JP2018148872A - Purification system - Google Patents

Purification system Download PDF

Info

Publication number
JP2018148872A
JP2018148872A JP2017077237A JP2017077237A JP2018148872A JP 2018148872 A JP2018148872 A JP 2018148872A JP 2017077237 A JP2017077237 A JP 2017077237A JP 2017077237 A JP2017077237 A JP 2017077237A JP 2018148872 A JP2018148872 A JP 2018148872A
Authority
JP
Japan
Prior art keywords
water
microbubble
purification
discharge device
area
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
Application number
JP2017077237A
Other languages
Japanese (ja)
Other versions
JP6186534B1 (en
Inventor
哲雄 野村
Tetsuo Nomura
哲雄 野村
美恵 千葉
Mie Chiba
美恵 千葉
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Nano Device Co Ltd
Original Assignee
Nano Device Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Nano Device Co Ltd filed Critical Nano Device Co Ltd
Application granted granted Critical
Publication of JP6186534B1 publication Critical patent/JP6186534B1/en
Priority to PCT/JP2018/009709 priority Critical patent/WO2018168844A1/en
Priority to CN201880004200.0A priority patent/CN109936980B/en
Publication of JP2018148872A publication Critical patent/JP2018148872A/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01KANIMAL HUSBANDRY; CARE OF BIRDS, FISHES, INSECTS; FISHING; REARING OR BREEDING ANIMALS, NOT OTHERWISE PROVIDED FOR; NEW BREEDS OF ANIMALS
    • A01K61/00Culture of aquatic animals
    • A01K61/60Floating cultivation devices, e.g. rafts or floating fish-farms
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01KANIMAL HUSBANDRY; CARE OF BIRDS, FISHES, INSECTS; FISHING; REARING OR BREEDING ANIMALS, NOT OTHERWISE PROVIDED FOR; NEW BREEDS OF ANIMALS
    • A01K63/00Receptacles for live fish, e.g. aquaria; Terraria
    • A01K63/04Arrangements for treating water specially adapted to receptacles for live fish
    • 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/80Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in fisheries management
    • Y02A40/81Aquaculture, e.g. of fish

Abstract

PROBLEM TO BE SOLVED: To provide an open non-circulation type culture system capable of suppressing proliferation (reproduction) of bacteria, and increasing a dissolved oxygen amount in the whole area of a cultivation area.SOLUTION: A part of an open river 1 is set as a cultivation area 2 having a rectangular shape in a plane view, and each discharge device 3 ia arranged respectively on two facing sides 2a, 2b which are parallel to a flow in four sides partitioning the cultivation area 2. By introducing air into each discharge device 3, bubbles having various kind of particle sizes of mm, μm and nm units are formed and intermingled into water. As a result of interminglement, dissolved oxygen is improved greatly.SELECTED DRAWING: Figure 1

Description

本発明は、自然の河川、池、海などの開放された領域の一部を浄化するシステムに関する   The present invention relates to a system for purifying a part of an open area such as a natural river, pond, or sea.

浄化システムの一態様として、陸上において水を循環させて再利用しながら飼育する閉鎖循環式養殖システムが広く採用されている。   As an embodiment of the purification system, a closed circulation culture system that circulates water on the land and breeds it while reusing is widely adopted.

例えば、特許文献1は本発明者が提案したものであり、この特許文献1には、閉鎖循環式養殖システムとして、水槽内の1つのコーナから対向するコーナに向かって微細気泡を含んだ水を送りだすポンプとノズルを配置し、前記対向するコーナには水槽内に循環流を形成するためのパドルミキサーを配置し、更に水槽内にはナノ銀粒子を担持した抗菌部材を吊下げ支持した構造が開示されている。   For example, Patent Document 1 has been proposed by the present inventor. In Patent Document 1, as a closed-circulation aquaculture system, water containing fine bubbles from one corner in a water tank toward the opposite corner is provided. A pump and a nozzle to be sent out are arranged, a paddle mixer for forming a circulating flow in the water tank is arranged in the opposite corner, and a structure in which an antibacterial member carrying nano silver particles is suspended and supported in the water tank. It is disclosed.

また特許文献2には、海水を循環させながら海水中のアンモニア等の窒素成分を除去する閉鎖循環式養殖システムとして、海水中の固形物を取り除く物理的ろ過部と、海水を電気分解して活性塩素種を発生させると共にこの活性塩素種で海水中の窒素成分を除去する電気分解・窒素除去部と、活性塩素種を中和する塩素中和部とを、海水の流れ方向に沿ってこの順に配置したものが提案されている。   Patent Document 2 discloses a closed-circulation aquaculture system that removes nitrogen components such as ammonia in seawater while circulating seawater, a physical filtration unit that removes solids in seawater, and electrolysis of seawater to activate it. An electrolysis / nitrogen removal unit that generates chlorine species and removes nitrogen components in seawater with this active chlorine species, and a chlorine neutralization unit that neutralizes active chlorine species in this order along the flow direction of seawater Arrangements have been proposed.

特許文献3には、複数の所定長さの養殖用パイプを接続して循環路とする閉鎖循環式養殖システムとして、観察用窓を設け、養殖用パイプ内の状態を観察するものが提案されている。   Patent Document 3 proposes a closed circulation type aquaculture system in which a plurality of aquaculture pipes of a predetermined length are connected to form a circulation path, and an observation window is provided to observe the state in the aquaculture pipe. Yes.

特許文献4には、魚介類を養殖する陸上養殖施設として、物理浄化処理手段、生物浄化処理手段、化学浄化処理手段及び電気化学浄化処理手段を備えたものが提案されている。   Patent Document 4 proposes an on-shore aquaculture facility for culturing fish and shellfish that includes a physical purification processing means, a biological purification processing means, a chemical purification processing means, and an electrochemical purification processing means.

特許文献5には、ナノバブルを含む水を生体表面に接触させることにより、生体の疲労回復を行うナノバブル利用生体疲労回復方法が提案されている。   Patent Document 5 proposes a nanobubble-based biological fatigue recovery method that recovers fatigue of a living body by bringing water containing nanobubbles into contact with the surface of the living body.

特許文献6には、海上、湖沼、河川、汽水域等の一般水域の水質浄化用法として、変動する自然エネルギーを圧縮空気の形で貯蔵し空気を高分子樹脂フィルムに生成されたクレーズに強制的に透過させることにより自然に近い状態で溶存酸素量を増加させる方法が提案されている。   In Patent Document 6, as a method for purifying water in general water areas such as sea, lakes, rivers, brackish water areas, fluctuating natural energy is stored in the form of compressed air, and the air is forced to craze generated in a polymer resin film. A method has been proposed in which the amount of dissolved oxygen is increased in a state close to nature by permeating it into the water.

特許文献7には、発泡・凝縮工程を複数回繰り返す微細化方法が提案され、この微細化方法において、セラミック表面に担持したナノ銀粒子に水を接触させることで、ナノ銀粒子が保持するゼータ電位により菌類や藻類を破壊・除去することが記載されている。   Patent Document 7 proposes a micronization method in which the foaming / condensation process is repeated a plurality of times. In this micronization method, water is brought into contact with the nanosilver particles supported on the ceramic surface, thereby holding the zeta that is retained by the nanosilver particles. It describes that fungi and algae are destroyed and removed by electric potential.

特許文献8には、ナノバブルの製造に関する基本的な以下の内容が開示されている。先ず、鉄イオンやナトリウムイオンなどの電解質イオンが混入した高い電気伝導度の水溶液中に10〜50μmの微小気泡を作成する。次いで、上記の微小気泡に対し物理的刺激を加えることで、急激に微小気泡を直径50〜500nmに縮小(ナノ化)する。このナノ化した気泡は急激に縮小したため、単位面積当たりの電荷量が大幅に増加して気液界面に吸着した水素イオンや水酸化物イオンの静電気的な反発力が働き、また水素イオン、水酸化物イオン及び電解質イオンが気液界面の縮小に伴って微小な体積中に高濃度に濃縮してナノ化した微小気泡周囲を囲む殻として働くため、特有の機能を発揮すると解釈されている。   Patent Document 8 discloses the following basic contents regarding the production of nanobubbles. First, 10-50 μm microbubbles are formed in an aqueous solution having high electrical conductivity mixed with electrolyte ions such as iron ions and sodium ions. Next, by applying physical stimulation to the microbubbles, the microbubbles are rapidly reduced (nanoized) to a diameter of 50 to 500 nm. Since these nano-sized bubbles have shrunk rapidly, the amount of charge per unit area is greatly increased, and electrostatic repulsion of hydrogen ions and hydroxide ions adsorbed on the gas-liquid interface works. It is interpreted that the oxide ion and the electrolyte ion function as a shell surrounding the microbubbles which are concentrated into a minute volume and nanonized as the gas-liquid interface shrinks, and thus exhibit a unique function.

特許第6092454号公報Japanese Patent No. 6092454 特開2003−274796号公報JP 2003-27496 A 特開2005−021142号公報JP 2005-021142 A 特開2014−209899号公報JP 2014-209899 A 特開2007−054655号公報JP 2007-045455 A 特開2006−320259号公報JP 2006-320259 A 特開2014−198333号公報JP 2014-198333 A 特許第4144669号公報Japanese Patent No. 4144669

閉鎖循環式養殖システムは、気候・赤潮などの外的要因による影響が少なく生産性に優れ、水温の調整が可能なため養殖期間の短縮化を図ることができ、排水が殆どでないため環境への影響が少なく、区画漁業権等の漁業法の制約を受けないなどの利点がある一方、ウィルスや魚病等が飼育水槽内に持ち込まれると、飼育魚が全滅してしまう。   The closed-circulation aquaculture system is less affected by external factors such as climate and red tide, is highly productive, and can adjust the water temperature to shorten the cultivation period. While there are advantages such as being less affected and not subject to restrictions on fishery laws such as parcel fishery rights, if a virus, fish disease, etc. are brought into the breeding aquarium, the farmed fish will be annihilated.

これに対し、河川や水路などをそのまま利用した開放非循環式養殖システムにあっては、水質の管理が難しく、水流の速度が遅い状況では溶存酸素量が不足し量産に向かない場合が多い。   On the other hand, in an open non-circulation aquaculture system that uses rivers and waterways as they are, it is difficult to manage the water quality, and the amount of dissolved oxygen is often insufficient in situations where the water flow rate is slow, which is not suitable for mass production.


特許文献1は、閉鎖された水槽に適用されるものであり、これをそのまま河川などの開放された領域に適用することはできない。また特許文献1では1つのコーナのみにポンプとノズルを設けているが、本願発明は領域を区画する辺のうち対向する2つの辺のそれぞれに相手方の辺に向かって斜め且つ互いに打ち消し合わない方向に微細気泡を含んだ水を吐出する吐出装置を複数設けている。特許文献1は流れのない水槽内に流れを形成するため、対向するコーナにも吐出装置を設けると、互いに吐出装置からの流れが打ち消し合って循環流を形成することが出来ない。

Patent Document 1 is applied to a closed water tank, and cannot be applied to an open area such as a river as it is. Further, in Patent Document 1, a pump and a nozzle are provided in only one corner. However, in the present invention, each of two opposing sides among the sides defining the region is inclined toward the other side and does not cancel each other. A plurality of discharge devices for discharging water containing fine bubbles are provided. Since Patent Document 1 forms a flow in a water tank without flow, if a discharge device is also provided at the opposite corner, the flows from the discharge devices cancel each other and a circulation flow cannot be formed.

特許文献2〜特許文献7に記載される河川や水路などをそのまま利用した開放非循環式養殖システムにあっては、水質の管理が難しく、水流の速度が遅い状況では溶存酸素量が不足し量産に向かない場合が多い。しかしながら、上記した何れの先行技術文献も、河川や水路などをそのまま利用した開放領域の浄化には有効ではない。   In the open non-circulation aquaculture system using the rivers and waterways described in Patent Document 2 to Patent Document 7 as they are, it is difficult to manage the water quality, and the amount of dissolved oxygen is insufficient in the situation where the water flow rate is slow. Often not suitable for. However, none of the above-described prior art documents is effective for purifying an open area using a river or a water channel as it is.

また、特許文献8では、水中に10〜50μmの微小気泡を作成する前に、当該水に電解質イオンを混入させている。電解質イオンは気泡が500nm以下のナノサイズになった際に、気液界面の縮小に伴って濃縮されナノ化した気泡周囲を取り囲む殻として働くのであるが、電解質イオンの溶け込み量が少ないと殻も強固にはならず、ナノサイズを維持できる期間も短くなる。 Moreover, in patent document 8, before producing 10-50 micrometers microbubble in water, the electrolyte ion is mixed in the said water. Electrolyte ions act as a shell that surrounds the bubble that is concentrated and nanonized as the gas-liquid interface shrinks when the bubble becomes nano-sized below 500 nm. However, if the amount of electrolyte ion penetration is small, the shell also The period during which the nano-size can be maintained is shortened.

上記の課題を解決するため本願発明は、河川、池、海などの開放された領域を一部を浄化するシステムであって、前記開放された領域の一部を平面視で矩形状をなす浄化領域として設定し、この浄化領域を区画する辺のうち対向する2つの辺のそれぞれに相手方の辺に向かって斜め且つ互いに打ち消し合わない方向に微細気泡を含んだ水を吐出する吐出装置が配置され、この吐出装置は、水中に直径500nm以上の微小気泡を発生させる微小気泡発生部と、この微小気泡発生部の下流側に配置される金属イオン付加部と、この金属イオン付加部の下流側に配置される微小気泡縮小部とからなり、前記金属イオン付加部には、アルカリ金属の酸化物、アルカリ土類金属の酸化物、第8〜10属元素の酸化物の少なくとも1つからなるセラミックが充填され、前記微小気泡縮小部には気泡を縮小させる力を作用させる流路が形成された構成である。   In order to solve the above problems, the present invention is a system for purifying a part of an open area such as a river, a pond, or the sea, wherein the part of the open area is rectangular in a plan view. A discharge device that discharges water containing fine bubbles in a direction that is oblique to the other side and does not cancel each other out is arranged on each of two opposing sides that define the purification region. The discharge device includes a microbubble generating unit that generates microbubbles having a diameter of 500 nm or more in water, a metal ion adding unit disposed on the downstream side of the microbubble generating unit, and a downstream side of the metal ion adding unit. The metal ion adding portion is a ceramic comprising at least one of an alkali metal oxide, an alkaline earth metal oxide, and an oxide of group 8 to 10 elements. There is filled, the said microbubble reduction unit is configured to channel applying a force to reduce the bubbles were formed.

前記浄化領域内には多孔質部材の表面にナノ銀粒子が担持された抗菌部材を配置してもよい。   An antibacterial member having nano silver particles supported on the surface of the porous member may be disposed in the purification region.

また、浄化領域を区画する辺の近傍に大気を水中に取り込むパドルミキサーを配置してもよい。このようにすることで、溶存酸素量を更に高めることができる。   Further, a paddle mixer that takes air into the water may be disposed in the vicinity of the side that defines the purification region. By doing in this way, the amount of dissolved oxygen can be further increased.

本発明に係る浄化システムによれば、河川などの開放された自然の水を利用したシステムであるので、エビや魚などにストレスがかからず病気等が発生しにくい。特に、浄化領域を矩形状に画定する辺のうち、対向する2つの辺の一方から他方に向かって強制的に微細気泡を含む水を噴出するため、溶存酸素量を高めることができる。
特に河川などの流れがある場合には、浄化領域のみならずその下流領域に浄化された水が流れるため、効果は更に高まる。
According to the purification system of the present invention, since it is a system that uses open natural water such as rivers, shrimp and fish are not stressed and diseases are not likely to occur. In particular, among the sides that define the purification region in a rectangular shape, water containing fine bubbles is forcibly ejected from one of two opposing sides toward the other, so that the amount of dissolved oxygen can be increased.
In particular, when there is a flow such as a river, the effect is further enhanced because the purified water flows not only in the purification region but also in the downstream region.

ノズルから噴出する水には、nmサイズの気泡、μmサイズの気泡、mmサイズの気泡など各種サイズの気泡が含まれているので、殺菌・滅菌効果の他に、養殖領域全域に亘って溶存酸素量を高く維持することが可能となる。 The water ejected from the nozzle contains bubbles of various sizes such as nm-size bubbles, μm-size bubbles, and mm-size bubbles, so in addition to the sterilization and sterilization effects, dissolved oxygen over the entire culture area The amount can be kept high.

また、浄化領域には常に新鮮な水が供給されるのであるが、万一水中に菌類や藻類が多量に含まれていても、多孔質部材の表面に担持されたナノ銀粒子と接触し、菌類や藻類が破壊・除去され、エビや養殖魚の全滅が生じる可能性が極めて少ない。特に、ノズルの上流側に濾過部を設け、この濾過部内に多孔質部材の表面にナノ銀粒子が担持された抗菌部材を収納する構成とした場合には、ナノ銀粒子と接触が確実に行われ、更に効果は高まる。 In addition, fresh water is always supplied to the purification region, but even if a large amount of fungi and algae are contained in the water, it comes into contact with the nano silver particles supported on the surface of the porous member, It is extremely unlikely that fungi and algae will be destroyed and removed, and shrimp and farmed fish will be destroyed. In particular, when a filtration part is provided on the upstream side of the nozzle and an antibacterial member in which nanosilver particles are supported on the surface of the porous member is housed in the filtration part, contact with the nanosilver particles is ensured. The effect is further enhanced.

本発明に係る浄化システムの平面図Plan view of the purification system according to the present invention 吐出装置の構成図Configuration diagram of dispensing device 微小気泡縮小部の構造を説明した断面図Sectional view explaining the structure of the microbubble reduction part ろ過材の斜視図Perspective view of filter media パドルミキサーの側面図Side view of paddle mixer

図1に示す実施例にあっては、水流が形成される河川に適用する例を示している。尚、本発明は河川に限らず水の流入と流出が自由な開放された領域、例えば池、湖、海、水路などにも適用できる。   In the embodiment shown in FIG. 1, an example applied to a river where a water flow is formed is shown. The present invention is not limited to rivers and can be applied to open areas where water can freely flow in and out, such as ponds, lakes, seas, and waterways.

図示例にあっては、開放された河川1の一部を平面視で矩形状をなす浄化領域2として設定し、この浄化領域2を区画する4つの辺のうち流れに平行な2つの対向する辺2a、2bのそれぞれに吐出装置3を配置している。   In the illustrated example, a part of the opened river 1 is set as a purification region 2 having a rectangular shape in plan view, and two of the four sides that define the purification region 2 are opposed to each other parallel to the flow. Discharge device 3 is arranged in each of sides 2a and 2b.

尚、浄化領域2を区画する4つの辺は壁や板等で形成されるものではなく、吐出装置3を配置する位置を決めるための架空の線であるが、この線に沿って養殖エビや養殖魚が逃げ出したり、外敵が入り込まないようにするための網を設けることができる。   The four sides that define the purification region 2 are not formed by walls or plates, but are fictitious lines for determining the position where the discharge device 3 is arranged. A net can be provided to prevent farmed fish from escaping and foreign enemies from entering.

吐出装置3は図2に示すように、筒状ケース1の一端を河川水などの入口4とし、他端を機能水の出口5としている。この実施例では入口4の径が出口5の径よりも大きく設定されている。   As shown in FIG. 2, the discharge device 3 has one end of the cylindrical case 1 as an inlet 4 for river water and the other end as an outlet 5 for functional water. In this embodiment, the diameter of the inlet 4 is set larger than the diameter of the outlet 5.

入口4に続く筒状ケース内には微小気泡発生部6が設けられ、この微小気泡発生部6内にはステンレスネットやステンレスウール7などが充填されている。ステンレスネットやステンレスウール7の代わりに金属網や多孔板などでもよい。   In the cylindrical case following the inlet 4, a microbubble generator 6 is provided, and the microbubble generator 6 is filled with stainless steel net, stainless wool 7, or the like. Instead of the stainless steel net or stainless steel wool 7, a metal net or a perforated plate may be used.

上記微小気泡発生部6の下流側には金属イオン付加部8が連続して設けられている。この金属イオン付加部8内には粒径1〜10mmのセラミック粒子9が充填されている。   A metal ion adding unit 8 is continuously provided downstream of the microbubble generating unit 6. The metal ion adding portion 8 is filled with ceramic particles 9 having a particle diameter of 1 to 10 mm.

セラミック粒子9としては、例えば、Si酸化物とAl酸化物を主成分とし、その他の成分として、NaやKなどのアルカリ金属酸化物、MgやCaなどのアルカリ土類金属酸化物、Fe、Co、Niなどの第8〜10族元素の酸化物が挙げられる。尚、Si酸化物とAl酸化物の合計は、90〜95wt%が好ましい。90wt%以下だとセラミックが脆くなって壊れやすくなる。   Examples of the ceramic particles 9 include Si oxide and Al oxide as main components, and other components such as alkali metal oxides such as Na and K, alkaline earth metal oxides such as Mg and Ca, Fe, Co, and the like. And oxides of Group 8 to 10 elements such as Ni. In addition, 90-95 wt% of the sum total of Si oxide and Al oxide is preferable. If it is 90 wt% or less, the ceramic becomes brittle and breaks easily.

セラミック粒子9には、TiやCrなどの遷移金属の酸化物やPなどの非金属の酸化物を含んでもよい。機能水を効果的に製造するには、セラミック粒子中のアルカリ土類金属の酸化物の含量は、アルカリ金属の酸化物の含量の25%以上(重量比)であることが望ましく、またセラミック粒子が第8〜10族元素に属する元素から少なくとも1種の元素の酸化物を0.1〜3重量%含むことが望ましい。   The ceramic particles 9 may include an oxide of a transition metal such as Ti or Cr or a non-metal oxide such as P. In order to effectively produce functional water, it is desirable that the content of the alkaline earth metal oxide in the ceramic particles is 25% or more (weight ratio) of the content of the alkali metal oxide. Preferably contains 0.1 to 3% by weight of an oxide of at least one element selected from elements belonging to Group 8 to Group 10 elements.

前記金属イオン付加部8の下流部は絞られて微小気泡縮小部(ノズル)10につながっている。微小気泡縮小部10は図3に示すように、隔壁11に複数のノズル孔12が形成され、その下流には合流した噴出流を平行に下流に導く直線状の縮小力作用部13が連続している。この縮小力作用部13ではケルビンヘルムホルツ不安定などの不安定環境を作り出すことで、微小気泡(マイクロバブル)が500nm以下のナノサイズまでに更に縮小される。   A downstream portion of the metal ion adding portion 8 is squeezed and connected to a microbubble reducing portion (nozzle) 10. As shown in FIG. 3, the microbubble reduction part 10 is formed with a plurality of nozzle holes 12 in the partition wall 11, and a linear reduction force action part 13 for guiding the merged jet flow downstream in parallel is provided downstream of the nozzle hole 12. ing. The reducing force acting unit 13 creates an unstable environment such as Kelvin Helmholtz instability, whereby microbubbles are further reduced to a nano size of 500 nm or less.

微小気泡に縮小力を作用する手段としては、特許文献8に開示されたような超音波、高速回転、圧縮・膨張などでもよいが、本実施例のように、金属イオン付加部6の下流部に微小気泡縮小部8を連続して設けることで、特別の動力を必要としないでナノバブルを作り出すことができる。   As means for applying the reducing force to the microbubbles, ultrasonic waves, high-speed rotation, compression / expansion, etc. as disclosed in Patent Document 8 may be used. However, as in this embodiment, the downstream portion of the metal ion addition unit 6 is used. By providing the microbubble reduction part 8 continuously, nanobubbles can be created without requiring special power.

以上において、入口4から微小気泡発生部6に導入された水はステンレスネットやステンレスウール7間を通過することによって、ミクロンサイズの微小気泡(マイクロバブル)が水中に形成される。尚、微小気泡(マイクロバブル)は原料水に別途空気を送り込まなくともキャビテーション現象によって自動的に発生する。   As described above, the water introduced from the inlet 4 to the microbubble generator 6 passes between the stainless steel net and the stainless wool 7, whereby micron-sized microbubbles (microbubbles) are formed in the water. Microbubbles are automatically generated by a cavitation phenomenon without sending air separately to the raw water.

微小気泡発生部6おいて生成されたミクロンサイズの微小気泡が混入した水は金属イオン付加部8に導入され、セラミック粒子と接触することで水中にセラミックを構成している金属酸化物から金属イオンが溶け込む。この金属イオンの濃度は微小気泡の気液界面において高くなっていると推定される。   Water mixed with micron-sized microbubbles generated in the microbubble generating unit 6 is introduced into the metal ion adding unit 8 and comes into contact with the ceramic particles to form metal ions from the metal oxide constituting the ceramic in the water. Melts. The concentration of this metal ion is estimated to be high at the gas-liquid interface of the microbubbles.

金属イオンとミクロンサイズの微小気泡を含んだ水はノズル12を介して微小気泡縮小部10の微小力作用部13に送りだされ、更に小さなナノバブル(50〜500nm)となって出口5から噴出する。   Water containing metal ions and micron-sized microbubbles is sent to the microforce acting part 13 of the microbubble reducing part 10 through the nozzle 12, and becomes smaller nanobubbles (50 to 500 nm) and ejects from the outlet 5. .

図示例では、微小気泡発生部6と金属イオン付加部8とを1つの容器内に連続的に配置したが、それぞれを別の容器に分離して配管などでつなげてもよい。また、微小気泡縮小部8の縮小力作用部13は単純な直線状流路としたが、ナノ化を促進する撹拌部材等を配置してもよい。   In the illustrated example, the microbubble generating unit 6 and the metal ion adding unit 8 are continuously arranged in one container, but each may be separated into another container and connected by piping or the like. Moreover, although the reduction force action part 13 of the microbubble reduction part 8 is a simple linear flow path, a stirring member or the like that promotes nano-ization may be disposed.

微小気泡縮小部(ノズル)10の軸線は、気泡が混入した水の噴出方向が相手方の辺から噴出される水と打ち消し合わない方向とする。河川のように上流から下流に水が流れている場合には、ノズル10の噴出方向は水の流れ方向に対して90°以下とするのが好ましい。この実施例にあっては、辺2aに配置された吐出装置3からの水が辺2bに配置された吐出装置3に向かい、辺2bに配置された吐出装置3からの水が辺2aに配置された吐出装置3に向かうようにし、流れに沿って連続的に蛇行する動きを形成している。   The axis of the microbubble reduction part (nozzle) 10 is set so that the direction of ejection of water mixed with bubbles does not cancel the water ejected from the other side. When water flows from upstream to downstream as in a river, the ejection direction of the nozzle 10 is preferably 90 ° or less with respect to the water flow direction. In this embodiment, water from the discharge device 3 disposed on the side 2a faces the discharge device 3 disposed on the side 2b, and water from the discharge device 3 disposed on the side 2b is disposed on the side 2a. It moves toward the discharged discharge device 3 and forms a continuous meandering movement along the flow.

また、浄化領域2内には所定数のろ過材20を間隔を開けて吊り下げ支持している。濾過材20は図4に示すように板材21の両面に溶岩などを細かく砕いた多孔質部材を収納したメッシュ袋22を取付け、更にこれらを紐23で連結したものとしている。多孔質部材の表面には前記した濾過部8内に充填した多孔質部材と同様にナノ銀粒子が担持されている。 A predetermined number of filter media 20 are suspended and supported in the purification region 2 at intervals. As shown in FIG. 4, the filter medium 20 has mesh bags 22 containing porous members obtained by finely pulverizing lava and the like attached to both surfaces of a plate material 21, and these are connected by strings 23. Nanosilver particles are supported on the surface of the porous member in the same manner as the porous member filled in the filtration unit 8 described above.

濾過材20の構造は上記に限るものではなく、浄化領域2を流れる水が効率良く接触することで、殺菌及び浄化が効果的に行えるものであればよい。 The structure of the filter medium 20 is not limited to the above, and any structure that can effectively sterilize and purify the water flowing through the purification region 2 in an efficient contact with the filter medium 20 may be used.

また、浄化領域2を区画する辺2a、2bにパドルミキサー24が設けられている。実施例では吐出装置3の下流に隣接して配置しているが、配置する箇所はこれに限らない。 A paddle mixer 24 is provided on the sides 2 a and 2 b that define the purification region 2. In the embodiment, it is arranged adjacent to the downstream of the discharge device 3, but the place to arrange is not limited to this.

パドルミキサー24は図5に示すように、辺2a、2bに直交する軸25に複数の羽根26を取付け、羽根26の回転により水中に大気(酸素)を取り入れる。 As shown in FIG. 5, the paddle mixer 24 has a plurality of blades 26 attached to a shaft 25 orthogonal to the sides 2 a and 2 b, and the air (oxygen) is taken into the water by the rotation of the blades 26.

本発明に係る浄化システムは、エビや各種魚類や酸素を必要とする水生植物の養殖に限らず、水の浄化自体に利用することができる。   The purification system according to the present invention is not limited to the cultivation of shrimp, various fish, and aquatic plants that require oxygen, but can also be used for water purification itself.

1…河川、2…浄化領域、2a、2b…浄化領域を区画する辺、3…吐出装置、4…吐出装置の入口、5…吐出装置の出口、6…微小気泡発生部、7…ステンレスウール、8…金属イオン付加部、9…セラミック粒子、10…微小気泡縮小部、11…隔壁、12…ノズル孔、13…縮小力作用部、20…濾過材、21…板材、22…メッシュ袋、23…紐、24…パドルミキサー、25…軸、26…羽根。   DESCRIPTION OF SYMBOLS 1 ... River, 2 ... Purification | cleaning area | region, 2a, 2b ... Side which divides purification | cleaning area | region 3 ... Discharge apparatus, 4 ... Inlet of discharge apparatus, 5 ... Outlet of discharge apparatus, 6 ... Microbubble generation part, 7 ... Stainless steel wool 8 ... Metal ion addition part, 9 ... Ceramic particles, 10 ... Microbubble reduction part, 11 ... Partition, 12 ... Nozzle hole, 13 ... Reduction force action part, 20 ... Filter material, 21 ... Plate material, 22 ... Mesh bag, 23 ... string, 24 ... paddle mixer, 25 ... shaft, 26 ... blade.

Claims (4)

河川、池、海などの開放された領域を一部を浄化するシステムであって、前記開放された領域の一部を平面視で矩形状をなす浄化領域として設定し、この浄化領域を区画する辺のうち対向する2つの辺のそれぞれに相手方の辺に向かって斜め且つ互いに打ち消し合わない方向に微細気泡を含んだ水を吐出する吐出装置が配置され、この吐出装置は、水中に直径500nm以上の微小気泡を発生させる微小気泡発生部と、この微小気泡発生部の下流側に配置される金属イオン付加部と、この金属イオン付加部の下流側に配置される微小気泡縮小部とからなり、前記金属イオン付加部には、アルカリ金属の酸化物、アルカリ土類金属の酸化物、第8〜10属元素の酸化物の少なくとも1つからなるセラミックが充填され、前記微小気泡縮小部には気泡を縮小させる力を作用させる流路が形成されていることを特徴とする浄化システム。   A system for partially purifying open areas such as rivers, ponds, and seas, wherein a part of the open area is set as a purification area having a rectangular shape in plan view, and the purification area is partitioned. A discharge device that discharges water containing fine bubbles is arranged in each of two opposite sides of the side in a direction that is oblique to the other side and does not cancel each other, and the discharge device has a diameter of 500 nm or more in water. Consisting of a microbubble generating part for generating a microbubble, a metal ion adding part arranged on the downstream side of the microbubble generating part, and a microbubble reducing part arranged on the downstream side of the metal ion adding part, The metal ion addition part is filled with a ceramic made of at least one of an alkali metal oxide, an alkaline earth metal oxide, and an oxide of group 8 to 10 elements, and the microbubble reduction part is Purification system wherein the flow path for applying a force to reduce the bubbles are formed. 請求項1に記載の浄化システムにおいて、前記浄化領域内には多孔質部材の表面にナノ銀粒子が担持された抗菌部材が配置されていることを特徴とする浄化システム。   The purification system according to claim 1, wherein an antibacterial member having nano silver particles supported on the surface of a porous member is disposed in the purification region. 請求項1に記載の浄化システムにおいて、前記対向する2つの辺の近傍には大気を水中に取り込むパドルミキサーが配置されることを特徴とする浄化システム。   The purification system according to claim 1, wherein a paddle mixer that takes air into water is disposed in the vicinity of the two opposing sides. 請求項1乃至3の何れかに記載の浄化システムにおいて、前記開放された領域の一部は、養殖に利用されることを特徴とする浄化システム。   4. The purification system according to claim 1, wherein a part of the opened area is used for aquaculture.
JP2017077237A 2017-03-14 2017-04-10 Purification system Active JP6186534B1 (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
PCT/JP2018/009709 WO2018168844A1 (en) 2017-03-14 2018-03-13 Purification system
CN201880004200.0A CN109936980B (en) 2017-03-14 2018-03-13 Purification system

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
JP2017048010 2017-03-14
JP2017048010 2017-03-14

Publications (2)

Publication Number Publication Date
JP6186534B1 JP6186534B1 (en) 2017-08-23
JP2018148872A true JP2018148872A (en) 2018-09-27

Family

ID=59678229

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2017077237A Active JP6186534B1 (en) 2017-03-14 2017-04-10 Purification system

Country Status (3)

Country Link
JP (1) JP6186534B1 (en)
CN (1) CN109936980B (en)
WO (1) WO2018168844A1 (en)

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2011020005A (en) * 2009-07-13 2011-02-03 Dainichi Kogyo:Kk Nano bubble generator
JP2011230055A (en) * 2010-04-27 2011-11-17 Opt Creation:Kk Method and system for producing nanobubble fucoidan water
JP2013523448A (en) * 2010-07-15 2013-06-17 コリア・インスティテュート・オブ・マシナリー・アンド・マテリアルズ Swivel unit-based microbubble generator
JP6092454B1 (en) * 2016-09-20 2017-03-08 創美環境技研合同会社 Closed circulation aquaculture system
JP6127196B1 (en) * 2016-12-26 2017-05-10 創美環境技研合同会社 Functional water production apparatus and production method

Family Cites Families (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4144669B2 (en) * 2004-03-05 2008-09-03 独立行政法人産業技術総合研究所 Method for producing nanobubbles
US7997563B2 (en) * 2005-01-13 2011-08-16 National University Corporation University Of Tsukuba Micro-bubble generator, vortex breakdown nozzle for micro-bubble generator, vane swirler for micro-bubble generator, micro-bubble generating method, and micro-bubble applying device
CN101007244A (en) * 2006-01-23 2007-08-01 中岛竹志 Preparation method of active liquid containing micro-gas and implementation method using said liquid
CN201444821U (en) * 2009-05-12 2010-05-05 南通市吉腾鼓风机有限公司 Micro-porous oxygen feeding plate
CN103112959B (en) * 2011-11-16 2016-08-24 深圳市锦源新能科技有限公司 Nanometer micro bubble generation device
KR20150005010A (en) * 2013-07-04 2015-01-14 이주봉 Apparatus for producing sterilized water comprising chlorine and ozone
KR20150040134A (en) * 2013-10-04 2015-04-14 (주)범용테크놀러지 Nano bubble generator

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2011020005A (en) * 2009-07-13 2011-02-03 Dainichi Kogyo:Kk Nano bubble generator
JP2011230055A (en) * 2010-04-27 2011-11-17 Opt Creation:Kk Method and system for producing nanobubble fucoidan water
JP2013523448A (en) * 2010-07-15 2013-06-17 コリア・インスティテュート・オブ・マシナリー・アンド・マテリアルズ Swivel unit-based microbubble generator
JP6092454B1 (en) * 2016-09-20 2017-03-08 創美環境技研合同会社 Closed circulation aquaculture system
JP6127196B1 (en) * 2016-12-26 2017-05-10 創美環境技研合同会社 Functional water production apparatus and production method

Also Published As

Publication number Publication date
JP6186534B1 (en) 2017-08-23
CN109936980A (en) 2019-06-25
CN109936980B (en) 2021-11-02
WO2018168844A1 (en) 2018-09-20

Similar Documents

Publication Publication Date Title
JP6762467B2 (en) Aeration device
RU2553900C2 (en) Microbubble generator and device for microbubble generation
US9061925B2 (en) Liquid treatment methods and apparatus
JP5067695B2 (en) Ballast water treatment equipment
WO2004016344A1 (en) Minute air bubble-containing liquid matter and device for manufacturing the liquid matter
CN103562142A (en) Apparatus for generating fine bubbles having a positive charge and water treatment apparatus using same
KR101702345B1 (en) Apparatus and Method for Removing Algae
JP6092454B1 (en) Closed circulation aquaculture system
JP6186534B1 (en) Purification system
JP2003144002A (en) Container for transporting live fish
JP2000167575A (en) Apparatus and method for purifying water
KR101980335B1 (en) Total layer circulation injection system for water purifying
JP6047518B2 (en) Water quality improvement method and apparatus
JP5584869B1 (en) Sterilization treatment apparatus and sterilization treatment method
JP7121399B2 (en) Fish and shellfish culture water purification device, fish and shellfish culture device, and method for purifying fish and shellfish culture water
JP6429827B2 (en) Raw water treatment equipment
KR101953854B1 (en) Sulfur reactor for making of artificial sea water
JP3749156B2 (en) Liquid quality reformer
JP5589170B1 (en) Sterilization treatment apparatus and sterilization treatment method
AU2012203894B2 (en) Ballast water treatment methods and apparatus
JP2021079324A (en) Denitration treatment apparatus
KR20140085706A (en) Ballast water management system for Ship

Legal Events

Date Code Title Description
A871 Explanation of circumstances concerning accelerated examination

Free format text: JAPANESE INTERMEDIATE CODE: A871

Effective date: 20170428

A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20170428

A975 Report on accelerated examination

Free format text: JAPANESE INTERMEDIATE CODE: A971005

Effective date: 20170612

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20170725

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20170731

R150 Certificate of patent or registration of utility model

Ref document number: 6186534

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150

S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

S533 Written request for registration of change of name

Free format text: JAPANESE INTERMEDIATE CODE: R313533

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250