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JP4493371B2 - Concentration separation method of sludge - Google Patents
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JP4493371B2 - Concentration separation method of sludge - Google Patents

Concentration separation method of sludge Download PDF

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JP4493371B2
JP4493371B2 JP2004059909A JP2004059909A JP4493371B2 JP 4493371 B2 JP4493371 B2 JP 4493371B2 JP 2004059909 A JP2004059909 A JP 2004059909A JP 2004059909 A JP2004059909 A JP 2004059909A JP 4493371 B2 JP4493371 B2 JP 4493371B2
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JP2005246229A (en
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太一 上坂
一久 西森
英俊 桝谷
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Kubota Corp
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Description

本発明は、下水、産業排水、生活排水等における汚泥の濃縮分離方法に関する。 The present invention relates to a method for concentrating and separating sludge in sewage, industrial wastewater, domestic wastewater and the like .

従来、汚泥の濃縮分離方法としては、例えば、図5に示すような加圧浮上分離法が挙げられる。すなわち、浮上分離槽41の前段に、原水を貯留する貯留槽42が設置され、貯留槽42に凝集剤を添加して攪拌することにより、汚泥を凝集させている。上記浮上分離槽41には、原水の一部を加圧して供給する加圧系43が設けられている。   Conventionally, as a method for concentrating and separating sludge, for example, a pressurized flotation separation method as shown in FIG. That is, a storage tank 42 for storing raw water is installed in the front stage of the floating separation tank 41, and the sludge is aggregated by adding a flocculant to the storage tank 42 and stirring. The levitation separation tank 41 is provided with a pressurizing system 43 that supplies a part of raw water under pressure.

上記加圧系43は空気圧縮機(図示省略)と加圧ポンプ44と空気溶解槽45と減圧弁46とで構成されており、空気を加圧して原水に溶解させた後、常圧に戻す際に析出する微細な気泡47を浮上分離槽41内の汚泥粒子に付着させて、浮上分離を行っている。   The pressurizing system 43 includes an air compressor (not shown), a pressurizing pump 44, an air dissolving tank 45, and a pressure reducing valve 46. After the air is pressurized and dissolved in raw water, the pressure is returned to normal pressure. The fine bubbles 47 deposited at this time are attached to the sludge particles in the floating separation tank 41 to perform the floating separation.

しかしながら上記加圧浮上分離法では、大量の空気を加圧して溶解させるため、高圧の空気を得るための大掛かりな加圧装置が必要であるといった問題がある。
また、別の方法として、図6に示すように、膜分離槽49内に浸漬型の膜分離装置50を設け、膜分離槽49の前段に汚泥貯留槽51を設置したものがある(例えば、特許文献1参照)。
However, in the pressurized flotation separation method, since a large amount of air is pressurized and dissolved, there is a problem that a large-scale pressurizing device for obtaining high-pressure air is necessary.
As another method, as shown in FIG. 6, there is a method in which a submerged membrane separation device 50 is provided in a membrane separation tank 49 and a sludge storage tank 51 is installed in front of the membrane separation tank 49 (for example, Patent Document 1).

これによると、汚泥貯留槽51から膜分離槽49に供給された汚泥は、膜分離装置50によって膜分離され、膜透過水と濃縮汚泥とが膜分離槽49から排出される。
しかしながら上記浸漬型の膜分離装置50を用いた汚泥の濃縮分離方法では、膜分離槽49内の汚泥濃度が高くなると、膜分離装置50の膜面に汚泥が付着して膜面が閉塞し、濃縮効率が低下し、膜の洗浄を頻繁に行わなければならないといった問題がある。
特開平8−323399号公報
According to this, the sludge supplied to the membrane separation tank 49 from the sludge storage tank 51 is membrane-separated by the membrane separation apparatus 50, and the membrane permeated water and the concentrated sludge are discharged from the membrane separation tank 49.
However, in the sludge concentration and separation method using the immersion type membrane separation device 50, when the sludge concentration in the membrane separation tank 49 increases, the sludge adheres to the membrane surface of the membrane separation device 50, and the membrane surface is blocked. There is a problem that the concentration efficiency is lowered and the membrane must be frequently washed.
JP-A-8-323399

本発明は、大掛かりな加圧装置を用いずに浮上分離が可能であり、また、膜分離の際の膜の閉塞を減少させることが可能で、効率が良く、低コストの汚泥の濃縮分離方法を提供することを目的とする。 The present invention is capable of flotation separation without using a large-scale pressurization apparatus, and can reduce membrane clogging during membrane separation, and is an efficient and low-cost method for concentrating and separating sludge. The purpose is to provide .

上記目的を達成するために、本第1発明は、汚泥を膜分離する膜分離槽と、汚泥を浮上分離する浮上分離槽とを用いた汚泥の濃縮分離方法であって、
上記膜分離槽と浮上分離槽との間で汚泥を循環させながら、膜分離槽内において汚泥を膜分離して濃縮する濃縮工程と、
上記両槽内の汚泥が所定濃度まで濃縮されると、上記両槽間における汚泥の循環を停止し、上記浮上分離槽内に過酸化水素を供給して気泡を発生させ、この気泡の上昇によって浮上分離槽内の汚泥を浮上分離する浮上分離工程と、
上記浮上分離工程によって得られた高濃縮汚泥を浮上分離槽内から除去する液分離工程とからなるものである。
In order to achieve the above object, the first invention is a method for concentrating and separating sludge using a membrane separation tank for separating sludge into a membrane and a floating separation tank for levitating and separating sludge,
A concentration step of separating and concentrating the sludge in the membrane separation tank while circulating the sludge between the membrane separation tank and the floating separation tank;
When the sludge in the two tanks is concentrated to a predetermined concentration, the circulation of the sludge between the two tanks is stopped, hydrogen peroxide is supplied into the floating separation tank to generate bubbles, and the rise of the bubbles A flotation separation step for flotation separation of sludge in the flotation separation tank;
And a liquid separation step of removing the highly concentrated sludge obtained by the above-described floating separation step from the inside of the floating separation tank .

これによると、膜分離によって汚泥が所定濃度まで濃縮されると、浮上分離工程を開始するため、上記濃縮工程を行っている時は膜分離槽内の汚泥濃度が所定濃度よりも低い状態で、膜分離されている。これにより、膜面に付着する汚泥の量が減って膜面の閉塞が減少する。   According to this, when the sludge is concentrated to a predetermined concentration by membrane separation, in order to start the flotation separation step, the sludge concentration in the membrane separation tank is lower than the predetermined concentration when performing the concentration step, The membrane is separated. Thereby, the quantity of the sludge adhering to a film surface reduces, and the obstruction | occlusion of a film surface reduces.

また、上記浮上分離工程では、浮上分離槽内に過酸化水素を供給することにより、化学反応によって気泡が発生するため、大掛かりな加圧装置を用いて気泡を発生させる必要はない。また、汚泥が所定濃度まで濃縮されているので、上記気泡が単独で上昇して脱気してしまうことはなく、ほとんど全ての気泡が汚泥中の固形物に付着して固形物と共に上昇し、このため、浮上分離の効率が向上する。さらに、過酸化水素の強力な酸化力によって、浮上分離槽内が酸化雰囲気になる。したがって、有機性汚泥の腐敗等により生成された高分子物が上記酸化雰囲気で分解されて分散化し、気泡が付着し易くなるため、浮上分離の効率がより一段と向上する。   Further, in the above-described levitation separation step, bubbles are generated by a chemical reaction by supplying hydrogen peroxide into the levitation separation tank, so that it is not necessary to generate bubbles using a large pressure device. In addition, since the sludge is concentrated to a predetermined concentration, the bubbles do not rise and deaerate alone, almost all the bubbles adhere to the solid matter in the sludge and rise with the solid matter, For this reason, the efficiency of floating separation improves. Furthermore, the inside of the floating separation tank becomes an oxidizing atmosphere due to the strong oxidizing power of hydrogen peroxide. Therefore, the polymer produced by the decay of organic sludge and the like is decomposed and dispersed in the oxidizing atmosphere, and bubbles are easily attached, so that the efficiency of flotation separation is further improved.

また、上記液分離工程において、浮上分離により得られた高濃縮汚泥を浮上分離槽内から除去しているため、浮上分離槽内の汚泥は低濃度に保たれる。これによって、引き続いて上記濃縮工程を行った際、汚泥が両槽間で循環して混合するため、両槽内の汚泥濃度の上昇が抑制される。   Moreover, in the said liquid separation process, since the highly concentrated sludge obtained by the floating separation is removed from the inside of the floating separation tank, the sludge in the floating separation tank is kept at a low concentration. Thereby, when the said concentration process is performed subsequently, since sludge circulates and mixes between both tanks, the raise of the sludge density | concentration in both tanks is suppressed.

さらに、膜分離と浮上分離とを別々の槽で行っているため、過酸化水素により発生した気泡を抱いた(付着した)汚泥が膜分離槽内の膜分離装置の中に付着するのを防止することができる。したがって、膜分離を再開するとき、上記気泡を抱いた汚泥が膜分離の障害になることはない。   In addition, since membrane separation and levitation separation are performed in separate tanks, sludge containing (attached) bubbles generated by hydrogen peroxide is prevented from adhering to the membrane separation device in the membrane separation tank. can do. Therefore, when the membrane separation is resumed, the sludge holding the bubbles does not become an obstacle to the membrane separation.

また、本第発明は、浮上分離工程において、浮上分離槽内に過酸化水素を供給した後、浮上分離槽内を攪拌するものである。 Further, according to the second invention, in the levitation separation step, after the hydrogen peroxide is supplied into the levitation separation tank, the inside of the levitation separation tank is agitated .

本発明によると、大掛かりな加圧装置を用いずに浮上分離が可能であり、膜分離の際の膜の閉塞を減少させることが可能で、汚泥の濃縮分離が効率良く低コストで行える。   According to the present invention, levitation separation is possible without using a large-scale pressurizing device, and it is possible to reduce membrane clogging during membrane separation, and sludge can be concentrated and separated efficiently and at low cost.

以下、本発明における第1の実施の形態を図1,図2に基づいて説明する。
1は汚泥の濃縮分離設備であり、汚泥を濃縮分離する濃縮槽2と、この濃縮槽2の前段にある貯留槽3とが設けられている。上記濃縮槽2内には、汚泥をろ過する浸漬型の膜分離装置4が設置されている。上記膜分離装置4には、膜を透過した分離水を濃縮槽2の外部へ取り出して放流する分離水取出管路5が接続されている。この分離水取出管路5には、吸引ろ過を行うための吸引ポンプ7が接続されている。また、濃縮槽2内には、膜分離装置4の下方から空気を吹き出す曝気装置6が設けられている。
Hereinafter, a first embodiment of the present invention will be described with reference to FIGS.
1 is a sludge concentration and separation facility, and is provided with a concentration tank 2 for concentration and separation of sludge, and a storage tank 3 in the preceding stage of the concentration tank 2. In the concentration tank 2, an immersion type membrane separator 4 for filtering sludge is installed. Connected to the membrane separation device 4 is a separation water extraction pipe 5 for taking out the separation water that has passed through the membrane to the outside of the concentration tank 2 and discharging it. A suction pump 7 for performing suction filtration is connected to the separated water extraction pipe 5. In addition, an aeration apparatus 6 that blows air from below the membrane separation apparatus 4 is provided in the concentration tank 2.

また、濃縮槽2には、浮上分離用の気泡8を発生させる過酸化水素(H)を供給するための過酸化水素供給系9が設けられている。この過酸化水素供給系9は、過酸化水素を貯留する過酸化水素用タンク10と、このタンク10内の過酸化水素を濃縮槽2内の下部に供給する過酸化水素用供給管路11と、この管路11に設けられたポンプ23とで構成されている。また、濃縮槽2内には、供給された過酸化水素を攪拌する攪拌機12が設けられている。 Further, the concentration tank 2 is provided with a hydrogen peroxide supply system 9 for supplying hydrogen peroxide (H 2 O 2 ) for generating bubbles 8 for floating separation. The hydrogen peroxide supply system 9 includes a hydrogen peroxide tank 10 that stores hydrogen peroxide, and a hydrogen peroxide supply line 11 that supplies the hydrogen peroxide in the tank 10 to the lower part of the concentration tank 2. The pump 23 is provided in the pipe 11. In the concentration tank 2, a stirrer 12 for stirring the supplied hydrogen peroxide is provided.

また、濃縮槽2の上部には、浮上分離によって得られさらに溢流したり或いは掻き取られて液面から除去された高濃縮汚泥を濃縮汚泥貯留槽14へ排出する排出管路15が接続されている。さらに、貯留槽3内に凝集剤を添加する凝集剤添加装置22と、濃縮槽2内にpH調整剤を添加するpH調整剤添加装置24とが設けられている。   Further, a discharge pipe 15 is connected to the upper part of the concentration tank 2 to discharge the highly concentrated sludge obtained by floating separation and overflowed or scraped off and removed from the liquid surface to the concentrated sludge storage tank 14. Yes. Further, a flocculant adding device 22 for adding a flocculant into the storage tank 3 and a pH adjusting agent adding device 24 for adding a pH adjusting agent into the concentration tank 2 are provided.

また、上記濃縮分離設備1には、濃縮汚泥貯留槽14に貯留された高濃縮汚泥を脱水する脱水機16と、脱水機16から排出されるろ液を貯留するろ液貯留槽17と、ろ液貯留槽17内のろ液を上記貯留槽3へ返送する返送管路18と、貯留槽3内の汚泥を含んだ排水を濃縮槽2に受け入れる汚泥受入管路19とが設けられている。尚、上記返送管路18と汚泥受入管路19とにはそれぞれポンプ20,21が接続されている。   Further, the concentration separation facility 1 includes a dehydrator 16 that dehydrates highly concentrated sludge stored in the concentrated sludge storage tank 14, a filtrate storage tank 17 that stores filtrate discharged from the dehydrator 16, and a filter. A return pipe 18 for returning the filtrate in the liquid storage tank 17 to the storage tank 3 and a sludge receiving pipe 19 for receiving waste water containing sludge in the storage tank 3 in the concentration tank 2 are provided. Pumps 20 and 21 are connected to the return pipe 18 and the sludge receiving pipe 19, respectively.

以下、上記濃縮分離設備1を用いた汚泥の濃縮分離方法を説明する。
上記汚泥の濃縮分離方法は濃縮工程Aと浮上分離工程Bと液分離工程Cとからなり、各工程A〜Cの詳細は次の通りである。
Hereinafter, a method for concentration and separation of sludge using the concentration and separation facility 1 will be described.
The sludge concentration and separation method includes a concentration step A, a flotation separation step B, and a liquid separation step C. Details of each step A to C are as follows.

(1)上記濃縮工程Aにおいて、先ず、貯留槽3内の汚泥を含んだ排水を汚泥受入管路19から濃縮槽2内へ受け入れ、曝気装置6を作動させて曝気を開始し、吸引ポンプ7を作動させて膜分離装置4によるろ過を開始する。   (1) In the concentration step A, first, wastewater containing sludge in the storage tank 3 is received from the sludge receiving pipe 19 into the concentration tank 2, and the aeration apparatus 6 is operated to start aeration. To start filtration by the membrane separation device 4.

(2)上記濃縮工程Aを複数回繰り返して、膜分離により濃縮槽2内の汚泥が次第に濃縮され、濃縮槽2内の汚泥濃度が所定濃度(例えば1.5%)まで濃縮されると、次に、上記浮上分離工程Bにおいて、吸引ポンプ7を停止して膜分離装置4によるろ過を停止し、曝気装置6による曝気を停止し、過酸化水素用タンク10内の過酸化水素(液体)を濃縮槽2内の下部へ供給し、攪拌機12で攪拌する。これにより、過酸化水素が化学反応を起して濃縮槽2内に酸素ガス等の気泡8が多量に発生し、この気泡8の上昇によって、濃縮槽2内の汚泥が浮上分離され、液面に高濃縮汚泥が浮上する。   (2) When the concentration step A is repeated a plurality of times, the sludge in the concentration tank 2 is gradually concentrated by membrane separation, and the sludge concentration in the concentration tank 2 is concentrated to a predetermined concentration (for example, 1.5%), Next, in the levitation separation step B, the suction pump 7 is stopped, the filtration by the membrane separation device 4 is stopped, the aeration by the aeration device 6 is stopped, and the hydrogen peroxide (liquid) in the hydrogen peroxide tank 10 is stopped. Is supplied to the lower part of the concentration tank 2 and stirred by the stirrer 12. As a result, hydrogen peroxide causes a chemical reaction to generate a large amount of bubbles 8 such as oxygen gas in the concentration tank 2, and the rising of the bubbles 8 causes the sludge in the concentration tank 2 to float and be separated. Highly concentrated sludge emerges.

(3)その後、液分離工程Cにおいて、濃縮槽2への過酸化水素の供給を停止し、上記高濃縮汚泥を溢流や掻き取りによって液面から除去し排出管路15より濃縮汚泥貯留槽14へ排出する。尚、上記過酸化水素を濃縮槽2内へ供給した後、pH調整剤添加装置24によってpH調整剤を濃縮槽2内へ添加し、濃縮槽2内のpHを調整してもよい。   (3) Thereafter, in the liquid separation step C, the supply of hydrogen peroxide to the concentration tank 2 is stopped, the highly concentrated sludge is removed from the liquid surface by overflow or scraping, and the concentrated sludge storage tank is discharged from the discharge line 15. Drain to 14. In addition, after supplying the hydrogen peroxide into the concentration tank 2, the pH adjuster adding device 24 may add a pH adjuster into the concentration tank 2 to adjust the pH in the concentration tank 2.

(4)その後、上記濃縮工程Aへ戻る。
上記のような汚泥の濃縮分離方法によると、膜分離装置4の膜分離によって濃縮槽2内の汚泥が所定濃度まで濃縮されると、膜分離装置4による濃縮工程Aを停止し、浮上分離工程Bを開始するため、上記濃縮工程Aを行っている時は濃縮槽2内の汚泥濃度が所定濃度よりも低い状態で、膜分離されている。これにより、膜分離装置4の膜面に付着する汚泥の量が減って膜面の閉塞が減少し、メンテナンスの回数を減らすことができる。また、濃縮工程Aにおいては、曝気装置6から吹き出た空気の気泡が膜分離装置4の膜面に接触しながら上昇するため、膜面が洗浄され、これにより、膜面の閉塞がさらに減少する。
(4) Thereafter, the process returns to the concentration step A.
According to the sludge concentration and separation method as described above, when the sludge in the concentration tank 2 is concentrated to a predetermined concentration by the membrane separation of the membrane separation device 4, the concentration step A by the membrane separation device 4 is stopped, and the floating separation step. In order to start B, when performing the concentration step A, membrane separation is performed in a state where the sludge concentration in the concentration tank 2 is lower than a predetermined concentration. Thereby, the quantity of the sludge adhering to the membrane surface of the membrane separator 4 decreases, the blockage | closure of a membrane surface reduces, and the frequency | count of a maintenance can be reduced. Further, in the concentration step A, air bubbles blown out from the aeration device 6 rise while contacting the membrane surface of the membrane separation device 4, so that the membrane surface is washed, thereby further reducing the membrane surface blockage. .

また、上記浮上分離工程Bでは、濃縮槽2内に過酸化水素を供給することにより、化学反応によって酸素ガス等の気泡8が多量に発生するため、大掛かりな加圧装置を用いて気泡8を発生させる必要はない。また、濃縮槽2内の汚泥濃度が希薄な場合では上記気泡8が単独で上昇して脱気してしまう恐れがあるが、汚泥が所定濃度まで濃縮されているので、上記気泡8が単独で上昇して脱気することはなく、ほとんど全ての気泡8が汚泥中の固形物に付着して固形物と共に上昇し、このため、浮上分離の効率が改善される。   Further, in the above-described levitation separation process B, since hydrogen peroxide is supplied into the concentration tank 2, a large amount of bubbles 8 such as oxygen gas are generated by a chemical reaction. Therefore, the bubbles 8 are formed using a large pressure device. There is no need to generate it. Further, when the sludge concentration in the concentration tank 2 is thin, the bubbles 8 may rise and be degassed alone. However, since the sludge is concentrated to a predetermined concentration, the bubbles 8 are independent. There is no rise and degassing, and almost all of the bubbles 8 adhere to the solid matter in the sludge and rise together with the solid matter, thereby improving the efficiency of flotation separation.

さらに、過酸化水素の強力な酸化力によって、濃縮槽2内が酸化雰囲気になる。したがって、濃縮槽2内が好気状態となって汚泥の改質効果がある。また、汚泥が有機性汚泥である場合、有機性汚泥の腐敗等により生成された高分子物が上記酸化雰囲気で分解されて分散化し、気泡8が付着し易くなるため、浮上分離の効率がより一段と向上する。尚、上記濃縮工程Aにおける曝気により、有機性汚泥の腐敗が解消される効果もある。また、濃縮槽2内に未反応の凝集剤(残留ポリマー)が流入しても、未反応の凝集剤は過酸化水素により加水分解されるため、膜分離装置4の膜面に未反応の凝集剤が付着するのを防止できる。   Furthermore, the inside of the concentration tank 2 becomes an oxidizing atmosphere by the strong oxidizing power of hydrogen peroxide. Therefore, the inside of the concentration tank 2 is in an aerobic state and has a sludge reforming effect. In addition, when the sludge is organic sludge, the polymer produced by the decay of the organic sludge is decomposed and dispersed in the oxidizing atmosphere, and the bubbles 8 are more likely to adhere. Improve further. In addition, there is also an effect that the decay of the organic sludge is eliminated by aeration in the concentration step A. Even if unreacted flocculant (residual polymer) flows into the concentration tank 2, the unreacted flocculant is hydrolyzed by hydrogen peroxide, so that unreacted flocculant is formed on the membrane surface of the membrane separation device 4. It is possible to prevent the agent from adhering.

また、上記液分離工程Cでは、濃縮槽2内の液面から高濃縮汚泥を濃縮汚泥貯留槽14へ排出するため、濃縮槽2内の汚泥濃度の上昇が抑制され、濃縮槽2内の汚泥濃度を所定濃度よりも低く保つことができる。   Further, in the liquid separation step C, the highly concentrated sludge is discharged from the liquid level in the concentration tank 2 to the concentrated sludge storage tank 14, so that the increase in the sludge concentration in the concentration tank 2 is suppressed, and the sludge in the concentration tank 2 is suppressed. The concentration can be kept lower than the predetermined concentration.

尚、濃縮槽2内における過酸化水素の濃度は、例えば、SS1.5%に対して、0.02〜0.4%(1〜25%対SS)としている。これは、弱アルカリ域で用いる方が、反応性が高く、且つ、気泡8がよく発生するためである。   In addition, the density | concentration of the hydrogen peroxide in the concentration tank 2 is 0.02-0.4% (1-25% vs. SS) with respect to SS1.5%, for example. This is because the use in the weak alkali region has higher reactivity and the bubbles 8 are more often generated.

また、実験では、濃縮工程Aにおいて膜分離によって濃縮槽2内の汚泥濃度が1.5%まで濃縮された際、浮上分離工程Bにおいて、過酸化水素を供給して浮上分離を行った場合、2〜6%の固形物が浮上し、この固形物を除去した後、濃縮槽2内全体の汚泥濃度の平均が1%以下に低下した。   Further, in the experiment, when the sludge concentration in the concentration tank 2 was concentrated to 1.5% by membrane separation in the concentration step A, in the floating separation step B, when hydrogen peroxide was supplied and the floating separation was performed, After 2 to 6% of solid matter floated and this solid matter was removed, the average sludge concentration in the entire concentration tank 2 was reduced to 1% or less.

また、濃縮汚泥貯留槽14内に貯留された高濃縮汚泥は脱水機16で脱水され、脱水の際に脱水機16から排出されたろ液は、凝集剤を含んでおり、一旦、ろ液貯留槽17内に貯留され、その後、返送水としてろ液貯留槽17から返送管路18を通って貯留槽3へ返送される。   The highly concentrated sludge stored in the concentrated sludge storage tank 14 is dehydrated by the dehydrator 16, and the filtrate discharged from the dehydrator 16 at the time of dehydration contains a flocculant. 17, and then returned to the storage tank 3 from the filtrate storage tank 17 through the return pipe 18 as return water.

上記実施の形態では、濃縮工程Aにおいて、一旦、曝気を開始すると、所期の汚泥の濃縮分離が完了するまで連続的に曝気を行ってもよい。
上記実施の形態では、吸引ポンプ7による吸引圧を利用して、膜分離装置4によるろ過を行っているが、吸引ポンプ7を用いず、自然水頭を利用してろ過を行ってもよい。また、汚泥の所定濃度を例えば1.5%に設定しているが、この値に限定されるものではなく、汚泥や膜分離装置4の種類等様々な条件に応じて、変えてもよい。
In the above embodiment, once the aeration is started in the concentration step A, the aeration may be continuously performed until the intended concentration and separation of the sludge is completed.
In the said embodiment, although the filtration by the membrane separator 4 is performed using the suction pressure by the suction pump 7, you may filter using a natural head without using the suction pump 7. FIG. Moreover, although the predetermined density | concentration of sludge is set to 1.5%, for example, it is not limited to this value, You may change according to various conditions, such as the kind of sludge and the membrane separation apparatus 4. FIG.

上記実施の形態では、凝集剤添加装置22で凝集剤を貯留槽3内に添加しているが、濃縮槽2内に添加してもよい。
次に、本発明における第2の実施の形態を図3,図4に基づいて説明する。
In the above embodiment, the flocculant is added to the storage tank 3 by the flocculant adding device 22, but may be added to the concentration tank 2.
Next, a second embodiment of the present invention will be described with reference to FIGS.

濃縮分離設備29には槽体30が設けられており、この槽体30は、仕切壁31によって、汚泥を膜分離する膜分離槽32と、汚泥を浮上分離する浮上分離槽33とに区分けされている。上記膜分離槽32内には、浸漬型の膜分離装置4が設置されている。上記膜分離装置4には分離水を膜分離槽32の外部へ取り出して放流する分離水取出管路5が接続され、この分離水取出管路5には吸引ポンプ7が接続されている。また、膜分離槽32内には曝気装置6が設けられている。   A tank body 30 is provided in the concentration and separation facility 29, and the tank body 30 is divided by a partition wall 31 into a membrane separation tank 32 that separates sludge from a membrane and a floating separation tank 33 that floats and separates sludge. ing. An immersion type membrane separation device 4 is installed in the membrane separation tank 32. The membrane separation device 4 is connected to a separation water extraction pipe 5 for taking out and discharging the separated water to the outside of the membrane separation tank 32, and a suction pump 7 is connected to the separation water extraction pipe 5. An aeration apparatus 6 is provided in the membrane separation tank 32.

上記浮上分離槽33には、浮上分離用の気泡8を発生させる過酸化水素(H)を供給するための過酸化水素供給系9が設けられている。過酸化水素供給系9は過酸化水素用タンク10と過酸化水素用供給管路11とポンプ23とで構成されている。また、浮上分離槽33内には、供給された過酸化水素を攪拌する攪拌機12が設けられている。 The floating separation tank 33 is provided with a hydrogen peroxide supply system 9 for supplying hydrogen peroxide (H 2 O 2 ) for generating bubbles 8 for floating separation. The hydrogen peroxide supply system 9 includes a hydrogen peroxide tank 10, a hydrogen peroxide supply line 11, and a pump 23. A stirrer 12 for stirring the supplied hydrogen peroxide is provided in the floating separation tank 33.

上記槽体30には、貯留槽3から供給された汚泥を浮上分離槽33と膜分離槽32との間で循環させる循環手段34が設けられている。この循環手段34は、浮上分離槽33内の汚泥を膜分離槽32へ供給する循環管路35と、この循環管路35に設けられた循環ポンプ36と、上記仕切壁31に形成されて両槽32,33に連通する連通口37とで構成されている。   The tank body 30 is provided with a circulating means 34 for circulating the sludge supplied from the storage tank 3 between the floating separation tank 33 and the membrane separation tank 32. The circulation means 34 is formed in the circulation pipe 35 for supplying the sludge in the floating separation tank 33 to the membrane separation tank 32, the circulation pump 36 provided in the circulation pipe 35, and the partition wall 31. The communication port 37 communicates with the tanks 32 and 33.

また、浮上分離槽33の上部には、浮上分離によって得られさらに溢流したり或いは掻き取られて液面から除去された高濃縮汚泥を濃縮汚泥貯留槽14へ排出する排出管路15が接続されている。   Further, a discharge pipe 15 is connected to the top of the flotation separation tank 33 to discharge the highly concentrated sludge obtained by flotation separation and further overflowed or scraped off and removed from the liquid surface to the concentrated sludge storage tank 14. ing.

さらに、上記濃縮分離設備28には、脱水機16と、ろ液貯留槽17と、返送管路18と、貯留槽3内の汚泥を浮上分離槽33に受け入れる汚泥受入管路19とが設けられている。また、貯留槽3内に凝集剤を添加する凝集剤添加装置22と、浮上分離槽33内にpH調整剤を添加するpH調整剤添加装置24とが設けられている。   Further, the concentration and separation facility 28 is provided with a dehydrator 16, a filtrate storage tank 17, a return pipe 18, and a sludge receiving pipe 19 for receiving sludge in the storage tank 3 in the floating separation tank 33. ing. Further, a flocculant adding device 22 for adding a flocculant to the storage tank 3 and a pH adjusting agent adding device 24 for adding a pH adjusting agent to the floating separation tank 33 are provided.

以下、上記濃縮分離設備29を用いた汚泥の濃縮分離方法を説明する。
上記汚泥の濃縮分離方法は濃縮工程Aと浮上分離工程Bと液分離工程Cとからなり、各工程A〜Cの詳細は次の通りである。
Hereinafter, a method for concentrating and separating sludge using the concentration and separation facility 29 will be described.
The sludge concentration and separation method includes a concentration step A, a flotation separation step B, and a liquid separation step C. Details of each step A to C are as follows.

(1)上記濃縮工程Aにおいて、先ず、貯留槽3内の汚泥を含んだ排水を汚泥受入管路19から浮上分離槽33内へ受け入れ、循環ポンプ36を作動して、浮上分離槽33内の汚泥を循環管路35から膜分離槽32へ供給することにより、膜分離槽32内の汚泥が連通口37を通って浮上分離槽33へ流れる。これにより、膜分離槽32と浮上分離槽33との間で汚泥が循環し、この状態で、曝気装置6を作動させて曝気を開始し、吸引ポンプ7を作動させて膜分離装置4によるろ過を開始する。そして、上記ろ過により分離された分離水が膜分離槽32から分離水取出管路5を通って排出され、両槽32,33内の水位が所定水位より低下すると、上記のように、再び、貯留槽3内の汚泥を汚泥受入管路19から浮上分離槽33内へ受け入れて、両槽32,33内の水位を所定水位まで上げる。   (1) In the concentration step A, first, wastewater containing sludge in the storage tank 3 is received from the sludge receiving pipe 19 into the floating separation tank 33, the circulation pump 36 is operated, By supplying the sludge from the circulation pipe 35 to the membrane separation tank 32, the sludge in the membrane separation tank 32 flows to the floating separation tank 33 through the communication port 37. Thereby, sludge circulates between the membrane separation tank 32 and the floating separation tank 33. In this state, the aeration apparatus 6 is operated to start aeration, and the suction pump 7 is operated to perform filtration by the membrane separation apparatus 4. To start. Then, when the separated water separated by the filtration is discharged from the membrane separation tank 32 through the separated water extraction conduit 5, and when the water level in both tanks 32 and 33 falls below a predetermined water level, as described above, The sludge in the storage tank 3 is received from the sludge receiving pipe 19 into the floating separation tank 33, and the water levels in both tanks 32 and 33 are raised to a predetermined water level.

(2)上記濃縮工程Aを複数回繰り返して、膜分離により両槽32,33内の汚泥が次第に濃縮され、両槽32,33内の汚泥濃度が所定濃度まで濃縮されると、次に、上記浮上分離工程Bにおいて、循環ポンプ36を停止して、膜分離槽32と浮上分離槽33との間における汚泥の循環を停止し、さらに、吸引ポンプ7を停止して膜分離装置4によるろ過を停止し、曝気装置6による曝気を停止する。その後、過酸化水素用タンク10内の過酸化水素(液体)を浮上分離槽33内の下部へ供給し、攪拌機12で攪拌する。これにより、過酸化水素が化学反応を起して浮上分離槽33内に酸素ガス等の気泡8が多量に発生し、この気泡8の上昇によって、浮上分離槽33内の汚泥が浮上分離され、浮上分離槽33内の液面に高濃縮汚泥が浮上する。   (2) When the concentration step A is repeated a plurality of times, the sludge in both tanks 32 and 33 is gradually concentrated by membrane separation, and the sludge concentration in both tanks 32 and 33 is concentrated to a predetermined concentration. In the levitation separation step B, the circulation pump 36 is stopped, the sludge circulation between the membrane separation tank 32 and the levitation separation tank 33 is stopped, and further, the suction pump 7 is stopped and the filtration by the membrane separation device 4 is performed. And aeration by the aeration apparatus 6 is stopped. Thereafter, hydrogen peroxide (liquid) in the hydrogen peroxide tank 10 is supplied to the lower part of the floating separation tank 33 and stirred by the stirrer 12. As a result, hydrogen peroxide causes a chemical reaction to generate a large amount of bubbles 8 such as oxygen gas in the floating separation tank 33, and as the bubbles 8 rise, sludge in the floating separation tank 33 is floated and separated. Highly concentrated sludge floats on the liquid level in the levitation separation tank 33.

(3)その後、液分離工程Cにおいて、浮上分離槽33への過酸化水素の供給を停止し、浮上分離槽33内の高濃縮汚泥を溢流や掻き取りによって液面から除去し排出管路15より濃縮汚泥貯留槽14へ排出する。尚、上記過酸化水素を浮上分離槽33内へ供給した後、pH調整剤添加装置24によってpH調整剤を浮上分離槽33内へ添加し、pHを調整してもよい。   (3) Thereafter, in the liquid separation step C, the supply of hydrogen peroxide to the floating separation tank 33 is stopped, and the highly concentrated sludge in the floating separation tank 33 is removed from the liquid surface by overflow or scraping, and the discharge pipe 15 is discharged to the concentrated sludge storage tank 14. In addition, after supplying the hydrogen peroxide into the floating separation tank 33, the pH adjusting agent may be added to the floating separation tank 33 by the pH adjusting agent adding device 24 to adjust the pH.

(4)その後、上記濃縮工程Aへ戻る。
上記のような汚泥の濃縮分離方法によると、両槽32,33で汚泥を循環させながら、膜分離装置4の膜分離によって両槽32,33内の汚泥が所定濃度まで濃縮されると、膜分離装置4による濃縮工程Aを停止し、浮上分離工程Bを開始するため、上記濃縮工程Aを行っている時は両槽32,33内の汚泥濃度が所定濃度よりも低い状態で、膜分離されている。これにより、膜分離装置4の膜面に付着する汚泥の量が減って膜面の閉塞が減少し、メンテナンスの回数を減らすことができる。また、濃縮工程Aにおいては、曝気装置6から吹き出た空気の気泡が膜分離装置4の膜面に接触しながら上昇するため、膜面が洗浄され、これにより、膜面の閉塞がさらに減少する。
(4) Thereafter, the process returns to the concentration step A.
According to the sludge concentration and separation method as described above, when the sludge in both tanks 32 and 33 is concentrated to a predetermined concentration by membrane separation of the membrane separation device 4 while circulating the sludge in both tanks 32 and 33, the membrane In order to stop the concentration step A by the separation device 4 and start the floating separation step B, the membrane separation is performed with the sludge concentration in both tanks 32 and 33 being lower than the predetermined concentration during the concentration step A. Has been. Thereby, the quantity of the sludge adhering to the membrane surface of the membrane separator 4 decreases, the blockage | closure of a membrane surface reduces, and the frequency | count of a maintenance can be reduced. Further, in the concentration step A, air bubbles blown out from the aeration device 6 rise while contacting the membrane surface of the membrane separation device 4, so that the membrane surface is washed, thereby further reducing the membrane surface blockage. .

また、上記浮上分離工程Bでは、浮上分離槽33内に過酸化水素を供給することにより、化学反応によって酸素ガス等の気泡8が多量に発生するため、大掛かりな加圧装置を用いて気泡8を発生させる必要はない。また、浮上分離槽33内の汚泥濃度が希薄な場合では上記気泡8が単独で上昇して脱気してしまう恐れがあるが、両槽32,33内の汚泥が所定濃度まで濃縮されているので、上記気泡8が単独で上昇して脱気することはなく、ほとんど全ての気泡8が浮上分離槽33内の汚泥中の固形物に付着して固形物と共に上昇し、このため、浮上分離の効率が改善される。   Further, in the above-described levitation separation step B, since hydrogen peroxide is supplied into the levitation separation tank 33, a large amount of bubbles 8 such as oxygen gas are generated by a chemical reaction. It is not necessary to generate Further, when the sludge concentration in the levitation separation tank 33 is thin, there is a possibility that the bubbles 8 will rise alone and degas, but the sludge in both tanks 32 and 33 is concentrated to a predetermined concentration. Therefore, the bubbles 8 are not lifted up and degassed, and almost all the bubbles 8 are attached to the solids in the sludge in the floating separation tank 33 and rise together with the solids. Efficiency is improved.

さらに、過酸化水素の強力な酸化力によって、浮上分離槽33内が酸化雰囲気になる。したがって、浮上分離槽33内が好気状態となって汚泥の改質効果がある。また、汚泥が有機性汚泥である場合、有機性汚泥の腐敗等により生成された高分子物が上記酸化雰囲気で分解されて分散化し、気泡8が付着し易くなるため、浮上分離の効率がより一段と向上する。尚、上記濃縮工程Aにおける曝気により、有機性汚泥の腐敗が解消される効果もある。また、浮上分離槽33内に未反応の凝集剤(残留ポリマー)が流入しても、未反応の凝集剤は過酸化水素により加水分解されるため、膜分離装置4の膜面に未反応の凝集剤が付着するのを防止できる。   Furthermore, the inside of the floating separation tank 33 becomes an oxidizing atmosphere by the strong oxidizing power of hydrogen peroxide. Therefore, the inside of the floating separation tank 33 is in an aerobic state and has a sludge reforming effect. In addition, when the sludge is organic sludge, the polymer produced by the decay of the organic sludge is decomposed and dispersed in the oxidizing atmosphere, and the bubbles 8 are more likely to adhere. Improve further. In addition, there is also an effect that the decay of the organic sludge is eliminated by aeration in the concentration step A. Even if unreacted flocculant (residual polymer) flows into the levitation separation tank 33, the unreacted flocculant is hydrolyzed by hydrogen peroxide. It is possible to prevent the flocculant from adhering.

また、上記液分離工程Cでは、浮上分離槽33内の液面から高濃縮汚泥を濃縮汚泥貯留槽14へ排出するため、浮上分離槽33内の汚泥濃度の上昇が抑制される。これにより、引き続いて、上記濃縮工程Aを行った際、汚泥が両槽32,33間で循環して混合するため、両槽32,33内の汚泥濃度を所定濃度よりも低く保つことができる。   Further, in the liquid separation step C, highly concentrated sludge is discharged from the liquid level in the floating separation tank 33 to the concentrated sludge storage tank 14, so that an increase in the sludge concentration in the floating separation tank 33 is suppressed. Thereby, when the said concentration process A is performed continuously, since sludge circulates and mixes between both tanks 32 and 33, the sludge density | concentration in both tanks 32 and 33 can be kept lower than predetermined concentration. .

さらに、先述した第1の実施の形態では、図1に示すように、膜分離と浮上分離とを同じ槽2で行っているため、過酸化水素により発生した気泡8を抱いた(付着した)汚泥が膜分離装置4の膜面等に付着する恐れがあるが、これに対して、上記第2の実施の形態では、図3に示すように、膜分離と浮上分離とを別々の槽32,33で行っているため、過酸化水素により発生した気泡8を抱いた(付着した)汚泥が膜分離槽32内の膜分離装置4の膜面等に付着するのを防止することができる。したがって、膜分離を再開するとき、上記気泡8を抱いた汚泥が膜分離の障害になることはない。   Further, in the first embodiment described above, as shown in FIG. 1, since the membrane separation and the floating separation are performed in the same tank 2, the bubbles 8 generated by hydrogen peroxide are held (attached). There is a risk that sludge may adhere to the membrane surface of the membrane separation device 4. On the other hand, in the second embodiment, as shown in FIG. 33, it is possible to prevent the sludge holding (attached) bubbles 8 generated by hydrogen peroxide from adhering to the membrane surface of the membrane separation device 4 in the membrane separation tank 32. Therefore, when the membrane separation is resumed, the sludge holding the bubbles 8 does not become an obstacle to the membrane separation.

上記第2の実施の形態では、例えば、汚泥を10倍に濃縮する場合、上記膜分離槽32における濃縮工程Aで5倍に濃縮し、上記浮上分離槽33における浮上分離工程Bで2倍に濃縮するといった組合せが可能である。   In the second embodiment, for example, when sludge is concentrated 10 times, it is concentrated 5 times in the concentration step A in the membrane separation tank 32 and doubled in the floating separation step B in the floating separation tank 33. Combinations such as enrichment are possible.

上記第2の実施の形態では、濃縮工程Aでは過酸化水素の供給を停止しているが、嫌気化を防止するために、濃縮工程Aにおいても過酸化水素を浮上分離槽33に供給してもよい。また、上記各工程A〜Cのサイクルを短縮することで、過酸化水素の供給量を削減できる。また、循環ポンプ36を停止している時間で、浮上分離が完了するならば、膜分離装置4により連続的にろ過し続けることも可能である。   In the second embodiment, the supply of hydrogen peroxide is stopped in the concentration step A. However, in order to prevent anaerobization, hydrogen peroxide is supplied to the floating separation tank 33 also in the concentration step A. Also good. Moreover, the supply amount of hydrogen peroxide can be reduced by shortening the cycle of each said process AC. Further, if the levitation separation is completed within the time when the circulation pump 36 is stopped, the membrane separation device 4 can continue to filter continuously.

上記第2の実施の形態では、浮上分離工程Bにおいて膜分離装置4によるろ過を停止しているが、そのままろ過を継続して行ってもよい。また、浮上分離工程Bにおいて曝気装置6による曝気を停止しているが、そのまま曝気を継続して行ってもよい。また、濃縮工程Aにおいて、一旦、曝気を開始すると、所期の汚泥の濃縮分離が完了するまで連続的に曝気を行ってもよい。   In the second embodiment, the filtration by the membrane separation device 4 is stopped in the flotation separation step B, but the filtration may be continued as it is. Further, although aeration by the aeration apparatus 6 is stopped in the floating separation step B, aeration may be continued as it is. In the concentration step A, once aeration is started, aeration may be continuously performed until the intended concentration and separation of sludge is completed.

上記第2の実施の形態では、凝集剤添加装置22で凝集剤を貯留槽3内に添加しているが、膜分離槽32や浮上分離槽33内に添加してもよい。   In the second embodiment, the flocculant adding device 22 adds the flocculant into the storage tank 3, but the flocculant may be added into the membrane separation tank 32 and the floating separation tank 33.

本発明の第1の実施の形態における汚泥の濃縮分離設備の図である。It is a figure of the concentration separation equipment of sludge in a 1st embodiment of the present invention. 同、汚泥の濃縮分離方法の手順を示すフローチャートである。It is a flowchart which shows the procedure of the concentration separation method of sludge. 本発明の第2の実施の形態における汚泥の濃縮分離設備の図である。It is a figure of the sludge concentration separation equipment in the 2nd embodiment of the present invention. 同、汚泥の濃縮分離方法の手順を示すフローチャートである。It is a flowchart which shows the procedure of the concentration separation method of sludge. 従来の汚泥の濃縮分離設備の図である。It is a figure of the conventional concentration separation equipment of sludge. 従来の汚泥の濃縮分離設備の図である。It is a figure of the conventional concentration separation equipment of sludge.

符号の説明Explanation of symbols

1 濃縮分離設備
2 濃縮槽
4 膜分離装置
8 気泡
9 過酸化水素供給系
29 濃縮分離設備
32 膜分離槽
33 浮上分離槽
34 循環手段
DESCRIPTION OF SYMBOLS 1 Concentration separation equipment 2 Concentration tank 4 Membrane separation device 8 Bubble 9 Hydrogen peroxide supply system 29 Concentration separation equipment 32 Membrane separation tank 33 Floating separation tank 34 Circulation means

Claims (2)

汚泥を膜分離する膜分離槽と、汚泥を浮上分離する浮上分離槽とを用いた汚泥の濃縮分離方法であって、
上記膜分離槽と浮上分離槽との間で汚泥を循環させながら、膜分離槽内において汚泥を膜分離して濃縮する濃縮工程と、
上記両槽内の汚泥が所定濃度まで濃縮されると、上記両槽間における汚泥の循環を停止し、上記浮上分離槽内に過酸化水素を供給して気泡を発生させ、この気泡の上昇によって浮上分離槽内の汚泥を浮上分離する浮上分離工程と、
上記浮上分離工程によって得られた高濃縮汚泥を浮上分離槽内から除去する液分離工程とからなることを特徴とする汚泥の濃縮分離方法。
A method for concentrating and separating sludge using a membrane separation tank for separating sludge into membranes and a levitating separation tank for levitating and separating sludge,
A concentration step of separating and concentrating the sludge in the membrane separation tank while circulating the sludge between the membrane separation tank and the floating separation tank;
When the sludge in the two tanks is concentrated to a predetermined concentration, the circulation of the sludge between the two tanks is stopped, hydrogen peroxide is supplied into the floating separation tank to generate bubbles, and the rise of the bubbles A flotation separation step for flotation separation of sludge in the flotation separation tank;
A method for concentrating and separating sludge, comprising: a liquid separation step for removing highly concentrated sludge obtained by the above-described flotation separation step from the inside of the flotation separation tank.
浮上分離工程において、浮上分離槽内に過酸化水素を供給した後、浮上分離槽内を攪拌することを特徴とする請求項1記載の汚泥の濃縮分離方法。 2. The method for concentrating and separating sludge according to claim 1, wherein in the flotation separation step, after the hydrogen peroxide is supplied into the flotation separation tank, the flotation separation tank is stirred.
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