薄くなる。   In the tank body 15C of the storage tank 11C, the sewage from the introduction pipe 13 is introduced into the upstream chamber 15a, and further gently flows toward the downstream chamber 15c while passing through the communication hole 59, and is kept stationary in the process. The At that time, the oil and fat F in the sewage is floated and separated in the upstream chamber 15a and the downstream chamber 15c, respectively, and the coarse solid S is settled and separated. The oil layer and the sedimentation separation layer generated in the upstream chamber 15a and the downstream chamber 15c are the thickest in the upstream chamber 15a and the thinnest in the downstream chamber 15c.

槽本体15Cは、可溶化手段を形成する底部57、及び側壁25を備えている。可溶化手段により、粗大固形分S中の有機物成分が溶出された一次処理水は、排出管17から排出され、移送管を備えた一次処理水排出ライン27を通って固液分離装置5に供給される。   The tank body 15C includes a bottom portion 57 that forms a solubilizing means, and a side wall 25. The primary treated water from which the organic component in the coarse solid S is eluted by the solubilizing means is discharged from the discharge pipe 17 and supplied to the solid-liquid separation device 5 through the primary treated water discharge line 27 provided with a transfer pipe. Is done.

本実施形態に係る汚水処理装置1Cによれば、第1、または第2の実施形態に係る汚水処理装置1A,1Bと同様の効果、つまり、膜分離装置9に過負荷を与える油脂分F、及び固形分Sが、前段の浄化装置3Bにおいて除去されるという効果を奏する。さらに、浄化装置3Cは、固形分沈降分離手段、及び可溶化手段として機能する貯留槽11Cを備えており、生物処理装置7において窒素化合物、及びリン化合物を生物学的に除去する上で必要となる有機物成分を粗大固形分Sの可溶化によって補うことができる。その結果として、生物処理装置7と膜分離装置9とを併用することで有機汚濁物、窒素化合物、及びリン化合物を効果的に除去すると共に、膜分離装置9の負荷を低減して高品質の再生水を安定的に得ることができる。   According to the sewage treatment apparatus 1C according to the present embodiment, the same effect as the sewage treatment apparatuses 1A and 1B according to the first or second embodiment, that is, the oil and fat content F that overloads the membrane separation apparatus 9, In addition, the solid content S is removed by the purification device 3B in the previous stage. Furthermore, the purification device 3C includes a storage tank 11C that functions as a solids sedimentation separation unit and a solubilization unit, and is necessary for biologically removing nitrogen compounds and phosphorus compounds in the biological treatment device 7. The organic component can be supplemented by solubilization of the coarse solid S. As a result, by using the biological treatment device 7 and the membrane separation device 9 together, organic pollutants, nitrogen compounds, and phosphorus compounds are effectively removed, and the load on the membrane separation device 9 is reduced, resulting in high quality. Reclaimed water can be obtained stably.

さらに、第3実施形態に係る汚水処理装置1Cによれば、貯留槽11Cの槽本体15Cが仕切壁55で区切られているので、汚水W中の残存夾雑物の除去を期待でき、後段に配置している固液分離装置5への負荷を低減できる。   Furthermore, according to the sewage treatment apparatus 1C according to the third embodiment, since the tank body 15C of the storage tank 11C is partitioned by the partition wall 55, it can be expected to remove the remaining contaminants in the sewage W, and is disposed in the subsequent stage. It is possible to reduce the load on the solid-liquid separator 5 that is being operated.

さらに、浄化装置3Cの導入管13は、排出管17が設けられた下流室15cとは別の貯留室である上流室15aに設けられているので、下流室15cでは、導入管13から導入される汚水の流れに影響され難くなり、従って、下流室15cでは汚水を静置状態に保持し易くなる。   Furthermore, since the introduction pipe 13 of the purification device 3C is provided in the upstream chamber 15a which is a storage chamber different from the downstream chamber 15c in which the discharge pipe 17 is provided, the introduction pipe 13 is introduced from the introduction pipe 13 in the downstream chamber 15c. Therefore, it becomes difficult to be influenced by the flow of sewage, and thus it is easy to keep the sewage in a stationary state in the downstream chamber 15c.

以下に実施例を挙げて、本実施の形態をさらに具体的に説明するが、本発明の範囲は以下の実施例のみに限定されるものではない。
[実施例]
Hereinafter, the present embodiment will be described more specifically with reference to examples. However, the scope of the present invention is not limited to the following examples.
[Example]

下記水質の原水(汚水)を、上述の第1実施形態に係る汚水処理装置(図2参照)によって処理した。
(原水水質:浄化装置による浄化前)
溶解性BOD:100mg/L
T−P:4mg/L
T−N:37mg/L
Raw water (sewage) having the following water quality was treated by the sewage treatment apparatus (see FIG. 2) according to the first embodiment described above.
(Raw water quality: before purification by purification equipment)
Solubility BOD: 100mg / L
TP: 4 mg / L
TN: 37 mg / L

原水流量、各槽の滞留時間、汚泥混合液返送量等の処理条件は以下の通りとした。
(処理条件)
The processing conditions such as the raw water flow rate, the residence time of each tank, and the sludge mixed liquid return amount were as follows.
(Processing conditions)

原水流量 :15m/hr
浄化装置滞留時間 :8hr
嫌気槽滞留時間 :1.5hr
無酸素槽滞留時間 :3hr
好気槽滞留時間 :4hr
汚泥混合液の嫌気槽への返送量 :15m/hr
汚泥混合液の無酸素槽への返送量 :30m/hr
嫌気槽中活性汚泥濃度 :5,000mg/L
無酸素槽中活性汚泥濃度 :7,500mg/L
好気槽中活性汚泥濃度 :10,000mg/L
なお、分離膜には中空糸MF膜モジュール(旭化成ケミカルズ(株) マイクローザMUNC−620A)を用いた。
[比較例]
Raw water flow rate: 15m 3 / hr
Purification device residence time: 8 hr
Anaerobic tank residence time: 1.5 hr
Oxygen tank retention time: 3 hr
Aerobic tank residence time: 4 hr
Return amount of sludge mixture to anaerobic tank: 15 m 3 / hr
Return amount of sludge mixture to oxygen-free tank: 30m 3 / hr
Activated sludge concentration in anaerobic tank: 5,000 mg / L
Activated sludge concentration in anoxic tank: 7,500 mg / L
Activated sludge concentration in the aerobic tank: 10,000 mg / L
A hollow fiber MF membrane module (Asahi Kasei Chemicals Corporation Microza MUNC-620A) was used as the separation membrane.
[Comparative example]

浄化装置を設けない以外は、上述の本実施例と同様の構成として、本実施例と同じ条件で実験を行った。生物処理装置7へ流入する一次処理水は集合住宅・工場から出る原水(汚水)と同じである。浄化装置を有する本実施例と、浄化装置が無い比較例による原水水質、最終処理水質(膜分離装置で得られた再生水)の比較を表1に示した。表1に示されるように、本実施例では浄化装置を経由することで原水(汚水)に対して、生物処理装置7に流入する一次処理水中の溶解性BOD、T−N、T−Pの濃度がいずれも高くなる。これは浄化装置により糞塊等の固形分からBOD、T−N、T−Pが溶出した為である。それにより、比較例に比べ、本実施例では、BOD:T−N:T−Pの比率が生物処理を行う適正条件になるように原水水質が調整され、伴って最終処理水のT−N:T−Pの濃度が低下していることが分かる。本汚水処理装置による生物処理性の向上効果が確認できた。   An experiment was conducted under the same conditions as in this example, except that no purification device was provided, with the same configuration as in this example. The primary treated water flowing into the biological treatment apparatus 7 is the same as the raw water (sewage) coming out of the apartment house / factory. Table 1 shows a comparison of the raw water quality and the final treated water quality (reclaimed water obtained by the membrane separation device) according to the present example having the purification device and the comparative example without the purification device. As shown in Table 1, in this embodiment, the soluble BOD, TN, and TP in the primary treated water flowing into the biological treatment device 7 with respect to the raw water (sewage) by passing through the purification device. Both concentrations are high. This is because BOD, TN, and TP were eluted from the solids such as feces by the purification device. Thereby, compared with a comparative example, in a present Example, raw | natural water quality is adjusted so that the ratio of BOD: TN: TP may become an appropriate condition for performing biological treatment, and TN of final treated water is accompanied by it. : It turns out that the density | concentration of TP is falling. The biological treatment improvement effect by this sewage treatment equipment was confirmed.

Figure 2013000670
Figure 2013000670

1A,1B,1C…汚水処理装置、3A,3B,3C…浄化装置、5…固液分離手段、7…生物処理装置、9…膜分離装置、11A,11B,11C…貯留槽(油分浮上分離手段、固形分沈降分離手段、可溶化手段)、13…導入管(浄化装置の導入部)、15A,15B,15C…槽本体、15a…上流室(貯留室)、15c…下流室(貯留室)、17…排出管(浄化装置の排出部)、19,20,55…仕切壁、21,24,57…底部(槽本体の底部)、22,23,59…連通孔、25…側壁。   DESCRIPTION OF SYMBOLS 1A, 1B, 1C ... Sewage treatment device, 3A, 3B, 3C ... Purification device, 5 ... Solid-liquid separation means, 7 ... Biological treatment device, 9 ... Membrane separation device, 11A, 11B, 11C ... Reservoir Means, solids sedimentation and separation means, solubilization means), 13 ... introduction pipe (introduction part of the purification device), 15A, 15B, 15C ... tank body, 15a ... upstream chamber (reservoir chamber), 15c ... downstream chamber (reservoir chamber) ), 17 ... discharge pipe (discharge part of the purifier), 19, 20, 55 ... partition wall, 21, 24, 57 ... bottom (bottom part of the tank body), 22, 23, 59 ... communication holes, 25 ... side walls.

Claims (8)

下水道幹線に向かって流れる汚水の一部を受け入れて浄化処理する浄化装置と、
前記浄化装置で得られた処理水から、有機汚濁物、窒素化合物、及びリン化合物を生物学的に除去する生物処理装置と、
前記生物処理装置で得られた生物処理水から濁質を分離除去して再生水を得る膜分離装置と、を備え、
前記浄化装置は、前記汚水中の油分を浮上分離する油分浮上分離手段と、前記汚水中の固形分を沈降分離する固形分沈降分離手段と、前記固形分沈降分離手段で沈降分離された固形分を滞留させて可溶化する可溶化手段と、を有することを特徴とする汚水処理装置。
A purification device that receives and purifies a part of the sewage flowing toward the sewer main line, and
A biological treatment apparatus for biologically removing organic pollutants, nitrogen compounds, and phosphorus compounds from the treated water obtained by the purification apparatus;
A membrane separation device for separating and removing turbidity from the biological treatment water obtained by the biological treatment device to obtain reclaimed water,
The purifying apparatus includes an oil flotation separating unit that floats and separates an oil component in the wastewater, a solid sedimentation separation unit that settles and separates a solid component in the wastewater, and a solid content that has been settled and separated by the solids sedimentation separation unit. And a solubilizing means for solubilizing and solubilizing the wastewater treatment apparatus.
前記可溶化手段での前記汚水の滞留時間は、1時間以上で、且つ24時間以下であることを特徴とする請求項1記載の汚水処理装置。   The sewage treatment apparatus according to claim 1, wherein a residence time of the sewage in the solubilizing means is 1 hour or more and 24 hours or less. 前記可溶化手段での前記汚水の滞留時間は、2時間以上で、且つ8時間以下であることを特徴とする請求項1記載の汚水処理装置。   The sewage treatment apparatus according to claim 1, wherein a residence time of the sewage in the solubilizing means is 2 hours or more and 8 hours or less. 前記浄化装置で得られた前記処理水中の残存夾雑物を物理的に分離除去し、前記残存夾雑物を除去した処理水を前記生物処理装置に供給する固液分離装置を更に備えることを特徴とする請求項1〜3のいずれか一項記載の汚水処理装置。   Further comprising a solid-liquid separation device that physically separates and removes the residual impurities in the treated water obtained by the purification device, and supplies the treated water from which the residual impurities have been removed to the biological treatment device. The sewage treatment apparatus according to any one of claims 1 to 3. 前記浄化装置は、前記油分浮上分離手段、及び前記固形分沈降分離手段として機能する前記汚水の貯留槽を有し、
前記貯留槽は、前記汚水を受け入れる導入部と、前記汚水を静置状態に保持して前記汚水から前記油分を浮上分離すると共に、前記汚水から前記固形分を沈降分離する槽本体と、前記油分、及び前記固形分が分離された前記処理水を前記槽本体から排出する排出部と、を有することを特徴とする請求項1〜4のいずれか一項記載の汚水処理装置。
The purification device has the oil levitation separation means and the sewage storage tank functioning as the solids sedimentation separation means,
The storage tank includes an introduction part that receives the wastewater, a tank main body that floats and separates the oil from the wastewater while holding the wastewater in a stationary state, and sinks and separates the solid from the wastewater, and the oil And a discharge section for discharging the treated water from which the solid content has been separated from the tank body.
前記槽本体は、沈降する前記固形分が堆積する底部と、前記底部の周縁に沿って立設されると共に、前記固形分を保持する側壁とを有し、
前記可溶化手段は、前記固形分を滞留させる前記底部、及び前記側壁によって形成されることを特徴とする請求項5記載の汚水処理装置。
The tank body has a bottom portion on which the solid content that settles and a side wall that is erected along the periphery of the bottom portion and holds the solid content,
6. The sewage treatment apparatus according to claim 5, wherein the solubilizing means is formed by the bottom part for retaining the solid content and the side wall.
前記貯留槽は、前記槽本体を区切る仕切壁と、前記仕切壁を挟んで隣接する貯留室同士を連通する連通孔と、を有することを特徴とする請求項5または6記載の汚水処理装置。   The sewage treatment apparatus according to claim 5 or 6, wherein the storage tank includes a partition wall that divides the tank main body, and a communication hole that connects adjacent storage chambers with the partition wall interposed therebetween. 前記導入部は、前記仕切壁によって区切られた複数の前記貯留室のうち、いずれか一つの前記貯留室に設けられ、前記排出部は、複数の前記貯留室のうち、前記導入部が設けられた前記貯留室とは別の前記貯留室に設けられていることを特徴とする請求項7記載の汚水処理装置。   The introduction portion is provided in any one of the storage chambers divided by the partition wall, and the discharge portion is provided with the introduction portion of the plurality of storage chambers. The sewage treatment apparatus according to claim 7, wherein the sewage treatment apparatus is provided in the storage chamber different from the storage chamber.
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