JP5360550B2 - Aoko control method - Google Patents

Aoko control method Download PDF

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JP5360550B2
JP5360550B2 JP2009024259A JP2009024259A JP5360550B2 JP 5360550 B2 JP5360550 B2 JP 5360550B2 JP 2009024259 A JP2009024259 A JP 2009024259A JP 2009024259 A JP2009024259 A JP 2009024259A JP 5360550 B2 JP5360550 B2 JP 5360550B2
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water
vibration wave
wave generator
stirring blade
generator
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JP2010158657A (en
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虎東 朴
篤 宮田
還三 丸田
裕 大井川
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Shinshu University NUC
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E60/00Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
    • Y02E60/30Hydrogen technology
    • Y02E60/36Hydrogen production from non-carbon containing sources, e.g. by water electrolysis
    • 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
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

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  • Mixers Of The Rotary Stirring Type (AREA)
  • Electrolytic Production Of Non-Metals, Compounds, Apparatuses Therefor (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a technology for reducing the biomass of algae including toxic water blooms (toxic algae), and for controlling the concentration of phosphorus in water, because nutrient salts such as phosphorus in industrial wastewater and agricultural/livestock wastewater accelerate eutrophication of aquatic environments as typified by seas, rivers, lakes, reservoirs, etc., and thus the massive proliferation phenomenon of blue-green algae (so-called water blooms) caused by the eutrophication occurs in water sources around the world and has become a serious environmental problem. <P>SOLUTION: A vibration-wave generator controls the growth of the toxic water blooms. Furthermore, an oxygen/ozone generator suppresses the elution of phosphorus which is regarded as necessary for the growth of phytoplankton (algae), from bottom mud, and promotes the adsorption of phosphorus to the bottom mud. <P>COPYRIGHT: (C)2010,JPO&amp;INPIT

Description

産業排水と農業・畜産排水中のリン等の栄養塩類が、海、河川、湖沼、溜池等に代表される水圏環境の富栄養化を加速化させ、富栄養化で起こる藍藻類の大増殖現象(いわゆるアオコ)が世界各地の水圏環境に発生し、大きな環境問題化しており、今後水圏環境におけるアオコの抑制は必要不可欠である。本発明は、このような有毒アオコ(有毒藻類)を含む藻類の発生を制御する技術に関する。  Nutrients such as phosphorus in industrial wastewater and agricultural / livestock wastewater accelerate eutrophication of the aquatic environment represented by the sea, rivers, lakes, ponds, etc. (So-called blue-green) has occurred in the hydrosphere environment around the world and has become a major environmental problem, and it is essential to control blue-green aquatic environment in the future. The present invention relates to a technique for controlling the generation of algae including such a poisonous auko (toxic algae).

アオコ抑制のための湖沼や河川等の水圏環境における浄化装置は、多数考案されているが従来の方法は、単純に空気又は、酸素を湖沼の深層に送り込む技術が主である。また、海外ではアオコを死滅させる化学薬品(重金属、除草剤、吸着剤など)を用いることが多いが根本的な解決方法にはならず、新たな環境問題を引き起こす例も報告されている。また、薬品を使用する際には経費が高くなることと他生物の影響を懸念することも多いことから使用許可を得ることが困難である。ジェットポンプといった人工的水流、湖沼の曝気、人工的攪拌、化学的処理、溶藻菌・ファージ、超音波等の様々な方法が試みられてきたが、藍藻類の処理時・処理後に発生するラン藻毒素溶出や、水質への影響等の問題点がある。これら従来のアオコ抑制技術は、アオコ発生後の水圏環境を対象として処理を行う点で共通している。水圏環境におけるアオコの主な発生は、長年蓄積された底泥からの栄養塩類の溶出が大きな原因となっている。本発明は、底泥からの栄養塩類を抑制することで、アオコの発生を抑制する有効な方法を開発することを目的とした。
従来から、湖沼浄化装置(特許文献1)やアオコ除去装置(特許文献2)、水浄化システム及び水流発生攪拌混合機(特許文献3)、水浄化システム(特許文献4)等あるが、水圏環境をアオコが発生しにくい環境に変化させる方法の開発に該当するものは無い。
特開平5−237493号公報 特開平11−70382号公報 特開2006−835号公報 特開2007−7603号公報
Many purification devices have been devised in aquatic environments such as lakes and rivers for the control of sea cucumbers, but the conventional methods are mainly based on technology that simply sends air or oxygen into the deep layers of the lakes. In addition, chemicals (such as heavy metals, herbicides, adsorbents, etc.) that kill mushrooms are often used overseas, but this is not a fundamental solution, and examples of causing new environmental problems have been reported. In addition, when using chemicals, it is difficult to obtain permission to use because the cost is high and there are many concerns about the effects of other organisms. Various methods such as artificial water flow such as jet pump, aeration of lakes, artificial stirring, chemical treatment, lytic algae / phage, ultrasonic, etc. have been tried. Runs generated during and after treatment of cyanobacteria There are problems such as algal toxin elution and effects on water quality. These conventional sea cucumber suppression techniques are common in that processing is performed for the hydrosphere environment after the sea bream has occurred. The major outbreak of sea lions in the hydrosphere environment is largely due to the elution of nutrients from the bottom mud accumulated over many years. An object of the present invention is to develop an effective method for suppressing the occurrence of blue seaweed by suppressing nutrient salts from the bottom mud.
Conventionally, there are a lake purification device (Patent Document 1), a sea cucumber removal device (Patent Document 2), a water purification system, a water flow generation agitation mixer (Patent Document 3), a water purification system (Patent Document 4), etc. There is nothing that corresponds to the development of a method to change the environment to the environment where blue-green is unlikely to occur.
JP-A-5-237493 Japanese Patent Laid-Open No. 11-70382 Japanese Patent Laid-Open No. 2006-835 JP 2007-7603 A

アオコなどの藻類の繁殖を制限しているのは、主にリン類の量だと言われている。一般的に藻類は、冬季に死滅沈降して底泥中に堆積するが、底泥中の細菌や微生物が藻類の死骸を分解して、リン酸態リン(PO−P)ができて水中に溶出する。このリンを栄養源として翌年に再び藻類が発生するという循環ができている。したがって、水圏環境に蓄積された栄養塩類の除去又は溶出を防ぐことがアオコを抑制することになる。湖沼や溜池等は古いものが多く、長年にわたって外部から絶え間なく供給される栄養塩類が底泥に蓄積されており、これを除去し、流入する栄養塩類を削減できれば恒久的な水質改善になる。
水源地として利用される、湖沼・ダム湖などでは、水温が20℃以上となる環境下で特にアオコが発生し、浄水処理中に凝集沈殿剤とアオコのカビ臭(ジオスミン等)の除去のために多額の費用を負担している。そこで本発明は、従来の藻類装置で問題点として挙げられた、他生物への影響が少ないアオコの成長阻害の物理的方法に着目した点が特徴である。異常発生し続けるアオコ(有毒藻類)を無害の藻類に変えることと生物量の発生を抑制し減少させることで水圏環境の環境改善に負荷をかけずに行うことが本発明で解決しようとする課題である。
It is said that it is mainly the amount of phosphorus that restricts the growth of algae and other algae. Typically algae, but is deposited on the bottom mud dying precipitation in winter, bacteria and microorganisms Sediment is decomposed carcasses of algae, and be phosphorus Santai phosphorus (PO 4 -P) water To elute. Using this phosphorus as a nutrient source, the algae are generated again in the following year. Therefore, preventing the removal or elution of nutrients accumulated in the aquatic environment suppresses the sea cucumber. Many lakes and ponds are old, and nutrients that are constantly supplied from the outside have accumulated in the bottom mud for many years. If this can be removed and the nutrients that flow in can be reduced, the water quality will be improved permanently.
In the lakes and dam lakes that are used as water sources, water flounder is generated especially in an environment where the water temperature is 20 ° C or higher, and in order to remove the coagulant precipitant and the mold odor (such as diosmine) during water purification treatment. It bears a large amount of expenses. Therefore, the present invention is characterized by focusing on a physical method for inhibiting the growth of sea cucumber, which has been cited as a problem in the conventional algal apparatus and has little influence on other organisms. The problem to be solved by the present invention is to change aquatic (toxic algae), which continues to occur abnormally, into harmless algae and to suppress and reduce the generation of biomass without burdening the environment improvement of the hydrosphere environment. It is.

本発明は、アオコ制御システムとして、振動波発生装置と酸素及びオゾン発生装置の組合わせで構成されている。振動波発生装置は、特許第3980557号「液流発生装置」を使用し、水圏環境に浮かべるための筏部分、装置を支えるための基台部、攪拌翼及び攪拌翼を回転させるための動力から成る。従来の攪拌装置とは攪拌翼の形状が大きく異なり、媒質を振動させて攪拌を行うことができる。攪拌翼が2つ以上あるものを多翼式、単体のものを一翼式と呼称する。従来の攪拌装置と比較すると低速回転で運用されるため媒質中の回転抵抗が少なく、耐久性に優れている。
本発明は、フロートを備える基台に、振動波発生装置と酸素発生装置とを取り付けた装置を利用してアオコの発生を抑制するアオコ制御方法であって、前記振動波発生装置は、回転軸に垂直に配され、回転軸の回転とともに水を揺動させる振動作用を生じさせる、扁平なラグビーボール状に形成された振動翼と、前記回転軸に斜めに交差して配され、回転軸の回転とともに水に連続的な流れを発生させる流動翼とからなる攪拌翼と、攪拌翼を回転させる動力とを備え、前記基台により支持して前記振動波発生装置と前記酸素発生装置とを湖中に設置し、夏季等のアオコが発生する水圏環境下においては、前記振動波発生装置と前記酸素発生装置とを併用稼働させて、湖底からの栄養塩類の溶出を抑制してアオコの発生を防止または軽減し、冬季等のアオコが発生しない水圏環境下においては、前記振動波発生装置のみを稼働させ、湖底からの栄養塩類を溶出、回収することを特徴とする。
また、前記酸素発生装置として、水の電気分解による酸素発生装置を用いることを特徴とし、湖中の深さ方向において、水面に近い側と水面から離れる側とにそれぞれ攪拌翼を備え、上側の攪拌翼は回転軸が垂直配置され、下側の攪拌翼は回転軸が水平配置された振動波発生装置を用いることを特徴とする。
The present invention is configured by a combination of a vibration wave generator and oxygen and ozone generators as a water scale control system. The oscillatory wave generator uses Japanese Patent No. 3980557 “Liquid Flow Generator”, from the heel part for floating in the aquatic environment, the base part for supporting the apparatus, the stirring blade and the power for rotating the stirring blade Become. The shape of the stirring blade is greatly different from that of a conventional stirring device, and stirring can be performed by vibrating the medium. One having two or more stirring blades is called a multi-blade type, and one having a single stirring blade is called a one-wing type. Compared with a conventional stirring device, since it is operated at a low speed, the rotational resistance in the medium is small and the durability is excellent.
The present invention is a water scale control method for suppressing the generation of water using a device in which a vibration wave generator and an oxygen generator are attached to a base including a float, wherein the vibration wave generator is a rotating shaft. The oscillating wing formed in the shape of a flat rugby ball that produces a vibrating action that swings water with the rotation of the rotating shaft, and is arranged obliquely intersecting the rotating shaft, A stirring blade comprising a fluid blade that generates a continuous flow in water as it rotates, and a power that rotates the stirring blade, and is supported by the base to support the vibration wave generator and the oxygen generator. In the aquatic environment where aquatics are generated during summer, etc., the vibration wave generator and the oxygen generator are operated in combination to suppress the release of nutrients from the bottom of the lake. Prevent or reduce winter Under aquatic environment-bloom does not occur etc., it is operated only the vibration generator, eluting the nutrients from lake, and recovering.
Further, the oxygen generator is an oxygen generator by electrolysis of water, and in the depth direction in the lake, a stirring blade is provided on each of the side close to the water surface and the side away from the water surface, The agitating blade uses a vibration wave generator in which the rotation axis is vertically arranged, and the lower agitating blade is horizontally arranged in the rotation axis.

攪拌翼の振動波発生原理を説明する。媒質中のある点における流速や圧力は大きくなったり小さくなったりといった変化を繰り返しており、規則的または不規則的な繰り返し変化を振動と総称する。揺動とは、例えば容器に入れた液体を揺すると、液体が波打って揺れる現象のことである。揺動では、液体の形状は容器の形状に沿って変化するが、流れはほとんど起きず、揺するのをやめると液体粒子は元の位置に戻る。この現象は、水面に浮かべた物質(木の葉等)で観察することができる。攪拌翼の回転には電気等の動力が必要であり、回転に要したエネルギーが媒質中を伝播するエネルギーや流動に費やされるエネルギーに転嫁すると考えられる。(エネルギー保存の法則)
攪拌翼の構成は、本体の回転軸に対して垂直に配置されている振動翼(Wave Wing)で、やや扁平にしたラクビーボール状の膨らんだ形である。この振動翼が媒質中を回転すると、振動部分の体積に相当する媒質を押しよけるが、翼の通過後は、押しよけられた媒質が元の位置に戻ろうとする揺動が発生する。この連続動作により媒質中に振動効果が得られる。この振動翼に対して半分位の膨らみで、回転軸中心部から斜めに交差するよう固定された翼が流動翼(Flow Wing)である。この流動翼が媒質中を回転すると、パドルが水を押し出すように連続的な流動(流れ)を発生させる。すなわち流動翼は、媒質を構成する物質粒子自体を移流及び拡散させることができる。従来、水圏環境に流動を発生させる手段としては、プロペラ、スクリュー等の回転力を利用して流動を発生させる方法、また噴射流体のエネルギーを外部から水圏環境に与えて流動を起こす方法がある。いずれの方法も発生した流れを装置から遠方領域まで効率よく拡散させる事は困難である。その原因は、プロペラ等を高速回転して発生させる流れは、乱流状態であり瞬間的には大きな流速を発生させることはできるが、乱流に伴うエネルギー損失などの減衰作用により、装置からの距離が遠くになるにつれて流速が低下するためである。したがって、これらの方法で水圏環境に大域的な流動を発生させることは、エネルギー効率が悪く、遠方領域に影響を与えるためには構造が大きくなり、経済性や耐久性が乏しくなるため、実用に適さないのが現状である。
攪拌翼を回転することで誘起される媒質の流速については、撹拌翼の大きさや回転数に依存するが、例えば水中で直径1.0mの撹拌翼が毎分180回転する場合は、最大で約10.0[m/s]の流速が得られるが、水中を伝播する圧力波の伝播速度は 約1,500[m/s]に達する。すなわち、媒質の流速と圧力波の伝播速度は異なる現象の速度をあらわす。圧力波の伝播は流動とは異なり、媒質を構成する粒子そのものが流動のように移動するのではなく、媒質が振動することにより、エネルギーが媒質中を伝播していく現象である。媒質自体はある点を中心に振動するのみで、移流はしない。一方、流動とは前述したように媒質の流れであり、媒質構成粒子自体が移動していく現象である。一般に、振動や揺動を含む波動現象はエネルギーの伝播現象であり、流動現象と比較するとエネルギーの損失が少なく、エネルギーを遠方まで輸送することが可能である。流動の場合は、媒質の減衰が原因で、流れを遠方に拡散するためには非常に大きなエネルギーを要し、逆に小さなエネルギーでは、減衰により流れを遠方に拡散することができない。しかし提示する振動波発生装置は、媒質に振動と流動を交互に繰り返し生成させることにより遠方領域まで流動の影響を及ぼすことが可能であり、実証実験では、小さな入力エネルギー(600W程度)で湖沼全域(60,000m3)に低速で大域的な流動作用が可能であることを確認した。このように振動エネルギーと流動エネルギーの相乗効果で遠方領域まで媒質を連続的に運動させる事ができ、且つ装置構造が簡単で耐久性と経済性の高いものを提供することを可能とした。
The principle of vibration wave generation of the stirring blade will be described. Changes in flow velocity and pressure at a certain point in the medium repeatedly increase and decrease, and regular or irregular repetitive changes are collectively referred to as vibration. Oscillation is a phenomenon in which, for example, when a liquid placed in a container is shaken, the liquid undulates and shakes. In rocking, the shape of the liquid changes along the shape of the container, but almost no flow occurs, and when the shaking is stopped, the liquid particles return to their original positions. This phenomenon can be observed with substances floating on the water surface (such as leaves of trees). The rotation of the stirring blades requires power such as electricity, and it is considered that the energy required for the rotation is transferred to the energy propagating in the medium and the energy consumed for the flow. (Laws of energy conservation)
The configuration of the stirring blade is a vibrating blade (Wave Wing) arranged perpendicular to the rotation axis of the main body, and has a slightly flattened rugby ball shape. When this oscillating blade rotates in the medium, the medium corresponding to the volume of the vibrating portion is pushed away, but after passing through the wing, the oscillated medium tries to return to its original position. This continuous operation provides a vibration effect in the medium. A wing that is half-bulged with respect to this oscillating blade and is fixed so as to cross obliquely from the center of the rotating shaft is a flow wing. When this fluid blade rotates in the medium, a continuous flow (flow) is generated so that the paddle pushes out water. That is, the fluid blade can advect and diffuse the material particles constituting the medium. Conventionally, as means for generating a flow in the aquatic environment, there are a method for generating a flow by using a rotational force such as a propeller and a screw, and a method for causing a flow by applying energy of a jetting fluid to the aquatic environment from the outside. In either method, it is difficult to efficiently diffuse the generated flow from the apparatus to a far region. The cause is that the flow generated by rotating the propeller etc. at high speed is in a turbulent state and can generate a large flow rate instantaneously, but due to the damping action such as energy loss accompanying turbulent flow, This is because the flow velocity decreases as the distance increases. Therefore, generating global flows in the aquatic environment using these methods is not energy efficient, increases the structure to affect distant areas, and reduces economic efficiency and durability. The current situation is not suitable.
The flow rate of the medium induced by rotating the stirring blade depends on the size and the number of rotations of the stirring blade.For example, when a stirring blade having a diameter of 1.0 m in water rotates 180 rpm, the maximum is about 10.0. Although a flow velocity of [m / s] is obtained, the propagation speed of pressure waves propagating in water reaches about 1,500 [m / s]. That is, the flow velocity of the medium and the propagation velocity of the pressure wave represent different phenomena. Unlike the flow, the propagation of the pressure wave is a phenomenon in which the energy itself propagates through the medium as the medium vibrates rather than the particles themselves constituting the medium moving. The medium itself only vibrates around a point, not advection. On the other hand, the flow is the flow of the medium as described above, and is a phenomenon in which the medium constituting particles themselves move. In general, wave phenomena including vibrations and oscillations are energy propagation phenomena, and energy loss is less than that of flow phenomena, and energy can be transported far away. In the case of flow, because of the attenuation of the medium, very large energy is required to diffuse the flow far away. Conversely, with small energy, the flow cannot be diffused far away due to attenuation. However, the proposed vibration wave generator can influence the flow to a distant region by alternately generating vibration and flow in the medium, and in the demonstration experiment, the entire lake area with a small input energy (about 600W). (60,000 m 3 ) It was confirmed that a global flow action was possible at low speed. In this way, the synergistic effect of vibration energy and flow energy can continuously move the medium to a distant region, and it is possible to provide a device having a simple structure and high durability and economy.

酸素発生装置は、特許第40353023号「液体浄化装置」参照:微細気泡(マイクロバブル・ナノバブル)発生装置併用例である。水圏環境への酸素の拡散により対象とする水圏環境を好気的とし、植物プランクトンの成長に必要とされているリンの底泥からの溶出を抑えることとリンの底泥への吸着を促進することができる。通常の酸素発生装置では湖沼の深層に酸素を送り込むことは装置が大掛かりで、運転コストもかかり、設置及び運営に課題が残る。しかし提示する振動波発生装置と併用することにより、小さな入力エネルギーで対象水圏環境全域に微細気泡(マイクロバブル・ナノバブル)を拡散させ好気的とし、底泥からのリンの溶出を抑える。 The oxygen generator is a combination example of microbubbles and nanobubbles generators: see Japanese Patent No. 40353030 “Liquid Purification Device”. Making the target aquatic environment aerobic by diffusing oxygen into the aquatic environment, suppressing the elution of phosphorus required for phytoplankton growth from the bottom mud and promoting the adsorption of phosphorus to the bottom mud be able to. In a normal oxygen generator , sending oxygen into the deep layers of the lake is large and the operation cost is high, and there are problems in installation and operation. However, when used in combination with the vibration wave generator presented here, microbubbles (microbubbles and nanobubbles) are diffused throughout the target hydrosphere environment with a small amount of input energy, making it aerobic and suppressing phosphorus elution from the bottom mud.

上記酸素発生装置の他に、水の電気分解装置(水電解電極)による組合わせがある。この方法は、少ない動力で水深の深い場所でも酸素を発生させ、水圏環境全域に拡散させることができる。また同時発生した水素は回収してエネルギーとして再利用することも可能である。 In addition to the oxygen generator , there is a combination using a water electrolyzer (water electrolysis electrode). With this method, oxygen can be generated even in deep water with less power and diffused throughout the hydrosphere environment. Simultaneously generated hydrogen can be recovered and reused as energy.

本発明の実証実験を水源地(60,000m)で、2002年〜2005年まで振動波発生装置と併用した酸素及びオゾン発生装置との一例とした、微細気泡(マイクロバブル・ナノバブル)発生装置を用いて水質浄化を目的として行った。2003年は攪拌翼が2つの多翼式のみ、2004年は一翼式と微細気泡(マイクロバブル・ナノバブル)発生装置の併用、2005年は一翼式のみ、2006年は設置せずPO−P濃度を調べた結果、各年のPO−P濃度は2003年が35μgL−1、2004年が14μgL−1、2005年が14μgL−1、2006年が11μgL−1を示した。
振動波装置が底泥中の栄養塩類溶出速度に与える影響を確かめるため、1トン水槽での栄養塩類溶出実験を行った。実験結果は、DO消費速度は振動波装置区で3.5mgO−1day−1、対照区で1.1mgO−1day−1を示した。実験22日目のDO濃度は酸素供給区で4.0mgO−1、振動波装置+酸素供給区で6.9mgO−1を示した。実験22日目のPO−P濃度は対照区で552μgL−1、振動波装置区で948μgL−1、酸素供給区と振動波装置+酸素供給区で検出限界以下を示した。15〜22日目でのPO−P溶出速度は、対照区で26mg m−2day−1、振動波装置区で48mg m−2day−1を示した。本実験結果より、アオコ制御には、外部負荷を制限し、振動波発生装置と酸素供給装置を同時に稼動させることが適切である。この方法は水圏環境を効率的に好気的にし、還元状態になりやすい底泥の表面を酸化状態とし、酸化鉄の薄層を形成し、底泥中の栄養塩の溶出を抑制することでアオコ発生を制御する(DOの増加はPOの供給を抑え、消費を促す)ことが可能である。
Fine bubble (micro bubble / nano bubble) generator as an example of oxygen and ozone generator in combination with vibration wave generator from 2002 to 2005 at water source (60,000 m 3 ) Was used for the purpose of water purification. In 2003, only a multi-blade type with two agitating blades, in 2004 a single-blade type and a microbubble (nanobubble) generator were used together, in 2005, only one-wing type, and in 2006, PO 4 -P concentration without installation the results of examining, PO 4 -P concentration of each year in 2003 35μgL -1, in 2004 14μgL -1, in 2005 14μgL -1, in 2006 showed the 11μgL -1.
In order to confirm the influence of the vibration wave device on the elution rate of nutrients in the bottom mud, a nutrient elution experiment was conducted in a 1-ton water tank. Experimental results, DO consumption rate showed 3.5mgO 2 L -1 day -1, 1.1mgO 2 L -1 day -1 in the control group in the vibration wave apparatus Ward. DO concentrations of the experimental day 22 showed 4.0mgO 2 L -1, 6.9mgO 2 L -1 vibration wave apparatus + oxygen supply ku oxygen supply Ward. PO 4 -P concentration of experimental 22 day 552MyugL -1 in the control group, 948MyugL -1 vibration wave apparatus Ward showed below the detection limit of oxygen supply ku a vibration wave device + oxygenation reserve. PO 4 -P dissolution rate at 15 to 22 day, 26 mg m -2 day -1 in the control group showed 48 mg m -2 day -1 vibration wave apparatus Ward. From the results of this experiment, it is appropriate to limit the external load and operate the vibration wave generator and the oxygen supply device at the same time for the aquo control. This method makes the aquatic environment efficient and aerobic, makes the bottom mud surface that tends to be reduced to an oxidized state, forms a thin layer of iron oxide, and suppresses the elution of nutrient salts in the bottom mud. It is possible to control the occurrence of blue water (increasing DO suppresses supply of PO 4 and promotes consumption).

振動波発生装置で酸素及びオゾン発生装置を併用しない場合は、水圏環境底部を嫌気的に誘導するため底泥中の栄養塩類が溶出しやすくなる。POはOがあると一部が周囲の金属イオン(Fe,Al,Ca,Mg等)と結合し、植物が利用できない不溶物の状態で存在する。Oが不足してくると金属から離れPO−Pとして水中に溶出し植物プランクトンの栄養となる。Oを供給しない単体での稼動はDO消費速度が3倍、PO−P溶出速度が2倍となる。湖底には有機物が含まれるヘドロ等の堆積物があり水中微生物による分解(化学反応)作用が振動波によって活性化され、高速に促進される。この化学反応により湖底の酸素は消費され、嫌気性環境となる。O不足の湖底から底泥中の栄養塩類が溶出する(水中に継続的にPO−Pが補給)ことは湖底の堆積物の負荷軽減になる。振動波発生装置単体稼動では栄養塩類が堆積していた1年目は多量の栄養塩類が溶出する(水圏環境底部の環境改善の始まり)ため、むしろアオコは大量発生する。負荷軽減の水圏環境底部土壌改良効果には2〜3年の期間が必要となる。これは浚渫に近い効果が見込まれるとともに、浚渫工事で必要な浚渫泥の処理が不要になる。また大量に発生したアオコに対しては、死滅させると毒素拡散の可能性あり、回収しないと栄養塩類の再供給となるため、回収し毒素を抽出した上で肥料(リン)等へのリサイクルすることも可能である。When the vibration wave generator does not use oxygen and ozone generators together, the bottom of the aquatic environment is anaerobically induced, so that nutrient salts in the bottom mud are easily eluted. PO 4 is partly bound to surrounding metal ions (Fe, Al, Ca, Mg, etc.) in the presence of O 2 and exists in an insoluble state that cannot be used by plants. When O 2 runs short, it leaves the metal and elutes in water as PO 4 -P and becomes nutrition for phytoplankton. Operation with a single unit not supplying O 2 increases the DO consumption rate by a factor of 3, and the PO 4 -P elution rate by a factor of two. There are sediments such as sludge containing organic matter on the bottom of the lake, and the action of decomposition (chemical reaction) by underwater microorganisms is activated by vibration waves and accelerated at high speed. This chemical reaction consumes oxygen at the bottom of the lake, creating an anaerobic environment. The elution of nutrients in the bottom mud from the O 2 deficient lake bottom (continuous supply of PO 4 -P in the water) reduces the load on the sediment on the lake bottom. In the first year when the oscillatory wave generator is in operation, a large amount of nutrients are eluted in the first year when the nutrients have accumulated (beginning of environmental improvement at the bottom of the hydrosphere environment), so a large amount of sea cucumbers are generated. A period of 2 to 3 years is required for the soil improvement effect at the bottom of the aquatic environment to reduce the load. This is expected to have an effect similar to dredging, and the treatment of dredged mud required for dredging work is unnecessary. In addition, the aquatic mushrooms that are produced in large quantities may diffuse toxins if they are killed. If they are not collected, nutrients will be resupplied, so they will be collected and extracted into toxins and recycled to fertilizer (phosphorus), etc. It is also possible.

振動波発生装置と酸素及びオゾン発生装置を併用したアオコ制御方法の応用例として、水温が20℃以上となる水圏環境下(例えば夏季)で特にアオコ(有毒藻類含む)が発生するため、振動波発生装置と酸素及びオゾン発生装置を併用稼動させて、湖底からの栄養塩類の溶出を抑制することでアオコの発生を防止又は軽減する。反対に、水温が20℃以下となる水圏環境下(例えば冬季)は、水温が低いためアオコの発生はないため、振動波発生装置単体で稼動させることにより、堆積した湖底からの栄養塩類PO−Pを溶出、回収することが可能である。As an application example of the blue sea cucumber control method using both the vibration wave generator and oxygen and ozone generators, the blue water (including toxic algae) is generated especially in the aquatic environment (for example, summer) when the water temperature is 20 ° C. or higher. The generation device and the oxygen and ozone generation device are operated in combination to prevent or reduce the occurrence of sea cucumber by suppressing the elution of nutrient salts from the lake bottom. On the other hand, in a hydrosphere environment where the water temperature is 20 ° C. or lower (for example, in winter), since the water temperature is low, there is no occurrence of aquatic plants. Therefore, the nutrient wave PO 4 from the accumulated lake bottom can be operated by operating the vibration wave generator alone. -P can be eluted and collected.

水質汚染が進行する水圏環境は、水源地であることも多く、又水域に生息する生態系へ影響を考慮すると、装置の動作によりヘドロを巻き上げて縣濁が発生することは避けなければならない。提案する攪拌翼は翼を中心に上下に二層の対流が発生し、撹拌翼から底泥に向かう強い水流が存在しないため、従来の攪拌翼で発生する底泥の巻上げとそれに伴う懸濁を生じない。また、撹拌翼の回転数は50〜180rpm程度で運転するため、水域は低速な流動を生じるのみで、ヘドロの巻き上げや懸濁は生じない The aquatic environment where water pollution progresses is often a water source, and considering the impact on ecosystems inhabiting the water area, it is necessary to avoid the occurrence of turbidity by rolling up sludge due to the operation of the device. The proposed stirring blade has two layers of convection up and down around the blade, and there is no strong water flow from the stirring blade to the bottom mud. Does not occur. Further, since the rotation speed of the stirring blade is operated at about 50 to 180 rpm, the water area only generates a low-speed flow, and the sludge is not wound or suspended .

図1は本発明に係る装置の一実施例の説明図である。以下これらの図面に基づき説明をする。
アオコ制御装置1、フロート 2、筏形基台 3、基台部4、で骨組みが構成されている。基台部4を中央、縦に配置し水中に浮かべると、基台部4が2/3位水中に沈む。振動波発生装置は、基台部にモーター 5、シャフト 6、ギヤボックス 7、攪拌翼(水平配置) 8、攪拌翼(垂直配置)9、が配置されている。攪拌翼は垂直回転の振動翼 9a、斜め交差回転の流動翼 9b、で構成されている。図は攪拌翼が2つの多翼式で構成されている。酸素発生装置 10、は水中モーター 11、吸込み口(ストレーナー付)12、吸水ホース 13、攪拌筒 14、インペラー(吐出口)15、吸気口(調整弁付)16、吸気ホース 17、で構成されており、水中モーター 11が始動すると吸込み口(ストレーナー付)12より水が吸水されて、吸水ホース 13、攪拌筒 14、を通りインペラー(拡散口)15で吐き出される。この一連の循環流速により、小さい吸気口(調整弁付)16は負圧となり、空気が吸気ホース 17を通じて導入される。この空気は攪拌筒 14に送られ、水と空気が粉砕混合されて微細気泡となりインペラー(拡散口)15から水中に放出拡散される。電源の供給は、モーター 5と水中モーター 11の電源ケーブル 18が電源供給されている結線ボックス 19に接続されている。
FIG. 1 is an explanatory view of an embodiment of an apparatus according to the present invention. The following description is based on these drawings.
A framework is constituted by the aoko control device 1, the float 2, the bowl-shaped base 3, and the base 4. If the base part 4 is arranged vertically in the center and floats in the water, the base part 4 sinks into the 2/3 rank water. In the vibration wave generator, a motor 5, a shaft 6, a gear box 7, a stirring blade (horizontal arrangement) 8, and a stirring blade (vertical arrangement) 9 are arranged on the base. The stirring blade is composed of a vertically rotating vibrating blade 9a and a slanting cross rotating fluid blade 9b. In the figure, the stirring blade is composed of two multi-blade types. The oxygen generator 10 includes a submersible motor 11, a suction port (with a strainer) 12, a water suction hose 13, a stirring cylinder 14, an impeller (discharge port) 15, a suction port (with adjustment valve) 16, and a suction hose 17. When the underwater motor 11 is started, water is sucked from the suction port (with strainer) 12 and discharged through the water absorption hose 13 and the stirring tube 14 through the impeller (diffusion port) 15. Due to this series of circulation flow rates, the small intake port (with adjustment valve) 16 becomes negative pressure, and air is introduced through the intake hose 17. This air is sent to the stirring cylinder 14, and water and air are pulverized and mixed to form fine bubbles, which are discharged and diffused from the impeller (diffusion port) 15 into the water. The power supply is connected to a connection box 19 to which a power cable 18 of the motor 5 and the underwater motor 11 is supplied with power.

振動波発生装置及び酸素発生装置の要部説明図である。It is principal part explanatory drawing of a vibration wave generator and an oxygen generator. 振動波発生装置及び電気分解酸素発生装置(水電解電極)の組合せ図。The combination figure of a vibration wave generator and an electrolysis oxygen generator (water electrolysis electrode). 振動波発生装置及び電気分解酸素発生装置(水電解電極)と自然エネルギー(ソーラー、風力等)発電装置との組合せ図。The combination figure of a vibration wave generator, an electrolysis oxygen generator (water electrolysis electrode), and a natural energy (solar, wind power, etc.) power generator.

1・・・アオコ制御装置、2・・・フロート、3・・・筏形基台、4・・・基台部、5・・・モーター、6・・・シャフト、7・・・ギヤボックス、8・・・攪拌翼(水平配置)、9・・・攪拌翼(垂直配置)、9a・・・振動翼、9b・・・流動翼、10・・・酸素発生装置、11・・・水中モーター、12・・・吸込み口(ストレーナー付)、13・・・吸水ホース、14・・・攪拌筒、15・・・インペラー(吐出口)、16・・・吸気口(調整弁付)、17・・・吸気ホース、18・・・電源ケーブル、19・・・結線ボックス
20・・・電気分解酸素発生装置(水電解電極)、21・・・自然エネルギー発電、22・・・充放電制御装置
DESCRIPTION OF SYMBOLS 1 ... Blue control device, 2 ... Float, 3 ... Vertical base, 4 ... Base part, 5 ... Motor, 6 ... Shaft, 7 ... Gear box, DESCRIPTION OF SYMBOLS 8 ... Stirring blade (horizontal arrangement), 9 ... Stirring blade (vertical arrangement), 9a ... Vibration blade, 9b ... Fluid blade, 10 ... Oxygen generator, 11 ... Submersible motor , 12 ... Suction port (with strainer), 13 ... Water absorption hose, 14 ... Stirring cylinder, 15 ... Impeller (discharge port), 16 ... Air intake port (with adjusting valve), 17. ..Intake hose, 18 ... Power cable, 19 ... Connection box 20 ... Electrolytic oxygen generator (water electrolysis electrode), 21 ... Natural energy power generation, 22 ... Charge / discharge control device

Claims (3)

フロートを備える基台に、振動波発生装置と酸素発生装置とを取り付けた装置を利用してアオコの発生を抑制するアオコ制御方法であって、
前記振動波発生装置は、回転軸に垂直に配され、回転軸の回転とともに水を揺動させる振動作用を生じさせる、扁平なラグビーボール状に形成された振動翼と、前記回転軸に斜めに交差して配され、回転軸の回転とともに水に連続的な流れを発生させる流動翼とからなる攪拌翼と、攪拌翼を回転させる動力とを備え、
前記基台により支持して前記振動波発生装置と前記酸素発生装置とを湖中に設置し、
夏季等のアオコが発生する水圏環境下においては、前記振動波発生装置と前記酸素発生装置とを併用稼働させて、湖底からの栄養塩類の溶出を抑制してアオコの発生を防止または軽減し、
冬季等のアオコが発生しない水圏環境下においては、前記振動波発生装置のみを稼働させ、湖底からの栄養塩類を溶出、回収することを特徴とするアオコ制御方法。
It is a blue-spot control method that suppresses the occurrence of blue-spots using a device in which a vibration wave generator and an oxygen generator are attached to a base including a float,
The vibration wave generator is arranged perpendicular to the rotation shaft, and generates a vibration action that causes water to swing with rotation of the rotation shaft. The vibration blade is formed in a flat rugby ball shape, and is inclined to the rotation shaft. A stirring blade composed of a fluid blade that is arranged to intersect and generates a continuous flow in the water along with the rotation of the rotating shaft, and a power for rotating the stirring blade,
The vibration wave generator and the oxygen generator are installed in a lake supported by the base,
In the aquatic environment where aquatic is generated in summer, etc., the vibration wave generator and the oxygen generator are operated in combination to prevent or reduce the occurrence of aquatic by suppressing the elution of nutrients from the lake bottom,
A water-bloom control method comprising operating only the vibration wave generator and eluting and recovering nutrient salts from the bottom of a lake in aquatic environments where water-bloom does not occur such as in winter.
前記酸素発生装置として、水の電気分解による酸素発生装置を用いることを特徴とする請求項1記載のアオコ制御方法。 2. The method of controlling a sea urchin according to claim 1, wherein an oxygen generator by electrolysis of water is used as the oxygen generator. 湖中の深さ方向において、水面に近い側と水面から離れる側とにそれぞれ攪拌翼を備え、上側の攪拌翼は回転軸が垂直配置され、下側の攪拌翼は回転軸が水平配置された振動波発生装置を用いることを特徴とする請求項1記載のアオコ制御方法。   In the depth direction in the lake, a stirring blade is provided on each of the side closer to the water surface and the side away from the water surface. The upper stirring blade has a rotating shaft arranged vertically, and the lower stirring blade has a rotating shaft arranged horizontally. 2. The method of controlling a sea urchin according to claim 1, wherein a vibration wave generator is used.
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JP3980557B2 (en) * 2002-09-24 2007-09-26 有限会社モブロン設計事務所 Liquid flow generator
JP4600924B2 (en) * 2005-02-10 2010-12-22 滋賀県 Hydrogen recovery type electrolytic water quality improvement device

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101982989B1 (en) * 2018-12-13 2019-05-27 김석이 Floating type Green tide Removal device

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