JP2005185902A - Method and equipment for treating sludge - Google Patents

Method and equipment for treating sludge Download PDF

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JP2005185902A
JP2005185902A JP2003428134A JP2003428134A JP2005185902A JP 2005185902 A JP2005185902 A JP 2005185902A JP 2003428134 A JP2003428134 A JP 2003428134A JP 2003428134 A JP2003428134 A JP 2003428134A JP 2005185902 A JP2005185902 A JP 2005185902A
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sludge
concentration
drying
concentrated
concentrating
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Takeo Oshima
武雄 大島
Mikimasa Yamaguchi
幹昌 山口
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Fuji Electric Co Ltd
Tsukishima Kikai Co Ltd
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Fuji Electric Systems Co Ltd
Tsukishima Kikai Co Ltd
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for treating sludge which is suitable for the treatment of the sludge produced particularly in a small scaled water treatment plant and by which the treatment efficiency is improved, and equipment for treating the sludge which promotes cost saving and space saving. <P>SOLUTION: The method for treating the sludge is provided with a concentration process for concentrating the sludge M by a concentration means 2 and a drying process for supplying the concentrated sludge N concentrated in the concentration process with a water content nearly as it is to a drying means 4 and drying. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

本発明は、特に浄水場において発生する上水汚泥のような汚泥を処理するのに好適な汚泥の処理方法および処理設備に関するものである。   TECHNICAL FIELD The present invention relates to a sludge treatment method and treatment equipment suitable for treating sludge such as clean water sludge generated particularly at a water purification plant.

この種の汚泥の処理においては、汚泥を濃縮手段によって濃縮する濃縮工程と、この濃縮工程で濃縮させられた濃縮汚泥を脱水手段によって脱水する脱水工程と、この脱水工程で濃縮汚泥を脱水した脱水汚泥をさらに乾燥手段によって乾燥する乾燥工程とにより、汚泥の含水率を順次低減させるとともにその減量化を図るようにしている。ここで、特許文献1には、浄水場における上水道の浄化工程で発生する上水汚泥の処理において、濃縮手段としては加圧浮上濃縮槽を用いることが、また脱水手段としては例えばフィルタープレスを用いることが記載されている。
特開平6−182348号公報
In this type of sludge treatment, a concentration step for concentrating sludge by a concentration means, a dehydration step for dewatering the concentrated sludge concentrated in this concentration step by a dehydration means, and a dehydration step for dewatering the concentrated sludge in this dewatering step. In addition, the moisture content of the sludge is sequentially reduced and reduced by a drying process in which the sludge is further dried by a drying means. Here, in Patent Document 1, in the treatment of water sludge generated in the purification process of waterworks at a water purification plant, a pressure levitation concentration tank is used as a concentration means, and a filter press is used as a dehydration means, for example. It is described.
JP-A-6-182348

ところが、このような浄水場において発生する上水汚泥の量は、例えば下水処理場で発生する下水汚泥の量などに比べると少なく、特に小規模な浄水場においては僅かでしかない。しかしながら、そのような僅かな上水汚泥を処理するためにも、従来は濃縮、脱水、乾燥の3工程で処理を行わなければならず、各工程に対してそれぞれ濃縮手段、脱水手段、および乾燥手段が必要とされて設備が増えるため、小規模な浄水場でも省コスト、省スペース化が困難であった。また、特に上記脱水工程における脱水手段として特許文献1記載のようなフィルタープレスを用いた場合には、この脱水工程における処理が回分式(バッチ式)とならざるを得ず、しかもこのようなフィルタープレスによる脱水には長時間を要することもあるので、汚泥の処理効率を向上させるにも自ずと限度があった。   However, the amount of water sewage sludge generated in such a water purification plant is small compared to, for example, the amount of sewage sludge generated in a sewage treatment plant, and is particularly small in a small water purification plant. However, in order to treat such a small amount of water sludge, conventionally, the treatment must be performed in three steps of concentration, dehydration, and drying. Concentration means, dehydration means, and drying are performed for each step. Since measures are required and facilities increase, it is difficult to save cost and space even in small water treatment plants. In particular, when a filter press as described in Patent Document 1 is used as a dehydrating means in the dehydration step, the treatment in the dehydration step must be a batch type (batch type), and such a filter Since dehydration by the press may take a long time, there was a limit to improving the sludge treatment efficiency.

本発明は、このような背景の下になされたもので、特に小規模の浄水場において発生する汚泥の処理に用いて好適で、処理効率の向上を図ることが可能な汚泥の処理方法、および設備の省コスト、省スペース化を促すことが可能な汚泥の処理設備を提供することを目的としている。   The present invention has been made under such a background, and is particularly suitable for use in the treatment of sludge generated in a small-scale water purification plant, and is capable of improving the treatment efficiency, and The object is to provide a sludge treatment facility that can promote cost saving and space saving of the facility.

上記課題を解決して、このような目的を達成するために、本発明の汚泥の処理方法は、汚泥を濃縮手段によって濃縮する濃縮工程と、この濃縮工程で濃縮させられた濃縮汚泥を略そのままの含水率で乾燥手段に供給して乾燥する乾燥工程とを備えてなることを特徴とする。また、本発明の汚泥の処理設備は、汚泥を濃縮する濃縮手段と、この濃縮手段によって濃縮させられた濃縮汚泥が略そのままの含水率で供給されて該濃縮汚泥を乾燥する乾燥手段とを備えてなることを特徴とする。   In order to solve the above problems and achieve such an object, the sludge treatment method of the present invention comprises a concentration step of concentrating sludge by a concentration means, and the concentrated sludge concentrated in this concentration step as it is. And a drying step of supplying to the drying means at a moisture content of and drying. Further, the sludge treatment facility of the present invention comprises a concentration means for concentrating the sludge, and a drying means for drying the concentrated sludge by supplying the concentrated sludge concentrated by the concentration means at a substantially moisture content. It is characterized by.

従って、このように構成された汚泥の処理方法および処理設備では、濃縮工程において濃縮手段により所定の含水率にまで濃縮された汚泥が、間にフィルタープレス等の脱水手段による脱水工程を介することなく、濃縮された略そのままの含水率で乾燥工程の乾燥手段に供給されて乾燥させられるので、特に小規模な浄水場において発生する僅かな量の上水汚泥を処理するのに適用して効果的であり、脱水工程による処理を要することなく省略して連続的かつ効率的な汚泥の処理を促すことができる。また、フィルタープレス等の脱水手段も不要となるので、これを省略して処理設備の省コスト、省スペース化を図ることができる。   Therefore, in the sludge treatment method and treatment equipment configured as described above, the sludge concentrated to a predetermined moisture content by the concentration means in the concentration step does not pass through the dehydration step by the dehydration means such as a filter press. Since it is supplied to the drying means in the drying process at a concentrated almost intact moisture content, it is effectively applied to treat a small amount of water sludge generated in a small-scale water purification plant. Therefore, it is possible to promote continuous and efficient sludge treatment by omitting the treatment by the dehydration process. Further, since no dehydrating means such as a filter press is required, the cost can be saved and the space can be saved by omitting this.

ここで、上記濃縮手段としては、上記汚泥を濾過することによって濃縮する手段であるのが望ましい。また濃縮工程において濃縮手段により濃縮された濃縮汚泥を連続的に乾燥工程の乾燥手段に供給して円滑な乾燥処理を図るには、上記汚泥の処理方法においては、上記濃縮工程と上記乾燥工程との間で、上記濃縮汚泥を略そのままの含水率で一時貯留することが望ましく、また上記処理設備においては、上記濃縮手段と上記乾燥手段との間に、上記濃縮汚泥を略そのままの含水率で一時貯留する一時貯留槽を備えるのが望ましい。すなわち、こうして濃縮汚泥を一時貯留しておくことにより、例えば濃縮工程で処理される汚泥量に変動が生じても乾燥工程には一定量の汚泥を供給することができ、連続処理を維持して安定した乾燥汚泥の生成を図ることができる。   Here, the concentration means is preferably a means for concentration by filtering the sludge. In addition, in order to smoothly supply the concentrated sludge concentrated by the concentration means in the concentration step to the drying means in the drying step, the sludge treatment method includes the concentration step, the drying step, and the like. It is desirable to temporarily store the concentrated sludge at a substantially unchanged moisture content, and in the treatment facility, the concentrated sludge is kept at a substantially unchanged moisture content between the concentration means and the drying means. It is desirable to provide a temporary storage tank for temporary storage. That is, by temporarily storing concentrated sludge in this way, for example, even if fluctuations occur in the amount of sludge processed in the concentration step, a constant amount of sludge can be supplied to the drying step, and continuous processing is maintained. Stable dry sludge can be generated.

また、上記濃縮手段としては、乾燥工程における処理効率を考慮すると、より濃縮効率の高いものを用いるのが望ましく、例えば濃縮槽内に配設された濾過手段に一端が接続されるとともに他端は濃縮槽外の上記濾過手段よりも低い位置に開口した濾液排出管を備え、上記濃縮槽に供給された汚泥を上記濾過手段によって濾過して、その濾液を上記濾液排出管を介して自然流下により排出するとともに上記濾過手段表面に上記濃縮汚泥を生成するサイフォン式濾過濃縮装置を用いるのが望ましい。そして、このように濃縮手段としてサイフォン式濃縮装置を用いた場合には、この濃縮手段の上記濃縮槽を、上記乾燥手段の上方に配置することにより、上記濾過手段に接続される上記濾液排出管の一端と濾過槽外に開口する他端との高さの差を大きく確保することができ、すなわちそのサイフォン力を確実に確保して、より効率的な汚泥の濃縮を図ることにより濃縮汚泥の含水率を低減して、かかる濃縮汚泥を乾燥工程に直接的に供給しても確実な乾燥汚泥を得ることが可能となり、一層効率的な処理を促すことが可能となる。   Further, as the concentration means, it is desirable to use a higher concentration efficiency in consideration of the processing efficiency in the drying process. For example, one end is connected to the filtration means disposed in the concentration tank, and the other end is A filtrate discharge pipe opened at a position lower than the filtration means outside the concentration tank is provided, the sludge supplied to the concentration tank is filtered by the filtration means, and the filtrate is naturally flowed through the filtrate discharge pipe. It is desirable to use a siphon type filtration concentration apparatus that discharges and produces the concentrated sludge on the surface of the filtration means. And when a siphon type concentrating device is used as the concentrating means in this way, the filtrate discharge pipe connected to the filtering means by disposing the concentrating tank of the concentrating means above the drying means. The difference in height between one end of the filter and the other end that opens outside the filtration tank can be ensured, that is, the siphon force can be reliably ensured to concentrate the sludge more efficiently. Even if the moisture content is reduced and the concentrated sludge is directly supplied to the drying step, it is possible to obtain a reliable dry sludge, and it is possible to promote more efficient treatment.

図1および図2は、本発明の汚泥の処理設備の一実施形態を示すものであり、以下この処理設備について説明しながら該処理設備を用いた本発明の汚泥の処理方法の一実施形態についても説明する。本実施形態の処理設備は、上述したような比較的小規模の浄水場において、例えば上水の膜濾過処理設備から排出される洗浄排水の汚泥等の上水汚泥を処理するものであって、この洗浄排水Wが保持される排水槽1と、濃縮手段としてのサイフォン式濃縮装置2、一時貯留槽3、および本実施形態における乾燥手段としての撹拌羽根内蔵型間接加熱乾燥機4によって概略構成されている。そして、これらサイフォン式濃縮装置2、一時貯留槽3、および撹拌羽根内蔵型間接加熱乾燥機4は、図1に示すとおりこの順に上から下に向けて上下方向に配設されており、すなわち濃縮手段としてのサイフォン式濃縮装置2が乾燥手段としての撹拌羽根内蔵型間接加熱乾燥機4の上方に配設されている。   1 and 2 show an embodiment of the sludge treatment facility of the present invention. While describing the treatment facility, one embodiment of the sludge treatment method of the present invention using the treatment facility will be described below. Also explained. The treatment facility of the present embodiment treats the sewage sludge such as the sludge of the washing drainage discharged from the membrane filtration treatment facility of the water in the relatively small water purification plant as described above, The drainage tank 1 in which the washing waste water W is held, a siphon type concentrating device 2 as a concentration means, a temporary storage tank 3, and a stirring blade built-in type indirect heating dryer 4 as a drying means in the present embodiment. ing. The siphon type concentrating device 2, the temporary storage tank 3, and the stirring blade built-in type indirect heating dryer 4 are arranged in this order from top to bottom as shown in FIG. A siphon-type concentrating device 2 as a means is disposed above a stirring blade built-in type indirect heating dryer 4 as a drying means.

このうち、まず排水槽1には、上述のような膜濾過処理設備において上水を濾過する中空糸膜等よりなる膜モジュールを洗浄した後の洗浄排水Wが保持され、この排水槽1の底部に沈降した汚泥Mはポンプ11によって上記サイフォン式濃縮装置2に供給されるとともに、比較的清澄な上澄水Cは例えば紫外線によってクリプト類が殺菌された後に上記膜濾過処理設備に戻されたりする。ここで、この排水槽1からサイフォン式濃縮装置(濃縮手段)2に供給される汚泥の含水率は98〜99wt%程度である。   Among these, first, the drainage tank 1 holds the cleaning wastewater W after washing the membrane module made of a hollow fiber membrane or the like for filtering the clean water in the membrane filtration processing equipment as described above. The sludge M that has settled on is supplied to the siphon type concentrator 2 by the pump 11, and the relatively clear supernatant water C is returned to the membrane filtration equipment after the crypts are sterilized by, for example, ultraviolet rays. Here, the moisture content of the sludge supplied from the drainage tank 1 to the siphon type concentrator (concentration means) 2 is about 98 to 99 wt%.

このサイフォン式濃縮装置2は、底部に排出口21Aが設けられた濃縮槽21内に濾過手段22が配設されるとともに、この濾過手段22には濾液排出管23の一端が接続されたものであり、この濾液排出管23の他端は濃縮槽21外に取り回されて上記濾過手段22よりも下方に延びた後に2方に分岐させられ、その一方はバルブ23Aを介して濾液槽24に開口させられるとともに、他方はバルブ23Bを介して真空ポンプ25に接続されている。なお、真空ポンプ25の吐出側は濾液槽24にも接続可能とされている。   The siphon type concentrating device 2 has a filtering means 22 disposed in a concentrating tank 21 provided with a discharge port 21A at the bottom, and one end of a filtrate discharge pipe 23 is connected to the filtering means 22. Yes, the other end of the filtrate discharge pipe 23 is routed outside the concentration tank 21 and extends downward from the filtration means 22, and then is branched into two directions. One of the filtrate discharge pipes 23 is fed to the filtrate tank 24 via a valve 23A. While being opened, the other is connected to the vacuum pump 25 via a valve 23B. The discharge side of the vacuum pump 25 can be connected to the filtrate tank 24 as well.

また、上記濃縮槽21はその底部側が逆三角形状とされた断面ホームベース型とされ、上記排出口21Aにはバルブ21Bが備えられていて、このバルブ21Bは図1に示すように上記一時貯留槽3と図2(ロ)に示すように未濃縮汚泥排出槽21Cとに切換可能に接続されている。さらに、上記濾過手段22は、例えば濾過板22Aの外側に濾布22Bが張り渡されるとともに、この濾布22Bの内側に上記一端が開口するように濾液排出管23が上記濾過板22Aに接続されたものとされており、このような濾過板22Aが上記底部との間に間隔をあけて吊り下げられるように濃縮槽21内に複数設けられた構成とされている。   The concentrating tank 21 has a cross-sectional home base type whose bottom side is an inverted triangle, and the discharge port 21A is provided with a valve 21B. The valve 21B is provided with the temporary storage as shown in FIG. As shown in FIG. 2 (b), the tank 3 is connected to the unconcentrated sludge discharge tank 21C in a switchable manner. Further, in the filtering means 22, for example, a filter cloth 22B is stretched outside the filter plate 22A, and a filtrate discharge pipe 23 is connected to the filter plate 22A so that the one end is opened inside the filter cloth 22B. A plurality of such filter plates 22 </ b> A are provided in the concentration tank 21 so as to be suspended from the bottom portion.

このようなサイフォン式濃縮装置(濃縮手段)2による汚泥Mの濃縮工程について、図1により説明すると、まずバルブ21Bを閉じた状態で濃縮槽21内に汚泥Mを給泥して充填し、次いでバルブ23Aを閉じるとともにバルブ23Bを開いて真空ポンプ25により濾液排出管23から吸引を行う。すると、濃縮槽21内の汚泥Mが濾過手段22の濾布22Bによって濾過されて、その濾液Lが濾液排出管23を通り濃縮槽21外に導かれて濾過手段22よりも下方に抜き出されるので、その後はバルブ23Bを閉じるとともにバルブ23Aを開いて濾液排出管23の他端を開放すると、真空ポンプ25を駆動せずとも濾液Lは図2(イ)に示すようにサイフォンの原理によって濾液排出管23を連続的に自然流下して濾液槽24に排出される一方、濾過手段22の濾布22B表面には、汚泥M中の固形分が濾し残されて濃縮し濃縮汚泥Nが生成される。   The concentration process of sludge M by the siphon type concentrator (concentration means) 2 will be described with reference to FIG. 1. First, the sludge M is supplied and filled in the concentration tank 21 with the valve 21B closed, and then. The valve 23A is closed and the valve 23B is opened, and suction is performed from the filtrate discharge pipe 23 by the vacuum pump 25. Then, the sludge M in the concentrating tank 21 is filtered by the filter cloth 22B of the filtering means 22, and the filtrate L is led out of the concentrating tank 21 through the filtrate discharge pipe 23 and extracted below the filtering means 22. Therefore, when the valve 23B is closed and the valve 23A is opened to open the other end of the filtrate discharge pipe 23, the filtrate L is filtered by the siphon principle as shown in FIG. 2 (a) without driving the vacuum pump 25. While the discharge pipe 23 continuously flows down naturally and is discharged to the filtrate tank 24, the solid content in the sludge M is left on the surface of the filter cloth 22B of the filtration means 22 and concentrated to produce concentrated sludge N. The

こうして濃縮汚泥Nが生成されたなら、図2(ロ)に示すようにバルブ21Bを開いて排出口21Aを未濃縮汚泥排出槽21Cに接続し、濃縮槽21内に残された未濃縮汚泥Pを排出する。次いで、排出口21Aの接続を一時貯留槽3側に切り換え、真空ポンプ25の吐出側を濾液槽24に接続することにより、図2(ハ)に示すように濾液排出管23には、濾液槽24に開口した他端から濾過手段22の接続された一端に向けて、真空ポンプ25から吐出した圧縮空気Aが供給されることとなって、濾布22B表面に生成した上記濃縮汚泥Nが、この圧縮空気Aにより濾布22Bから剥離して濃縮槽21底部に落下し、排出口21Aから一時貯留槽3に供給される。ここで、この濃縮手段によって汚泥Mを濃縮した濃縮汚泥Nの含水率は90〜85wt%程度とされる。   When the concentrated sludge N is generated in this way, as shown in FIG. 2 (b), the valve 21B is opened, the discharge port 21A is connected to the unconcentrated sludge discharge tank 21C, and the unconcentrated sludge P left in the concentration tank 21 is obtained. Is discharged. Next, the connection of the discharge port 21A is switched to the temporary storage tank 3 side, and the discharge side of the vacuum pump 25 is connected to the filtrate tank 24, so that the filtrate discharge pipe 23 has a filtrate tank as shown in FIG. The compressed air A discharged from the vacuum pump 25 is supplied from the other end opened to 24 toward one end to which the filtration means 22 is connected, and the concentrated sludge N generated on the surface of the filter cloth 22B is The compressed air A peels off the filter cloth 22B, falls to the bottom of the concentration tank 21, and is supplied to the temporary storage tank 3 from the discharge port 21A. Here, the water content of the concentrated sludge N obtained by concentrating the sludge M by this concentrating means is about 90 to 85 wt%.

上記一時貯留槽3は、その底部が先細りとなったタンク状とされ、この底部の下端に設けられた排出口31がダンパ32等を介して上記撹拌羽根内蔵型間接加熱乾燥機(乾燥手段)4と液密かつ気密に接続されている。この一時貯留槽3に供給された濃縮汚泥Nは、単に一時貯留されるだけであってその含水率は変化することがなく、ダンパ32を開閉することにより排出口31から所定量ずつ撹拌羽根内蔵型間接加熱乾燥機4に供給される。   The temporary storage tank 3 is formed in a tank shape having a tapered bottom, and a discharge port 31 provided at the lower end of the bottom is provided with a stirring blade built-in type indirect heating dryer (drying means) via a damper 32 or the like. 4 is liquid-tight and air-tightly connected. The concentrated sludge N supplied to the temporary storage tank 3 is merely temporarily stored and its moisture content does not change. By opening and closing the damper 32, a predetermined amount of stirring blades are built in from the discharge port 31. It is supplied to the mold indirect heating dryer 4.

一方、この撹拌羽根内蔵型間接加熱乾燥機4は、上下が閉塞されるとともに下側の周面が下方に向かうに従い漸次縮径する円錐台状の本体41を備えた真空容器とされ、この本体41内部はバルブ41Aを介して上記真空ポンプ25と接続されることにより真空状態に減圧可能とされている。また、この本体41の上部を閉塞する天板部41Bには、その中央からやや離れた位置に供給口42が設けられて、上記ダンパ32を介して本体41内の真空状態を維持したまま一時貯留槽3の排出口31と接続可能とされるとともに、本体41の下端部には排出口43が設けられていて、この排出口43は、やはり本体41内の真空状態を維持可能なダンパ44を介して、コンテナ等の回収手段45に開口させられている。   On the other hand, the indirect heating dryer 4 with a built-in stirring blade is a vacuum vessel including a truncated cone-shaped main body 41 whose upper and lower sides are closed and whose lower peripheral surface gradually decreases in diameter as it goes downward. 41 is connected to the vacuum pump 25 via a valve 41A so that the pressure can be reduced to a vacuum state. In addition, the top plate portion 41B that closes the upper portion of the main body 41 is provided with a supply port 42 at a position slightly away from the center thereof, and temporarily maintains the vacuum state in the main body 41 via the damper 32. A discharge port 43 can be connected to the discharge port 31 of the storage tank 3, and a discharge port 43 is provided at the lower end portion of the main body 41. The discharge port 43 is also a damper 44 that can maintain the vacuum state in the main body 41. And is opened to a collection means 45 such as a container.

さらに、上記天板部41Bの中央には、モータ等の回転駆動装置46が設けられ、その回転軸46Aに沿って撹拌羽根47が取り付けられている。この撹拌羽根47は、回転駆動装置46によって回転可能に取り付けられている。さらにまた、この本体41の周面部はジャケット構造41Cとされていて、該ジャケット構造41C内には図示されない蒸気発生手段から蒸気Sが供給可能、または油を媒体とし電気ヒータで加熱する構成とされている。   Further, a rotation driving device 46 such as a motor is provided at the center of the top plate portion 41B, and a stirring blade 47 is attached along the rotation shaft 46A. The stirring blade 47 is rotatably attached by a rotation drive device 46. Furthermore, the peripheral surface portion of the main body 41 has a jacket structure 41C, and steam S can be supplied from a steam generating means (not shown) into the jacket structure 41C, or heated by an electric heater using oil as a medium. ing.

このような撹拌羽根内蔵型間接加熱乾燥機4による乾燥工程においては、本実施形態では上記真空ポンプ25によって本体41内が真空状態とされた上で、上記ダンパ32を介してこの真空状態を維持したまま、一時貯留槽3から濃縮汚泥Nが本体41内に供給される。そして、こうして供給された濃縮汚泥Nは、上記回転駆動装置46によって本体41の中心軸回りに撹拌羽根47により撹拌・混合されつつ、上記ジャケット構造41C内に供給される蒸気Sまたは電気ヒータで加熱された媒体によりこの本体41内周面から間接的に加熱され、乾燥されて造粒させられる。さらに、こうして乾燥・造粒された乾燥汚泥Dは、ダンパ44によって本体41内の真空状態を維持したまま排出口43から排出されて上記コンテナ等の回収手段45によって回収され、クリプト類が殺菌されて例えば造粒乾燥土などとして有効利用される。なお、このようにして乾燥工程を経た上記乾燥汚泥Dの含水率は、40wt%程度とされる。   In such a drying process by the stirring blade built-in type indirect heating dryer 4, in this embodiment, the inside of the main body 41 is evacuated by the vacuum pump 25 and the vacuum state is maintained via the damper 32. As it is, the concentrated sludge N is supplied from the temporary storage tank 3 into the main body 41. The concentrated sludge N thus supplied is heated by the steam S or the electric heater supplied into the jacket structure 41C while being stirred and mixed by the rotary driving device 46 around the central axis of the main body 41 by the stirring blade 47. The medium is indirectly heated from the inner peripheral surface of the main body 41, dried and granulated. Further, the dried sludge D thus dried and granulated is discharged from the discharge port 43 while the vacuum state in the main body 41 is maintained by the damper 44 and recovered by the recovery means 45 such as the container, and the crypts are sterilized. For example, it is effectively used as granulated dry soil. In addition, the moisture content of the dried sludge D having undergone the drying process in this way is set to about 40 wt%.

従って、このように構成された汚泥Mの処理設備、および該処理設備を用いた汚泥Mの処理方法においては、汚泥Mが濃縮手段による濃縮工程によって濃縮させられた濃縮汚泥Nが、そのままの含水率で乾燥手段に供給されて乾燥工程により乾燥させられることにより乾燥汚泥Dとして処理され、従来のようにこれら濃縮工程と乾燥工程の間にフィルタープレス等の脱水手段による脱水工程を要することがない。このため、処理設備としては上述のような脱水手段のためのコストやスペースを削減することができるとともに、処理方法としては一般的に回分処理とならざるを得ない脱水工程が省かれることで汚泥Mの処理を連続的に行うことが可能となって効率的となり、例えば本実施形態のように下水処理場等に比べて汚泥の生成量が僅かな小規模浄水場等における上水汚泥の処理に適用して特に好適である。   Therefore, in the sludge M treatment equipment configured as described above and the sludge M treatment method using the treatment equipment, the concentrated sludge N obtained by concentrating the sludge M in the concentration step by the concentrating means is used as it is. The dried sludge D is supplied to the drying means at a rate and dried by the drying process, so that there is no need for a dehydration process by a dehydration means such as a filter press between the concentration process and the drying process as in the prior art. . For this reason, the processing equipment can reduce the cost and space for the dehydrating means as described above, and the processing method is generally sludge by eliminating a dehydrating process that must be a batch process. It becomes possible to perform the treatment of M continuously and it becomes efficient. For example, as in the present embodiment, the treatment of water sewage sludge in a small-scale water purification plant or the like that produces a small amount of sludge compared to a sewage treatment plant or the like It is particularly suitable when applied to.

また、本実施形態での処理設備では、これら濃縮手段としての上記サイフォン式濃縮装置2と乾燥手段としての撹拌羽根内蔵型間接加熱乾燥機4との間に一時貯留槽3が備えられており、本実施形態の処理方法ではサイフォン式濃縮装置2によって濃縮された濃縮汚泥Nが、そのままの含水率でこの一時貯留槽3に一時貯留されてから、撹拌羽根内蔵型間接加熱乾燥機4に供給されるようになされている。このため、例えば上記小規模浄水場等において発生する上水汚泥の発生量に変動が生じて、これに伴い濃縮手段に供給される汚泥Mの量および該濃縮手段により濃縮された濃縮汚泥Nの量にも変動が生じたとしても、この一時貯留槽3に貯留される濃縮汚泥Nの量を調整することにより、乾燥手段には一定の含水率の濃縮汚泥Nを概ね均等な供給量で供給することが可能となり、この乾燥手段による乾燥工程においては、例えば上記ジャケット構造41Cに供給する蒸気Sの圧力を増減したり電気ヒータの温度を調節してその乾燥条件を変動させたりする必要がなく、安定した濃縮汚泥Nの乾燥を行うことが可能となる。ただし、このような濃縮汚泥Nの供給量に変動が生じるおそれがない場合には、一時貯留槽3を省略することも可能である。   Further, in the treatment facility in the present embodiment, a temporary storage tank 3 is provided between the siphon type concentrating device 2 as the concentrating means and the stirring blade built-in type indirect heating dryer 4 as the drying means, In the treatment method of the present embodiment, the concentrated sludge N concentrated by the siphon type concentrator 2 is temporarily stored in the temporary storage tank 3 with the moisture content as it is, and then supplied to the indirect heating dryer 4 with a built-in stirring blade. It has been made so that. For this reason, for example, the amount of generated water sludge generated in the small-scale water purification plant or the like fluctuates, and accordingly, the amount of sludge M supplied to the concentration means and the concentration of the concentrated sludge N concentrated by the concentration means. Even if the amount also fluctuates, by adjusting the amount of concentrated sludge N stored in the temporary storage tank 3, the drying means is supplied with the concentrated sludge N having a constant water content with a substantially uniform supply amount. In the drying process by this drying means, for example, there is no need to increase or decrease the pressure of the steam S supplied to the jacket structure 41C or to change the drying conditions by adjusting the temperature of the electric heater. It becomes possible to dry the stable concentrated sludge N. However, the temporary storage tank 3 can be omitted when there is no possibility that the supply amount of the concentrated sludge N varies.

さらに、本実施形態の処理設備では、上記濃縮手段として、汚泥Mが供給される濃縮槽21内に濾過手段22が配設され、この濾過手段22には濾液排出管23の一端が接続されるとともに、該濾液排出管23の他端は濃縮槽21外の濾過手段22よりも低い位置に開口されて、上記汚泥Mを濾過手段22によって濾過した濾液Lをサイフォンの原理によって自然流下により排出して濃縮汚泥を濾過手段22の表面に生成するサイフォン式濃縮装置2が用いられている。そして、さらに本実施形態ではこのサイフォン式濃縮装置2が、乾燥手段としての撹拌羽根内蔵型間接加熱乾燥機4、および一時貯留槽3の上方に設けられており、すなわちこれらサイフォン式濃縮装置2、一時貯留槽3、および撹拌羽根内蔵型間接加熱乾燥機4がこの順に上下方向に配設されてサイフォン式濃縮装置2が処理設備中最上部に位置させられているので、上記濾過手段22と濾液排出管23の他端との高低差を大きく確保することが可能となって、濾過手段22による濾過能力の向上を図ることができ、従って汚泥Mの効率的な濃縮を図ることができる。   Further, in the treatment facility of the present embodiment, as the concentration means, a filtration means 22 is disposed in the concentration tank 21 to which the sludge M is supplied, and one end of a filtrate discharge pipe 23 is connected to the filtration means 22. At the same time, the other end of the filtrate discharge pipe 23 is opened at a position lower than the filtration means 22 outside the concentration tank 21, and the filtrate L obtained by filtering the sludge M by the filtration means 22 is discharged by natural flow according to the siphon principle. Thus, a siphon type concentrating device 2 that generates concentrated sludge on the surface of the filtering means 22 is used. In this embodiment, the siphon type concentrator 2 is provided above the stirring blade built-in type indirect heating dryer 4 and the temporary storage tank 3 as drying means, that is, the siphon type concentrator 2, Since the temporary storage tank 3 and the indirect heating dryer 4 with a built-in stirring blade are arranged in this order in the vertical direction and the siphon type concentrating device 2 is located at the uppermost part in the processing equipment, the filtration means 22 and the filtrate A large difference in height from the other end of the discharge pipe 23 can be ensured, and the filtration capacity of the filtration means 22 can be improved. Therefore, the sludge M can be efficiently concentrated.

一方、本実施形態では、乾燥手段として、本体41内に供給された濃縮汚泥Nを該本体41内に内蔵された撹拌羽根47によって混合しつつ間接的に加熱して乾燥する撹拌羽根内蔵型間接加熱乾燥機4が用いられており、含水率が均一で、しかも適当な粒径に造粒された乾燥汚泥Dを生成することが可能となって、上述したような乾燥土として一層有効利用しやすくなる。また、本実施形態の撹拌羽根内蔵型間接加熱乾燥機4では、上記本体41が真空容器とされて真空ポンプ25に接続されることにより本体1内を真空状態(減圧状態)として濃縮汚泥Nを真空乾燥させることができ、濃縮汚泥Nの含水率が高かったりしても効率的な乾燥を図って所定の含水率の乾燥汚泥Dを得ることが可能となる。   On the other hand, in the present embodiment, as the drying means, the concentrated sludge N supplied in the main body 41 is mixed by the stirring blade 47 built in the main body 41 and heated indirectly to dry, and the stirring blade built-in type indirect The heat dryer 4 is used, and it becomes possible to produce the dried sludge D having a uniform moisture content and granulated to an appropriate particle size, and can be used more effectively as the above-mentioned dry soil. It becomes easy. Further, in the indirect heating dryer 4 with a built-in stirring blade of the present embodiment, the main body 41 is made into a vacuum vessel and connected to the vacuum pump 25, whereby the inside of the main body 1 is brought into a vacuum state (depressurized state), and concentrated sludge N It can be dried in vacuum, and even if the moisture content of the concentrated sludge N is high, it is possible to obtain a dry sludge D having a predetermined moisture content by efficiently drying.

しかも、この本体41の濃縮汚泥Nの供給口42および乾燥汚泥Dの排出口43には本体41内の真空状態を維持するダンパ32,44が備えられているので、汚泥N,Dの供給・排出の度に本体41内の真空状態が損なわれたりすることがなく、一層効率的な乾燥を図ることができる。加えて、この本体41内を真空状態とする真空ポンプ25が、濃縮手段としてのサイフォン式濃縮装置2の濾過手段22から濾液排出管23を介して濾液Lを初期に吸引する真空ポンプ25と共用とされているので、さらに処理設備の省コスト・省スペース化を図ることができて効率的である。ただし、場合によってはこのように本体41内を減圧することなく、常圧で濃縮汚泥Nを乾燥するようにしてもよい。   In addition, the supply port 42 for the concentrated sludge N and the discharge port 43 for the dried sludge D of the main body 41 are provided with dampers 32 and 44 for maintaining the vacuum state in the main body 41. The vacuum state in the main body 41 is not impaired every time it is discharged, and more efficient drying can be achieved. In addition, the vacuum pump 25 that evacuates the main body 41 is shared with the vacuum pump 25 that initially sucks the filtrate L from the filtration means 22 of the siphon type concentrator 2 as the concentration means through the filtrate discharge pipe 23. Therefore, it is possible to further reduce the cost and space of the processing equipment, which is efficient. However, in some cases, the concentrated sludge N may be dried at normal pressure without reducing the pressure inside the main body 41 in this way.

さらに、この本体41の下側は下方に向かうに従い漸次縮径する円錐台状とされて、いわゆるすり鉢状とされ、その周面部がジャケット構造41Cとされて間接加熱される一方、上記撹拌羽根47はこの本体41の中心軸回りに該本体41がなす上記円錐台の内部で回転するようになされている。従って、本体41上部の供給口42から当該撹拌羽根内蔵型間接加熱乾燥機4に供給された濃縮汚泥Nは、撹拌羽根47の回転により本体41内周面に摺接させられつつ撹拌・混合されて一層均一な含水率に乾燥されるとともに、排出口43が設けられた本体41下部では上記中心軸に直交する断面が小さいために受熱量が大きく、さらに効率的かつ確実な乾燥を図ることが可能となる。なお、本実施形態ではこうして濃縮汚泥Nを間接加熱するのに本体41の周面部をジャケット構造41Cとして上記S等の熱媒を供給するようにしているが、例えばこの周面部に電熱線を巻回したり油を媒体として伝熱ヒータ構造により濃縮汚泥Nを加熱・乾燥するようにしてもよい。   Further, the lower side of the main body 41 is formed into a truncated cone shape that gradually decreases in diameter as it goes downward, so as to form a so-called mortar shape, and the peripheral surface portion thereof is indirectly heated as a jacket structure 41C, while the stirring blade 47 Is rotated around the central axis of the main body 41 within the truncated cone formed by the main body 41. Accordingly, the concentrated sludge N supplied from the supply port 42 at the top of the main body 41 to the indirect heating dryer 4 with a built-in stirring blade is stirred and mixed while being brought into sliding contact with the inner peripheral surface of the main body 41 by the rotation of the stirring blade 47. In addition to being dried to a more uniform moisture content, the lower portion of the main body 41 provided with the discharge port 43 has a small cross section perpendicular to the central axis, so that the amount of heat received is large, and more efficient and reliable drying can be achieved. It becomes possible. In this embodiment, in order to indirectly heat the concentrated sludge N in this way, the peripheral surface portion of the main body 41 is used as the jacket structure 41C to supply the heat medium such as S. For example, a heating wire is wound around the peripheral surface portion. The concentrated sludge N may be heated and dried by rotating or using oil as a medium by a heat transfer heater structure.

本発明の汚泥の処理設備の一実施形態を示す概略図である。It is the schematic which shows one Embodiment of the processing equipment of the sludge of this invention. 図1に示す実施形態における濃縮工程を示す図である。It is a figure which shows the concentration process in embodiment shown in FIG.

符号の説明Explanation of symbols

2 サイフォン式濃縮装置(濃縮手段)
3 一時貯留槽
4 撹拌羽根内蔵型間接加熱乾燥機(乾燥手段)
21 濃縮槽
22 濾過手段
23 濾液排出管
24 濾液槽
25 真空ポンプ
32,44 ダンパ
41 撹拌羽根内蔵型間接加熱乾燥機の本体
41C 本体41のジャケット構造
47 撹拌羽根
W 洗浄排水
M 汚泥
N 濃縮汚泥
L 濾液
D 乾燥汚泥
S 蒸気
2 Siphon type concentrator (concentration means)
3 Temporary storage tank 4 Indirect heating dryer with built-in stirring blade (drying means)
DESCRIPTION OF SYMBOLS 21 Concentration tank 22 Filtration means 23 Filtrate discharge pipe 24 Filtrate tank 25 Vacuum pump 32, 44 Damper 41 Main body of indirect heating dryer with built-in stirring blade 41C Jacket structure of main body 41 47 Stirring blade W Wash drainage M Sludge N Concentrated sludge L Filtrate D Dry sludge S Steam

Claims (6)

汚泥を濃縮手段によって濃縮する濃縮工程と、この濃縮工程で濃縮させられた濃縮汚泥を略そのままの含水率で乾燥手段に供給して乾燥する乾燥工程とを備えてなることを特徴とする汚泥の処理方法。 A sludge comprising a concentration step for concentrating sludge by a concentration means, and a drying step for supplying the concentrated sludge concentrated in this concentration step to the drying means with substantially the same moisture content and drying the sludge. Processing method. 上記濃縮手段が、上記汚泥を濾過することによって濃縮する手段であることを特徴とする請求項1に記載の汚泥の処理方法。 The method for treating sludge according to claim 1, wherein the concentration means is means for concentrating the sludge by filtering. 上記濃縮工程と上記乾燥工程との間で、上記濃縮汚泥を略そのままの含水率で一時貯留することを特徴とする請求項1または請求項2に記載の汚泥の処理方法。 The method for treating sludge according to claim 1 or 2, wherein the concentrated sludge is temporarily stored at a substantially unchanged moisture content between the concentration step and the drying step. 汚泥を濃縮する濃縮手段と、この濃縮手段によって濃縮させられた濃縮汚泥が略そのままの含水率で供給されて該濃縮汚泥を乾燥する乾燥手段とを備えてなることを特徴とする汚泥の処理設備。 A sludge treatment facility comprising: a concentration means for concentrating sludge; and a drying means for drying the concentrated sludge by supplying the concentrated sludge concentrated by the concentration means at a substantially unchanged water content. . 上記濃縮手段と上記乾燥手段との間には、上記濃縮汚泥を略そのままの含水率で一時貯留する一時貯留槽が備えられていることを特徴とする請求項4に記載の汚泥の処理設備。 The sludge treatment facility according to claim 4, wherein a temporary storage tank is provided between the concentrating means and the drying means to temporarily store the concentrated sludge at a substantially unchanged moisture content. 上記濃縮手段は、濃縮槽内に配設された濾過手段に一端が接続されるとともに他端は濃縮槽外の上記濾過手段よりも低い位置に開口した濾液排出管を備え、上記濃縮槽に供給された汚泥を上記濾過手段によって濾過して、その濾液を上記濾液排出管を介して自然流下により排出するとともに上記濾過手段表面に上記濃縮汚泥を生成する濾過濃縮装置であり、この濃縮手段の上記濃縮槽が、上記乾燥手段の上方に配置されていることを特徴とする請求項4または請求項5に記載の汚泥の処理設備。
The concentrating means is provided with a filtrate discharge pipe having one end connected to the filtering means disposed in the concentrating tank and the other end opened at a position lower than the filtering means outside the concentrating tank, and is supplied to the concentrating tank The filtered sludge is filtered by the filtering means, the filtrate is discharged by natural flow through the filtrate discharge pipe, and the concentrated sludge is generated on the surface of the filtering means. The sludge treatment facility according to claim 4 or 5, wherein a concentration tank is disposed above the drying means.
JP2003428134A 2003-12-24 2003-12-24 Method and equipment for treating sludge Pending JP2005185902A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008212768A (en) * 2007-02-28 2008-09-18 Metawater Co Ltd Filtration and concentration apparatus, and filtration and concentration method

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008212768A (en) * 2007-02-28 2008-09-18 Metawater Co Ltd Filtration and concentration apparatus, and filtration and concentration method
JP4695107B2 (en) * 2007-02-28 2011-06-08 メタウォーター株式会社 Filtration concentration apparatus and filtration concentration method

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