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JP7394452B2 - Algae removal equipment and algae treatment system - Google Patents
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JP7394452B2 - Algae removal equipment and algae treatment system - Google Patents

Algae removal equipment and algae treatment system Download PDF

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JP7394452B2
JP7394452B2 JP2020034505A JP2020034505A JP7394452B2 JP 7394452 B2 JP7394452 B2 JP 7394452B2 JP 2020034505 A JP2020034505 A JP 2020034505A JP 2020034505 A JP2020034505 A JP 2020034505A JP 7394452 B2 JP7394452 B2 JP 7394452B2
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吉男 藤岡
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特許法第30条第2項適用 (1)試験の実施による公開 試験日 令和1年7月1日から11月30日 試験場所 千波湖(茨城県水戸市千波町3080)Application of Article 30, Paragraph 2 of the Patent Act (1) Publication by conducting a test Test date: July 1, 2020 to November 30, 2020 Test location: Senba Lake (3080 Chinaba-cho, Mito City, Ibaraki Prefecture)

本発明は、藻類除去装置及び藻類処理システムに係り、特に湖沼や池等の閉鎖水域に発生した藻類を収集する藻類収集手段を備えた藻類除去装置及び藻類収集手段で収集した藻類を回収した後、最終的に処理するまでの藻類処理システムに関する。 The present invention relates to an algae removal device and an algae treatment system, and in particular to an algae removal device equipped with an algae collection means for collecting algae generated in a closed water area such as a lake or pond, and after collecting algae collected by the algae collection means. , concerning algae treatment systems up to final treatment.

近年、工業の発展や人口の増加などにより、湖沼や池等の閉鎖水域において水中のリンや窒素の栄養分濃度が増加し、閉鎖水域が富栄養化状態になり易い。この結果、アオコや赤潮等と呼ばれる植物性プランクトンである藻類が大量発生し、水が緑色や赤色に濁ってしまう現象がしばしば見られる。 In recent years, due to industrial development and population growth, the concentration of nutrients such as phosphorus and nitrogen in water in closed water bodies such as lakes and ponds has increased, and closed water bodies are likely to become eutrophic. As a result, large amounts of algae, which are phytoplankton, called blue-green algae or red tide occur, often turning the water cloudy green or red.

富栄養化した水から速やかに栄養分を取り除くことができれば、水草や適度な植物性プランクトンで水を浄化することは可能である。しかし、水に溶けた栄養分を速やかに取り除くことは難しく、アオコや赤潮等の藻類が大量発生し易い。 If nutrients can be quickly removed from eutrophic water, it is possible to purify the water with aquatic plants and a moderate amount of phytoplankton. However, it is difficult to quickly remove nutrients dissolved in water, and algae such as blue-green algae and red tide tend to grow in large quantities.

大量発生したアオコや赤潮等の藻類を放置すると、その水域の酸素濃度が低下して魚が死んだり、水辺やその水域の水を水源とする水道水に異臭がしたりする被害が発生する。この為、閉鎖性水域が富栄養化する原因を改善すると同時に、水中のこれらの藻類を排除する必要がある。 If large amounts of algae such as blue-green algae and red tide are left untreated, the oxygen concentration in the water area will drop, causing fish to die and causing damage such as strange odors to the water's edge and tap water sourced from the water area. For this reason, it is necessary to eliminate these algae in the water while simultaneously improving the causes of eutrophication in closed water bodies.

例えば藻類の代表例であるアオコは、比較的に球状な藍藻類(数ミクロン程度のミクロシスチス:Microcystisが主な構成)であり、細胞内のガス胞によって水面から数cm程度下の表層水中に浮遊している。そして、アオコが大量発生すると、数十~数百μmスケールの立体構造を有するアオコの群体がマット状になって水面を覆う。アオコの群体は数百以上の細胞が一定の規則性を有して集合したものである。このような群体状のアオコの処理方法としては、例えば特許文献1や特許文献2がある。 For example, blue-green algae, which is a typical example of algae, is a relatively spherical blue-green algae (mainly composed of Microcystis of several microns), which floats in the surface water several centimeters below the water surface due to intracellular gas vesicles. are doing. When a large amount of blue-green algae occurs, colonies of blue-green algae with a three-dimensional structure on the scale of tens to hundreds of micrometers form a mat and cover the water surface. A colony of blue-green algae is an aggregation of hundreds or more cells with a certain regularity. Examples of methods for treating such colonies of blue-green algae include Patent Document 1 and Patent Document 2.

特許文献1では、取水ポンプで吸い込んだ群体状のアオコを含む水を、超音波照射器に通してアオコを破壊することによりアオコの比重を重くした後、遠心濃縮機及び遠心脱水機にかけて脱水して固形物化することで、閉鎖性水域からアオコを効率よく回収する方法が提案されている(超音波方式)。 In Patent Document 1, water containing colonies of blue-green algae sucked in by a water intake pump is passed through an ultrasonic irradiator to destroy the blue-green algae to increase the specific gravity of the blue-green algae, and then subjected to a centrifugal concentrator and a centrifugal dehydrator to dehydrate the water. A method has been proposed to efficiently collect blue-green algae from closed bodies of water by turning it into a solid substance (ultrasonic method).

また、特許文献2では、取水ポンプで吸い込んだ群体状のアオコを含む水を、筒体の両端から対向噴射させて筒体内で水を衝突させることにより、群体状のアオコを細かく分断することが提案されている(対向噴射方式)。また、特許文献2には、アオコのガス胞を破壊して沈降し易くした後、元の閉鎖性水域に戻すことが提案されている。アオコの群体構造を細かく分断し、またガス胞を破壊して沈降し易くして閉鎖性水域に戻せば、閉鎖性水域に存在する動物プランクトンによる捕食が促進され、閉鎖性水域におけるアオコの増殖を抑制することができる。 Furthermore, in Patent Document 2, water containing colonies of algal blooms sucked in by a water intake pump is injected from both ends of a cylindrical body in opposite directions, and the water collides within the cylinder, thereby breaking up the colonies of algal blooms into small pieces. Proposed (opposite injection method). Further, Patent Document 2 proposes that after destroying the gas vesicles of algae to make it easier to settle, the algae can be returned to its original closed water area. If the colony structure of blue-green algae is divided into small pieces, and the gas vesicles are destroyed to make it easier to settle and returned to the closed water area, predation by zooplankton existing in the closed water body will be promoted, and the proliferation of algae in the closed water area will be promoted. Can be suppressed.

このように、閉鎖水域からアオコを採取した後のアオコ処理に関しては各種の提案がなされている。しかし、閉鎖水域に発生したアオコを如何に効率的に収集して回収するかに関する技術は十分とは言えない。 As described above, various proposals have been made regarding the treatment of algal blooms after they have been collected from closed water bodies. However, technology regarding how to efficiently collect and recover algal blooms that occur in closed water bodies is not sufficient.

例えば、特許文献3には、藻類を衝撃で破壊する衝撃殺藻装置を備えた水質保全装置が開示され、川の被保全水域に設置された事例が開示されている。この水質保全装置は、表層水中に含まれる藻類を水質保全装置の衝撃殺藻装置に導くための誘導手段を備えている。 For example, Patent Document 3 discloses a water quality conservation device equipped with an impact algaecide device that destroys algae by impact, and discloses an example in which the device is installed in a water area of a river to be conserved. This water quality maintenance device is equipped with a guide means for guiding algae contained in surface water to the impact algaecide device of the water quality maintenance device.

この誘導手段は、河川の上流側への表層水の流れを遮る上流側フェンスと、下流側への表層水の流れを遮る下流側フェンスと、上流側フェンスに逆ハの字状に向いており、上流側から下流側への風が吹いたときに表層水を水質保全装置の取水口に導く導流フェンスと、表層水を導流フェンスから衝撃殺藻装置に導く水路とで構成されている。 This guiding means is oriented in an inverted V-shape to the upstream fence that blocks the flow of surface water to the upstream side of the river, the downstream fence that blocks the flow of surface water to the downstream side, and the upstream fence. , consists of a diversion fence that guides surface water to the water intake of the water quality maintenance device when the wind blows from the upstream side to the downstream side, and a channel that guides surface water from the diversion fence to the impact algaecide device. .

これにより、河川の下流側から上流側に吹く風につられて表層水が流され、表層水中の藻類が上流側フェンス近傍に集められ、その後、上流側から下流側に吹く風につられて表層水が流され、上流側フェンス近傍に集められた藻類の大部分が導流フェンスを介して取水口に取り込まれるというものである。即ち、特許文献3の誘導手段は、上流側から下流側への一方向の風によって表層水が流されたときに藻類の収集効果が高まるように構成されている。 As a result, the surface water is washed away by the wind blowing from the downstream side of the river to the upstream side, algae in the surface water gathers near the upstream fence, and then the surface water is washed away by the wind blowing from the upstream side to the downstream side. is washed away, and most of the algae collected near the upstream fence are taken into the water intake via the diversion fence. That is, the guiding means of Patent Document 3 is configured so that the effect of collecting algae is enhanced when surface water is blown away by wind in one direction from the upstream side to the downstream side.

特開平8-33888号公報Japanese Patent Application Publication No. 8-33888 特開2006-238703号公報Japanese Patent Application Publication No. 2006-238703 特開2002-079293号公報Japanese Patent Application Publication No. 2002-079293

しかしながら、特許文献3の藻類を収集するための誘導手段は、河川には効果的かもしれないが、湖沼や池等の閉鎖水域のように風の吹く向きによって表層水の流れる方向がその都度変化し、表層水中に浮いた藻類の流れもそれに応じて変化する場合には効果的と言えない。 However, the guiding means for collecting algae in Patent Document 3 may be effective for rivers, but in closed water areas such as lakes and ponds, the direction in which surface water flows changes depending on the direction in which the wind blows. However, it cannot be said to be effective if the flow of algae floating in the surface water changes accordingly.

即ち、従来技術の水質保全装置の誘導手段は、1方向のみの表層水の流れ(上述の上流側から下流側への流れ)にしか対応できない。これにより、湖沼や池等の閉鎖水域のように風の吹く向きによって表層水の流れる方向がその都度変化し、表層水中に浮いた藻類の流れもそれに応じて変化する場合には、風の吹く向きに応じて誘導手段の向きをその都度変える必要がある。あるいは風の吹く向きに予め複数基の水質保全装置を配置しておく必要がある。したがって、閉鎖水域における藻類の収集及び回収効率が悪いと共に複数基配置する場合には装置コストが高くなる。 That is, the guiding means of the conventional water quality maintenance device can only handle the flow of surface water in one direction (the flow from the upstream side to the downstream side as described above). As a result, if the direction in which the surface water flows changes depending on the direction in which the wind blows, such as in closed water bodies such as lakes and ponds, and the flow of algae floating in the surface water also changes accordingly, It is necessary to change the direction of the guiding means each time depending on the direction. Alternatively, it is necessary to place multiple water quality maintenance devices in advance in the direction in which the wind blows. Therefore, the collection and recovery efficiency of algae in a closed water area is poor, and when multiple units are installed, the equipment cost increases.

本発明はこのような事情に鑑みてなされたもので、湖沼や池等の閉鎖水域に発生した藻類を風の向きに関係なく効率的に収集することができる藻類収集手段を備えた藻類除去装置及び藻類収集手段で収集した藻類を回収して藻類を最終的に処理するまでの藻類処理システムを提供することを目的とする。 The present invention was made in view of these circumstances, and provides an algae removal device equipped with an algae collection means that can efficiently collect algae that has grown in closed water areas such as lakes and ponds, regardless of the direction of the wind. Another object of the present invention is to provide an algae treatment system from collecting algae collected by an algae collection means to final treatment of the algae.

本発明の藻類除去装置は目的を達成するために、沼や池等の閉鎖水域の表層水中に浮遊する藻類を収集する藻類収集手段を備えた藻類除去装置において、藻類収集手段は、閉鎖水域の表層水中に浮くことが可能な複数本の第1棒状部材を放射状に配置して、浮遊する藻類が流入する流入口が流出口よりも拡径された逆ハの字状の収集水路を放射状に複数形成した藻類収集部と、閉鎖水域の表層水中に浮くことが可能な複数本の第2棒状部材を、複数の収集水路の流出口に連続して平行に配置して、複数の収集水路で収集された藻類を複数の収集水路のうちの1つの収集水路に誘導する複数の誘導水路を形成する藻類誘導部と、複数本の第1棒状部材及び複数本の第2棒状部材を連結固定する連結固定部材と、を少なくとも備えたことを特徴とする。 In order to achieve the purpose of the algae removal device of the present invention, the algae removal device is equipped with an algae collection means for collecting algae floating in the surface water of a closed water body such as a swamp or pond. A plurality of first rod-shaped members capable of floating in surface water are arranged radially to form an inverted V-shaped collection channel in which the inlet into which floating algae flows is larger in diameter than the outlet. A plurality of algae collection sections formed and a plurality of second rod-shaped members capable of floating in the surface water of a closed water area are arranged consecutively and parallel to the outlet of the plurality of collection channels, and A plurality of first rod-shaped members and a plurality of second rod-shaped members are connected and fixed to an algae guiding section that forms a plurality of guiding waterways that guide the collected algae to one of the plurality of collection waterways. The device is characterized in that it includes at least a connecting and fixing member.

本発明の藻類除去装置によれば、閉鎖水域の表層水中に浮くことが可能な複数本の第1棒状部材を放射状に配置することによって、浮遊する藻類が流入するための逆ハの字状の収集水路を東西南北の全方位に向けて複数形成するようにした。また、閉鎖水域の表層水中に浮くことが可能な複数本の第2棒状部材を、複数の収集水路の流出口に連続して平行に配置して、複数の収集水路で収集された藻類を複数の収集水路のうちの1つの収集水路に誘導する複数の誘導水路を形成するようにした。そして、連結固定部材によって、複数本の第1棒状部材及び複数本の第2棒状部材を連結固定することで藻類収集手段を一体的に構築した。 According to the algae removal device of the present invention, by radially arranging the plurality of first rod-shaped members that can float in the surface water of a closed water area, an inverted V-shaped structure is formed for floating algae to flow into the algae removal device. Multiple collection channels were formed in all directions, north, south, east and west. In addition, a plurality of second rod-shaped members capable of floating in the surface water of a closed water area are arranged consecutively and parallel to the outlet of the plurality of collection channels, so that a plurality of algae collected in the plurality of collection channels can be collected. A plurality of guiding channels are formed to guide the vehicle to one of the collecting channels. Then, the algae collection means was integrally constructed by connecting and fixing the plurality of first rod-like members and the plurality of second rod-like members using the connecting and fixing member.

これにより、湖沼や池等の閉鎖水域のように風の吹く向きによって表層水の流れる方向がその都度変化し、藻類の流れる方向もそれに応じて変化する場合であっても、藻類の大分部は何れかの収集水路(1つ又は複数)に流れ込むようにすることができる。 As a result, even if the direction of flow of surface water changes depending on the direction of wind blowing, such as in closed water bodies such as lakes and ponds, and the direction of flow of algae changes accordingly, most of the algae It may flow into any collection channel(s).

本発明の藻類除去装置の態様としては、1つの収集水路には、複数の収集水路で収集した藻類を回収する藻類回収手段が配置されることが好ましい。これにより、藻類の収集と回収との両方を一度に行うことが可能な藻類除去装置を構築した。 As an aspect of the algae removal device of the present invention, it is preferable that one collection waterway is provided with an algae collection means for collecting algae collected in a plurality of collection waterways. As a result, we constructed an algae removal device that can both collect and recover algae at the same time.

これにより、複数の収集水路の何れかに流れ込んだ藻類は誘導水路を通って藻類回収手段に導かれて藻類回収手段で回収される。 As a result, algae that has flowed into any one of the plurality of collection waterways is guided to the algae collection means through the guide waterway and collected by the algae collection means.

したがって、湖沼や池等の閉鎖水域に発生した藻類を風の向きに関係なく効率的に収集して回収することができるだけでなく、複数の収集水路ごとに藻類回収手段を備える必要がないので、藻類除去装置のコストも低く抑えることができる。 Therefore, not only can algae generated in closed water bodies such as lakes and ponds be efficiently collected and recovered regardless of the wind direction, but there is no need to provide algae recovery means for each of multiple collection channels. The cost of the algae removal device can also be kept low.

本発明の藻類除去装置の態様としては、複数の収集水路は4水路であって、4本の第1棒状部材が90°間隔で放射状に配置されていることが好ましい。3水路でも放射状の収集水路は可能であるが、3水路の場合には1つの収集水路の逆ハの字角度が120°になる。これにより、風の向きによっては、収集水路にせっかく流れ込んだ藻類が再び収集水路から流れ出てしまう危険がある。 As an aspect of the algae removal device of the present invention, it is preferable that the plurality of collection channels are four channels, and the four first rod-shaped members are arranged radially at 90° intervals. Radial collection channels are also possible with three channels, but in the case of three channels, the inverted V-shaped angle of one collection channel is 120°. As a result, depending on the direction of the wind, there is a risk that algae that have flowed into the collection waterway may flow out of the collection waterway again.

また、収集水路が5本以上になると、その分だけ誘導水路の水路数を多くする必要があり、1本あたりの誘導水路の水路幅が狭くなる。これにより、導入水路における表層水の流れが滞留し易くなるので、収集水路で収集した藻類を藻類回収手段で回収する回収効率が低下する危険がある。 Furthermore, when the number of collection channels increases to five or more, it is necessary to increase the number of guide channels by that much, and the width of each guide channel becomes narrower. As a result, the flow of surface water in the introduction waterway tends to stagnate, so there is a risk that the collection efficiency of collecting algae collected in the collection waterway by the algae collection means will be reduced.

本発明の藻類除去装置の態様としては、第1棒状部材及び第2棒状部材は両端が水密された塩ビパイプであることが好ましい。塩ビパイプは、軽量性、耐衝撃性、耐食性、耐久性、加工性に優れ価格的にも安価であると共に、両端が水密されて内部に空気が溜まった塩ビパイプは表層水中に水路を形成できる程度に適度に浮くことができる。 As an aspect of the algae removal device of the present invention, it is preferable that the first rod-shaped member and the second rod-shaped member are PVC pipes whose both ends are watertight. PVC pipes are lightweight, impact resistant, corrosion resistant, durable, and workable, and are inexpensive. PVC pipes are watertight at both ends and have air trapped inside, allowing them to form waterways in surface water. Can float to a certain extent.

本発明の藻類除去装置の好ましい態様としては、収集水路の第1棒状部材は入れ子構造によって伸縮自在であることが好ましい。閉鎖水域の大きさや形状は画一的ではないので、第1棒状部材を入れ子構造にすることで、閉鎖水域の大きさに応じて収集水路の大きさを可変できるだけでなく、藻類除去装置を設置する閉鎖水域の形状に応じて複数本の第1棒状部材の長さをそれぞれ変えることで、複雑な形状の閉鎖水域にも対応できる。 In a preferred embodiment of the algae removal device of the present invention, the first rod-shaped member of the collection waterway is preferably expandable and retractable by a nested structure. Since the size and shape of closed water bodies are not uniform, by making the first rod-shaped member a nested structure, it is possible to not only change the size of the collection channel depending on the size of the closed water area, but also to install an algae removal device. By changing the lengths of the plurality of first rod-shaped members depending on the shape of the closed water area, it is possible to cope with a closed water area with a complicated shape.

本発明の藻類除去装置の態様としては、藻類収集手段は、第1棒状部材に吊設され、第1棒状部材と略同等の幅を有するシート状部材と、シート状部材を表層水中に垂下させる錘部材と、を更に有することが好ましい。 In an aspect of the algae removal device of the present invention, the algae collecting means includes a sheet-like member suspended from a first rod-like member and having a width substantially equal to that of the first rod-like member, and a sheet-like member suspended in surface water. It is preferable to further include a weight member.

これにより、収集水路に流れ込んだ藻類が第1棒状部材を潜って再び閉鎖水域に戻ってしまうことを確実に防止できる。 Thereby, it is possible to reliably prevent algae that have flowed into the collection waterway from passing through the first rod-shaped member and returning to the closed water area.

本発明の藻類除去装置の態様としては、藻類収集手段は、複数の収集水路の逆ハの字角度の変動を防止する逆ハの字角度変動防止手段を更に有し、逆ハの字角度変動防止手段は、収集水路を形成する複数本の第1棒状部材の流入口の位置にそれぞれ立設されたピン部材と、ピン部材の隣接するピン部材同士を緊張した状態で連結する紐状部材と、で構成されていることが好ましい。 As an aspect of the algae removal device of the present invention, the algae collecting means further includes a reverse V-shaped angle variation prevention means for preventing fluctuations in the reverse V-shaped angle of the plurality of collection channels, The prevention means includes pin members erected at respective inlet positions of the plurality of first rod-like members forming the collection waterway, and a string-like member that connects adjacent pin members in a tensioned state. , is preferably configured.

これにより、収集水路の逆ハの字角度が設定よりも拡がってしまうのを防止できると共に、収集水路の破損を防止できる。即ち、収集水路を構成する第1棒状部材の長さが長い場合には、風の吹く向きに流れる表層水の流れで第1棒状部材が湾曲し、逆ハの字角度が設定よりも拡がってしまう場合が考えられる。逆ハの字角度が設定よりも拡がると、上述の3水路の場合でも説明したが、風の向きによっては、収集水路にせっかく流れ込んだ藻類が再び収集水路から流れ出てしまう危険がある。また、逆ハの字角度の拡がりが大きい場合には第1棒状部材が折れる等の破損につながる。 Thereby, it is possible to prevent the inverted V-shaped angle of the collection waterway from becoming wider than the setting, and it is also possible to prevent damage to the collection waterway. That is, when the length of the first rod-shaped member constituting the collection waterway is long, the first rod-shaped member is curved by the flow of surface water flowing in the direction in which the wind blows, and the inverted V-shaped angle becomes wider than the setting. There may be cases where it is stored away. As explained in the case of the three canals mentioned above, if the inverted V-shaped angle becomes wider than the setting, depending on the direction of the wind, there is a risk that the algae that have flowed into the collection canal will flow out of the collection canal again. Furthermore, if the inverted V-shaped angle expands too much, the first rod-shaped member may break or otherwise be damaged.

本発明の藻類除去装置の態様としては、複数の誘導水路には、誘導水路の表層水に収集水路から藻類回収手段へ向いた水流を発生させる水流発生手段が設けられていることが好ましい。 As an aspect of the algae removal device of the present invention, it is preferable that the plurality of guide channels are provided with a water flow generating means for generating a water flow in the surface water of the guide channels from the collection channel toward the algae collection means.

表層水の流れに同伴して収集水路に流れ込んだ藻類は誘導水路を通って藻類回収手段に回収される。この場合、表層水の流れは逆ハの字の収集水路から水路幅が狭い誘導水路に変わるので、誘導水路内に表層水の滞留が発生する懸念がある。誘導水路の水路幅を広くすれば解決できるが、藻類回収手段の藻類を表層水と一緒に吸引する吸引ノズルの幅との関係で水路幅が制限される。 The algae that flowed into the collection channel along with the flow of surface water pass through the guide channel and are collected by the algae collection means. In this case, the flow of surface water changes from an inverted V-shaped collection channel to a narrow guide channel, so there is a concern that surface water may accumulate in the guide channel. This problem can be solved by widening the guide channel, but the width of the channel is limited by the width of the suction nozzle that sucks the algae together with surface water in the algae collecting means.

本発明における誘導水路には、誘導水路の表層水に収集水路から藻類回収手段へ向いた水流を発生させる水流発生手段を備えたので、誘導水路内に表層水の滞留が発生するのを防止できる。これにより、閉鎖水域の藻類を一層効率的に収集して回収することができる。 Since the guiding channel of the present invention is equipped with a water flow generating means for generating a water flow in the surface water of the guiding channel from the collection channel toward the algae collection means, it is possible to prevent surface water from stagnation in the guiding channel. . This allows algae in closed water areas to be collected and recovered more efficiently.

本発明の藻類除去装置の態様としては、藻類回収手段は、藻類収集手段で藻類と一緒に収集された閉鎖水域のゴミ類を分離して藻類を選択的に回収する機構を備えていることが好ましい。 As an aspect of the algae removal device of the present invention, the algae collecting means may be equipped with a mechanism for selectively collecting the algae by separating garbage from the closed water area collected together with the algae by the algae collecting means. preferable.

本発明の藻類除去装置の態様としては、藻類回収手段は、収集した藻類を含む表層水が流通可能な門型の装置フレームと、装置フレーム内に前記表層水の流通方向に直交して横向きに配置され、周面にゴミ分離用のフィルタが形成されるとともに側面に浮遊藻類を表層水と一緒に吸引して取り込む吸引配管の一方端部及び前記フィルタを洗う水を吐出する吐出配管の一方端部を内部に導く導入口が開口された円筒状のゴミ分離ドラムと、装置フレームに回転自在に片持ち支持され、ゴミ分離ドラムの両端部周面をそれぞれ3点支持する合計6個の支持ローラと、6個の支持ローラの少なくとも1つに回転動力を付与してゴミ分離ドラムを回転する回転動力手段と、装置フレームに固定され、ゴミ分離ドラムの下部が表層水中に浸漬するように装置フレームを浮かせる浮き部材と、ゴミ分離ドラム内に設けられ、吸引配管に連通状態で支持されるとともにゴミ分離ドラムの軸芯方向に長いスロット形状の吸引口が表層水中に位置するように形成された吸引ノズルと、ゴミ分離ドラム内に設けられ、吐出配管に連通状態で支持されるとともにゴミ分離ドラムの軸芯方向に長いスロット形状の吐出口が表層水の水面上に位置するように形成された吐出ノズルと、ゴミ分離ドラムの外面に突起した状態で複数枚設けられ、ゴミ分離ドラムの軸芯方向に長い板状のスキーマと、を備えることが好ましい。 In an embodiment of the algae removal device of the present invention, the algae collecting means includes a gate-shaped device frame through which surface water containing collected algae can flow, and a device frame arranged horizontally in a direction perpendicular to the flow direction of the surface water. one end of a suction piping that is arranged to form a dust separation filter on its circumferential surface, and one end of a suction piping that suctions and takes in floating algae together with surface water on the side surface, and one end of a discharge piping that discharges water that washes the filter. A cylindrical dust separation drum with an opening for introducing the dust into the inside, and a total of six support rollers that are supported rotatably on the device frame at three points each on the circumferential surface of both ends of the dust separation drum. a rotary power means for rotating the dust separation drum by applying rotational power to at least one of the six support rollers; and a rotational power means fixed to the apparatus frame so that the lower part of the dust separation drum is immersed in surface water. a suction member installed in the dust separation drum, supported in communication with the suction piping, and formed such that a slot-shaped suction port that is long in the axial direction of the dust separation drum is located in the surface water. A nozzle and a discharge outlet provided in the dust separation drum, supported in communication with the discharge piping, and having a slot-shaped discharge port that is long in the axial direction of the dust separation drum and positioned above the water surface of the surface water. It is preferable to include a nozzle and a plurality of plate-shaped schemas that are provided in a protruding state on the outer surface of the dust separation drum and are long in the axial direction of the dust separation drum.

ここで、「表層水が流通可能」とは、表層水が滞らないで流れることを意味する。 Here, "surface water can flow" means that surface water flows without stagnation.

本発明の藻類回収手段によれば、湖沼、池、河川、閉鎖性海域等のアオコ等の浮遊藻類が大量発生した閉鎖性水域に、ゴミ分離ドラムの下部が表層水中に浸漬するように浮遊藻類収集装置を浮かべる。これにより、ゴミ分離ドラム内に設けられた吸引ノズルの吸引口が表層水中に浸漬する。 According to the algae collecting means of the present invention, floating algae can be collected in closed water bodies such as lakes, ponds, rivers, closed sea areas, etc. where floating algae such as blue-green algae have grown in large quantities, so that the lower part of the garbage separation drum is immersed in the surface water. Float the collection device. As a result, the suction port of the suction nozzle provided in the dust separation drum is immersed in the surface water.

そして、ゴミ分離ドラムを回転させるとともに吸引配管に吸引力を付与する。ゴミ分離ドラムの回転によって、ゴミ分離ドラムの外面に突起された複数枚のスキーマは、浮遊藻類収集装置の周囲に浮遊する浮遊藻類を掻き集めるとともに、門型の装置フレームの前門側からゴミ分離ドラムの下部を通過して後門側に流通する表層水の流れを形成する。 Then, while rotating the dust separation drum, a suction force is applied to the suction pipe. As the garbage separation drum rotates, the multiple schemas protruding from the outer surface of the garbage separation drum scrape up floating algae floating around the floating algae collection device, and the garbage separation drum is removed from the front gate side of the gate-shaped device frame. Forms a flow of surface water that passes through the lower part of the gate and flows toward the rear gate.

この表層水の流れにより、スキーマで掻き集められた浮遊藻類は表層水と一緒にゴミ分離ドラムのフィルタを通過して吸引口から吸引配管に取り込まれる。一方、スキーマで浮遊藻類と一緒に掻き集められたゴミ類はゴミ分離ドラムのフィルタで分別され、表層水の流れに乗って装置フレームの後面から閉鎖性水域に戻る。 Due to the flow of the surface water, the floating algae scraped up by the schema pass through the filter of the dust separation drum together with the surface water and are taken into the suction pipe from the suction port. On the other hand, the garbage scraped together with the floating algae in the schema is separated by the filter in the garbage separation drum, and returned to the closed water area from the rear of the device frame along with the flow of surface water.

また、吐出ノズルからゴミ分離ドラムのフィルタ内面に水を吐出してフィルタを自動洗浄するので、フィルタが目詰まりしにくい。更には、装置フレームを門型形状とし、装置フレームに回転自在に片持ち支持される6個の支持ローラでゴミ分離ドラムの両端部周面を3点支持するようにした。したがって、門型の装置フレームの前門側からゴミ分離ドラムの下部を通過して後門側に流通する表層水の流れが、装置フレームや支持ローラによって邪魔されないので、浮遊藻類がゴミ分離ドラムの近辺で滞留することがない。 Furthermore, since the filter is automatically cleaned by discharging water from the discharge nozzle onto the inner surface of the filter of the dust separation drum, the filter is less likely to become clogged. Furthermore, the device frame is shaped like a gate, and the dust separation drum is supported at three points on both end circumferential surfaces by six support rollers rotatably supported by the device frame in a cantilevered manner. Therefore, the flow of surface water flowing from the front gate side of the gate-shaped device frame to the rear gate side after passing through the lower part of the garbage separation drum is not obstructed by the device frame or support rollers, so floating algae can be collected near the garbage separation drum. There is no stagnation.

これにより、アオコ等の浮遊藻類のみを選択的に収集することができ、メンテナンスもほとんど必要ない藻類回収手段を提供することができる。 Thereby, it is possible to selectively collect only floating algae such as blue-green algae, and it is possible to provide an algae collection means that requires almost no maintenance.

本発明の藻類処理システムは目的を達成するために、請求項2に記載の藻類除去装置と、藻類除去装置の前記藻類収集手段で収集されてから藻類回収手段で回収された藻類を破壊する多段渦巻ポンプ構造の藻類破壊手段と、を備えたことを特徴とする。 In order to achieve the object, the algae treatment system of the present invention includes the algae removal device according to claim 2, and a multi-stage method for destroying the algae collected by the algae collection means of the algae removal device and then collected by the algae collection means. The present invention is characterized by comprising an algae destruction means having a spiral pump structure.

本発明の藻類処理システムによれば、湖沼や池等の閉鎖水域に発生した藻類を藻類収集手段によって風の向きに関係なく効率的に収集し、藻類と一緒に収集されたゴミ類を藻類回収手段で分離して藻類のみを選択的に回収し、回収した藻類を藻類破壊手段で最終的に処理するまでの一連の藻類処理システムを構築することができる。 According to the algae treatment system of the present invention, algae generated in closed water bodies such as lakes and ponds can be efficiently collected by the algae collection means regardless of the wind direction, and garbage collected together with the algae can be collected as algae. It is possible to construct a series of algae treatment systems that include separating the algae with a means to selectively collect only the algae, and finally processing the collected algae with an algae destruction means.

本発明の藻類除去装置によれば、湖沼や池等の閉鎖水域に発生した藻類を藻類収集手段によって風の向きに関係なく効率的に収集することができる。更には、藻類除去装置において、1つの収集水路に、複数の収集水路で収集した藻類を回収する藻類回収手段を配置することにより、藻類の収集と回収との両方を一度に効率的に行うことが可能な藻類除去装置を構築することができる。 According to the algae removal device of the present invention, algae generated in closed water bodies such as lakes and ponds can be efficiently collected by the algae collecting means regardless of the direction of the wind. Furthermore, in the algae removal device, by arranging an algae collection means for collecting algae collected in a plurality of collection waterways in one collection waterway, both collection and recovery of algae can be performed efficiently at once. It is possible to construct an algae removal device that can remove algae.

また、本発明の藻類処理システムは、本発明の藻類除去装置を備えているので、収集及び回収した藻類を最終的に処理するまでの一連の藻類処理システムを構築することができる。 Further, since the algae treatment system of the present invention includes the algae removal device of the present invention, it is possible to construct a series of algae treatment systems up to the final treatment of collected and recovered algae.

本発明の藻類処理システムの全体構成図Overall configuration diagram of the algae treatment system of the present invention 藻類除去装置の俯瞰図Overhead view of algae removal equipment 藻類除去装置の主として藻類収集手段を説明する説明図Explanatory diagram mainly explaining the algae collection means of the algae removal device 藻類収集手段の収集水路が3水路の場合の説明図Explanatory diagram when there are three collection channels for algae collection means 藻類収集手段の収集水路が7水路の場合の説明図Explanatory diagram when there are 7 collection channels for algae collection means 収集水路の第1棒状部材を伸縮自在にした態様の説明図An explanatory diagram of an embodiment in which the first rod-shaped member of the collection waterway is made expandable and retractable. 収集水路の第1棒状部材に表層水中に垂下するシート部材と逆ハの字角度変動防止手段を設けた態様の説明図An explanatory diagram of an embodiment in which the first rod-shaped member of the collection waterway is provided with a sheet member hanging down into surface water and an inverted V-shaped angle variation prevention means. 藻類収集手段の導入水路に設けた水流発生手段の説明図An explanatory diagram of the water flow generation means installed in the introduction channel of the algae collection means 水流発生手段を説明する拡大図Enlarged diagram explaining water flow generation means 藻類除去装置の藻類回収手段の斜視図Perspective view of algae collection means of algae removal device 藻類回収手段のパンチングメタル形式のゴミ分離ドラム周辺の斜視図Perspective view of the area around the punched metal type garbage separation drum of algae collection means 藻類回収手段の金網形式のゴミ分離ドラム周辺の斜視図Perspective view of the area around the wire-mesh type garbage separation drum of the algae collection means 藻類回収手段の吸引ノズルの斜視図Perspective view of the suction nozzle of the algae collection means 藻類回収手段の吐出ノズルの斜視図Perspective view of the discharge nozzle of the algae collection means 多段渦巻ポンプ構造の藻類破壊装置の説明図Explanatory diagram of an algae destruction device with a multi-stage centrifugal pump structure 藻類処理システムの主として藻類収集手段の作用を説明する説明図Explanatory diagram mainly explaining the action of the algae collection means of the algae treatment system アオコを収集する従来の装置の説明図Illustration of a conventional device for collecting blue-green algae 浮遊藻類処理システムに脱気手段を設けた説明図Explanatory diagram of a floating algae treatment system equipped with deaeration means 本発明の藻類処理システムにおいて、藻類回収手段と藻類破壊装置とを一体化した斜視図A perspective view of an integrated algae collection means and an algae destruction device in the algae treatment system of the present invention.

以下、添付図面にしたがって本発明の藻類除去装置及び藻類処理システムの好ましい実施の形態について説明する。 Preferred embodiments of the algae removal device and algae treatment system of the present invention will be described below with reference to the accompanying drawings.

本発明は以下の好ましい実施の形態により説明される。本発明の範囲を逸脱することなく、多くの手法により変更を行うことができ、本実施の形態以外の他の実施の形態を利用することができる。したがって、本発明の範囲内における全ての変更が特許請求の範囲に含まれる。 The invention is illustrated by the following preferred embodiments. Modifications may be made in many ways and other embodiments may be utilized without departing from the scope of the invention. Accordingly, all modifications within the scope of the invention are included in the claims.

ここで、図中、同一の記号で示される部分は、同様の機能を有する同様の要素である。また、本明細書中で、数値範囲を" ~ "を用いて表す場合は、" ~ "で示される上限、下限の数値も数値範囲に含むものとする。 Here, parts indicated by the same symbols in the figures are similar elements having similar functions. In addition, in this specification, when a numerical range is expressed using " to ", the upper and lower limit values indicated by " to " are also included in the numerical range.

[藻類処理システム]
図1は、本発明の藻類処理システム10の実施の形態の全体構成図であり、主として、藻類除去装置12と、藻類除去装置12によって収集及び回収した藻類を破壊する藻類破壊装置14とで構成される。また、閉鎖水域に浮遊する藻類の一例としてアオコの例で以下に説明する。
[Algae treatment system]
FIG. 1 is an overall configuration diagram of an embodiment of an algae treatment system 10 of the present invention, which is mainly composed of an algae removal device 12 and an algae destruction device 14 that destroys algae collected and recovered by the algae removal device 12. be done. Further, as an example of algae floating in a closed water area, an example of blue-green algae will be explained below.

藻類処理システム10の説明として、閉鎖水域15のアオコを収集した後、閉鎖水域15から回収し、最終的にアオコを破壊処理するまでのプロセスの流れに沿って装置を順番に説明する。 As an explanation of the algae treatment system 10, the apparatus will be explained in order along the process flow from collecting algal blooms in the closed water area 15, collecting them from the closed water area 15, and finally destroying the algal blooms.

(藻類除去装置)
藻類除去装置12は、主として、閉鎖水域15の表層水中に浮遊するアオコを収集する藻類収集手段12Aと、収集した藻類を閉鎖水域15から回収する藻類回収手段12Bとで構成される。なお、本実施の形態の藻類除去装置12は、藻類収集手段12Aと藻類回収手段12Bとの両方を備えた例で説明するが、藻類収集手段12Aのみの構成の場合も本発明の藻類除去装置12に含む。
(Algae removal device)
The algae removal device 12 mainly includes an algae collection means 12A that collects algae floating in the surface water of the closed water area 15, and an algae collection means 12B that collects the collected algae from the closed water area 15. Although the algae removal device 12 of the present embodiment will be described as an example including both the algae collection means 12A and the algae collection means 12B, the algae removal device of the present invention can also be used in a case where only the algae collection means 12A is configured. Included in 12.

<藻類収集手段>
図2は、藻類収集手段12Aを閉鎖水域15に設置した俯瞰図であり、図3は藻類収集手段12Aの上面図である。
<Algae collection means>
FIG. 2 is an overhead view of the algae collection means 12A installed in the closed water area 15, and FIG. 3 is a top view of the algae collection means 12A.

図2及び図3に示すように、藻類収集手段12Aは、主として、藻類収集部13と、藻類誘導部17と、藻類収集部13及び藻類誘導部17を一体的に連結固定する連結固定部材19とで構成される。本実施の形態では、連結固定部材19として井桁構造のものを使用したが、これに限定されるものではない。 As shown in FIGS. 2 and 3, the algae collecting means 12A mainly includes an algae collecting section 13, an algae guiding section 17, and a connecting and fixing member 19 that integrally connects and fixes the algae collecting section 13 and the algae guiding section 17. It consists of In this embodiment, a parallel cross structure is used as the connecting and fixing member 19, but the present invention is not limited to this.

藻類収集部13は、閉鎖水域15の表層水中に浮くことが可能な複数本の第1棒状部材13A、13A…を放射状に配置して、浮遊するアオコが流入する流入口13Bが流出口13Cよりも拡径された逆ハの字状の収集水路13D、13D…を放射状に複数形成することによって構成される。そして、複数の収集水路13Dのうちの一つに藻類回収手段12Bが浮遊した状態で配置される。 The algae collection unit 13 has a plurality of first rod-shaped members 13A, 13A... that are capable of floating in the surface water of the closed water area 15 arranged radially so that an inlet 13B through which floating algal blooms flows is closer to an outlet 13C. It is also constructed by forming a plurality of collection channels 13D, 13D, . Then, the algae collecting means 12B is arranged in a floating state in one of the plurality of collection channels 13D.

なお、収集水路13Dを3水路以上形成することで、収集水路13Dを放射状に配置することができる。しかし、図2及び図3に示すように、4本の第1棒状部材13Aを90°間隔で放射状に配置して収集水路13Dを4水路とし、収集水路13Dの逆ハの字状角度θを90°にすることが一層好ましい。 Note that by forming three or more collection waterways 13D, the collection waterways 13D can be arranged radially. However, as shown in FIGS. 2 and 3, four first rod members 13A are arranged radially at 90° intervals to form four collection channels 13D, and the inverted V-shaped angle θ of the collection channels 13D is More preferably, the angle is 90°.

この理由は、図4に示すように、3水路の場合には1つの収集水路13Dの逆ハの字状角度θが120°の鈍角になるので、収集水路13Dに流れ込んだアオコが再び収集水路13Dから流れ出てしまう危険がある。例えば、図4の矢印P方向から風が吹いた場合、風に対して流入口13Bが向き最もアオコを収集し易い収集水路13D内には矢印Q方向の表層水の流れが生じるので、収集水路13Dに収集されたアオコが再び収集水路13Dから流れ出てしまう危険がある。 The reason for this is that, as shown in Figure 4, in the case of three waterways, the inverted V-shaped angle θ of one collection waterway 13D is an obtuse angle of 120°, so the algae that has flowed into the collection waterway 13D will return to the collection waterway. There is a danger that it will flow out of 13D. For example, when the wind blows from the direction of arrow P in FIG. There is a risk that the blue-green algae collected in 13D will flow out of the collection waterway 13D again.

一方、図5に示すように、収集水路が5水路以上になると、その分だけ藻類誘導部17の誘導水路17Bの水路数を多くする必要があり、1本あたりの誘導水路17Bの水路幅Wが狭くなる。したがって、誘導水路17Bにおいて表層水の流れが滞留し易くなる。これにより、収集水路13Dで収集したアオコが藻類回収手段12Bに効率的に流れ難くなる危険がある。ちなみに、誘導水路17Bでの表層水の滞留を防止するには、1本あたりの誘導水路17Bの水路幅Wは100mm以上であることが好ましい。 On the other hand, as shown in FIG. 5, when the number of collection channels is five or more, it is necessary to increase the number of guide channels 17B of the algae guiding section 17 accordingly, and the channel width W of each guide channel 17B is increased. becomes narrower. Therefore, the flow of surface water tends to stay in the guiding waterway 17B. Thereby, there is a risk that the algae collected in the collection waterway 13D will be difficult to flow efficiently to the algae collection means 12B. Incidentally, in order to prevent surface water from stagnation in the guide channel 17B, it is preferable that the channel width W of each guide channel 17B is 100 mm or more.

したがって、本発明の実施の形態では、収集水路13Dを4水路とし、4本の第1棒状部材13A同士が90°間隔で放射状に配置されている場合で以下に説明する。 Therefore, in the embodiment of the present invention, a case will be described below in which there are four collection channels 13D, and the four first rod-shaped members 13A are arranged radially at 90° intervals.

また、藻類誘導部17は、閉鎖水域15の表層水中に浮くことが可能な複数本の第2棒状部材17A、17A…を、複数の収集水路13Dの流出口13Cに連続して平行に配置して、複数の収集水路13Dで収集されたアオコを藻類回収手段12Bに向けて誘導する複数の誘導水路17B、17B…を形成することによって構成される。 In addition, the algae guide unit 17 arranges a plurality of second rod-shaped members 17A, 17A, which are capable of floating in the surface water of the closed water area 15, continuously and parallel to the outlet ports 13C of the plurality of collection channels 13D. It is configured by forming a plurality of guiding waterways 17B, 17B, . . . that guide the algae collected in the plurality of collecting waterways 13D toward the algae collecting means 12B.

そして、連結固定部材19によって、収集水路13Dを形成する複数本の第1棒状部材13Aと、誘導水路17Bを形成する複数本の第2棒状部材17Aを連結固定して一体化する。これにより、藻類収集手段12Aが構築される。 Then, the plurality of first rod-shaped members 13A forming the collection waterway 13D and the plurality of second rod-shaped members 17A forming the guide waterway 17B are connected and fixed to be integrated by the connection and fixing member 19. Thereby, the algae collecting means 12A is constructed.

第1棒状部材13A及び第2棒状部材17Aは、水に浮くことができ、閉鎖水域15の表層水の流れをガイド可能な太さの棒状部材であれば特に限定されないが、両端が水密された塩ビパイプであることが好ましい。塩ビパイプは、軽量性、耐衝撃性、耐食性、耐久性、加工性に優れ価格的にも安価であると共に、両端が水密されて内部に空気が溜まった塩ビパイプは表層水の水路を形成できる程度に適度に浮くことができる。 The first rod-shaped member 13A and the second rod-shaped member 17A are not particularly limited as long as they are rod-shaped members that can float on water and have a thickness that can guide the flow of surface water in the closed water area 15, but both ends are watertight. Preferably, it is a PVC pipe. PVC pipes are lightweight, impact resistant, corrosion resistant, durable, and workable, and are inexpensive. PVC pipes are watertight at both ends and have air trapped inside, allowing them to form a channel for surface water. Can float to a certain extent.

第1棒状部材13A及び第2棒状部材17Aの直径は、風の吹く向きに流れる表層水の流れをガイドでき、且つ表層水の流れに同伴して浮遊するアオコが乗り越えたり潜り込んだりして収集水路13Dや誘導水路17Bから流れ出てしまわない程度の太さがあればよい。また、第1棒状部材13A及び第2棒状部材17Aの直径が太すぎると、重くなり取扱いに不便であるだけでなく、誘導水路17Bの水路幅を狭める原因になる。具体的には、第1棒状部材13A及び第2棒状部材17Aの直径は、50~100mm程度であることが好ましい。 The diameters of the first rod-shaped member 13A and the second rod-shaped member 17A are such that they can guide the flow of surface water flowing in the direction in which the wind blows, and allow algal blooms floating along with the flow of surface water to climb over or submerge into the collection channel. It only needs to be thick enough to prevent it from flowing out of the guide waterway 13D and the guide waterway 17B. Moreover, if the diameters of the first rod-shaped member 13A and the second rod-shaped member 17A are too large, they will not only be heavy and inconvenient to handle, but also cause the width of the guide channel 17B to be narrowed. Specifically, the diameter of the first rod-shaped member 13A and the second rod-shaped member 17A is preferably about 50 to 100 mm.

また、第1棒状部材13Aと第2棒状部材17Aとは別個の棒状部材として予め形成し、後から継手部材(図示せず)で繋ぐこともできる。しかし、塩ビパイプは加工し易いので、本実施の形態のように、第1棒状部材13Aと第2棒状部材17Aを連続した1本の塩ビパイプで形成することができる。例えば、図3に示すように、2本の塩ビパイプの一端部側をへの字状に折曲加工して第2棒状部材17Aの部分を形成し、更に2本の塩ビパイプの一端部側をフック状に折曲加工して第2棒状部材17Aの部分を形成する。そして、4本の塩ビパイプを図3のように並べると共に4本の塩ビパイプを連結固定部材19で一体的に固定する。これにより、藻類収集手段12Aを形成することができる。 Further, the first rod-shaped member 13A and the second rod-shaped member 17A can be formed in advance as separate rod-shaped members, and then connected later with a joint member (not shown). However, since PVC pipes are easy to process, the first rod-shaped member 13A and the second rod-shaped member 17A can be formed from one continuous PVC pipe as in this embodiment. For example, as shown in FIG. 3, one end side of two PVC pipes is bent into a curved shape to form the second rod-shaped member 17A, and one end side of two PVC pipes is further bent. is bent into a hook shape to form the second rod-shaped member 17A. Then, the four PVC pipes are lined up as shown in FIG. 3, and the four PVC pipes are integrally fixed using the connecting and fixing member 19. Thereby, algae collecting means 12A can be formed.

また、図6に示すように、収集水路13Dで使用する第1棒状部材13Aは入れ子構造によって伸縮自在であることが好ましい。閉鎖水域15の大きさや形状は画一的ではないので、第1棒状部材13Aを入れ子構造にすることで、閉鎖水域15の大きさに応じて収集水路13Dの大きさを可変できる。更には、第1棒状部材13Aを入れ子構造にすることによって、閉鎖水域15の形状に応じて複数本の第1棒状部材13Aの長さをそれぞれ変えることで、複雑な形状の閉鎖水域15にも対応した収集水路13Dを形成できる。 Moreover, as shown in FIG. 6, it is preferable that the first rod-shaped member 13A used in the collection waterway 13D is expandable and retractable due to its nested structure. Since the size and shape of the closed water area 15 are not uniform, the size of the collection waterway 13D can be varied according to the size of the closed water area 15 by forming the first rod-shaped member 13A into a nested structure. Furthermore, by forming the first rod-shaped members 13A into a nested structure, the lengths of the plurality of first rod-shaped members 13A can be changed according to the shape of the closed water area 15, so that even complex-shaped closed water areas 15 can be accommodated. A corresponding collection channel 13D can be formed.

この場合、入れ子構造にすることによって水密性が失われないように、水密手段を設けることが好ましい。水密手段としては、水密にできればどのようなものでもよいが、例えば図6に示す構造とすることができる。図6に示すように、太い第1棒状部材13A1と細い第1棒状部材13A2との伸縮ストローク部分Sを螺合構造21にすると共に、嵌合する境界位置にシール部材23(例えばOリング)を設ける。これにより、第1棒状部材13Aを入れ子構造にしても水密性を維持することができる。 In this case, it is preferable to provide watertight means so that watertightness is not lost due to the nested structure. The watertight means may be of any type as long as it can be made watertight, and for example, the structure shown in FIG. 6 can be used. As shown in FIG. 6, the expansion/contraction stroke portion S between the thick first rod-like member 13A1 and the thin first rod-like member 13A2 is made into a screw structure 21, and a sealing member 23 (for example, an O-ring) is provided at the boundary position where they fit together. establish. Thereby, watertightness can be maintained even if the first rod-shaped member 13A has a nested structure.

図7は、藻類収集手段12Aの好ましい態様で、図7の(A)は収集水路13Dを形成する第1棒状部材13Aを側面から見た図であり、図7の(B)は第1棒状部材13Aを一方端側から見た図である。 7 shows a preferred embodiment of the algae collecting means 12A, FIG. 7(A) is a side view of the first rod-shaped member 13A forming the collection channel 13D, and FIG. 7(B) is a side view of the first rod-shaped member 13A. It is a figure which looked at member 13A from one end side.

図7に示すように、藻類収集手段12Aは、第1棒状部材13Aに吊設され、第1棒状部材13Aと略同等の幅を有するシート状部材25と、シート状部材25を表層水中に垂下させる錘部材27と、を更に有する。符号29は、シート状部材と錘部材とを結ぶ紐状部材である。これにより、収集水路13Dに流れ込んだアオコが第1棒状部材13Aの下を潜って再び閉鎖水域15に戻ってしまう危険を確実に回避することができる。 As shown in FIG. 7, the algae collecting means 12A includes a sheet-like member 25 that is suspended from the first rod-like member 13A and has approximately the same width as the first rod-like member 13A, and a sheet-like member 25 that is suspended in the surface water. It further includes a weight member 27 for causing the load. Reference numeral 29 is a string-like member that connects the sheet-like member and the weight member. Thereby, it is possible to reliably avoid the risk that the blue-green algae that has flowed into the collection waterway 13D will go under the first rod-shaped member 13A and return to the closed water area 15 again.

また、図2~図5及び図7に示すように、複数の収集水路13Dの逆ハの字角度θの変動を防止する逆ハの字角度変動防止手段31を更に有することが好ましい。逆ハの字角度変動防止手段31は、収集水路13Dを形成する複数本の第1棒状部材13Aの流入口13Bの位置にそれぞれ立設されたピン部材31Aと、ピン部材31Aの隣接するピン部材31A同士を緊張した状態で連結する紐状部材31Bと、で構成される。 Further, as shown in FIGS. 2 to 5 and 7, it is preferable to further include an inverted V-shaped angle variation prevention means 31 for preventing variations in the inverted V-shaped angle θ of the plurality of collection channels 13D. The inverted V-shaped angle variation prevention means 31 includes pin members 31A each erected at the position of the inlet 13B of the plurality of first rod-shaped members 13A forming the collection waterway 13D, and adjacent pin members of the pin member 31A. It is composed of a string-like member 31B that connects the members 31A in a tensed state.

これにより、収集水路13Dの逆ハの字角度θが設定よりも拡がってしまうのを防止できると共に、収集水路13Dの破損を防止できる。即ち、収集水路13Dを構成する第1棒状部材13Aの長さが長い場合には、風の吹く向きに流れる表層水の流れで第1棒状部材13Aが湾曲し、逆ハの字角度θが設定よりも拡がってしまう場合が考えられる。逆ハの字角度θが設定よりも拡がると、上述の3水路の場合でも説明したが、風の向きによっては、収集水路13Dにせっかく流れ込んだアオコが再び収集水路13Dから流れ出てしまう危険がある。また、逆ハの字角度θの拡がりが大きい場合には第1棒状部材13Aが折れる等の破損につながる。 Thereby, it is possible to prevent the inverted V-shaped angle θ of the collection waterway 13D from becoming wider than the setting, and it is also possible to prevent damage to the collection waterway 13D. That is, when the length of the first rod-shaped member 13A constituting the collection waterway 13D is long, the first rod-shaped member 13A is curved by the flow of surface water flowing in the direction in which the wind blows, and the inverted V-shaped angle θ is set. There is a possibility that it will spread further than the above. As explained in the case of the three waterways mentioned above, if the inverted V-shaped angle θ becomes wider than the setting, depending on the direction of the wind, there is a risk that the blue-green algae that has flowed into the collection waterway 13D may flow out from the collection waterway 13D again. . Furthermore, if the inverted V-shaped angle θ is wide enough, the first rod-shaped member 13A may break or otherwise be damaged.

上記説明では、藻類収集手段12Aを構成する収集水路13Dと誘導水路17Bとのうち、収集水路13Dについて主として説明した。しかし、収集水路13Dで収集したアオコを如何に効率的に藻類回収手段12Bまで誘導するかが重要になる。したがって、複数の誘導水路17Bには、誘導水路17Bの表層水に収集水路13Dから藻類回収手段12Bへ向いた水流を発生させる水流発生手段33を設けることが一層好ましい。 In the above description, the collection waterway 13D was mainly explained among the collection waterway 13D and the guide waterway 17B that constitute the algae collecting means 12A. However, it is important how to efficiently guide the algae collected in the collection waterway 13D to the algae collection means 12B. Therefore, it is more preferable to provide the plurality of guiding channels 17B with a water flow generating means 33 that generates a water flow in the surface water of the guiding channels 17B from the collection channel 13D toward the algae collection means 12B.

図8は、誘導水路17Bに水流発生手段33を設けた上面図であり、図9は図8の水流発生手段33を主として説明する部分拡大斜視図である。 FIG. 8 is a top view of the water flow generation means 33 provided in the guiding waterway 17B, and FIG. 9 is a partially enlarged perspective view mainly illustrating the water flow generation means 33 of FIG. 8.

図8及び図9に示すように、水流発生手段33は、3本の誘導水路17Bにそれぞれ設けられた3基の水車33Aと、3基の水車33Aの中心を貫通支持する回転軸33Bと、誘導水路17Bを構成する4本の第2棒状部材17Aの上にそれぞれ設けられ、回転軸33Bを回転自在に支持する4基の軸受33Cと、回転軸33Bを矢印F方向に回転させる回転動力機構33Dとで構成される。 As shown in FIGS. 8 and 9, the water flow generation means 33 includes three water turbines 33A provided in each of the three guide channels 17B, and a rotating shaft 33B that penetrates and supports the centers of the three water turbines 33A. Four bearings 33C that are respectively provided on the four second rod-shaped members 17A that constitute the guiding waterway 17B and rotatably support the rotating shaft 33B, and a rotational power mechanism that rotates the rotating shaft 33B in the direction of arrow F. 33D.

回転動力機構33Dとしては、回転軸33Bの一端に第1プーリ33Eを設け、井桁構造の連結固定部材19の上に設けたモータ33Fの回転軸33Gに取り付けた第2プーリ33Hとにタイミングベルト33Jで掛け渡すことで構成されている。 As the rotational power mechanism 33D, a first pulley 33E is provided at one end of the rotating shaft 33B, and a timing belt 33J is attached to a second pulley 33H attached to the rotating shaft 33G of the motor 33F provided on the connecting and fixing member 19 having a grid structure. It is constructed by passing it over.

なお、モータ33F及び軸受33Cは防水性のものを使用することが良く、軸受33Cとしては樹脂軸受を使用することができる。また、本発明の実施の形態の藻類処理システム10では、システム全体をコントロールする制御部(図示せず)は、閉鎖水域の陸地に配置した藻類破壊装置14に設置されている。したがって、モータ33Fには、制御部からの無線指示によって制御するための無線付帯設備を設け、水流発生手段33のコントロール(例えばモータ33FのON-OFFや水車33Aの回転速度等)を行うことが好ましい。 Note that the motor 33F and the bearing 33C are preferably waterproof, and a resin bearing can be used as the bearing 33C. Further, in the algae treatment system 10 according to the embodiment of the present invention, a control unit (not shown) that controls the entire system is installed in the algae destruction device 14 placed on land in a closed water area. Therefore, it is possible to provide the motor 33F with wireless auxiliary equipment for controlling it by wireless instructions from the control unit, and to control the water flow generating means 33 (for example, ON/OFF of the motor 33F, rotation speed of the water turbine 33A, etc.). preferable.

これにより、誘導水路17Bに藻類回収手段12Bに向いた表層水の水流が発生するので、収集水路13Dによって収集されたアオコは、誘導水路17Bを速やかに流れて藻類回収手段12Bに達する。したがって、アオコを藻類回収手段12Bで一層効率的に回収することができる。 As a result, a flow of surface water directed toward the algae collection means 12B is generated in the guiding waterway 17B, so the algal blooms collected by the collection waterway 13D quickly flow through the guiding waterway 17B and reach the algae collection means 12B. Therefore, algae can be collected more efficiently by the algae collecting means 12B.

なお、図9において、第2棒状部材17Aの先端部17A1(藻類回収手段12Bの側)の径を細くしている。これは、誘導水路17Bの先端部を拡径することで、水車33Aによる表層水の強制的な水流に対する誘導水路17Bの水流抵抗が生じにくくなるので、誘導水路の流れを一層スムーズに行うことができる。 In addition, in FIG. 9, the diameter of the tip part 17A1 (algae collecting means 12B side) of the second rod-shaped member 17A is made smaller. This is because by enlarging the diameter of the tip of the guide channel 17B, water flow resistance in the guide channel 17B against the forced flow of surface water by the water turbine 33A is less likely to occur, so that the flow in the guide channel can be made smoother. can.

(藻類回収手段)
図2及び図3に示すように、藻類回収手段12Bは、藻類収集手段12Aの放射状に形成されている複数の収集水路13Dの1つに浮いた状態で配置される。
(Algae collection means)
As shown in FIGS. 2 and 3, the algae collection means 12B is arranged in a floating state in one of the plural collection channels 13D formed radially in the algae collection means 12A.

図10は、藻類回収手段12Bの斜視図である。
図10に示すように、藻類回収手段12Bは、主として、装置フレーム26と、ゴミ分離ドラム28と、ゴミ分離ドラム28を装置フレーム26に回転自在に支持する複数の支持ローラ30、30…と、ゴミ分離ドラム28を回転させるモータ32(回転動力手段)と、装置フレーム26を浮かせる浮き部材34と、吸引ノズル36と、吐出ノズル38と、複数枚のスキーマ40、40…とで構成される。
FIG. 10 is a perspective view of the algae collection means 12B.
As shown in FIG. 10, the algae collection means 12B mainly includes a device frame 26, a garbage separation drum 28, and a plurality of support rollers 30, 30, . . . that rotatably support the garbage separation drum 28 on the device frame 26. It is composed of a motor 32 (rotational power means) that rotates the dust separation drum 28, a floating member 34 that floats the device frame 26, a suction nozzle 36, a discharge nozzle 38, and a plurality of schemas 40, 40, . . .

そして、藻類収集手段12Aの収集水路13Dで収集されて誘導水路17Bを通って藻類回収手段12Bに集められたアオコは藻類回収手段12Bの吸引ノズル36から表層水と一緒に吸引される。なお、以下の説明において、アオコを含む表層水を以下「アオコ含有水」と言うことにする。 The algae collected in the collection waterway 13D of the algae collection means 12A, passed through the guide waterway 17B, and collected in the algae collection means 12B are sucked together with the surface water from the suction nozzle 36 of the algae collection means 12B. In addition, in the following description, surface water containing algae will be hereinafter referred to as "water containing algae."

装置フレーム26は、アオコ含有水が流通可能な門型形状に形成される。即ち、左右に対向して立設された四角形な一対の脚フレーム26A、26Aの上端同士を四角形な上面フレーム26Bで連結した門型形状をしたフレーム構造を有する。この門型の装置フレーム26によって、アオコ含有水を停滞させることなく装置フレーム26の前門側A(図10の表面側)から後門側B(図10の裏面側)に流通可能な水路が形成される。 The device frame 26 is formed into a gate shape through which algae-containing water can flow. That is, it has a gate-shaped frame structure in which the upper ends of a pair of rectangular leg frames 26A, 26A, which are erected to face each other on the left and right sides, are connected to each other by a rectangular upper surface frame 26B. This gate-shaped device frame 26 forms a waterway through which algae-containing water can flow from the front gate side A (front side in FIG. 10) to the rear gate side B (back side in FIG. 10) of the device frame 26 without stagnation. Ru.

装置フレーム26の材質としては、水に対して腐食しにくい材質であれば特に限定しないが、ステンレス又は硬質樹脂を好適に使用することができる。なお、装置フレーム26は、表層水を停滞させることなく流通可能なフレーム構造であれば、上記した門型形状に限定されない。 The material of the device frame 26 is not particularly limited as long as it is not easily corroded by water, but stainless steel or hard resin can be suitably used. Note that the device frame 26 is not limited to the above-described gate shape as long as it has a frame structure that allows surface water to flow without stagnation.

ゴミ分離ドラム28は、円筒形状に形成され、装置フレーム26のフレーム構造内に表層水の流通方向に直交して横向きに配置される。ゴミ分離ドラム28の大きさは、例えば直径が300mm~500mm程度、長さが500mm~1500mm程度に形成される。ゴミ分離ドラム28の材質は、水に対して腐食しにくい材質であれば特に限定しないが、ステンレスを好適に使用することができる。 The dust separation drum 28 is formed in a cylindrical shape and is disposed laterally within the frame structure of the device frame 26 orthogonal to the flow direction of surface water. The size of the dust separation drum 28 is, for example, approximately 300 mm to 500 mm in diameter and approximately 500 mm to 1500 mm in length. The material of the dust separation drum 28 is not particularly limited as long as it is not easily corroded by water, but stainless steel can be suitably used.

また、図11及び図12に示すように、ゴミ分離ドラム28の周面にはフィルタ42が形成され、周面両端部に支持ローラ30が接するための平坦部44が形成される。更に、ゴミ分離ドラム28の側面には側板46が設けられ、側板46にはアオコを表層水と一緒に吸引して取り込む吸引配管20の一方端部及びフィルタ42を洗う水を吐出する吐出配管22の一方端部をゴミ分離ドラム28内に導くための導入口48が開口されている。 Further, as shown in FIGS. 11 and 12, a filter 42 is formed on the circumferential surface of the dust separation drum 28, and flat portions 44 for contacting the support roller 30 are formed at both ends of the circumferential surface. Further, a side plate 46 is provided on the side surface of the garbage separation drum 28, and the side plate 46 has one end of a suction pipe 20 that sucks and takes in algal blooms together with surface water, and a discharge pipe 22 that discharges water that washes the filter 42. An introduction port 48 is opened to introduce one end of the dust separation drum 28 into the dust separation drum 28.

図11のゴミ分離ドラム28は、フィルタ42をパンチングメタルで形成したものであり、図12のゴミ分離ドラム28はフィルタ42を金網で形成したものである。パンチングメタル及び金網の目開き(孔径D)は、2mm~5mmの範囲が好ましい。 The dust separation drum 28 in FIG. 11 has a filter 42 made of punched metal, and the dust separation drum 28 in FIG. 12 has a filter 42 made of wire mesh. The opening (pore diameter D) of the punching metal and wire mesh is preferably in the range of 2 mm to 5 mm.

従来技術で述べたように、アオコの群体は数十~数百μmのスケールであり、フィルタ42の目開きが2mm以上であればアオコ含有水中の群体状のアオコがフィルタ42を通過可能であり、5mm以下であれば、アオコ含有水中のゴミ類等がフィルタ42を通過しないようにできる。また、詳細は後記するが、フィルタ42の目開きが5mm以下であれば、藻類破壊装置14のインペラを目詰まりさせることもない。 As described in the prior art, colonies of algae have a scale of several tens to hundreds of μm, and if the opening of the filter 42 is 2 mm or more, the algae in the form of a colony in water containing algae can pass through the filter 42. , 5 mm or less, it is possible to prevent dirt and the like in water containing blue-green algae from passing through the filter 42. Further, although details will be described later, if the opening of the filter 42 is 5 mm or less, the impeller of the algae destruction device 14 will not be clogged.

また、図10に示すように、ゴミ分離ドラム28は、装置フレーム26の対向する一対の脚フレーム26A,26Aにそれぞれ3個ずつ回転自在に片持ち支持された合計6個の支持ローラ30によってゴミ分離ドラム28の両端部周面(平坦部44)がそれぞれ3点支持される。 Further, as shown in FIG. 10, the dust separation drum 28 is supported by a total of six support rollers 30 rotatably supported by a pair of leg frames 26A, 26A of the apparatus frame 26, three of which are rotatably supported. Both end peripheral surfaces (flat parts 44) of the separation drum 28 are supported at three points, respectively.

3点支持する3個の支持ローラ30のうち、2個の支持ローラ30はゴミ分離ドラム28の端部周面の下部位置を同一の水平レベルで支持し、残りの支持ローラ30はゴミ分離ドラム28の端部周面の上端位置を支持する。3個の支持ローラ30を結ぶ形状が正三角形になるようにすることが好ましい。図10では、ゴミ分離ドラム28の端部周面の上端位置を支持する支持ローラ30は、装置フレーム26から下方に突起させたフランジ26Cに支持させている。 Of the three support rollers 30 supported at three points, two support rollers 30 support the bottom position of the end peripheral surface of the dust separation drum 28 at the same horizontal level, and the remaining support rollers 30 support the dust separation drum 28 at the same horizontal level. The upper end position of the end circumferential surface of 28 is supported. It is preferable that the shape connecting the three support rollers 30 is an equilateral triangle. In FIG. 10, the support roller 30 that supports the upper end position of the peripheral surface of the end portion of the dust separation drum 28 is supported by a flange 26C that projects downward from the device frame 26.

また、支持ローラ30は、装置フレーム26側の円板状の大径部30Aと、大径部30Aに連続する円柱状の小径部30Bとで段差構造に形成され、ゴミ分離ドラム28の端部周面に小径部30Bが接するとともに端部側面に大径部30Aが接する。このように、支持ローラ30を段差構造にすることにより、ゴミ分離ドラム28の軸芯方向へのズレを防止している。 Further, the support roller 30 is formed in a stepped structure with a disk-shaped large diameter portion 30A on the apparatus frame 26 side and a cylindrical small diameter portion 30B continuous to the large diameter portion 30A, and has a stepped structure at the end of the dust separation drum 28. The small diameter portion 30B is in contact with the circumferential surface, and the large diameter portion 30A is in contact with the end side surface. In this way, by forming the support roller 30 into a stepped structure, the dust separation drum 28 is prevented from shifting in the axial direction.

なお、支持ローラ30は、装置フレーム26に片持ち支持された軸30Cに軸受(図示せず)を介してローラ部を設ける態様、又は装置フレーム26に固定した軸受に支持ローラ30の軸30Cを支持させる態様の何れでもよい。この場合、軸受は水中での回転に好適な樹脂軸受を使用することが好ましい。 Note that the support roller 30 can be configured such that a roller portion is provided on a shaft 30C that is cantilever-supported on the device frame 26 via a bearing (not shown), or that the shaft 30C of the support roller 30 is attached to a bearing that is fixed to the device frame 26. Any mode of support may be used. In this case, it is preferable to use a resin bearing suitable for rotation in water.

また、上面フレーム26Bから水平に突出したフランジ26Dにモータ32が設置され、モータ32の回転軸32Aにプーリ50が設けられる。モータ32は、藻類収集手段12Aで述べたと同様に防水性のモータを使用することが好ましいと共に、藻類破壊装置14の制御部からの無線指示によって制御するための無線付帯設備を設け、コントロール(例えばモータのON-OFFや水車の回転速度等)を行うことが好ましい。 Further, a motor 32 is installed on a flange 26D that projects horizontally from the upper frame 26B, and a pulley 50 is installed on a rotating shaft 32A of the motor 32. The motor 32 is preferably a waterproof motor as described for the algae collection means 12A, and is provided with wireless accessory equipment for controlling by wireless instructions from the control unit of the algae destruction device 14. It is preferable to turn the motor ON and OFF, the rotation speed of the water wheel, etc.

一方、ゴミ分離ドラム28の上端位置を支持する一対の支持ローラ30のうちの一方の回転駆動用の支持ローラ30にもプーリ52が設けられる。図12では、プーリ52として支持ローラ30の大径部30Aを兼用する場合で図示したが、プーリ52を別途設けてもよい。 On the other hand, a pulley 52 is also provided on one of the pair of support rollers 30 that supports the upper end of the dust separation drum 28 for rotational driving. Although FIG. 12 shows a case in which the large diameter portion 30A of the support roller 30 is also used as the pulley 52, the pulley 52 may be provided separately.

そして、モータ32のプーリ50と支持ローラ30のプーリ52との間に無端状のタイミングベルト54が掛け渡される。これにより、モータ32を駆動するとタイミングベルト54を介して回転駆動用の支持ローラ30が回転し、更にゴミ分離ドラム28が回転する。この場合、回転駆動用の支持ローラ30の回転動力がゴミ分離ドラム28に伝達され易いように、回転駆動用の支持ローラ30の小径部30Bの周面とゴミ分離ドラム28の端部である平坦部44の周面をゴム性にして滑らないようにしたり、小径部30Bの周面と平坦部44の周面に軸芯方向に平行なストライプ溝を複数形成したりしてもよい。 An endless timing belt 54 is stretched between the pulley 50 of the motor 32 and the pulley 52 of the support roller 30. As a result, when the motor 32 is driven, the rotationally driven support roller 30 is rotated via the timing belt 54, and the dust separation drum 28 is further rotated. In this case, in order to easily transmit the rotational power of the rotationally driven support roller 30 to the dust separation drum 28, the peripheral surface of the small diameter portion 30B of the rotationally driven support roller 30 and the flat end portion of the dust separation drum 28 are The circumferential surface of the portion 44 may be made of rubber to prevent slipping, or a plurality of striped grooves parallel to the axial direction may be formed on the circumferential surface of the small diameter portion 30B and the circumferential surface of the flat portion 44.

浮き部材34は、装置フレーム26の左右両側の脚フレーム26Aに固定され、ゴミ分離ドラム28の下部が表層水中に浸漬するように装置フレーム26を浮上させる。浮き部材34としては、特に限定されず、発泡スチロール、両端が閉塞された空洞な樹脂製の筒体(例えば塩ビパイプ)等を使用できる。 The floating members 34 are fixed to the leg frames 26A on both the left and right sides of the device frame 26, and float the device frame 26 so that the lower part of the dust separation drum 28 is immersed in the surface water. The floating member 34 is not particularly limited, and may be a polystyrene foam, a hollow resin cylinder with both ends closed (for example, a PVC pipe), or the like.

図10及び図13に示すように、吸引ノズル36は、ゴミ分離ドラム28内に設けられ、吸引配管20に連通状態で支持される。また、吸引ノズル36は、ゴミ分離ドラム28の軸芯方向に長いスロット形状の吸引口36Aが表層水中に浸漬するように形成される(図1参照)。 As shown in FIGS. 10 and 13, the suction nozzle 36 is provided within the dust separation drum 28 and supported in communication with the suction piping 20. Further, the suction nozzle 36 is formed such that a slot-shaped suction port 36A that is long in the axial direction of the dust separation drum 28 is immersed in the surface water (see FIG. 1).

したがって、上記した浮き部材34は、吸引ノズル36の吸引口36Aが表層水中に浸漬するように、浮力を調整することができることが好ましい。浮き部材34の浮力を調整する方法としては、例えば両端が閉塞された空洞な樹脂製の筒体の内部に入れるウエイト調整部材の量を変える方法がある。 Therefore, it is preferable that the buoyancy of the floating member 34 described above can be adjusted so that the suction port 36A of the suction nozzle 36 is immersed in the surface water. As a method for adjusting the buoyancy of the floating member 34, for example, there is a method of changing the amount of the weight adjusting member inserted into a hollow resin cylinder whose both ends are closed.

また、吸引ノズル36は、装置フレーム26の前門側Aの方向を向いて斜め下向きに配置される(図10参照)。更に、吸引ノズル36は、吸引配管20に連通される連通口(図示せず)よりも吸引口36Aが大きなラッパ管状に形成される(図13参照)。吸引口36Aのスロット形状の開口面積はスキーマ40の矩形面積よりも大きいことが好ましい。これにより、装置フレーム26の前門側Aから後門側Bに流れるアオコ含有水が吸引ノズル36の吸引口36Aから取り込まれ易くなっている。 Further, the suction nozzle 36 is arranged diagonally downward, facing toward the front gate side A of the device frame 26 (see FIG. 10). Furthermore, the suction nozzle 36 is formed in a trumpet-like shape with a suction port 36A larger than a communication port (not shown) communicating with the suction pipe 20 (see FIG. 13). It is preferable that the slot-shaped opening area of the suction port 36A is larger than the rectangular area of the schema 40. As a result, algae-containing water flowing from the front gate side A to the rear gate side B of the device frame 26 is easily taken in through the suction port 36A of the suction nozzle 36.

図10及び図14に示すように、吐出ノズル38は、ゴミ分離ドラム28内に設けられ、吐出配管22に連通状態で支持される。また、吐出ノズル38は、ゴミ分離ドラム28の軸芯方向に長いスロット形状の吐出口38Aが表層水の水面上に露出するように形成される(図1参照)。また、吐出ノズル38は、吐出配管22に連通される連通口(図示せず)よりも吐出口38Aが小さな逆ラッパ管状に形成される(図14参照)。これにより、吐出ノズル38の吐出口38Aから洗浄水を勢いよくゴミ分離ドラム28のフィルタ42内面に吹き付けることができ、フィルタ42の洗浄効果を高めることができる。 As shown in FIGS. 10 and 14, the discharge nozzle 38 is provided within the dust separation drum 28 and supported in communication with the discharge pipe 22. Further, the discharge nozzle 38 is formed such that a slot-shaped discharge port 38A that is long in the axial direction of the dust separation drum 28 is exposed above the water surface of the surface water (see FIG. 1). Further, the discharge nozzle 38 is formed in the shape of an inverted trumpet tube in which a discharge port 38A is smaller than a communication port (not shown) communicating with the discharge pipe 22 (see FIG. 14). Thereby, the cleaning water can be vigorously sprayed onto the inner surface of the filter 42 of the dust separation drum 28 from the discharge port 38A of the discharge nozzle 38, and the cleaning effect of the filter 42 can be enhanced.

なお、図1に示すように、ゴミ分離ドラム28の外側に、フィルタ42の外面を洗浄する洗浄ノズル56を設ければ、フィルタ42の洗浄効果を更に高めることができる。この場合、洗浄ノズル56は分岐配管58を介して吐出配管22の途中に連通されるようにすることが好ましい。これにより、洗浄水のための配管を別途設ける必要がない。 Note that, as shown in FIG. 1, if a cleaning nozzle 56 for cleaning the outer surface of the filter 42 is provided outside the dust separation drum 28, the cleaning effect of the filter 42 can be further enhanced. In this case, it is preferable that the cleaning nozzle 56 be communicated with the discharge pipe 22 via the branch pipe 58. This eliminates the need to separately provide piping for cleaning water.

図10に示すように、スキーマ40は、ゴミ分離ドラム28の外面に突起した状態で複数枚設けられ、ゴミ分離ドラム28の軸芯方向に長い四角板状に形成される。したがって、スキーマ40はゴミ分離ドラム28の回転と一緒に回転し、藻類収集手段12Aの誘導水路17Bから流れてきたアオコを掻き集める。スキーマ40の数は特に限定しないが、ゴミ分離ドラム28の周方向に等間隔で4枚以上であることが好ましい。 As shown in FIG. 10, a plurality of schemata 40 are provided in a protruding state on the outer surface of the dust separation drum 28, and are formed in the shape of a rectangular plate that is long in the axial direction of the dust separation drum 28. Therefore, the schema 40 rotates together with the rotation of the garbage separation drum 28, and scrapes up the algal blooms flowing from the guiding waterway 17B of the algae collecting means 12A. Although the number of schemas 40 is not particularly limited, it is preferable that there are four or more schemata arranged at equal intervals in the circumferential direction of the dust separation drum 28.

そして、藻類回収手段12Bの吸引ノズル36によって吸引されたアオコ含有水は、陸地に配置された藻類破壊装置14に送液される。図1に示すように、藻類回収手段12Bは、吸引配管20と吐出配管22とにより藻類破壊装置14に連結される。また、吐出配管22に圧力調整手段16が設けられるとともに、圧力調整手段16と藻類破壊装置14との間に圧力計24が設けられる。 The algae-containing water sucked by the suction nozzle 36 of the algae collection means 12B is sent to the algae destruction device 14 located on land. As shown in FIG. 1, the algae collection means 12B is connected to the algae destruction device 14 through a suction pipe 20 and a discharge pipe 22. Further, a pressure regulating means 16 is provided in the discharge pipe 22, and a pressure gauge 24 is provided between the pressure regulating means 16 and the algae destruction device 14.

次に、藻類処理システム10の藻類破壊装置14について説明する。 Next, the algae destruction device 14 of the algae treatment system 10 will be explained.

(藻類破壊装置)
図15の(A)は多段渦巻ポンプ構造の浮遊藻類破壊装置14の全体構成図であり、(B)は多段渦巻ポンプ構造の内部の一部を拡大した断面図である。
(algae destruction device)
FIG. 15(A) is an overall configuration diagram of the floating algae destruction device 14 having a multi-stage volute pump structure, and FIG. 15(B) is an enlarged cross-sectional view of a part of the inside of the multi-stage volute pump structure.

多段渦巻ポンプ構造の藻類破壊装置14は、ケーシング62内にインペラ64(羽根車)を備えたインペラ室66を複数段形成し、1段の場合より圧力が上がるように構成したものである。浮遊藻類破壊装置14は、陸地18に設置した架台68上に設置される。 The algae destruction device 14 having a multi-stage centrifugal pump structure is configured such that a plurality of impeller chambers 66 each having an impeller 64 (impeller) are formed in a casing 62 so that the pressure is higher than in the case of one stage. The floating algae destruction device 14 is installed on a pedestal 68 installed on land 18.

図15(A)に示すように、円筒形状のケーシング62の一方端側の側面中央部にポンプ入口70が開口され、他方端部に形成され内部に排出室が形成された排出部72の周面にポンプ出口74が開口される。そして、ポンプ入口70に吸引配管20の他方端が接続され、ポンプ出口74に吐出配管22の他方端が接続される。 As shown in FIG. 15(A), a pump inlet 70 is opened at the center of the side surface of one end of a cylindrical casing 62, and a discharge part 72 is formed at the other end and has a discharge chamber formed therein. A pump outlet 74 is opened in the surface. The other end of the suction pipe 20 is connected to the pump inlet 70, and the other end of the discharge pipe 22 is connected to the pump outlet 74.

また、排出部72に隣接してインペラ64を回転するモータ76が配置される。モータ76の回転軸76Aはケーシング62を貫通して取り付けられ、ケーシング62と回転する回転軸76Aとの間隙から水が漏れないように軸シール(図示せず)が施される。なお、回転軸76Aを支持する軸受については図示を省略している。 Further, a motor 76 for rotating the impeller 64 is arranged adjacent to the discharge section 72 . The rotating shaft 76A of the motor 76 is attached to pass through the casing 62, and a shaft seal (not shown) is applied to prevent water from leaking from the gap between the casing 62 and the rotating rotating shaft 76A. Note that illustration of a bearing that supports the rotating shaft 76A is omitted.

また、ケーシング62内は3枚の仕切壁78によって4つのインペラ室66に分割され、4段の多段渦巻ポンプ構造に形成される。なお、図15では4段の多段渦巻ポンプ構造の一例で説明するが、段数は4段~10段の範囲であることが好ましい。また、圧力は0.5MPa(5kgf/cm)以上の能力を有することが好ましい。 Furthermore, the inside of the casing 62 is divided into four impeller chambers 66 by three partition walls 78, forming a four-stage multi-stage centrifugal pump structure. Although FIG. 15 illustrates an example of a four-stage multi-stage centrifugal pump structure, the number of stages is preferably in the range of 4 to 10 stages. Moreover, it is preferable to have a pressure capacity of 0.5 MPa (5 kgf/cm 2 ) or more.

また、3枚の仕切壁78の中心部には連通口80がそれぞれ開口される。そして、4つのインペラ室66にはそれぞれインペラ64が配設され、それぞれのインペラ64は3つの連通口80を通して配設されたモータ76の回転軸76Aに支持される。仕切壁78に形成された連通口80の直径はモータ76の回転軸76Aの直径よりも大きく形成され、連通口80を介して4つのインペラ室66が連通される。 Furthermore, communication ports 80 are opened in the centers of the three partition walls 78, respectively. An impeller 64 is disposed in each of the four impeller chambers 66, and each impeller 64 is supported by a rotating shaft 76A of a motor 76 disposed through three communication ports 80. The diameter of the communication port 80 formed in the partition wall 78 is larger than the diameter of the rotating shaft 76A of the motor 76, and the four impeller chambers 66 are communicated through the communication port 80.

図15(B)に示すように、インペラ64は、複数枚からなる羽根64Aの両側を2枚のシュラウト64B(側板)で覆い、2枚のシュラウト64Bのうちのポンプ入口70側のシュラウト中心部に吸込口82を形成し、周縁部に排出隙間84を形成したクローズド型のインペラ64が設けられる。インペラ64の排出隙間84の幅Wは4mm~10mmが好ましく、より好ましくは5mm~7mmである。 As shown in FIG. 15(B), the impeller 64 has two shrouds 64B (side plates) covering both sides of a plurality of blades 64A, and a center portion of the shrout on the pump inlet 70 side of the two shrouds 64B. A closed-type impeller 64 is provided, which has a suction port 82 formed therein and a discharge gap 84 formed around its periphery. The width W of the discharge gap 84 of the impeller 64 is preferably 4 mm to 10 mm, more preferably 5 mm to 7 mm.

そして、モータ76を駆動して4枚のインペラ64を高速回転すると、インペラ64の外周部が遠心力の作用で高圧になり、インペラ64の中心部は遠心力がほとんど作用しないため低圧になる。これにより、ケーシング62のポンプ入口70が低圧になりポンプ入口70に吸引力が発生し、この吸引力によって藻類回収手段12Bの吸引ノズル36からアオコ含有水が吸引される。 When the motor 76 is driven to rotate the four impellers 64 at high speed, the outer circumference of the impeller 64 becomes high pressure due to the action of centrifugal force, and the center part of the impeller 64 becomes low pressure because almost no centrifugal force acts thereon. As a result, the pressure at the pump inlet 70 of the casing 62 becomes low, and a suction force is generated at the pump inlet 70, and the algae-containing water is sucked from the suction nozzle 36 of the algae collection means 12B by this suction force.

また、図1に示すように、吐出配管22の途中には、圧力調整手段16が設けられるとともにポンプ出口74と圧力調整手段16との間に圧力計24が設けられる。圧力調整手段16は、吐出配管22の流路を絞ることによって多段渦巻ポンプ構造の吐出圧力を高めるものであり、吐出圧力を0.5MPa(5kgf/cm)以上、1.0MPa(10kgf/cm)以下に調整することが好ましい。 Further, as shown in FIG. 1, a pressure adjustment means 16 is provided in the middle of the discharge pipe 22, and a pressure gauge 24 is provided between the pump outlet 74 and the pressure adjustment means 16. The pressure adjustment means 16 increases the discharge pressure of the multistage centrifugal pump structure by narrowing the flow path of the discharge piping 22, and increases the discharge pressure to 0.5 MPa (5 kgf/cm 2 ) or more, 1.0 MPa (10 kgf/cm 2 ) or more. 2 ) It is preferable to adjust to the following.

クローズド型のインペラ64は、液体に効率良く遠心力を与えることができるが、インペラ64の排出隙間84は上記の如く狭く、アオコ含有水中のアオコ等の異物が詰まり易い。したがって、藻類回収手段12Bのゴミ分離ドラム28のフィルタ42の目開きを、インペラ64の排出隙間84の幅Wよりも小さく設定することが好ましい。 Although the closed type impeller 64 can efficiently apply centrifugal force to the liquid, the discharge gap 84 of the impeller 64 is narrow as described above, and is easily clogged with foreign matter such as algae in the algae-containing water. Therefore, it is preferable that the opening of the filter 42 of the dust separation drum 28 of the algae collecting means 12B is set smaller than the width W of the discharge gap 84 of the impeller 64.

[アオコ処理方法]
次に、上記の如く構成された藻類処理システム10によって閉鎖水域に発生したアオコを藻類収集手段12Aで収集した後、藻類回収手段12Bで回収し、最終的に藻類破壊装置14でアオコを破壊するまでの処理方法を説明する。
[Blue-green algae treatment method]
Next, algae generated in the closed water area by the algae treatment system 10 configured as described above is collected by the algae collection means 12A, then collected by the algae collection means 12B, and finally the algae destruction device 14 destroys the algae. The processing method up to this point will be explained.

図16は、閉鎖水域15の一例として、瓢箪形状の沼15Aに発生したアオコが吹き溜まりに堆積している図であり、堆積されたアオコを本発明の実施の形態の藻類処理システム10によって処理する一例である。 FIG. 16 is a diagram showing, as an example of the closed water area 15, algal blooms generated in a gourd-shaped swamp 15A are deposited in a snowdrift, and the accumulated blue-green blooms are treated by the algae treatment system 10 according to the embodiment of the present invention. This is an example.

図16において、網目形状で示した部分は、沼15AにM方向の風が吹いたときに、沼15Aの一方側の吹き溜まり部に堆積したアオコ群体35,35を示す。また、ドット形状で示した部分は、沼15AにN方向の風が吹いたときに、沼15Aの他方側の吹き溜まり部に堆積したアオコ群体37,37を示す。 In FIG. 16, the mesh-shaped portion indicates algae colonies 35, 35 that were deposited in a snowdrift on one side of the swamp 15A when the wind in the M direction blows in the swamp 15A. Furthermore, the dot-shaped portions indicate algae colonies 37, 37 that were deposited in the snowdrift on the other side of the swamp 15A when the wind in the N direction blows in the swamp 15A.

この場合、沼15Aの広さや形によって、アオコを収集及び回収する藻類除去装置12Aの設置数や設置場所を適宜選定することができるが、ここでは瓢箪形状の沼15Aの両端エリアに藻類除去装置12Aをそれぞれ(合計2基)設けた場合で説明する。 In this case, depending on the size and shape of the swamp 15A, the number and installation locations of the algae removal devices 12A for collecting and recovering blue-green algae can be appropriately selected. A case will be explained in which 12A each (two units in total) are provided.

先ず、藻類除去装置12における藻類収集手段12Aの作用について説明する。 First, the operation of the algae collection means 12A in the algae removal device 12 will be explained.

図16に示すように、藻類収集手段12Aの藻類収集部13は、浮遊するアオコが流入するための逆ハの字状の収集水路13Dを放射状に4水路形成している。これにより、4水路の収集水路13Dは、沼15Aの東西南北の全方位をカバーすることができる。また、本実施の形態では、4水路の収集水路13Dのうち、アオコ群体35,37が堆積された吹き溜まりに流入口13Bが向いていない収集水路13Dに藻類回収手段12Bを配置することで、主として残りの3水路でアオコを収集するようにした。 As shown in FIG. 16, the algae collection section 13 of the algae collection means 12A has four radial inverted V-shaped collection channels 13D into which floating algal blooms flow. Thereby, the four collection waterways 13D can cover all directions of the swamp 15A, north, south, east and west. Moreover, in this embodiment, by arranging the algae collecting means 12B in the collecting channel 13D among the four collecting channels 13D, where the inlet 13B is not facing the snowdrift where the algae colonies 35 and 37 are deposited, the algae collecting means 12B is mainly Blue-green algae was collected from the remaining three waterways.

これにより、沼15Aに矢印M、N,K,Rの何れかの向きの風が吹いて表層水の流れる方向が変化し、表層水の流れに乗ってアオコ群体35,37の流れる方向もそれに応じて変化する場合であっても、アオコ群体35,37の大分部は何れかの収集水路13D(1つ又は複数)に流れ込む。 As a result, wind blows in the direction of arrows M, N, K, and R in the swamp 15A, changing the direction in which the surface water flows, and the direction in which the algae colonies 35 and 37 flow along with the flow of the surface water also changes accordingly. Even if it changes accordingly, most of the algae colonies 35, 37 flow into any one of the collection channels 13D (one or more).

したがって、沼15Aに発生したアオコを、沼15Aに吹く風の向きに関係なく効率的に収集することができる。更には、複数の収集水路13Dごとに藻類回収手段12Bを備える必要がないので、藻類回収手段12Bの装置コストも低く抑えることができる。 Therefore, blue-green algae occurring in the swamp 15A can be efficiently collected regardless of the direction of the wind blowing in the swamp 15A. Furthermore, since it is not necessary to provide the algae collection means 12B for each of the plurality of collection channels 13D, the device cost of the algae collection means 12B can also be kept low.

図16では、2基の藻類除去装置12を使用したが、沼15Aの大きさが小さい場合には、沼15Aの中央部に1基の藻類除去装置12を設定することで対応も可能である。 In FIG. 16, two algae removal devices 12 are used, but if the size of the swamp 15A is small, it is also possible to set one algae removal device 12 in the center of the swamp 15A. .

そして、4水路の収集水路13Dの何れかに流れ込んだアオコは誘導水路17Bを通って藻類回収手段12Bに導かれ、藻類回収手段12Bで回収される。 The algal blooms that have flowed into any of the four collection channels 13D are guided to the algae collection means 12B through the guide waterway 17B and collected by the algae collection means 12B.

ちなみに、図17は、従来技術(特許文献3)の誘導手段39Aを備えた水質保全装置39でアオコ群体35,37を収集する場合である。 Incidentally, FIG. 17 shows a case where blue-green algae colonies 35 and 37 are collected using a water quality maintenance device 39 equipped with a guiding means 39A according to the prior art (Patent Document 3).

従来技術の水質保全装置39の誘導手段39Aは、1方向のみの表層水の流れにしか対応できないので、図17に示すように、吹き溜まり部に堆積した4つのアオコ群体35,37を収集するには、アオコ群体35,37ごとに4基の水質保全装置39を設置しなくてはならず、効率が悪いと共に装置コストが高くなる。 Since the guiding means 39A of the water quality maintenance device 39 of the prior art can only handle the flow of surface water in one direction, it is difficult to collect the four algae colonies 35 and 37 deposited in the snowdrift as shown in FIG. In this case, four water quality maintenance devices 39 must be installed for each blue-green algae colony 35, 37, resulting in poor efficiency and high device cost.

また、本発明の好ましい態様の藻類収集手段12Aは、収集及び回収の効率を高めるための以下の好ましい構成を行っている。 Moreover, the algae collection means 12A of the preferred embodiment of the present invention has the following preferred configuration for increasing collection and recovery efficiency.

即ち、収集水路13Dの第1棒状部材13Aにシート状部材25を表層水中に垂下させるようにしたので、収集水路13Dに流れ込んだアオコを確実に収集できる。 That is, since the sheet-like member 25 is made to hang down into the surface water from the first rod-like member 13A of the collection waterway 13D, the algae that has flowed into the collection waterway 13D can be reliably collected.

また、本発明における好ましい態様の藻類収集手段12Aでは、収集水路13Dの第1棒状部材13Aを入れ子構造にして伸縮自在にしたので、沼15Aの大きさに応じて収集水路13Dの大きさを可変できる。更には、収集水路13Dの第1棒状部材13Aを入れ子構造にして伸縮自在にしたので、沼15Aの形状に応じて複数本の第1棒状部材13Aの長さをそれぞれ変えることで、収集水路13Dの逆ハの字角度θを維持したまま、複雑な形状の沼15Aにも放射状に収集水路13Dを形成することができる。 In addition, in the algae collection means 12A of the preferred embodiment of the present invention, the first rod-shaped member 13A of the collection waterway 13D is made into a nested structure so that it can be expanded and contracted, so that the size of the collection waterway 13D can be changed according to the size of the swamp 15A. can. Furthermore, since the first rod-like members 13A of the collection waterway 13D are made to have a nested structure and are expandable, the lengths of the plurality of first rod-like members 13A can be changed according to the shape of the swamp 15A. The collection channels 13D can be formed radially even in the complex-shaped swamp 15A while maintaining the inverted V-shaped angle θ.

上記の如く、藻類収集手段12Aの収集水路13Dで収集されたアオコは、誘導水路17Bを通って藻類回収手段12Bで回収される。 As mentioned above, the algae collected in the collection waterway 13D of the algae collection means 12A passes through the guide waterway 17B and is collected by the algae collection means 12B.

この回収において、本発明における好ましい態様の藻類収集手段12Aでは、複数の誘導水路17Bに収集水路13Dから藻類回収手段12Bへ向いた表層水の水流を発生させる水流発生手段33を設けるようにした。これにより、誘導水路17B内に表層水の滞留が発生するのを防止できるので、沼15Aに発生したアオコ群体35,37を一層効率的に収集して回収することができる。 In this collection, the algae collection means 12A of the preferred embodiment of the present invention is provided with a water flow generation means 33 that generates a water flow of surface water directed from the collection waterway 13D toward the algae collection means 12B in the plurality of guiding waterways 17B. This can prevent surface water from accumulating in the guiding waterway 17B, making it possible to more efficiently collect and recover the blue-green algae colonies 35, 37 that have occurred in the swamp 15A.

次に、藻類回収手段12Bの作用を説明する。 Next, the operation of the algae collection means 12B will be explained.

藻類回収手段12Bは、藻類収集手段12Aでアオコと一緒に収集された沼15Aのゴミ類を分離してアオコを選択的に回収する機構を備えている。即ち、ゴミ分離ドラム28内に設けられた吸引ノズル36の吸引口36Aが表層水中に浸漬する。ただし、ゴミ分離ドラム28の側板46に形成した導入口48が表層水中に浸漬しないようにする。 The algae collection means 12B is equipped with a mechanism for selectively collecting the algae by separating the garbage in the swamp 15A collected together with the algae by the algae collection means 12A. That is, the suction port 36A of the suction nozzle 36 provided in the dust separation drum 28 is immersed in the surface water. However, the introduction port 48 formed in the side plate 46 of the dust separation drum 28 should not be immersed in the surface water.

そして、藻類回収手段12Bのモータ32を駆動して、ゴミ分離ドラム28を図1の矢印方向Xに回転させる。これにより、ゴミ分離ドラム28の外面に突起された複数枚のスキーマ40によって、藻類回収手段12Bの周囲に浮遊するアオコが掻き集められると共に、門型の装置フレーム26の前門側Aからゴミ分離ドラム28の下部を通過して後門側Bにアオコ含有水の流れが形成される。 Then, the motor 32 of the algae collecting means 12B is driven to rotate the dust separation drum 28 in the direction of the arrow X in FIG. As a result, algal blooms floating around the algae collection means 12B are scraped up by the plurality of schemata 40 protruding from the outer surface of the garbage separation drum 28, and the garbage separation drum 28 is removed from the front gate side A of the gate-shaped device frame 26. A flow of algae-containing water is formed on the posterior gate side B by passing through the lower part of the water.

この場合、装置フレーム26を前門側Aから後門側Bにアオコ含有水が流通可能な門型形状とし、さらに装置フレーム26に回転自在に片持ち支持された6個の支持ローラ30でゴミ分離ドラム28の両端部周面を3点支持するようにしたので、アオコやゴミ類が装置フレーム26や支持ローラ30に引っ掛かり、アオコ含有水の流れを停滞させることを防止できる。これにより、アオコ含有水中のアオコを吸引ノズル36の吸引口36Aから効率的に吸引することができるだけでなく、ゴミ類が滞留しないのでメンテナンスが容易になる。 In this case, the device frame 26 is formed into a gate shape that allows water containing algae to flow from the front gate side A to the rear gate side B, and furthermore, six support rollers 30 rotatably supported by the device frame 26 are connected to a dust separation drum. Since the circumferential surface of both ends of the tube 28 is supported at three points, it is possible to prevent algal blooms and dirt from getting caught on the device frame 26 and the support rollers 30 and stagnate the flow of algae-containing water. Thereby, not only can the algal blooms in the algae-containing water be efficiently suctioned from the suction port 36A of the suction nozzle 36, but also maintenance is facilitated since no dirt remains.

また、装置フレーム26に回転自在に片持ち支持された6個の支持ローラ30でゴミ分離ドラム28の両端部周面を3点支持することにより、ゴミ分離ドラム28を安定に支持することができる。一方、スキーマ40でアオコと一緒に掻き集められたゴミ類は、ゴミ分離ドラム28のフィルタ42で分離され、門型の装置フレーム26の前門側Aから後門側Bに流れる表層水の流れに乗って装置フレーム26の後門側Bから沼15Aに戻る。 Further, by supporting the circumferential surface of both ends of the dust separation drum 28 at three points with six support rollers 30 rotatably supported by the device frame 26, the dust separation drum 28 can be stably supported. . On the other hand, the garbage collected together with algae in the schema 40 is separated by the filter 42 of the garbage separation drum 28, and is carried on the flow of surface water flowing from the front gate side A to the rear gate side B of the gate-shaped device frame 26. Return to the swamp 15A from the rear gate side B of the device frame 26.

これにより、アオコ等の浮遊藻類のみを選択的に収集することができ、メンテナンスもほとんど必要ない藻類回収手段12Bを提供することができる。 Thereby, it is possible to provide an algae collection means 12B that can selectively collect only floating algae such as blue-green algae and requires almost no maintenance.

そして、吸引ノズル36の吸引口36A吸引されたアオコ含有水は、吸引配管20を通ってアオコを破壊する藻類破壊装置14に送られる。 The algae-containing water sucked into the suction port 36A of the suction nozzle 36 is sent through the suction pipe 20 to the algae destruction device 14 that destroys the algae.

次に、藻類回収手段12Bで回収したアオコを破壊する藻類破壊装置14の作用について説明する。 Next, the operation of the algae destruction device 14 for destroying the algae collected by the algae collection means 12B will be explained.

即ち、多段渦巻ポンプ構造の藻類破壊装置14のモータ76を駆動して、4つのインペラ64を高速回転させる。これにより、藻類破壊装置14のケーシング62のポンプ入口70に吸引力が発生するので、吸引配管20を介して藻類回収手段12Bの吸引ノズル36に吸引力が付与される。したがって、スキーマ40で掻き集められたアオコ含有水はゴミ分離ドラム28のフィルタ42を通過して吸引ノズル36の吸引口36Aから吸引配管20に取り込まれ、吸引配管20を流れて藻類破壊装置14に送液される。 That is, the motor 76 of the algae destruction device 14 having a multi-stage centrifugal pump structure is driven to rotate the four impellers 64 at high speed. As a result, a suction force is generated at the pump inlet 70 of the casing 62 of the algae destruction device 14, so that the suction force is applied to the suction nozzle 36 of the algae collection means 12B via the suction pipe 20. Therefore, the blue-green algae-containing water collected by the schema 40 passes through the filter 42 of the garbage separation drum 28, is taken into the suction pipe 20 from the suction port 36A of the suction nozzle 36, flows through the suction pipe 20, and is sent to the algae destruction device 14. liquid.

藻類破壊装置14に送液されたアオコ含有水は、ケーシング62のポンプ入口70から1段目のインペラ室66に取り込まれる。そして、アオコ含有水は1段目のインペラ64の吸込口82から吸い込まれ、遠心力によって排出隙間84からケーシング62の内面に向かって高圧で吐出される。 The blue-green algae-containing water sent to the algae destruction device 14 is taken into the first-stage impeller chamber 66 from the pump inlet 70 of the casing 62 . The blue-green algae-containing water is sucked in from the suction port 82 of the first-stage impeller 64, and is discharged at high pressure from the discharge gap 84 toward the inner surface of the casing 62 due to centrifugal force.

これにより、アオコ含有水中のアオコがケーシング62の内面に勢い良く衝突するので、アオコの群体が細かく分断処理されるとともに、アオコの細胞のガス胞が破壊処理される。更には、藻類破壊装置14のケーシング62内に一定の高圧(0.5MPa以上)を加えることでアオコの細胞のガス胞を効率的に破壊することができる。 As a result, the blue-green algae in the blue-green algae-containing water collide with the inner surface of the casing 62 with great force, so that the colony of blue-green algae is finely divided and the gas sacs of the cells of the blue-green algae are destroyed. Furthermore, by applying a certain high pressure (0.5 MPa or more) inside the casing 62 of the algae destruction device 14, the gas sacs of the algae cells can be efficiently destroyed.

この場合、アオコ等の浮遊藻類の種類によって、分断処理及び破壊処理に適切な藻類破壊装置14の圧力が異なるので、圧力調整手段16によって調整することが好ましい。 In this case, since the appropriate pressure of the algae destruction device 14 for dividing and destroying varies depending on the type of floating algae such as blue-green algae, it is preferable to adjust the pressure using the pressure adjustment means 16.

1段目のインペラ64の排出隙間84から吐出されたアオコ含有水は、1段目の仕切壁78の連通口80から2段目のインペラ室66に流速を上げて流入し、2段目のインペラ64によって1段目のインペラ64と同様の分断処理及び破壊処理が行われる。同様に、アオコ含有水は3段目及び4段目のインペラ64によって更に分断処理及び破壊処理が繰り返された後、排出部72のポンプ出口74から吐出配管22に排出される。 The blue-green algae-containing water discharged from the discharge gap 84 of the first-stage impeller 64 flows into the second-stage impeller chamber 66 from the communication port 80 of the first-stage partition wall 78 at an increased flow rate, and flows into the second-stage impeller chamber 66. The impeller 64 performs the same dividing and breaking processes as the first-stage impeller 64 . Similarly, the algae-containing water is further subjected to repeated dividing and destruction processes by the third and fourth impellers 64, and then is discharged from the pump outlet 74 of the discharge section 72 to the discharge pipe 22.

このように、多段渦巻ポンプ構造の藻類破壊装置14は、インペラ64の段数が増えるごとにアオコ含有水の流速が上昇してインペラ64の排出隙間84からケーシング62の内面にアオコ含有水が勢いよく衝突してアオコを破壊する衝突破壊と、ケーシング62内に一定の高圧(0.5MPa以上)を加えてアオコを破壊する圧力破壊との2つの破壊作用を多段に行うことができる。これにより、アオコ含有水中のアオコの群体を効率的に分断及び破壊することができる。 In this way, in the algae destruction device 14 having a multi-stage centrifugal pump structure, as the number of stages of the impeller 64 increases, the flow rate of the water containing algae increases, and the water containing algae increases from the discharge gap 84 of the impeller 64 to the inner surface of the casing 62. Two destructive actions can be performed in multiple stages: collision destruction in which the algae are destroyed by collision, and pressure destruction in which a certain high pressure (0.5 MPa or more) is applied within the casing 62 to destroy the algae. Thereby, colonies of blue-green algae in water containing blue-green algae can be efficiently divided and destroyed.

ちなみに、アオコ含有水に含有されるアオコの全てを分断及び破壊した場合を100%とした場合、従来の藻類破壊装置のアオコの分断処理効果及び破壊処理効果は80%程度が限界であったが、本発明における藻類破壊装置14は略90%以上にすることができる。即ち、本発明の藻類処理システム10で採用した藻類破壊装置14でアオコ含有水を処理することによって、分断処理や破壊処理での未処理なアオコを略無くすことができる。これにより、本発明の藻類処理システム10で処理したアオコ含有水を沼15Aに戻してもアオコの増殖を確実に抑制することができる。 By the way, when dividing and destroying all of the algal blooms contained in algae-containing water is taken as 100%, the effectiveness of conventional algae destruction devices for dividing and destroying algal blooms was limited to about 80%. , the algae destruction device 14 in the present invention can be approximately 90% or more. That is, by treating algae-containing water with the algae destruction device 14 employed in the algae treatment system 10 of the present invention, it is possible to substantially eliminate untreated algae in the dividing or destruction treatment. Thereby, even if the algae-containing water treated with the algae treatment system 10 of the present invention is returned to the swamp 15A, the growth of algal blooms can be reliably suppressed.

上記の藻類破壊装置14によるアオコの分断処理及び破壊処理において、アオコ含有水中に気泡が混在している場合、藻類破壊装置14において圧力低下が生じ、分断処理及び破壊処理の効果が低減し易い。 In the above algae destruction device 14, when air bubbles are mixed in the algae-containing water in the algae destruction device 14, a pressure drop occurs in the algae destruction device 14, which tends to reduce the effectiveness of the algae destruction device 14.

この対策として、図18に示すように藻類破壊装置14と吸引配管20との間に脱気槽60(脱気手段)を設けることが好ましい。即ち、藻類回収手段12Bの吸引ノズル36で吸引されたアオコ含有水を脱気槽60に流入させて貯留することにより、アオコ含有水中の気泡を脱気する。この場合、吸引ノズル36の吸引力として、藻類破壊装置14で発生する吸引力を利用できないので、吸引配管20に取水ポンプ(図示せず)を備える。 As a countermeasure against this, it is preferable to provide a deaeration tank 60 (deaeration means) between the algae destruction device 14 and the suction pipe 20, as shown in FIG. That is, the algae-containing water sucked by the suction nozzle 36 of the algae collection means 12B is caused to flow into the degassing tank 60 and stored therein, thereby deaerating the air bubbles in the algae-containing water. In this case, since the suction force generated by the algae destruction device 14 cannot be used as the suction force of the suction nozzle 36, the suction pipe 20 is provided with a water intake pump (not shown).

そして、藻類破壊装置14を縦向きに配置して、ケーシング62のポンプ入口70が脱気槽60に貯留されたアオコ含有水中の槽底近くに位置するように設置する。これにより、藻類破壊装置14に取り込まれるアオコ含有水中の気泡を無くすことができるので、分断処理及び破壊処理の効果を低減させることがない。 Then, the algae destruction device 14 is arranged vertically so that the pump inlet 70 of the casing 62 is located near the bottom of the algae-containing water stored in the deaeration tank 60. This makes it possible to eliminate air bubbles in the algae-containing water that is taken into the algae destruction device 14, so that the effects of the dividing treatment and destruction treatment are not reduced.

なお、図18では、脱気手段として脱気槽60を設けることで説明したが、吸引配管20の途中に真空ポンプを備えた脱気装置(図示せず)を配設するようにしてもよい。 In addition, in FIG. 18, the explanation has been made by providing the deaeration tank 60 as a deaeration means, but a deaeration device (not shown) equipped with a vacuum pump may be provided in the middle of the suction piping 20. .

なお、藻類破壊装置14で分断処理及び破壊処理がなされた後の処理水をアオコ含有処理水と言うことにする。 It should be noted that the treated water that has been subjected to the dividing treatment and destruction treatment in the algae destruction device 14 will be referred to as blue-green algae-containing treated water.

次に、藻類破壊装置14から吐出配管22に排出されたアオコ含有処理水は、吐出ノズル38の吐出口38Aからゴミ分離ドラム28の内面に向けて勢いよく吐出される。これにより、ゴミ分離ドラム28の表面にポリエチレン袋等のゴミが張り付いていても、ゴミ分離ドラム28の内側から吐出される水により、張り付いたゴミを吹き飛ばしてフィルタ42から引きはがすことができる。 Next, the algae-containing treated water discharged from the algae destruction device 14 to the discharge pipe 22 is vigorously discharged from the discharge port 38A of the discharge nozzle 38 toward the inner surface of the dust separation drum 28. As a result, even if garbage such as a polyethylene bag is stuck to the surface of the garbage separation drum 28, the water discharged from the inside of the garbage separation drum 28 can blow away the stuck garbage and peel it off from the filter 42. .

また、吐出配管22から分岐した分岐配管58によって、吐出配管22を流れるアオコ含有処理水の一部は洗浄ノズル56からゴミ分離ドラム28のフィルタ42の外面に向けて勢いよく吐出される。フィルタ42の洗浄能力を有する吐出圧力としては0.1MPaあればよい。したがって、藻類破壊装置14の圧力が0.5MPa以上を確保し、且つ吐出ノズル38及び洗浄ノズル56からの吐出圧力が0.1MPaになるように圧力調整手段16を調整すればよい。 In addition, by a branch pipe 58 branching from the discharge pipe 22, a part of the algae-containing treated water flowing through the discharge pipe 22 is vigorously discharged from the cleaning nozzle 56 toward the outer surface of the filter 42 of the dust separation drum 28. The discharge pressure that has the ability to clean the filter 42 only needs to be 0.1 MPa. Therefore, the pressure adjustment means 16 may be adjusted so that the pressure of the algae destruction device 14 is 0.5 MPa or more, and the discharge pressure from the discharge nozzle 38 and the cleaning nozzle 56 is 0.1 MPa.

これにより、アオコ含有処理水によってゴミ分離ドラム28のフィルタ42を自動洗浄することができる。この場合、アオコ含有処理水中のアオコは、従来技術で述べたアオコの群体(数十~数百μmスケール)よりも更に細かいので、フィルタ42を目詰まりさせることはない。 Thereby, the filter 42 of the dust separation drum 28 can be automatically cleaned with the treated water containing blue-green algae. In this case, the algae in the algae-containing treated water are finer than the algae colonies (scale of several tens to hundreds of μm) described in the prior art, so they do not clog the filter 42.

そして、自動洗浄によりフィルタ42から除去されたゴミ類は、門型の装置フレーム26の前門側Aから後門側Bに至る表層水の流れによって装置フレーム26の後門側Bから沼15Aに戻る。 Then, the dirt removed from the filter 42 by automatic cleaning returns to the swamp 15A from the rear gate side B of the device frame 26 by the flow of surface water from the front gate side A to the rear gate side B of the gate-shaped device frame 26.

これにより、本発明の浮遊藻類処理システム10は、藻類収集手段12Aによって、沼15A等の閉鎖水域15に吹く風の向きに関係なく、アオコを効率的に収集して、藻類回収手段12Bで回収できるだけでなく、藻類回収手段12Bのメンテナンスがほとんど必要ない。更には、上記構造の藻類破壊装置14によって優れた分断処理効果及び破壊処理効果を達成することができる。 As a result, the floating algae treatment system 10 of the present invention allows the algae collection means 12A to efficiently collect algae regardless of the direction of the wind blowing in the closed water area 15 such as the swamp 15A, and the algae collection means 12B to collect the algae. Not only this, but also almost no maintenance of the algae collection means 12B is required. Furthermore, the algae destruction device 14 having the above structure can achieve excellent dividing and destruction effects.

なお、図示しないが、アオコ含有処理水が吐出ノズル38の吐出口38Aからゴミ分離ドラム28の内面に向けて勢いよく吐出されることを利用して、水圧で水車のようにゴミ分離ドラム28を回転することでモータ32を使用しない構成は可能である。即ち、ゴミ分離ドラム28の内面に水車の羽根を複数枚形成し、吐出ノズル38の吐出口38Aからのアオコ含有処理水を羽根に当てることでゴミ分離ドラム28を回転させる。 Although not shown, the fact that the treated water containing algae is vigorously discharged from the discharge port 38A of the discharge nozzle 38 toward the inner surface of the garbage separation drum 28 is used to move the garbage separation drum 28 like a water wheel using water pressure. A configuration in which the motor 32 is not used by rotating is possible. That is, a plurality of water wheel blades are formed on the inner surface of the garbage separation drum 28, and the garbage separation drum 28 is rotated by applying the algae-containing treated water from the discharge port 38A of the discharge nozzle 38 to the blades.

[藻類処理システムの別形態]
図19の藻類処理システム10は、上記した藻類回収手段12Bの装置フレーム26に多段渦巻ポンプ構造の浮遊藻類破壊装置14を搭載して一体型とした場合の斜視図である。上記した別体型の藻類処理システム10も一体型の浮遊藻類処理システム10も構成する部材は同様であるので、構成部材の説明は省略する。
[Another form of algae treatment system]
The algae treatment system 10 of FIG. 19 is a perspective view in which the floating algae destruction device 14 having a multi-stage volute pump structure is mounted on the device frame 26 of the algae collection means 12B described above to form an integrated system. Since the components constituting the separate algae treatment system 10 and the integrated floating algae treatment system 10 described above are the same, explanations of the components will be omitted.

また、図19の一体型の浮遊藻類処理システム10には、別体型で説明した圧力計24、洗浄ノズル56、脱気槽60(脱気手段)については図示していない。 Furthermore, the integrated floating algae treatment system 10 in FIG. 19 does not show the pressure gauge 24, cleaning nozzle 56, and deaeration tank 60 (deaeration means), which were explained separately.

このように、藻類処理システム10を一体型にすることにより、藻類処理システム10をコンパクト化できるだけでなく、運搬等の取り扱いが容易になる。また、一体型の場合、藻類回収手段12Bのゴミ分離ドラム28を回転させるモータ32、及び藻類破壊装置14のインペラ64を回転させるモータ76の電源装置(図示せず)を装置フレーム26に搭載すれば、湖沼、池、河川、閉鎖性海域等の閉鎖性水域15を自由に移動させて浮遊藻類の処理を行うことができる。 In this way, by making the algae treatment system 10 into an integrated type, it is not only possible to make the algae treatment system 10 more compact, but also easier to transport and handle. In the case of an integrated type, a power supply device (not shown) for the motor 32 that rotates the garbage separation drum 28 of the algae collection means 12B and the motor 76 that rotates the impeller 64 of the algae destruction device 14 is mounted on the device frame 26. For example, floating algae can be treated by freely moving a closed water area 15 such as a lake, pond, river, or closed sea area.

なお、上記した処理システム10でアオコを処理する例で説明したが、赤潮にも同様に適用することができる。 Although the above-mentioned processing system 10 has been described as an example of treating blue-green algae, the present invention can be similarly applied to red tide.

10…藻類処理システム、12…藻類除去装置、12A…藻類収集手段、12B…藻類回収手段、13…藻類収集部、13A…第1棒状部材、13A1…太い第1棒状部材、13A2…細い第1棒状部材、13B…流入口、13C…流出口、13D…収集水路、14…藻類破壊装置、15…閉鎖水域、15A…沼、16…圧力調整手段、17…藻類誘導部、17A…第2棒状部材、17A1…第2棒状部材の先端部、17B…誘導水路、18…陸地、19…連結固定部材、20…吸引配管、21…螺合構造、22…吐出配管、23…シール部材、24…圧力計、25…シート状部材、26…装置フレーム、26A…脚フレーム、26B…上面フレーム、26C…フランジ、26D…フランジ、27…錘部材、28…ゴミ分離ドラム、29…紐状部材、30…支持ローラ、30A…大径部、30B…小径部、30C…軸、31…逆ハの字角度変動防止手段、31A…ピン部材、31B…紐状部材、32… モータ、33A…水車、33B…回転軸、33C…軸受、33D…回転動力機構、33E…第1プーリ、33F…モータ、33G…モータの回転軸、33H…第2プーリ、33J…タイミングベルト、34…浮き部材、35、37…アオコ群体、36…吸引ノズル、36A…吸引口、38…吐出ノズル、38A…吐出口、40…スキーマ、42 …フィルタ、44…ゴミ分離ドラムの平坦部、46…ゴミ分離ドラムの側板、48…側板の導入口、50、52…プーリ、54…タイミングベルト、56…洗浄ノズル、58…分岐配管、60…脱気槽、62…ケーシング、64…インペラ、64A…羽根、64B…シュラウト、66…インペラ室、68…架台、70…ポンプ入口、72…排出部、74…ポンプ出口、76…モータ、76A…回転軸、78…仕切壁、80…仕切壁の連通口、82…吸込口、84…排出隙間 DESCRIPTION OF SYMBOLS 10... Algae treatment system, 12... Algae removal device, 12A... Algae collection means, 12B... Algae collection means, 13... Algae collection part, 13A... First rod-shaped member, 13A1... Thick first rod-shaped member, 13A2... Thin first rod-shaped member Rod-shaped member, 13B...Inlet, 13C...Outlet, 13D...Collection channel, 14...Algae destruction device, 15...Closed water area, 15A...Swamp, 16...Pressure adjustment means, 17...Algae guiding section, 17A...Second rod-shaped Member, 17A1...Tip of second rod-shaped member, 17B...Guiding waterway, 18...Land, 19...Connection fixing member, 20...Suction piping, 21...Threaded structure, 22...Discharge piping, 23...Sealing member, 24... Pressure gauge, 25... Sheet member, 26... Device frame, 26A... Leg frame, 26B... Top frame, 26C... Flange, 26D... Flange, 27... Weight member, 28... Dust separation drum, 29... String member, 30 ...Support roller, 30A...Large diameter part, 30B...Small diameter part, 30C...Shaft, 31...Inverted V-shaped angle fluctuation prevention means, 31A...Pin member, 31B...String member, 32...Motor, 33A...Water wheel, 33B ... Rotating shaft, 33C... Bearing, 33D... Rotating power mechanism, 33E... First pulley, 33F... Motor, 33G... Rotating shaft of motor, 33H... Second pulley, 33J... Timing belt, 34... Floating member, 35, 37 ... Blue-green algae colony, 36... Suction nozzle, 36A... Suction port, 38... Discharge nozzle, 38A... Discharge port, 40... Schema, 42... Filter, 44... Flat part of garbage separation drum, 46... Side plate of garbage separation drum, 48 ... Side plate inlet, 50, 52... Pulley, 54... Timing belt, 56... Cleaning nozzle, 58... Branch piping, 60... Deaeration tank, 62... Casing, 64... Impeller, 64A... Vane, 64B... Shrout, 66 ... Impeller chamber, 68 ... Frame, 70 ... Pump inlet, 72 ... Discharge part, 74 ... Pump outlet, 76 ... Motor, 76A ... Rotating shaft, 78 ... Partition wall, 80 ... Communication port of partition wall, 82 ... Suction port, 84...Discharge gap

Claims (10)

沼や池の閉鎖水域の表層水中に浮遊する藻類を収集する藻類収集手段を備えた藻類除去装置において、
前記藻類収集手段は、
前記閉鎖水域の表層水中に浮くことが可能な複数本の第1棒状部材を放射状に配置して、前記浮遊する藻類が流入する流入口が流出口よりも拡径された逆ハの字状の収集水路を放射状に複数形成した藻類収集部と、
前記閉鎖水域の表層水中に浮くことが可能な複数本の第2棒状部材を、前記複数の収集水路の前記流出口に連続して平行に配置して、前記複数の収集水路で収集された藻類を前記複数の収集水路のうちの1つの収集水路に誘導する複数の誘導水路を形成する藻類誘導部と、
前記複数本の第1棒状部材及び前記複数本の第2棒状部材を連結固定する連結固定部材と、を少なくとも備え
前記藻類収集手段は、
前記第1棒状部材に吊設され、前記第1棒状部材と略同等の幅を有するシート状部材と、
前記シート状部材を前記表層水中に垂下させる錘部材と、を更に有する藻類除去装置
In an algae removal device equipped with an algae collection means for collecting algae floating in the surface water of a closed water area such as a swamp or pond ,
The algae collecting means includes:
A plurality of first rod-shaped members capable of floating in the surface water of the closed water area are arranged radially to form an inverted V-shape in which the inlet through which the floating algae flows has a diameter larger than that of the outlet. An algae collection section with multiple collection channels formed in a radial pattern;
A plurality of second rod-shaped members capable of floating in the surface water of the closed water area are arranged continuously and parallel to the outlet ports of the plurality of collection waterways to collect algae in the plurality of collection waterways. an algae guiding section forming a plurality of guiding waterways that guide the algae to one of the plurality of collecting waterways;
At least a connecting and fixing member that connects and fixes the plurality of first rod-like members and the plurality of second rod-like members ,
The algae collecting means includes:
a sheet-like member suspended from the first rod-like member and having a width substantially equal to that of the first rod-like member;
An algae removal device further comprising: a weight member that suspends the sheet-like member into the surface water .
前記1つの収集水路には、前記複数の収集水路で収集した藻類を回収する藻類回収手段が配置される請求項1に記載の藻類除去装置。 The algae removal device according to claim 1, wherein the one collection waterway is provided with an algae collection means for collecting the algae collected in the plurality of collection waterways. 前記複数の収集水路は4水路であって、4本の前記第1棒状部材が90°間隔で放射状に配置されている請求項1又は2に記載の藻類除去装置。 The algae removal device according to claim 1 or 2, wherein the plurality of collection waterways are four waterways, and the four first rod-shaped members are arranged radially at 90° intervals. 前記第1棒状部材及び前記第2棒状部材は両端が水密された塩ビパイプである請求項1から3の何れか1項に記載の藻類除去装置。 The algae removal device according to any one of claims 1 to 3, wherein the first rod-shaped member and the second rod-shaped member are PVC pipes whose ends are watertight. 前記収集水路の前記第1棒状部材は入れ子構造によって伸縮自在である請求項1から4の何れか1項に記載の藻類除去装置。 The algae removal device according to any one of claims 1 to 4, wherein the first rod-shaped member of the collection waterway is expandable and retractable by a nested structure. 前記藻類収集手段は、
前記複数の収集水路の逆ハの字角度の変動を防止する逆ハの字角度変動防止手段を更に有し、
前記逆ハの字角度変動防止手段は、
前記収集水路を形成する複数本の第1棒状部材の前記流入口の位置にそれぞれ立設されたピン部材と、
前記ピン部材の隣接するピン部材同士を緊張した状態で連結する紐状部材と、で構成されている請求項1からの何れか1項に記載の藻類除去装置。
The algae collecting means includes:
further comprising an inverted V-shaped angle variation prevention means for preventing variation in the inverted V-shaped angle of the plurality of collection waterways;
The inverted V-shaped angle fluctuation prevention means is
pin members each erected at the position of the inlet of the plurality of first rod-shaped members forming the collection waterway;
The algae removal device according to any one of claims 1 to 5 , further comprising a string-like member that connects adjacent pin members of the pin member under tension.
前記複数の誘導水路には、前記誘導水路の表層水に前記収集水路から前記藻類回収手段へ向いた水流を発生させる水流発生手段が設けられている請求項2に記載の藻類除去装置。 3. The algae removal device according to claim 2, wherein the plurality of guiding channels are provided with water flow generating means for generating a water flow in the surface water of the guiding channels from the collecting channel toward the algae collecting means. 前記藻類回収手段は、前記藻類収集手段で藻類と一緒に収集された前記閉鎖水域のゴミ類を分離して前記藻類を選択的に回収する機構を備えている請求項2に記載の藻類除去装置。 The algae removal device according to claim 2, wherein the algae collecting means includes a mechanism for separating garbage in the closed water area collected together with the algae by the algae collecting means and selectively collecting the algae. . 前記藻類回収手段は、
前記収集した藻類を含む前記表層水が流通可能な門型の装置フレームと、
前記装置フレーム内に前記表層水の流通方向に直交して横向きに配置され、周面にゴミ分離用のフィルタが形成されるとともに側面に浮遊藻類を表層水と一緒に吸引して取り込む吸引配管の一方端部及び前記フィルタを洗う水を吐出する吐出配管の一方端部を内部に導く導入口が開口された円筒状のゴミ分離ドラムと、
前記装置フレームに回転自在に片持ち支持され、前記ゴミ分離ドラムの両端部周面をそれぞれ3点支持する合計6個の支持ローラと、
前記6個の支持ローラの少なくとも1つに回転動力を付与して前記ゴミ分離ドラムを回転する回転動力手段と、
前記装置フレームに固定され、前記ゴミ分離ドラムの下部が前記表層水中に浸漬するように前記装置フレームを浮かせる浮き部材と、
前記ゴミ分離ドラム内に設けられ、前記吸引配管に連通状態で支持されるとともに前記ゴミ分離ドラムの軸芯方向に長いスロット形状の吸引口が前記表層水中に位置するように形成された吸引ノズルと、
前記ゴミ分離ドラム内に設けられ、前記吐出配管に連通状態で支持されるとともに前記ゴミ分離ドラムの軸芯方向に長いスロット形状の吐出口が前記表層水の水面上に位置するように形成された吐出ノズルと、
前記ゴミ分離ドラムの外面に突起した状態で複数枚設けられ、前記ゴミ分離ドラムの軸芯方向に長い板状のスキーマと、を備えている請求項2に記載の藻類除去装置。
The algae collection means includes:
a gate-shaped device frame through which the surface water containing the collected algae can flow;
Suction piping is disposed horizontally in the apparatus frame perpendicular to the flow direction of the surface water, and has a filter for separating dust formed on its peripheral surface, and a suction piping that suctions and takes in floating algae together with the surface water on its side surface. a cylindrical dust separation drum having one end and an inlet opening for introducing one end of a discharge pipe for discharging water for washing the filter;
a total of six support rollers that are rotatably supported by the device frame in a cantilevered manner and support each of the peripheral surfaces of both ends of the dust separation drum at three points;
Rotational power means for applying rotational power to at least one of the six support rollers to rotate the dust separation drum;
a floating member fixed to the device frame and floating the device frame so that a lower part of the trash separation drum is immersed in the surface water;
a suction nozzle provided in the dust separation drum, supported in communication with the suction piping, and formed such that a slot-shaped suction port that is long in the axial direction of the dust separation drum is located in the surface water; ,
A slot-shaped discharge port provided in the dust separation drum, supported in communication with the discharge pipe, and elongated in the axial direction of the dust separation drum is formed so as to be located above the surface of the surface water. a discharge nozzle;
The algae removal device according to claim 2, further comprising a plurality of plate-shaped schemas protruding from the outer surface of the dust separation drum and long in the axial direction of the dust separation drum.
請求項2に記載の藻類除去装置と、
前記藻類除去装置の前記藻類収集手段で収集されてから前記藻類回収手段で回収された藻類を破壊する多段渦巻ポンプ構造の藻類破壊手段と、を備えたことを特徴とする藻類処理システム。
The algae removal device according to claim 2;
An algae destruction means having a multi-stage spiral pump structure for destroying algae collected by the algae collection means of the algae removal device and then collected by the algae collection means.
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