JP2005230588A - Treating method for foaming scum - Google Patents

Treating method for foaming scum Download PDF

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JP2005230588A
JP2005230588A JP2004039207A JP2004039207A JP2005230588A JP 2005230588 A JP2005230588 A JP 2005230588A JP 2004039207 A JP2004039207 A JP 2004039207A JP 2004039207 A JP2004039207 A JP 2004039207A JP 2005230588 A JP2005230588 A JP 2005230588A
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container
sludge
scum
physical force
outside
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Makoto Nomura
誠 埜村
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Kurita Water 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
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    • Y02W10/10Biological treatment of water, waste water, or sewage

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  • Treatment Of Sludge (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a treating method for foaming scum by which the foaming scum can be easily liquefied and treated without requiring addition of large-scale equipment concerned with a water cleaning function and without using chemicals, or the like. <P>SOLUTION: As the treating method for the foaming scum, in activated sludge treatment which cleans impurities in water by using aerobic bacteria, the foaming scum 11 produced by activity of actinomycetes is moved to another vessel 12 and physical force (fall of the vessel 12, application of vibration and application of shock by blow) is applied to the vessel 12 from the outside to defoam and liquefy the foaming scum 11 in the vessel 12. Then, liquefied sludge is blended with sludge to be discharged as excess sludge outside a system and obtained sludge mixture is subjected to thickening dehydration by a dehydrator 15 and is treated as industrial waste (dehydrated cake). <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

本発明は、活性汚泥処理において放線菌の活動によって発生した発泡スカムの処理方法に関するものである。   The present invention relates to a method for treating foam scum generated by the activity of actinomycetes in activated sludge treatment.

好気性微生物を用いて排水中の不純物を浄化する活性汚泥処理においては、排水を曝気槽において活性汚泥と混合して曝気し、好気性処理により排水中の有機固形物を分解した後、曝気処理後の汚泥混合液を沈澱池に導き、ここで活性汚泥及び非生物分解性物質の固形分と水とに分離し、上澄水を処理水として排出する一方、固形分はその一部を曝気槽に返送して活性汚泥として利用し、残部を余剰汚泥として排出している。   In activated sludge treatment that purifies impurities in wastewater using aerobic microorganisms, wastewater is mixed with activated sludge in an aeration tank and aerated, and after aerobic treatment decomposes organic solids in wastewater, aeration treatment The sludge mixture afterwards is guided to the sedimentation basin, where it separates into activated sludge and non-biodegradable substance solids and water, and the supernatant water is discharged as treated water, while a part of the solids is in the aeration tank. It is returned to the factory and used as activated sludge, and the remainder is discharged as excess sludge.

ところで、曝気槽では好気性菌である放線菌にとって必要な酸素が十分与えられるために該放線菌が異常に増殖することがある。そして、活性汚泥中の放線菌濃度が高まると、放線菌が生物由来の界面活性剤様の物質を放出し、気泡と共に水面に浮上するが、このとき、汚泥フロックの一部がこの気泡と放線菌放出物とに付着して浮上するため、これらが発泡スカムとなって曝気槽の表面に蓄積していく。   By the way, in the aeration tank, the oxygen necessary for actinomycetes, which are aerobic bacteria, is sufficiently supplied, so that the actinomycetes may grow abnormally. When the concentration of actinomycetes in activated sludge increases, actinomycetes release biologically derived surfactant-like substances and float on the water surface together with bubbles. At this time, some of the sludge flocs are released from these bubbles and rays. Since they adhere to the fungus discharge and float, they become foam scum and accumulate on the surface of the aeration tank.

発泡スカムは、曝気槽から沈澱池に流入し、沈澱池で固液分離されず処理水に混入して水質の悪化を招いたり、風に吹き飛ばされたり、発泡が激しいときには曝気槽からオーバーフローしたりして、周囲の環境を汚染したりすることがある。   Foaming scum flows into the sedimentation pond from the aeration tank and does not separate into solid and liquid in the sedimentation pond, causing deterioration of the water quality, blowing off in the wind, and overflowing from the aeration tank when foaming is severe. And may contaminate the surrounding environment.

そこで、曝気槽や沈澱池には、発泡スカムを除去するためのスカムスキマー等のスカム除去装置が設けられている。その他、発泡スカムの処理方法としては、浮遊する発泡スカムに水を散水してスカムを物理的に破砕する消泡散水法がある。又、生物学的に放線菌を抑制する方法として、放線菌の増殖速度以上の速さで汚泥として系外に排出する汚泥滞留時間制御法(例えば、特許文献1参照)等が従来から知られている。   Therefore, a scum removing device such as a scum skimmer for removing foamed scum is provided in the aeration tank and the settling basin. In addition, as a method for treating foamed scum, there is a defoaming watering method in which water is sprinkled on a floating foamed scum to physically break the scum. In addition, as a method for biologically suppressing actinomycetes, a sludge residence time control method for discharging sludge out of the system as a sludge at a speed higher than the growth rate of actinomycetes (see, for example, Patent Document 1) has been conventionally known. ing.

又、近年、発泡スカムの除去或は発生を抑制するための種々の提案がなされている。例えば、活性汚泥処理設備の曝気槽や沈澱池において発生した発泡スカムをスカムスキマーで排出したスカム水に対して種々の殺菌手段(オゾンの注入、紫外線の照射、塩素系殺菌剤の添加、超音波の利用等)を施したり(特許文献2参照)、沈澱池からの汚泥を曝気槽に返送する前に、別の返送汚泥曝気槽に導入して意図的にスカムを生成させて除去し、返送汚泥中の放線菌濃度を低下させてから汚泥を曝気槽に返送する方法が提案されている(特許文献3参照)。   In recent years, various proposals have been made to suppress the removal or generation of foam scum. For example, various sterilization means (injection of ozone, irradiation of ultraviolet rays, addition of chlorine-based disinfectant, ultrasonic wave, etc.) against scum water discharged from a scum skimmer from foamed scum generated in an aeration tank or a sedimentation pond of an activated sludge treatment facility (Refer to Patent Document 2) or before returning sludge from the sedimentation basin to the aeration tank, it is introduced into another return sludge aeration tank to intentionally generate and remove scum and return A method has been proposed in which the concentration of actinomycetes in sludge is reduced and the sludge is returned to the aeration tank (see Patent Document 3).

更に、消泡散水法において、消泡水に加水分解酵素を直接添加して放線菌を溶菌する方法(特許文献4)、スカム解消剤を活性汚泥処理系に添加して放線菌による発泡スカムの発生を抑制する方法(特許文献5参照)等も提案されている。   Furthermore, in the defoaming water spray method, a method of lysing actinomycetes by directly adding a hydrolase to the defoaming water (Patent Document 4), adding a scum-removing agent to the activated sludge treatment system, A method for suppressing the generation (see Patent Document 5) has also been proposed.

特開平8−309383号公報JP-A-8-309383 特開平6−262167号公報JP-A-6-262167 特開平8−299980号公報JP-A-8-299980 特開平8−112591号公報Japanese Patent Application Laid-Open No. 8-112591 特開平11−267681号公報JP-A-11-267681

ところが、従来の方法では、その方法を実施するための大掛かりな設備が付加されるために装置のコストアップを招いたり、消泡剤や殺菌剤等の薬剤を用いるために処理水が汚れる等の問題があった。   However, in the conventional method, a large-scale facility for carrying out the method is added, so that the cost of the apparatus is increased, or the treated water is contaminated because a chemical such as an antifoaming agent or a disinfectant is used. There was a problem.

本発明は上記問題に鑑みてなされたもので、その目的とする処は、水の浄化機能に関わるような大掛かりな設備の付加を要することなく、又、薬剤等を使用することなく簡単に発泡スカムを液状化させてこれを処理することができる発泡スカムの処理方法を提供することにある。   The present invention has been made in view of the above-mentioned problems, and its intended process is that foaming can be easily performed without requiring the addition of large-scale equipment related to the water purification function and without using chemicals or the like. An object of the present invention is to provide a method for treating foamed scum capable of liquefying scum and treating it.

上記目的を達成するため、請求項1記載の発明は、好気性微生物を用いて水中の不純物を浄化する活性汚泥処理において、放線菌の活動によって発生した発泡スカムを別の容器に移し、該容器に外部から物理的な力を加えることによって、容器内の発泡スカムを消泡させて液状化させることを特徴とする。   In order to achieve the above object, the invention described in claim 1 is directed to an activated sludge treatment for purifying impurities in water using an aerobic microorganism, and the foamed scum generated by the activity of actinomycetes is transferred to another container. By applying a physical force from the outside, the foamed scum in the container is defoamed and liquefied.

請求項2記載の発明は、請求項1記載の発明において、前記容器を落下させてこれに外部から前記物理的な力を加えることを特徴とする。   The invention according to claim 2 is characterized in that, in the invention according to claim 1, the container is dropped and the physical force is applied to the container from the outside.

請求項3記載の発明は、請求項1記載の発明において、前記容器に振動を与えてこれに外部から前記物理的な力を加えることを特徴とする。   According to a third aspect of the present invention, in the first aspect of the invention, the container is vibrated and the physical force is applied to the container from the outside.

請求項4記載の発明は、請求項1記載の発明において、前記容器に打撃による衝撃を与えてこれに外部から前記物理的な力を加えることを特徴とする。   According to a fourth aspect of the present invention, in the first aspect of the present invention, the container is subjected to impact by hitting and the physical force is applied to the container from the outside.

請求項5記載の発明は、請求項1〜4の何れかに記載の発明において、前記容器内で液状化した汚泥を、余剰汚泥として系外に排出する汚泥に混合し、混合した汚泥を脱水機で濃縮脱水し或は加熱することで脱水乾燥することを特徴とする。   Invention of Claim 5 mixes the sludge liquefied in the said container in the invention in any one of Claims 1-4 with the sludge discharged | emitted out of the system as surplus sludge, and dehydrates the mixed sludge It is characterized in that it is concentrated and dehydrated by a machine or dehydrated and dried by heating.

本発明者の実験によれば、活性汚泥処理において放線菌の活動によって発生した発泡スカムを別の容器に移し、該容器に外部から物理的な力(落下による衝撃、振動、打撃による衝撃等)を加えれば、容器内の発泡スカムが消泡して液状化することが確認された。   According to the experiment of the present inventor, the foamed scum generated by the activity of actinomycetes in the activated sludge treatment is transferred to another container, and physical force (impact by dropping, vibration, impact by impact, etc.) is externally applied to the container. Was added, it was confirmed that the foam scum in the container was defoamed and liquefied.

従って、請求項1〜4記載の発明によれば、設備の付加を要することなく、又、薬剤等を使用することなく、単に容器に外部から物理的な力を加えるだけで簡単に発泡スカムを液状化させてこれを処理することができる。   Therefore, according to the first to fourth aspects of the present invention, the foam scum can be easily formed by simply applying physical force from the outside to the container without the need for additional equipment or using chemicals. It can be liquefied and treated.

又、請求項5記載の発明によれば、容器内で予め液状化した汚泥を、余剰汚泥として系外に排出する汚泥と共に脱水機で発泡することなく濃縮脱水できるようにしたため、脱水によって得られた脱水ケーキを無害な産業廃棄物として処理することができる。勿論、加熱することで脱水乾燥させることができる。   Further, according to the invention described in claim 5, the sludge previously liquefied in the container can be concentrated and dehydrated without being foamed by the dehydrator together with the sludge discharged out of the system as surplus sludge. The dehydrated cake can be treated as harmless industrial waste. Of course, it can be dehydrated and dried by heating.

以下に本発明の実施の形態を添付図面に基づいて説明する。   Embodiments of the present invention will be described below with reference to the accompanying drawings.

図1は本発明方法を実施するための活性汚泥処理設備の模式図であり、同図において、1は曝気槽であって、この曝気槽1には、流入管2を経て下水や排水等の原水が導入される。   FIG. 1 is a schematic diagram of an activated sludge treatment facility for carrying out the method of the present invention. In FIG. 1, reference numeral 1 denotes an aeration tank. The aeration tank 1 is connected to sewage, drainage, etc. via an inflow pipe 2. Raw water is introduced.

そして、曝気槽1においては、散気管3から噴射される空気によって曝気しながら活性汚泥法によって生物処理が施され、原水中の有機物が分解される。尚、散気管3にはコンプレッサ4から圧縮空気が供給されている。   In the aeration tank 1, biological treatment is performed by the activated sludge method while aeration is performed by air jetted from the air diffuser 3, and organic substances in the raw water are decomposed. The air diffuser 3 is supplied with compressed air from the compressor 4.

而して、曝気槽1にて曝気処理された後の汚泥混合液は、移送管5を経て沈澱池6に導入され、ここで活性汚泥及び非生物分解性の固形分(分離汚泥と称する)と水とに分離され、上澄水は処理水として排水管7から排出される一方、分離汚泥は分離汚泥排出管8から取り出され、その一部は返送汚泥として返送管9から前記曝気槽1に返送されて生物処理に供される。又、残余の分離汚泥は、余剰汚泥として排出される。   Thus, the sludge mixed solution after aeration treatment in the aeration tank 1 is introduced into the sedimentation basin 6 through the transfer pipe 5, where activated sludge and non-biodegradable solids (referred to as separated sludge) are introduced. The supernatant water is discharged from the drain pipe 7 as treated water, while the separated sludge is taken out from the separated sludge discharge pipe 8, and a part thereof is returned from the return pipe 9 to the aeration tank 1 as return sludge. Returned for biological treatment. The remaining separated sludge is discharged as excess sludge.

ところで、曝気槽1では好気性菌である放線菌にとって必要な酸素が十分与えられるために該放線菌が異常に増殖する。そして、活性汚泥中の放線菌濃度が高まると、放線菌が生物由来の界面活性剤様の物質を放出し、気泡と共に水面に浮上するが、このとき、汚泥フロックの一部が気泡に付着して浮上するため、これらが発泡スカム11となって曝気槽1の表面に蓄積していく。   By the way, in the aeration tank 1, since oxygen required for actinomycetes which are aerobic bacteria is sufficiently given, the actinomycetes grow abnormally. When the concentration of actinomycetes in activated sludge increases, actinomycetes release biologically derived surfactant-like substances and float on the water surface with bubbles, but at this time, some of the sludge flocs adhere to the bubbles. Therefore, they become foamed scum 11 and accumulate on the surface of the aeration tank 1.

而して、本実施の形態では、曝気槽1内の水面上に層を成して浮遊している発泡スカム11を不図示の柄杓等によってすくい取って別の容器12に移し、この容器12に外部から物理的な力を加えるようにした。   Thus, in the present embodiment, the foamed scum 11 floating in layers on the water surface in the aeration tank 1 is scooped with a handle not shown or the like and transferred to another container 12, and this container 12 Added physical force to the outside.

ここで、容器12に外部から物理的な力を加える具体的な例としては、図2〜図3に示すような方法が考えられる。   Here, as a specific example in which a physical force is applied to the container 12 from the outside, the methods shown in FIGS.

即ち、図2に示す例は、容器12を地面に落下させてこれに外部から衝撃を与える方法であり、図3(a)に示す例は、偏心カム13の回転によって容器12を上下に振動させる方法であり、同図(b)は容器12を振動子14に固定してこれに上下振動を与える方法である。又、図4に示す例は、容器12を打撃してこれに衝撃を与える方法であり、その具体的な方法としては、足で容器12を蹴ったり、棒等で容器12を叩く等の動作が含まれる。   That is, the example shown in FIG. 2 is a method of dropping the container 12 on the ground and applying an impact to the container 12 from the outside. In the example shown in FIG. 3A, the container 12 is vibrated up and down by the rotation of the eccentric cam 13. FIG. 2B shows a method in which the container 12 is fixed to the vibrator 14 and a vertical vibration is applied thereto. Further, the example shown in FIG. 4 is a method of hitting the container 12 and applying an impact thereto. As a specific method, an operation such as kicking the container 12 with a foot or hitting the container 12 with a stick or the like. Is included.

ところで、本発明者の実験によれば、図2に示す例によって容器12に外部から衝撃を加えたことで、容器12内の発泡スカム11が消泡して液状化することが確認された。具体的には、初め容量:100L(リットル)であった発泡スカムが、繰り返し3回の落下の実施で5Lにまで減容し、発泡の無い液状となった。   By the way, according to the experiment of the present inventor, it was confirmed that the foam scum 11 in the container 12 was defoamed and liquefied by applying an external impact to the container 12 in the example shown in FIG. Specifically, the foam scum, which initially had a volume of 100 L (liter), was reduced to 5 L by repeated three drops and became a liquid without foaming.

従って、本実施の形態によれば、水の浄化機能に関わるような大掛かりな設備の付加を要することなく、又、薬剤等を使用することなく、単に容器12に外部から物理的な力を加えるだけで簡単に発泡スカム11を液状化させてこれを処理することができる。具体的には、図5(a)に示すように、例えば容積100Lの容器12内に略同量の発泡スカム11を移し、図2〜図4に示す何れかの方法によって容器12に外部から物理的な力を加えると、図5(b)に示すように、容器12内の発泡スカム11が液状化してその容積が5L、つまり1/20にまで縮小した。   Therefore, according to the present embodiment, a physical force is simply applied to the container 12 from the outside without adding a large-scale facility related to the water purification function and without using a medicine or the like. Simply, the foamed scum 11 can be liquefied and treated. Specifically, as shown in FIG. 5A, for example, substantially the same amount of foamed scum 11 is transferred into a container 12 having a volume of 100 L, and the container 12 is externally applied by any of the methods shown in FIGS. When a physical force was applied, as shown in FIG. 5B, the foamed scum 11 in the container 12 was liquefied and its volume was reduced to 5 L, that is, 1/20.

このような装置は、水の浄化機能に関わる設備とは別個に設置することができ、又、設置場所も選ばず、使用しないときは撤去することもできる。勿論、水の浄化機能に影響を与えることもない。   Such a device can be installed separately from the equipment related to the water purification function, and can be removed when not in use, regardless of the installation location. Of course, the water purification function is not affected.

そして、本実施の形態では、図1に示すように、発泡スカム11を容器12内で液状化させるため、沈澱池6から排出される前記余剰汚泥と混合し、混合した汚泥を脱水機15で濃縮脱水することができる。従って、曝気槽1にて発生した発泡スカム11を最終的には余剰汚泥と共に脱水処理して固形物である脱水ケーキに変えることができ、この脱水ケーキを無害な産業廃棄物として処理することができる。又、加熱することで、脱水乾燥することもできる。   In the present embodiment, as shown in FIG. 1, in order to liquefy the foamed scum 11 in the container 12, the excess sludge discharged from the sedimentation basin 6 is mixed, and the mixed sludge is dehydrated by a dehydrator 15. It can be concentrated and dehydrated. Therefore, the foamed scum 11 generated in the aeration tank 1 can be finally dehydrated together with excess sludge to be converted into a dehydrated cake that is a solid, and this dehydrated cake can be treated as harmless industrial waste. it can. Moreover, dehydration drying can also be performed by heating.

本発明は、処理活性汚泥処理において放線菌の活動によって発生した発泡スカムの処理方法としての利用可能性が高い。   The present invention has high applicability as a method for treating foam scum generated by the activity of actinomycetes in the treatment activated sludge treatment.

本発明方法を実施するための活性汚泥処理設備の模式図である。It is a schematic diagram of the activated sludge processing equipment for enforcing the method of the present invention. 容器に外部から物理的な力を加える例として容器を落下させる方法を示す図である。It is a figure which shows the method of dropping a container as an example which applies a physical force to the container from the outside. (a),(b)は容器に外部から物理的な力を加える例として容器に振動を与える方法を示す図である。(A), (b) is a figure which shows the method of giving a vibration to a container as an example which applies a physical force to the container from the outside. 容器に外部から物理的な力を加える例として容器に打撃による衝撃を与える方法を示す図である。It is a figure which shows the method of giving the impact by impact to a container as an example which applies a physical force to the container from the outside. (a)は容器に物理的な力を加える前の容器内の状態を示す図、(b)は容器に物理的な力を加えた後の容器内の状態を示す図である。(A) is a figure which shows the state in the container before applying a physical force to a container, (b) is a figure which shows the state in a container after applying a physical force to a container.

符号の説明Explanation of symbols

1 曝気槽
2 流入管
3 散気管
4 コンプレッサ
5 移送管
6 沈澱池
7 排水管
8 分離汚泥排出管
9 返送管
10 汚泥フロック
11 発泡スカム
12 容器
13 偏心カム
14 振動子
15 脱水機
DESCRIPTION OF SYMBOLS 1 Aeration tank 2 Inflow pipe 3 Aeration pipe 4 Compressor 5 Transfer pipe 6 Settling pond 7 Drain pipe 8 Separation sludge discharge pipe 9 Return pipe 10 Sludge floc 11 Foam scum 12 Container 13 Eccentric cam 14 Vibrator 15 Dehydrator

Claims (5)

好気性微生物を用いて水中の不純物を浄化する活性汚泥処理において、放線菌の活動によって発生した発泡スカムを別の容器に移し、該容器に外部から物理的な力を加えることによって、容器内の発泡スカムを消泡させて液状化させることを特徴とする発泡スカムの処理方法。   In activated sludge treatment that purifies impurities in water using aerobic microorganisms, the foam scum generated by the activity of actinomycetes is transferred to another container, and physical force is applied to the container from the outside. A method for treating foamed scum, wherein the foamed scum is defoamed and liquefied. 前記容器を落下させてこれに外部から前記物理的な力を加えることを特徴とする請求項1記載の発泡スカムの処理方法。   The foam scum treatment method according to claim 1, wherein the container is dropped and the physical force is applied to the container from outside. 前記容器に振動を与えてこれに外部から前記物理的な力を加えることを特徴とする請求項1記載の発泡スカムの処理方法。   2. The foam scum treatment method according to claim 1, wherein the physical force is applied to the container by applying vibration to the container. 前記容器に打撃による衝撃を与えてこれに外部から前記物理的な力を加えることを特徴とする請求項1記載の発泡スカムの処理方法。   2. The foam scum treatment method according to claim 1, wherein the container is subjected to impact by striking and the physical force is applied to the container from the outside. 前記容器内で液状化した汚泥を、余剰汚泥として系外に排出する汚泥に混合し、混合した汚泥を脱水機で濃縮脱水し或は加熱することで脱水乾燥することを特徴とする請求項1〜4の何れかに記載の発泡スカムの処理方法。   The sludge liquefied in the container is mixed with sludge discharged out of the system as surplus sludge, and the mixed sludge is dehydrated and dried by concentrating and dehydrating with a dehydrator or heating. The processing method of the foaming scum in any one of -4.
JP2004039207A 2004-02-17 2004-02-17 Treating method for foaming scum Pending JP2005230588A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2013006155A (en) * 2011-06-24 2013-01-10 Mitsubishi Heavy Ind Ltd Defoaming device and method of used discharged seawater and discharge system of used discharged seawater

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2013006155A (en) * 2011-06-24 2013-01-10 Mitsubishi Heavy Ind Ltd Defoaming device and method of used discharged seawater and discharge system of used discharged seawater

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