JP2958316B1 - Water purification equipment - Google Patents
Water purification equipmentInfo
- Publication number
- JP2958316B1 JP2958316B1 JP10293840A JP29384098A JP2958316B1 JP 2958316 B1 JP2958316 B1 JP 2958316B1 JP 10293840 A JP10293840 A JP 10293840A JP 29384098 A JP29384098 A JP 29384098A JP 2958316 B1 JP2958316 B1 JP 2958316B1
- Authority
- JP
- Japan
- Prior art keywords
- water
- tank
- inner tank
- raw water
- annular space
- 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.)
- Expired - Fee Related
Links
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Biological Treatment Of Waste Water (AREA)
Abstract
【要約】
【課題】設置面積が小さく構造が簡単で、浄化性能と経
済性に優れた浄水装置を提供する。
【解決手段】浄水装置1は同心状に配置された円筒形の
外槽2と内槽10を有する。内槽10の底部は開口して
外槽2と連通している。両槽の間の環状の空間は、活性
土壌部20により上下に区画される。活性土壌部の下方
の空間と、内槽の内部には、汚濁水中の固形物を吸着す
る接触材40が設けられる。外槽2の中心には吸引管8
がある。流入管31で外槽2の上部に導入された汚濁水は
周方向に移動しながら下降し、活性土壌部を通過して処
理され、接触材40に接触しながら旋回して内槽10内に
入り、上昇して浄化水導出手段50から槽外に導出され
る。剥離して底部に堆積した固形物は、吸引管8 を通し
て槽外に効率的に吸い出せる。運転に動力がかからず経
済的である。An object of the present invention is to provide a water purification apparatus having a small installation area, a simple structure, and excellent purification performance and economic efficiency. A water purification apparatus has a cylindrical outer tank and an inner tank arranged concentrically. The bottom of the inner tank 10 is open and communicates with the outer tank 2. The annular space between both tanks is vertically divided by the active soil part 20. A contact member 40 for adsorbing solids in the polluted water is provided in the space below the active soil portion and inside the inner tank. At the center of the outer tank 2 is a suction pipe 8
There is. The contaminated water introduced into the upper part of the outer tank 2 by the inflow pipe 31 moves down in the circumferential direction, descends, is processed through the active soil part, turns while contacting the contact material 40, and turns into the inner tank 10. It enters, rises and is drawn out of the tank from the purified water deriving means 50. The solids that have separated and deposited on the bottom can be efficiently sucked out of the tank through the suction pipe 8. It is economical because no power is required for driving.
Description
【0001】[0001]
【発明の属する技術分野】本発明は、汚濁された水を浄
化するための浄水装置に関する。本発明の浄水装置は、
堀、湖沼、河川の水質改善や、家畜のし尿処理等に利用
することができる。TECHNICAL FIELD The present invention relates to a water purification device for purifying polluted water. The water purification device of the present invention is
It can be used to improve the water quality of moats, lakes and marshes, and rivers, and to treat human wastes.
【0002】[0002]
【従来の技術】近年、堀、湖沼、河川等の水質汚染が急
速に進み、深刻の度合いを深めて地球規模の問題にまで
なっている。その原因は多岐にわたるが、例えば家庭雑
排水、降雨汚染水、工場排水、家畜のし尿等の水域への
流入が主要な原因と考えられる。その対策としては、下
水道の整備や工場排水基準の制定等が行われている。し
かしながら、現状では、多くの堀、湖沼、河川等におい
て臭気・アオコの発生等が見られ、水質の改善は必ずし
も進んでいないのが実情である。2. Description of the Related Art In recent years, water pollution of moats, lakes, marshes, rivers, and the like has rapidly progressed, and the severity of the pollution has deepened to a global scale. Although the causes are various, it is considered that the main cause is, for example, inflow of domestic wastewater, rainfall contaminated water, industrial wastewater, livestock night soil and the like into water bodies. As a countermeasure, maintenance of sewerage and establishment of factory drainage standards are being carried out. However, at present, odors and blue-green algae are generated in many moats, lakes, marshes, rivers, and the like, and water quality has not always been improved.
【0003】上述した堀、湖沼、河川等における水質汚
染は、当該水域への流入水の不足や水の循環の不足によ
り酸素不足と富栄養化(窒素、リン等)が進行すること
によって発生すると考えられる。[0003] Water pollution in moats, lakes, marshes, rivers and the like described above is caused by insufficient oxygen and eutrophication (nitrogen, phosphorus, etc.) due to lack of inflow of water and lack of circulation of water. Conceivable.
【0004】このような問題を解決するために、従来は
水中ポンプや噴水を設置することにより水に流れを起こ
して酸素を水に溶かし込み、また水底には軽石等の多孔
石や活性炭等の層を敷設することによって水中の汚濁物
質を除去していた。In order to solve such a problem, conventionally, a submersible pump or a fountain is installed to cause a flow in the water to dissolve oxygen into the water, and a porous stone such as pumice or activated carbon such as activated carbon is provided on the bottom of the water. By laying a layer, pollutants in the water were removed.
【0005】しかしながら、以上説明したような従来の
大規模な浄化設備は、例えば河川等の場合には降雨水に
影響されて増水や洪水が発生するため、実際には十分な
効果をあげることができなかった。[0005] However, the conventional large-scale purification facilities as described above, for example, in the case of rivers and the like, are affected by rainwater and cause increased water and floods. could not.
【0006】そこで、従来は、図13及び図14に示す
ような浄水設備が河川・湖沼・堀等に隣接して設置され
ていた。図13は横流れ浄化方式と呼ばれ、図14は縦
流れ浄化方式と呼ばれている。Therefore, conventionally, water purification facilities as shown in FIGS. 13 and 14 have been installed adjacent to rivers, lakes, marshes, moats and the like. FIG. 13 is called a horizontal flow purification system, and FIG. 14 is called a vertical flow purification system.
【0007】図13に示す横流れ浄化方式の浄化装置
は、箱形の浄化槽100を有している。浄化槽100の
内部は左右互い違いに設けられた複数の隔壁101によ
って水平面内で蛇行した流路が形成されている。この浄
化槽100の流路内には、汚濁物質が付着する接触部材
が設けられている。浄化槽100の入り口から導入され
た汚濁水は流路を流れる間に接触部材に接触し、汚濁物
質は接触部材に付着する。接触部材に付着した汚濁物質
は浄化槽100の底に沈殿する。流路を通り抜けた水は
浄化された水として浄化槽100外に排出され、又は直
列に連結して設置された次の浄化槽に導入される。[0007] The purification apparatus of the lateral flow purification system shown in FIG. 13 has a box-shaped purification tank 100. The inside of the septic tank 100 has a flow path meandering in a horizontal plane formed by a plurality of partition walls 101 provided alternately on the left and right. A contact member to which pollutants adhere is provided in the flow path of the septic tank 100. The contaminated water introduced from the inlet of the septic tank 100 comes into contact with the contact member while flowing through the flow path, and the pollutant adheres to the contact member. The contaminants attached to the contact member settle at the bottom of the septic tank 100. The water that has passed through the flow path is discharged as purified water out of the septic tank 100, or introduced into the next septic tank installed in series.
【0008】図14に示す縦流れ浄化方式の浄化装置も
箱形の浄化槽200を有している。この浄化槽200の
内部は上下互い違いに設けられた複数の隔壁201によ
って上下方向に蛇行した流路が形成されている。この浄
化槽200の流路内には、汚濁物質が付着する接触部材
が設けられている。浄化槽200の入り口から導入され
た汚濁水は流路を流れる間に接触部材に接触し、汚濁物
質は接触部材に付着する。接触部材に付着した汚濁物質
は浄化槽200の底に沈殿する。流路を通り抜けた水は
浄化された水として浄化槽200外に排出され、又は直
列に連結して設置された次の浄化槽に導入される。[0008] The purification apparatus of the vertical flow purification system shown in FIG. 14 also has a box-shaped purification tank 200. Inside the septic tank 200, a flow path meandering in the vertical direction is formed by a plurality of partition walls 201 provided alternately up and down. A contact member to which the pollutant adheres is provided in the flow path of the septic tank 200. The polluted water introduced from the entrance of the septic tank 200 contacts the contact member while flowing through the flow path, and the pollutant adheres to the contact member. The contaminants attached to the contact member settle at the bottom of the septic tank 200. The water that has passed through the flow path is discharged as purified water out of the septic tank 200, or is introduced into the next septic tank installed in series.
【0009】[0009]
【発明が解決しようとする課題】原水の移動は接触部材
に接触している流速が均一であることが望ましく、その
ためには原水が移動する流速が流路内のどの位置でも一
定になることが望ましい。しかしながら上述した従来の
浄化装置は、箱形の浄化槽内に設けられた断面矩形の直
線的なジグザグの流路を汚濁水が流れる構造であった。
このため、縦流れ・横流れのどちらの方式の装置におい
ても、流れ方向に対して中央部の流速が隔壁側に比して
速くなり、流速が一定にならないという問題があった。
また、どちらの方式の装置においても、多数の隔壁が必
要であり、構造が複雑であるという問題があった。In the movement of raw water, it is desirable that the flow velocity in contact with the contact member is uniform, and for that purpose, the flow velocity of raw water must be constant at any position in the flow path. desirable. However, the above-described conventional purification apparatus has a structure in which polluted water flows through a straight zigzag flow path having a rectangular cross section provided in a box-shaped purification tank.
For this reason, in both the vertical flow and the horizontal flow systems, there is a problem that the flow velocity in the central part is faster than the partition wall side in the flow direction, and the flow velocity is not constant.
In addition, both types of devices require a large number of partition walls, and there is a problem that the structure is complicated.
【0010】図13に示した横流れ浄化方式の場合、浄
化槽100をあまり深くすると、底における流速が表層
側に比べて遅くなる。このため、浄化槽100をあまり
深くすることはできず、従って必要な容積を得るために
は広い設置面積が必要になるという問題があった。In the case of the lateral flow purification system shown in FIG. 13, when the purification tank 100 is too deep, the flow velocity at the bottom becomes slower than that at the surface. Therefore, there is a problem that the septic tank 100 cannot be made too deep, so that a large installation area is required to obtain a required volume.
【0011】また、浄化槽の底に沈殿して堆積した浮遊
固形物は定期的に除去しなければならない。どちらの方
式の装置においても、浮遊固形物の定期的な除去は、浄
化槽内の接触部材を一旦槽外に撤去した後、吸引等によ
り行っている。即ち、従来の装置によれば、多くの接触
部材をそのままにして堆積物の除去を行うことができ
ず、メンテナンスのために浄化槽内の接触部材を定期的
に出し入れしなければならないという問題があった。Further, suspended solids deposited and deposited on the bottom of the septic tank must be periodically removed. In both types of apparatuses, the periodic removal of suspended solids is performed by suction or the like after once removing the contact member in the septic tank outside the tank. That is, according to the conventional apparatus, there is a problem that the deposit cannot be removed while leaving many contact members as they are, and the contact members in the septic tank need to be periodically taken in and out for maintenance. Was.
【0012】本発明は、設置面積が小さく構造が簡単で
ありながら浄化性能に優れた浄水装置を提供することを
目的としている。An object of the present invention is to provide a water purification apparatus which has a small installation area and a simple structure, and has excellent purification performance.
【0013】[0013]
【課題を解決するための手段】請求項1に記載された浄
水装置(1)は、底部が閉止された筒形の外槽(2)
と、開口した底部が前記外槽の底部よりも上方に位置す
るように前記外槽の内部に設けられた内槽(10)と、
前記外槽と前記内槽の間の環状の空間を上部と下部に分
割するように該空間内に設けられた活性土壌部(20)
と、前記外槽に接続されて前記環状の空間の前記上部に
原水を流入させる原水供給手段(30)と、前記環状の
空間の前記下部と前記内槽の内部に設けられて前記原水
中の汚濁物質が付着する接触部材(40)と、前記内槽
の水面の近傍に設けられて浄化水を外に導く浄化水導出
手段(50)とを有している。A water purifier (1) according to the present invention has a cylindrical outer tank (2) having a closed bottom.
An inner tank (10) provided inside the outer tank such that the opened bottom is located above the bottom of the outer tank;
An activated soil portion (20) provided in the space so as to divide an annular space between the outer tank and the inner tank into an upper part and a lower part;
A raw water supply means (30) connected to the outer tub to allow raw water to flow into the upper part of the annular space, and a raw water supply means (30) provided in the lower part of the annular space and inside the inner tub, It has a contact member (40) to which pollutants adhere, and a purified water deriving means (50) provided near the water surface of the inner tank and guiding purified water to the outside.
【0014】請求項2に記載された浄水装置(1)は、
請求項1記載の浄水装置において、前記活性土壌部(2
0)が、前記環状の空間を上部と下部に分割するように
該空間内に設けられた通水性の保持材(メッシュ材2
1)と、前記保持材に保持された活性土壌(22)を有
していることを特徴としている。[0014] The water purification apparatus (1) according to claim 2 is
The water purification device according to claim 1, wherein the active soil portion (2)
0) is a water-permeable holding material (mesh material 2) provided in the annular space so as to divide the annular space into an upper portion and a lower portion.
1) and an active soil (22) held by the holding material.
【0015】請求項3に記載された浄水装置(1)は、
請求項1記載の浄水装置において、前記原水供給手段
(30)が、前記環状の空間の上部に原水を導く原水流
入管(31)と、前記原水流入管から供給された原水を
前記環状の空間内において周方向に向かわせる方向規制
部材(33)とを有していることを特徴としている。[0015] The water purification apparatus (1) according to claim 3 is
2. The water purification device according to claim 1, wherein the raw water supply means (30) includes a raw water inflow pipe (31) for guiding raw water to an upper part of the annular space, and a raw water supplied from the raw water inflow pipe into the annular space. 3. And a direction regulating member (33) for turning in the circumferential direction.
【0016】請求項4に記載された浄水装置(1)は、
請求項1記載の浄水装置において、前記浄化水導出手段
(50)が、閉止された底面と開口した上面とを有し、
内槽の略中央に設けられて浄化水を受け入れる筒形の浄
化水収納槽(51)と、前記浄化水収納槽に連通して前
記外槽の外に導出される浄化水導水管(52)とを有す
ることを特徴としている。[0016] The water purification device (1) according to claim 4 is
The purified water purifier according to claim 1, wherein the purified water deriving means (50) has a closed bottom surface and an open top surface,
A purified water storage tank (51) provided substantially at the center of the inner tank and receiving purified water, and a purified water conduit (52) communicated with the purified water storage tank and led out of the outer tank. And characterized in that:
【0017】請求項5に記載された浄水装置(1)は、
請求項1記載の浄水装置において、前記外槽の底部の略
中央に沈殿した汚泥を受ける汚泥受け槽(6)が設けら
れ、前記汚泥受け槽に沈殿した汚泥を前記外槽及び前記
内槽の外に吸い上げるための吸引管(8)が設けられた
ことを特徴としている。[0017] The water purification device (1) according to claim 5 is
2. The water purification apparatus according to claim 1, further comprising a sludge receiving tank (6) for receiving the settled sludge substantially at the center of the bottom of the outer tank, and supplying the sludge settled in the sludge receiving tank to the outer tank and the inner tank. It is characterized in that a suction pipe (8) for sucking up outside is provided.
【0018】請求項6に記載された浄水装置(1)は、
請求項5記載の浄水装置において、前記汚泥受け槽
(6)と前記外槽(2)の底部の少なくともいずれか一
方が、テーパ状に形成されていることを特徴としてい
る。[0018] The water purification apparatus (1) according to claim 6 is
The water purification apparatus according to claim 5, wherein at least one of the bottom of the sludge receiving tank (6) and the bottom of the outer tank (2) is formed in a tapered shape.
【0019】請求項7に記載された浄水装置(1)は、
請求項1記載の浄水装置において、前記外槽(2)と前
記内槽(10)は実質的に円筒形であり、両槽は実質的
に同心状に配置されていることを特徴としている。The water purifier (1) according to claim 7 is
The water purifier according to claim 1, wherein the outer tank (2) and the inner tank (10) are substantially cylindrical, and both tanks are arranged substantially concentrically.
【0020】請求項8に記載された浄水装置(1)は、
請求項1記載の浄水装置において、前記外槽(2)の底
部に複数の内槽支持基礎(11)を設置し、前記内槽
(10)を前記内槽支持基礎上に設置したことを特徴と
している。The water purifier (1) according to claim 8 is
The water purifier according to claim 1, wherein a plurality of inner tank support bases (11) are installed at the bottom of the outer tank (2), and the inner tank (10) is installed on the inner tank support base. And
【0021】請求項9に記載された浄水装置(1)は、
請求項1記載の浄水装置において、水平面内における前
記環状の空間の断面積と、水平面内における前記内槽
(10)の断面積の比が、ほぼ1:1であることを特徴
としている。According to a ninth aspect of the present invention, there is provided a water purification device (1).
2. The water purification apparatus according to claim 1, wherein a ratio of a cross-sectional area of the annular space in a horizontal plane to a cross-sectional area of the inner tank (10) in a horizontal plane is approximately 1: 1.
【0022】請求項10に記載された浄水装置(1)
は、請求項1記載の浄水装置において、前記環状の空間
における水の流速(周方向の流速と上下方向の流速の少
なくともいずれか一方)と、前記内槽(10)の内部に
おける水の流速が実質的に等しいことを特徴としてい
る。[0022] A water purification apparatus according to claim 10 (1).
The water purifier according to claim 1, wherein a flow rate of the water in the annular space (at least one of a flow rate in a circumferential direction and a flow rate in a vertical direction) and a flow rate of the water in the inner tank (10) are reduced. It is characterized by being substantially equal.
【0023】請求項11に記載された浄水装置(1)
は、請求項1記載の浄水装置において、前記外槽(2)
は水圧に耐えうる剛性を備えており、前記内槽(10)
は円筒形に保持した可撓性材料からなることを特徴とし
ている。[0023] A water purification apparatus (1) according to claim 11.
The water purifier according to claim 1, wherein the outer tank (2) is provided.
Is provided with rigidity that can withstand water pressure, and the inner tank (10)
Is made of a flexible material held in a cylindrical shape.
【0024】請求項12に記載された浄水装置(1)
は、請求項11記載の浄水装置において、前記可撓性材
料(不織布12)の上端と下端が環状の保持材(13)
によって保持されており、前記保持材は前記外槽(2)
の上部に掛け渡した桁材(41)から吊り下げられてい
ることを特徴としている。[0024] A water purification apparatus (1) according to claim 12.
The holding material (13) according to claim 11, wherein an upper end and a lower end of the flexible material (nonwoven fabric 12) are annular.
The holding material is held by the outer tub (2).
Is suspended from a girder material (41) extended over the upper part of the girder.
【0025】請求項13に記載された浄水装置(1)
は、請求項2記載の浄水装置において、前記原水が前記
環状の空間の上部から前記下部に移動する間、前記原水
中に溶出した活性土壌(22)の微生物が前記原水内に
おいて粘性物質を生成して前記原水中の汚濁物質を吸着
する作用が促進されるとともに、前記原水が前記内槽
(10)の下部から前記内槽(10)の内部に入り、前
記内槽(10)の内部の上方へと移動する間に、前記粘
性物質に吸着された前記汚濁物質が前記接触部材(4
0)に付着することを特徴としている。[0025] A water purification apparatus (1) according to claim 13.
The microorganism according to claim 2, wherein the microorganisms of the active soil (22) eluted in the raw water generate a viscous substance in the raw water while the raw water moves from the upper part to the lower part of the annular space. As a result, the action of adsorbing pollutants in the raw water is promoted, and the raw water enters the inside of the inner tank (10) from the lower part of the inner tank (10), and the inside of the inner tank (10) During the upward movement, the contaminant adsorbed by the viscous substance is transferred to the contact member (4
0).
【0026】[0026]
【発明の実施の形態】図1〜図12を参照して本発明の
実施の形態を説明する。図1〜図3に示すように、本例
の浄水装置1は全体として2重構造の円筒体であり、そ
の円筒の軸を実質的に鉛直にした姿勢で、略下半部が地
中に埋設されるように設置されている。外側の壁を構成
する外槽2は、水圧に耐えるために、コンクリートや、
ライナープレートやコルゲートパイプ等の鋼板のよう
に、剛性を備えた材料で形成されている。外槽2の底部
は基礎3によって閉止されている。基礎3は、地盤上に
設けられた栗石4と、その上に形成された基礎コンクリ
ート部5からなる。外槽2の底部を構成する基礎コンク
リート部5は、中心が低いテーパ状になっている。基礎
コンクリート部5の中央には汚泥受け槽6が設けられて
いる。汚泥受け槽6は逆円錐台形の凹部7を有してい
る。外槽2の上部は開口している。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the present invention will be described with reference to FIGS. As shown in FIG. 1 to FIG. 3, the water purification device 1 of the present embodiment is a cylindrical body having a double structure as a whole, and the lower half is substantially underground in a posture in which the axis of the cylinder is substantially vertical. It is installed to be buried. The outer tub 2 constituting the outer wall is made of concrete,
It is formed of a rigid material such as a steel plate such as a liner plate or a corrugated pipe. The bottom of the outer tub 2 is closed by a foundation 3. The foundation 3 is composed of a rubble stone 4 provided on the ground and a foundation concrete part 5 formed thereon. The base concrete part 5 constituting the bottom of the outer tub 2 is tapered at the center. A sludge receiving tank 6 is provided at the center of the basic concrete section 5. The sludge receiving tank 6 has an inverted truncated conical recess 7. The upper part of the outer tank 2 is open.
【0027】本例では、下半部を埋設構造として構造物
としての強度と安定性を高めたが、地下に基礎を設けず
に地面上に直接建設すれば建設費を安価に抑えることが
できる。In this example, the lower half is buried to increase the strength and stability of the structure. However, if it is constructed directly on the ground without providing an underground foundation, the construction cost can be reduced. .
【0028】図1に示すように、外槽2の中心にある汚
泥受け槽6には吸引管8が設けられている。吸引管8の
下端は、汚泥受け槽6の底面に所定の間隔をおいて対峙
している。吸引管8は、外槽2の中心軸と略一致した位
置に設けられている。図4に示すように、吸引管8は、
汚泥受け槽6の凹部7の開口に設置された略十字状の支
持具9に支えられている。吸引管8は、外槽2の中心線
に沿って上方に導かれており、槽外に出てから水平方向
に曲折して槽の外方に延出されている。図示しないが、
吸引管8には真空ポンプ等の吸引手段が連結されてい
る。又は、必要に応じて連結される。本浄水装置1で汚
濁水の浄化を行う過程において汚泥が外槽2の底部に落
ち、汚泥受け槽6の凹部7に溜まった量がある程度にな
ったら、吸引管8に連結されたポンプ等の吸引手段を作
動させ、沈殿した汚泥を吸引管8を通して槽の外に吸い
出す。As shown in FIG. 1, a suction pipe 8 is provided in a sludge receiving tank 6 at the center of the outer tank 2. The lower end of the suction pipe 8 faces the bottom surface of the sludge receiving tank 6 at a predetermined interval. The suction pipe 8 is provided at a position substantially coincident with the center axis of the outer tub 2. As shown in FIG. 4, the suction tube 8
It is supported by a substantially cross-shaped support 9 installed at the opening of the recess 7 of the sludge receiving tank 6. The suction pipe 8 is guided upward along the center line of the outer tub 2, and after being out of the tub, is bent in a horizontal direction and extends to the outside of the tub. Although not shown,
Suction means such as a vacuum pump is connected to the suction pipe 8. Alternatively, they are linked as needed. In the process of purifying the polluted water with the present water purification device 1, when the sludge falls to the bottom of the outer tank 2 and the amount of the sludge accumulated in the concave portion 7 of the sludge receiving tank 6 reaches a certain level, a pump or the like connected to the suction pipe 8 is used. The suction means is operated, and the precipitated sludge is sucked out of the tank through the suction pipe 8.
【0029】図1〜図3に示すように、外槽2の内部に
は内槽10が設置されている。内槽10は、底部が開口
した円筒形であり、外槽2より直径も高さも小さい。内
槽10と外槽2は実質的に同心円状に配置されている。
また、内槽10の開口した底部は、外槽2の底部よりも
上方に位置している。即ち、外槽2の底部には、所定間
隔で複数の(本例では6基の)内槽支持基礎11が周状
に固定されており、この内槽支持基礎11の上に、開口
した内槽10の底部が載置されて固定されている。内槽
支持基礎11としては、適当な外径の鋼管等を用いるこ
とができる。内槽10は大きな水圧を受けないので、外
槽2のような剛性の高い材料で堅固に構成する必要はな
いが、不透水性があり、汚水(汚濁水)に対してある程
度の耐久性のある素材を用いることが好ましい。As shown in FIGS. 1 to 3, an inner tank 10 is provided inside the outer tank 2. The inner tank 10 has a cylindrical shape with an open bottom, and is smaller in diameter and height than the outer tank 2. The inner tank 10 and the outer tank 2 are arranged substantially concentrically.
The open bottom of the inner tank 10 is located higher than the bottom of the outer tank 2. That is, a plurality of (six in this example) inner tank support bases 11 are fixed circumferentially at predetermined intervals on the bottom of the outer tank 2. The bottom of the tank 10 is placed and fixed. As the inner tank support base 11, a steel pipe or the like having an appropriate outer diameter can be used. Since the inner tank 10 is not subjected to a large water pressure, it is not necessary to form the inner tank 10 with a rigid material such as the outer tank 2, but it is impermeable and has a certain degree of durability against sewage (polluted water). It is preferable to use a certain material.
【0030】内槽10は大きな水圧は受けないので、可
撓性のある不透水性素材を用いてもよい。例えば、図5
に示すように、不織布12等を筒状に形成し、剛性を有
する環状の保持材13を上下両端に設け、上側の保持材
13を以て外槽2内に吊り下げてもよい。その場合に
は、前記内槽支持基礎11は必要ない。Since the inner tank 10 does not receive a large water pressure, a flexible water-impermeable material may be used. For example, FIG.
As shown in (2), the nonwoven fabric 12 and the like may be formed in a cylindrical shape, and rigid holding members 13 may be provided at both upper and lower ends, and may be suspended in the outer tank 2 with the upper holding members 13. In that case, the inner tank support base 11 is not required.
【0031】図1に示すように、外槽2と内槽10の間
には環状の空間が区画されるが、この空間内には活性土
壌部20が設けられている。活性土壌部20は、前記環
状の空間を上部と下部に分割するように該空間内に設け
られた通水性の保持材であるメッシュ材21と、このメ
ッシュ材21の上に設置された活性土壌22とを有して
いる。メッシュ材21は図6に示すように扇形のユニッ
トからなる。外槽2の内周面と内槽10の外周面との間
には、複数個の支持体23が所定間隔で放射状に固定さ
れており、メッシュ材21のユニットはこの支持体23
上に載置・固定されている。メッシュ材21の上にある
活性土壌は、外部の水に溶出しうるような透過性の袋体
に充填されている。この袋詰めの活性土壌は、前記環状
の空間の上部と下部を完全に区画するように密に配置さ
れるものではなく、槽内を流れる原水に浸って原水内に
溶出するようになっていればよい。なお、活性土壌22
を保持するための保持材としては、活性土壌を保持でき
る通水性のある部材であればよく、前述したようなメッ
シュ材21の他に、スリットが形成された板材でもよ
い。As shown in FIG. 1, an annular space is defined between the outer tank 2 and the inner tank 10, and an active soil portion 20 is provided in this space. The active soil portion 20 includes a mesh material 21 which is a water-permeable holding material provided in the space so as to divide the annular space into an upper portion and a lower portion, and an active soil installed on the mesh material 21. 22. The mesh member 21 is composed of a fan-shaped unit as shown in FIG. A plurality of supports 23 are fixed radially at predetermined intervals between the inner peripheral surface of the outer tub 2 and the outer peripheral surface of the inner tub 10.
Mounted and fixed on top. The active soil on the mesh material 21 is filled in a permeable bag that can be eluted into external water. The active soil in the bag is not densely arranged so as to completely separate the upper and lower parts of the annular space, but is immersed in the raw water flowing in the tank and eluted into the raw water. I just need. The active soil 22
As a holding material for holding the material, any member having water permeability that can hold active soil may be used. In addition to the mesh material 21 as described above, a plate material having slits may be used.
【0032】活性土壌とは、汚染物質(汚濁物質)を土
壌的な環境の中で凝集高分子化する機能を備えた細菌を
含む土壌乃至土壌様物質を指す。このような土壌物質を
槽中に溶出させることにより、微生物に対する原水内の
環境を変え、原水中にも存在する微生物の活動を誘導し
て土壌中で行われているのと同様の腐食過程を進行させ
る。例えば、ある条件下において好気性細菌は有機物を
摂取し、酸素を利用してエネルギーを得るとともに細胞
成分を合成するが、前記活性土壌はこのような作用を有
するものであってもよい。即ち、この場合には、原水
(廃水)中の有機物は水と炭酸ガスと細胞成分に変わ
る。この場合、活性土壌は、主としてズーグシア、アナ
モロバクター、アルカリゲネス、フラボバクテリウム、
シュードモナス、大腸菌等の細菌や原生動物が固まって
不定形のブロックを形成し、これらの微生物が分泌する
粘性多糖類やゼラチン物質がブロック形成を促し、活性
土壌はその表面に原水のコロイド物質や浮遊物質を吸い
取り、原水の浄化を行う。このように、本例で用いる活
性土壌は、土壌微生物群に本来の土壌的環境を与えて細
菌の固有の活動を活発にさせることを目的としている。
ここでは、土壌中の腐食過程で生じているのと同様な過
程が生成されており、さらに他の雑菌等に対して抗菌作
用もある。The active soil refers to a soil or soil-like substance containing bacteria having a function of coagulating and polymerizing pollutants (pollutants) in a soil-like environment. By dissolving such soil substances into the tank, the environment in the raw water for microorganisms is changed, and the activity of microorganisms that are also present in the raw water is induced to cause the same corrosion process as that performed in soil. Let go. For example, under certain conditions, aerobic bacteria ingest organic matter, use oxygen to obtain energy, and synthesize cell components. The active soil may have such an effect. That is, in this case, the organic matter in the raw water (waste water) is changed into water, carbon dioxide, and cellular components. In this case, the active soil is mainly Zugsia, Anamorobacter, Alcaligenes, Flavobacterium,
Bacteria and protozoa such as Pseudomonas and Escherichia coli solidify to form irregular blocks, and viscous polysaccharides and gelatin substances secreted by these microorganisms promote block formation. Absorb substances and purify raw water. As described above, the active soil used in the present example is intended to provide the soil microorganisms with an original soil environment and activate the inherent activity of bacteria.
Here, a process similar to that occurring in the corrosion process in the soil is generated, and further, has an antibacterial action against other germs and the like.
【0033】本例で用いている活性土壌によれば、次の
ような効果がある。 悪臭の発生がない。 高次処理施設なしで処理水BODが低下する。 イオン性物質の除去が可能である。 雑菌の抑制は土壌菌群の働きで成されるので塩素の添
加等が不要である。 汚泥の土壌還元が可能である。According to the active soil used in this example, the following effects are obtained. There is no odor. The BOD of the treated water decreases without the advanced treatment facility. Removal of ionic substances is possible. Since the control of various bacteria is performed by the action of the soil bacteria group, it is not necessary to add chlorine or the like. Sludge can be reduced to soil.
【0034】図1、図7及び図8に示すように、外槽2
の上部には原水供給手段30が接続連通されている。原
水供給手段30は、前記環状の空間の上部、即ち活性土
壌部20の上方の空間に原水を流入させる。原水供給手
段30は、前記環状の空間の上部に原水を導く原水流入
管31を有している。原水流入管31は外槽2の半径方
向に沿って配置されている。原水流入管31には流入量
調整バルブ32が設けられている。そして、前記環状の
空間の上部において、原水流入管31には方向規制部材
33が連結されている。図7及び図8に示すように、方
向規制部材33は上面と前面が開放された塵取り状の筐
体であり、前記環状の空間の周方向に前面を向けてい
る。方向規制部材33の幅は外槽2と内槽10の間隔よ
りも小さく、原水の表面の流れは阻害されない。よっ
て、前記原水流入管31から供給された原水は、前記環
状の空間内で方向規制部材33に入り、周方向に向けて
送りだされる。なお、図示しないが、前記原水流入管3
1は前記環状の空間の上部に方向規制部材33なしで直
接原水を供給するようになっていてもよい。その場合、
前記原水流入管31の先端を周方向に沿って配置して水
面に斜めに向ければ、この管から出る原水は槽内で周方
向に移動する。即ち、槽内に供給された原水に周方向の
指向性を与えることができる。As shown in FIG. 1, FIG. 7 and FIG.
Raw water supply means 30 is connected and connected to the upper part of. The raw water supply means 30 causes the raw water to flow into the upper part of the annular space, that is, the space above the active soil part 20. The raw water supply means 30 has a raw water inflow pipe 31 for guiding raw water above the annular space. The raw water inflow pipe 31 is arranged along the radial direction of the outer tub 2. The raw water inflow pipe 31 is provided with an inflow amount adjustment valve 32. A direction regulating member 33 is connected to the raw water inflow pipe 31 in the upper part of the annular space. As shown in FIGS. 7 and 8, the direction regulating member 33 is a dust-shaped casing having an open upper surface and a front surface, and the front surface is directed in the circumferential direction of the annular space. The width of the direction regulating member 33 is smaller than the interval between the outer tub 2 and the inner tub 10, and the flow of the raw water on the surface is not hindered. Therefore, the raw water supplied from the raw water inflow pipe 31 enters the direction regulating member 33 in the annular space and is sent out in the circumferential direction. Although not shown, the raw water inflow pipe 3
1 may supply raw water directly to the upper part of the annular space without the direction regulating member 33. In that case,
If the tip of the raw water inflow pipe 31 is arranged along the circumferential direction and is directed obliquely to the water surface, the raw water flowing out of the pipe moves in the circumferential direction in the tank. That is, the directivity in the circumferential direction can be given to the raw water supplied into the tank.
【0035】図1に示すように、前記環状の空間の下
部、即ち前記活性土壌部20の下方の空間には、前記原
水中の汚濁物質が付着する接触部材40が設けられてい
る。また、前記内槽10の内部にも、同一の接触部材4
0が設けられている。接触部材40は流れる原水(汚濁
水)に接触して汚濁水中の浮遊汚泥を付着させる。接触
部材40に付着した浮遊汚泥は、ある程度の量になると
自然剥離して外槽2の底部に堆積し、テーパ面によって
汚泥受け槽6の凹部7内に集まる。本例では、長い帯状
の不織布を用いた。接触部材40は水中の浮遊物が付着
するものであればよく、不織布の他、可撓性板、鉄板、
メッシュ、綿布等、種々の材質・材料が使用できる。ま
た、単一の素材でなく、木炭・活性炭・多孔石等を長尺
の網状袋体に詰めたものを貯留槽内に吊り下げて使用す
ることもできる。As shown in FIG. 1, a contact member 40 to which pollutants in the raw water adhere is provided below the annular space, that is, a space below the active soil portion 20. The same contact member 4 is also provided inside the inner tank 10.
0 is provided. The contact member 40 comes into contact with the flowing raw water (polluted water) to attach floating sludge in the polluted water. When a certain amount of the suspended sludge adheres to the contact member 40, the suspended sludge spontaneously separates and accumulates on the bottom of the outer tank 2, and collects in the recess 7 of the sludge receiving tank 6 by the tapered surface. In this example, a long band-shaped nonwoven fabric was used. The contact member 40 may be anything to which a floating substance in water adheres. In addition to the nonwoven fabric, a flexible plate, an iron plate,
Various materials such as mesh and cotton cloth can be used. Further, instead of a single material, charcoal, activated carbon, porous stone or the like packed in a long net-like bag can be used by suspending it in a storage tank.
【0036】本例の接触部材40は、長い帯状の不織布
である。内槽10の内部にある接触部材40は、図1、
図3、図10に示すように、円筒形の外槽2及び内槽1
0の上部の開口に掛け渡された桁材41からつり下げら
れており、円筒形の槽の軸方向に平行な状態で槽内に吊
り下げられている。桁材41は、2本の主桁42と、主
桁42に連結された多数のつなぎ桁43からなる。図1
0に示すように、内槽10の内部では、接触部材40
は、つなぎ桁43から吊りボルト44で吊り下げられて
いる。内槽10内での接触部材40の配置は、槽の中心
から略放射状でもよいし、縦横一定の間隔で設けてもよ
い。図9に示すように、外槽2と内槽10の間の空間に
ある接触部材40は、外槽2と内槽10の上端から吊り
ボルト44で吊り下げられている。The contact member 40 of this embodiment is a long band-shaped nonwoven fabric. The contact member 40 inside the inner tank 10 is shown in FIG.
As shown in FIGS. 3 and 10, the cylindrical outer tank 2 and the inner tank 1
It is suspended from the girder 41 spanned over the opening at the top of the 0, and is suspended in the tank in a state parallel to the axial direction of the cylindrical tank. The beam 41 includes two main beams 42 and a number of connecting beams 43 connected to the main beam 42. FIG.
As shown in FIG.
Is suspended from the connecting beam 43 by suspension bolts 44. The arrangement of the contact members 40 in the inner tank 10 may be substantially radial from the center of the tank, or may be provided at fixed vertical and horizontal intervals. As shown in FIG. 9, the contact member 40 in the space between the outer tub 2 and the inner tub 10 is suspended from the upper ends of the outer tub 2 and the inner tub 10 by suspension bolts 44.
【0037】図1、図11及び図12に示すように、前
記内槽10の中央には浄化水を槽外に導くための浄化水
導出手段50が設けられている。まず、内槽10の略中
央には、水面に近接して浄化水収納槽51が設けられて
いる。浄化水収納槽51は、閉止された底面と開口した
上面とを有しており、開口した上面が内槽10の水面に
略一致している。このため、内槽10の中央の水面にあ
る浄化水は、浄化水収納槽51内に流れ込む。この浄化
水収納槽51には浄化水導水管52が接続連通されてお
り、浄化水を前記外槽2の外に導出することができる。
浄化水導水管52には制水バルブ53が連結されてい
る。なお、前記吸引管8は浄化水収納槽51の中央を水
密状態で貫通している。As shown in FIGS. 1, 11 and 12, a purified water deriving means 50 for guiding purified water to the outside of the tank is provided at the center of the inner tank 10. First, at substantially the center of the inner tank 10, a purified water storage tank 51 is provided near the water surface. The purified water storage tank 51 has a closed bottom surface and an open top surface, and the open top surface substantially matches the water surface of the inner tank 10. For this reason, the purified water on the central water surface of the inner tank 10 flows into the purified water storage tank 51. A purified water conduit 52 is connected to the purified water storage tank 51 so that purified water can be led out of the outer tank 2.
A water control valve 53 is connected to the purified water conduit 52. The suction pipe 8 penetrates the center of the purified water storage tank 51 in a watertight state.
【0038】外槽2と内槽10の各直径は、両槽の間の
環状の空間における汚濁水の流速が内槽10内における
汚濁水の流速と実質的に等しくなるように設定されてい
る。そのために、外槽2と内槽10の間の環状の空間の
横断面の面積は、内槽10の円形の横断面の面積とほぼ
等しくなっている。The diameters of the outer tank 2 and the inner tank 10 are set so that the flow rate of the contaminated water in the annular space between the two tanks is substantially equal to the flow rate of the contaminated water in the inner tank 10. . Therefore, the cross-sectional area of the annular space between the outer tub 2 and the inner tub 10 is substantially equal to the area of the circular cross-section of the inner tub 10.
【0039】前述したように外槽2と内槽10の間の環
状の空間における汚濁水の流速は、内槽10内における
汚濁水の流速と実質的に等しい。そして、本浄水装置1
内のいずれの位置においても、即ち各槽の壁体に近い部
分でも壁体から離れた部分でも、処理される水の流速は
ほぼ一定に保たれる。従って、槽内に配置された接触部
材40と水との接触状態は槽内のあらゆる位置において
略均一であり、ほぼすべての接触部材40が本来の機能
を発揮して汚濁水中の浮遊汚泥(汚濁物質)を効率的に
付着することができる。As described above, the flow rate of the contaminated water in the annular space between the outer tank 2 and the inner tank 10 is substantially equal to the flow rate of the contaminated water in the inner tank 10. And this water purification device 1
The flow rate of the water to be treated is kept almost constant at any position in the inside, that is, at a portion near or away from the wall of each tank. Therefore, the contact state between the contact member 40 arranged in the tank and the water is substantially uniform at all positions in the tank, and almost all the contact members 40 perform their original functions and the floating sludge (polluted) in the polluted water is discharged. Substance) can be efficiently attached.
【0040】浮遊汚泥(汚濁物質)の付着効果をあげる
ためには、浄化すべき汚濁水の流速と、接触部材40に
接触させる時間を適宜に設定する。接触部材40の種類
や数量等の条件にもよるが、例えば浄化後に達成される
水質を浮遊汚泥の30〜50%が付着・沈降させる程度
とすれば、流速1cm/sec以下、好ましくは0.5
〜1mm/sec程度とし、浄化時間は数時間が適当で
ある。一般に、原水の汚濁度が高いほど、流下距離を長
くする必要がある。浄化容量に比例して設備容量の増大
が必要である。In order to increase the adhesion effect of suspended sludge (pollutant), the flow rate of the polluted water to be purified and the time for contacting the contact member 40 are appropriately set. Although depending on conditions such as the type and number of the contact members 40, if the water quality achieved after purification is such that 30 to 50% of the suspended sludge adheres and settles, the flow rate is 1 cm / sec or less, preferably 0.1 cm / sec or less. 5
Approximately 1 mm / sec, and several hours is appropriate for the purification time. In general, the higher the turbidity of raw water, the longer the flow down distance needs to be. It is necessary to increase the installed capacity in proportion to the purification capacity.
【0041】さらに、本例の浄水装置1によれば、原水
は、外槽2と内槽10の間の環状の空間の上部、即ち活
性土壌部20の上方に入り、円筒の周方向に流れながら
下降していく。そして、活性土壌部20に接触して活性
土壌を水中に溶出させる。そして汚濁水は、環状の空間
の下部に入り周方向に流れながら接触部材に接触して下
降する。さらに原水は内槽に入り、周方向に流れながら
上昇して接触部材に接触する。Further, according to the water purification apparatus 1 of this embodiment, the raw water enters the upper part of the annular space between the outer tank 2 and the inner tank 10, that is, above the active soil part 20, and flows in the circumferential direction of the cylinder. While descending. Then, the active soil is brought into contact with the active soil portion 20 to elute the active soil into water. Then, the contaminated water comes into contact with the contact member and descends while flowing in the lower part of the annular space and flowing in the circumferential direction. Further, the raw water enters the inner tank, rises while flowing in the circumferential direction, and comes into contact with the contact member.
【0042】ここで、原水中には微生物が元々存在して
いるが、溶出した活性土壌が微生物に対する原水内の環
境を変え、原水中に元々存在した微生物の活動を誘導し
て土壌中で行われているのと同様の腐食過程を進行させ
る。即ち、原水中の微生物が分泌する粘性多糖類やゼラ
チン物質は原水のコロイド物質や浮遊物質を吸い取り、
これが接触部材に付着する。このようにして、原水中の
浮遊物質は活性土壌の作用でゲル状になり、さらに槽内
を周方向に流れながら接触部材に付着して原水から分離
される。処理された水は、内槽10の上部に達し、その
中央部において浄化水収納槽51に集められて浄化水導
水管52から外に送りだされる。Here, microorganisms are originally present in the raw water, but the eluted active soil changes the environment of the microorganisms in the raw water, and induces the activity of the microorganisms originally present in the raw water to be carried out in the soil. Proceed with the same corrosion process as has been done. In other words, viscous polysaccharides and gelatin substances secreted by microorganisms in raw water absorb colloidal substances and suspended substances in raw water,
This adheres to the contact member. In this way, the suspended solids in the raw water are gelled by the action of the active soil, and further adhere to the contact members while flowing in the tank in the circumferential direction, and are separated from the raw water. The treated water reaches the upper portion of the inner tank 10, is collected in the purified water storage tank 51 at the center, and is sent out from the purified water conduit 52.
【0043】この間、外槽2、内槽10内のほとんど全
ての位置において、汚濁水はほぼ一定の流速で流れる。
従って、槽内に配置された接触部材40と水との接触状
態はいずれの位置においても均一であり、ほぼすべての
接触部材40が本来の機能を発揮し汚濁水中の浮遊汚泥
(汚濁物質)を効率的に付着させることができる。During this time, the polluted water flows at a substantially constant flow rate at almost all positions in the outer tank 2 and the inner tank 10.
Therefore, the contact state between the contact member 40 disposed in the tank and the water is uniform at any position, and almost all the contact members 40 perform their original functions to remove floating sludge (pollutant) in the polluted water. It can be attached efficiently.
【0044】接触部材40に付着した汚泥がある程度の
量になると、剥離して外槽2の底部のテーパ部分に堆積
する。堆積物はさらに汚泥受け槽6の凹部7に集まる。
前述した従来の横流れ又は縦流れ浄化方式の浄化装置に
おいては、貯留槽の底に堆積した汚泥を除去するために
は、貯留槽内に設置した接触部材40を取り出し、その
後に大きな貯留槽のひろい底面の全体にわたって堆積物
の除去作業を行う必要があった。しかしながら、本発明
によれば、槽内の下半部が汚泥の収納のための空間とし
て空けてあるので、大量の汚泥が堆積しても浄水作業に
は問題がない。堆積した汚泥を取り出すにあたっては、
接触部材40を取り出す必要はない。吸引管8に連結し
たポンプ等の吸引手段を作動させるだけで、槽内に沈殿
した汚泥を吸引管8を通して外に効率的に吸い出すこと
ができる。When a certain amount of sludge adheres to the contact member 40, the sludge peels off and deposits on the tapered portion at the bottom of the outer tank 2. The sediment further collects in the recess 7 of the sludge receiving tank 6.
In the above-mentioned conventional purification device of the horizontal flow or vertical flow purification method, in order to remove sludge deposited on the bottom of the storage tank, the contact member 40 installed in the storage tank is taken out, and then the large storage tank is spread. It was necessary to remove the deposits over the entire bottom surface. However, according to the present invention, since the lower half in the tank is open as a space for storing sludge, there is no problem in water purification work even if a large amount of sludge is accumulated. When removing the accumulated sludge,
It is not necessary to take out the contact member 40. Only by operating a suction means such as a pump connected to the suction pipe 8, the sludge settled in the tank can be efficiently sucked out through the suction pipe 8.
【0045】本発明において、接触部材40を交換する
場合には、クレーン等によって桁材41を持ち上げて吊
り下げられた接触部材40を槽から抜き出す。又は、桁
材41はそのままとし、各接触部材40を桁材41から
外して槽から抜き出す。In the present invention, when replacing the contact member 40, the girder member 41 is lifted by a crane or the like, and the suspended contact member 40 is extracted from the tank. Alternatively, the beam members 41 are left as they are, and the respective contact members 40 are removed from the beam members 41 and extracted from the tank.
【0046】以上説明した浄水装置を2基以上連結して
さらに高度処理する浄水設備としてもよい。即ち、複数
の浄水装置を、第1の浄水装置から第2の浄水装置へと
順次低い位置に設置し、第1の浄水装置の浄化水導水管
を第2の浄水装置の原水流入管に接続し、以下同様に前
の浄水装置の浄化水導水管を後の浄水装置の原水流入管
に接続する。このようにすれば大量の原水を高度処理で
き、又は浄水効果を高めることができる。[0046] Two or more water purification devices described above may be connected to provide a water purification facility for further advanced treatment. That is, a plurality of water purifiers are sequentially installed at lower positions from the first water purifier to the second water purifier, and the purified water conduit of the first water purifier is connected to the raw water inflow pipe of the second water purifier. Then, similarly, the purified water conduit of the preceding water purification device is connected to the raw water inflow pipe of the later water purification device. In this way, a large amount of raw water can be highly treated, or the water purification effect can be enhanced.
【0047】本例では外槽と内槽は円筒形であったが槽
の形状は問わない。要するに、外槽と、外槽の内部に設
けられて外槽と底部で連通している内槽があればよく、
その形状は例えば多角筒状でもよい。また、本例では槽
内において原水が周方向へ運動したが、必ずしも周方向
の運動が必須ではない。要するに、槽内において原水が
外槽から内槽へと順次移動していけばよく、その移動の
方向が周方向でなく上下方向であっても同様の効果が得
られる。上下方向の移動の場合でも、その流速の好まし
い値は、周方向の流速の場合と略同様である。In this embodiment, the outer tank and the inner tank are cylindrical, but the shape of the tank is not limited. In short, it is sufficient if there is an outer tank and an inner tank provided inside the outer tank and communicating with the outer tank at the bottom,
The shape may be, for example, a polygonal cylindrical shape. Further, in this example, the raw water has moved in the circumferential direction in the tank, but the circumferential movement is not always essential. In short, it is sufficient that the raw water moves sequentially from the outer tank to the inner tank in the tank, and the same effect can be obtained even if the direction of the movement is not the circumferential direction but the vertical direction. In the case of vertical movement, the preferable value of the flow velocity is substantially the same as that in the case of the circumferential flow velocity.
【0048】以上説明したように、本発明の浄水装置に
よれば、次のような効果が得られる。 (1) 活性土壌と接触部材の組み合わせによって汚濁水を
効率的に処理することができる。 (2) 処理すべき汚濁水が接触部材に接触している時間に
むらがないので、浮遊汚泥を効率よく除去することがで
きる。 (3) 地下埋設が可能である。 (4) 汚泥は槽のテーパー形状の底に堆積するので、これ
をバキューム等で槽外に直接取り出すことができ、汚泥
の除去が容易である。As described above, according to the water purification apparatus of the present invention, the following effects can be obtained. (1) Polluted water can be treated efficiently by a combination of active soil and contact members. (2) Since the time during which the polluted water to be treated is in contact with the contact member is not uneven, the suspended sludge can be efficiently removed. (3) Underground burial is possible. (4) Sludge accumulates on the tapered bottom of the tank, so that it can be taken out of the tank directly by vacuum or the like, and the sludge can be easily removed.
【0049】[0049]
【発明の効果】本発明によれば、筒形の内槽と外槽の間
に活性土壌部を設け、さらに活性土壌部の下方と内槽の
内部に接触部材を設け、活性土壌部の上方に導入した汚
濁水を旋回させながら移動させることによって活性土壌
と接触部材で効率的な処理を行うことができる。即ち、
円筒形の槽内において汚濁水を均一な流速で周方向に移
動させ、活性土壌で汚濁水を処理した後、さらに槽内の
接触部材に均一に接触させて汚泥(汚濁物質)を効率的
に付着・除去することができる。しかも、槽の底部に汚
泥受け槽を設けて堆積物を集めやすくし、そこに吸引管
を既設して容易に堆積物を吸引除去出きるようにしてあ
る。従って、本発明によれば、設置面積が小さく構造が
簡単でありながら浄化性能とメンテナンス性に優れた浄
水装置及び浄水設備を実現できるという効果がある。さ
らに、本例の浄水装置は運転にほとんど動力を必要とせ
ず経済的であるという実用上優れた効果も有している。According to the present invention, an active soil portion is provided between a cylindrical inner tank and an outer tank, and a contact member is provided below the active soil portion and inside the inner tank, and the contact member is provided above the active soil portion. By moving the polluted water introduced into the container while swirling, efficient treatment can be performed with the active soil and the contact member. That is,
After moving the contaminated water in the cylindrical tank at a uniform flow rate in the circumferential direction and treating the contaminated water with the activated soil, the sludge (contaminated material) is efficiently contacted with the contact members in the tank evenly. Can be attached and removed. In addition, a sludge receiving tank is provided at the bottom of the tank to facilitate the collection of the sediment, and a suction pipe is provided therein so that the sediment can be easily removed by suction. Therefore, according to the present invention, there is an effect that it is possible to realize a water purification device and a water purification facility which are small in installation area and simple in structure, and excellent in purification performance and maintainability. Further, the water purification apparatus of this embodiment has an excellent practical effect that it requires little power for operation and is economical.
【図1】本発明の浄水装置の断面図である。FIG. 1 is a sectional view of a water purification device of the present invention.
【図2】図1のA−A切断線における断面図である。FIG. 2 is a sectional view taken along line AA of FIG. 1;
【図3】図1のB−B切断線における断面図である。FIG. 3 is a cross-sectional view taken along the line BB of FIG. 1;
【図4】図1の矢視Cにおける拡大図である。FIG. 4 is an enlarged view as viewed from an arrow C in FIG. 1;
【図5】本発明の浄水装置における内槽の他の形態例を
示す斜視図である。FIG. 5 is a perspective view showing another embodiment of the inner tank in the water purification device of the present invention.
【図6】本発明の浄水装置における活性土壌部のメッシ
ュ材を示す平面図である。FIG. 6 is a plan view showing a mesh material of an active soil portion in the water purification device of the present invention.
【図7】本発明の浄水装置における原水供給手段を示す
斜視図である。FIG. 7 is a perspective view showing raw water supply means in the water purification device of the present invention.
【図8】本発明の浄水装置における原水供給手段と水面
との位置関係を示す断面図である。FIG. 8 is a sectional view showing a positional relationship between raw water supply means and a water surface in the water purification device of the present invention.
【図9】本発明の浄水装置における接触部材とその吊り
構造を示す図である。FIG. 9 is a diagram showing a contact member and a suspension structure of the contact member in the water purification device of the present invention.
【図10】本発明の浄水装置における接触部材とその吊
り構造を示す図である。FIG. 10 is a diagram showing a contact member and a suspension structure thereof in the water purification device of the present invention.
【図11】本発明の浄水装置における浄化水導出手段の
平面図である。FIG. 11 is a plan view of purified water deriving means in the water purification device of the present invention.
【図12】本発明の浄水装置における浄化水導出手段の
断面図である。FIG. 12 is a sectional view of purified water deriving means in the water purification device of the present invention.
【図13】従来の浄水装置である横流れ浄化方式の浄化
装置を示す平面図及び側断面図である。FIG. 13 is a plan view and a side cross-sectional view showing a purification device of a lateral flow purification type which is a conventional water purification device.
【図14】従来の浄水装置である縦流れ浄化方式の浄化
装置を示す平面図及び側断面図である。FIG. 14 is a plan view and a sectional side view showing a purification device of a vertical flow purification type which is a conventional water purification device.
1 浄水装置 2 外槽 6 汚泥受け槽 8 吸引管 10 内槽 11 内槽支持基礎 13 保持材 20 活性土壌部 21 通水性の保持材としてのメッシュ材 22 活性土壌 30 原水供給手段 31 原水流入管 33 方向規制部材 40 接触部材 41 桁材 50 浄化水導出手段 51 浄化水収納槽 52 浄化水導水管 DESCRIPTION OF SYMBOLS 1 Water purification apparatus 2 Outer tank 6 Sludge receiving tank 8 Suction tube 10 Inner tank 11 Inner tank support base 13 Retaining material 20 Active soil part 21 Mesh material as a retaining material for water permeability 22 Active soil 30 Raw water supply means 31 Raw water inflow pipe 33 Direction regulating member 40 Contact member 41 Beam member 50 Purified water deriving means 51 Purified water storage tank 52 Purified water conduit
フロントページの続き (73)特許権者 000231110 日本鋼管ライトスチール株式会社 埼玉県熊谷市大字三ケ尻6100番地 (73)特許権者 596143277 ユニオンヒューム管株式会社 東京都台東区雷門2丁目3番12号 (72)発明者 芦野 勝邦 神奈川県茅ヶ崎市高田3−1−2 (72)発明者 澁谷 宏 神奈川県横浜市保土ヶ谷区上菅田町144 −71 (72)発明者 森 雅人 山形県新庄市小田島町7−36 (72)発明者 瀬谷 藤夫 福島県いわき市泉丘1−21−20 (72)発明者 江尻 洋 埼玉県熊谷市拾六間788−26 (72)発明者 恩田 實 埼玉県熊谷市新堀641−208 (56)参考文献 特開 平8−132084(JP,A) 特公 昭58−57239(JP,B2) 特公 昭60−26599(JP,B2) (58)調査した分野(Int.Cl.6,DB名) C02F 3/00 - 3/34 Continued on the front page (73) Patentee 000231110 Nippon Kokan Light Steel Co., Ltd. 6100, Sankeijiri, Kumagaya-shi, Saitama (73) Patentee 596143277 Union Hume Tube Co., Ltd. 2-3-12 Kaminarimon, Taito-ku, Tokyo (72 ) Inventor Katsukuni Ashino 3-1-2 Takada, Chigasaki-shi, Kanagawa Prefecture (72) Inventor Hiroshi Shibuya 144-71, Kasugada-cho, Hodogaya-ku, Yokohama-shi, Kanagawa-ken (72) Inventor Masato Mori 7- Odajimacho, Shinjo-shi, Yamagata Prefecture 36 (72) Inventor Fujio Seya 1-21-20 Izumigaoka, Iwaki-shi, Fukushima Prefecture (72) Inventor Hiroshi Ejiri 788-26, Jurokuma, Kumagaya-shi, Saitama Prefecture (72) Inventor Minoru Onda 641- Niibori, Kumagaya-shi, Saitama Prefecture 208 (56) References JP-A-8-13284 (JP, A) JP-B-58-57239 (JP, B2) JP-B-60-26599 (JP, B2) (58) Fields investigated (Int. 6 , DB name) C02F 3/00-3/34
Claims (13)
うに前記外槽の内部に設けられた内槽と、 前記外槽と前記内槽の間の環状の空間を上部と下部に分
割するように該空間内に設けられた活性土壌部と、 前記外槽に接続され、前記環状の空間の前記上部に原水
を流入させる原水供給手段と、 前記環状の空間の前記下部と前記内槽の内部に設けられ
て前記原水中の汚濁物質が付着する接触部材と、 前記内槽の水面の近傍に設けられて浄化水を外に導く浄
化水導出手段とを有する浄水装置。A cylindrical outer tank having a closed bottom; an inner tank provided inside the outer tank such that an open bottom is located above a bottom of the outer tank; An active soil portion provided in the space so as to divide the annular space between the inner tank and the inner tank into an upper part and a lower part, and connected to the outer tank to allow raw water to flow into the upper part of the annular space. A raw water supply means, a contact member provided inside the lower part of the annular space and the inner tank and to which pollutants in the raw water adhere, and provided near the water surface of the inner tank to remove purified water. Water purification device having purified water deriving means for guiding water.
部と下部に分割するように該空間内に設けられた通水性
の保持材と、前記保持材に保持された活性土壌を有して
いる請求項1記載の浄水装置。2. The active soil portion includes a water-permeable holding material provided in the space so as to divide the annular space into an upper portion and a lower portion, and active soil held by the holding material. The water purification device according to claim 1, wherein
上部に原水を導く原水流入管と、前記原水流入管から供
給された原水を前記環状の空間内において周方向に向か
わせる方向規制部材とを有している請求項1記載の浄水
装置。3. A raw water supply pipe for guiding raw water to an upper portion of the annular space, and a direction regulating member for directing raw water supplied from the raw water inflow pipe in the circumferential direction in the annular space. The water purification device according to claim 1, comprising:
と開口した上面とを有し、内槽の略中央に設けられて浄
化水を受け入れる筒形の浄化水収納槽と、前記浄化水収
納槽に連通して前記外槽の外に導出される浄化水導水管
とを有する請求項1記載の浄水装置。4. A purified water storage tank having a closed bottom surface and an open upper surface, provided substantially at the center of an inner tank, for receiving purified water, and said purified water storage tank. The water purification device according to claim 1, further comprising a purified water conduit connected to a storage tank and led out of the outer tank.
を受ける汚泥受け槽が設けられ、前記汚泥受け槽に沈殿
した汚泥を前記外槽及び前記内槽の外に吸い上げるため
の吸引管が設けられた請求項1記載の浄水装置。5. A sludge receiving tank for receiving the settled sludge substantially at the center of the bottom of the outer tank, and a suction pipe for sucking the sludge settled in the sludge receiving tank out of the outer tank and the inner tank. The water purification device according to claim 1, further comprising:
くともいずれか一方が、テーパ状に形成されている請求
項5記載の浄水装置。6. The water purification apparatus according to claim 5, wherein at least one of the sludge receiving tank and the bottom of the outer tank is formed in a tapered shape.
あり、両槽は実質的に同心状に配置されていることを特
徴とする請求項1記載の浄水装置。7. The water purification apparatus according to claim 1, wherein said outer tank and said inner tank are substantially cylindrical, and both tanks are arranged substantially concentrically.
設置し、前記内槽を前記内槽支持基礎上に設置した請求
項1記載の浄水装置。8. The water purification apparatus according to claim 1, wherein a plurality of inner tank support bases are installed at the bottom of the outer tank, and the inner tank is installed on the inner tank support base.
積と、水平面内における前記内槽の断面積の比が、ほぼ
1:1である請求項1記載の浄水装置。9. The water purifier according to claim 1, wherein a ratio of a cross-sectional area of the annular space in a horizontal plane to a cross-sectional area of the inner tank in a horizontal plane is approximately 1: 1.
前記内槽の内部における水の流速が実質的に等しい請求
項1記載の浄水装置。10. The flow rate of water in the annular space,
The water purifier according to claim 1, wherein the flow rates of the water inside the inner tank are substantially equal.
ており、前記内槽は円筒形に保持した可撓性材料からな
る請求項1記載の浄水装置。11. The water purifier according to claim 1, wherein the outer tub has rigidity enough to withstand water pressure, and the inner tub is made of a flexible material held in a cylindrical shape.
保持材によって保持されており、前記保持材は前記外槽
の上部に掛け渡した桁材から吊り下げられている請求項
11記載の浄水装置。12. The flexible material according to claim 11, wherein an upper end and a lower end of the flexible material are held by an annular holding member, and the holding member is hung from a girder material bridged over an upper portion of the outer tub. Water purification equipment.
前記下部に移動する間、前記原水中に溶出した活性土壌
の微生物が前記原水内において粘性物質を生成して前記
原水中の汚濁物質を吸着する作用が促進されるととも
に、 前記原水が前記内槽の下部から前記内槽の内部に入り、
前記内槽の内部の上方へと移動する間に、前記粘性物質
に吸着された前記汚濁物質が前記接触部材に付着するこ
とを特徴とする請求項2記載の浄水装置。13. While the raw water moves from the upper part of the annular space to the lower part, microorganisms of active soil eluted in the raw water generate viscous substances in the raw water to remove pollutants in the raw water. While the action of adsorbing is promoted, the raw water enters the inner tank from the lower part of the inner tank,
The water purification apparatus according to claim 2, wherein the polluted substance adsorbed by the viscous substance adheres to the contact member while moving upward inside the inner tank.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP10293840A JP2958316B1 (en) | 1998-10-15 | 1998-10-15 | Water purification equipment |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
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JP10293840A JP2958316B1 (en) | 1998-10-15 | 1998-10-15 | Water purification equipment |
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Publication Number | Publication Date |
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JP2958316B1 true JP2958316B1 (en) | 1999-10-06 |
JP2000117277A JP2000117277A (en) | 2000-04-25 |
Family
ID=17799844
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Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP10293840A Expired - Fee Related JP2958316B1 (en) | 1998-10-15 | 1998-10-15 | Water purification equipment |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2958316B1 (en) |
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1998
- 1998-10-15 JP JP10293840A patent/JP2958316B1/en not_active Expired - Fee Related
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Publication number | Publication date |
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JP2000117277A (en) | 2000-04-25 |
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