JP2003190982A - Material for purifying water, bag-in material for purifying water, facility for purifying water using this, and method for purifying water - Google Patents

Material for purifying water, bag-in material for purifying water, facility for purifying water using this, and method for purifying water

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Publication number
JP2003190982A
JP2003190982A JP2001395105A JP2001395105A JP2003190982A JP 2003190982 A JP2003190982 A JP 2003190982A JP 2001395105 A JP2001395105 A JP 2001395105A JP 2001395105 A JP2001395105 A JP 2001395105A JP 2003190982 A JP2003190982 A JP 2003190982A
Authority
JP
Japan
Prior art keywords
water
bacillus subtilis
water purification
bag
purification material
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP2001395105A
Other languages
Japanese (ja)
Inventor
Katsumi Fukuoka
勝巳 福岡
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Individual
Original Assignee
Individual
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to JP2001395105A priority Critical patent/JP2003190982A/en
Publication of JP2003190982A publication Critical patent/JP2003190982A/en
Pending legal-status Critical Current

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Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Biological Treatment Of Waste Water (AREA)
  • Treatment Of Biological Wastes In General (AREA)
  • Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a material for purifying water by using a microorganism having a high durability against a variation of environment and harmless for human body, a facility for purifying water, and a method for purifying water. <P>SOLUTION: The material 17 for purifying water has a bamboo charcoal and Bacillus Subtilis carried by this bamboo charcoal. The facility 20 for purifying water is provided with treating tanks 2-6 capable of storing water to be treated discharged from home and a porous block 18 disposed in the treating tanks 2-6 and carrying Bacillus Subtilis or the material 17 for purifying water. In the method for purifying water, the porous block 18 carrying Bacillus Subtilis or the material 17 for purifying water is piled in a water passage to form weirs 22, 23 and air is involved in water by the water exceeding the weirs 22, 23 from an upstream side and dropping off to feed an oxygen to Bacillus Subtilis. <P>COPYRIGHT: (C)2003,JPO

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、枯草菌を用いて汚
水の浄化を行う水質浄化材、袋入り水質浄化材、これを
用いた水質浄化設備および水質浄化方法に関する。
TECHNICAL FIELD The present invention relates to a water purification material for purifying sewage using Bacillus subtilis, a water purification material in a bag, a water purification facility and a water purification method using the same.

【0002】[0002]

【従来の技術】従来、家庭用の浄化槽は、下水道ができ
るまでの暫定的な設備として用いられ、下水道設備が完
成した後には撤去され、下水道終末処理場でまとめて処
理されていた。このような大型処理場は建設に多大な費
用がかかり、自治体によっては、一人あたりの設備費用
が70〜80万円程度かかることになる。また、この設
備の運転には電気代等の多大な運転費用と人手が必要と
なっていた。一方、汚染された河川を浄化する方法が多
く開発されており、近年においては、微生物の力を利用
して汚物を分解する方法も多く採用されている。近年で
は、このような微生物の力を利用して、家庭用の浄化槽
の処理能力を上げ、衛生的で恒久的な施設の設置への期
待が高まっている。
2. Description of the Related Art Conventionally, household septic tanks have been used as provisional equipment until sewerage was completed, and were removed after the sewerage equipment was completed and collectively treated at the sewerage terminal treatment plant. Construction of such a large-scale treatment plant is very expensive, and depending on the local government, the facility cost per person is about 700,000 to 800,000 yen. In addition, the operation of this equipment requires a large operating cost such as electricity bill and manpower. On the other hand, many methods for purifying polluted rivers have been developed, and in recent years, many methods for decomposing waste by utilizing the power of microorganisms have also been adopted. In recent years, there is an increasing expectation that the treatment capacity of household septic tanks will be increased by utilizing the power of such microorganisms, and that sanitary and permanent facilities will be installed.

【0003】[0003]

【発明が解決しようとする課題】しかしながら、前記従
来の河川や家庭からの排水の浄化方法は、大がかりなも
のになるため、利用しようとする菌を定期的に大量に補
充しなければならず、運転に多大な手間と費用が発生す
るという問題がある。また、河川や家庭からの排水は温
度の変動等菌に対する条件が厳しく、菌を生存させてお
くことも困難である。そこで本発明が解決しようとする
課題は、環境の変化に対する耐性が高く、人体に無害な
微生物を用いて、メンテナンスの簡単な水質浄化材、袋
入り水質浄化材、これを用いた水質浄化設備および水質
浄化方法を提供することにある。
However, since the conventional methods for purifying wastewater from rivers and households are large-scaled, it is necessary to periodically replenish the bacteria to be used in large amounts, There is a problem that a great deal of time and money is required for driving. In addition, drainage from rivers and households has severe conditions against bacteria such as temperature fluctuations, and it is difficult to keep the bacteria alive. Therefore, the problem to be solved by the present invention is high resistance to environmental changes, using microorganisms that are harmless to the human body, a water purification material that is easy to maintain, a water purification material in a bag, and water purification equipment using the same. To provide a water purification method.

【0004】[0004]

【課題を解決するための手段】前記課題を解決するた
め、本発明の水質浄化材は、所定粒度に粉砕された竹炭
と、この竹炭に担持された枯草菌とを有する。枯草菌
は、土壌・枯草など自然界に広く分布するグラム陽性・
芽胞形成性の大型の桿菌で、芽胞は数時間の煮沸に耐え
ることができる。納豆菌は、枯草菌の一種である。竹炭
は多孔質の部材であり、脱臭効果を有している。本発明
は、竹炭を粉砕したものを枯草菌の担体として用いてい
るので、水中の窒素、リンを除去して、生物化学的酸素
要求量(BOD)を下げることができる。また、繊維の
方向に沿って形成された空洞部内に枯草菌が担持される
ので、この空洞内を流れる水と枯草菌が効率よく接触す
る。
In order to solve the above problems, the water purification material of the present invention comprises bamboo charcoal crushed to a predetermined particle size and Bacillus subtilis carried on the bamboo charcoal. Bacillus subtilis is a gram-positive species widely distributed in nature such as soil and hay.
A large spore-forming bacillus that can withstand boiling for several hours. Bacillus natto is a type of Bacillus subtilis. Bamboo charcoal is a porous member and has a deodorizing effect. In the present invention, crushed bamboo charcoal is used as a carrier for Bacillus subtilis, so that nitrogen and phosphorus in water can be removed to lower the biochemical oxygen demand (BOD). In addition, since Bacillus subtilis is carried in the cavity formed along the direction of the fiber, the water flowing in the cavity and Bacillus subtilis efficiently contact with each other.

【0005】本発明の袋入り水質浄化材は、所定粒度に
粉砕された竹炭と、この竹炭に担持された枯草菌とを、
通水性および可撓性を有する袋体に封入している。袋体
に封入するので、竹炭および枯草菌の流出が防止され、
また、袋体が可撓性を有するので、設置場所の形状に合
わせて外形を変えることができる。
The bag-type water purification material of the present invention comprises bamboo charcoal pulverized to a predetermined particle size and Bacillus subtilis carried on the bamboo charcoal.
It is enclosed in a bag having water permeability and flexibility. Since it is sealed in a bag, bamboo charcoal and Bacillus subtilis are prevented from flowing out,
Further, since the bag body is flexible, the outer shape can be changed according to the shape of the installation place.

【0006】前記袋体にみかんの皮および粉砕された火
山弾等の多孔質構造を有する石を封入することも可能で
ある。みかんの皮を枯草菌に分解させることで、枯草菌
の活性を高め、その数を増加させるという作用が生じ
る。また、多孔質構造を有する石を入れることにより枯
草菌に対する担体となると共に水中に投入したときのお
もりにもなる。
It is also possible to enclose a mandarin orange peel and a stone having a porous structure such as a crushed volcanic bomb in the bag. By decomposing mandarin orange peel into Bacillus subtilis, the action of enhancing the activity of Bacillus subtilis and increasing its number occurs. In addition, by incorporating a stone having a porous structure, it becomes a carrier for Bacillus subtilis and also serves as a weight when placed in water.

【0007】前記竹炭、前記枯草菌、前記みかんの皮、
および前記石の重量比を、その誤差が10%以内となる
範囲内で、5:2:1:2とすることも可能である。か
かる構成によって、枯草菌の活性が高められる。
[0007] The bamboo charcoal, the Bacillus subtilis, the orange peel,
It is also possible to set the weight ratio of the stones to 5: 2: 1: 2 within a range where the error is within 10%. With such a constitution, the activity of Bacillus subtilis is enhanced.

【0008】前記袋体に、粉砕した竹の葉を、全体に対
する重量比が20〜50%となる範囲で封入することも
可能である。竹の葉を混入することにより、枯草菌の餌
となり、枯草菌の活性をさらに高められる。
[0008] It is also possible to enclose crushed bamboo leaves in the bag in an amount of 20 to 50% by weight relative to the whole. By mixing bamboo leaves, it becomes a bait of Bacillus subtilis and the activity of Bacillus subtilis can be further enhanced.

【0009】本発明に係る水質浄化設備は、家庭から排
出された処理水を貯留可能な処理槽と、この処理槽内に
配置された枯草菌を担持した多孔質ブロック、または請
求項2〜5のいずれかの項に記載の袋入り水質浄化材と
を備えている。多孔質ブロックは、処理槽に固定して設
けられ、または処理槽内で処理水に接触可能な位置に配
置されている。所定形状の多孔質ブロックを設けるの
で、整列して設置することができ、また、袋入り水質浄
化材を設けるので、異形の処理槽にも対応できる。
In the water purification equipment according to the present invention, a treatment tank capable of storing treated water discharged from a home, a porous block supporting Bacillus subtilis placed in the treatment tank, or claim 2 to 5 is provided. The water purification material in a bag according to any one of 1. The porous block is provided so as to be fixed to the treatment tank, or is arranged at a position where it can come into contact with the treatment water in the treatment tank. Since the porous block having a predetermined shape is provided, the blocks can be arranged in line, and since the water purification material in the bag is provided, it can be applied to an irregular treatment tank.

【0010】前記処理槽を、既設の側溝を複数に仕切っ
て形成することも可能である。かかる構成によって、処
理槽の設置にかかる手間と費用を省略し、迅速な設備の
設置を行うことができる。
It is also possible to form the processing tank by dividing the existing side groove into a plurality of partitions. With such a configuration, it is possible to save the labor and cost for installing the processing tank and to quickly install the equipment.

【0011】本発明に係る水質浄化方法は、枯草菌を担
持した多孔質ブロックおよび請求項2〜5のいずれかの
項に記載の袋入り水質浄化材のうちの一方または両方
を、水路内に積層して堰を形成し、上流側から前記堰を
越えて落下する水により空気を水中に巻き込んで、前記
枯草菌に酸素を供給する。枯草菌は好気性菌なので、水
中に酸素を供給することにより処理能力を上げることが
できる。
In the water purification method according to the present invention, one or both of the porous block supporting Bacillus subtilis and the bag-shaped water purification material according to any one of claims 2 to 5 are provided in a water channel. Oxygen is supplied to the Bacillus subtilis by stacking layers to form a weir, and entraining air in the water by water falling from the upstream side over the weir. Since Bacillus subtilis is an aerobic bacterium, the treatment capacity can be improved by supplying oxygen to water.

【0012】[0012]

【発明の実施の形態】以下、本発明の実施の形態につい
て説明する。 (実施の形態1)図1は本発明の第1の実施の形態に係
る水質浄化材を用いた水質浄化設備の構成を示す説明図
である。水質浄化設備1は、家庭から排出された処理水
を貯留可能な複数の処理槽2〜6と、家屋7の排水場所
から各処理槽2〜6に接続された複数の排水管8と、ト
イレ9と処理槽5をつないだ排水管8の途中位置に配置
された便槽10とを有している。
BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of the present invention will be described below. (Embodiment 1) FIG. 1 is an explanatory diagram showing a configuration of a water purification facility using a water purification material according to a first embodiment of the present invention. The water purification facility 1 includes a plurality of treatment tanks 2 to 6 capable of storing treated water discharged from homes, a plurality of drainage pipes 8 connected to the treatment tanks 2 to 6 from a drainage place of a house 7, and a toilet. 9 and a waste tank 10 connected to the treatment tank 5 at an intermediate position of a drain pipe 8.

【0013】各処理槽2〜6は、それぞれの上端部を連
通する通水路11で連結され、最下流側の処理槽6は、
排水路12を介して河川13に接続されている。台所1
4、洗濯機15の排水部、トイレ9に接続された処理槽
2、3、5の容積はそれぞれ100リットル、風呂場1
6に接続された処理槽4の容積は200リットル、トイ
レ9に接続された便槽10と、最下流側の処理槽6の容
積はそれぞれ1000リットルに形成されている。各処
理槽2〜6及び便槽10の底部には、その容積に応じ
て、水質浄化材17および枯草菌を担持した多孔質ブロ
ック18が配置されている。なお、各処理槽2〜6は、
家屋7の近傍に配置されている側溝に仕切りを配置する
ことによって設けてもよく、このように構成することに
より、施工を簡単かつ迅速に行うことができる。
The processing tanks 2 to 6 are connected by a water passage 11 which communicates their upper ends, and the processing tank 6 on the most downstream side is
It is connected to the river 13 via the drainage channel 12. Kitchen 1
4, the drainage part of the washing machine 15 and the treatment tanks 2, 3, and 5 connected to the toilet 9 have a volume of 100 liters each, and a bathroom 1
The volume of the treatment tank 4 connected to 6 is 200 liters, and the volume of the toilet tank 10 connected to the toilet 9 and the treatment tank 6 on the most downstream side are 1000 liters. At the bottom of each of the treatment tanks 2 to 6 and the toilet tank 10, a water purification material 17 and a porous block 18 carrying Bacillus subtilis are arranged according to their volumes. In addition, each processing tank 2-6
The partition may be provided by arranging the partition in the side groove arranged in the vicinity of the house 7, and the construction can be performed easily and quickly.

【0014】ここで、水質浄化材17について詳しく説
明する。図2は水質浄化材17の側断面図を示す。水質
浄化材17は、通水性および可撓性を有する植物性やプ
ラスチック製の繊維からなる袋体19と、所定粒度に粉
砕されてこの中に封入された竹炭、これに担持された枯
草菌、みかんの皮および粉砕された石を有している。そ
して、竹炭、枯草菌、みかんの皮および粉砕された石
を、5:2:1:2の割合で混合しており、この割合の
誤差は、10%以内にしている。また、これらの混合物
には、粉砕した竹の葉を、竹の葉を含む全体に対する重
量比が20〜50%となる範囲で混入している。なお、
水質浄化材は、竹炭および枯草菌のみで構成することも
可能で、さらに、この竹炭および枯草菌に、竹の葉を、
竹の葉を含む全体に対する重量比が20〜50%となる
範囲で混入することも可能である。袋体19の一端部に
は、水質浄化材17を吊り下げ可能なフック部材26が
設けられている。
Here, the water purification material 17 will be described in detail. FIG. 2 shows a side sectional view of the water purification material 17. The water purification material 17 is a bag body 19 made of plant or plastic fiber having water permeability and flexibility, bamboo charcoal crushed to a predetermined particle size and enclosed therein, Bacillus subtilis carried on the charcoal, It has mandarin orange peel and crushed stone. Then, bamboo charcoal, Bacillus subtilis, mandarin orange peel and crushed stone are mixed at a ratio of 5: 2: 1: 2, and the error of this ratio is within 10%. In addition, crushed bamboo leaves are mixed in these mixtures in a weight ratio of 20 to 50% with respect to the whole including the bamboo leaves. In addition,
The water purification material can be composed only of bamboo charcoal and Bacillus subtilis, and further, bamboo leaves are added to the bamboo charcoal and Bacillus subtilis.
It is also possible to mix in a weight ratio of 20 to 50% with respect to the whole including bamboo leaves. At one end of the bag body 19, a hook member 26 capable of suspending the water purification material 17 is provided.

【0015】水質浄化材17は、平面視したときの大き
さを例えば20×40cm程度に形成し、その重量を5
〜20kg程度にしている。この水質浄化材17を各処
理槽2〜6及び便槽10に投入すると、袋体19の内部
に水分が浸透し、枯草菌が水中の大腸菌や腐敗菌等を分
解して、竹炭等の孔部内で繁殖する。
The water purification material 17 is formed to have a size of, for example, about 20 × 40 cm in plan view, and its weight is 5 cm.
Approximately 20 kg. When this water purification material 17 is put into each of the treatment tanks 2 to 6 and the toilet tank 10, moisture penetrates into the bag body 19, and Bacillus subtilis decomposes E. coli and putrefactive bacteria in the water to form holes such as bamboo charcoal. Breeds within the department.

【0016】次に多孔質ブロック18について説明す
る。図3は多孔質ブロック18の斜視図を示す。多孔質
ブロック18は、図3に示すように、例えば、長方形に
形成することができる。多孔質ブロック18は、砂、石
と共に担体に保持された枯草菌を、セメントペーストと
共に混練し、固化させたものである。セメント製品は強
アルカリ性を示すが、本発明に係る枯草菌は、PH3〜
PH11の範囲の強酸性から強アルカリ性の範囲で生存
できるので、多孔質ブロック18の内部に繁殖可能な状
態で閉じこめることができる。
Next, the porous block 18 will be described. FIG. 3 shows a perspective view of the porous block 18. As shown in FIG. 3, the porous block 18 can be formed in a rectangular shape, for example. The porous block 18 is obtained by kneading Bacillus subtilis held on a carrier together with sand and stone together with cement paste and solidifying the mixture. Cement products show strong alkalinity, but Bacillus subtilis according to the present invention is
Since it can survive in the strongly acidic to strongly alkaline range of PH11, it can be confined in the porous block 18 in a state where it can reproduce.

【0017】この多孔質ブロック18を各処理槽2〜6
及び便槽10に投入すると、孔部から内部に水分が浸透
し、枯草菌が水中の大腸菌や腐敗菌等を分解しながら繁
殖する。処理槽2〜6及び便槽10には、水質浄化材1
7と多孔質ブロック18のいずれも用いることができ
る。例えば、処理槽2,3,5には水質浄化材17また
は多孔質ブロック18を1個、便槽10および処理槽6
には水質浄化材17または多孔質ブロック18を2個使
用する。また、処理槽4には、水質浄化材17を1個お
よび内容物の量を半分に減らした水質浄化材17を1個
用いることができ、また、多孔質ブロック18を1個と
半分用いることもできる。水質浄化材17は、処理槽2
〜6に架け渡して設けられた支持棒材27にロープを介
して吊り下げて使用される。また、多孔質ブロック18
は、上端にフック部材を備えると共に本体部に通水性を
有する網状袋体に収納されている。多孔質ブロック18
は、ロープを介して支持棒材27に吊り下げられて使用
される。かかる構成によって、水質浄化材17と多孔質
ブロック18の通水性がよくなるので、枯草菌の活性を
向上させることができる。
Each of the treatment tanks 2 to 6 is provided with the porous block 18.
Also, when placed in the toilet tank 10, water permeates into the interior from the hole, and Bacillus subtilis propagates while decomposing E. coli and spoilage bacteria in the water. In the treatment tanks 2 to 6 and the toilet tank 10, the water purification material 1
Both 7 and porous block 18 can be used. For example, the treatment tanks 2, 3 and 5 each include one water purification material 17 or one porous block 18, the toilet tank 10 and the treatment tank 6
For this purpose, two water purification materials 17 or two porous blocks 18 are used. Further, in the treatment tank 4, it is possible to use one water purification material 17 and one water purification material 17 in which the amount of contents is reduced to half, and one porous block 18 and half are used. You can also The water purification material 17 is used in the treatment tank 2
6 to 6 are used by suspending them via a rope on a supporting rod member 27 that is provided so as to span over 6 to 6. In addition, the porous block 18
Is housed in a mesh bag having a hook member at the upper end and water permeability in the main body. Porous block 18
Is used by being suspended from the support rod 27 via a rope. With such a structure, the water purifying material 17 and the porous block 18 have good water permeability, and thus the activity of Bacillus subtilis can be improved.

【0018】家屋7から流れ出る排水は、排水管8から
処理槽2〜4に流入し、水質浄化材17または多孔質ブ
ロック18に含まれる枯草菌の働きによって浄化され
る。また、トイレ9から排出される汚物は、便槽10と
処理槽5でそれぞれ浄化される。浄化された水は処理槽
2〜6を、通水路11を介して順に運ばれ、さらに排水
路12から河川13に放流される。かかる構成によっ
て、大がかりな下水処理施設を建造する必要がなくな
り、簡単に下水の処理を行うことができる。
The waste water flowing out from the house 7 flows into the treatment tanks 2 to 4 through the drain pipe 8 and is purified by the action of Bacillus subtilis contained in the water purification material 17 or the porous block 18. In addition, the waste discharged from the toilet 9 is purified in the toilet tank 10 and the treatment tank 5, respectively. The purified water is sequentially carried through the treatment tanks 2 to 6 via the water passage 11, and is further discharged from the drainage passage 12 to the river 13. With such a configuration, it is not necessary to construct a large-scale sewage treatment facility, and sewage treatment can be performed easily.

【0019】(実施の形態2)図4は、本発明の第2の
実施の形態に係る水質浄化設備を示す断面図である。水
質浄化設備20は、水路21内に配置された多数の多孔
質ブロック18からなる堰22と、堰22の下流側に配
置された多数の水質浄化材17からなる堰23とを有し
ている。
(Embodiment 2) FIG. 4 is a sectional view showing a water purification facility according to a second embodiment of the present invention. The water purification facility 20 has a weir 22 made up of a large number of porous blocks 18 arranged in a water channel 21, and a weir 23 made up of a large number of water purification materials 17 arranged downstream of the weir 22. .

【0020】水路21は、コンクリートからなる底板2
4及び側壁25を有し、上方に開口した溝形に形成され
ている。堰22の上流側には、水路21の両側壁25の
上端部に架け渡して設けられた支持部材に多孔質ブロッ
ク18が吊下げて配置されている。堰22と堰23の間
の底板24上には、複数の多孔質ブロック18が少しの
隙間をあけて並べて配置されている。また、堰23は、
堰22より低く設けられている。
The water channel 21 is a bottom plate 2 made of concrete.
4 and a side wall 25, and is formed in a groove shape that opens upward. On the upstream side of the weir 22, the porous block 18 is arranged so as to be suspended from a supporting member provided over the upper ends of the side walls 25 of the water channel 21. On the bottom plate 24 between the weir 22 and the weir 23, a plurality of porous blocks 18 are arranged side by side with a small gap. In addition, the weir 23,
It is provided lower than the weir 22.

【0021】水路21に流れる汚水は、堰22の多孔質
ブロック18の上側を越えて下流側に流れ、また、汚水
の一部は、多孔質ブロック18の内部を通過して下流側
に流れる。堰22を越えて落下する水は、周囲の空気を
巻き込んで水中に混入、溶解させ、多孔質ブロック18
から流出した枯草菌に酸素を供給する。
The sewage flowing in the water channel 21 flows to the downstream side beyond the upper side of the porous block 18 of the weir 22, and a part of the sewage passes through the inside of the porous block 18 to the downstream side. The water falling over the weir 22 is engulfed by the surrounding air to be mixed and dissolved in the water, and the porous block 18
Oxygen is supplied to the Bacillus subtilis spilled from the.

【0022】次いで、堰22の下流側に流れた汚水は、
堰23の水質浄化材17の上側を越えて下流側に流れ、
また、汚水の一部は、水質浄化材17の内部を通過して
下流側に流れる。堰23を越えて落下する水は、周囲の
空気を巻き込んで水中に混入、溶解させ、水質浄化材1
7から流出した枯草菌に酸素を供給する。
Next, the sewage flowing downstream of the weir 22 is
Flows over the water purification material 17 of the weir 23 to the downstream side,
Moreover, a part of the sewage passes through the inside of the water purification material 17 and flows to the downstream side. The water falling over the weir 23 is engulfed by the surrounding air to be mixed and dissolved in the water, and the water purification material 1
Oxygen is supplied to Bacillus subtilis flowing out from 7.

【0023】また、水路21に流れる汚水は、吊り下げ
られた多孔質ブロック18及び底板24上に配置された
多孔質ブロック18内も通過して、枯草菌による水質浄
化を促進される。かかる構成によって、枯草菌を活性化
させ、汚水の処理を迅速に進めることができる。
The sewage flowing in the water channel 21 also passes through the suspended porous block 18 and the porous block 18 arranged on the bottom plate 24 to promote water purification by Bacillus subtilis. With such a configuration, Bacillus subtilis can be activated and the treatment of sewage can be promptly advanced.

【0024】[0024]

【実施例】図1に示す水路において水質の試験を行っ
た。水路の水を採取して1回目の試験を行い、10日後
に2回目の試験を行った。表1に、1回目と2回目の試
験結果を示す。なお、外観は濁から澄に変化し、臭気は
下水臭から無に変化した。
Example A water quality test was conducted in the channel shown in FIG. The water in the waterway was sampled for the first test, and 10 days later, the second test was performed. Table 1 shows the results of the first and second tests. The appearance changed from turbid to clear, and the odor changed from sewage odor to nothing.

【0025】[0025]

【表1】 [Table 1]

【0026】生物化学的酸素要求量(BOD)は120
mg/Lから7.5mg/Lに減少し、浮遊物質(S
S)も83mg/Lから3mg/Lに減少した。また、
大腸菌群数も4000個/Lから430個/Lに減少し
たので、確実に浄化が進行したといえる。海でのアオコ
の発生を抑えるための指標となる窒素含有量とリン含有
量のうち、窒素含有量は5.2mg/Lから10mg/
Lに増加している。これは、窒素含有量を測定するサン
プルの採取時に上流側にある学校から大量の排水があっ
たため浄化されていない排水がそのまま測定されたと考
えられる。
Biochemical oxygen demand (BOD) is 120
mg / L to 7.5 mg / L, and suspended solids (S
S) also decreased from 83 mg / L to 3 mg / L. Also,
Since the number of coliforms also decreased from 4000 / L to 430 / L, it can be said that the purification proceeded reliably. Of the nitrogen content and phosphorus content, which are indicators for suppressing the occurrence of blue-green algae in the sea, the nitrogen content ranges from 5.2 mg / L to 10 mg / L.
It has increased to L. It is considered that this was because the unpurified wastewater was measured as it was because there was a large amount of wastewater from the school upstream when the sample for measuring the nitrogen content was collected.

【0027】[0027]

【発明の効果】本発明によれば次の効果を奏する。 (1)水質浄化材は、竹炭を粉砕したものを枯草菌の担
体として用いているので、繊維方向に空洞部が形成さ
れ、この空洞部内に担持された枯草菌によって、水の浄
化を効率よく行うことができる。 (2)竹炭および枯草菌を、袋体に封入すると、竹炭お
よび枯草菌の流出が防止され、菌の補充回数を減らすこ
とができ、また、袋体が可撓性を有するので、設置場所
の形状に合わせて外形を変えることができ、設置の自由
度を上げることができる。 (3)袋体にみかんの皮を封入すると、みかんの皮を枯
草菌に分解させて枯草菌の活性を高め、その数を増加さ
せることができ、水中での使用開始時の浄水作業が迅速
に行われる。 (4)多孔質構造を有する石を入れると、枯草菌の担持
を行うとともに、石の重量によって、水質浄化材が浮き
上がることを防止できる。 (5)竹炭、枯草菌、みかんの皮および石の重量比を
5:2:1:2とすると、枯草菌の活性が高められ、浄
水を迅速に行うことができる。 (6)竹の葉を封入すると、枯草菌の活性を高めること
ができる。 (7)水質浄化設備は、枯草菌を担持した多孔質ブロッ
クを備えているので、整列して設置することができ、ま
た、袋体に封入された水質浄化材を設けるので、異形の
処理槽にも対応できる。 (8)水質浄化方法は、多孔質ブロックまたは水質浄化
材で堰を形成し、堰を越えて落下する水により空気を水
中に巻き込んで、枯草菌に酸素を供給するので、好気性
菌である枯草菌の処理能力を上げることができる。
The present invention has the following effects. (1) Since the water purification material uses crushed bamboo charcoal as a carrier for Bacillus subtilis, a hollow portion is formed in the fiber direction, and the Bacillus subtilis carried in the hollow portion efficiently purifies water. It can be carried out. (2) By enclosing bamboo charcoal and Bacillus subtilis in a bag, outflow of bamboo charcoal and Bacillus subtilis can be prevented, the number of times of replenishment of bacteria can be reduced, and the bag has flexibility, so The outer shape can be changed according to the shape, and the degree of freedom in installation can be increased. (3) When the mandarin orange peel is enclosed in the bag, the mandarin orange peel can be decomposed into Bacillus subtilis and the activity of Bacillus subtilis can be increased, and the number of them can be increased. The water purification work at the start of use in water is quick. To be done. (4) When a stone having a porous structure is added, it is possible to support Bacillus subtilis and prevent the water purification material from rising due to the weight of the stone. (5) When the weight ratio of bamboo charcoal, Bacillus subtilis, mandarin orange peel and stone is set to 5: 2: 1: 2, the activity of Bacillus subtilis is enhanced and water purification can be performed quickly. (6) Encapsulating bamboo leaves can enhance the activity of Bacillus subtilis. (7) The water purification equipment is equipped with a porous block supporting Bacillus subtilis, so that it can be installed side by side. In addition, since the water purification material enclosed in the bag is provided, a modified treatment tank is provided. Can also be used. (8) The water purification method is an aerobic bacterium because a weir is formed from a porous block or a water purification material, air is entrained in the water by the water falling over the weir, and oxygen is supplied to Bacillus subtilis. The processing ability of Bacillus subtilis can be improved.

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

【図1】 本発明の第1の実施の形態に係る水質浄化材
を用いた水質浄化設備の構成を示す説明図である。
FIG. 1 is an explanatory diagram showing a configuration of a water purification facility using a water purification material according to a first embodiment of the present invention.

【図2】 同水質浄化設備に用いられる水質浄化材の側
断面図である。
FIG. 2 is a side sectional view of a water purification material used in the same water purification facility.

【図3】 同水質浄化設備に用いられる多孔質ブロック
の斜視図である。
FIG. 3 is a perspective view of a porous block used in the same water purification facility.

【図4】 本発明の第2の実施の形態に係る水質浄化設
備を示す断面図である。
FIG. 4 is a cross-sectional view showing a water purification facility according to a second embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1 水質浄化設備 2〜6 処理槽 7 家屋 8 排水管 9 トイレ 10 便槽 11 通水路 12 排水路 13 河川 14 台所 15 洗濯機 16 風呂場 17 水質浄化材 18 多孔質ブロック 19 袋体 20 水質浄化設備 21 水路 22,23 堰 24 底板 25 側壁 26 フック部材 27 支持棒材 1 Water purification equipment 2-6 processing tanks 7 houses 8 drainage pipes 9 toilets 10 toilet tanks 11 waterways 12 drainage channels 13 rivers 14 kitchen 15 washing machine 16 bathroom 17 Water purification material 18 Porous block 19 bags 20 Water purification equipment 21 waterways 22,23 weir 24 Bottom plate 25 side wall 26 Hook members 27 Support bar

Claims (8)

【特許請求の範囲】[Claims] 【請求項1】 所定粒度に粉砕された竹炭と、この竹炭
に担持された枯草菌とを有することを特徴とする水質浄
化材。
1. A water purification material comprising bamboo charcoal crushed to a predetermined particle size and Bacillus subtilis carried on the bamboo charcoal.
【請求項2】 所定粒度に粉砕された竹炭と、この竹炭
に担持された枯草菌とを、通水性および可撓性を有する
袋体に封入したことを特徴とする袋入り水質浄化材。
2. A water purification material in a bag, characterized in that bamboo charcoal crushed to a predetermined particle size and Bacillus subtilis carried on the charcoal are enclosed in a bag having water permeability and flexibility.
【請求項3】 前記袋体にみかんの皮および粉砕された
多孔質構造を有する石を封入したことを特徴とする請求
項2に記載の袋入り水質浄化材。
3. The water purification material in a bag according to claim 2, wherein mandarin orange peel and crushed stone having a porous structure are enclosed in the bag.
【請求項4】 前記竹炭、前記枯草菌、前記みかんの
皮、および前記石の重量比を、その誤差が10%以内と
なる範囲内で、5:2:1:2としたことを特徴とする
請求項3に記載の袋入り水質浄化材。
4. The weight ratio of the bamboo charcoal, the Bacillus subtilis, the mandarin orange peel, and the stone is set to 5: 2: 1: 2 within a range where the error is within 10%. The water purification material in a bag according to claim 3.
【請求項5】 前記袋体に、粉砕した竹の葉を、全体に
対する重量比が20〜50%となる範囲で封入したこと
を特徴とする請求項2から4のいずれかの項に記載の袋
入り水質浄化材。
5. The bag body according to claim 2, wherein crushed bamboo leaves are enclosed in the bag body in a weight ratio of 20 to 50%. Water purification material in a bag.
【請求項6】 家庭から排出された処理水を貯留可能な
処理槽と、この処理槽内に配置された枯草菌を担持した
多孔質ブロックまたは請求項2〜5のいずれかの項に記
載の袋入り水質浄化材とを備えたことを特徴とする水質
浄化設備。
6. A treatment tank capable of storing treated water discharged from a home, a porous block supporting Bacillus subtilis loaded in the treatment tank, or the treatment tank according to claim 2. A water purification facility comprising a bag of water purification material.
【請求項7】 前記処理槽は、既設の側溝を複数に仕切
って形成したことを特徴とする水質浄化設備。
7. The water purification facility, wherein the treatment tank is formed by dividing an existing side groove into a plurality of partitions.
【請求項8】 枯草菌を担持した多孔質ブロックおよび
請求項2〜5のいずれかの項に記載の袋入り水質浄化材
のうちの一方または両方を、水路内に積層して堰を形成
し、上流側から前記堰を越えて落下する水により空気を
水中に巻き込んで、前記枯草菌に酸素を供給することを
特徴とする水質浄化方法。
8. A weir is formed by stacking one or both of a porous block supporting Bacillus subtilis and the water purification material in a bag according to any one of claims 2 to 5 in a water channel. A method for purifying water, characterized in that air is entrained in water by water falling from the upstream side over the weir to supply oxygen to the Bacillus subtilis.
JP2001395105A 2001-12-26 2001-12-26 Material for purifying water, bag-in material for purifying water, facility for purifying water using this, and method for purifying water Pending JP2003190982A (en)

Priority Applications (1)

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JP2001395105A JP2003190982A (en) 2001-12-26 2001-12-26 Material for purifying water, bag-in material for purifying water, facility for purifying water using this, and method for purifying water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2001395105A JP2003190982A (en) 2001-12-26 2001-12-26 Material for purifying water, bag-in material for purifying water, facility for purifying water using this, and method for purifying water

Publications (1)

Publication Number Publication Date
JP2003190982A true JP2003190982A (en) 2003-07-08

Family

ID=27601623

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Link
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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009095738A (en) * 2007-10-16 2009-05-07 Aoyama Eco System:Kk Molding for water purification and manufacturing method of the same
JP2012235732A (en) * 2011-05-11 2012-12-06 Noriomi Watanabe Hydroponic method for zingiber mioga
JP2020049393A (en) * 2018-09-21 2020-04-02 松本工業株式会社 Sewage disposal method
JP2020048429A (en) * 2018-09-21 2020-04-02 松本工業株式会社 Method for producing nitrated nutrient solution from human excrement
JP2022050994A (en) * 2020-09-18 2022-03-31 株式会社ASPiA Oil removal method

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009095738A (en) * 2007-10-16 2009-05-07 Aoyama Eco System:Kk Molding for water purification and manufacturing method of the same
JP2012235732A (en) * 2011-05-11 2012-12-06 Noriomi Watanabe Hydroponic method for zingiber mioga
JP2020049393A (en) * 2018-09-21 2020-04-02 松本工業株式会社 Sewage disposal method
JP2020048429A (en) * 2018-09-21 2020-04-02 松本工業株式会社 Method for producing nitrated nutrient solution from human excrement
JP2022050994A (en) * 2020-09-18 2022-03-31 株式会社ASPiA Oil removal method

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