JPH09206788A - Water quality purification method and water quality purification apparatus used for the same - Google Patents
Water quality purification method and water quality purification apparatus used for the sameInfo
- Publication number
- JPH09206788A JPH09206788A JP4050896A JP4050896A JPH09206788A JP H09206788 A JPH09206788 A JP H09206788A JP 4050896 A JP4050896 A JP 4050896A JP 4050896 A JP4050896 A JP 4050896A JP H09206788 A JPH09206788 A JP H09206788A
- Authority
- JP
- Japan
- Prior art keywords
- water
- vegetation
- bed
- filter bed
- raw water
- 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.)
- Granted
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)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
- Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)
- Physical Water Treatments (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】この発明は、湾、池、湖沼、ダム
などの比較的水流の少ない水域の水質の浄化方法とこれ
に用いる装置に関し、より詳しくは、水域の曝気と、曝
気によって凝集フロックに気泡を吸着浮上させて、浮上
した凝集フロックを、水性植物と濾床とを利用して分解
させることによって、水質の浄化とその再汚濁を防止す
る方法と、この方法に使用するための装置に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for purifying water in a water area having a relatively small water flow such as a bay, a pond, a lake, a dam, and an apparatus used therefor, and more specifically, to aeration of the water area and aggregation by aeration. A method for adsorbing and floating air bubbles on flocs and decomposing the flocculated flocs by utilizing an aqueous plant and a filter bed to prevent purification of water quality and its recontamination, and a method for use in this method. Regarding the device.
【0002】[0002]
【従来の技術】近年、地球規模で環境問題が取り上げら
れるうち、水質汚濁の問題は早急に解決しなければなら
ない重要な課題である。とくに閉鎖性水域に於ける水質
の悪化に対しては、我々の生活に密接に関係しているた
め、その改善を最優先で図る必要がある。2. Description of the Related Art While environmental problems have been taken up on a global scale in recent years, the problem of water pollution is an important issue that must be solved immediately. In particular, regarding the deterioration of water quality in closed water areas, it is necessary to improve it because it is closely related to our lives.
【0003】水域の水質浄化の方法として、下水道の整
備が最も有効であるが、下水道の普及が困難な地区で
は、水域を直接浄化する直接浄化方法が行われている。
そのうち最近開発された加圧浮上分離方式が、水域の窒
素、リン系の有機物処理に用いられている。The most effective method for purifying the water quality in the water area is to improve the sewerage system. However, in areas where the sewerage system is difficult to spread, a direct water purification method is used to directly purify the water area.
Among them, the recently developed pressure floating separation method is used for treating nitrogen and phosphorus organic matter in water bodies.
【0004】この加圧浮上分離方法は、主に下水道や工
場排水等の高度処理に用いられるが、これを水域の直接
浄化に用いる場合、微細気泡によって浮上させられたフ
ロックの回収処分方法が問題となる。浮上フロックの回
収は、人力か回収装置で行われるが、いずれも回収した
汚物の処理が必要となるため、メインテナンスに要する
コストがかかり、その対策に苦慮している。This pressure floating separation method is mainly used for advanced treatment of sewers, factory wastewater, etc., but when it is used for direct purification of water bodies, a method of collecting and disposing flocs floated by fine bubbles is a problem. Becomes Floating flocs are collected manually or by a collecting device, but in both cases, it is necessary to dispose of the collected filth, which requires maintenance costs, and we are struggling to take measures against it.
【0005】大型システムを用いて短期間に加圧浮上分
離方式による直接浄化を行った場合、一時的には浄化す
るものの時間の経過により再汚濁化が進むため、その防
止策としてコンパクトなシステムを用いて常時連続的に
行った場合でも、浮上フロック回収処分方法に問題がい
ぜん残ってしまう。When direct purification is carried out by a pressurized flotation separation method using a large system for a short period of time, although it is temporarily purified, recontamination progresses over time, so a compact system should be used as a preventive measure. Even if it is carried out continuously at all times, there are still problems with the method for collecting and disposing of floc flocs.
【0006】直接浄化方法の一つに曝気方式がある。こ
の方式は、活性汚泥法にみられる曝気によって生物フロ
ックを水中に浮遊させながら、有機物を酸化分解するも
のである。生物処理は高度処理の一つで、専ら好気的に
行われ、窒素、アンモニア、藻類、臭気、鉄、マンガン
等を除去するなど、汚濁原水の浄化に極めて有効な手段
である。しかし、一般に曝気に使用される気泡は直径1
〜数mmの大きさのため、曝気処理効率が悪く、浄化に
時間がかかるといった問題がある。An aeration method is one of the direct purification methods. This method is to oxidize and decompose organic matter while suspending biological flocs in water by aeration as seen in the activated sludge method. Biological treatment is one of the advanced treatments and is carried out exclusively aerobically, and is a very effective means for purifying polluted raw water by removing nitrogen, ammonia, algae, odor, iron, manganese, and the like. However, bubbles used for aeration generally have a diameter of 1
Since the size is up to several mm, there is a problem that aeration treatment efficiency is poor and purification takes time.
【0007】さらに直接浄化方法の一つの植生浄化方式
は、水域内の窒素、リンの吸収のため、育成、除去の簡
単なホテイアオイ、イグサ、ヨシ等の植物を利用し、こ
れを水面に浮かべることにより栄養塩類を摂取させて、
繁殖するアオコ等の藻類(植物性プランクトン)の成育
を抑制するものである。植生浄化は、ホテイアオイ等の
植物と汚濁水との接触を水域内の水の自然循環に頼って
おり、表面上の水質改善しか行われないため部分的な処
理におわり、水域全体の均一な浄化に問題がある。Further, one of the direct purification methods is a vegetation purification method, in which plants such as water hyacinth, rush, reed and the like which are easy to grow and remove are floated on the water surface in order to absorb nitrogen and phosphorus in the water area. To ingest nutrients,
It suppresses the growth of algae (phytoplankton) such as blue-green algae that breed. Vegetation purification relies on the natural circulation of water in the water area to contact plants such as water hyacinth and polluted water, and only the water quality on the surface is improved, resulting in partial treatment and uniform purification of the entire water area. I have a problem.
【0008】本出願人は、これら従来の水質浄化方法及
び水質浄化装置の欠点を解消するものとして、先に「水
質浄化方法とこれに用いる装置」の名称で特許出願をし
た(特願平7−46185)。この方法は、「汚濁した
原水に凝集剤と気泡とを放出し、原水と凝集剤とにより
生じた凝集フロックに、気泡を吸着させて水面まで浮上
させ、浮上した凝集フロックを水性植物により分解させ
る」ものである。The present applicant has previously filed a patent application under the name of "water purification method and apparatus used therefor" as a solution to the above drawbacks of the conventional water purification method and water purification apparatus (Japanese Patent Application No. 7-83242). -46185). This method "releases a flocculant and bubbles to polluted raw water, causes the flocs generated by the raw water and the flocculating agent to adsorb the bubbles and float to the water surface, and the flocculated flocs are decomposed by an aqueous plant." It is something.
【0009】また装置は、「汚濁した原水を吸引するポ
ンプと、吸引された原水に凝集剤を添加する凝集剤タン
クと、ポンプへ接続されて原水へ空気を混合するエゼク
タと、エゼクタに接続された加圧タンクとからなって、
水面に浮上して移動可能な気泡発生装置の周囲には、移
動可能なフェンスを設けるとともに、フェンスの中心下
の水中に加圧タンクに接続された気泡発生ノズルを設け
て、気泡発生装置とフェンスとの間に、浮上した凝集フ
ロックを分解させる水性植物を設けた」ものである。The apparatus also includes a pump for sucking polluted raw water, a coagulant tank for adding a coagulant to the sucked raw water, an ejector connected to the pump for mixing air into the raw water, and an ejector connected to the ejector. Consisting of a pressurized tank,
A movable fence is installed around the bubble generator that floats on the surface of the water and is movable, and a bubble generating nozzle connected to a pressure tank is provided in the water under the center of the fence so that the bubble generator and fence Between them and an aquatic plant that decomposes flocculated flocs that have surfaced. "
【0010】これにより、凝集フロックの回収の手間を
要せず、効率的かつ連続的に水質浄化を行うことができ
るうえ、再汚濁を防止することが可能になった。しかし
ながら、浮上した凝集フロックの分解を水性植物だけに
頼るのには限度があり、さらなる効率化が要求された。As a result, it is possible to efficiently and continuously purify the water quality without the trouble of collecting the floc, and to prevent recontamination. However, there is a limit to relying only on the aquatic plants for the decomposition of the flocculated flocs, and further efficiency is required.
【0011】[0011]
【発明が解決しようとする課題】この発明が解決しよう
とする課題は、水域全体の均一で早急な水質浄化を、フ
ロックの回収廃棄処理を必要としないで、さらに効率
的、かつ連続的に行うことにある。SUMMARY OF THE INVENTION The problem to be solved by the present invention is to carry out uniform and quick water purification of the entire water area more efficiently and continuously without the need to collect and dispose of flocs. Especially.
【0012】[0012]
【課題を解決するための手段】この発明の水質浄化方法
は、汚濁した原水に凝集剤と気泡とを放出し、原水と凝
集剤とにより生じた凝集フロックに気泡を吸着させて浮
上させて、水性植物と、礫又は/及び木炭からなる濾床
とに注ぎ、凝集フロックを水性植物と濾床とで分解させ
ることに特徴がある。The water purification method of the present invention releases a flocculant and bubbles to polluted raw water, and causes the flocs generated by the raw water and the flocculant to adsorb the bubbles and float them. It is characterized in that it is poured into an aqueous plant and a filter bed made of gravel and / or charcoal to decompose agglomerated flocs between the aqueous plant and the filter bed.
【0013】即ち、直接浄化方法の曝気方式と植生浄化
及び濾床方式とを効果的に組み合わせたもので、凝集フ
ロックの回収の手間を必要とせず、又再汚濁を防止でき
るものである。That is, it is an effective combination of the aeration method of the direct purification method and the vegetation purification and filter bed method, which does not require the trouble of collecting the floc of flocs and can prevent recontamination.
【0014】又、この方法に用いる装置の特徴は以下の
点にある。即ち、汚濁した原水を吸引するポンプと、吸
引された原水に凝集剤を添加する凝集剤タンクと、ポン
プへ接続されて原水へ空気を混合するエゼクタと、エゼ
クタに接続された加圧タンクとからなり、水面に浮上し
て移動可能な気泡発生装置の下方の水中に加圧タンクに
接続された気泡発生ノズルを設ける。The features of the apparatus used in this method are as follows. That is, from a pump that sucks polluted raw water, a coagulant tank that adds a coagulant to the sucked raw water, an ejector that is connected to the pump to mix air into the raw water, and a pressure tank that is connected to the ejector. Therefore, a bubble generating nozzle connected to a pressure tank is provided in the water below the bubble generating device that can float and move to the water surface.
【0015】そして、気泡発生装置の周囲に、水性植物
を植られて浮上する吸水性、通気性のある植生床と、植
生床の上に礫又は/及び木炭からなる濾床とを配設する
とともに、原水と凝集剤とにより生じた凝集フロックに
付着して浮上する気泡を気泡発生装置へ向かって斜上さ
せて、気泡発生装置と、植生床と濾床との間を通って濾
床に注がせる誘導部材を設ける。Around the air bubble generator, a water-absorbing and air-permeable vegetation bed in which an aqueous plant is planted and floated, and a filter bed made of gravel and / or charcoal are arranged on the vegetation bed. At the same time, the bubbles that adhere to the floc generated by the raw water and the flocculant and float up are inclined toward the bubble generator, and pass through the bubble generator, the vegetation bed and the filter bed to the filter bed. Provide a guiding member for pouring.
【0016】この発明の別の水質浄化装置は、前記気泡
発生装置の下方の水中に加圧タンクに接続された気泡発
生ノズルを設け、気泡発生装置の周囲に配設したフロ−
トの上に、排水マット、水性植物を植えた植生床、礫又
は/及び木炭からなる濾床を順次積み重ねるとともに、
フロ−トは、原水と凝集剤とにより生じた凝集フロック
に付着して浮上する気泡を気泡発生装置へ向かって斜上
させて、気泡発生装置と、フロ−ト、排水層、植生床、
濾床との間を通って濾床に注がせる誘導面を設けたこと
に特徴がある。In another water quality purifying apparatus of the present invention, a bubble generating nozzle connected to a pressure tank is provided in water below the bubble generating apparatus, and the flow generating apparatus is provided around the bubble generating apparatus.
A drainage mat, a vegetation bed planted with an aqueous plant, a filter bed made of gravel or / and charcoal are sequentially stacked on top of
The float is a bubble generating device, a float, a drainage layer, a vegetation floor, which causes bubbles that adhere to floc generated by the raw water and the flocculant and float up toward the bubble generating device.
It is characterized in that it has a guide surface through which it can be poured into the filter bed.
【0017】[0017]
【発明の実施の形態】まず図3により気泡発生装置1に
ついて説明する。気泡発生装置1は、浮き台2の上に設
けられた凝集剤タンク3、ポンプ4、エゼクタ5、加圧
タンク6からなる。7はポンプ4に接続された吸引ホ−
スで、先端にはストレ−ナ8が取付けられている。9は
加圧タンク6に接続された排出ホ−スで、先端には気泡
発生ノズル10が取付けられている。なお、11a、1
1bはバルブである。気泡発生装置1は浮き台2により
移動自在である。又、気泡発生ノズル10は、後述する
気泡発生装置1の中心下方の水中に設置される。BEST MODE FOR CARRYING OUT THE INVENTION First, a bubble generator 1 will be described with reference to FIG. The bubble generation device 1 includes a flocculant tank 3, a pump 4, an ejector 5, and a pressure tank 6 provided on the floating table 2. 7 is a suction hose connected to the pump 4.
A strainer 8 is attached to the tip of the strainer. A discharge hose 9 is connected to the pressure tank 6, and a bubble generating nozzle 10 is attached to the tip thereof. Note that 11a, 1
1b is a valve. The bubble generator 1 is movable by a floating table 2. Further, the bubble generating nozzle 10 is installed in the water below the center of the bubble generating device 1 described later.
【0018】汚濁した原水Wは、ストレ−ナ8、吸引ホ
−ス7を通って、凝集剤とともにポンプ4へ吸い込ま
れ、空気を吸い込むエゼクタ5で気液混合液となって加
圧タンク6へ送り込まれる。加圧タンク6で加圧された
気液混合液は、気体溶解液となって加圧タンク6から送
り出され、排出ホ−ス9により気泡発生ノズル10へ供
給される。気泡発生ノズル10からは、気体溶解液から
溶解した気体、即ち空気が気泡となって連続的に排出さ
れる。The polluted raw water W passes through the strainer 8 and the suction hose 7 and is sucked into the pump 4 together with the coagulant, and becomes a gas-liquid mixed liquid by the ejector 5 which sucks air to the pressure tank 6. Sent in. The gas-liquid mixed liquid pressurized in the pressure tank 6 becomes a gas solution, is sent out from the pressure tank 6, and is supplied to the bubble generation nozzle 10 by the discharge hose 9. From the bubble generation nozzle 10, the gas dissolved from the gas solution, that is, air, is continuously discharged as bubbles.
【0019】気泡発生ノズル10として公知のものを使
用できるが、この発明では、先に本出願人が開発し、既
に特許出願をした「微細気泡排出装置」(特願平6−2
98923)を用いている。この装置は、曝気に極めて
効果的な数10ミクロン以下の微細気泡を連続的に発生
できるものである。Although a known bubble generating nozzle 10 can be used, in the present invention, the "fine bubble discharging device" previously developed by the present applicant and already applied for a patent (Japanese Patent Application No. 6-2).
98923) is used. This device is capable of continuously generating extremely small bubbles of several tens of microns or less, which is extremely effective for aeration.
【0020】この装置を図4により概説する。12は排
出ホ−ス9を着脱する接続筒、13は外筒接続筒、14
は内筒で接続筒12に取付けられている。15は蓋で、
内筒14の先端部を閉塞する。This device is outlined by FIG. Reference numeral 12 is a connection tube for attaching and detaching the discharge hose 9, 13 is an outer tube connection tube, 14
Is attached to the connecting cylinder 12 by an inner cylinder. 15 is a lid,
The tip of the inner cylinder 14 is closed.
【0021】16は内筒14に貫設された噴出孔群で、
内径2〜4mm、実施例では3mmの微細小径である。
17はビスで、適宜選択された噴出孔16に螺着され
て、状況に応じて、噴出孔16の数を調整できるように
なってる。Reference numeral 16 denotes a group of ejection holes penetrating the inner cylinder 14,
The inner diameter is 2 to 4 mm, and in the embodiment, the diameter is 3 mm.
Reference numeral 17 denotes a screw, which is screwed into an appropriately selected ejection hole 16 so that the number of ejection holes 16 can be adjusted according to the situation.
【0022】18は外筒であって、外筒接続筒13に取
付けられ、内筒14を内包して前部(排出ホ−ス9と反
対側)は内筒14の先方へ延出するとともに、先端部は
開放されている。Reference numeral 18 denotes an outer cylinder, which is attached to the outer cylinder connecting cylinder 13 and encloses the inner cylinder 14 so that the front portion (the side opposite to the discharge hose 9) extends beyond the inner cylinder 14. , The tip is open.
【0023】そこで、排出ホ−ス9から凝集剤とともに
内筒14へ供給された気体溶解液は、微細な噴出孔16
群からの噴出と、外筒18により噴出孔16からの噴出
直後の流速が抑えられることによって、一気に圧力を開
放しながら排出される。その結果、気体溶解液に溶解し
た気体、即ち空気は多数の微細気泡となって浮上するこ
とになる。Therefore, the gas-dissolved liquid supplied from the discharge hose 9 to the inner cylinder 14 together with the coagulant is a fine ejection hole 16
The jetting from the group and the flow velocity immediately after the jetting from the jetting hole 16 are suppressed by the outer cylinder 18, so that the pressure is released at a stroke. As a result, the gas dissolved in the gas solution, that is, air, becomes a large number of fine bubbles and floats.
【0024】気泡発生ノズル10の設置位置は、水底か
らやや高い位置とするとよい。又、エゼクタ5からの空
気の供給量が少ない場合には、必要に応じて図示しない
コンプレッサをエゼクタ5へ接続する。The bubble generating nozzle 10 may be installed at a position slightly higher than the bottom of the water. If the amount of air supplied from the ejector 5 is small, a compressor (not shown) is connected to the ejector 5 as needed.
【0025】次に、水質浄化装置を図1により概説す
る。19は植生床、20は植生床19の上に形成される
濾床で、気泡発生装置1の周囲に設けられている。この
発明では、植生浄化法に水性植物APとしてヨシ、ガマ
等の抽水植物を利用する。植生床19としては吸水性、
通気性に優れたかつ浮力のあるスポンジブロック、例え
ばセルロ−ススポンジブロックを採用し、水性植物AP
の種を植えて、成育させる。濾床20は、径5〜10c
mの礫、又は木炭を採用する。なお、礫と木炭とを混ぜ
合わせて形成してもよい。Next, the water purification apparatus will be outlined with reference to FIG. 19 is a vegetation bed, 20 is a filter bed formed on the vegetation bed 19, and is provided around the bubble generating apparatus 1. In the present invention, water-extracted plants such as reeds and cattails are used as the aqueous plants AP in the vegetation purification method. Water absorption as the vegetation floor 19,
A water-based plant AP that employs a sponge block having excellent air permeability and buoyancy, for example, a cellulose sponge block.
Plant seeds and grow. The filter bed 20 has a diameter of 5 to 10c.
Use m gravel or charcoal. Note that gravel and charcoal may be mixed and formed.
【0026】21は逆漏斗状の誘導部材で、漏斗の口2
1aと、気泡発生装置1へ向かって斜上する円錐斜面の
誘導面21bとから形成されている。この誘導部材21
は、ガラス繊維強化プラスチックなどの強化プラスチッ
クで造られている。22は公知のリング状のフェンスで
あって、植生床19、濾床20の外側に設けられて、移
動可能であり、浄化装置が風や流れによる移動を阻止す
る。Reference numeral 21 denotes an inverted funnel-shaped guide member, which is the mouth 2 of the funnel.
1a and a guide surface 21b that is a conical slope that slopes upward toward the bubble generating device 1. This guide member 21
Is made of reinforced plastics such as glass fiber reinforced plastics. Reference numeral 22 is a well-known ring-shaped fence, which is provided outside the vegetation floor 19 and the filter floor 20 and is movable, and the purifying device blocks movement due to wind or flow.
【0027】上述の構成から、気泡発生ノズル10から
凝集剤とともに放出された気泡は、凝集フロックを付着
して浮上するが、誘導面21bに沿って、気泡発生装置
1へ向かって斜上したのち、気泡発生装置1と口21a
との間を通って、原水Wとともに濾床20へ注がれる。With the above-mentioned structure, the bubbles discharged from the bubble generating nozzle 10 together with the coagulant adhere to the flocculating flocs and float, but after they obliquely ascend toward the bubble generating device 1 along the guide surface 21b. , Bubble generator 1 and mouth 21a
And the raw water W is poured into the filter bed 20.
【0028】濾床20に注がれた凝集フロックは、まず
濾床20に生息する細菌、原虫などの生物により分解さ
れ、残りは植生床19に至る。植生床19には水性植物
APが植えられているので、残った凝集フロックは、こ
の水性植物APで分解される。The aggregated flocs poured into the filter bed 20 are first decomposed by organisms such as bacteria and protozoa that live in the filter bed 20, and the rest reach the vegetation bed 19. Since the aqueous plants AP are planted in the vegetation bed 19, the remaining flocs are decomposed by the aqueous plants AP.
【0029】植生床19に植えられた水性植物APは、
水中の窒素、リン等の有機物を吸収して繁殖し、増大す
る。又、濾床20の礫、木炭も次第に浄化能力が衰え
る。そこで繁殖、増大した植物群や、浄化能力の衰えた
礫、木炭を容易に撤去、交換できるようにするため、植
生床19、濾床20を互いに連結、開放自在な複数個に
分割すると便利である。例えば図2のように、6個に分
割する。同様に、誘導部材21も6個分割される。同図
中23は筒体のセパレ−タで、気泡発生装置1と口21
aとの間隔を保つ。The aqueous plant AP planted on the vegetation floor 19 is
It absorbs organic substances such as nitrogen and phosphorus in water, propagates, and increases. Further, the purification ability of the gravel and charcoal of the filter bed 20 gradually declines. Therefore, it is convenient to connect the vegetation bed 19 and the filter bed 20 to each other and divide them into a plurality of openable pieces in order to easily remove and replace vegetation groups that have propagated and increased, gravel and charcoal that have deteriorated purification ability, and can be replaced easily. is there. For example, as shown in FIG. 2, it is divided into six pieces. Similarly, the guide member 21 is also divided into six pieces. In the figure, reference numeral 23 is a cylindrical separator, which is a bubble generator 1 and a mouth 21.
Keep the distance from a.
【0030】まず、分割された誘導部材21を図5で示
す。21cは口21aと誘導面21bを連結する左右の
側板、21dは両側板21cの上部を連結する外側板で
ある。分割された植生床19及び濾床20はこの誘導部
材21内に収容される。なお図6、図7のように、植生
床19の外縁を立ち上がらせて外壁19aを形成し、濾
床20を形成する礫、木炭が外へこぼれ落ちないように
するとよい。分割された誘導部材21は、相互に紐、
鎖、フックとリングなどの締結手段で着脱自在に連結さ
れる。First, the divided guiding member 21 is shown in FIG. Reference numeral 21c is a left and right side plate that connects the mouth 21a and the guide surface 21b, and 21d is an outer plate that connects the upper portions of both side plates 21c. The divided vegetation bed 19 and filter bed 20 are housed in this guide member 21. As shown in FIGS. 6 and 7, it is preferable that the outer edge of the vegetation floor 19 is raised to form the outer wall 19a so that the gravel and charcoal forming the filter bed 20 do not fall outside. The divided guide members 21 are strings,
It is detachably connected by a fastening means such as a chain, a hook and a ring.
【0031】24は植生床19を下から支持するネット
で、誘導部材21の上部内壁に固定したフック26に、
ネット24の取付けたリング25を着脱自在に係止し、
ネット24ごと植生床19及び濾床20を持ち出せるよ
うにしている。但し、礫、木炭がこぼれ落ちないように
ネット24の目を細かくし、濾床20を包み込むように
すれば、前記外壁19aを必要としない。Reference numeral 24 is a net for supporting the vegetation floor 19 from below, which is attached to the hook 26 fixed to the upper inner wall of the guide member 21,
Retainably attach the ring 25 attached to the net 24,
The vegetation bed 19 and the filter bed 20 can be taken out together with the net 24. However, if the net 24 is made fine so as to prevent the gravel and charcoal from spilling and the filter bed 20 is wrapped around the net 24, the outer wall 19a is not necessary.
【0032】図8は他の実施の形態を示す。27はフロ
−トで、気泡発生装置1へ向かって斜上する誘導面27
aを有し、内部に発泡スチロ−ルなどの浮力材27bが
収容されている。28は錘である。このフロ−ト27
は、ガラス繊維強化プラスチックなどの強化プラスチッ
クで形成されている。FIG. 8 shows another embodiment. 27 is a float, which is a guide surface 27 that slopes upward toward the bubble generating device 1.
and a buoyancy member 27b such as foam styrol is housed inside. 28 is a weight. This float 27
Are made of reinforced plastics such as glass fiber reinforced plastics.
【0033】29はフロ−ト27に着脱自在に載せられ
た排水マット、排水マット29の上には前記の植生マッ
ト30、植生マット30の上には濾床20が載せられて
いる。植生マット30には、前記スポンジブロックを用
いることもできる。A drainage mat 29 is detachably mounted on the float 27, the above-mentioned vegetation mat 30 is mounted on the drainage mat 29, and the filter bed 20 is mounted on the vegetation mat 30. The sponge block may be used for the vegetation mat 30.
【0034】31はフロ−ト27、排水マット29、植
生マット30の外側部を取り囲む排水外壁で、排水マッ
ト29からしみ出る水を排出できるように、プラスチッ
クの波板が用いられているが、プラスチック又は金属製
のネットに替えることもできる。32はセパレ−タで、
気泡発生装置1とフロ−ト27との間隔を保持するとと
もに、凝集フロックを吸着した気泡を上昇させる通路を
形成する。この波板のセパレ−タ32に替えて、筒体を
用いてもよい。なお、フロ−ト27の内周縁、外周縁を
立ち上がらせて、濾床20の礫、木炭がこぼれ落ちない
ようにすることもできる。又、フロ−ト27、排水マッ
ト29、植生マット30を着脱自在に分割することも可
能である。Reference numeral 31 denotes a drainage outer wall surrounding the outsides of the float 27, the drainage mat 29 and the vegetation mat 30, and a corrugated plate made of plastic is used so that the water oozing out from the drainage mat 29 can be discharged. It can be replaced with a plastic or metal net. 32 is a separator,
The gap between the bubble generator 1 and the float 27 is maintained, and a passage for raising bubbles adsorbing the flocs is formed. A cylindrical body may be used instead of the separator 32 of the corrugated plate. Note that the inner peripheral edge and the outer peripheral edge of the float 27 may be raised to prevent gravel and charcoal of the filter bed 20 from spilling. Further, the float 27, the drainage mat 29 and the vegetation mat 30 can be detachably divided.
【0035】[0035]
【発明の効果】加圧浮上分離方式で浮上した凝集フロッ
クの回収を必要としないため、メンテナンスフリ−とな
りコストダウンが図れる。EFFECTS OF THE INVENTION Since it is not necessary to collect the flocculated flocs that have been floated by the pressure floating separation method, the maintenance is free and the cost can be reduced.
【0036】曝気により十分な溶存酸素が与えられるた
め、通常の植物浄化に比べて浄化効率がよく、又、気
泡、とくに実施形態のような微細な気泡を使用すると空
気溶解効率が高まり浄化効率が向上する。さらに、気
泡、とくに微細な気泡曝気時に水の強制循環が行えるた
め、水域全体の浄化が均一にしかも早く行なえる。Since a sufficient amount of dissolved oxygen is provided by aeration, the purification efficiency is higher than that in normal plant purification, and the use of air bubbles, especially the fine air bubbles as in the embodiment, increases the air dissolution efficiency and improves the air purification efficiency. improves. Furthermore, since forced circulation of water can be performed during aeration of bubbles, especially fine bubbles, the entire water area can be uniformly and quickly purified.
【0037】圧力循環浄化施設として、アオコの主な原
因種であるミクロキスティスを含む水を、加圧タンクで
一定時間加圧することにより、ミクロキスティスのガス
胞を破壊するので、アオコの増殖を直接抑制できる。As a pressure circulation purification facility, water containing microcystis, which is the main causative species of water-bloom, is pressurized in a pressure tank for a certain period of time to destroy the gas vesicles of microcystis, so that the growth of water-bloom is directly Can be suppressed.
【0038】又、加圧浮上分離方式、曝気方式、植生浄
化方式、濾床浄化方式は、各々窒素、リン系の有機物処
理に加え、BOD、COD、SS等の大幅な削減に効果
があることから、これらを組み合わせることにより、さ
らに効率のよい水質浄化を図れる。The pressure floating separation method, aeration method, vegetation purification method, and filter bed purification method are effective in significantly reducing BOD, COD, SS, etc. in addition to nitrogen and phosphorus-based organic matter treatment, respectively. Therefore, by combining these, more efficient water purification can be achieved.
【0039】浮き島として水面に浮かんでおり、水域内
の所望の位置に移動が可能であるため、水域全体を効率
よく浄化できるうえ、水性植物を使用しているので、美
観的にも優れ、自然との調和がとれた環境が創造され
る。Since it floats on the surface of the water as a floating island and can be moved to a desired position within the water area, the entire water area can be efficiently purified, and because it uses water-based plants, it is aesthetically pleasing and natural. An environment in harmony with is created.
【図1】装置全体の側面概念図である。FIG. 1 is a side conceptual view of the entire apparatus.
【図2】装置全体の平面略図である。FIG. 2 is a schematic plan view of the entire device.
【図3】微細気泡発生装置の概念図である。FIG. 3 is a conceptual diagram of a fine bubble generator.
【図4】微細気泡発生ノズルの断面図である。FIG. 4 is a cross-sectional view of a fine bubble generation nozzle.
【図5】分割された誘導部材の斜視図である。FIG. 5 is a perspective view of a divided guide member.
【図6】分割された誘導部材等の平面図であるFIG. 6 is a plan view of a divided guide member and the like.
【図7】図6のA−A線拡大端面図である。7 is an enlarged end view taken along line AA of FIG.
【図8】他の実施形態の側面断面図である。FIG. 8 is a side sectional view of another embodiment.
1 気泡発生装置 3 凝集剤タンク 4 ポンプ 5 エゼクタ 6 加圧タンク 10 気泡発生ノズル 19 植生床 20 濾床 27 フロ−ト 29 排水マット 30 植生マット AP 水性植物 W 原水 1 Bubble Generator 3 Coagulant Tank 4 Pump 5 Ejector 6 Pressurized Tank 10 Bubble Generation Nozzle 19 Vegetation Bed 20 Filter Bed 27 Float 29 Drainage Mat 30 Vegetation Mat AP Water Plant W Raw Water
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C02F 9/00 502 C02F 9/00 502Z 503 503A 504 504A 504E (72)発明者 岡部 喜洋 岡山県岡山市四御神463番地の1 (72)発明者 田中 英樹 兵庫県赤穂市鷏和512番地の152─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification number Reference number within the agency FI Technical indication C02F 9/00 502 C02F 9/00 502Z 503 503A 504 504A 504E (72) Inventor Yoshihiro Okabe Okayama Okayama 1 of 463 Shimikami, Ichi (72) Inventor Hideki Tanaka 152 of 512, Sumiwa, Ako City, Hyogo Prefecture
Claims (5)
し、原水と凝集剤とにより生じた凝集フロックに気泡を
吸着させて浮上させて、水性植物と、礫又は/及び木炭
からなる濾床とに注ぎ、凝集フロックを水性植物と濾床
とで分解させる水質浄化方法。1. A coagulant and air bubbles are released into polluted raw water, and the air bubbles are adsorbed and floated on the floc generated by the raw water and the coagulant to obtain a filter comprising an aqueous plant and gravel and / or charcoal. A water purification method in which the flocs are poured into a floor and decomposed by flocculation with an aqueous plant and a filter bed.
された原水に凝集剤を添加する凝集剤タンクと、ポンプ
へ接続されて原水へ空気を混合するエゼクタと、エゼク
タに接続された加圧タンクとからなり、水面に浮上して
移動可能な気泡発生装置の下方の水中に加圧タンクに接
続された気泡発生ノズルを設け、気泡発生装置の周囲
に、水性植物を植られて浮上する吸水性、通気性のある
植生床と、植生床の上に礫又は/及び木炭からなる濾床
とを配設するとともに、原水と凝集剤とにより生じた凝
集フロックに付着して浮上する気泡を気泡発生装置へ向
かって斜上させて、気泡発生装置と、植生床と濾床との
間を通って濾床に注がせる誘導部材を設けてなる水質浄
化装置。2. A pump for sucking polluted raw water, a coagulant tank for adding a coagulant to the sucked raw water, an ejector connected to the pump for mixing air into the raw water, and a pressurizer connected to the ejector. A bubble-generating nozzle that is connected to a pressurized tank is provided in the water below the bubble-generating device, which is composed of a tank and floats above the water surface and is movable. A vegetation bed that is air-permeable and breathable, and a filter bed made of gravel and / or charcoal is placed on the vegetation bed, and bubbles that float by adhering to the floc generated by the raw water and the flocculant are formed. A water purification device which is provided with an air bubble generator and a guide member which is slanted upward toward the generator and can be poured into the filter bed between the vegetation bed and the filter bed.
浮上するフェンスが設けられている請求項2の水質浄化
装置。3. The water purification apparatus according to claim 2, wherein a movable floating fence is provided around the vegetation floor and the filter bed.
分割されており、各分割された植生床及び濾床とは、植
生床及び濾床を囲む各分割された誘導部材に着脱自在な
ネットで支持されている請求項2又は3の水質浄化装
置。4. The guide member is divided into a plurality of vegetation beds and filter beds, and each divided vegetation bed and filter bed is attached to and detached from each divided guide member surrounding the vegetation floor and filter beds. The water purification device according to claim 2 or 3, which is supported by a free net.
された原水に凝集剤を添加する凝集剤タンクと、ポンプ
へ接続されて原水へ空気を混合するエゼクタと、エゼク
タに接続された加圧タンクとからなり、水面に浮上して
移動可能な気泡発生装置の下方の水中に加圧タンクに接
続された気泡発生ノズルを設け、気泡発生装置の周囲に
配設したフロ−トの上に、排水マット、水性植物を植え
た植生床、礫又は/及び木炭からなる濾床を順次積み重
ねるとともに、フロ−トは、原水と凝集剤とにより生じ
た凝集フロックに付着して浮上する気泡を気泡発生装置
へ向かって斜上させて、気泡発生装置と、フロ−ト、排
水層、植生床、濾床との間を通って濾床に注がせる誘導
面を有する水質浄化装置。5. A pump for sucking polluted raw water, a coagulant tank for adding a coagulant to the sucked raw water, an ejector connected to the pump for mixing air into the raw water, and a pressurizer connected to the ejector. A bubble generating nozzle connected to the pressure tank is provided in the water below the bubble generating device which is composed of a tank and floats on the water surface and is movable, and on a float arranged around the bubble generating device, Drainage mats, vegetation beds planted with aqueous plants, filter beds made of gravel and / or charcoal are stacked in sequence, and the floats generate bubbles by adhering to floc flocs generated by raw water and flocculant. A water purification device having a guide surface that is slanted upward toward the device and can be poured into the filter bed through the space between the bubble generator and the float, drainage layer, vegetation bed, and filter bed.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP4050896A JP3049384B2 (en) | 1996-02-02 | 1996-02-02 | Water purification method and water purification device used for the method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP4050896A JP3049384B2 (en) | 1996-02-02 | 1996-02-02 | Water purification method and water purification device used for the method |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH09206788A true JPH09206788A (en) | 1997-08-12 |
JP3049384B2 JP3049384B2 (en) | 2000-06-05 |
Family
ID=12582496
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Application Number | Title | Priority Date | Filing Date |
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JP4050896A Expired - Fee Related JP3049384B2 (en) | 1996-02-02 | 1996-02-02 | Water purification method and water purification device used for the method |
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JP2015061962A (en) * | 2013-09-21 | 2015-04-02 | 株式会社シビルテック | Pollution prevention apparatus and method |
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