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JPH105776A - Treating device of organic waste water - Google Patents

Treating device of organic waste water

Info

Publication number
JPH105776A
JPH105776A JP16712296A JP16712296A JPH105776A JP H105776 A JPH105776 A JP H105776A JP 16712296 A JP16712296 A JP 16712296A JP 16712296 A JP16712296 A JP 16712296A JP H105776 A JPH105776 A JP H105776A
Authority
JP
Japan
Prior art keywords
tank
flow rate
gas
aeration tank
waste water
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP16712296A
Other languages
Japanese (ja)
Inventor
Kazuhiro Nomura
和弘 野村
Tatsuo Suzuki
達雄 鈴木
Hirohiko Akese
博彦 明瀬
Michio Itoi
道雄 糸井
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
SANMETSUKU KK
SERUPOOLE KOGYO KK
Hazama Ando Corp
Original Assignee
SANMETSUKU KK
SERUPOOLE KOGYO KK
Hazama Gumi Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by SANMETSUKU KK, SERUPOOLE KOGYO KK, Hazama Gumi Ltd filed Critical SANMETSUKU KK
Priority to JP16712296A priority Critical patent/JPH105776A/en
Publication of JPH105776A publication Critical patent/JPH105776A/en
Pending legal-status Critical Current

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  • Treatment Of Biological Wastes In General (AREA)

Abstract

PROBLEM TO BE SOLVED: To efficiently and sufficiently treat organic waste water with changing quantity and quality by providing a gas-liquid mixer for mixing the organic waste water with air in a flow rate adjusting tank or an aeration tank, in an organic waste water treating device provided with the flow rate adjusting tank, the aeration tank and a precipitation tank. SOLUTION: This device is provided with the flow rate adjusting tank 1 for performing 1st order storage of the organic discharge water, the aeration tank 2 for mixing the waste water fed from the flow rate adjusting tank 1 with air and being brought into contact with microorganisms, and the precipitation tank 3 for precipitating sludge of the discharge water fed from the aeration tank 2. The gas-liquid mixer 5 is provided on the flow rate adjusting tank 1, and this gas-liquid mixer 5 force-feeds oxygen into the discharge water sucked from the flow rate adjusting tank 1 and mixes with it, and then the discharge water is fed back to the flow rate adjusting tank 1. Thus, the discharge water incorporating a large quantity of oxygen, accelerates activation of microorganisms in the aeration tank 2. Also, the gas-liquid mixer 5 provided between a concentrating tank 4 and the aeration tank 2 activates microorganisms by mixing oxygen into the separated liquid sucked from the concentrating tank 4.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、排水の水質処理装
置に関し、詳細には、し尿や食品工場等から排出される
有機排水の処理装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an apparatus for treating water quality of wastewater, and more particularly, to an apparatus for treating organic wastewater discharged from human waste and food factories.

【0002】[0002]

【従来の技術】し尿や食品工場等から排出される有機排
水を処理する場合には、例えば図3に示す工程を経て処
理され、河川等に放流されるのが一般的である。以下図
3を説明する。流量調整槽100は、食品工場等から排
出される排水の原水を貯水するための槽であり、以降の
工程の処理能力に応じた水量を曝気槽へ送流するポンプ
を具備するものである。曝気槽101は、送流された排
水に微生物と空気(酸素等)を混合させ、排水中の有機
物を当該微生物に生物的処理させるものである。これに
より、排水中の有機物を低減させることができるが、そ
の結果として微生物が肥大し汚泥化する。 沈殿槽10
2は、肥大化した微生物を汚泥として沈殿させるもので
あり、所定時間経過後、その上澄液を河川等に放流し、
汚泥を次工程の濃縮槽103へ搬送するものである。従
って、沈殿槽102はポンプあるいはパイプラインを具
備し、これにより半液状物である汚泥を濃縮槽103へ
搬送する。濃縮槽103は、汚泥をろ過する装置を具備
し、汚泥を固体と液体に分離するものである。分離され
た固体は産業廃棄物として処分され、残留汚泥を含む液
体は曝気槽101にポンプなどで還流され再処理され
る。
2. Description of the Related Art In the case of treating human wastewater and organic wastewater discharged from food factories and the like, it is general that the wastewater is processed through, for example, the process shown in FIG. 3 and discharged into a river or the like. FIG. 3 will be described below. The flow rate adjusting tank 100 is a tank for storing raw water of wastewater discharged from a food factory or the like, and includes a pump for sending an amount of water according to the processing capacity of the subsequent process to the aeration tank. The aeration tank 101 mixes microorganisms and air (oxygen or the like) into the sent wastewater, and biologically treats the microorganisms in the wastewater. As a result, the organic matter in the wastewater can be reduced, but as a result, the microorganisms are enlarged and sludge is formed. Settling tank 10
2 is to sediment the enlarged microorganisms as sludge, and after a lapse of a predetermined time, discharge the supernatant to a river or the like,
The sludge is transported to the concentration tank 103 in the next step. Therefore, the sedimentation tank 102 is provided with a pump or a pipeline, and thereby transports the semi-liquid sludge to the concentration tank 103. The concentration tank 103 is provided with a device for filtering sludge, and separates sludge into solid and liquid. The separated solid is disposed of as industrial waste, and the liquid containing residual sludge is returned to the aeration tank 101 by a pump or the like and reprocessed.

【0003】[0003]

【発明が解決しようとする課題】ここで、し尿や食品工
場等から排出される有機排水の量あるいは質は、時間
帯、季節等によって大きく変動するものであり、年間を
通じて一定ではないことが知られている。従って、当該
排水処理装置を設計するにあたり、排水量等が多大な季
節等に沿って大規模な処理装置を設計すれば、他の季節
等において装置を十分に稼働させる必要が無く、処理装
置の敷地、設置の費用および管理維持費等の経済的な点
から妥当でない。一方、平均的な排水量等を意図して当
該処理装置を設計したのでは、排水量等が過大な場合に
排水を十分に処理することができず、そのような処理排
水を河川に放流することにより環境汚染は免れず、かと
いって、処理装置の設備拡大改修は処理の一時停止を余
儀なくさせ、また多大な経費を必要とするといった問題
点があった。
Here, it is known that the amount or quality of the organic wastewater discharged from night soil and food factories fluctuates greatly depending on the time of day, season, and the like, and is not constant throughout the year. Have been. Therefore, in designing the wastewater treatment device, if a large-scale treatment device is designed in accordance with the season when the amount of wastewater is large, it is not necessary to operate the device sufficiently in other seasons and the like, It is not appropriate from the economic point of installation cost and maintenance cost. On the other hand, if the treatment equipment is designed with the intention of an average amount of wastewater, the wastewater cannot be sufficiently treated when the amount of wastewater is excessive, and by discharging such treated wastewater to a river. Environmental pollution is unavoidable. However, the expansion and renovation of the processing equipment has a problem that the processing must be temporarily stopped and a large amount of cost is required.

【0004】また、排水量等が処理装置の処理能力を上
回った場合の対策としては、前記沈殿工程において、沈
殿槽に凝集剤を投入し、汚泥の凝固沈殿化促進を図る方
法や、前記曝気槽101の工程において、曝気槽に酵素
などの特殊薬剤を投入し微生物の活性化を図る方法があ
る。しかしながら、上記薬剤等は高価なものであり、継
続的な投入には適応しない。さらに、前者の凝集剤投入
による方法によれば、微生物の活性化を著しく害するた
め、生物処理が好適に実施されず、生物処理が極めて重
要な排水処理では致命的であり、また、後者の酵素等の
投入による方法によれば、当該酵素等の量、質を当該処
理排水に適合させなければ十分な効果を得られないため
に、その調整等の管理を更に必要とするといった問題点
もあった。
[0004] As a countermeasure when the amount of wastewater exceeds the treatment capacity of the treatment apparatus, a method of introducing a flocculant into the sedimentation tank in the sedimentation step to promote coagulation and sedimentation of the sludge or the aeration tank In the step 101, there is a method of activating a microorganism by introducing a special agent such as an enzyme into an aeration tank. However, the above-mentioned drugs and the like are expensive and are not adapted to continuous input. Furthermore, according to the former method using a flocculant, the activation of microorganisms is significantly impaired, so that biological treatment is not suitably performed, and biological treatment is fatal in wastewater treatment, which is extremely important. However, there is also a problem that if the quantity and quality of the enzyme and the like are not adapted to the treated wastewater, a sufficient effect cannot be obtained, and thus further control of adjustment and the like is required. Was.

【0005】従って、本発明の目的は、量、質が時々に
よって変動する排水を無駄なく十分に、かつ経済的に処
理しうる有機排水の処理装置を提供することにある。
SUMMARY OF THE INVENTION Accordingly, an object of the present invention is to provide an organic wastewater treatment apparatus capable of sufficiently and economically treating wastewater whose quantity and quality fluctuate from time to time.

【0006】[0006]

【課題を解決するための手段】本発明によれば、有機排
水を一時貯水するための流量調整槽と、当該流量調整槽
から所定量の有機排水を送流され、これに空気の混合と
微生物との接触を行なう曝気槽と、当該曝気槽から送流
された有機排水の汚泥を沈殿するための沈殿槽とを備え
る有機排水の処理装置において、前記流量調整槽または
前記曝気槽にその有機排水に空気を混合させる気液混合
機を設けたことを特徴とする有機排水の処理装置が提供
される。また、本発明によれば、有機排水を一時貯水す
るための流量調整槽と、当該流量調整槽から所定量の有
機排水を送流され、これに空気の混合と微生物との接触
を行なう曝気槽と、当該曝気槽から送流された有機排水
の汚泥を沈殿し、その上澄液を河川等に放流するための
沈殿槽と、当該沈殿槽の底部汚泥を濃縮し、その脱離液
を前記曝気槽に還流する濃縮槽とを備える有機排水の処
理装置において、前記濃縮槽と前記曝気槽との間と、前
記流量調整槽または前記曝気槽のどちらか一方とにその
有機排水に空気を混合させる気液混合機を設けたことを
特徴とする有機排水の処理装置が提供される。
According to the present invention, a flow regulating tank for temporarily storing organic waste water, and a predetermined amount of organic waste water are sent from the flow regulating tank, where air is mixed with microorganisms. An aeration tank for contacting with an aeration tank, and a sedimentation tank for sedimenting the sludge of the organic wastewater sent from the aeration tank, wherein the organic wastewater is supplied to the flow rate adjustment tank or the aeration tank. Provided with a gas-liquid mixer for mixing air with the organic wastewater. Further, according to the present invention, a flow rate adjusting tank for temporarily storing organic waste water, and an aeration tank for sending a predetermined amount of organic waste water from the flow rate adjusting tank and mixing it with air and contacting with microorganisms. And sedimentation of the sludge of the organic wastewater sent from the aeration tank, a sedimentation tank for discharging the supernatant to a river or the like, and concentrating the bottom sludge of the sedimentation tank. In an organic wastewater treatment device including a concentration tank that returns to an aeration tank, air is mixed with the organic wastewater between the concentration tank and the aeration tank and either the flow rate adjustment tank or the aeration tank. An apparatus for treating organic wastewater, comprising a gas-liquid mixer for causing the mixture to flow.

【0007】前記気液混合機は、付加的に設置した前記
各部から排水を吸引、還流するためのポンプ等の吸引手
段を具備したものであり、また、酸素または純オゾンガ
ス、あるいはそれらを含有した空気を、吸引した排水に
混合させるコンプレッサー等の気液混合手段を少くとも
具備するものである。気液混合機は、通常は停止させる
ものであって、排水量が、処理装置の処理量を超過した
場合に作動させるものである。本発明の有機排水の処理
装置によれば、気液混合機により排水へ空気を効率良く
混合し、排水の酸素等の含有率を向上することにより、
微生物の活性化を促進することができるため、生物処理
が極めて重要な排水処理においては、特に有効な処理を
効率良く行なうことができる。従って、全体として比較
的小規模な処理装置であっても、気液混合機をその処理
量に応じて作動させることにより、効率良く排水処理を
行なうことができる。
The gas-liquid mixer is provided with a suction means such as a pump for sucking and refluxing waste water from each of the additionally provided parts, and further contains oxygen or pure ozone gas or contains them. The apparatus is provided with at least gas-liquid mixing means such as a compressor for mixing air with the suctioned waste water. The gas-liquid mixer is normally stopped, and is operated when the amount of wastewater exceeds the processing amount of the processing apparatus. According to the organic wastewater treatment device of the present invention, the air is efficiently mixed into the wastewater by the gas-liquid mixer to improve the content of oxygen and the like in the wastewater,
Since the activation of microorganisms can be promoted, particularly effective wastewater treatment can be efficiently performed in wastewater treatment where biological treatment is extremely important. Therefore, even if the processing apparatus is relatively small as a whole, the wastewater treatment can be efficiently performed by operating the gas-liquid mixer according to the processing amount.

【0008】前記設置、撤去自在に設けたとは、処理が
要求される排水の量および質に応じて、前記気液混合機
を付加的に設置、撤去可能である意である。すなわち、
気液混合機は、処理すべき排水量に対し、気液混合機を
除く本発明にかかる有機排水の処理装置全体の処理能力
が劣る場合に必要に応じて設置し、必要が無ければ、撤
去して別途保管しても良い。当該設置の選択をすること
により処理装置全体として、量、質が時々によって変化
する排水に対し極めて合理的な処理を可能とする。しか
も、気液混合機は吸引手段と気液混合手段とを備えれば
十分であり、設置、撤去及び保管に際し広範な敷地、お
よび大規模な施工工事を必要とせず、経済的負担は少な
い。
[0008] The term "installable and removable" means that the gas-liquid mixer can be additionally installed and removed according to the amount and quality of wastewater required to be treated. That is,
The gas-liquid mixer is installed as necessary when the processing capacity of the entire organic wastewater treatment apparatus according to the present invention is inferior to the amount of wastewater to be treated, excluding the gas-liquid mixer, and is removed if unnecessary. May be stored separately. By selecting the installation, it is possible to perform extremely rational treatment of wastewater whose quantity and quality change from time to time as a whole of the treatment apparatus. Moreover, the gas-liquid mixer only needs to include the suction means and the gas-liquid mixing means, and does not require a wide area and large-scale construction work for installation, removal, and storage, so that the economic burden is small.

【0009】気液混合機を設置する前記各部の原水量
と、気液混合機により循環される循環水量との体積割合
は、1:1乃至10、特に1:3が好適である。また、
循環水量と混合する空気量との体積割合は、排水の汚濁
濃度や混合する空気の性状により適宜定めるものである
が、循環水量:空気量=1:0.05乃至0.4、特に
1:0.2が好適である。さらに、気液混合機を設置す
る前記各部の水交換率(各部の容量m3/循環量m3
時)は、排水の汚濁濃度等により適宜定めるものである
が、概ね数回/時が好適である。
The volume ratio of the amount of raw water in each section where the gas-liquid mixer is installed to the amount of circulating water circulated by the gas-liquid mixer is preferably from 1: 1 to 10, particularly preferably 1: 3. Also,
The volume ratio of the amount of circulating water to the amount of air to be mixed is appropriately determined depending on the pollutant concentration of the wastewater and the properties of the air to be mixed, but the amount of circulating water: air amount = 1: 0.05 to 0.4, particularly 1: 0.2 is preferred. Furthermore, the water exchange rate of each part where the gas-liquid mixer is installed (volume m 3 of each part / circulation amount m 3 /
The time) is appropriately determined depending on the pollutant concentration of the waste water, etc., and is preferably several times / hour.

【0010】[0010]

【実施例】 以下、
本発明の好適な実施例を添付図面に基づいて説明する。
図1は、本発明にかかる有機排水処理装置の処理工程を
示す図である。図中の、流量調整槽1、曝気槽2、沈殿
槽3および濃縮槽4で行なわれる処理は図3に示した従
来の処理装置と同様であるため、説明を省略する。気液
混合機5、5’は、共に後述する図2の構成を採用する
ものであって、このうち気液混合機5は流量調整槽1に
貯水された排水を吸引し、これに酸素を圧送、混入させ
た後、流量調整槽1に還流させる。従って、流量調整槽
1に貯水された排水は酸素を多く含有したものとなり、
次工程の曝気槽2において、微生物の活性化を促進し、
有機物質の含有量を著しく低下させる。また、流量調整
槽1には通常、微生物を投入しないが、空気中及び排水
中にも微生物は存在するものであるため、気液混合機5
により酸素を含有させることにより、自然界に存在する
微生物が活性化され、有機物の含有量を低下させるとい
う効果も奏する。
[Examples]
Preferred embodiments of the present invention will be described with reference to the accompanying drawings.
FIG. 1 is a view showing a process of an organic wastewater treatment apparatus according to the present invention. In the figure, the processes performed in the flow control tank 1, aeration tank 2, sedimentation tank 3, and concentration tank 4 are the same as those of the conventional processing apparatus shown in FIG. Each of the gas-liquid mixers 5 and 5 'adopts the configuration shown in FIG. 2 described later. Among them, the gas-liquid mixer 5 sucks the wastewater stored in the flow rate adjusting tank 1, and supplies oxygen thereto. After being fed under pressure and mixed, the mixture is returned to the flow control tank 1. Therefore, the wastewater stored in the flow control tank 1 contains a large amount of oxygen,
In the aeration tank 2 in the next step, the activation of microorganisms is promoted,
Significantly reduce the content of organic substances. Although microorganisms are not usually introduced into the flow control tank 1, since microorganisms are present in the air and wastewater, the gas-liquid mixer 5 is used.
By containing oxygen, the effect of activating microorganisms existing in the natural world and reducing the content of organic substances is also exerted.

【0011】一方、濃縮槽4と曝気槽2との間に設けら
れた気液混合機5’は、濃縮槽4からの脱離液を吸引
し、これに酸素を混合させることにより、排水にそもそ
も存在する油分および凝集剤あるいは沈殿槽3により一
時的に投入された凝集剤等により鈍化する微生物の活性
を活発化することができる。図2は、流量調整槽1に気
液混合機5を設置した状態を示す構成図である。気液混
合機5は、循環ポンプ6、コンプレッサ7および撹拌器
8を基本的構成とするものである。各々の作用について
は、循環ポンプ6は、管9およびジョイント部11を介
して、流量調整槽1から排水を汲み上げ、撹拌器8へと
循環させる。撹拌器8において排水は、コンプレッサ7
から酸素を供給され、撹拌器8により撹拌されることに
より、混合が促進される。酸素が混合した排水は、管
9’およびジョイント部11を介して、流量調整槽1に
還流される。
On the other hand, a gas-liquid mixer 5 ′ provided between the concentration tank 4 and the aeration tank 2 sucks the desorbed liquid from the concentration tank 4 and mixes it with oxygen to produce waste water. The activity of microorganisms that are slowed down by the oil and coagulant originally present or the coagulant temporarily supplied by the sedimentation tank 3 can be activated. FIG. 2 is a configuration diagram showing a state where the gas-liquid mixer 5 is installed in the flow rate adjusting tank 1. The gas-liquid mixer 5 basically has a circulation pump 6, a compressor 7, and a stirrer 8. Regarding each operation, the circulation pump 6 pumps up the wastewater from the flow control tank 1 via the pipe 9 and the joint portion 11 and circulates the wastewater to the stirrer 8. The waste water in the stirrer 8 is supplied to the compressor 7
Is supplied from the mixture, and the mixture is stirred by the stirrer 8, thereby promoting the mixing. The wastewater mixed with oxygen is returned to the flow control tank 1 through the pipe 9 ′ and the joint 11.

【0012】かかる構成により、処理される排水は常に
多量の酸素を含むものとなるため、微生物の活性化が促
進され、好適に排水処理が行なわれる。また、気液混合
機5、5’は図2に示すとおり極めて簡素な構成であ
り、設置場所も取らないので必要に応じて、設置、撤去
を可能とする。
[0012] With this configuration, the wastewater to be treated always contains a large amount of oxygen, so that the activation of microorganisms is promoted and the wastewater treatment is suitably performed. The gas-liquid mixers 5 and 5 'have a very simple configuration as shown in FIG. 2 and do not require an installation place, so that they can be installed and removed as needed.

【0013】表1に本発明にかかる有機排水の処理装置
による排水処理の実験結果を示す。
Table 1 shows the results of experiments on wastewater treatment by the organic wastewater treatment apparatus according to the present invention.

【0014】[0014]

【表1】 [Table 1]

【0015】本実験は、し尿処理場に本願発明にかかる
有機排水の処理装置を設置したものであり、表1中の日
付の8月19日後に、図1に示した処理装置について、
気液混合機5を付加設置したものである。気液混合機5
の設置前においては、設計水量の最大375%の排水を
受け入れ、また、凝集剤の影響で生物浄化が十分でな
く、沈殿槽3において汚泥の沈降性が不良であり、沈殿
槽から汚泥が流出していた。気液混合機5を設置した8
月19日以降における顕著な結果を以下に述べる。 BOD(生物科学的酸素要求量)が低下(日前:8.6〜
64→日後:3〜13ppm)した。汚泥の沈降性が向上し、沈
殿槽3からの流出がなくなった。汚泥の沈降性を表 す
SVI(Sludege Volume Index)を算出すると、日前:25
0→日後:120となった。 曝気槽中の溶存酸素濃度を向上できた(日前:2→日
後:4ppm)。その結果として、曝気槽2での曝気量を低減
でき、消費電力を低減できた。 凝集剤、栄養剤、pH調整剤を添加する必要が無くな
った。 汚泥の活性が高まり、汚泥の自己分解が進み処理処分
する汚泥量が50〜60%低減できた。 このように、気液混合機5を付加設置することが極めて
有効であることが確認できる。
In this experiment, an organic wastewater treatment apparatus according to the present invention was installed in a human waste treatment plant. On August 19, the date shown in Table 1, the treatment apparatus shown in FIG.
The gas-liquid mixer 5 is additionally provided. Gas-liquid mixer 5
Before the installation, the wastewater with a maximum of 375% of the design water volume was accepted, the biological purification was not enough due to the influence of the flocculant, the sedimentation of the sludge was poor in the sedimentation tank 3, and the sludge flowed out from the sedimentation tank. Was. 8 equipped with gas-liquid mixer 5
The remarkable results after March 19 are described below. BOD (Biological oxygen demand) decreased (before: 8.6-
64 → day later: 3 to 13 ppm). The sedimentation of the sludge was improved, and the outflow from the settling tank 3 was eliminated. The SVI (Sludege Volume Index), which indicates the sedimentation of sludge, was calculated.
0 → Day later: 120. The dissolved oxygen concentration in the aeration tank could be improved (before: 2 → day: 4 ppm). As a result, the amount of aeration in the aeration tank 2 can be reduced, and the power consumption can be reduced. There is no need to add coagulants, nutrients, and pH adjusters. The activity of sludge increased, and the amount of sludge to be disposed of was reduced by 50 to 60% due to the progress of self-decomposition of sludge. Thus, it can be confirmed that the additional installation of the gas-liquid mixer 5 is extremely effective.

【0016】[0016]

【発明の効果】以上述べてきたとおり、本発明の有機排
水の処理装置によれば、気液混合機を設けることによ
り、比較的小規模な処理装置であっても、時々によって
量、質が変動する有機排水を無駄なく十分に処理するこ
とができる。気液混合機は、極めて簡素な構成であるた
め、その設置、撤去をすることも可能であり、また、当
該処理装置の設計に際し、全体として比較的小規模な設
計仕様を採用することができるため、経済的負担も少な
い。
As described above, according to the organic wastewater treatment apparatus of the present invention, by providing a gas-liquid mixer, even a relatively small-scale treatment apparatus can sometimes have a small quantity and quality. The fluctuating organic wastewater can be sufficiently treated without waste. Since the gas-liquid mixer has a very simple configuration, it can be installed and removed, and when designing the processing apparatus, a relatively small design specification can be adopted as a whole. Therefore, the economic burden is small.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明の有機排水の処理装置の処理工程を示す
図である。
FIG. 1 is a view showing a treatment process of an organic wastewater treatment device of the present invention.

【図2】流量調整槽1及び気液混合機5の構成を示す図
である。
FIG. 2 is a diagram showing a configuration of a flow rate adjusting tank 1 and a gas-liquid mixer 5;

【図3】従来の有機排水の処理装置の処理工程を示す図
である。
FIG. 3 is a view showing a processing step of a conventional organic wastewater treatment apparatus.

【符号の説明】[Explanation of symbols]

1.流量調整槽 5.気液混合機 6.循環ポンプ 7.コンプレッサ 8.撹拌器 9、9’.管 10.曝気槽2への管 11.ジョイント部 1. Flow control tank 5. Gas-liquid mixer 6. Circulation pump 7. Compressor 8. Stirrer 9, 9 '. Tube 10. 10. Pipe to aeration tank 2 Joint part

───────────────────────────────────────────────────── フロントページの続き (72)発明者 鈴木 達雄 東京都港区北青山2−5−8 株式会社間 組内 (72)発明者 明瀬 博彦 神奈川県藤沢市本藤沢2−14−4 株式会 社サンメック内 (72)発明者 糸井 道雄 東京都中央区日本橋2−2−18 セルポー ル工業株式会社内 ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Tatsuo Suzuki 2-5-8 Kita-Aoyama, Minato-ku, Tokyo Tokyo, Japan (72) Inventor Hirohiko Akase 2-14-4 Motofujisawa, Fujisawa-shi, Kanagawa Corporation Inside Sunmec (72) Inventor Michio Itoi Inside 2-2-18 Nihonbashi, Chuo-ku, Tokyo Cellpore Industries, Ltd.

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 有機排水を一時貯水するための流量調整
槽と、当該流量調整槽から所定量の有機排水を送流さ
れ、これに空気の混合と微生物との接触とを行なう曝気
槽と、当該曝気槽から送流された有機排水の汚泥を沈殿
するための沈殿槽とを備える有機排水の処理装置におい
て、 前記流量調整槽または前記曝気槽にその有機排水に空気
を混合させる気液混合機を設けたことを特徴とする有機
排水の処理装置。
1. A flow rate adjusting tank for temporarily storing organic waste water, an aeration tank for sending a predetermined amount of organic waste water from the flow rate adjusting tank, and mixing the air with the microorganism and contacting with microorganisms. An organic wastewater treatment device comprising: a sedimentation tank for sedimenting the organic wastewater sent from the aeration tank; and a gas-liquid mixer that mixes the organic wastewater with the flow rate adjustment tank or the aeration tank. An organic wastewater treatment device, comprising:
【請求項2】 有機排水を一時貯水するための流量調整
槽と、当該流量調整槽から所定量の有機排水を送流さ
れ、これに空気の混合と微生物との接触を行なう曝気槽
と、当該曝気槽から送流された有機排水の汚泥を沈殿
し、その上澄液を河川等に放流するための沈殿槽と、当
該沈殿槽の底部汚泥を濃縮し、その脱離液を前記曝気槽
に還流する濃縮槽とを備える有機排水の処理装置におい
て、 前記濃縮槽と前記曝気槽との間と、前記流量調整槽また
は前記曝気槽のどちらか一方とにその有機排水に空気を
混合させる気液混合機を設けたことを特徴とする有機排
水の処理装置。
2. A flow regulating tank for temporarily storing organic waste water, an aeration tank which is supplied with a predetermined amount of organic waste water from the flow regulating tank and mixes air therewith and makes contact with microorganisms. The sediment of the organic wastewater sent from the aeration tank is settled, and the sedimentation tank for discharging the supernatant liquid to rivers, etc., and the bottom sludge of the sedimentation tank are concentrated, and the desorbed liquid is sent to the aeration tank. An organic wastewater treatment device comprising a recirculating concentration tank, wherein a gas-liquid mixture between the concentration tank and the aeration tank, and either the flow rate adjustment tank or the aeration tank and air mixed with the organic wastewater. An organic wastewater treatment device comprising a mixer.
【請求項3】 前記気液混合機を設置、撤去自在に設け
たことを特徴とする請求項1又は2に記載の有機排水の
処理装置。
3. The organic wastewater treatment apparatus according to claim 1, wherein the gas-liquid mixer is installed and removed.
JP16712296A 1996-06-27 1996-06-27 Treating device of organic waste water Pending JPH105776A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP16712296A JPH105776A (en) 1996-06-27 1996-06-27 Treating device of organic waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP16712296A JPH105776A (en) 1996-06-27 1996-06-27 Treating device of organic waste water

Publications (1)

Publication Number Publication Date
JPH105776A true JPH105776A (en) 1998-01-13

Family

ID=15843854

Family Applications (1)

Application Number Title Priority Date Filing Date
JP16712296A Pending JPH105776A (en) 1996-06-27 1996-06-27 Treating device of organic waste water

Country Status (1)

Country Link
JP (1) JPH105776A (en)

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