JP2006102701A - Apparatus for cleaning water - Google Patents

Apparatus for cleaning water Download PDF

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JP2006102701A
JP2006102701A JP2004295541A JP2004295541A JP2006102701A JP 2006102701 A JP2006102701 A JP 2006102701A JP 2004295541 A JP2004295541 A JP 2004295541A JP 2004295541 A JP2004295541 A JP 2004295541A JP 2006102701 A JP2006102701 A JP 2006102701A
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stage tank
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JP4502772B2 (en
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Michiyoshi Sugiyama
倫義 杉山
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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
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    • Y02W10/10Biological treatment of water, waste water, or sewage

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Abstract

<P>PROBLEM TO BE SOLVED: To provide an apparatus for cleaning water, the construction cost or maintenance cost of which can be reduced. <P>SOLUTION: This apparatus for cleaning water is constituted so that water is cleaned by using a water activating agent constituted of a gravelly material obtained from a mixture of porous lapillus, which is oxidized/sterilized to improve the adsorption property and air dissolving efficiency thereof and is made suitable as the culture medium of a microbe, with black earth and/or a powdery material obtained by powdering a clay-like material. The apparatus for cleaning water is provided with: a first stage tank for continuously receiving the water to be treated from the upstream side and storing a predetermined amount of the water to be treated; a second stage tank for continuously receiving the water which is to be treated and is discharged from the first stage tank and storing a predetermined amount of the water to be treated; and a communicative port for making the water to be treated in the first stage tank communicate with the water to be treated in the second stage tank. The water activating agent is brought into contact with the water to be treated in both of the first stage tank and the second stage tank. <P>COPYRIGHT: (C)2006,JPO&NCIPI

Description

本発明は、水質浄化装置に関し、より詳細には、構造が簡単で建設や維持に要する費用を削減することができる水質浄化装置に関する。   The present invention relates to a water purification apparatus, and more particularly to a water purification apparatus that has a simple structure and can reduce the cost required for construction and maintenance.

人間の様々な活動により産業廃水や生活廃水が生じ、これらの処理には、下水道や水質浄化装置の建設に多額の投資が必要であるうえ、その運転、維持に多額の費用がかかっている。この水質浄化装置の建設や維持に要する費用を削減するため様々な水質浄化装置が研究開発されているが(例えば、特許文献1参照。)、大規模な建設工事を要したり構造が複雑であるため、かかる費用は依然として満足できるものではない。   Various human activities generate industrial wastewater and domestic wastewater. These treatments require a large investment in the construction of sewers and water purification equipment, and a large cost in operation and maintenance. Various water purification devices have been researched and developed in order to reduce the cost required for the construction and maintenance of this water purification device (see, for example, Patent Document 1). However, a large-scale construction work or a complicated structure is required. As such, such costs are still not satisfactory.

一方、本願の発明者は平成5年(1993)9月27日に発明の名称を「水質活性剤とその製造方法」とする特許出願をしており、該特許出願は平成11年(1999)3月26日に特許番号第2903359号(以下、「前特許公報」という。なお、この特許を以下、「前特許」という。)として特許された(特許文献2参照。)。
前特許は、「酸化処理により殺菌し、吸着性と空気溶解効率とを向上させるとともに、微生物培地に適するようにした多孔質の火山礫と黒土との混合物から得られる礫状物、及び又は粘土状物を粉末化した粉末物からなる水質活性剤」(前特許公報中、請求項1)に係るものであり、かかる水質活性剤は「水道水、水槽、プ−ル、川、池、湖沼、生活排水、産業排水を、効率的に極めて低コストで浄化処理」(前特許公報中、段落番号0038)できるものである。
On the other hand, the inventor of the present application filed a patent application entitled “Water quality activator and its production method” on September 27, 1993, which was filed in 1999. On March 26, it was patented as Patent No. 2903359 (hereinafter referred to as “previous patent publication”, hereinafter referred to as “previous patent”) (see Patent Document 2).
The previous patent states that “pebbles and / or clay obtained from a mixture of porous volcanic gravel and black soil that is sterilized by oxidation treatment to improve adsorption and air dissolution efficiency and suitable for microbial media. The water quality activator comprising a powdered product obtained by pulverizing the form "(Claim 1 in the previous patent publication). The water quality activator is" tap water, water tank, pool, river, pond, lake " In addition, domestic wastewater and industrial wastewater can be efficiently purified at a very low cost ”(paragraph number 0038 in the previous patent publication).

特開2004−181362号公報(例えば、請求項1)Japanese Patent Laying-Open No. 2004-181362 (for example, claim 1) 特許第2903359号公報Japanese Patent No. 2903359

しかしながら、前特許に係る「酸化処理により殺菌し、吸着性と空気溶解効率とを向上させるとともに、微生物培地に適するようにした多孔質の火山礫と黒土との混合物から得られる礫状物、及び又は粘土状物を粉末化した粉末物からなる水質活性剤」(以下、「本活性剤」という。)を用い、高効率で水質浄化を行うための水質浄化装置はこれまで確立されていなかった。   However, according to the previous patent, “pebbles obtained from a mixture of porous volcanic gravel and black soil sterilized by oxidation treatment, improving adsorption and air dissolution efficiency, and suitable for a microbial medium, and Alternatively, a water purification device for performing water purification with high efficiency using a water quality activator made of powdered clay-like material (hereinafter referred to as “activator”) has not been established so far. .

そこで、本発明においては、本活性剤を用いて高効率に水質浄化を行うことができる水質浄化装置を提供することを目的とし、それにより水質浄化装置の建設や維持に要する費用を削減する。   Therefore, an object of the present invention is to provide a water purification device that can perform water purification with high efficiency using this activator, thereby reducing the cost required for construction and maintenance of the water purification device.

本発明の水質浄化装置(以下、「本装置」という。)は、酸化処理により殺菌し、吸着性と空気溶解効率とを向上させるとともに、微生物培地に適するようにした多孔質の火山礫と黒土との混合物から得られる礫状物、及び又は粘土状物を粉末化した粉末物からなる水質活性剤を用いる水質浄化装置であって、上方から被処理水を連続的に受け入れ被処理水を所定量保有する初段槽と、該初段槽から排出される被処理水を連続的に受け入れ被処理水を所定量保有する次段槽と、該初段槽に保有される被処理水中と該次段槽に保有される被処理水中とを連通させる連通口と、を備えてなり、該初段槽及び該次段槽の両方が保有する被処理水に該水質活性剤が接触するものである、水質浄化装置である。   The water purification apparatus of the present invention (hereinafter referred to as “the present apparatus”) is sterilized by oxidation treatment to improve the adsorptivity and air dissolution efficiency, and is suitable for a porous volcanic gravel and black soil suitable for a microbial medium. Water purification apparatus using a water quality activator comprising a gravel-like material obtained from a mixture with the above and / or a powdered material obtained by pulverizing clay-like material, and continuously receiving the water to be treated from above. A first-stage tank that holds a fixed amount, a next-stage tank that continuously receives treated water discharged from the first-stage tank, and holds a predetermined amount of treated water; treated water that is held in the first-stage tank; and the next-stage tank And a communication port for communicating with the water to be treated held in the water treatment, wherein the water activator is in contact with the water to be treated held in both the first-stage tank and the next-stage tank. Device.

まず、本装置において使用する「酸化処理により殺菌し、吸着性と空気溶解効率とを向上させるとともに、微生物培地に適するようにした多孔質の火山礫と黒土との混合物から得られる礫状物、及び又は粘土状物を粉末化した粉末物からなる水質活性剤」(本活性剤)は、前特許公報(特許番号第2903359号)の請求項1に係る水質活性剤であり、本活性剤の製造方法等は前特許公報において詳しく説明がされているのでここでは説明を省略する。
本装置は、本活性剤を用いる水質浄化装置である。初段槽は、上方から被処理水を連続的に受け入れ被処理水を所定量保有する。そして、次段槽は、初段槽から排出される被処理水を連通口を経由して連続的に受け入れ被処理水を所定量保有する。なお、連通口は、初段槽に保有される被処理水中と、次段槽に保有される被処理水中と、を連通させるように形成されている。このような初段槽が保有する被処理水と、次段槽が保有する被処理水と、の両方に本活性剤が接触することで、初段槽と次段槽との両方において被処理水の水質が浄化される。また、本装置は、このように初段槽、次段槽、連通口及び本活性剤により簡単に構成することができ、建設や維持に要する費用を抑えることができることに加え、本活性剤を用いて高効率に水質浄化を行うことができる。
First, “pebbles obtained from a mixture of porous volcanic gravel and black soil that is sterilized by oxidation treatment, improves adsorption and air dissolution efficiency, and is suitable for a microbial medium. And / or a water quality activator comprising a powdered product of a clay-like material ”(this activator) is the water quality activator according to claim 1 of the previous patent publication (Patent No. 2903359). Since the manufacturing method and the like are described in detail in the previous patent publication, the description is omitted here.
This apparatus is a water purification apparatus using this activator. The first stage tank continuously receives treated water from above and holds a predetermined amount of treated water. The next-stage tank continuously receives the treated water discharged from the first-stage tank via the communication port and holds a predetermined amount of treated water. The communication port is formed so as to allow communication between the water to be treated held in the first tank and the water to be treated held in the next tank. This activator is in contact with both the water to be treated in the first tank and the water to be treated in the next tank, so that the water to be treated in both the first tank and the next tank. Water quality is purified. In addition, the apparatus can be simply configured by the first-stage tank, the next-stage tank, the communication port, and the present activator as described above, and in addition to suppressing the cost required for construction and maintenance, the present activator is used. Water purification with high efficiency.

また、前述したように初段槽に保有される被処理水中と、次段槽に保有される被処理水中と、を連通させるように連通口を形成することで、初段槽から次段槽に被処理水を穏やかに進入させることができ、被処理水中に浮遊する浮遊物や本活性剤を次段槽に留めることにより次段槽における水質浄化を促進することができる。かかる浮遊物や本活性剤は水よりも比重が大きいものが多いことから、これらのものを次段槽によりうまく留めるには連通口を次段槽に保有される被処理水のできるだけ深い位置に形成することが好ましい(連通口を経由して次段槽に進入したこれらのものが次段槽から脱出するためには、連通口から上方へ移動する必要があり、連通口を深くすることで脱出に必要な上方への移動距離を増加させることができ、それによってこれらのものが不意に次段槽から脱出することを防止又は減少させることができる。)。
このことからは連通口(次段槽の内部に連通口が開いた部分の最上部の位置によって判断する。)は、次段槽に保有される被処理水の深さ(次段槽に保有される被処理水の最も深い位置の深さ)の半分よりも深い位置に形成されるようにしてもよい(即ち、次段槽の内部に連通口が開いた部分の最上部の位置pが、次段槽に保有される被処理水の最も深い位置の深さdの1/2よりも下方に位置する。また、より好ましくは位置pは深さdの1/3よりも下方に位置し、最も好ましくは位置pは深さdの1/4よりも下方に位置する。なお、これら「深さdの1/2よりも下方」、「深さdの1/3よりも下方」及び「dの1/4よりも下方」等は、被処理水の該最も深い位置における被処理水の最下部(換言すれば、次段槽の底面)から鉛直上方にそれぞれ「深さdの1/2」、「深さdの1/3」及び「dの1/4」行った位置よりも下方であることをいう。
Further, as described above, the communication port is formed so as to communicate the treated water held in the first-stage tank and the treated water held in the next-stage tank, so that the first-stage tank is covered with the next-stage tank. The treated water can be made to enter gently, and water purification in the next-stage tank can be promoted by retaining the suspended matter floating in the treated water and the present activator in the next-stage tank. Since many of these suspended solids and this activator have a specific gravity greater than that of water, in order to keep them well in the next-stage tank, the communication port is located as deep as possible in the treated water held in the next-stage tank. It is preferable to form (in order for these things that have entered the next tank through the communication port to escape from the next tank, it is necessary to move upward from the communication port. The upward travel distance required for escape can be increased, thereby preventing or reducing the inadvertent escape of these from the next tank.)
From this, the communication port (determined by the position of the uppermost part of the portion where the communication port is opened inside the next-stage tank) is the depth of the water to be treated in the next-stage tank. (The depth of the deepest position of the water to be treated) may be formed at a position deeper than half (that is, the uppermost position p of the portion where the communication port is opened inside the next-stage tank) In addition, it is located below 1/2 of the depth d of the deepest position of the water to be treated in the next tank, and more preferably, the position p is located below 1/3 of the depth d. Most preferably, the position p is located below ¼ of the depth d, which are “below ½ of the depth d” and “below 3 of the depth d”. And “below ¼ of d”, etc., lead from the bottom of the water to be treated at the deepest position of the water to be treated (in other words, from the bottom of the next tank). Refers to each above "1/2 depth d", than the "1/4 of d" go position and "one-third of the depth d" is lower.

前記初段槽と前記次段槽とによって形成される槽の対を2以上直列に備え、該2以上直列に備えられる対のいずれかの対である上流対の前記次段槽から排出される被処理水を、該2以上直列に備えられる対のうち該上流対とは異なる対である下流対の前記初段槽が受け入れるもの(以下、「複数対装置」という。)であってもよい。
こうすることで初段槽と次段槽とによって形成される槽の対が複数直列に連結され、上流側に位置する対から下流側に位置する対へと被処理水が流れることで複数の対によって被処理水がうまく水質浄化される(例えば、浄化度を高くすることで、本装置によって処理された水の水質をより良くすることができる。)。
Two or more pairs of tanks formed by the first-stage tank and the next-stage tank are provided in series, and are discharged from the next-stage tank of the upstream pair that is one of the pairs provided in series of two or more. The treated water may be received by the first-stage tank of the downstream pair, which is a pair different from the upstream pair among the pairs provided in series with two or more (hereinafter, referred to as “multiple pair apparatus”).
In this way, a plurality of pairs of tanks formed by the first-stage tank and the next-stage tank are connected in series, and the treated water flows from the pair located on the upstream side to the pair located on the downstream side. As a result, the quality of the water to be treated can be improved (for example, by increasing the degree of purification, the quality of the water treated by this apparatus can be improved).

複数対装置の場合、前記上流対の前記次段槽の上端部から溢流(あふれ流れる)する被処理水を、前記下流対の前記初段槽が受け入れるもの(以下、「溢流本装置」という。)であってもよい。
こうすることで上流側に位置する対から下流側に位置する対へ被処理水を受け渡す格別の機構を要さないので、本装置を簡単に構成することができると共に、保守点検作業を減少させることができる(本装置に係る建設や維持に要する費用を抑えることができる。)。
In the case of a multi-pair device, the first-stage tank of the downstream pair receives treated water that overflows (overflows) from the upper end of the next-stage tank of the upstream pair (hereinafter referred to as “overflow main apparatus”). .).
This eliminates the need for a special mechanism for passing the treated water from the pair located upstream to the pair located downstream, so that the apparatus can be easily configured and maintenance work can be reduced. (The cost required for construction and maintenance of the apparatus can be reduced).

前記水質活性剤を表面に保持し被処理水に潜入する保持物を、さらに備えてなるもの(以下、「保持物本装置」という。)であってもよい。
こうすることで粉末状の水質活性剤が被処理水中に単に浮遊している場合に比して、水質活性剤が保持物の表面に保持されることにより水質活性剤の不意の散逸を防止又は減少させ水質活性剤を被処理水に確実に接触させることができる。なお、保持物は、初段槽及び/又は次段槽(即ち、初段槽のみの場合、次段槽のみの場合、初段槽と次段槽との両方の場合、のいずれか)の内部に配設される(無論、保持物表面に保持された水質活性剤が被処理水に接触するように保持物は配設される。)。
また、保持物としては、被処理水に潜入した状態で水質活性剤を表面に保持することができるものであればいかなるものであってもよく何ら限定されるものではないが、例えば、水質活性剤を保持する表面の面積が大きい網目状物、ラシヒリング、レシングリング、くら型等のようなものを用いてもよい。なお、ポリエチレンやポリアミド等のような樹脂材料を用いて保持物を形成すれば、水質活性剤が保持物表面にうまく保持されるので好ましい。とりわけ柔軟な樹脂材料を用いた網目状物を保持物とすれば、保持物が配設される空間の形状に合わせてうまく保持物の形状を変化させることができるので好ましい。なお、保持物の表面に水質活性剤は保持されるとは、継続(例えば、数時間以上、好ましくは1日以上、より好ましくは7日以上、最も好ましくは1月以上)して該表面に水質活性剤が保持されれば足り、永久的又は半永久的に保持されることまでは必ずしも要さない(無論、永久的又は半永久的に保持されてよいことは言うまでもない。)。
It may further comprise a retentate that retains the water quality activator on the surface and sneaks into the water to be treated (hereinafter referred to as “retained material apparatus”).
In this way, compared with the case where the powdery water activator is simply suspended in the water to be treated, the water activator is retained on the surface of the retentate, thereby preventing the sudden dissipation of the water activator. The water quality activator can be reduced and reliably contacted with the water to be treated. The retentate is placed inside the first tank and / or the next tank (that is, only the first tank, only the next tank, or both the first tank and the next tank). (Of course, the retentate is disposed such that the water quality activator retained on the retentate surface comes into contact with the water to be treated).
In addition, the retained material is not limited in any way as long as it can retain the water quality active agent on the surface in a state of being infiltrated into the water to be treated. A net-like material having a large surface area for holding the agent, a Raschig ring, a lesser ring, a crown shape, or the like may be used. In addition, it is preferable to form the retentate using a resin material such as polyethylene or polyamide because the water quality activator is well retained on the retentate surface. In particular, it is preferable to use a mesh-like object using a flexible resin material as the holding object because the shape of the holding object can be changed well according to the shape of the space in which the holding object is disposed. The retention of the water quality active agent on the surface of the retentate is continued (for example, several hours or more, preferably one day or more, more preferably seven days or more, most preferably one month or more) on the surface. It is sufficient if the water quality active agent is retained, and it is not always necessary to retain it permanently or semipermanently (of course, it may be retained permanently or semipermanently).

結合材で固形化されている前記水質活性剤が、被処理水に潜入するように配設されるものであってもよい。
ここに「結合材で固形化されている水質活性剤」とは、前特許(特許番号第2903359号)の請求項2に係る水質活性剤(即ち、結合材によって固形化されている本活性剤)であり、該活性剤の製造方法等は前特許において詳しく説明がされているのでここでは説明を省略する。
このように固形化されている水質活性剤を被処理水中に潜入させて用いることで、粉末状の水質活性剤が被処理水中に浮遊している場合に比して、水質活性剤の不意の散逸を防止又は減少させ水質活性剤を被処理水に確実に接触させることができる。なお、結合材で固形化されている水質活性剤は、初段槽及び/又は次段槽(即ち、初段槽のみの場合、次段槽のみの場合、初段槽と次段槽との両方の場合)の内部に配設される(無論、結合材で固形化されている水質活性剤が被処理水に接触するように配設される。)。
The water quality activator solidified by the binder may be disposed so as to infiltrate the water to be treated.
Here, “the water quality activator solidified by the binder” means the water quality activator according to claim 2 of the previous patent (Patent No. 2903359) (that is, the present activator solidified by the binder). The method for producing the activator and the like have been described in detail in the previous patent and will not be described here.
By using the water quality active agent that has been solidified in this way, the water quality active agent is unexpectedly used compared to the case where the powdered water quality active agent is suspended in the water to be treated. Dissipation is prevented or reduced, and the water quality activator can be brought into contact with the water to be treated. The water quality activator solidified with the binder is the first tank and / or the next tank (that is, only the first tank, only the next tank, both the first tank and the next tank). (Of course, the water quality activator solidified with the binder is arranged so as to come into contact with the water to be treated).

前記初段槽と前記次段槽とは、被処理水を収容する槽体と、該槽体の内部において前記初段槽と前記次段槽との間を仕切るように形成された隔壁と、によって形成され、該隔壁に前記連通口が形成されるものであってもよい。
こうすることで初段槽と次段槽とを、共通する槽体を用い、連通口が形成された隔壁によって槽体内部を仕切ることで形成することができるので、本装置を簡単に構成することができる。なお、「槽体」とは、その内部空間に被処理水を収容することができる器状のものであればいかなるものであってもよく何ら限定されるものではないが、例えば、底板と、該底板の周囲に立設された側板と、を含んで形成される容器状のもの(例えば、内部空間が直方体形状を有する容器状のものであってもよい。)を例示することができる。
The first-stage tank and the next-stage tank are formed by a tank body that stores the water to be treated, and a partition that is formed inside the tank body so as to partition the first-stage tank and the next-stage tank. In addition, the communication port may be formed in the partition wall.
In this way, the first stage tank and the next stage tank can be formed by using a common tank body and partitioning the inside of the tank body by a partition wall formed with a communication port. Can do. The “tank” is not limited in any way as long as it is a container that can accommodate the water to be treated in its internal space. For example, the bottom plate, And a side plate erected around the bottom plate (for example, the inner space may be a container having a rectangular parallelepiped shape).

溢流本装置の場合、前記初段槽と前記次段槽とは、被処理水を収容する槽体と、該槽体の内部において前記初段槽と前記次段槽との間を仕切るように形成された隔壁と、によって形成され、該隔壁は、同一の前記対を構成する前記初段槽と前記次段槽との間に配設され前記連通口が形成される連通口隔壁と、前記上流対の前記次段槽と前記下流対の前記初段槽との間に配設され上端部から被処理水が溢流する堰隔壁と、を含んでなり、該連通口隔壁と該堰隔壁とが交互に配設されるものであってもよい。
こうすることで初段槽と次段槽とを、共通する槽体を用い、連通口が形成された隔壁によって槽体内部を仕切ることで形成することができるので、本装置を簡単に構成することができる。なお、「槽体」とは、上述の説明と同様であるので、ここでは説明を省略する。
また、ここでは隔壁は、連通口が形成される連通口隔壁(同一の前記対を構成する初段槽と次段槽との間に配設される。)と、上端部から被処理水が溢流する堰隔壁(上流対の次段槽と下流対の初段槽との間に配設される。)と、を含み、これら連通口隔壁と堰隔壁とが交互に配設されることで、初段槽と次段槽とによって形成される槽の対を2以上直列に備える複数対装置において上流対の次段槽の上端部から溢流(あふれ流れる)する被処理水を下流対の初段槽が受け入れる溢流本装置を簡単に構成することができる。
In the case of the overflow main unit, the first-stage tank and the next-stage tank are formed so as to partition the tank body for storing the water to be treated and the first-stage tank and the next-stage tank inside the tank body. A partition wall disposed between the first-stage tank and the next-stage tank constituting the same pair, the communication port partition wall forming the communication port, and the upstream pair. A dam partition wall disposed between the next-stage tank and the downstream pair of the first-stage tanks and overflowing with water to be treated from an upper end portion, wherein the communication port partition walls and the dam partition walls are alternately arranged. It may be arranged in.
In this way, the first stage tank and the next stage tank can be formed by using a common tank body and partitioning the inside of the tank body by a partition wall formed with a communication port. Can do. Note that the “tank” is the same as described above, and thus the description thereof is omitted here.
In addition, here, the partition wall is a communication port partition wall (formed between the first tank and the next tank forming the same pair) in which a communication port is formed, and the water to be treated overflows from the upper end. And a weir partition wall (disposed between the upstream pair next-stage tank and the downstream pair first-stage tank), and these communication port partition walls and weir partition walls are alternately disposed, In a multi-pair device comprising two or more tank pairs formed in series by the first-stage tank and the next-stage tank, the first-stage tank of the downstream pair is treated with the treated water that overflows (overflows) from the upper end of the next-stage tank of the upstream pair. It is possible to easily construct the overflow apparatus to be received by the apparatus.

前記被処理水が、酸素ガスを含む気体と接触するもの(以下、「酸素接触本装置」という。)であってもよい。
こうすることで酸素ガスを含む気体と被処理水との接触により被処理水中に酸素ガスが溶解し(被処理水中に溶存酸素ガスが存在する。)、本活性剤による被処理水の水質浄化がうまく行われる。
「酸素ガスを含む気体」とは、酸素ガスを含み被処理水と好ましくない反応を生じないものであればいかなるものであってもよく何ら限定されるものではないが、例えば、空気や、不活性ガス(例えば、窒素、希ガス(ヘリウム、ネオン、アルゴン等)等)と酸素ガスとを含む混合気体等を例示することができる。
The water to be treated may be in contact with a gas containing oxygen gas (hereinafter referred to as “oxygen contact apparatus”).
By doing so, the oxygen gas is dissolved in the water to be treated by contact between the gas containing oxygen gas and the water to be treated (the dissolved oxygen gas exists in the water to be treated), and the water purification of the water to be treated by the present activator is performed. Is done well.
The “gas containing oxygen gas” is not particularly limited as long as it contains oxygen gas and does not cause an undesirable reaction with the water to be treated. Examples thereof include a mixed gas containing an active gas (for example, nitrogen, a rare gas (such as helium, neon, or argon)) and an oxygen gas.

酸素接触本装置の場合、前記初段槽及び前記次段槽の少なくとも一方が、該一方が保有する被処理水の上方に前記気体(酸素ガスを含む気体)が存する空間を有するものであってもよい。
こうすることで初段槽や次段槽が保有する被処理水と、該被処理水の上方に存する酸素ガスを含む気体と、をうまく簡単に接触(被処理水の水面と該気体とが接触する。)させることができるので、酸素接触本装置を簡単に構成することができる。なお、初段槽及び次段槽の両方が、被処理水の上方に前記気体(酸素ガスを含む気体)が存する空間を有するようにしてよいことは言うまでもない。
In the case of this oxygen contact apparatus, even if at least one of the first-stage tank and the next-stage tank has a space in which the gas (gas containing oxygen gas) exists above the water to be treated, which one of the tanks holds. Good.
By doing so, the water to be treated in the first tank and the next tank and the gas containing oxygen gas existing above the water to be treated can be easily and easily contacted (the water surface of the water to be treated and the gas are in contact with each other). Therefore, the oxygen contact apparatus can be configured easily. Needless to say, both the first-stage tank and the next-stage tank may have a space where the gas (gas containing oxygen gas) exists above the water to be treated.

保持物本装置を用いて被処理水の水質を浄化する場合、保持物の表面に本活性剤を保持させる必要がある。このためには保持物の表面に、水中に懸濁又は溶解した本活性剤を接触させることでうまく保持させることができる。また、水中に懸濁又は溶解した本活性剤を表面に接触させた保持物は水分が付着している等によって取扱が煩雑になりやすいことから、水中に懸濁又は溶解した本活性剤を接触させる前に保持物を所定位置(保持物本装置が被処理水を水質浄化する際に保持物が存すべき位置をいう。通常、初段槽や次段槽の内部である。)に予め配設しておき、その後、水中に懸濁又は溶解した本活性剤を接触させれば作業をうまく行うことができる。即ち、保持物本装置を用いて被処理水の水質を浄化する場合、所定位置に配設した前記保持物に、水中に懸濁又は溶解した前記水質活性剤を接触させる接触ステップと、該接触ステップの後、前記被処理水を前記初段槽に連続的に供給する供給ステップと、を含むようにしてもよい。   When purifying the quality of the water to be treated using the retained material apparatus, it is necessary to retain the active agent on the surface of the retained material. For this purpose, the active agent suspended or dissolved in water can be successfully held on the surface of the retentate. In addition, the retentate that is brought into contact with the surface of the active agent suspended or dissolved in water tends to be cumbersome due to moisture adhering to it, so that the active agent suspended or dissolved in water is contacted. Before holding, the holding material is arranged in advance in a predetermined position (the position where the holding material should be present when the holding material main apparatus purifies the water to be treated. Usually, it is inside the first-stage tank or the next-stage tank). Then, if the active agent suspended or dissolved in water is brought into contact, the operation can be performed successfully. That is, when purifying the quality of water to be treated using the retentate apparatus, a contact step of bringing the water quality activator suspended or dissolved in water into contact with the retentate disposed at a predetermined position; After the step, a supply step of continuously supplying the water to be treated to the first tank may be included.

以下、本発明の実施の形態を図面を参照して説明する。しかしながら、これらによって本発明は何ら制限されるものではない。   Hereinafter, embodiments of the present invention will be described with reference to the drawings. However, the present invention is not limited by these.

図1は、一実施形態の本発明の水質浄化装置(本装置)11の正面図であり、図2は、図1のA−A断面図(後述の槽体13や隔壁21a1、21a2、21a3、21a4、21a5、21a6、21b1、21b2、21b3、21b4、21b5等の理解を容易にするための概略断面図であり、後述の保持物15や固形活性剤17は図示していない。)である。図1及び図2を参照して、本装置11について説明する。
本装置11は、大まかには、被処理水を収容する槽体13と、槽体13の内部に配設された隔壁21a1、21a2、21a3、21a4、21a5、21a6、21b1、21b2、21b3、21b4、21b5と、本活性剤を表面に保持し被処理水に潜入する保持物15と、結合材で固形化されている本活性剤(以下、「固形活性剤」という。)17と、を備えてなる。なお、図1中、(鉛直)上方向を矢印Bにて、そして(鉛直)下方向を矢印Cにて、それぞれ示した。また、図2中、後述する第1槽31a、第2槽31b、第3槽31c、第4槽31d、第5槽31e、第6槽31f、第7槽31g、第8槽31h、第9槽31i、第10槽31j、第11槽31k及び第12槽31lの内部に記載された寸法は、各槽の長さLに沿った寸法を記載したものである。
FIG. 1 is a front view of a water purification device (this device) 11 according to an embodiment of the present invention, and FIG. 2 is a cross-sectional view taken along a line AA in FIG. 1 (a tank body 13 and partition walls 21a1, 21a2, 21a3 described later). , 21a4, 21a5, 21a6, 21b1, 21b2, 21b3, 21b4, 21b5, etc. are schematic cross-sectional views for facilitating understanding, and the retainer 15 and the solid activator 17 described later are not shown. . The apparatus 11 will be described with reference to FIGS. 1 and 2.
In general, the apparatus 11 includes a tank body 13 for storing the water to be treated, and partition walls 21a1, 21a2, 21a3, 21a4, 21a5, 21a6, 21b1, 21b2, 21b3, 21b4 disposed inside the tank body 13. 21b5, a retentate 15 that holds the active agent on the surface and infiltrates into the water to be treated, and a main active agent (hereinafter referred to as “solid active agent”) 17 that is solidified with a binder. It becomes. In FIG. 1, the (vertical) upward direction is indicated by an arrow B, and the (vertical) downward direction is indicated by an arrow C. In FIG. 2, a first tank 31a, a second tank 31b, a third tank 31c, a fourth tank 31d, a fifth tank 31e, a sixth tank 31f, a seventh tank 31g, an eighth tank 31h, a ninth tank, which will be described later. The dimensions described inside the tank 31i, the tenth tank 31j, the eleventh tank 31k, and the twelfth tank 31l are the dimensions along the length L of each tank.

槽体13は、コンクリートによって形成された中空の略直方体形状を有しており、その内部空間13aも略直方体形状を有している。具体的には、槽体13は、略水平に略長方形の主表面を向けて配設された底板13bと、底板13bの周囲に略鉛直方向に向けて立設された側板13cと、略水平に略長方形の主表面を向けて配設された蓋板13dと、を含んで形成される容器状をしている。なお、槽体13が形成する略直方体の12の辺のうち、4の辺は鉛直方向に略向いており、残りの8の辺は水平方向に略向くように槽体13は配設されている。
なお、ここでの槽体13の内部空間13aの寸法は、長さL=125cm(図1及び2参照)、幅W=15cm(図2参照)、高さH=50cm(図1参照)であった。
The tank body 13 has a hollow, substantially rectangular parallelepiped shape made of concrete, and its internal space 13a also has a substantially rectangular parallelepiped shape. Specifically, the tank body 13 includes a bottom plate 13b disposed substantially horizontally with a substantially rectangular main surface facing, a side plate 13c erected around the bottom plate 13b in a substantially vertical direction, and substantially horizontal. And a lid plate 13d disposed with the substantially rectangular main surface facing the main body. Of the 12 sides of the substantially rectangular parallelepiped formed by the tank body 13, the tank body 13 is arranged so that 4 sides are substantially oriented in the vertical direction and the remaining 8 sides are substantially oriented in the horizontal direction. Yes.
In addition, the dimension of the internal space 13a of the tank body 13 here is length L = 125cm (refer FIG.1 and 2), width W = 15cm (refer FIG.2), and height H = 50cm (refer FIG.1). there were.

隔壁21a1、21a2、21a3、21a4、21a5、21a6、21b1、21b2、21b3、21b4、21b5は、いずれも略長方形の主表面を有する板状をしており、互いの主表面が略平行になるように槽体13の内部空間13aを規定する内壁に取り付けられている(それぞれの主表面は、略鉛直に向いている。)。
隔壁21a1、21a2、21a3、21a4、21a5、21a6、21b1、21b2、21b3、21b4、21b5は、隔壁の下端と槽体13の内壁との間に連通口23a1、23a2、23a3、23a4、23a5、23a6が形成される連通口隔壁21a1、21a2、21a3、21a4、21a5、21a6と、上端部から被処理水が溢流する堰隔壁21b1、21b2、21b3、21b4、21b5と、の2種類が配設されている。なお、連通口隔壁21a1、21a2、21a3、21a4、21a5、21a6の下端部(下縁)は、一の水平面に略属するようにされている(即ち、連通口隔壁21a1、21a2、21a3、21a4、21a5、21a6の下端部(下縁)の高さはほぼ同じである。)。また、堰隔壁21b1、21b2、21b3、21b4、21b5の上端部(上縁)は、一の水平面に略属するようにされている(即ち、堰隔壁21b1、21b2、21b3、21b4、21b5の上端部(上縁)の高さはほぼ同じである。)。そして、これら連通口隔壁21a1、21a2、21a3、21a4、21a5、21a6と、堰隔壁21b1、21b2、21b3、21b4、21b5と、は、図1及び図2中の右側から左側に向かって(即ち、後述するように被処理水が流れる方向に沿って)、連通口隔壁21a1、堰隔壁21b1、連通口隔壁21a2、堰隔壁21b2、連通口隔壁21a3、堰隔壁21b3、連通口隔壁21a4、堰隔壁21b4、連通口隔壁21a5、堰隔壁21b5、連通口隔壁21a6のように連通口隔壁と堰隔壁とが交互に配設されている。
Each of the partition walls 21a1, 21a2, 21a3, 21a4, 21a5, 21a6, 21b1, 21b2, 21b3, 21b4, and 21b5 has a plate shape having a substantially rectangular main surface so that the main surfaces are substantially parallel to each other. Are attached to the inner wall defining the internal space 13a of the tank body 13 (the main surfaces of the tank body 13 are oriented substantially vertically).
The partition walls 21a1, 21a2, 21a3, 21a4, 21a5, 21a6, 21b1, 21b2, 21b3, 21b4, 21b5 are communication ports 23a1, 23a2, 23a3, 23a4, 23a5, 23a6 between the lower ends of the partition walls and the inner wall of the tank body 13. There are provided two types of communication port partition walls 21a1, 21a2, 21a3, 21a4, 21a5, 21a6, and weir partition walls 21b1, 21b2, 21b3, 21b4, 21b5 where the water to be treated overflows from the upper end. ing. Note that the lower end portions (lower edges) of the communication port partition walls 21a1, 21a2, 21a3, 21a4, 21a5, and 21a6 substantially belong to one horizontal plane (that is, the communication port partition walls 21a1, 21a2, 21a3, 21a4, The heights of the lower ends (lower edges) of 21a5 and 21a6 are substantially the same.) Further, the upper end portions (upper edges) of the dam partitions 21b1, 21b2, 21b3, 21b4, and 21b5 belong to one horizontal plane (that is, the upper ends of the dam partitions 21b1, 21b2, 21b3, 21b4, and 21b5). (The height of the upper edge is almost the same.) And these communication port partition walls 21a1, 21a2, 21a3, 21a4, 21a5, 21a6 and dam partition walls 21b1, 21b2, 21b3, 21b4, 21b5 are directed from the right side to the left side in FIGS. As described later, along the direction in which the water to be treated flows), the communication port partition wall 21a1, the dam partition wall 21b1, the communication port partition wall 21a2, the dam partition wall 21b2, the communication port partition wall 21a3, the dam partition wall 21b3, the communication port partition wall 21a4, and the dam partition wall 21b4. The communication port partition walls and the weir partition walls are alternately arranged like a communication port partition wall 21a5, a weir partition wall 21b5, and a communication port partition wall 21a6.

これら隔壁21a1、21a2、21a3、21a4、21a5、21a6、21b1、21b2、21b3、21b4、21b5と、槽体13の内部空間13aを規定する内壁と、によって、槽体13の内部空間13aに複数の槽が形成されている。具体的には、図1及び図2中の右側から左側に向かって(即ち、後述するように被処理水が流れる方向に沿って)、第1槽31a、第2槽31b、第3槽31c、第4槽31d、第5槽31e、第6槽31f、第7槽31g、第8槽31h、第9槽31i、第10槽31j、第11槽31k及び第12槽31lの12の槽が形成されている。
そして、第1槽31aから第2槽31bへは連通口23a1により連通し、第2槽31bから第3槽31cへは堰隔壁21b1の上方の空間(槽体13の内部空間13a)により連通し、第3槽31cから第4槽31dへは連通口23a2により連通し、第4槽31dから第5槽31eへは堰隔壁21b2の上方の空間(槽体13の内部空間13a)により連通し、第5槽31eから第6槽31fへは連通口23a3により連通し、第6槽31fから第7槽31gへは堰隔壁21b3の上方の空間(槽体13の内部空間13a)により連通し、第7槽31gから第8槽31hへは連通口23a4により連通し、第8槽31hから第9槽31iへは堰隔壁21b4の上方の空間(槽体13の内部空間13a)により連通し、第9槽31iから第10槽31jへは連通口23a5により連通し、第10槽31jから第11槽31kへは堰隔壁21b5の上方の空間(槽体13の内部空間13a)により連通し、第11槽31kから第12槽31lへは連通口23a6により連通している。
These partition walls 21a1, 21a2, 21a3, 21a4, 21a5, 21a6, 21b1, 21b2, 21b3, 21b4, 21b5 and an inner wall that defines the inner space 13a of the tank body 13 have a plurality of internal spaces 13a. A tank is formed. Specifically, from the right side to the left side in FIGS. 1 and 2 (that is, along the direction in which the water to be treated flows as described later), the first tank 31a, the second tank 31b, and the third tank 31c. 12 tanks of 4th tank 31d, 5th tank 31e, 6th tank 31f, 7th tank 31g, 8th tank 31h, 9th tank 31i, 10th tank 31j, 11th tank 31k, and 12th tank 31l. Is formed.
The first tank 31a communicates with the second tank 31b through the communication port 23a1, and the second tank 31b communicates with the third tank 31c through the space above the weir partition wall 21b1 (the internal space 13a of the tank body 13). The third tank 31c communicates with the fourth tank 31d through the communication port 23a2, and the fourth tank 31d communicates with the fifth tank 31e through the space above the weir partition wall 21b2 (the internal space 13a of the tank body 13). The fifth tank 31e communicates with the sixth tank 31f through the communication port 23a3, and the sixth tank 31f communicates with the seventh tank 31g through the space above the weir partition wall 21b3 (the internal space 13a of the tank body 13). The seventh tank 31g communicates with the eighth tank 31h through the communication port 23a4, and the eighth tank 31h communicates with the ninth tank 31i through the space above the weir bulkhead 21b4 (the internal space 13a of the tank body 13). No. from tank 31i The 0 tank 31j communicates with the communication port 23a5, the 10th tank 31j communicates with the 11th tank 31k via the space above the weir partition wall 21b5 (the internal space 13a of the tank body 13), and the 11th tank 31k to the 12th tank. The tank 31l communicates with the communication port 23a6.

槽体13(蓋板13d)には、第1槽31aの上方に位置するように被処理水(原水)41の注入口43が形成されている。かかる注入口43から注入された被処理水(原水)41は第1槽31aへ進入する。
一方、第12槽31lを規定する槽体13の側板13cの所定の高さには、被処理水(処理済水)51が流出する排水口53が形成されている。
The tank body 13 (lid plate 13d) is formed with an inlet 43 for water to be treated (raw water) 41 so as to be positioned above the first tank 31a. Water to be treated (raw water) 41 injected from the injection port 43 enters the first tank 31a.
On the other hand, a drain port 53 through which treated water (treated water) 51 flows out is formed at a predetermined height of the side plate 13c of the tank body 13 that defines the twelfth tank 31l.

そして、第1槽31a、第2槽31b、第3槽31c、第4槽31d、第5槽31e、第6槽31f、第7槽31g、第8槽31h、第9槽31i、第10槽31j、第11槽31k及び第12槽31lそれぞれの下部には、保持物15が充填されている。ここでは保持物15としては、東京戸張株式会社の製品名称:PE防鳥網Aー50(網目の大きさは45mmの略正方形)を用い、各槽それぞれに9m×1.6mのPE防鳥網Aー50を2枚ずつ充填している(即ち、本装置11全体では、9m×1.6mのPE防鳥網Aー50が、2枚/槽×12槽=24枚用いられている。)。
なお、第1槽31a、第2槽31b、第3槽31c、第4槽31d、第5槽31e、第6槽31f、第7槽31g、第8槽31h、第9槽31i、第10槽31j、第11槽31k及び第12槽31lに充填された保持物15は、排水口53よりも充分低い位置に配設されている(充填された保持物15の上面は、排水口53よりも低い。)。
And the 1st tank 31a, the 2nd tank 31b, the 3rd tank 31c, the 4th tank 31d, the 5th tank 31e, the 6th tank 31f, the 7th tank 31g, the 8th tank 31h, the 9th tank 31i, the 10th tank The holding | maintenance 15 is filled in the lower part of 31j, the 11th tank 31k, and the 12th tank 31l. Here, as the retainer 15, the product name of Tokyo Tobari Co., Ltd .: PE bird net A-50 (mesh size is approximately square of 45 mm) is used, and each tank has a PE bird of 9 m × 1.6 m. Two pieces of mesh A-50 are filled (that is, the entire apparatus 11 uses 9 m × 1.6 m PE bird net A-50, 2 sheets / tank × 12 tanks = 24 sheets). .)
The first tank 31a, the second tank 31b, the third tank 31c, the fourth tank 31d, the fifth tank 31e, the sixth tank 31f, the seventh tank 31g, the eighth tank 31h, the ninth tank 31i, and the tenth tank. 31j, the 11th tank 31k, and the 12th tank 31l filled with the retentate 15 are disposed at a position sufficiently lower than the drain port 53 (the upper surface of the filled retentate 15 is higher than the drain port 53. Low.).

さらに、第2槽31bの内部のうち、保持物15の上方であって排水口53よりも低い位置(後述するように、点線Mによって示される水面位置よりも低い位置)に、固形活性剤17が配設されている。ここでは図示していないが、固形状の固形活性剤17は、堰隔壁21b1の上端部に一端が取り付けられた線材の他端に吊り下げられ支持されることで所定位置に配置されている。
なお、固形活性剤17は、前特許(特許番号第2903359号)の請求項2に係る水質活性剤を用いており、該活性剤の製造方法等は前特許公報において詳しく説明がされているのでここでは説明を省略する。
Furthermore, in the second tank 31b, the solid activator 17 is positioned above the retentate 15 and lower than the drain port 53 (a position lower than the water surface position indicated by the dotted line M, as will be described later). Is arranged. Although not shown here, the solid solid activator 17 is arranged at a predetermined position by being suspended and supported by the other end of a wire rod having one end attached to the upper end of the weir partition wall 21b1.
The solid activator 17 uses the water quality activator according to claim 2 of the previous patent (Patent No. 2903359), and the method for producing the activator is described in detail in the previous patent publication. The description is omitted here.

かかる本装置11の使用方法を説明する。
まず、予め保持物15(本活性剤が表面に保持される前のもの)及び固形状の固形活性剤17を配設する。具体的には、東京戸張株式会社の網(製品名称:PE防鳥網Aー50)を折り畳んだものによって構成される保持物15(本活性剤が表面に保持される前のもの)を、第1槽31a、第2槽31b、第3槽31c、第4槽31d、第5槽31e、第6槽31f、第7槽31g、第8槽31h、第9槽31i、第10槽31j、第11槽31k及び第12槽31lそれぞれの所定位置(図1に示すように各槽の下部)に充填し配設する。そして、固形状の固形活性剤17を、堰隔壁21b1の上端部に一端が取り付けられた線材の他端に吊り下げ支持することで所定位置に配設する。
A method of using the apparatus 11 will be described.
First, the holding | maintenance thing 15 (thing before this active agent is hold | maintained on the surface) and the solid-state solid active agent 17 are arrange | positioned previously. Specifically, a retainer 15 (before the active agent is retained on the surface) constituted by a folded net (product name: PE bird net A-50) of Tokyo Tohari Co., Ltd., 1st tank 31a, 2nd tank 31b, 3rd tank 31c, 4th tank 31d, 5th tank 31e, 6th tank 31f, 7th tank 31g, 8th tank 31h, 9th tank 31i, 10th tank 31j, It fills and arrange | positions to the predetermined position (lower part of each tank as shown in FIG. 1) of each of the 11th tank 31k and the 12th tank 31l. And solid solid activator 17 is arrange | positioned in a predetermined position by suspending and supporting to the other end of the wire rod which one end was attached to the upper end part of dam partition 21b1.

第1に、被処理水(原水)41の注入口43から水(例えば、上水、工業用水等)を注入し、槽体13の内部空間13aの所定深さまで水を張り込む。この所定深さは、図1中、点線M(排水口53から水があふれ始める位置)によって示されている(なお、点線Mに水面がきた場合、槽体13の内部空間13aに張り込まれる水は約90リットルである。)。
第2に、粉体の本活性剤(前特許(特許番号第2903359号)の請求項1に係る水質活性剤)27gを水2リットルに投入し、充分攪拌混合した。得られた本活性剤と水との混合物(以下、「本混合物」という。)を注入口43から槽体13の内部空間13a(具体的には、第1槽31a)へ注入する。
First, water (for example, clean water, industrial water, etc.) is injected from the inlet 43 of the water to be treated (raw water) 41, and water is filled to a predetermined depth in the internal space 13a of the tank body 13. This predetermined depth is indicated by a dotted line M (a position where water begins to overflow from the drain port 53) in FIG. 1 (when the water surface comes to the dotted line M, it is stuck in the internal space 13a of the tank body 13). Water is about 90 liters).
Secondly, 27 g of the powdery activator (the water quality activator according to claim 1 of the previous patent (Patent No. 2903359)) was put into 2 liters of water and sufficiently stirred and mixed. The obtained mixture of the active agent and water (hereinafter referred to as “the present mixture”) is injected from the injection port 43 into the internal space 13a of the tank body 13 (specifically, the first tank 31a).

第3に、被処理水(原水)41を注入口43から槽体13の内部空間13a(具体的には、第1槽31a)へ注入する。被処理水(原水)41の注入は、35日間連続して行われ、毎日250リットル/日をほぼ一定の体積流量にて注入した(即ち、該一定の体積流量は、250リットル/24時間=約10.4リットル/時間である。)。なお、ここでは被処理水(原水)41として食品加工所の廃水を用い、その分析結果を表1に示す(表1中、「l(リットル)」は「l」がリットルを表していることを示している。)。また、前述したように、点線Mに水面がある場合、槽体13の内部空間13aに張り込まれる水は約90リットルであるので、被処理水が槽体13の内部空間13aへ滞留する平均滞留時間は90リットル/(10.4リットル/時間)=8〜9時間である。
被処理水(原水)41の注入を開始すると、上記第2において第1槽31aに注入された本混合物は、連通口23a1を経て第1槽31aから第2槽31bへ移動し、第2槽31bから第3槽31cへは堰隔壁21b1の上部を溢流して移動し、第3槽31cから第4槽31dへは連通口23a2を経て移動し、第4槽31dから第5槽31eへは堰隔壁21b2の上部を溢流して移動し、第5槽31eから第6槽31fへは連通口23a3を経て移動し、第6槽31fから第7槽31gへは堰隔壁21b3の上部を溢流して移動し、第7槽31gから第8槽31hへは連通口23a4を経て移動し、第8槽31hから第9槽31iへは堰隔壁21b4の上部を溢流して移動し、第9槽31iから第10槽31jへは連通口23a5を経て移動し、第10槽31jから第11槽31kへは堰隔壁21b5の上部を溢流して移動し、第11槽31kから第12槽31lへは連通口23a6を経て移動する。このように本混合物が第1槽31aから第12槽31lへ移動する間に、第1槽31aから第12槽31lまでの各槽に配設された保持物15(本活性剤が表面に保持される前のもの)と本混合物とが接触し、本混合物に含まれる本活性剤が、第1槽31aから第12槽31lまでの各槽に配設された保持物15の表面に保持される。
また、注入された被処理水(原水)41も、第1槽31a、第2槽31b、第3槽31c、第4槽31d、第5槽31e、第6槽31f、第7槽31g、第8槽31h、第9槽31i、第10槽31j、第11槽31k及び第12槽31lをこの順番で移動(本活性剤を表面に保持した保持物15の該表面との接触を含む。また、第2槽31bにおいては、固形活性剤17とも接触する。)し、この移動中に水質が浄化され、最終的には被処理水(処理済水)51として排水口53からあふれ出ることで排水される。
Third, water to be treated (raw water) 41 is injected from the inlet 43 into the internal space 13a of the tank body 13 (specifically, the first tank 31a). The water to be treated (raw water) 41 was continuously injected for 35 days, and 250 liters / day was injected every day at a substantially constant volume flow rate (that is, the constant volume flow rate was 250 liters / 24 hours = About 10.4 liters / hour). In this case, wastewater from a food processing plant is used as treated water (raw water) 41, and the analysis results are shown in Table 1 (in Table 1, “l (liter)” means “l” means liter). Is shown.) Further, as described above, when there is a water surface on the dotted line M, since the water to be inserted into the internal space 13a of the tank body 13 is about 90 liters, the average of the water to be treated staying in the internal space 13a of the tank body 13 The residence time is 90 liters / (10.4 liters / hour) = 8-9 hours.
When the injection of the water to be treated (raw water) 41 is started, the mixture injected into the first tank 31a in the second is moved from the first tank 31a to the second tank 31b via the communication port 23a1, and the second tank From 31b to the third tank 31c, the upper part of the dam 21b1 overflows and moves, from the third tank 31c to the fourth tank 31d moves through the communication port 23a2, and from the fourth tank 31d to the fifth tank 31e. It overflows and moves over the upper part of the dam partition wall 21b2, moves from the fifth tank 31e to the sixth tank 31f via the communication port 23a3, and overflows from the sixth tank 31f to the seventh tank 31g over the upper part of the dam partition wall 21b3. Move from the seventh tank 31g to the eighth tank 31h via the communication port 23a4, and move from the eighth tank 31h to the ninth tank 31i by overflowing the upper portion of the weir partition wall 21b4, and the ninth tank 31i. To the 10th tank 31j through the communication port 23a5 And, from the 10th tank 31j to 11 tank 31k moves to overflow the top of the weir bulkhead 21b5, the eleventh tank 31k to 12th tank 31l moves through the communication port 23a6. Thus, while this mixture moves from the 1st tank 31a to the 12th tank 31l, the holding | maintenance material 15 (this active agent hold | maintains on the surface) arrange | positioned in each tank from the 1st tank 31a to the 12th tank 31l. The active agent contained in the mixture is held on the surface of the holding material 15 disposed in each tank from the first tank 31a to the twelfth tank 31l. The
In addition, the treated water (raw water) 41 injected also includes the first tank 31a, the second tank 31b, the third tank 31c, the fourth tank 31d, the fifth tank 31e, the sixth tank 31f, the seventh tank 31g, The 8th tank 31h, the 9th tank 31i, the 10th tank 31j, the 11th tank 31k, and the 12th tank 31l are moved in this order (including the contact with the surface of the retentate 15 holding the activator on the surface. In the second tank 31b, the solid activator 17 is also contacted.) During this movement, the water quality is purified, and finally overflows from the drain port 53 as treated water (treated water) 51. Drained.

(表1)被処理水(原水)の分析結果
・透視度:9.0度
・pH:5.0
・BOD:100mg/l(リットル)
・CODMn:89mg/l(リットル)
・SS:45mg/l(リットル)
・全窒素:8.38mg/l(リットル)
・全燐:1.50mg/l(リットル)
(Table 1) Analysis result of treated water (raw water)-Permeability: 9.0 degrees-pH: 5.0
・ BOD: 100mg / l (liter)
-CODMn: 89 mg / l (liter)
・ SS: 45mg / l (liter)
・ Total nitrogen: 8.38 mg / l (liter)
・ Total phosphorus: 1.50 mg / l (liter)

第4に、被処理水(原水)41の注入を開始してから35日経過後、排水口53から排水されている被処理水(処理済水)51を採取し、上述した被処理水(原水)41の分析と同様の分析を行った。その被処理水(処理済水)51の分析結果を表2に示す。
なお、被処理水(原水)41の注入を開始してから35日が経過するまでに被処理水(原水)41のCODMn値は、約70〜250mg/l(リットル)程度の範囲で日々変動したが、この変動幅に比して被処理水(処理済水)51のCODMn値の変動は極めて小さかった。
また、被処理水の浄化機構は必ずしも明らかではないが、次のように推測される。即ち、被処理水(原水)41の注入を開始してから1〜2週間程度で、保持物15の表面に汚泥状の物質が付着し成長することが観察される。該汚泥状の物質中に生物相が生じ、この生物相によって水質が浄化されるものと推測される。
Fourth, after 35 days from the start of the injection of the treated water (raw water) 41, the treated water (treated water) 51 drained from the drain port 53 is collected and the treated water (raw water) described above is collected. ) The same analysis as 41 was performed. The analysis results of the treated water (treated water) 51 are shown in Table 2.
In addition, the CODMn value of the water to be treated (raw water) 41 fluctuates every day in the range of about 70 to 250 mg / l (liter) until 35 days have passed since the injection of the water to be treated (raw water) 41 was started. However, the change in the CODMn value of the water to be treated (treated water) 51 was extremely small compared to this fluctuation range.
Moreover, although the purification mechanism of to-be-processed water is not necessarily clear, it estimates as follows. That is, it is observed that a sludge-like substance adheres to the surface of the retentate 15 and grows in about one to two weeks after the injection of the water to be treated (raw water) 41 is started. It is presumed that biota is generated in the sludge-like substance, and water quality is purified by this biota.

(表2)被処理水(処理済水)の分析結果
・透視度:13.0度
・pH:5.9
・BOD:53mg/l(リットル)
・CODMn:35mg/l(リットル)
・SS:13mg/l(リットル)
・全窒素:5.21mg/l(リットル)
・全燐:0.90mg/l(リットル)
(Table 2) Analysis result of treated water (treated water)-Permeability: 13.0 degrees-pH: 5.9
・ BOD: 53mg / l (liter)
-CODMn: 35 mg / l (liter)
SS: 13 mg / l (liter)
・ Total nitrogen: 5.21 mg / l (liter)
・ Total phosphorus: 0.90 mg / l (liter)

このように本装置11は簡単に構成することができ、空気等のエアー曝気を行う必要がなくかつ第1槽31a、第2槽31b、第3槽31c、第4槽31d、第5槽31e、第6槽31f、第7槽31g、第8槽31h、第9槽31i、第10槽31j、第11槽31k及び第12槽31lの各槽を自然に移動(自然流下)する中で被処理水(原水)41をうまく水質浄化することができる。空気等のエアー曝気や、被処理水の強制移動(例えば、ポンプによる圧送や、モータにより駆動される攪拌羽根による攪拌等)を要さないことから、これらに要する構成を省略することができるので、本装置11は、該構成を付設する場合に比して簡単に構成することができると共に、該構成の保守点検に要する費用を削減することができる。
なお、本装置11は、被処理水(原水)41の水質や量等に応じて適宜設計を変更することができることは言うまでもない。例えば、水路(第1槽31a、第2槽31b、第3槽31c、第4槽31d、第5槽31e、第6槽31f、第7槽31g、第8槽31h、第9槽31i、第10槽31j、第11槽31k及び第12槽31lによって構成される被処理水が流れる流路)の寸法(例えば、第1槽31aから第12槽31lの各槽の水平面内における寸法や深さ)を変更したり、被処理水の平均滞留時間を変えたり(槽体13の内部空間13aの容量や、被処理水(原水)41の供給体積速度を変更する等)、本活性剤を表面に保持した保持物15の量を変更したり、固形状の固形活性剤17の量(第2槽31b中に配設する固形活性剤17の量を変更することや、固形活性剤17を配設する槽の数を変更することもできる。)を変更したりを自由に行うことができる。
また、ここでは被処理水の温度は約20℃であったが、必要に応じて加温や冷却が行われてよいことは言うまでもない。
In this way, the present apparatus 11 can be simply configured, and it is not necessary to perform air aeration such as air, and the first tank 31a, the second tank 31b, the third tank 31c, the fourth tank 31d, and the fifth tank 31e. The sixth tank 31f, the seventh tank 31g, the eighth tank 31h, the ninth tank 31i, the tenth tank 31j, the eleventh tank 31k, and the twelfth tank 31l are naturally moved (naturally flowed). The treated water (raw water) 41 can be purified with good water quality. Since it does not require air aeration such as air or forced movement of the water to be treated (for example, pumping by pump or stirring by a stirring blade driven by a motor), the configuration required for these can be omitted. The apparatus 11 can be easily configured as compared with the case where the configuration is attached, and can reduce the cost required for maintenance and inspection of the configuration.
In addition, it cannot be overemphasized that this apparatus 11 can change a design suitably according to the water quality, quantity, etc. of to-be-processed water (raw water) 41. FIG. For example, a water channel (first tank 31a, second tank 31b, third tank 31c, fourth tank 31d, fifth tank 31e, sixth tank 31f, seventh tank 31g, eighth tank 31h, ninth tank 31i, The dimension (depth, for example, in the horizontal plane of each tank from the first tank 31a to the twelfth tank 31l) of the tenth tank 31j, the eleventh tank 31k, and the twelfth tank 31l. ), Changing the average residence time of the water to be treated (changing the capacity of the internal space 13a of the tank body 13, the supply volume speed of the water to be treated (raw water) 41, etc.) The amount of the retentate 15 held in the container is changed, the amount of the solid solid activator 17 (the amount of the solid activator 17 disposed in the second tank 31b is changed, or the solid activator 17 is disposed. You can change the number of tanks to be installed.) It can be.
Moreover, although the temperature of to-be-processed water was about 20 degreeC here, it cannot be overemphasized that heating and cooling may be performed as needed.

以上説明したように、本装置11は、酸化処理により殺菌し、吸着性と空気溶解効率とを向上させるとともに、微生物培地に適するようにした多孔質の火山礫と黒土との混合物から得られる礫状物、及び又は粘土状物を粉末化した粉末物からなる水質活性剤(即ち、本活性剤(前特許(特許番号第2903359号)の請求項1に係る水質活性剤))を用いる水質浄化装置である。本装置11は、上方から被処理水を連続的に受け入れ被処理水を所定量保有する初段槽(第1槽31a、第3槽31c、第5槽31e、第7槽31g、第9槽31i、第11槽31k)と、該初段槽(第1槽31a、第3槽31c、第5槽31e、第7槽31g、第9槽31i、第11槽31k)から排出される被処理水を連続的に受け入れ被処理水を所定量保有する次段槽(第2槽31b、第4槽31d、第6槽31f、第8槽31h、第10槽31j、第12槽31l)と、該初段槽(第1槽31a、第3槽31c、第5槽31e、第7槽31g、第9槽31i、第11槽31k)に保有される被処理水中と該次段槽(第2槽31b、第4槽31d、第6槽31f、第8槽31h、第10槽31j、第12槽31l)に保有される被処理水中とを連通させる連通口23a1、23a2、23a3、23a4、23a5、23a6と、を備えてなり、そして該初段槽(第1槽31a、第3槽31c、第5槽31e、第7槽31g、第9槽31i、第11槽31k)及び該次段槽(第2槽31b、第4槽31d、第6槽31f、第8槽31h、第10槽31j、第12槽31l)の両方が保有する被処理水に該水質活性剤(本活性剤)が接触する(第2槽31bにおいては固形状の固形活性剤17(本活性剤が固形化されたものである。)と、保持物15の表面に保持された本活性剤と、が接触し、第2槽31b以外の槽それぞれにおいては保持物15の表面に保持された本活性剤が接触する。)。
なお、初段槽たる第1槽31aに対応する次段槽は第2槽31bであり、かかる初段槽たる第1槽31aに保有される被処理水中と次段槽たる第2槽31bに保有される被処理水中とを連通口23a1が連通させる。同様に、初段槽たる第3槽31cに対応する次段槽は第4槽31dであり、かかる初段槽たる第3槽31cに保有される被処理水中と次段槽たる第4槽31dに保有される被処理水中とを連通口23a2が連通させる。初段槽たる第5槽31eに対応する次段槽は第6槽31fであり、かかる初段槽たる第5槽31eに保有される被処理水中と次段槽たる第6槽31fに保有される被処理水中とを連通口23a3が連通させる。初段槽たる第7槽31gに対応する次段槽は第8槽31hであり、かかる初段槽たる第7槽31gに保有される被処理水中と次段槽たる第8槽31hに保有される被処理水中とを連通口23a4が連通させる。初段槽たる第9槽31iに対応する次段槽は第10槽31jであり、かかる初段槽たる第9槽31iに保有される被処理水中と次段槽たる第10槽31jに保有される被処理水中とを連通口23a5が連通させる。そして、初段槽たる第11槽31kに対応する次段槽は第12槽31lであり、かかる初段槽たる第11槽31kに保有される被処理水中と次段槽たる第12槽31lに保有される被処理水中とを連通口23a6が連通させる。
As described above, the device 11 is sterilized by oxidation treatment to improve the adsorptivity and air dissolution efficiency, and is a gravel obtained from a mixture of porous volcanic gravel and black soil suitable for a microbial medium. Water purification using a powdery product obtained by pulverizing a powdery product and / or a clay-like product (that is, the present active agent (the water quality active agent according to claim 1 of the previous patent (Patent No. 2903359))) Device. This apparatus 11 is a first-stage tank (first tank 31a, third tank 31c, fifth tank 31e, seventh tank 31g, ninth tank 31i) that continuously receives treated water from above and holds a predetermined amount of treated water. , Eleventh tank 31k) and the first stage tank (first tank 31a, third tank 31c, fifth tank 31e, seventh tank 31g, ninth tank 31i, eleventh tank 31k) Next-stage tank (second tank 31b, fourth tank 31d, sixth tank 31f, eighth tank 31h, tenth tank 31j, twelfth tank 31l) continuously receiving a predetermined amount of water to be treated and the first stage To-be-treated water held in the tanks (first tank 31a, third tank 31c, fifth tank 31e, seventh tank 31g, ninth tank 31i, eleventh tank 31k) and the next-stage tank (second tank 31b, 4th tank 31d, 6th tank 31f, 8th tank 31h, 10th tank 31j, 12th tank 31l) Communication ports 23a1, 23a2, 23a3, 23a4, 23a5, 23a6 for communicating with the inside, and the first tank (first tank 31a, third tank 31c, fifth tank 31e, seventh tank 31g, Both the ninth tank 31i, the eleventh tank 31k) and the next tank (the second tank 31b, the fourth tank 31d, the sixth tank 31f, the eighth tank 31h, the tenth tank 31j, the twelfth tank 31l) The water quality activator (this activator) comes into contact with the water to be treated (in the second tank 31b, the solid activator 17 (this activator is solidified) and the retentate 15. And the active agent held on the surface of the retentate 15 in each of the tanks other than the second tank 31b.)
The next tank corresponding to the first tank 31a, which is the first tank, is the second tank 31b. The second tank 31b is the water to be treated and the second tank 31b, which is the next tank. The communication port 23a1 communicates with the water to be treated. Similarly, the next tank corresponding to the third tank 31c, which is the first tank, is the fourth tank 31d, and is stored in the third tank 31c, which is the first tank, and in the fourth tank 31d, which is the next tank. The communication port 23a2 communicates with the water to be treated. The next tank corresponding to the fifth tank 31e, which is the first tank, is the sixth tank 31f. The treated water held in the fifth tank 31e, which is the first tank, and the sixth tank 31f, which is the next tank. The communication port 23a3 communicates with the treated water. The next tank corresponding to the 7th tank 31g as the first tank is the 8th tank 31h. The treated water held in the 7th tank 31g as the first tank and the 8th tank 31h as the next tank. The communication port 23a4 communicates with the treated water. The next tank corresponding to the 9th tank 31i as the first tank is the 10th tank 31j, the water to be treated held in the 9th tank 31i as the first tank and the 10th tank 31j as the next tank. The communication port 23a5 communicates with the treated water. The next tank corresponding to the eleventh tank 31k as the first tank is the twelfth tank 31l, which is held in the treated water held in the eleventh tank 31k as the first tank and in the twelfth tank 31l as the next tank. The communication port 23a6 communicates with the water to be treated.

また、連通口23a1、23a2、23a3、23a4、23a5、23a6いずれもが、各連通口が連通させる次段槽の内部に連通口が開いた部分の最上部の位置p(ここでは図1中、連通口隔壁21a1、21a2、21a3、21a4、21a5、21a6の下端位置。例として、連通口23a1が連通させる次段槽(第2槽31b)の内部に連通口23a1が開いた部分の最上部の位置pを図1中に位置pとして示した。)は、該次段槽に保有される被処理水の深さ(次段槽に保有される被処理水の最も深い位置の深さ)dの1/4よりも下方に位置する(無論、dの半分(1/2)よりも下方に位置する)。なお、前述したように、「深さdの半分(1/2)よりも下方」、「深さdの1/3よりも下方」及び「dの1/4よりも下方」等は、被処理水の該最も深い位置における被処理水の最下部(換言すれば、次段槽の底面。図1中では点線Qにより示した。)から鉛直上方にそれぞれ「深さdの1/2」、「深さdの1/3」及び「dの1/4」行った位置よりも下方であることをいう。また、ここでは深さdは、被処理水の該最も深い位置における被処理水の最下部(換言すれば、次段槽の底面。図1中では点線Qにより示した。)から点線Mによって示される水面までの距離である。   In addition, each of the communication ports 23a1, 23a2, 23a3, 23a4, 23a5, and 23a6 is located at the uppermost position p of the portion where the communication port is opened inside the next-stage tank that each communication port communicates (here, in FIG. The lower end position of the communication port partition walls 21a1, 21a2, 21a3, 21a4, 21a5, 21a6 As an example, the uppermost portion of the portion where the communication port 23a1 is opened inside the next tank (second tank 31b) to which the communication port 23a1 communicates The position p is shown as position p in FIG. 1.) is the depth of the treated water held in the next-stage tank (the depth of the deepest position of the treated water held in the next-stage tank) d. (Of course, it is located below half (1/2) of d). As described above, “below half (1/2) of the depth d”, “below 1/3 of the depth d”, “below 1/4 of d”, etc. “1/2 of the depth d” vertically upward from the lowest part of the treated water at the deepest position of the treated water (in other words, the bottom of the next-stage tank; indicated by the dotted line Q in FIG. 1). , “Below 1/3 of depth d” and “1/4 of d”. Further, here, the depth d is indicated by a dotted line M from the lowest part of the water to be treated at the deepest position (in other words, the bottom surface of the next-stage tank; indicated by the dotted line Q in FIG. 1). The distance to the indicated water surface.

そして、ここでは初段槽(第1槽31a、第3槽31c、第5槽31e、第7槽31g、第9槽31i、第11槽31k)と次段槽(第2槽31b、第4槽31d、第6槽31f、第8槽31h、第10槽31j、第12槽31l)とによって形成される槽の対を6(2以上)直列に備えている。具体的には、初段槽第1槽31aと次段槽第2槽31bとによって形成される第1の槽の対、初段槽第3槽31cと次段槽第4槽31dとによって形成される第2の槽の対、初段槽第5槽31eと次段槽第6槽31fとによって形成される第3の槽の対、初段槽第7槽31gと次段槽第8槽31hとによって形成される第4の槽の対、初段槽第9槽31iと次段槽第10槽31jとによって形成される第5の槽の対、そして初段槽第11槽31kと次段槽第12槽31lとによって形成される第6の槽の対、の6の槽の対が存する。
さらに、該2以上直列に備えられる対のいずれかの対である上流対の前記次段槽から排出される被処理水を、該2以上直列に備えられる対のうち該上流対とは異なる対である下流対の前記初段槽が受け入れる。即ち、上流対たる該第1の槽の対の次段槽第2槽31bから排出される被処理水を、該上流対たる該第1の槽の対とは異なる対である下流対たる該第2の槽の対の初段槽第3槽31cが受け入れる(上流対の次段槽第2槽31bの上端部から溢流する被処理水を、下流対の初段槽第3槽31cが受け入れる)。同様に、上流対たる該第2の槽の対の次段槽第4槽31dから排出される被処理水を、該上流対たる該第2の槽の対とは異なる対である下流対たる該第3の槽の対の初段槽第5槽31eが受け入れる(上流対の次段槽第4槽31dの上端部から溢流する被処理水を、下流対の初段槽第5槽31eが受け入れる)。上流対たる該第3の槽の対の次段槽第6槽31fから排出される被処理水を、該上流対たる該第3の槽の対とは異なる対である下流対たる該第4の槽の対の初段槽第7槽31gが受け入れる(上流対の次段槽第6槽31fの上端部から溢流する被処理水を、下流対の初段槽第7槽31gが受け入れる)。上流対たる該第4の槽の対の次段槽第8槽31hから排出される被処理水を、該上流対たる該第4の槽の対とは異なる対である下流対たる該第5の槽の対の初段槽第9槽31iが受け入れる(上流対の次段槽第8槽31hの上端部から溢流する被処理水を、下流対の初段槽第9槽31iが受け入れる)。そして、上流対たる該第5の槽の対の次段槽第10槽31jから排出される被処理水を、該上流対たる該第5の槽の対とは異なる対である下流対たる該第6の槽の対の初段槽第11槽31kが受け入れる(上流対の次段槽第10槽31jの上端部から溢流する被処理水を、下流対の初段槽第11槽31kが受け入れる)。
And here, the first tank (first tank 31a, third tank 31c, fifth tank 31e, seventh tank 31g, ninth tank 31i, eleventh tank 31k) and the next tank (second tank 31b, fourth tank). 6 (two or more) series of tanks formed by 31d, 6th tank 31f, 8th tank 31h, 10th tank 31j, and 12th tank 31l) are provided. Specifically, it is formed by the first tank pair formed by the first tank first tank 31a and the second tank second tank 31b, the first tank third tank 31c and the next tank fourth tank 31d. Formed by a pair of second tank, a third tank formed by a first tank 5th tank 31e and a next tank 6th tank 31f, a first tank 7th tank 31g and a next tank 8th tank 31h. The fourth tank pair, the fifth tank pair formed by the first tank 9th tank 31i and the next tank 10th tank 31j, and the first tank 11th tank 31k and the next tank 12th tank 31l. There are six tank pairs, a sixth tank pair formed by
Furthermore, the treated water discharged from the next-stage tank of the upstream pair which is one of the pairs provided in series of two or more is a pair different from the upstream pair among the pairs provided in series of two or more. The first-stage tank of the downstream pair that is That is, the water to be treated discharged from the second tank 31b of the next tank of the first tank pair that is the upstream pair is the downstream pair that is different from the pair of the first tank that is the upstream pair. The first tank 3c 31c of the second tank pair receives (the treated water overflowing from the upper end of the upstream tank 2nd tank 31b is received by the downstream first tank 3c). . Similarly, the treated water discharged from the next tank 4th tank 31d of the second tank pair as the upstream pair is a downstream pair which is a different pair from the second tank pair as the upstream pair. The first tank 5th tank 31e of the third tank pair receives (the water to be treated overflowing from the upper end of the upstream tank 4th tank 31d is received by the downstream first tank 5e 31e. ). The treated water discharged from the sixth tank 31f of the next-stage tank of the pair of the third tank as the upstream pair is the fourth of the downstream pair that is different from the pair of the third tank as the upstream pair. The first tank 7g 31g of the first tank of the pair of tanks receives (the treated water overflowing from the upper end of the sixth tank 31f of the upstream next tank is received by the seventh tank 31g of the downstream first tank). The treated water discharged from the next-stage tank 8th tank 31h of the fourth tank pair that is the upstream pair is the fifth downstream pair that is a different pair from the fourth tank pair that is the upstream pair. The first-stage tank 9th tank 31i of the pair of tanks receives (the treated water overflowing from the upper end of the upstream-stage next-stage tank 8th tank 31h is received by the first-stage tank 9th tank 31i of the downstream pair). Then, the water to be treated discharged from the next tank 10th tank 31j of the pair of the fifth tank that is the upstream pair is a downstream pair that is a different pair from the pair of the fifth tank that is the upstream pair. The first tank 11k of the first tank 31k of the sixth tank pair receives (the treated water overflowing from the upper end of the upstream tank 10th tank 31j is received by the downstream first tank 11k). .

また、ここでは前記水質活性剤(本活性剤(前特許(特許番号第2903359号)の請求項1に係る水質活性剤))を表面に保持し被処理水に潜入する保持物15を、さらに備えてなる。なお、保持物15は、東京戸張株式会社の網(製品名称:PE防鳥網Aー50)を折り畳んだものによって構成されており網目状物である。
加えて、結合材で固形化されている前記水質活性剤たる固形状の固形活性剤17(本活性剤が固形化されたものである。)が、被処理水に潜入するように第2槽31b中に配設されている。
Further, here, the water quality activator (the activator (the water quality activator according to claim 1 of the previous patent (patent number 2903359)) of the present activator) is held on the surface, and the retentate 15 entering the treated water is further Prepare. In addition, the holding | maintenance object 15 is comprised by what folded the net | network (product name: PE bird net A-50) of Tokyo Tohari Co., Ltd., and is a mesh-like thing.
In addition, the second tank so that the solid solid activator 17 (this activator is solidified) that is solidified with the binder is infiltrated into the water to be treated. It is arranged in 31b.

そして、初段槽(第1槽31a、第3槽31c、第5槽31e、第7槽31g、第9槽31i、第11槽31k)と次段槽(第2槽31b、第4槽31d、第6槽31f、第8槽31h、第10槽31j、第12槽31l)とは、被処理水を収容する槽体13と、槽体13の内部において初段槽(第1槽31a、第3槽31c、第5槽31e、第7槽31g、第9槽31i、第11槽31k)と次段槽(第2槽31b、第4槽31d、第6槽31f、第8槽31h、第10槽31j、第12槽31l)との間を仕切るように形成された隔壁21a1、21a2、21a3、21a4、21a5、21a6、21b1、21b2、21b3、21b4、21b5と、によって形成されている。また、隔壁21a1、21a2、21a3、21a4、21a5、21a6、21b1、21b2、21b3、21b4、21b5は、同一の前記対を構成する前記初段槽と前記次段槽との間に配設され前記連通口が形成される連通口隔壁21a1、21a2、21a3、21a4、21a5、21a6と、前記上流対の前記次段槽と前記下流対の前記初段槽との間に配設され上端部から被処理水が溢流する堰隔壁21b1、21b2、21b3、21b4、21b5と、の2種類を含んでなり、連通口隔壁21a1、21a2、21a3、21a4、21a5、21a6と堰隔壁21b1、21b2、21b3、21b4、21b5とが(被処理水が流れる方向に沿って)交互に配設されている。
なお、連通口隔壁21a1は、第1の槽の対を構成する初段槽第1槽31aと次段槽第2槽31bとの間に配設され連通口23a1が形成される。連通口隔壁21a2は、第2の槽の対を構成する初段槽第3槽31cと次段槽第4槽31dとの間に配設され連通口23a2が形成される。連通口隔壁21a3は、第3の槽の対を構成する初段槽第5槽31eと次段槽第6槽31fとの間に配設され連通口23a3が形成される。連通口隔壁21a4は、第4の槽の対を構成する初段槽第7槽31gと次段槽第8槽31hとの間に配設され連通口23a4が形成される。連通口隔壁21a5は、第5の槽の対を構成する初段槽第9槽31iと次段槽第10槽31jとの間に配設され連通口23a5が形成される。連通口隔壁21a6は、第6の槽の対を構成する初段槽第11槽31kと次段槽第12槽31lとの間に配設され連通口23a6が形成される。堰隔壁21b1は、上流対(第1の槽の対)の次段槽第2槽31bと下流対(第2の槽の対)の初段槽第3槽31cとの間に配設され上端部から被処理水が溢流する。堰隔壁21b2は、上流対(第2の槽の対)の次段槽第4槽31dと下流対(第3の槽の対)の初段槽第5槽31eとの間に配設され上端部から被処理水が溢流する。堰隔壁21b3は、上流対(第3の槽の対)の次段槽第6槽31fと下流対(第4の槽の対)の初段槽第7槽31gとの間に配設され上端部から被処理水が溢流する。堰隔壁21b4は、上流対(第4の槽の対)の次段槽第8槽31hと下流対(第5の槽の対)の初段槽第9槽31iとの間に配設され上端部から被処理水が溢流する。堰隔壁21b5は、上流対(第5の槽の対)の次段槽第10槽31jと下流対(第6の槽の対)の初段槽第11槽31kとの間に配設され上端部から被処理水が溢流する。
The first tank (first tank 31a, third tank 31c, fifth tank 31e, seventh tank 31g, ninth tank 31i, eleventh tank 31k) and the next tank (second tank 31b, fourth tank 31d, The sixth tank 31f, the eighth tank 31h, the tenth tank 31j, and the twelfth tank 31l) are the tank body 13 that stores the water to be treated and the first tank (first tank 31a, third tank) inside the tank body 13. Tank 31c, fifth tank 31e, seventh tank 31g, ninth tank 31i, eleventh tank 31k) and next tank (second tank 31b, fourth tank 31d, sixth tank 31f, eighth tank 31h, tenth tank). Partition wall 21a1, 21a2, 21a3, 21a4, 21a5, 21a6, 21b1, 21b2, 21b3, 21b4, 21b5 formed to partition between tank 31j and twelfth tank 31l). The partition walls 21a1, 21a2, 21a3, 21a4, 21a5, 21a6, 21b1, 21b2, 21b3, 21b4, and 21b5 are disposed between the first-stage tank and the next-stage tank that constitute the same pair. Water is to be treated from the upper end portion, which is disposed between the communication port partition walls 21a1, 21a2, 21a3, 21a4, 21a5, 21a6 and the upstream pair of the next-stage tank and the downstream pair of the first-stage tank. 2 types of dam partition walls 21b1, 21b2, 21b3, 21b4, 21b5 overflowing, communication port partition walls 21a1, 21a2, 21a3, 21a4, 21a5, 21a6 and dam partition walls 21b1, 21b2, 21b3, 21b4, 21b5 are alternately arranged (along the direction in which the water to be treated flows).
The communication port partition wall 21a1 is disposed between the first-stage tank first tank 31a and the next-stage tank second tank 31b constituting the first tank pair, and a communication port 23a1 is formed. The communication port partition wall 21a2 is disposed between the first-stage tank third tank 31c and the next-stage tank fourth tank 31d constituting the second tank pair, and a communication port 23a2 is formed. The communication port partition wall 21a3 is disposed between the first-stage tank fifth tank 31e and the next-stage tank sixth tank 31f constituting the third tank pair to form a communication port 23a3. The communication port partition wall 21a4 is disposed between the first-stage tank 7th tank 31g and the next-stage tank 8th tank 31h constituting the fourth tank pair, and the communication port 23a4 is formed. The communication port partition wall 21a5 is disposed between the first-stage tank 9th tank 31i and the next-stage tank 10th tank 31j constituting the fifth tank pair, and the communication port 23a5 is formed. The communication port partition wall 21a6 is disposed between the first-stage tank 11th tank 31k and the next-stage tank 12th tank 31l constituting the sixth tank pair, and a communication port 23a6 is formed. The weir bulkhead 21b1 is disposed between the upstream tank (first tank pair) next-stage tank second tank 31b and the downstream pair (second tank pair) first-stage tank third tank 31c. The treated water overflows. The dam partition wall 21b2 is disposed between the upstream tank (second tank pair) next-stage tank fourth tank 31d and the downstream pair (third tank pair) first-stage tank fifth tank 31e. The treated water overflows. The weir bulkhead 21b3 is disposed between the upstream tank (third tank pair) next-stage tank sixth tank 31f and the downstream pair (fourth tank pair) first-stage tank seventh tank 31g. The treated water overflows. The weir bulkhead 21b4 is disposed between the upstream tank (fourth tank pair) next-stage tank eighth tank 31h and the downstream pair (fifth tank pair) first-stage tank ninth tank 31i. The treated water overflows. The weir bulkhead 21b5 is disposed between the upstream tank (fifth tank pair) next-stage tank tenth tank 31j and the downstream pair (sixth tank pair) first-stage tank eleventh tank 31k. The treated water overflows.

そして、本装置11においては、第1槽31a、第2槽31b、第3槽31c、第4槽31d、第5槽31e、第6槽31f、第7槽31g、第8槽31h、第9槽31i、第10槽31j、第11槽31k及び第12槽31lの全ての槽が、該槽が保有する被処理水の上方に空気(酸素ガスを含む気体)が存する空間(点線Mによって示される水面よりも上方の槽体13の内部空間13aが該当する。なお、該空間の雰囲気は、外気と自由に流通することができるようになっており常に新鮮な空気が該空間には存在する。)を有する。該空間に存する空気と被処理水とは、点線Mによって示される水面において接触する。   And in this apparatus 11, 1st tank 31a, 2nd tank 31b, 3rd tank 31c, 4th tank 31d, 5th tank 31e, 6th tank 31f, 7th tank 31g, 8th tank 31h, 9th All of the tank 31i, the tenth tank 31j, the eleventh tank 31k, and the twelfth tank 31l are spaces (indicated by dotted lines M) in which air (gas containing oxygen gas) exists above the water to be treated. This corresponds to the internal space 13a of the tank body 13 above the surface of the water that is generated, and the atmosphere of the space can freely circulate with the outside air, and fresh air always exists in the space. .) The air existing in the space and the water to be treated are in contact with each other on the water surface indicated by the dotted line M.

また、本装置11の使用方法において説明した前記第2の工程(本混合物を注入口43から第1槽31aへ注入する工程)及び前記第3の工程(被処理水(原水)41を注入口43から第1槽31aへ注入する工程)は、本混合物が第1槽31aから第12槽31lへ移動する間に、第1槽31aから第12槽31lまでの各槽に配設された保持物15(本活性剤が表面に保持される前のもの)と本混合物とを接触させるので(本混合物に含まれる本活性剤が、第1槽31aから第12槽31lまでの各槽に配設された保持物15の表面に保持される。)、所定位置に配設した保持物15(本活性剤が表面に保持される前のもの)に、水中に懸濁又は溶解した前記水質活性剤(本活性剤)を接触させる接触ステップを構成する。そして、本混合物が、各槽に配設された保持物15(本活性剤が表面に保持される前のもの)と接触した後の前記第3の工程(被処理水(原水)41を注入口43から第1槽31aへ注入する工程)は、接触ステップの後、被処理水を初段槽(第1槽31a、第3槽31c、第5槽31e、第7槽31g、第9槽31i、第11槽31k)に連続的に供給する供給ステップを構成する。
このように上述した本装置11の使用方法は、保持物本装置を用いた水質浄化方法であって、所定位置に配設した保持物15(本活性剤が表面に保持される前のもの)に、水中に懸濁又は溶解した前記水質活性剤(本活性剤)を接触させる接触ステップと、該接触ステップの後、被処理水を初段槽(第1槽31a、第3槽31c、第5槽31e、第7槽31g、第9槽31i、第11槽31k)に連続的に供給する供給ステップと、を含んでなる、水質浄化方法である。
In addition, the second step (the step of injecting the mixture into the first tank 31a from the inlet 43) and the third step (the treated water (raw water) 41 are the inlets) described in the method of using the apparatus 11. 43, the step of pouring from the first tank 31a to the twelfth tank 31l while the mixture moves from the first tank 31a to the twelfth tank 31l. Since the product 15 (the one before the active agent is held on the surface) and the present mixture are brought into contact with each other (the present active agent contained in the present mixture is disposed in each tank from the first tank 31a to the twelfth tank 31l). The water quality activity suspended or dissolved in water in the holding material 15 (the one before the active agent is held on the surface) disposed in a predetermined position. The contact step which makes an agent (this active agent) contact is comprised. Then, the third step (treated water (raw water) 41 is poured after the mixture comes into contact with the retentate 15 (the one before the active agent is retained on the surface) disposed in each tank. In the step of injecting from the inlet 43 to the first tank 31a, after the contacting step, the first stage tank (first tank 31a, third tank 31c, fifth tank 31e, seventh tank 31g, ninth tank 31i) , Constitutes a supply step for continuously supplying to the eleventh tank 31k).
As described above, the method of using the device 11 is a water purification method using the retained material device, and the retained material 15 (before the active agent is retained on the surface) disposed at a predetermined position. A contact step in which the water quality active agent (this active agent) suspended or dissolved in water is contacted, and after the contact step, the water to be treated is supplied to the first stage tank (first tank 31a, third tank 31c, fifth tank). A tank 31e, a seventh tank 31g, a ninth tank 31i, and an eleventh tank 31k).

一実施形態の本発明の水質浄化装置(本装置)の正面図である。It is a front view of the water purification apparatus (this apparatus) of this invention of one Embodiment. 図1のA−A断面図である。It is AA sectional drawing of FIG.

符号の説明Explanation of symbols

11 本装置
13 槽体
13a 内部空間
13b 底板
13c 側板
13d 蓋板
15 保持物
17 固形活性剤
21a1、21a2、21a3、21a4、21a5、21a6、21b1、21b2、21b3、21b4、21b5 隔壁
(21a1、21a2、21a3、21a4、21a5、21a6 連通口隔壁)
(21b1、21b2、21b3、21b4、21b5 堰隔壁)
23a1、23a2、23a3、23a4、23a5、23a6 連通口
31a 第1槽
31b 第2槽
31c 第3槽
31d 第4槽
31e 第5槽
31f 第6槽
31g 第7槽
31h 第8槽
31i 第9槽
31j 第10槽
31k 第11槽
31l 第12槽
41 被処理水(原水)
43 注入口
51 被処理水(処理済水)
53 排水口
11 This apparatus 13 Tank 13a Internal space 13b Bottom plate 13c Side plate 13d Cover plate 15 Retained material 17 Solid activator 21a1, 21a2, 21a3, 21a4, 21a5, 21a6, 21b1, 21b2, 21b3, 21b4, 21b5 Partition (21a1, 21a2, 21a3, 21a4, 21a5, 21a6 communication port partition)
(21b1, 21b2, 21b3, 21b4, 21b5 weir bulkhead)
23a1, 23a2, 23a3, 23a4, 23a5, 23a6 Communication port 31a 1st tank 31b 2nd tank 31c 3rd tank 31d 4th tank 31e 5th tank 31f 6th tank 31g 7th tank 31h 8th tank 31i 9th tank 31j 10th tank 31k 11th tank 31l 12th tank 41 Water to be treated (raw water)
43 Inlet 51 Water to be treated (treated water)
53 Drain outlet

Claims (12)

酸化処理により殺菌し、吸着性と空気溶解効率とを向上させるとともに、微生物培地に適するようにした多孔質の火山礫と黒土との混合物から得られる礫状物、及び又は粘土状物を粉末化した粉末物からなる水質活性剤を用いる水質浄化装置であって、
上方から被処理水を連続的に受け入れ被処理水を所定量保有する初段槽と、該初段槽から排出される被処理水を連続的に受け入れ被処理水を所定量保有する次段槽と、該初段槽に保有される被処理水中と該次段槽に保有される被処理水中とを連通させる連通口と、を備えてなり、
該初段槽及び該次段槽の両方が保有する被処理水に該水質活性剤が接触するものである、水質浄化装置。
Sterilized by oxidation treatment to improve adsorptivity and air dissolution efficiency, and powdered gravel and / or clay obtained from a mixture of porous volcanic gravel and black soil suitable for microbial media A water purification device using a water quality activator comprising a powdered product,
A first-stage tank that continuously receives treated water from above and holds a predetermined amount of treated water; a next-stage tank that continuously receives treated water discharged from the first-stage tank and holds a predetermined amount of treated water; A communication port for communicating the treated water held in the first tank and the treated water held in the next tank;
A water purification apparatus in which the water quality activator is in contact with the water to be treated which both the first stage tank and the next stage tank hold.
前記連通口が、前記次段槽に保有される被処理水の深さの半分よりも深い位置に形成されるものである、請求項1に記載の水質浄化装置。       The water purification apparatus according to claim 1, wherein the communication port is formed at a position deeper than half of the depth of the water to be treated held in the next-stage tank. 前記初段槽と前記次段槽とによって形成される槽の対を2以上直列に備え、
該2以上直列に備えられる対のいずれかの対である上流対の前記次段槽から排出される被処理水を、該2以上直列に備えられる対のうち該上流対とは異なる対である下流対の前記初段槽が受け入れるものである、請求項1又は2に記載の水質浄化装置。
Two or more tank pairs formed by the first tank and the next tank are provided in series,
The treated water discharged from the upstream tank of the upstream pair, which is one of the pairs provided in series of two or more, is a pair different from the upstream pair among the pairs provided in series of two or more. The water purification apparatus according to claim 1 or 2, which is received by the first-stage tank of a downstream pair.
前記上流対の前記次段槽の上端部から溢流する被処理水を、前記下流対の前記初段槽が受け入れるものである、請求項3に記載の水質浄化装置。       The water purification apparatus according to claim 3, wherein the water to be treated that overflows from the upper end of the next-stage tank of the upstream pair is received by the first-stage tank of the downstream pair. 前記水質活性剤を表面に保持し被処理水に潜入する保持物を、さらに備えてなる、請求項1乃至4のいずれか1に記載の水質浄化装置。       The water purification apparatus according to any one of claims 1 to 4, further comprising a retentate that retains the water quality activator on a surface and infiltrates the water to be treated. 前記保持物が網目状物である、請求項5に記載の水質浄化装置。       The water purification apparatus according to claim 5, wherein the retentate is a mesh. 結合材で固形化されている前記水質活性剤が、被処理水に潜入するように配設されるものである、請求項1乃至6のいずれか1に記載の水質浄化装置。       The water purification apparatus according to any one of claims 1 to 6, wherein the water quality activator solidified with a binder is disposed so as to infiltrate into the water to be treated. 前記初段槽と前記次段槽とは、被処理水を収容する槽体と、該槽体の内部において前記初段槽と前記次段槽との間を仕切るように形成された隔壁と、によって形成され、
該隔壁に前記連通口が形成されるものである、請求項1乃至7のいずれか1に記載の水質浄化装置。
The first-stage tank and the next-stage tank are formed by a tank body that stores the water to be treated, and a partition that is formed inside the tank body so as to partition the first-stage tank and the next-stage tank. And
The water purification apparatus according to any one of claims 1 to 7, wherein the communication port is formed in the partition wall.
前記初段槽と前記次段槽とは、被処理水を収容する槽体と、該槽体の内部において前記初段槽と前記次段槽との間を仕切るように形成された隔壁と、によって形成され、
該隔壁は、同一の前記対を構成する前記初段槽と前記次段槽との間に配設され前記連通口が形成される連通口隔壁と、前記上流対の前記次段槽と前記下流対の前記初段槽との間に配設され上端部から被処理水が溢流する堰隔壁と、を含んでなり、該連通口隔壁と該堰隔壁とが交互に配設されるものである、請求項4に記載の水質浄化装置。
The first-stage tank and the next-stage tank are formed by a tank body that stores the water to be treated, and a partition that is formed inside the tank body so as to partition the first-stage tank and the next-stage tank. And
The partition wall includes a communication port partition wall disposed between the first-stage tank and the next-stage tank constituting the same pair, the communication port being formed, the next-stage tank of the upstream pair, and the downstream pair. A dam partition wall disposed between the first-stage tank and the water to be treated overflows from the upper end, and the communication port partition wall and the dam partition wall are alternately disposed. The water purification apparatus according to claim 4.
前記被処理水が、酸素ガスを含む気体と接触するものである、請求項1乃至9のいずれか1に記載の水質浄化装置。       The water purification apparatus according to any one of claims 1 to 9, wherein the treated water is in contact with a gas containing oxygen gas. 前記初段槽及び前記次段槽の少なくとも一方が、該一方が保有する被処理水の上方に前記気体が存する空間を有するものである、請求項10に記載の水質浄化装置。       The water purification apparatus according to claim 10, wherein at least one of the first-stage tank and the next-stage tank has a space in which the gas exists above the water to be treated that the one of the first-stage tank and the next-stage tank holds. 請求項5又は6に記載の水質浄化装置を用いた水質浄化方法であって、
所定位置に配設した前記保持物に、水中に懸濁又は溶解した前記水質活性剤を接触させる接触ステップと、
該接触ステップの後、前記被処理水を前記初段槽に連続的に供給する供給ステップと、を含んでなる、水質浄化方法。
A water purification method using the water purification device according to claim 5 or 6,
A contact step of bringing the water-soluble active agent suspended or dissolved in water into contact with the retentate disposed at a predetermined position;
A water quality purification method comprising, after the contacting step, a supply step of continuously supplying the treated water to the first tank.
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Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5848397U (en) * 1981-09-28 1983-04-01 原 正登 Floating floor for sewage treatment using anti-firestone
JPH05169055A (en) * 1991-12-20 1993-07-09 Yoko Hirata Sewage purifier and its filter medium
JPH06262191A (en) * 1993-03-12 1994-09-20 Masashi Kato Contact bed for treating water
JPH0796275A (en) * 1993-09-27 1995-04-11 I Ii Res Kk Water activator and production thereof
JPH08132084A (en) * 1994-11-15 1996-05-28 Sada Naritoshi Filter medium and its production
JPH10230252A (en) * 1997-02-20 1998-09-02 I Ii Res Kk Production of activated water and utilization thereof
JPH10272481A (en) * 1997-03-31 1998-10-13 Komaki Kensetsu Kk Treating vessel for contact oxidation of rivers and contact oxidation treating device of rivers
JP2001070965A (en) * 1999-06-29 2001-03-21 Hitachi Ltd Water treatment apparatus

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5848397U (en) * 1981-09-28 1983-04-01 原 正登 Floating floor for sewage treatment using anti-firestone
JPH05169055A (en) * 1991-12-20 1993-07-09 Yoko Hirata Sewage purifier and its filter medium
JPH06262191A (en) * 1993-03-12 1994-09-20 Masashi Kato Contact bed for treating water
JPH0796275A (en) * 1993-09-27 1995-04-11 I Ii Res Kk Water activator and production thereof
JP2903359B2 (en) * 1993-09-27 1999-06-07 アイイ−リサ−チ株式会社 Water activator and its production method
JPH08132084A (en) * 1994-11-15 1996-05-28 Sada Naritoshi Filter medium and its production
JPH10230252A (en) * 1997-02-20 1998-09-02 I Ii Res Kk Production of activated water and utilization thereof
JPH10272481A (en) * 1997-03-31 1998-10-13 Komaki Kensetsu Kk Treating vessel for contact oxidation of rivers and contact oxidation treating device of rivers
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