JP2005169241A - Aeration equipment - Google Patents

Aeration equipment Download PDF

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JP2005169241A
JP2005169241A JP2003412297A JP2003412297A JP2005169241A JP 2005169241 A JP2005169241 A JP 2005169241A JP 2003412297 A JP2003412297 A JP 2003412297A JP 2003412297 A JP2003412297 A JP 2003412297A JP 2005169241 A JP2005169241 A JP 2005169241A
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water
aeration
air diffuser
air
water channels
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JP3884735B2 (en
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Minoru Hayakawa
稔 早川
Masanobu Okata
政信 大方
Shoko Motomura
勝公 元村
Yoshiharu Sato
佳治 佐藤
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Sumitomo Heavy Industries Ltd
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Abstract

<P>PROBLEM TO BE SOLVED: To provide aeration equipment which can increase the amount of oxygen supply to water to be treated while controlling the load increase on a blower. <P>SOLUTION: The aeration equipment 10 comprises an aeration tank 12 for storing the water to be treated, two partition walls 14 which are installed vertically from a height position apart from the bottom of the aeration tank 12 with a prescribed gap, and divide the aeration tank 12 into first to third channels 18, 20, 22 sequentially in the aligning direction, and air diffusers 16 which are respectively installed in the central parts of the first and third channels 18, 22 in the depth direction. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

本発明は曝気設備に関し、より詳細には、下水やし尿、産業排水等の排水の処理に好適な曝気設備に関する。   The present invention relates to an aeration facility, and more particularly to an aeration facility suitable for treatment of wastewater such as sewage, human waste, and industrial wastewater.

下水処理場等の排水処理施設は、河川の富栄養化を防止するため、脱窒素や脱リンを行う必要が生じており、反応槽における高度処理が求められている。従って、排水処理場における好気性の反応槽の占有面積は抑制されながらも、酸素供給量の増大が求められるため、反応槽の深槽化と共に、曝気能力の増大が必要になっている。   In order to prevent eutrophication of rivers, wastewater treatment facilities such as sewage treatment plants need to be denitrified and dephosphorized, and advanced treatment in reaction tanks is required. Therefore, since the occupation area of the aerobic reaction tank in the wastewater treatment plant is suppressed, an increase in the oxygen supply amount is required, so that the aeration capacity needs to be increased along with the deepening of the reaction tank.

このような事情から、従来より、好気性の反応槽の中間部に隔壁を設けて2水路とし、一方の水路に散気装置を設けた曝気設備が利用されている。この曝気設備では、散気装置から排水中に空気を散気することで上昇水流を生じさせ、他方の水路に流れ込ませることで旋回水流を生じさせる。このように、2水路の間で旋回水流を生じさせることで、排水に空気中の酸素を取り込んで酸素供給量の増大を図っている。   Under such circumstances, conventionally, aeration equipment has been used in which a partition wall is provided in the middle part of an aerobic reaction tank to form two water channels, and an air diffuser is provided in one water channel. In this aeration equipment, an ascending water flow is generated by diffusing air from the diffuser into the waste water, and a swirling water flow is generated by flowing into the other water channel. In this way, by generating a swirling water flow between the two water channels, oxygen in the air is taken into the drainage to increase the oxygen supply amount.

しかしながら、近年、反応槽においてより高度な処理が求められており、曝気能力の一層の増大が求められている。そこで、特許文献1に開示されているように、反応槽内における一方の水路の中段に第1の散気装置を設け、更に反応槽の底部に第2の散気装置を設けて、酸素供給量の増大を図った曝気設備が利用されてきている。
特開平9−276891号公報
However, in recent years, more advanced treatment is required in the reaction tank, and further increase in aeration capacity is required. Therefore, as disclosed in Patent Document 1, a first air diffuser is provided in the middle of one of the water channels in the reaction tank, and a second air diffuser is provided at the bottom of the reaction tank to supply oxygen. Aeration equipment designed to increase the volume has been used.
Japanese Patent Laid-Open No. 9-276891

しかしながら、反応槽の底部では水圧が高くブロワへの負荷が高くなるため、上記した特許文献1に開示の曝気設備では、高圧のブロワを使用する必要が生じ、消費電力が増大するという問題があった。   However, since the water pressure is high at the bottom of the reaction tank and the load on the blower is high, the aeration equipment disclosed in Patent Document 1 described above requires the use of a high-pressure blower, resulting in an increase in power consumption. It was.

本発明は、上記した事情に鑑みて為されたものであり、ブロワへの負荷の増大を抑制しつつ被処理水中への酸素供給量の増大を図ることが可能な曝気設備を提供することを目的とする。   The present invention has been made in view of the above circumstances, and provides an aeration facility capable of increasing the amount of oxygen supplied to the water to be treated while suppressing an increase in load on the blower. Objective.

本発明に係る曝気設備は、(1)被処理水を貯留するための曝気槽と、(2)曝気槽の底面より所定間隙を隔てた高さ位置から鉛直方向に立設されており、曝気槽を並び方向に順に第1から第3の水路の3水路に区分する2つの仕切壁と、(3)第1及び第3の水路の深さ方向における中央部にそれぞれ設けられた散気装置と、を備えることを特徴とする。   The aeration equipment according to the present invention is (1) an aeration tank for storing water to be treated, and (2) a vertical position from a height position that is separated from the bottom of the aeration tank by a predetermined gap. Two partition walls that divide the tank into three water channels of the first to third water channels in order in the arrangement direction; and (3) an air diffuser provided at the center in the depth direction of the first and third water channels. And.

この曝気設備では、曝気槽を区分して設けられた3水路のうち、第2の水路を挟む第1及び第3の水路に散気装置がそれぞれ設けられている。従って、第1の水路と第2の水路との間、及び第3の水路と第2の水路との間で旋回水流を生じさせることができ、被処理水に空気中の酸素を十分に取り込んで酸素供給量の増大を図ることができる。このとき、散気装置はそれぞれの水路の深さ方向における中央部に設けられているため、曝気槽の底部に散気装置を設ける場合と比較して、ブロワへの負荷の増大を抑制することができる。   In this aeration facility, a diffuser is provided in each of the first and third water channels sandwiching the second water channel among the three water channels provided by dividing the aeration tank. Therefore, a swirling water flow can be generated between the first water channel and the second water channel, and between the third water channel and the second water channel, and oxygen in the air is sufficiently taken into the water to be treated. Thus, the oxygen supply amount can be increased. At this time, since the air diffuser is provided at the center in the depth direction of each water channel, the increase in the load on the blower is suppressed as compared with the case where the air diffuser is provided at the bottom of the aeration tank. Can do.

曝気設備は、第2の水路内で鉛直方向に沿って延びるように設けられた整流板を備えることを特徴としてもよい。このようにすれば、旋回水流の乱流が生じるおそれが低減され、酸素の溶解効率の向上が図られる。   The aeration facility may include a baffle plate provided so as to extend along the vertical direction in the second water channel. In this way, the risk of turbulent flow of the swirling water flow is reduced, and the oxygen dissolution efficiency is improved.

散気装置は、水面から4m〜6mの深さ位置に設けられていることを特徴としてもよい。水面から4mよりも浅い位置に散気装置が設けられていると、散気された空気との接触時間が短くなって、旋回水流が生じ難くなる傾向にある。また水面から6mよりも深い位置に散気装置が設けられていると、ブロワへの負荷が高くなる傾向にある。   The air diffuser may be provided at a depth of 4 to 6 m from the water surface. If the diffuser is provided at a position shallower than 4 m from the water surface, the contact time with the diffused air is shortened, and the swirling water flow tends not to be generated. Moreover, when the diffuser is provided at a position deeper than 6 m from the water surface, the load on the blower tends to increase.

本発明に係る曝気設備は、(1)被処理水を貯留するための曝気槽と、(2)曝気槽の底面より所定間隙を隔てた高さ位置から鉛直方向に立設されており、曝気槽を並び方向に順に第1から第4の水路の4水路に区分する3つの仕切壁と、(3)第1及び第2の水路のいずれか一方の深さ方向における中央部、及び第3及び第4の水路のいずれか一方の深さ方向における中央部にそれぞれ設けられた散気装置と、を備えることを特徴とする。   The aeration equipment according to the present invention is (1) an aeration tank for storing water to be treated, and (2) a vertical position from a height position that is separated from the bottom of the aeration tank by a predetermined gap. Three partition walls for sequentially dividing the tank into four water channels of the first to fourth water channels in the arrangement direction, (3) a central portion in the depth direction of one of the first and second water channels, and a third And an air diffuser provided at the center in the depth direction of either one of the fourth water channels.

この曝気設備では、曝気槽を区分して設けられた4水路のうち、第1及び第2の水路のいずれか一方、及び第3及び第4の水路のいずれか一方に散気装置がそれぞれ設けられている。従って、第1の水路と第2の水路との間、及び第3の水路と第4の水路との間で旋回水流を生じさせることができ、被処理水に空気中の酸素を十分に取り込んで酸素供給量の増大を図ることができる。このとき、散気装置はそれぞれの水路の深さ方向における中央部に設けられているため、曝気槽の底部に散気装置を設ける場合と比較して、ブロワへの負荷の増大を抑制することができる。   In this aeration equipment, a diffuser is provided in either one of the first and second water channels and in one of the third and fourth water channels among the four water channels provided by dividing the aeration tank. It has been. Accordingly, a swirling water flow can be generated between the first water channel and the second water channel, and between the third water channel and the fourth water channel, and oxygen in the air is sufficiently taken into the water to be treated. Thus, the oxygen supply amount can be increased. At this time, since the air diffuser is provided at the center in the depth direction of each water channel, the increase in the load on the blower is suppressed as compared with the case where the air diffuser is provided at the bottom of the aeration tank. Can do.

曝気設備は、第1及び第2の水路の上記一方とは異なる他方の深さ方向における中央部、及び第3及び第4の水路の上記一方とは異なる他方の深さ方向における中央部にそれぞれ設けられており、上記散気装置よりも散気量の小さい他の散気装置を備えることを特徴としてもよい。このようにすれば、酸素供給量のより一層の増大を図ることができる。   The aeration facility has a central portion in the other depth direction different from the one of the first and second water channels, and a central portion in the other depth direction different from the one of the third and fourth water channels, respectively. It is good also as providing the other air diffusing device with which the air diffusing amount is smaller than the said air diffusing device. In this way, it is possible to further increase the oxygen supply amount.

本発明によれば、ブロワへの負荷の増大を抑制しつつ被処理水中への酸素供給量の増大を図ることが可能な曝気設備が提供される。   ADVANTAGE OF THE INVENTION According to this invention, the aeration equipment which can aim at the increase in the oxygen supply amount to to-be-processed water is suppressed, suppressing the increase in the load to a blower.

以下、添付図面を参照して本発明の実施形態について説明する。なお、図面の説明において同一の要素には同一の符号を付し、重複する説明を省略する。
(第1実施形態)
図1は、本実施形態に係る曝気設備の構成を示す正断面図である。また図2は、図1に示すII-II線における断面図である。図1及び図2に示すように、曝気設備10は、曝気槽12、2つの仕切壁14、及び散気装置16を備えている。
Hereinafter, embodiments of the present invention will be described with reference to the accompanying drawings. In the description of the drawings, the same elements are denoted by the same reference numerals, and redundant description is omitted.
(First embodiment)
FIG. 1 is a front sectional view showing the configuration of the aeration equipment according to this embodiment. 2 is a cross-sectional view taken along the line II-II shown in FIG. As shown in FIGS. 1 and 2, the aeration equipment 10 includes an aeration tank 12, two partition walls 14, and an air diffuser 16.

曝気槽12は、底壁部12a、対向する左右側壁部12b,12c、及び対向する前後側壁部12d,12eを有している。2つの仕切壁14は、曝気槽12の前後側壁部12d,12eの間に横架され、曝気槽12の底面より所定間隙を隔てた高さ位置から、左右側壁部12b,12cに平行になるように鉛直方向に立設されている。これにより、曝気槽12は並び方向に順に第1から第3の水路18,20,22の3水路に区分されている。   The aeration tank 12 has a bottom wall portion 12a, opposed left and right side wall portions 12b and 12c, and opposed front and rear side wall portions 12d and 12e. The two partition walls 14 are horizontally mounted between the front and rear side wall portions 12d and 12e of the aeration tank 12, and are parallel to the left and right side wall portions 12b and 12c from a height position separated from the bottom surface of the aeration tank 12 by a predetermined gap. So as to stand vertically. Thereby, the aeration tank 12 is divided into the three water channels of the 1st to 3rd water channels 18, 20, and 22 in order in the arrangement direction.

散気装置16は、第1及び第3の水路18,22の深さ方向における中央部にそれぞれ設けられている。ここで、中央部とは、曝気槽12の深さをDとしたとき、その1/3〜2/3の深さの部分をいう。よって、10m程度の深さの深槽曝気槽を考えたとき、散気装置16は水面から4m〜6mの深さ位置に設けられていると好ましい。水面から4mよりも浅い位置に散気装置16が設けられていると、散気された空気との接触時間が短くなって、旋回水流が生じ難くなる傾向にある。また水面から6mよりも深い位置に散気装置16が設けられていると、ブロワ24への負荷が高くなる傾向にある。なお、散気装置16の深さ位置は、気泡が放出される散気面を基準として考える。 The air diffuser 16 is provided at the center of the first and third water channels 18 and 22 in the depth direction. Here, the central portion, when the depth of the aeration tank 12 was set to D w, refers to the depth portion of the 1 / 3-2 / 3. Therefore, when considering a deep tank aeration tank having a depth of about 10 m, the air diffuser 16 is preferably provided at a depth of 4 m to 6 m from the water surface. If the diffuser 16 is provided at a position shallower than 4 m from the water surface, the contact time with the diffused air is shortened, and the swirling water flow tends not to occur. Moreover, when the diffuser 16 is provided at a position deeper than 6 m from the water surface, the load on the blower 24 tends to increase. The depth position of the air diffuser 16 is considered based on the air diffused surface from which bubbles are released.

散気装置16は、図2に示すように、複数の散気体ユニット26を有している。本実施形態では、散気装置16は3つの散気体ユニット26を有している。散気体ユニット26は、図3に示すように、複数の散気体28をユニット化して構成されている。本実施形態では、4つの散気体28をユニット化して散気体ユニット26が構成されている。散気体28は、図4に示すように、躯体30と、多孔質セラミックや樹脂製多孔膜等の多孔質体32と、を有している。この散気体28では、躯体30上に多孔質体32を載置し、躯体30と多孔質体32との間に形成される空間Sに躯体30の底壁部に穿設された穴34を通して空気を供給することで、多孔質体32を通して散気が行われる。この多孔質体32の上面が散気面を構成する。   The air diffuser 16 has a plurality of air diffuser units 26 as shown in FIG. In the present embodiment, the air diffuser 16 has three air diffuser units 26. As shown in FIG. 3, the air diffuser unit 26 is configured by unitizing a plurality of air diffusers 28. In the present embodiment, the diffused gas unit 26 is configured by unitizing four diffused gases 28. As shown in FIG. 4, the diffused gas 28 includes a casing 30 and a porous body 32 such as a porous ceramic or a resin porous membrane. In this diffused gas 28, a porous body 32 is placed on the housing 30, and through a hole 34 drilled in the bottom wall portion of the housing 30 in a space S formed between the housing 30 and the porous body 32. By supplying air, air is diffused through the porous body 32. The upper surface of the porous body 32 constitutes a diffuser surface.

かかる構成の複数の散気体28が、図3に示すように、空気を分配するヘッダ管36に取り付けられ、さらに支持ポール38に支持されてユニット化されている。そして、ヘッダ管36が曝気槽12外のブロワ24に空気供給ラインLaを通して接続されている。このような散気体ユニット26を複数備えることで、散気装置16が構成されている。なお、散気装置16の構成は上記した構成のものに限定されるものではなく、被処理水中に微細気泡を散気することが可能な構成であれば、他の構成のものを利用してもよい。   As shown in FIG. 3, the plurality of diffused gases 28 having such a configuration are attached to a header pipe 36 that distributes air and further supported by a support pole 38 to be unitized. The header pipe 36 is connected to the blower 24 outside the aeration tank 12 through an air supply line La. The air diffusing device 16 is configured by providing a plurality of such air diffusing units 26. The configuration of the air diffuser 16 is not limited to the configuration described above, and any other configuration can be used as long as it can diffuse fine bubbles in the water to be treated. Also good.

ここで本実施形態では、第1の水路18に設けられた散気装置16の3つの散気体ユニット26は、それぞれ同じ深さ位置に設置されており吐出圧が同一でよいため、ブロワ24を共通化している。また、第3の水路22に設けられた散気装置16の3つの散気体ユニット26は、それぞれ同じ深さ位置に設置されており吐出圧が同一でよいため、ブロワ24を共通化している。更に、第1の水路18に設けられた散気装置16と第3の水路22に設けられた散気装置16は、それぞれ同じ深さ位置に設置されており吐出圧が同一でよいため、これらの間でもブロワ24を共通化している。このようにして、構成の簡略化が図られている。ただし、第1の水路18と第3の水路22のそれぞれでブロワを分けてもよく、更に各散気体ユニット26でブロワを分けてもよい。   Here, in the present embodiment, the three air diffuser units 26 of the air diffuser 16 provided in the first water channel 18 are installed at the same depth position, and the discharge pressure may be the same. It is common. Further, the three air diffusion units 26 of the air diffuser 16 provided in the third water channel 22 are respectively installed at the same depth position, and the discharge pressure may be the same, so the blower 24 is shared. Further, since the air diffuser 16 provided in the first water channel 18 and the air diffuser 16 provided in the third water channel 22 are respectively installed at the same depth position, the discharge pressure may be the same. The blower 24 is shared between the two. In this way, the configuration is simplified. However, the blower may be divided in each of the first water channel 18 and the third water channel 22, and further, the blower may be divided in each air diffuser unit 26.

2つの仕切壁14に囲まれた第2の水路20内には、鉛直方向に沿って延びるように複数の整流板40が設けられている。これら整流板40は、仕切壁14に直角に設けられている。   A plurality of rectifying plates 40 are provided in the second water channel 20 surrounded by the two partition walls 14 so as to extend along the vertical direction. These rectifying plates 40 are provided at right angles to the partition wall 14.

次に、上記した曝気設備10の作用及び効果について説明する。   Next, the operation and effect of the aeration equipment 10 described above will be described.

まず、図1に示すように、曝気槽12内に被処理水が貯留される。このとき、水面は仕切壁14の上端よりも上にある。そして、ブロワ24を作動させて空気供給ラインLaから散気装置16に向けて空気を供給する。すると、散気体28から微細気泡が被処理水中に散気され、第1及び第3の水路18,22内で上昇水流が生じる。そして、第1の水路18内で生じた上昇水流は第2の水路20内に流れ込み、図1の矢印αで示すように、第1の水路18と第2の水路20との間で旋回水流が生じる。一方、第3の水路22内で生じた上昇水流は第2の水路20内に流れ込み、図1の矢印βで示すように、第3の水路22と第2の水路20との間で旋回水流が生じる。これにより、被処理水に空気中の酸素が十分に取り込まれ、酸素供給量の増大が図られる。このとき、散気装置16はそれぞれの水路18,22の深さ方向における中央部に設けられているため、曝気槽12の底部に散気装置16を設ける場合と比較して、ブロワ24への負荷の増大を抑制することができる。   First, as shown in FIG. 1, water to be treated is stored in the aeration tank 12. At this time, the water surface is above the upper end of the partition wall 14. Then, the blower 24 is operated to supply air from the air supply line La toward the air diffuser 16. Then, fine bubbles are diffused from the diffused gas 28 into the water to be treated, and a rising water flow is generated in the first and third water channels 18 and 22. Then, the rising water flow generated in the first water channel 18 flows into the second water channel 20, and the swirling water flow between the first water channel 18 and the second water channel 20 as indicated by an arrow α in FIG. 1. Occurs. On the other hand, the ascending water flow generated in the third water channel 22 flows into the second water channel 20, and the swirling water flow between the third water channel 22 and the second water channel 20 as shown by the arrow β in FIG. Occurs. As a result, oxygen in the air is sufficiently taken into the water to be treated, and the oxygen supply amount is increased. At this time, since the air diffuser 16 is provided at the center in the depth direction of each of the water channels 18, 22, compared with the case where the air diffuser 16 is provided at the bottom of the aeration tank 12, An increase in load can be suppressed.

また、第2の水路20内には整流板40が設けられているため、旋回水流の乱流が生じるおそれが低減され、酸素の溶解効率の向上を図ることが可能となる。   Further, since the rectifying plate 40 is provided in the second water channel 20, the possibility of the turbulent flow of the swirling water flow is reduced, and the oxygen dissolution efficiency can be improved.

なお、図1及び図2を参照して説明した曝気設備10では、2つの仕切壁14がバランスよく配置され、第1及び第3の水路18,22が同程度の幅を有する場合について説明したが、第1及び第3の水路18,22の幅は、図5に示すように、異なっていてもよい。図5に示す曝気設備10では、一方の仕切壁14が曝気槽12の幅方向における中央部に設けられ、他方の仕切壁14が右側壁部12cの側の片寄った位置に設けられている。このようにしても、上記図1及び図2で示した曝気設備10と同様の作用効果を奏することができる。特に、既設の曝気設備は曝気槽の幅方向における中央部に仕切壁が設けられた2水路のタイプのものが多く、この場合はもう一つ仕切壁14を設けて3水路にし、第1及び第3の水路18,22に散気装置16を設置することで、既存の設備を有効利用して本実施形態に係る散気設備10を容易に構成することができる。   In addition, in the aeration equipment 10 demonstrated with reference to FIG.1 and FIG.2, the case where the two partition walls 14 are arrange | positioned with sufficient balance, and the 1st and 3rd water channels 18 and 22 have the width | variety comparable was demonstrated. However, the widths of the first and third water channels 18 and 22 may be different as shown in FIG. In the aeration equipment 10 shown in FIG. 5, one partition wall 14 is provided at the center in the width direction of the aeration tank 12, and the other partition wall 14 is provided at a position offset on the right side wall 12 c side. Even if it does in this way, there can exist the same effect as the aeration equipment 10 shown in the said FIG.1 and FIG.2. In particular, the existing aeration equipment is often of a two-water channel type in which a partition wall is provided at the center in the width direction of the aeration tank. In this case, another partition wall 14 is provided to form three water channels, By installing the air diffuser 16 in the third water channels 18 and 22, the air diffuser 10 according to the present embodiment can be easily configured by effectively utilizing existing facilities.

図6は、上記した曝気設備10を備えた排水処理設備50の構成を示す平面図である。図6に示すように、排水処理設備50は、前段より順に初沈槽52、上記した曝気設備10、及び後沈槽54を備えている。初沈槽52には、図示しない前段の沈砂池からポンプPで汲み上げられた排水が送られる。この初沈槽52では、排水が2〜3時間程度滞留され、沈砂池で沈まなかった細かい汚泥が底に沈められる。底に溜まった汚泥は、図示しない掻き寄せ装置により掻き寄せられ、ピット53に集められて引き出された後、図示しない汚泥処理施設に送られる。   FIG. 6 is a plan view showing the configuration of the wastewater treatment facility 50 including the aeration facility 10 described above. As shown in FIG. 6, the wastewater treatment facility 50 includes an initial settling tank 52, the above-described aeration facility 10, and a post-settling tank 54 in order from the previous stage. Drainage pumped up by a pump P is sent to the initial settling tank 52 from a preceding settling basin (not shown). In the initial settling tank 52, the waste water is retained for about 2 to 3 hours, and fine sludge that has not been sunk in the sand basin is submerged in the bottom. The sludge accumulated on the bottom is scraped by a scraping device (not shown), collected in the pit 53 and pulled out, and then sent to a sludge treatment facility (not shown).

初沈槽52を滞留した排水は、曝気設備10に送られる。曝気設備10の第1〜第3の水路18,20,22の並び方向は、初沈槽52、曝気設備10、及び後沈槽54の並び方向と直交している。初沈槽52と曝気設備10との間にはトラフ56が設けられており、これをオーバーフローした排水が曝気設備10に送られる。曝気設備10では、曝気槽12内に活性汚泥が加えられ、散気装置16により散気しながら、排水が6〜8時間程度かけてかき混ぜられる。これにより、排水中の汚れが分解される。そして、処理水が後段の後沈槽54に送られる。曝気設備10と後沈槽54との間にはトラフ58が設けられており、これをオーバーフローした処理水が後沈槽54に送られる。   The waste water staying in the initial settling tank 52 is sent to the aeration equipment 10. The arrangement direction of the first to third water channels 18, 20, and 22 of the aeration equipment 10 is orthogonal to the arrangement direction of the initial settling tank 52, the aeration equipment 10, and the post-settling tank 54. A trough 56 is provided between the initial settling tank 52 and the aeration equipment 10, and waste water overflowing the trough 56 is sent to the aeration equipment 10. In the aeration facility 10, activated sludge is added to the aeration tank 12, and the wastewater is stirred for about 6 to 8 hours while being diffused by the air diffuser 16. Thereby, the dirt in waste water is decomposed. Then, the treated water is sent to the subsequent post-sink tank 54. A trough 58 is provided between the aeration equipment 10 and the post-sink tank 54, and treated water overflowing this is sent to the post-sink tank 54.

後沈槽54では、処理水が3〜4時間程度滞留され、曝気設備10で生じた汚泥のかたまりが底に沈められる。底に溜まった汚泥は、図示しない掻き寄せ装置により掻き寄せられ、ピット55に集められて引き出された後、図示しない汚泥処理施設に送られる。上澄みの綺麗な処理水は、必要に応じて塩素消毒されて高度処理施設に送られた後、河川等の系外へ排出される。
(第2実施形態)
次に、本発明の第2実施形態について説明する。なお、上記した第1実施形態と同一の要素には同一の符号を附し、重複する説明を省略する。
In the post-sink tank 54, treated water is retained for about 3 to 4 hours, and a lump of sludge generated in the aeration facility 10 is submerged in the bottom. The sludge accumulated on the bottom is scraped by a scraping device (not shown), collected in the pit 55 and pulled out, and then sent to a sludge treatment facility (not shown). The clear treated water of the supernatant is sterilized with chlorine if necessary and sent to an advanced treatment facility and then discharged out of the system such as a river.
(Second Embodiment)
Next, a second embodiment of the present invention will be described. In addition, the same code | symbol is attached | subjected to the same element as above-mentioned 1st Embodiment, and the overlapping description is abbreviate | omitted.

図7は、第2実施形態に係る曝気設備の構成を示す正断面図である。図7に示すように、曝気設備60は、曝気槽12、3つの仕切壁14、及び散気装置16を備えている。   FIG. 7 is a front sectional view showing the configuration of the aeration equipment according to the second embodiment. As shown in FIG. 7, the aeration facility 60 includes an aeration tank 12, three partition walls 14, and an air diffuser 16.

曝気槽12は、第1実施形態で説明したのと同様に、底壁部12a、対向する左右側壁部12b,12c、及び対向する前後側壁部(図示しない)を有している。3つの仕切壁14は、曝気槽12の前後側壁部の間に横架され、曝気槽12の底面より所定間隙を隔てた高さ位置から、左右側壁部12b,12cに平行になるように鉛直方向に立設されている。これにより、曝気槽12は並び方向に順に第1から第4の水路62,64,66,68の4水路に区分されている。3つの仕切壁14のうち中間の仕切壁14は、上端の位置が他の2つの仕切壁14の上端の位置よりも高く、また下端の位置が他の2つの仕切壁14の下端の位置よりも低い。   The aeration tank 12 has a bottom wall portion 12a, opposed left and right side wall portions 12b and 12c, and opposed front and rear side wall portions (not shown), as described in the first embodiment. The three partition walls 14 are horizontally mounted between the front and rear side wall portions of the aeration tank 12, and are vertically arranged so as to be parallel to the left and right side wall portions 12b and 12c from a height position separated from the bottom surface of the aeration tank 12. Standing in the direction. Thereby, the aeration tank 12 is divided into four water channels of first to fourth water channels 62, 64, 66, and 68 in order in the arrangement direction. Of the three partition walls 14, the middle partition wall 14 has an upper end position higher than the upper end positions of the other two partition walls 14 and a lower end position that is lower than the lower end positions of the other two partition walls 14. Is also low.

散気装置16は、第2及び第3の水路64,66の深さ方向における中央部にそれぞれ設けられている。散気装置16は、第1実施形態で説明したものと同様である。   The air diffuser 16 is provided in the center part in the depth direction of the second and third water channels 64 and 66, respectively. The air diffuser 16 is the same as that described in the first embodiment.

次に、上記した曝気設備60の作用及び効果について説明する。   Next, the operation and effect of the aeration equipment 60 described above will be described.

まず、図7に示すように、曝気槽12内に被処理水が貯留される。このとき、水面は仕切壁14の上端よりも上にある。そして、ブロワ24を作動させて空気供給ラインLaから散気装置16に向けて空気を供給する。すると、散気体28から微細気泡が被処理水中に散気され、第2及び第3の水路64,66内で上昇水流が生じる。そして、第2の水路64内で生じた上昇水流は第1の水路62内に流れ込み、図7の矢印αで示すように、第2の水路64と第1の水路62との間で旋回水流が生じる。一方、第3の水路66内で生じた上昇水流は第4の水路68内に流れ込み、図7の矢印βで示すように、第3の水路66と第4の水路68との間で旋回水流が生じる。これにより、被処理水に空気中の酸素が十分に取り込まれ、酸素供給量の増大が図られる。このとき、散気装置16はそれぞれの水路の深さ方向における中央部に設けられているため、曝気槽12の底部に散気装置16を設ける場合と比較して、ブロワ24への負荷の増大を抑制することができる。なお、中間の仕切壁14は、上端の位置が他の2つの仕切壁14の上端の位置よりも高く、また下端の位置が他の2つの仕切壁14の下端の位置よりも低いため、第1及び第2の水路62,64を旋回する旋回水流と第3及び第4の水路66,68を旋回する旋回水流とを好適に分けることができ、乱流の発生が低減されて、空気中の酸素の溶解効率の向上が図られる。   First, as shown in FIG. 7, the water to be treated is stored in the aeration tank 12. At this time, the water surface is above the upper end of the partition wall 14. Then, the blower 24 is operated to supply air from the air supply line La toward the air diffuser 16. Then, fine bubbles are diffused from the diffused gas 28 into the water to be treated, and a rising water flow is generated in the second and third water channels 64 and 66. Then, the ascending water flow generated in the second water channel 64 flows into the first water channel 62, and the swirling water flow between the second water channel 64 and the first water channel 62 as shown by the arrow α in FIG. Occurs. On the other hand, the ascending water flow generated in the third water channel 66 flows into the fourth water channel 68, and the swirling water flow between the third water channel 66 and the fourth water channel 68 as shown by the arrow β in FIG. Occurs. As a result, oxygen in the air is sufficiently taken into the water to be treated, and the oxygen supply amount is increased. At this time, since the air diffuser 16 is provided at the center in the depth direction of each water channel, the load on the blower 24 is increased as compared with the case where the air diffuser 16 is provided at the bottom of the aeration tank 12. Can be suppressed. Note that the middle partition wall 14 has an upper end position higher than the upper end positions of the other two partition walls 14 and a lower end position lower than the lower end positions of the other two partition walls 14. The swirling water flow swirling through the first and second water channels 62 and 64 and the swirling water flow swirling through the third and fourth water channels 66 and 68 can be suitably separated, and the occurrence of turbulent flow is reduced, so that The oxygen dissolution efficiency is improved.

ここで、前述したように既設の曝気設備は、曝気槽の幅方向における中央部に仕切壁が設けられた2水路のタイプのものが多い。従って、この場合はもう二つ仕切壁14を設けて4水路にし、第2及び第3の水路64,66に散気装置16を設置することで、既存の設備を有効利用して本実施形態に係る散気設備60を容易に構成することができる。このとき、中間の仕切壁14がコンクリート等で設けられているのに対し、残りの2つの仕切壁14は、合成木材等により構成すると形成が容易であるため好ましい。
(第3実施形態)
次に、本発明の第3実施形態について説明する。なお、上記した第1及び第2実施形態と同一の要素には同一の符号を附し、重複する説明を省略する。
Here, as described above, many existing aeration equipments are of the two-water channel type in which a partition wall is provided at the center in the width direction of the aeration tank. Therefore, in this case, the two partition walls 14 are provided to form four water channels, and the air diffuser 16 is installed in the second and third water channels 64 and 66, so that the existing equipment can be used effectively and this embodiment can be used. The air diffusion facility 60 according to the above can be easily configured. At this time, the intermediate partition wall 14 is made of concrete or the like, whereas the remaining two partition walls 14 are preferably made of synthetic wood or the like because they are easy to form.
(Third embodiment)
Next, a third embodiment of the present invention will be described. In addition, the same code | symbol is attached | subjected to the element same as the above-mentioned 1st and 2nd embodiment, and the overlapping description is abbreviate | omitted.

図8は、第3実施形態に係る曝気設備の構成を示す正断面図である。図8に示すように、本実施形態に係る曝気設備70は、第1及び第4の水路62,68に新たに散気装置72が設置されている以外は、第2実施形態に係る曝気設備60と同様の構成を有している。   FIG. 8 is a front sectional view showing the configuration of the aeration equipment according to the third embodiment. As shown in FIG. 8, the aeration facility 70 according to the present embodiment has the aeration facility according to the second embodiment except that an aeration device 72 is newly installed in the first and fourth water channels 62 and 68. The configuration is the same as 60.

新たな散気装置72は、第1及び第4の水路62,68の深さ方向における中央部にそれぞれ設けられている。新たな散気装置72の散気量は、第2及び第3の水路64,66に設置された散気装置16の散気量よりも小さい。この散気装置72の散気量は、散気面の面積や風量を変えることで調整されている。なお、第1から第4の水路62,64,66,68に設けられた散気装置72は、それぞれ同じ深さ位置に設置されており吐出圧が同一でよいため、これらの間でブロワ24を共通化している。このようにして、構成の簡略化が図られている。ただし、第1から第4の水路62,64,66,68のそれぞれでブロワを分けてもよい。   The new air diffuser 72 is provided in the center part in the depth direction of the 1st and 4th water channels 62 and 68, respectively. The amount of air diffused by the new air diffuser 72 is smaller than the amount of air diffused by the air diffuser 16 installed in the second and third water channels 64 and 66. The amount of air diffused by the air diffuser 72 is adjusted by changing the area of the air diffuser and the air volume. The air diffusers 72 provided in the first to fourth water passages 62, 64, 66, and 68 are installed at the same depth position, and the discharge pressure may be the same. Is common. In this way, the configuration is simplified. However, the blower may be divided in each of the first to fourth water channels 62, 64, 66 and 68.

次に、上記した曝気設備70の作用及び効果について説明する。   Next, the operation and effect of the aeration equipment 70 described above will be described.

まず、図8に示すように、曝気槽12内に被処理水が貯留される。このとき、水面は仕切壁14の上端よりも上にある。そして、ブロワ24を作動させて空気供給ラインLaから散気装置16に向けて空気を供給する。すると、散気体28から微細気泡が被処理水中に散気され、第2及び第3の水路64,66内で上昇水流が生じる。そして、第2の水路64内で生じた上昇水流は第1の水路62内に流れ込み、図8の矢印αで示すように、第2の水路64と第1の水路62との間で旋回水流が生じる。一方、第3の水路66内で生じた上昇水流は第4の水路68内に流れ込み、図8の矢印βで示すように、第3の水路66と第4の水路68との間で旋回水流が生じる。   First, as shown in FIG. 8, the water to be treated is stored in the aeration tank 12. At this time, the water surface is above the upper end of the partition wall 14. Then, the blower 24 is operated to supply air from the air supply line La toward the air diffuser 16. Then, fine bubbles are diffused from the diffused gas 28 into the water to be treated, and a rising water flow is generated in the second and third water channels 64 and 66. Then, the rising water flow generated in the second water channel 64 flows into the first water channel 62, and the swirling water flow between the second water channel 64 and the first water channel 62 as shown by an arrow α in FIG. Occurs. On the other hand, the ascending water flow generated in the third water channel 66 flows into the fourth water channel 68, and the swirling water flow between the third water channel 66 and the fourth water channel 68 as shown by the arrow β in FIG. Occurs.

この旋回水流が定常状態になると、バルブ74を開いて散気装置72により被処理水中に小容量の空気を散気する。散気装置72からの小容量の空気は、定常状態となった旋回水流に牽引され、それぞれ第1及び第4の水路62,68を下降して、第2及び第3の水路64,66を上昇する旋回水流に乗る。これにより、風量の増大が図られ、被処理水中への酸素供給量の増大が一層図られる。このとき、散気装置72はそれぞれの水路62,68の深さ方向における中央部に設けられているため、曝気槽12の底部に散気装置を設ける場合と比較して、ブロワ24への負荷の増大を抑制することができる。   When this swirling water flow is in a steady state, the valve 74 is opened and a small volume of air is diffused into the water to be treated by the air diffuser 72. A small volume of air from the air diffuser 72 is pulled by the swirling water flow that is in a steady state, descends the first and fourth water channels 62 and 68, and passes through the second and third water channels 64 and 66. Ride the rising swirling water stream. As a result, the air volume is increased, and the amount of oxygen supplied to the water to be treated is further increased. At this time, since the air diffuser 72 is provided at the center of each of the water channels 62 and 68 in the depth direction, the load on the blower 24 is compared with the case where the air diffuser is provided at the bottom of the aeration tank 12. Can be suppressed.

なお、本発明は上記した実施形態に限定されることなく、種々の変形が可能である。例えば、第1実施形態で説明した排水処理設備50は、第2実施形態で説明した曝気設備60、或いは第3実施形態で説明した曝気設備70を備えていてもよい。   The present invention is not limited to the above-described embodiment, and various modifications can be made. For example, the wastewater treatment facility 50 described in the first embodiment may include the aeration facility 60 described in the second embodiment or the aeration facility 70 described in the third embodiment.

また、第2実施形態に係る曝気設備60において、散気装置16が設けられていない第1及び第4の水路62,68に整流板を設けてもよい。   Moreover, in the aeration equipment 60 according to the second embodiment, a current plate may be provided in the first and fourth water channels 62 and 68 where the air diffuser 16 is not provided.

また、第2実施形態に係る曝気設備60において、散気装置16は第2及び第3の水路64,66に設けられていたが、第1及び第3の水路64,66に散気装置16を設けてもよく、第1及び第4の水路62,68に散気装置16を設けてもよく、第2及び第4の水路64,68に散気装置16を設けてもよい。これに合わせて、第3実施形態に係る曝気設備70において、散気量の小さい新たな散気装置72を、散気装置16の設けられていない水路に設置するようにしてもよい。   In the aeration equipment 60 according to the second embodiment, the air diffuser 16 is provided in the second and third water channels 64 and 66, but the air diffuser 16 is disposed in the first and third water channels 64 and 66. The air diffuser 16 may be provided in the first and fourth water channels 62 and 68, and the air diffuser 16 may be provided in the second and fourth water channels 64 and 68. In accordance with this, in the aeration equipment 70 according to the third embodiment, a new aeration device 72 with a small amount of aeration may be installed in a water channel where the aeration device 16 is not provided.

第1実施形態に係る曝気設備の構成を示す正断面図である。It is a front sectional view showing the configuration of the aeration equipment according to the first embodiment. 図1に示すII-II線における断面図である。It is sectional drawing in the II-II line shown in FIG. 散気装置を構成する散気体ユニットの構成を示す平面図である。It is a top view which shows the structure of the air diffusion unit which comprises an air diffuser. 散気体ユニットを構成する散気体の構成を示す断面図である。It is sectional drawing which shows the structure of the diffused gas which comprises a diffused gas unit. 第1実施形態に係る曝気設備の変形例を示す正断面図である。It is a front sectional view showing a modification of the aeration equipment according to the first embodiment. 第1実施形態に係る曝気設備を備えた排水処理設備の構成を示す平面図である。It is a top view which shows the structure of the waste water treatment facility provided with the aeration equipment which concerns on 1st Embodiment. 第2実施形態に係る曝気設備の構成を示す正断面図である。It is a front sectional view showing the configuration of the aeration equipment according to the second embodiment. 第3実施形態に係る曝気設備の構成を示す正断面図である。It is a front sectional view showing the configuration of the aeration equipment according to the third embodiment.

符号の説明Explanation of symbols

10,60,70…曝気設備、12…曝気槽、14…仕切壁、16,72…散気装置、18,62…第1の水路、20,64…第2の水路、22,66…第3の水路、40…整流板、68…第4の水路。   10, 60, 70 ... aeration equipment, 12 ... aeration tank, 14 ... partition wall, 16, 72 ... diffuser, 18, 62 ... first water channel, 20, 64 ... second water channel, 22, 66 ... first 3 water channels, 40 ... current plate, 68 ... fourth water channel.

Claims (5)

被処理水を貯留するための曝気槽と、
前記曝気槽の底面より所定間隙を隔てた高さ位置から鉛直方向に立設されており、該曝気槽を並び方向に順に第1から第3の水路の3水路に区分する2つの仕切壁と、
前記第1及び第3の水路の深さ方向における中央部にそれぞれ設けられた散気装置と、
を備えることを特徴とする曝気設備。
An aeration tank for storing treated water;
Two partition walls standing vertically from a height position spaced apart from the bottom surface of the aeration tank, and dividing the aeration tank into three water channels of first to third water channels in order in the arrangement direction; ,
An air diffuser provided in the center of each of the first and third water channels in the depth direction;
An aeration facility characterized by comprising:
前記第2の水路内で鉛直方向に沿って延びるように設けられた整流板を備えることを特徴とする請求項1に記載の曝気設備。   The aeration equipment according to claim 1, further comprising a baffle plate provided so as to extend in a vertical direction in the second water channel. 前記散気装置は、水面から4m〜6mの深さ位置に設けられていることを特徴とする請求項1に記載の曝気設備。   The aeration apparatus according to claim 1, wherein the air diffuser is provided at a depth of 4 to 6 m from the water surface. 被処理水を貯留するための曝気槽と、
前記曝気槽の底面より所定間隙を隔てた高さ位置から鉛直方向に立設されており、該曝気槽を並び方向に順に第1から第4の水路の4水路に区分する3つの仕切壁と、
前記第1及び第2の水路のいずれか一方の深さ方向における中央部、及び前記第3及び第4の水路のいずれか一方の深さ方向における中央部にそれぞれ設けられた散気装置と、
を備えることを特徴とする曝気設備。
An aeration tank for storing treated water;
Three partition walls that are erected in a vertical direction from a height position that is separated from the bottom surface of the aeration tank by a predetermined distance, and that divides the aeration tank into four water channels of a first to a fourth water channel in the arrangement direction; ,
An air diffuser provided at a central portion in the depth direction of any one of the first and second water channels, and a central portion in the depth direction of any one of the third and fourth water channels,
An aeration facility characterized by comprising:
前記第1及び第2の水路の前記一方とは異なる他方の深さ方向における中央部、及び前記第3及び第4の水路の前記一方とは異なる他方の深さ方向における中央部にそれぞれ設けられており、前記散気装置よりも散気量の小さい他の散気装置を備えることを特徴とする請求項4に記載の曝気設備。   The first and second water channels are respectively provided in a central portion in the other depth direction different from the one and in the other central portion in the other depth direction different from the one of the third and fourth water channels. The aeration apparatus according to claim 4, further comprising another aeration device having a smaller amount of aeration than the aeration device.
JP2003412297A 2003-12-10 2003-12-10 Aeration equipment Expired - Fee Related JP3884735B2 (en)

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CN106045012A (en) * 2016-07-13 2016-10-26 农业部沼气科学研究所 Micropower slow-release type aeration structure and method
JP2019076887A (en) * 2017-10-23 2019-05-23 前澤工業株式会社 Waste water treatment apparatus and waste water treatment method
JP2020075224A (en) * 2018-11-09 2020-05-21 前澤工業株式会社 Sewage treatment device and method of sewage treatment
CN112479373A (en) * 2020-11-11 2021-03-12 绍兴水处理发展有限公司 Oxidation ditch sewage treatment process

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JP2000157848A (en) * 1998-11-26 2000-06-13 Kubota Corp Immersion type membrane separator
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JP2002066586A (en) * 2000-08-30 2002-03-05 Ngk Insulators Ltd Method for circulating nitrification fungus carrier for deep aeration tank

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JPH078982A (en) * 1993-06-23 1995-01-13 Hitachi Plant Eng & Constr Co Ltd Revolving flow aeration apparatus
JPH11128929A (en) * 1997-11-04 1999-05-18 Mitsubishi Kakoki Kaisha Ltd Solid-liquid separator for sludge mixed liquid
JP2000157848A (en) * 1998-11-26 2000-06-13 Kubota Corp Immersion type membrane separator
JP2000279993A (en) * 1999-03-31 2000-10-10 Nkk Corp Waste water treatment and apparatus therefor
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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010119980A (en) * 2008-11-21 2010-06-03 Jfe Steel Corp Wastewater treatment apparatus and method
CN106045012A (en) * 2016-07-13 2016-10-26 农业部沼气科学研究所 Micropower slow-release type aeration structure and method
JP2019076887A (en) * 2017-10-23 2019-05-23 前澤工業株式会社 Waste water treatment apparatus and waste water treatment method
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JP2020075224A (en) * 2018-11-09 2020-05-21 前澤工業株式会社 Sewage treatment device and method of sewage treatment
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CN112479373A (en) * 2020-11-11 2021-03-12 绍兴水处理发展有限公司 Oxidation ditch sewage treatment process

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