JP2008000720A - Purification apparatus - Google Patents

Purification apparatus Download PDF

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JP2008000720A
JP2008000720A JP2006174473A JP2006174473A JP2008000720A JP 2008000720 A JP2008000720 A JP 2008000720A JP 2006174473 A JP2006174473 A JP 2006174473A JP 2006174473 A JP2006174473 A JP 2006174473A JP 2008000720 A JP2008000720 A JP 2008000720A
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purification
filtration
chamber
tank
water
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JP4647553B2 (en
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Ryoichi Okamoto
良一 岡本
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Eiwa Kokudo Kankyo Kk
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Eiwa Kokudo Kankyo Kk
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a purification apparatus which can be miniaturized while ensuring purifying performance. <P>SOLUTION: The purification apparatus is equipped with a purification tank 10 having a plurality of purification chambers 2-8 for stepwisely purifying dirt-containing domestic wastewater of a toilet 50 and the like, and wastewater from a factory, a hotel, a hospital, etc., and a filtration tank 20 for filtering the above wastewater. A plurality of the purification chambers comprises an adsorption chamber 8 with an adsorbent 8d for adsorbing and removing suspension and the like in the wastewater. The filtration tank 20 comprises a suction means 21 connected to one purification chamber 5 among the purification chambers, installed upstream of the adsorption chamber 8, and sucking treated water in the purification chamber 5, a filter tank 22 having a filter medium 24, and filtering the sucked treated water, and a returning means 23 for returning the filtered treated water to the purification chamber 5 upstream of the adsorption chamber 8. The treated water in the purification chamber 5 is filtered repeatedly by the filtration tank 20. <P>COPYRIGHT: (C)2008,JPO&INPIT

Description

本発明は、汚泥成分を含有するトイレ等の家庭排水や工場、ホテル、病院等からの排水を浄化処理する浄化装置に関するものである。   The present invention relates to a purification device for purifying household wastewater such as toilets containing sludge components and wastewater from factories, hotels, hospitals and the like.

従来、前記浄化装置としては、沈殿分離室や接触ばっ気槽等を有した合併浄化槽が用いられており、特許文献2には、この合併浄化槽の下流に砂ろ過装置を設け、さらにその下流に膜分離装置等を設けた浄化装置が開示されている。この浄化装置では、合併浄化槽から排出される浄化水を砂ろ過装置に導入してろ過した後、その処理水を膜分離装置等に導入して浄化処理している。
特開2003−126893号公報
Conventionally, a combined septic tank having a precipitation separation chamber, a contact aeration tank, and the like is used as the clarifier, and in Patent Document 2, a sand filter is provided downstream of the combined septic tank, and further downstream thereof. A purification device provided with a membrane separation device or the like is disclosed. In this purification device, purified water discharged from the combined septic tank is introduced into a sand filtration device and filtered, and then the treated water is introduced into a membrane separation device and the like for purification treatment.
JP 2003-126893 A

前記の浄化装置は、合併浄化槽から排出された浄化水を砂ろ過装置に導入し、砂ろ過装置でろ過処理された処理水を下流の膜分離装置等に導出するというものであり、砂ろ過装置におけるろ過処理は1回しかなされない。そのため、大量の排水を処理する場合には、砂ろ過装置を大型化する必要がありコストがかかってしまうという問題がある。   The purification device introduces the purified water discharged from the combined septic tank into the sand filtration device, and guides the treated water filtered by the sand filtration device to a downstream membrane separation device, etc. The filtration process in is performed only once. Therefore, when processing a large amount of waste water, there is a problem that it is necessary to increase the size of the sand filtration device, which increases costs.

本発明は前記の点に鑑みてなされたものであり、ろ過装置を小型化することで省スペース化を図りつつ浄化性能を確保することのできる浄化装置を提供することを目的とする。   This invention is made | formed in view of the said point, and it aims at providing the purification apparatus which can ensure purification performance, aiming at space saving by reducing the size of a filtration apparatus.

前記課題を解決するために、本発明は、汚泥成分を含有するトイレ等の家庭排水や工場、ホテル、病院等からの排水を段階的に浄化する複数の浄化処理室を有する浄化処理槽と、前記排水をろ過処理するろ過処理槽とを有し、前記複数の浄化処理室が、前記排水中の浮遊物等を吸着除去する吸着材を有する吸着処理室を備えるとともに、前記ろ過処理槽が、前記浄化処理室のうち前記吸着処理室の上流に設けられた浄化処理室に連結されて、この浄化処理室内の処理水を吸引する吸引手段と、ろ材を有し前記吸引された処理水をろ過するろ過槽と、当該ろ過された処理水を前記吸着処理室の上流の浄化処理室に還流させる還流手段とを備え、このろ過処理槽によって、前記浄化処理室の処理水が繰り返しろ過されることを特徴とする浄化装置を提供する。   In order to solve the above-mentioned problems, the present invention provides a purification treatment tank having a plurality of purification treatment chambers for stepwise purification of domestic wastewater such as toilets containing sludge components and wastewater from factories, hotels, hospitals, etc. A filtration tank for filtering the waste water, and the plurality of purification treatment chambers include an adsorption treatment chamber having an adsorbent for adsorbing and removing suspended matters in the waste water, and the filtration tank. A suction unit that is connected to a purification treatment chamber provided upstream of the adsorption treatment chamber in the purification treatment chamber and sucks the treated water in the purification treatment chamber, and has a filter medium to filter the sucked treatment water. And a reflux means for refluxing the filtered treated water to the purification treatment chamber upstream of the adsorption treatment chamber, and the treated water in the purification treatment chamber is repeatedly filtered by the filtration treatment vessel. Purification device characterized by To provide.

このような構成によれば、吸着処理室の上流に設けられた浄化処理室の処理水が繰り返しろ過処理されるので、ろ過処理槽を大型化せずに処理水中の浮遊物等を十分に除去することができるとともに、吸着処理室に設けられる吸着材が目詰まりするのを抑止することができる。さらに、ろ材に付着した微生物と処理水が繰り返し接触することで、処理水中の有機性浮遊物等の微生物による分解処理が促進されるので、浄化性能を高めることができる。   According to such a configuration, since the treated water in the purification treatment chamber provided upstream of the adsorption treatment chamber is repeatedly filtered, the suspended matter in the treated water is sufficiently removed without increasing the size of the filtration tank. It is possible to prevent clogging of the adsorbent provided in the adsorption processing chamber. Furthermore, since the microorganisms adhering to the filter medium and the treated water repeatedly come into contact with each other, the decomposition treatment by microorganisms such as organic suspended solids in the treated water is promoted, so that the purification performance can be improved.

また本発明において、前記吸着処理室が、前記吸着材として活性炭収容体を有するのが好ましい。   In the present invention, it is preferable that the adsorption treatment chamber has an activated carbon container as the adsorbent.

このような構成によれば、活性炭収容体の目詰まりを抑止でき、比較的高価な活性炭のランニングコストを低く抑えることが可能になる。   According to such a configuration, clogging of the activated carbon container can be suppressed, and the running cost of the relatively expensive activated carbon can be kept low.

また本発明において、前記ろ過処理槽が、前記ろ材に付着した浮遊物等を除去するための逆洗水として、外部から水道水等を前記ろ過槽に導入するための逆洗水導入口を有するのが好ましい。   Moreover, in this invention, the said filtration tank has a backwash water inlet for introducing tap water etc. into the said filtration tank from the outside as backwash water for removing the floating substance adhering to the said filter medium, etc. Is preferred.

このような構成によれば、逆洗水導入口から水道水等を逆洗水として導入してろ材を逆洗することで、ろ材の処理能力を確保してろ材を繰り返し使用することが可能になる。   According to such a configuration, by introducing tap water or the like as backwash water from the backwash water introduction port and backwashing the filter medium, it is possible to ensure the processing capacity of the filter medium and repeatedly use the filter medium. Become.

また本発明において、前記ろ過処理槽が、前記ろ過槽の下流側の圧力を検出する圧力検出手段と、当該圧力検出手段の検出結果に基づいて、前記逆洗水導入口から逆洗水を導入するタイミングあるいは導入する逆洗水の量を制御する制御手段とを有するのが好ましい。   In the present invention, the filtration tank introduces backwash water from the backwash water inlet based on the pressure detection means for detecting the pressure on the downstream side of the filtration tank and the detection result of the pressure detection means. And control means for controlling the amount of backwash water to be introduced.

前記ろ材に処理水中の浮遊物が付着して閉塞すると、ろ過槽の下流側圧力は低下する。従って、この下流側圧力を検出してやれば、ろ材の閉塞具合を判断することができるので、この検出結果に基づいて逆洗水を導入するタイミングや導入する逆洗水の量を制御してやれば、適切なタイミングで効率よくろ材を逆洗することが可能になる。   When suspended matter in the treated water adheres to and clogs the filter medium, the downstream pressure of the filtration tank decreases. Therefore, if this downstream pressure is detected, the degree of blocking of the filter medium can be determined. Therefore, if the timing of introducing the backwash water and the amount of backwash water to be introduced are controlled based on this detection result, it is appropriate. It is possible to backwash the filter medium efficiently at an appropriate timing.

また本発明において、前記複数の浄化処理室のうち最下流の位置に、前記排水から生成された浄化水を貯留可能な浄化水貯留室が設けられるとともに、前記ろ過処理槽が、前記逆洗水導入口に接続されて、前記浄化水貯留室に貯留された浄化水を前記ろ過槽に逆洗水として供給する浄化水供給手段を有するのが好ましい。   Moreover, in this invention, while the purified water storage chamber which can store the purified water produced | generated from the said waste_water | drain is provided in the most downstream position among these purification treatment chambers, the said filtration treatment tank is the said backwash water It is preferable to have purified water supply means connected to the inlet and supplying purified water stored in the purified water storage chamber to the filtration tank as backwash water.

このような構成によれば、浄化水貯留室に貯留される浄化水を逆洗水として利用することができるので、逆洗水として水道水等を利用する場合に比べてコスト面で有利になる。   According to such a configuration, since the purified water stored in the purified water storage chamber can be used as the backwash water, it is advantageous in terms of cost compared to the case where tap water or the like is used as the backwash water. .

また本発明において、前記ろ材を逆洗する際に生じる浮遊物等を含む処理水を、前記複数の浄化処理室のうち最上流に設けられた浄化処理室に導出する処理水導出手段を前記ろ過処理槽に設けるのが好ましい。   Further, in the present invention, the filtration of the treated water deriving means for deriving treated water containing suspended matters generated when the filter medium is backwashed to a purification treatment chamber provided in the uppermost stream among the plurality of purification treatment chambers. It is preferable to provide in a processing tank.

このような構成によれば、前記浮遊物等を浄化処理室内に還流して再処理することができ、浮遊物等を含む汚水が外部に流出するのを抑止することができる。   According to such a configuration, the suspended matter or the like can be recirculated into the purification treatment chamber and reprocessed, and sewage containing the suspended matter or the like can be prevented from flowing out.

また本発明において、前記ろ過処理槽としてろ材を砂や石とする砂ろ過装置を用いれば、処理水中のSSを効率よく除去することができる。   Moreover, in this invention, if the sand filtration apparatus which uses a filter medium as sand or a stone is used as the said filtration treatment tank, SS in treated water can be removed efficiently.

以上のように、本発明によれば汚泥成分を含有するトイレ等の家庭排水や工場、ホテル、病院等からの排水を、装置を大型化することなく効率よく浄化できる浄化装置を提供することができる。   As described above, according to the present invention, it is possible to provide a purification device that can efficiently purify domestic wastewater such as toilets containing sludge components and wastewater from factories, hotels, hospitals, etc. without increasing the size of the device. it can.

図1よび図2は、本発明に係る浄化装置の実施形態を示している。   1 and 2 show an embodiment of a purification device according to the present invention.

この浄化装置1は、複数の浄化処理室2〜8を有する浄化処理槽10と、ろ過処理槽20とを備えている。この浄化処理槽10は、鋼板材、アルミニウム合金材、ステンレス鋼材、プラスチック材、PC(プレストレスコンクリート)材、鉄筋コンクリート材、FRP(繊維強化プラスチック)材またはプラスチック材等からなり、地中に埋設され、あるいは地上に立設された状態で使用されるものである。また、浄化処理室2〜8は、上流側から、沈殿分離室2、接触ばっ気室3、沈殿室4、第一接触ろ過室5、第二接触ろ過室6、沈殿ろ過室7および浄化水貯留室8(吸着処理室)となっており、その上面には各々清掃または点検用の開口部30〜34が形成されている。さらに前記開口部30〜34を開閉可能に閉止する閉止蓋が設置されている。前記ろ過処理槽20は前記第一接触ろ過室5、沈殿分離室2および浄化水貯留室8に連設されている。   The purification device 1 includes a purification treatment tank 10 having a plurality of purification treatment chambers 2 to 8 and a filtration treatment tank 20. The purification treatment tank 10 is made of a steel plate material, an aluminum alloy material, a stainless steel material, a plastic material, a PC (prestressed concrete) material, a reinforced concrete material, an FRP (fiber reinforced plastic) material or a plastic material, and is buried in the ground. Or, it is used in a standing condition on the ground. Further, the purification treatment chambers 2 to 8 are, from the upstream side, the precipitation separation chamber 2, the contact aeration chamber 3, the precipitation chamber 4, the first contact filtration chamber 5, the second contact filtration chamber 6, the precipitation filtration chamber 7, and the purified water. It is a storage chamber 8 (adsorption processing chamber), and openings 30 to 34 for cleaning or inspection are formed on the upper surface thereof. Furthermore, a closing lid for closing the openings 30 to 34 so as to be opened and closed is provided. The filtration tank 20 is connected to the first contact filtration chamber 5, the precipitation separation chamber 2, and the purified water storage chamber 8.

最上流に設けられた沈殿分離室2には、配管11を介して水洗トイレ50や浴室等の排水口に連結されて、汚水等を導入する導入口2aが設けられている。そして、この沈殿分離室2は、導入された汚水中の紙および粗大異物等の汚泥成分を沈殿させて分離した後に、その処理水を下流の接触ばっ気室3にオーバーフローさせて導出するよう構成されている。また、沈殿分離室2にはバッフルプレート2bが設けられており、前記接触ばっ気室3に浮遊物が流出するのを阻止するように区画されている。なお、前記沈殿分離室2において沈殿した固形分は、定期的(例えば1年毎)に外部に吸い出されて処理される。   The sedimentation separation chamber 2 provided in the uppermost stream is provided with an introduction port 2 a that is connected to a drainage port of a flush toilet 50 or a bathroom via a pipe 11 and introduces sewage or the like. The sedimentation separation chamber 2 is configured to precipitate and separate the sludge components such as paper and coarse foreign matters in the introduced wastewater, and then overflow the treated water into the downstream contact aeration chamber 3 to lead out. Has been. Further, a baffle plate 2 b is provided in the sedimentation separation chamber 2 and is partitioned so as to prevent floating substances from flowing into the contact aeration chamber 3. The solid content precipitated in the precipitation separation chamber 2 is sucked out and processed regularly (for example, every year).

また、前記配管11には、後述するろ過処理槽20の処理水導出手段26が連結されており、ろ過処理槽20から導出される逆洗後の処理水が沈殿分離室2に導入されるよう構成されている。   Further, the pipe 11 is connected with a treated water deriving means 26 of a filtration tank 20 described later, so that the treated water after backwashing led out from the filtration tank 20 is introduced into the precipitation separation chamber 2. It is configured.

沈殿分離室2の下流に設けられた接触ばっ気室3には、従来周知のプラスチック製接触材3aが充填されるとともに、ブロア60から供給された空気を放出する散気管3bが前記プラスチック製接触材3aの下方に配設されている。そして、前記沈殿分離室2の上部からオーバーフローすることにより導入された処理水に含まれる汚泥成分が、散気管3bから放出された空気によって撹拌されて、前記プラスチック製接触材3aに付着して生息する微生物により分解処理されるように構成されている。   A contact aeration chamber 3 provided downstream of the sedimentation separation chamber 2 is filled with a conventionally known plastic contact material 3a, and an air diffuser 3b for releasing air supplied from the blower 60 is provided with the plastic contact. It is arranged below the material 3a. And the sludge component contained in the treated water introduced by overflowing from the upper part of the sedimentation separation chamber 2 is agitated by the air released from the air diffuser 3b, adheres to the plastic contact material 3a, and inhabits. It is configured to be decomposed by the microorganisms.

前記接触ばっ気室3で処理された処理水は、下方に設けられた連通路3cを介して沈殿室4に導入される。沈殿室4では、前記接触ばっ気室3から導入された処理水中に含まれる前記微生物のかたまり等が沈殿し、その処理水が連結管12を介して第一接触ろ過室5にオーバーフローするよう構成されている。   The treated water treated in the contact aeration chamber 3 is introduced into the sedimentation chamber 4 through the communication path 3c provided below. The sedimentation chamber 4 is configured such that the microbial mass contained in the treated water introduced from the contact aeration chamber 3 precipitates, and the treated water overflows to the first contact filtration chamber 5 via the connecting pipe 12. Has been.

第一接触ろ過室5内には、メッシュ状の袋体内にカキ、ホタテ貝、ホッキ貝、真珠貝、アサリ、シジミ、はまぐり、アオヤギ、カラス貝、サザエ、ミル貝もしくは貝化石等からなる貝殻、または死滅して白化した珊瑚が収容されてなる貝殻・珊瑚製接触材5aが充填されるとともに、その下方にブロア60から供給された空気を放出する散気管5bが配設されている。そして、この貝殻・珊瑚製接触材5aには微生物が付着した状態で生息しており、前記沈殿室4からこの第一接触ろ過室5に導入された処理水中の汚泥成分が、散気管5bから放出された空気によって攪拌されつつ、前記貝殻・珊瑚製接触材5aに付着した微生物により分解処理されるように構成されている。   In the first contact filtration chamber 5, a shell made of oysters, scallops, sea bream, pearl oysters, clams, swordfish, clams, blue goats, crows, scallops, mill shells, shell fossils, etc. Alternatively, a shell / slag contact material 5a containing dead and whitened shells is filled, and an air diffuser 5b for discharging air supplied from the blower 60 is disposed below the shell / shell contact material 5a. The shell / smoked contact material 5a is inhabited with microorganisms attached thereto, and the sludge components in the treated water introduced from the sedimentation chamber 4 into the first contact filtration chamber 5 are diffused from the air diffuser 5b. It is configured to be decomposed by microorganisms adhering to the shell / smoked contact material 5a while being agitated by the released air.

また、この第一接触ろ過室5には、ろ過処理槽20が連結されており、第一接触ろ過室5に導入された処理水は、前記のように貝殻・珊瑚製接触材5aにより分解処理されるとともに、このろ過処理槽20によってろ過処理されるよう構成されている。   Moreover, the filtration tank 20 is connected to the first contact filtration chamber 5, and the treated water introduced into the first contact filtration chamber 5 is decomposed by the shell / smoked contact material 5a as described above. In addition, the filtration tank 20 is configured to be filtered.

ろ過処理槽20は、前記第一接触ろ過室5から処理水を吸引するための吸引ポンプ(吸引手段)21と、吸引された処理水をろ過処理するろ過槽22と、ろ過処理後の処理水を第一接触ろ過室5に還流する還流手段23とを備えている。また、ろ過槽22の内部には、図3に示すように、ろ材24として粒子の異なる複数種類の砂が充填されており、この砂は上方に向かうほど粒子が小さくなるように積層している。   The filtration tank 20 includes a suction pump (suction means) 21 for sucking treated water from the first contact filtration chamber 5, a filtration tank 22 for filtering the sucked treated water, and treated water after filtration. And a reflux means 23 for refluxing the first contact filtration chamber 5 to the first contact filtration chamber 5. Moreover, as shown in FIG. 3, the inside of the filtration tank 22 is filled with a plurality of types of sand having different particles as the filter medium 24, and the sand is laminated so that the particles become smaller toward the upper side. .

吸引ポンプ21により吸引された処理水はろ過槽22の上方に設けられた導入口22aからろ過槽22内に導入され、ろ材24内を下方に向けて通過することでろ過されていく。そして、このろ材24でろ過された処理水はろ過槽22の下方に設けられた還流手段23によって再び第一接触ろ過室5に導入され、前記貝殻・珊瑚製接触材5aにより分解処理されるとともに、再び、吸引ポンプ21によってろ過処理槽20内に導入される。このように、第一接触ろ過室5内の処理水は貝殻・珊瑚製接触材5aにより分解処理されつつ、繰り返しろ過処理槽20でろ過されることにより浄化されていく。特に、ろ過処理では、処理水に含まれるSSが除去される。従って、前記第一接触ろ過室5に充填された貝殻・珊瑚製接触材5aに対するSSの付着が抑止されるので、貝殻・珊瑚製接触材5aの浄化機能の低下を抑止することができる。   The treated water sucked by the suction pump 21 is introduced into the filtration tank 22 from an inlet 22a provided above the filtration tank 22, and is filtered by passing through the filter medium 24 downward. The treated water filtered by the filter medium 24 is again introduced into the first contact filtration chamber 5 by the reflux means 23 provided below the filter tank 22, and is decomposed by the shell / smoked contact material 5a. Again, it is introduced into the filtration tank 20 by the suction pump 21. In this manner, the treated water in the first contact filtration chamber 5 is purified by being repeatedly filtered through the filtration treatment tank 20 while being decomposed by the shell / boiled contact material 5a. In particular, in the filtration treatment, SS contained in the treated water is removed. Therefore, since adhesion of SS to the shell / smoked contact material 5a filled in the first contact filtration chamber 5 is suppressed, it is possible to suppress a decrease in the purification function of the shell / smoked contact material 5a.

また、ろ材24の表面には処理水に含まれていた微生物が付着して繁殖するため、処理水をろ材24に繰り返し導入することで、処理水に含まれる汚泥成分が微生物によって分解処理されるという効果がある。例えば、第一接触ろ過室5に3mの処理水が導入され、ろ過槽22の容量が0.9mの場合には、1日にろ過処理を7.2回繰り返すことができ、処理水を十分に浄化することができる。また、このように一つのろ過処理槽20でろ過処理を繰り返すよう構成することで、ろ過処理槽20を小型化することができ、装置全体の省スペース化を図ることができる。 Moreover, since microorganisms contained in the treated water adhere to the surface of the filter medium 24 and propagate, the sludge components contained in the treated water are decomposed by the microorganisms by repeatedly introducing the treated water into the filter medium 24. There is an effect. For example, when 3 m 3 treated water is introduced into the first contact filtration chamber 5 and the capacity of the filtration tank 22 is 0.9 m 3 , the filtration treatment can be repeated 7.2 times a day. Can be sufficiently purified. Moreover, the filtration process tank 20 can be reduced in size by comprising so that the filtration process may be repeated in one filtration process tank 20 in this way, and the space saving of the whole apparatus can be achieved.

前記のようにろ過処理および貝殻・珊瑚製接触材5aにより浄化された処理水は、次に第二接触ろ過室6に導入される。この第二接触ろ過室6は、第一接触ろ過室5と同様にメッシュ状の袋体内に貝殻等が収容されてなる貝殻・珊瑚製接触材6aが充填されるとともに、下方に設けられた散気管6bによって空気が供給されている。そして、導入された処理水中の汚泥成分が貝殻・珊瑚製接触材6aに付着する微生物によって分解処理されるよう構成されている。ここで、この第二接触ろ過室6に導入される処理水は、前記のようにろ過処理槽20によりSSが十分に除去された処理水であるため、貝殻・珊瑚製接触材6aの目詰まりが抑止され、浄化機能を十分に発揮することができる。   The treated water purified by the filtration treatment and the shell / smoked contact material 5 a as described above is then introduced into the second contact filtration chamber 6. As in the first contact filtration chamber 5, the second contact filtration chamber 6 is filled with a shell / smoked contact material 6 a in which a shell or the like is housed in a mesh-like bag body, and a dust disposed below. Air is supplied by the trachea 6b. And it is comprised so that the sludge component in the introduced treated water may be decomposed by microorganisms adhering to the shell / smoked contact material 6a. Here, since the treated water introduced into the second contact filtration chamber 6 is treated water from which SS has been sufficiently removed by the filtration treatment tank 20 as described above, the shell / smoked contact material 6a is clogged. Is suppressed, and the purification function can be sufficiently exerted.

第二接触ろ過室6で分解処理された処理水は、沈殿ろ過室7に導出される。沈殿ろ過室7は、多孔質体からなるゼオライトが収容されたろ過体7aを有し、導入された処理水中の不純物を沈殿させて汚水と上澄み水に分離するとともに、この上澄み水中の微細な不純物を前記ろ過体7aによりろ過して浄化水を生成するよう構成されている。そして、このろ過体7aも前記貝殻・珊瑚製接触材6aと同様にSSによる目詰まりが抑止されることで、十分な浄化機能を発揮することができる。   The treated water decomposed in the second contact filtration chamber 6 is led to the precipitation filtration chamber 7. The precipitation filtration chamber 7 has a filter body 7a in which a porous zeolite is accommodated, and precipitates impurities in the introduced treated water and separates them into sewage and supernatant water, and fine impurities in the supernatant water. Is filtered through the filter body 7a to generate purified water. And this filter body 7a can also exhibit sufficient purification | cleaning function by clogging by SS similarly to the said shell and smoked contact material 6a.

前記沈殿ろ過室7で生成された浄化水は、最後に、浄化水貯留室8にオーバーフローして導出される。この浄化水貯留室8には、図4に示すように、複数の透孔が形成された仕切り板8a,8bが上下に設置された吸着筒8cと、この吸着筒8c内の仕切り板8a,8b間に配設された吸着材である活性炭収容体8dと、浄化水貯留室8内の処理水を吸引して前記活性炭収容体8dの下方部に吐出する循環ポンプ40aおよび循環パイプ40bを有する循環手段40とが設けられている。前記活性炭収容体8dは、布材等からなる袋体内に石炭系の活性炭が充填されることにより構成されている。   The purified water generated in the precipitation filtration chamber 7 is finally discharged by overflowing into the purified water storage chamber 8. In the purified water storage chamber 8, as shown in FIG. 4, an adsorption cylinder 8c in which partition plates 8a and 8b in which a plurality of through holes are formed are installed up and down, and a partition plate 8a in the adsorption cylinder 8c, 8b includes an activated carbon container 8d that is an adsorbent disposed between 8b, and a circulation pump 40a and a circulation pipe 40b that suck the treated water in the purified water storage chamber 8 and discharge it to the lower portion of the activated carbon container 8d. Circulation means 40 is provided. The activated carbon container 8d is configured by filling a bag made of a cloth material or the like with coal-based activated carbon.

そして、前記循環手段40により活性炭収容体8dの下方部に吐出された処理水が、前記吸着筒8c内を通って前記浄化水貯留室8内を循環するとともに、その際に、活性炭収容体8d内の石炭系活性炭により色素成分が吸着されて効果的に脱色されるようになっている。脱色処理された浄化水は、図1に示すように、その一部がトイレ50の給水タンクに供給されるとともに、残りが、浄化水貯留室8内に貯留される。そして、この活性炭収容体8dも、前記貝殻・珊瑚製接触材6aおよび前記ろ過体7aと同様に、ろ過処理槽20のろ過作用により処理水中のSSが十分に除去されることで、目詰まりが抑止され浄化機能が長期に亘り確保されている。このため、活性炭収容体8dを頻繁に交換することに起因したランニングコストの増大を抑制できるという利点がある。   And the treated water discharged to the lower part of the activated carbon container 8d by the circulation means 40 circulates in the purified water storage chamber 8 through the adsorption cylinder 8c, and at that time, the activated carbon container 8d. The pigment component is adsorbed by the coal-based activated carbon inside and is effectively decolorized. As shown in FIG. 1, a part of the decolorized purified water is supplied to the water supply tank of the toilet 50 and the rest is stored in the purified water storage chamber 8. And this activated carbon container 8d is also clogged because SS in the treated water is sufficiently removed by the filtering action of the filtration treatment tank 20 in the same manner as the shell / smoked contact material 6a and the filter 7a. Deterred and the purification function is secured for a long time. For this reason, there is an advantage that an increase in running cost due to frequent replacement of the activated carbon container 8d can be suppressed.

ここで、図4に示すように、前記循環手段40の途中には微細気泡発生装置41が設けられている。この微細気泡発生装置41は、処理水にオゾンを供給する気体供給部41aと、供給されたオゾンを剪断しマイクロバブルと呼ばれる超微細気泡を発生させる気泡発生部41bとからなっている。前記気体供給部41aにはオゾン発生装置と接続可能な気体吸入口41dが設けられており、このオゾン発生装置で発生したオゾンを気体供給部41aに供給するよう構成されている。また、前記気泡発生部41bにはマイクロバブルを発生させる気泡発生部41cが設けられており、この気泡発生部41cにより前記供給されたオゾンがマイクロバブルとして処理水中に混入するようになっている。この気泡発生部41bで発生したマイクロバブルは処理水とともに浄化水貯留室8内に導入される。   Here, as shown in FIG. 4, a fine bubble generating device 41 is provided in the middle of the circulating means 40. The fine bubble generator 41 includes a gas supply unit 41a that supplies ozone to treated water, and a bubble generation unit 41b that shears the supplied ozone to generate ultrafine bubbles called microbubbles. The gas supply part 41a is provided with a gas inlet 41d that can be connected to an ozone generator, and ozone generated by the ozone generator is supplied to the gas supply part 41a. The bubble generation unit 41b is provided with a bubble generation unit 41c for generating microbubbles, and the ozone supplied by the bubble generation unit 41c is mixed into the treated water as microbubbles. The microbubbles generated in the bubble generating part 41b are introduced into the purified water storage chamber 8 together with the treated water.

マイクロバブルは泡径が10μm〜20μmほどの気泡であり水中での溶存効果が高い。また、オゾンには脱色効果があるので、このオゾンを含むマイクロバブルによって処理水の脱色が促進される。従って、浄化水貯留室8内の活性炭収容体8dの負担が軽減でき活性炭収容体8dの交換回数を減少できるので、ランニングコストの増大をさらに抑制することができる。また、この微細気泡発生装置41で発生するマイクロバブルには汚泥成分を除去する効果があるので、活性炭収容体8dに付着したSSが効果的に除去される。   Microbubbles are bubbles having a bubble diameter of about 10 μm to 20 μm, and have a high dissolution effect in water. Moreover, since ozone has a decoloring effect, decolorization of treated water is promoted by the microbubbles containing ozone. Accordingly, the burden on the activated carbon container 8d in the purified water storage chamber 8 can be reduced, and the number of replacements of the activated carbon container 8d can be reduced, so that an increase in running cost can be further suppressed. Further, since the microbubbles generated by the fine bubble generating device 41 have an effect of removing the sludge component, SS attached to the activated carbon container 8d is effectively removed.

以上のようにして、水洗トイレ50等から排出された汚水は各浄化処理室2〜8およびろ過処理槽20によって浄化され再び利用可能な浄化水となり、水洗トイレ50に還流される。特に、前記のように浄化水にマイクロバブルを含有させた場合には、このマイクロバブルによる汚泥成分除去作用により水洗トイレ50の汚れを効果的に除去することができる。   As described above, the sewage discharged from the flush toilet 50 or the like is purified by the respective purification treatment chambers 2 to 8 and the filtration treatment tank 20 to become purified water that can be used again, and is returned to the flush toilet 50. In particular, when microbubbles are contained in the purified water as described above, dirt on the flush toilet 50 can be effectively removed by the action of removing sludge components by the microbubbles.

ここで、前記貝殻・珊瑚製接触材5a,6aに含まれる貝殻は、炭酸カルシウムを主成分とし、リン酸カルシウムやカリウムおよび炭酸マグネシウム等の成分を含有したものであり、その真珠層が除去された状態で袋体内に収容されている。特に、真珠層を除去して多孔質の角柱層を露出させたカキ殻を使用すれば、カキ殻に付着した微生物と処理水中の汚泥成分との親和性が高まるので、前記微生物が好適に繁殖できる。そして、多孔質の角柱層において繁殖したこの微生物により、処理水中の汚泥成分を効果的に分解処理して排水を効率よく浄化することができる。   Here, the shell contained in the shell / smoked contact material 5a, 6a is mainly composed of calcium carbonate and contains components such as calcium phosphate, potassium and magnesium carbonate, and the nacreous layer is removed. It is housed in the bag. In particular, the use of oyster shells from which the nacreous layer is removed to expose the porous prismatic layer increases the affinity between microorganisms adhering to the oyster shells and sludge components in the treated water. it can. And by this microorganism propagated in the porous prismatic layer, the sludge component in the treated water can be effectively decomposed to efficiently purify the waste water.

ただし、真珠層を予め除去しない場合であっても、真珠層は浄化装置1の稼動中に自然と除去されるので、予め真珠層を除去した場合とほぼ同等の効果を得ることは可能である。   However, even if the nacreous layer is not removed in advance, the nacreous layer is naturally removed during the operation of the purification device 1, so that it is possible to obtain substantially the same effect as when the nacreous layer is removed in advance. .

次に、ろ材24を逆洗し、ろ材24からSS等の浮遊物を剥離させてろ過槽22のろ過性能を回復する方法について説明する。   Next, a method for backwashing the filter medium 24 and peeling off suspended matters such as SS from the filter medium 24 to recover the filtration performance of the filtration tank 22 will be described.

ろ過処理槽20は、前記吸引ポンプ21と還流手段23の他に、前記浄化水貯留室8に連結されて、この浄化水貯留室8に貯留される浄化水を前記ろ過槽22に供給するための浄化水吸引ポンプ25(浄化水供給手段)と、前記沈殿分離室2に接続される配管11に連結されて、ろ過槽22の逆洗後の排水をこの沈殿分離室2に排出する処理水導出手段26とを備えている。また、ろ過槽22の上方および下方には逆洗水導入口25a,25bが設けられており、それぞれ前記浄化水吸引ポンプ25に連結されている。   The filtration tank 20 is connected to the purified water storage chamber 8 in addition to the suction pump 21 and the reflux means 23, and supplies the purified water stored in the purified water storage chamber 8 to the filtration tank 22. The purified water suction pump 25 (purified water supply means) and the pipe 11 connected to the precipitation separation chamber 2, and treated water for discharging the waste water after backwashing of the filtration tank 22 to the precipitation separation chamber 2. Deriving means 26 is provided. Further, backwash water inlets 25 a and 25 b are provided above and below the filtration tank 22, and are connected to the purified water suction pump 25, respectively.

浄化水吸引ポンプ25により吸引された浄化水は、ろ過槽22の上方に設けられた逆洗水導入口25aからろ過槽22に導入され、ろ材24の表面を洗浄する。また、前記浄化水はろ過槽22の下方に設けられた逆洗水導入口25bからろ過槽22に導入され、ろ過槽22内をろ過方向とは逆方向に流れ、ろ材24に付着した浮遊物等を剥離させていく。そして、この剥離した浮遊物等を含む処理水は、ろ過槽22の上方に設けられた処理水導出口26aから前記処理水導出手段26によってろ過槽22の外部に導出される。さらに、この浮遊物等を含む処理水は、処理水導出手段26によって沈殿分離室2に還流されるよう構成されており、浮遊物等は沈殿分離室2で沈殿分離され、前記のように定期的に外部に吸い出されて処理される。   The purified water sucked by the purified water suction pump 25 is introduced into the filtration tank 22 from the backwash water inlet 25 a provided above the filtration tank 22, and the surface of the filter medium 24 is washed. Further, the purified water is introduced into the filtration tank 22 from a backwash water inlet 25 b provided below the filtration tank 22, flows in the filtration tank 22 in the direction opposite to the filtration direction, and floats attached to the filter medium 24. And so on. Then, the treated water containing the separated suspended matter and the like is led out of the filtration tank 22 by the treated water lead-out means 26 from a treated water outlet 26 a provided above the filtration tank 22. Further, the treated water containing the suspended matter is configured to be refluxed to the precipitation separation chamber 2 by the treated water deriving means 26, and the suspended matter is precipitated and separated in the precipitation separation chamber 2, and periodically as described above. Are sucked out and processed.

ここで、前記のようなろ材24の逆洗は適宜実施すればよいが、本実施形態では、ろ過槽22の下方に圧力センサ(圧力検出手段)27設けるとともに、この圧力センサ27の出力に基づいて前記逆洗のタイミングや逆洗水の量を制御する制御装置(制御手段)28を設けて、自動的に逆洗できるように構成している。   Here, the above-described backwashing of the filter medium 24 may be performed as appropriate, but in this embodiment, a pressure sensor (pressure detection means) 27 is provided below the filtration tank 22 and the output of the pressure sensor 27 is used. A control device (control means) 28 for controlling the timing of backwashing and the amount of backwashing water is provided so that the backwashing can be performed automatically.

すなわち、ろ材24が目詰まりして処理水が流れ難くなるとろ過槽22の下流側の圧力は低下していくので、この圧力を前記圧力センサ27で検出し、この検出値が所定値以下になった時に、前記浄化水吸引ポンプ25を駆動して逆洗水をろ過槽22に導入するように制御している。また、ろ過槽22に導入される逆洗水の導入量を調整する調整弁29を設け、この調整弁29の開度を制御することで浄化水の導入量を制御している。このようにすれば、ろ材24への浮遊物の付着度合いに応じて最適な条件で効率よく逆洗することができる。   That is, when the filter medium 24 is clogged and it becomes difficult for the treated water to flow, the pressure on the downstream side of the filtration tank 22 decreases. Therefore, this pressure is detected by the pressure sensor 27, and the detected value becomes a predetermined value or less. At this time, the purified water suction pump 25 is driven to control the backwash water to be introduced into the filtration tank 22. Moreover, the adjustment valve 29 which adjusts the introduction amount of the backwash water introduce | transduced into the filtration tank 22 is provided, and the introduction amount of purified water is controlled by controlling the opening degree of this adjustment valve 29. FIG. If it does in this way, according to the adhesion degree of the suspended | floating matter to the filter medium 24, it can backwash efficiently on optimal conditions.

ここで、前記逆洗を行う際には、前記吸引ポンプ21による処理水の吸引を停止させ、ろ過槽22に第一接触ろ過室5からの処理水が導入されないようにしておく。また、本実施形態では、前記ろ過槽22の下方に設けられた逆洗水導入口25bと、ろ過処理後の処理水を還流手段23によって第一接触ろ過室5に還流する還流口とが共通化されているが、前記浄化水吸引ポンプ25と逆洗水導入口25bとを連結する配管および前記還流手段23が接続される配管とに各々逆止弁を設けることで、逆洗時に浄化水が還流手段23を介して第一接触ろ過室5に導出されることを抑制している。   Here, when performing the backwash, the suction of the treated water by the suction pump 21 is stopped so that the treated water from the first contact filtration chamber 5 is not introduced into the filtration tank 22. Moreover, in this embodiment, the backwash water inlet 25b provided below the filtration tank 22 and the reflux port for refluxing the treated water after the filtration treatment to the first contact filtration chamber 5 by the reflux means 23 are common. However, by providing a check valve in each of the pipe connecting the purified water suction pump 25 and the backwash water inlet 25b and the pipe connected to the reflux means 23, the purified water can be used during backwashing. Is prevented from being led to the first contact filtration chamber 5 through the reflux means 23.

以上のように、本発明に係る前記実施形態によれば、第一接触ろ過室5にろ過処理槽20を連結し、第一接触ろ過室5内の処理水を繰り返しろ過することで、浄化機能を確保しつつろ過処理槽20を小型化することができる。また、処理水を繰り返しろ過処理することで、ろ材24に付着した微生物による処理水中の汚泥成分の分解処理が促進される。さらに、このろ過処理により処理水中のSSが除去されるので、第一接触ろ過室5に設けられた貝殻・珊瑚製接触材5aと、これより下流に設けられた第二接触ろ過室6の貝殻・珊瑚製接触材6a、沈殿ろ過室7のろ過体7aおよび浄化水貯留室8の活性炭収容体8dへのSSの付着が抑制され、これら接触材等の浄化機能を向上させることができる。また、この接触材等の交換期間を長くすることができるのでコスト面でも有利となる。   As mentioned above, according to the said embodiment which concerns on this invention, the filtration processing tank 20 is connected with the 1st contact filtration chamber 5, and the purification function is obtained by repeatedly filtering the treated water in the 1st contact filtration chamber 5. The filtration tank 20 can be downsized while ensuring the above. Further, by repeatedly filtering the treated water, the decomposition treatment of the sludge components in the treated water by the microorganisms attached to the filter medium 24 is promoted. Further, since SS in the treated water is removed by this filtration treatment, the shell / smoked contact material 5a provided in the first contact filtration chamber 5 and the shell of the second contact filtration chamber 6 provided downstream thereof. -Adherence of SS to the smoked contact material 6a, the filter body 7a of the sedimentation filtration chamber 7 and the activated carbon container 8d of the purified water storage chamber 8 is suppressed, and the purification function of these contact materials and the like can be improved. Moreover, since the exchange period of this contact material etc. can be lengthened, it becomes advantageous also in terms of cost.

ここで、前記実施形態では、沈殿分離室2の導入口2aを水洗トイレ50の排水口に接続して水洗トイレ50からの排水を浄化処理する場合について示したが、この水洗トイレ50の代わりに、工場、ホテル、病院等の排水設備に接続して工場等から排出される汚水を浄化処理するようにしたり、雨水集水桝や用水路等に接続して雨水等を浄化処理するようにしてもよい。   Here, in the said embodiment, although the case where the inlet 2a of the sedimentation separation chamber 2 was connected to the drain outlet of the flush toilet 50 and the waste water from the flush toilet 50 was purified was shown, instead of this flush toilet 50, it was shown. In addition, it can be connected to drainage facilities such as factories, hotels, hospitals, etc. to purify sewage discharged from factories, etc., or it can be connected to rainwater catchment or irrigation canals, etc. Good.

また、ろ過処理槽20を第一接触ろ過室5に連結した場合について示したが、これに限らず、他の浄化処理室に連結させてもよい。   Moreover, although shown about the case where the filtration processing tank 20 was connected with the 1st contact filtration chamber 5, you may connect not only to this but to another purification processing chamber.

また、前記ろ過処理槽20の逆洗水導入口25a,25bを浄化水貯留室8に接続した場合について示したが、この逆洗水導入口25a,25bを水道の蛇口等に接続して、水道水を逆洗水として供給するようにしてもよい。さらに、逆洗後の処理水を沈殿分離室2に導出する場合について示したが、外部へ排出するよう構成してもよい。   Moreover, although shown about the case where the backwash water inlet 25a, 25b of the said filtration tank 20 was connected to the purified water storage chamber 8, this backwash water inlet 25a, 25b was connected to the faucet etc. of water supply, Tap water may be supplied as backwash water. Furthermore, although the case where the treated water after backwashing is led out to the precipitation separation chamber 2 is shown, it may be configured to be discharged to the outside.

また、前記実施形態では、浄化装置1で処理された浄化水を水洗トイレ50の給水タンクに供給する場合について示したが、浄化水の利用方法はこれに限らず、農業用水や洗車用水や打ち水としての利用等、種々の方面での利用が可能である。   Moreover, in the said embodiment, although the case where the purified water processed with the purification apparatus 1 was supplied to the water supply tank of the flush toilet 50 was shown, the usage method of purified water is not restricted to this, Agricultural water, car wash water, and water hitting water It can be used in various directions such as as

また、前記実施形態では微細気泡発生装置41を浄化水貯留室8の循環手段40に接続した場合について示したが、この微細気泡発生装置41を、前記沈殿ろ過室7と浄化水貯留室8との間に設け、沈殿ろ過室7から導出される処理水にマイクロバブルを発生させ、マイクロバブルを含んだ処理水を浄化水貯留室8に導入するようにしてもよい。また、微細気泡発生装置41を前記沈殿ろ過室7や第一接触ろ過室5、第二接触ろ過室6等に接続してもよい。そして、このように微細気泡発生装置41を沈殿ろ過室7等に接続した場合には、沈殿ろ過室7のろ過体7aや第一接触ろ過室5および第二接触ろ過室6の貝殻・珊瑚製接触材5aおよび6a等に付着したSSが効果的に除去され、浄化性能が高められる。さらに、この微細気泡発生装置41の前記気体吸引口41dを大気開放にして気体供給部41aに空気を供給するようにしてもよい。この場合には、処理水中の溶存酸素が増加するため、浄化水を植物への散水等に用いる場合に植物の成長に有効に作用する。   Moreover, although the said embodiment showed about the case where the fine bubble generator 41 was connected to the circulation means 40 of the purified water storage chamber 8, this fine bubble generator 41 is connected to the said precipitation filtration chamber 7, the purified water storage chamber 8, and It is also possible to provide microbubbles in the treated water led out from the sedimentation filtration chamber 7 and introduce the treated water containing the microbubbles into the purified water storage chamber 8. Moreover, you may connect the fine bubble generator 41 to the said precipitation filtration chamber 7, the 1st contact filtration chamber 5, the 2nd contact filtration chamber 6, etc. FIG. When the microbubble generator 41 is thus connected to the precipitation filtration chamber 7 or the like, the filter body 7a of the precipitation filtration chamber 7, the shells and smoked products of the first contact filtration chamber 5 and the second contact filtration chamber 6 are prepared. SS attached to the contact materials 5a and 6a and the like is effectively removed, and the purification performance is improved. Further, the gas suction port 41d of the fine bubble generating device 41 may be opened to the atmosphere to supply air to the gas supply unit 41a. In this case, since dissolved oxygen in the treated water increases, when purified water is used for watering the plant, it effectively acts on the growth of the plant.

また、浄化処理室の組み合わせおよび各浄化処理室での処理手段は、前記に限らない。例えば、最上流の浄化処理室を、沈殿分離を行う沈殿分離室2に代えて嫌気性処理を行う嫌気性処理室としてもよい。   Further, the combination of purification treatment chambers and the processing means in each purification treatment chamber are not limited to the above. For example, the most upstream purification treatment chamber may be an anaerobic treatment chamber for performing anaerobic treatment instead of the precipitation separation chamber 2 for carrying out precipitation separation.

また、前記浄化水貯留室8内の浄化水を貯留する浄化水貯留タンクを別途設けて、前記浄化水吸引ポンプ25をこの浄化水貯留タンクに連結し、浄化水貯留タンク内の浄化水を逆洗水としてろ過槽22に供給するようにしてもよい。   Further, a purified water storage tank for storing purified water in the purified water storage chamber 8 is separately provided, and the purified water suction pump 25 is connected to the purified water storage tank so that the purified water in the purified water storage tank is reversed. You may make it supply to the filtration tank 22 as washing water.

また、ろ過処理槽20は砂をろ材とする砂ろ過装置に限らず、他のろ材を用いるものでもよい。   Moreover, the filtration tank 20 is not limited to a sand filtration device using sand as a filter medium, but may use other filter medium.

本発明に係る浄化装置の実施形態を示す説明図である。It is explanatory drawing which shows embodiment of the purification apparatus which concerns on this invention. 本発明に係る浄化装置の断面図である。It is sectional drawing of the purification apparatus which concerns on this invention. 本発明に係るろ過処理槽の断面図である。It is sectional drawing of the filtration processing tank which concerns on this invention. 浄化水貯留室に設けられた循環手段の具体的構成を示す斜視図である。It is a perspective view which shows the specific structure of the circulation means provided in the purified water storage chamber.

符号の説明Explanation of symbols

1 浄化装置
2 沈殿分離室
3 接触ばっ気室
4 沈殿室
5 第一接触ろ過室
5a 貝殻・珊瑚製接触材
6 第二接触ろ過室
6a 貝殻・珊瑚製接触材
7 沈殿ろ過室
8 浄化水貯留室(吸着処理室)
8d 活性炭収容体(吸着材)
10 浄化処理槽
20 ろ過処理槽
21 吸引ポンプ(吸引手段)
22 ろ過槽
23 還流手段
24 ろ材
25 浄化水吸引ポンプ(浄化水供給手段)
25a 逆洗水導入口
26 処理水導出手段
27 圧力センサ(圧力検出手段)
28 制御装置(制御手段)
50 水洗トイレ
DESCRIPTION OF SYMBOLS 1 Purification apparatus 2 Precipitation separation chamber 3 Contact aeration chamber 4 Precipitation chamber 5 First contact filtration chamber 5a Shell / smoked contact material 6 Second contact filtration chamber 6a Shell / smoked contact material 7 Precipitation filtration chamber 8 Purified water storage chamber (Adsorption processing chamber)
8d Activated carbon container (adsorbent)
10 Purification tank 20 Filtration tank 21 Suction pump (suction means)
22 Filtration tank 23 Recirculation means 24 Filter medium 25 Purified water suction pump (purified water supply means)
25a Backwash water inlet 26 Treated water outlet 27 Pressure sensor (pressure detector)
28 Control device (control means)
50 Flush toilet

Claims (7)

汚泥成分を含有するトイレ等の家庭排水や工場、ホテル、病院等からの排水を段階的に浄化する複数の浄化処理室を有する浄化処理槽と、
前記排水をろ過処理するろ過処理槽とを有し、
前記複数の浄化処理室が、前記排水中の浮遊物等を吸着除去する吸着材を有する吸着処理室を備えるとともに、
前記ろ過処理槽が、前記浄化処理室のうち前記吸着処理室の上流に設けられた浄化処理室に連結されて、この浄化処理室内の処理水を吸引する吸引手段と、ろ材を有し前記吸引された処理水をろ過するろ過槽と、当該ろ過された処理水を前記吸着処理室の上流の浄化処理室に還流させる還流手段とを備え、
このろ過処理槽によって、前記浄化処理室の処理水が繰り返しろ過されることを特徴とする浄化装置。
A purification treatment tank having a plurality of purification treatment rooms for gradually purifying domestic wastewater such as toilets containing sludge components and wastewater from factories, hotels, hospitals, etc .;
A filtration tank for filtering the waste water,
The plurality of purification treatment chambers include an adsorption treatment chamber having an adsorbent for adsorbing and removing suspended matters in the waste water, and the like.
The filtration tank is connected to a purification treatment chamber provided upstream of the adsorption treatment chamber in the purification treatment chamber, and has a suction means for sucking treated water in the purification treatment chamber, a filter medium, and the suction A filtration tank for filtering the treated water, and a reflux means for refluxing the filtered treated water to the purification treatment chamber upstream of the adsorption treatment chamber,
The purification apparatus characterized in that the treated water in the purification treatment chamber is repeatedly filtered by the filtration treatment tank.
請求項1記載の浄化装置であって、
前記吸着処理室が、前記吸着材として活性炭収容体を有することを特徴とする浄化装置。
The purification device according to claim 1,
The purification apparatus, wherein the adsorption treatment chamber has an activated carbon container as the adsorbent.
請求項1または2に記載の浄化装置であって、
前記ろ過処理槽が、前記ろ材に付着した浮遊物等を除去するための逆洗水として、外部から水道水等を前記ろ過槽に導入するための逆洗水導入口を有することを特徴とする浄化装置。
The purification device according to claim 1 or 2,
The filtration tank has a backwash water inlet for introducing tap water or the like into the filter tank from the outside as backwash water for removing suspended matter or the like attached to the filter medium. Purification equipment.
請求項3に記載の浄化装置であって、
前記ろ過処理槽が、前記ろ過槽の下流側の圧力を検出する圧力検出手段と、当該圧力検出手段の検出結果に基づいて、前記逆洗水導入口から逆洗水を導入するタイミングあるいは導入する逆洗水の量を制御する制御手段とを有することを特徴とする浄化装置。
The purification device according to claim 3,
The filtration treatment tank detects or introduces the backwash water from the backwash water introduction port based on the pressure detection means for detecting the pressure on the downstream side of the filtration tank and the detection result of the pressure detection means. And a control means for controlling the amount of backwash water.
請求項3または4に記載の浄化装置であって、
前記複数の浄化処理室のうち最下流の位置に、前記排水から生成された浄化水を貯留可能な浄化水貯留室が設けられるとともに、
前記ろ過処理槽が、前記逆洗水導入口に接続されて、前記浄化水貯留室に貯留された浄化水を前記ろ過槽に逆洗水として供給する浄化水供給手段を有することを特徴とする浄化装置。
The purification device according to claim 3 or 4,
A purified water storage chamber capable of storing purified water generated from the waste water is provided at the most downstream position among the plurality of purification processing chambers,
The filtration tank is connected to the backwash water inlet and has purified water supply means for supplying purified water stored in the purified water storage chamber to the filter tank as backwash water. Purification equipment.
請求項3〜5のいずれかに記載の浄化装置であって、
前記ろ材を逆洗する際に生じる浮遊物等を含む処理水を、前記複数の浄化処理室のうち最上流に設けられた浄化処理室に導出する処理水導出手段を前記ろ過処理槽に設けたことを特徴とする浄化装置。
A purification device according to any one of claims 3 to 5,
A treated water deriving means for deriving treated water including floating matters generated when backwashing the filter medium to the purification treatment chamber provided in the uppermost stream among the plurality of purification treatment chambers is provided in the filtration treatment tank. A purification device characterized by that.
請求項1〜6のいずれかに記載の浄化装置であって、
前記ろ過処理槽が、ろ材を砂や石とする砂ろ過装置であることを特徴とする浄化装置。
A purification device according to any one of claims 1 to 6,
A purification device, wherein the filtration tank is a sand filtration device using sand or stone as a filter medium.
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