JP4584958B2 - Sludge treatment equipment - Google Patents

Sludge treatment equipment Download PDF

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JP4584958B2
JP4584958B2 JP2007131060A JP2007131060A JP4584958B2 JP 4584958 B2 JP4584958 B2 JP 4584958B2 JP 2007131060 A JP2007131060 A JP 2007131060A JP 2007131060 A JP2007131060 A JP 2007131060A JP 4584958 B2 JP4584958 B2 JP 4584958B2
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sludge
ultrasonic
treatment
tank
sludge treatment
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JP2007203301A (en
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志津雄 三田
亮 張
正季 村岡
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Maezawa Industries Inc
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Description

本発明は、汚泥処理装置に関し、詳しくは、下水、産業排水、畜産排水等を処理する水処理施設で発生した汚泥に超音波によって処理する装置に関する。   The present invention relates to a sludge treatment apparatus, and more particularly, to an apparatus for treating sludge generated in a water treatment facility for treating sewage, industrial wastewater, livestock wastewater, and the like with ultrasonic waves.

一般に、下水、産業排水、畜産排水等の廃水の処理には生物処理が用いられており、生物学的なBOD成分の除去に伴って多量の余剰汚泥が排出されている。この汚泥は、砂分等の無機性懸濁物質と、主に微生物からなる有機性懸濁物質とで構成されており、近年、該汚泥中の微生物を物理的、化学的、生物的、あるいはこれらを組合わせた方法で破砕して廃水処理に返送する汚泥減量化や汚泥処理の高効率化が提案されている。   In general, biological treatment is used to treat wastewater such as sewage, industrial wastewater, and livestock wastewater, and a large amount of excess sludge is discharged with the removal of biological BOD components. This sludge is composed of inorganic suspended substances such as sand and organic suspended substances mainly composed of microorganisms. Recently, microorganisms in the sludge are physically, chemically, biologically or Proposals have been made to reduce sludge and to increase the efficiency of sludge treatment by crushing them using a combination of these methods and returning them to wastewater treatment.

汚泥中の微生物を破壊する物理的手段としては、汚泥に超音波を照射した際に発生するキャビテーションの効果によって微生物細胞を破壊する超音波処理法や、ミルと微生物との摩擦によって細胞を破壊するミル破砕法(例えば、特許文献1参照)が提案されている。また、化学的手段としては、オゾンや酸等の強力な酸化作用を利用して微生物の細胞を破壊するオゾン処理法(例えば、特許文献2参照)や薬品処理法が提案されている。さらに、生物的手段として、高温の好気性条件下で生育する特殊な微生物(好気性好熱細菌)が出す酵素により微生物細胞を溶解させて破壊する方法(例えば、特許文献3参照)が提案されている。
特開平11−156394号公報 特許第2973761号公報 特開平9−253699号公報
As physical means to destroy microorganisms in sludge, ultrasonic treatment method that destroys microbial cells by the effect of cavitation that occurs when ultrasonic waves are applied to sludge, and destruction of cells by friction between mill and microorganisms A mill crushing method (see, for example, Patent Document 1) has been proposed. As chemical means, an ozone treatment method (for example, refer to Patent Document 2) or a chemical treatment method that destroys microorganism cells using a strong oxidizing action such as ozone or acid has been proposed. Furthermore, as a biological means, a method is proposed in which microbial cells are lysed and destroyed by an enzyme produced by a special microorganism (aerobic thermophilic bacterium) that grows under high temperature aerobic conditions (for example, see Patent Document 3). ing.
JP-A-11-156394 Japanese Patent No. 2973761 JP-A-9-253699

これらの微生物細胞の破壊方法の中で、超音波処理は従来から様々な分野で利用されており、微生物細胞の破砕手段として早くから注目されていたにもかかわらず、汚泥に対する実用例はほとんど報告されていない。この理由の一つに、汚泥中に含まれる砂分等の無機性懸濁物質との接触によって汚泥中に設置した超音波振動子の摩耗が激しく、超音波振動子の寿命が短くなって交換を頻繁に行わなければならないため、ランニングコストが増大するという問題が挙げられる。   Among these microbial cell destruction methods, sonication has been used in various fields, and there have been few reports on practical examples of sludge, although it has been attracting attention as a means of disrupting microbial cells. Not. One reason for this is that the ultrasonic vibrator installed in the sludge is heavily worn by contact with inorganic suspended solids such as sand contained in the sludge, and the life of the ultrasonic vibrator is shortened and replaced. Therefore, there is a problem that the running cost increases.

そこで本発明は、水処理過程で発生する初沈汚泥や余剰汚泥に超音波処理を施す際の超音波振動子と無機性懸濁物質との接触を回避することによって超音波振動子の長寿命化を図れるとともに、汚泥中の有機性懸濁物質に超音波を効率よく照射することができる汚泥処理装置を提供することを目的としている。   Therefore, the present invention provides a long service life of the ultrasonic vibrator by avoiding contact between the ultrasonic vibrator and the inorganic suspended solid when the first settling sludge and surplus sludge generated in the water treatment process is subjected to ultrasonic treatment. An object of the present invention is to provide a sludge treatment apparatus capable of efficiently radiating ultrasonic waves to organic suspended solids in sludge.

上記目的を達成するため、本発明は、水処理工程で発生した汚泥に超音波を照射する汚泥処理装置において、下部に汚泥流入口を、上部に汚泥流出口を有する筒状の超音波処理槽を傾斜させて設置し、該超音波処理槽の傾斜方向上部側の部位に超音波振動子を配置したことを特徴としている。また、前記超音波処理槽を直列に複数段設置することも可能である。 To achieve the above object, the present invention provides a cylindrical ultrasonic treatment tank having a sludge inlet at the bottom and a sludge outlet at the top in a sludge treatment apparatus that irradiates the sludge generated in the water treatment process with ultrasonic waves. And an ultrasonic transducer is disposed at a portion on the upper side in the inclination direction of the ultrasonic treatment tank . It is also possible to install a plurality of the ultrasonic treatment tanks in series.

本発明によれば、汚泥の超音波処理を施す際に、汚泥中の砂分等の無機性懸濁物質が超音波振動子と接触することを回避できるので、超音波振動子の摩耗を低減して長寿命化を図れるとともに、超音波処理の対象となる汚泥中の有機性懸濁物質に対する超音波照射効率を向上させることができる。   According to the present invention, when ultrasonic treatment of sludge is performed, it is possible to avoid contact with the ultrasonic vibrator by inorganic suspended substances such as sand in the sludge, thereby reducing wear of the ultrasonic vibrator. Thus, it is possible to extend the life and improve the efficiency of ultrasonic irradiation with respect to the organic suspended substance in the sludge to be subjected to ultrasonic treatment.

図1は、本発明の汚泥処理装置の一形態例を示す系統図である。この汚泥処理装置31は、下部に汚泥流入口12を、上部に汚泥流出口13を有する筒状の超音波処理槽32において、該超音波処理槽32の一側方に偏倚させた状態で超音波振動子33を配置するとともに、該超音波振動子33の配置部位が上部側に位置するように前記超音波処理槽32を傾斜させて設置したものである。   FIG. 1 is a system diagram showing an embodiment of the sludge treatment apparatus of the present invention. The sludge treatment apparatus 31 is a cylindrical ultrasonic treatment tank 32 having a sludge inlet 12 in the lower part and a sludge outlet 13 in the upper part. The ultrasonic transducer 33 is arranged, and the ultrasonic treatment tank 32 is inclined and installed so that the arrangement site of the ultrasonic transducer 33 is located on the upper side.

このように、適当な角度に傾斜させた超音波処理槽32内の流路に適当な流速で汚泥を導入することにより、有機性懸濁物質に比べて比重の大きな無機性懸濁物質が傾斜方向下部側壁面に沿って流れる状態になるので、傾斜方向上部側に配置した超音波振動子33と無機性懸濁物質とが接触することが回避され、超音波振動子33の摩耗を低減して長寿命化を図ることができる。さらに、前記同様に、超音波振動子33の周辺における有機性懸濁物質の濃度上昇によって超音波照射効率も向上する。加えて、超音波処理槽32の傾斜角度と汚泥の流速とを適切に設定することにより、無機性懸濁物質を槽底部に沈殿させて槽外に抜き取ることができる。   In this way, by introducing sludge at an appropriate flow rate into the flow path in the ultrasonic treatment tank 32 inclined at an appropriate angle, the inorganic suspended material having a larger specific gravity than the organic suspended material is inclined. Since it flows along the lower side wall surface in the direction, it is possible to avoid contact between the ultrasonic vibrator 33 arranged on the upper side in the inclined direction and the inorganic suspended substance, and to reduce wear of the ultrasonic vibrator 33. To extend the service life. Further, similarly to the above, the ultrasonic irradiation efficiency is improved by increasing the concentration of the organic suspended substance around the ultrasonic vibrator 33. In addition, by appropriately setting the inclination angle of the ultrasonic treatment tank 32 and the flow rate of the sludge, the inorganic suspended solids can be precipitated at the bottom of the tank and extracted out of the tank.

なお、超音波処理槽32の径や傾斜角度は、流速等の処理条件や処理対象となる汚泥の性状等の条件に応じて設定されるものであり、例えば傾斜角度は、軸線を略水平な方向に向けることもできるが、通常は、10〜80度、好ましくは30〜60度の範囲が適当である。このとき、軸線の水平面に対する傾斜角度が80度を超えると、無機性懸濁物質と有機性懸濁物質との分離が困難となり、10度未満にすると無機性懸濁物質を槽底部に沈殿させることが困難となる。   The diameter and inclination angle of the ultrasonic treatment tank 32 are set according to processing conditions such as flow velocity and conditions such as the properties of sludge to be processed. For example, the inclination angle is substantially horizontal with respect to the axis. Although it can be directed in the direction, it is usually in the range of 10 to 80 degrees, preferably 30 to 60 degrees. At this time, if the angle of inclination of the axis with respect to the horizontal plane exceeds 80 degrees, separation of the inorganic suspended substance and the organic suspended substance becomes difficult, and if it is less than 10 degrees, the inorganic suspended substance is precipitated at the bottom of the tank. It becomes difficult.

また、超音波処理槽32の長さ方向の途中で傾斜角度を変えることも可能であり、超音波処理槽32内における超音波振動子33の位置は、傾斜方向上部側壁面に沿わせる必要はなく、軸線に近い位置であってもよい。さらに、超音波処理槽32の前段に、汚泥中に含まれている無機性懸濁物質を沈殿させて汚泥中から排除するための沈砂設備を設けてもよい。この沈砂設備は、汚泥の性状や処理量に応じて適当な構造のものを使用することができ、通常の水処理設備で用いられている設備を使用することが可能である。   It is also possible to change the inclination angle in the middle of the length direction of the ultrasonic treatment tank 32, and the position of the ultrasonic transducer 33 in the ultrasonic treatment tank 32 needs to be along the upper side wall surface in the inclination direction. There may be a position close to the axis. Furthermore, a sand settling facility for precipitating the inorganic suspended matter contained in the sludge and removing it from the sludge may be provided in the previous stage of the ultrasonic treatment tank 32. As the sand settling equipment, one having an appropriate structure can be used according to the properties and treatment amount of sludge, and equipment used in ordinary water treatment equipment can be used.

また、本発明の汚泥処理装置における超音波処理の条件は、従来から行われている超音波処理と同様に設定することができる。例えば、被超音波処理を施す汚泥の濃度(MLSS)は、通常、20000mg/L以下、好ましくは15000mg/L以下、特に10000mg/L以下が適当である。この汚泥濃度が高すぎると超音波が汚泥全体に伝わらず、所望の処理結果が得られないだけでなく、超音波振動子近辺の汚泥のみが強い超音波を受けて汚泥内の微生物が破壊され、微生物体内の難分解性CODが液相に移行して排水処理工程に悪影響を及ぼすことがあるので好ましくない。   Moreover, the conditions of the ultrasonic treatment in the sludge treatment apparatus of the present invention can be set in the same manner as in the conventional ultrasonic treatment. For example, the concentration (MLSS) of the sludge to be subjected to ultrasonic treatment is usually 20000 mg / L or less, preferably 15000 mg / L or less, particularly 10,000 mg / L or less. If the sludge concentration is too high, the ultrasonic wave will not be transmitted to the entire sludge and the desired treatment result will not be obtained. The refractory COD in the microorganisms is not preferable because it may shift to the liquid phase and adversely affect the wastewater treatment process.

超音波振動子における超音波の周波数は、15〜50kHz、好ましくは15〜40kHz、特に20〜30kHzが適当である。この周波数が低すぎると十分な処理効果が得られず、高すぎると汚泥中の微生物が破壊されてしまうので好ましくない。   The frequency of the ultrasonic wave in the ultrasonic vibrator is 15 to 50 kHz, preferably 15 to 40 kHz, particularly 20 to 30 kHz. If this frequency is too low, a sufficient treatment effect cannot be obtained, and if it is too high, microorganisms in the sludge are destroyed, which is not preferable.

また、超音波の強度は、照射対象となる汚泥の量や濃度に応じて適当に設定されるものであるが、一般的には、5〜100kWs/L、好ましくは10〜80kWs/L、特に20〜60kWs/Lが適当である。この超音波強度が小さすぎると、十分な効果が得られないことがあり、あまり高くしても、強度に比例した効果が得られるものではない。   The intensity of the ultrasonic wave is appropriately set according to the amount and concentration of sludge to be irradiated, but is generally 5 to 100 kWs / L, preferably 10 to 80 kWs / L, particularly 20-60 kWs / L is suitable. If the ultrasonic intensity is too small, a sufficient effect may not be obtained, and even if it is too high, an effect proportional to the intensity cannot be obtained.

これらの各条件、すなわち、汚泥濃度、超音波周波数、超音波強度、超音波照射汚泥量は、各々が各条件の要素となっており、処理にかかるコスト、処理時間等を考慮し、効率の良い条件に適宜変更することができる。また、図1に示したように、比較的小型の超音波処理槽を直列に複数段設置することによって超音波照射効率を向上させることができる。   Each of these conditions, i.e., sludge concentration, ultrasonic frequency, ultrasonic intensity, and ultrasonic irradiation sludge amount, is an element of each condition. It can be appropriately changed to good conditions. Moreover, as shown in FIG. 1, the ultrasonic irradiation efficiency can be improved by installing a plurality of stages of relatively small ultrasonic treatment tanks in series.

本発明の汚泥処理装置の一形態例を示す系統図である。It is a systematic diagram which shows one example of a sludge processing apparatus of this invention.

符号の説明Explanation of symbols

12…汚泥流入口、13…汚泥流出口、31…汚泥処理装置、32…超音波処理槽、33…超音波振動子   12 ... Sludge inlet, 13 ... Sludge outlet, 31 ... Sludge treatment device, 32 ... Ultrasonic treatment tank, 33 ... Ultrasonic vibrator

Claims (2)

水処理工程で発生した汚泥に超音波を照射する汚泥処理装置において、下部に汚泥流入口を、上部に汚泥流出口を有する筒状の超音波処理槽を傾斜させて設置し、該超音波処理槽の傾斜方向上部側の部位に超音波振動子を配置したことを特徴とする汚泥処理装置。 In the sludge treatment equipment that irradiates the sludge generated in the water treatment process with ultrasonic waves , the sludge inflow port is installed at the bottom and the cylindrical sonication tank with the sludge outflow port at the top is inclined, and the ultrasonic treatment is performed. A sludge treatment apparatus characterized in that an ultrasonic vibrator is disposed at a portion on the upper side in the inclination direction of the tank . 前記超音波処理槽を直列に複数段設置したことを特徴とする請求項1記載の汚泥処理装置。 The sludge treatment apparatus according to claim 1, wherein the ultrasonic treatment tank is installed in a plurality of stages in series.
JP2007131060A 2007-05-16 2007-05-16 Sludge treatment equipment Expired - Fee Related JP4584958B2 (en)

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Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6039867A (en) * 1996-05-23 2000-03-21 Telesonic Ag Device for continuous disintegration of activated sludge
JP2001259663A (en) * 2000-03-15 2001-09-25 Sekisui Chem Co Ltd Organic waste water treating method

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6039867A (en) * 1996-05-23 2000-03-21 Telesonic Ag Device for continuous disintegration of activated sludge
JP2001259663A (en) * 2000-03-15 2001-09-25 Sekisui Chem Co Ltd Organic waste water treating method

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