JPH0745039B2 - Wastewater treatment equipment - Google Patents
Wastewater treatment equipmentInfo
- Publication number
- JPH0745039B2 JPH0745039B2 JP27304588A JP27304588A JPH0745039B2 JP H0745039 B2 JPH0745039 B2 JP H0745039B2 JP 27304588 A JP27304588 A JP 27304588A JP 27304588 A JP27304588 A JP 27304588A JP H0745039 B2 JPH0745039 B2 JP H0745039B2
- Authority
- JP
- Japan
- Prior art keywords
- carrier
- reaction tank
- outside
- air lift
- gas
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Lifetime
Links
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Biological Treatment Of Waste Water (AREA)
Description
【発明の詳細な説明】 [発明の目的] (産業上の利用分野) 本発明は、有機物を含む廃水を処理する廃水処理装置に
係わり、特に廃水処理に伴って発生する担体表面の過剰
生物膜を除去する担体再生手段を改良した廃水処理装置
に関する。Description: [Object of the invention] (Field of industrial application) The present invention relates to a wastewater treatment apparatus for treating wastewater containing organic substances, and in particular, an excess biofilm on the surface of a carrier generated in association with the wastewater treatment. The present invention relates to a wastewater treatment device having improved carrier regenerating means for removing water.
(従来の技術) 従来のこの種の廃水処理装置は、第3図に示すように廃
水1を一旦調整槽2に導き、ここで廃水1から汚泥3を
沈降分離し、上側の上澄液がポンプ4により反応槽5に
送られる。この反応槽5の内部には砂,活性炭,アンス
ラサイト等の如き比重が1よりも大きい担体6が適宜な
量だけ投入され、かつ、反応槽5の縦方向にそってエア
リフト管7が立設されている。この反応槽5には外部の
加圧空気源8から反応槽内底部に設置される散気具9に
空気が供給され、これによって散気具8から発生する気
泡10で担体6を流動させながら担体表面に形成されてい
る好気性微生物で廃水中に含まれる有機物を除去した
後、この処理水11を反応槽5から河川に放流する。(Prior Art) In the conventional wastewater treatment apparatus of this type, as shown in FIG. 3, the wastewater 1 is once guided to a regulating tank 2, where sludge 3 is settled and separated from the wastewater 1, and the upper supernatant liquid It is sent to the reaction tank 5 by the pump 4. An appropriate amount of a carrier 6 having a specific gravity of more than 1 such as sand, activated carbon, anthracite, etc. is charged into the reaction tank 5 and an air lift pipe 7 is provided upright along the longitudinal direction of the reaction tank 5. Has been done. Air is supplied to the reaction vessel 5 from an external pressurized air source 8 to an air diffuser 9 installed at the bottom of the reaction vessel, whereby air bubbles 10 generated from the air diffuser 8 cause the carrier 6 to flow. After the organic substances contained in the wastewater are removed by the aerobic microorganisms formed on the surface of the carrier, the treated water 11 is discharged from the reaction tank 5 to the river.
ところで、上記廃水処理に伴って担体6の表面に生物膜
12が形成されるが、この生物膜12が過剰に形成されると
処理効率が著しく低下する。そこで、反応槽5上部の気
液分離筒13内側からポンプ等の輸送手段14で過剰な生物
膜12の堆積される担体6を採取して再生機構15に送り、
撹拌装置によりここで攪拌して過剰の生物膜12を強制剥
離し、この剥離された生物膜12を廃水ラインから再度調
整槽2へ送り、一方、生物膜12の剥離された担体6は再
生機構15から管体16を通って再び気液分離筒13を介して
反応槽5内部へ返還する構成となっている。By the way, a biofilm is formed on the surface of the carrier 6 along with the above wastewater treatment.
12 is formed, but if this biofilm 12 is excessively formed, the treatment efficiency is significantly reduced. Therefore, the carrier 6 on which the excess biofilm 12 is deposited is collected from the inside of the gas-liquid separation cylinder 13 above the reaction tank 5 by the transportation means 14 such as a pump and sent to the regeneration mechanism 15,
The excess biofilm 12 is forcibly peeled off by stirring with a stirring device, and the peeled biofilm 12 is sent again from the wastewater line to the adjusting tank 2, while the carrier 6 from which the biofilm 12 has been peeled off is regenerated by a regeneration mechanism. It is configured to return from 15 to the inside of the reaction tank 5 through the pipe body 16 and the gas-liquid separation cylinder 13 again.
(発明が解決しようとする課題) しかし、以上述べた従来の担体再生手段は、輸送手段14
であるポンプにより担体6がくだかれ、あるいは再生機
構15の攪拌処理時に担体6どうしがぶつかり合って、担
体6の損傷が非常に激しい。このため、比較的短い一定
期間ごとに全部の担体6を交換したり、あるいは担体6
の一部を補充したりする必要がある。また、再生機構15
で再生された担体6は管体16を通って反応槽5に送られ
るが、このとき再生機構15や管体16の流路が担体6によ
って閉塞されて度々トラブルが発生する等,実用面での
難点があった。(Problems to be Solved by the Invention) However, the above-described conventional carrier regenerating means is the transportation means 14
The carrier 6 is scraped by the pump, or the carriers 6 collide with each other during the stirring process of the regeneration mechanism 15, and the carrier 6 is extremely damaged. For this reason, all the carriers 6 may be replaced or the carriers 6 may be replaced at relatively constant intervals.
It is necessary to replenish a part of In addition, the playback mechanism 15
The carrier 6 regenerated in step 1 is sent to the reaction tank 5 through the pipe body 16. At this time, the regeneration mechanism 15 and the flow path of the pipe body 16 are blocked by the carrier 6 and troubles frequently occur. There was a drawback.
本発明は上記不具合を改善するためになされたもので、
担体を損傷させずに担体から容易に生物膜を除去し得、
また剥離された生物膜を含む廃水を適切に排出する廃水
処理装置を提供することを目的とする。The present invention has been made to improve the above problems,
Biofilm can be easily removed from the carrier without damaging the carrier,
Another object of the present invention is to provide a wastewater treatment device that appropriately discharges the wastewater containing the separated biofilm.
[発明の構成] (課題を解決するための手段) 本発明は、上記課題を解決するために、上部側反応部か
ら上部側沈澱部にかけてエアリフト管およびこのエアリ
フト管上部外側から上側に伸びる気液分離筒の順序で配
置された反応槽を有し、外部より前記反応槽のエアリフ
ト管内側へ送り込んだ気泡で比重が1よりも大きい担体
を流動させながら担体表面の好気性微生物で被処理水を
処理し、その処理水を気液分離筒の外側に設けた越流溝
から反応槽外部へ放出し、かつ、処理結果の懸濁物を越
流溝下部の前記沈澱部に沈澱させて前記反応槽外部へ放
出する廃水処理装置において、上部断面積が下部断面積
よりも小さい異径型の前記気液分離筒を用い、かつ、前
記処理水の放出ラインを開閉する開閉弁を設け、この開
閉弁を閉じて反応槽内部の液面を前記気液分離筒上部の
小面積部まで上げ、この小面積部で前記気泡の集中,消
失等による乱流を起こして前記担体表面に堆積する過剰
な生物膜を除去する廃水処理装置である。[Structure of the Invention] (Means for Solving the Problems) In order to solve the above-mentioned problems, the present invention provides an air lift pipe from the upper reaction part to the upper precipitation part, and a gas-liquid extending upward from the outside of the upper part of the air lift pipe. It has a reaction tank arranged in the order of a separating cylinder, and while the carrier having a specific gravity of more than 1 is made to flow by the bubbles sent from the outside into the air lift pipe of the reaction tank, the water to be treated is treated with aerobic microorganisms on the surface of the carrier. After the treatment, the treated water is discharged to the outside of the reaction tank through the overflow groove provided outside the gas-liquid separation cylinder, and the suspension of the treatment result is precipitated in the settling section below the overflow groove to carry out the reaction. In a wastewater treatment device that discharges to the outside of the tank, a gas-liquid separation cylinder of different diameter type with an upper cross-sectional area smaller than the lower cross-sectional area is used, and an opening / closing valve for opening and closing the discharge line of the treated water is provided. Close the valve and inside the reaction tank A wastewater treatment device that raises the liquid surface to a small area above the gas-liquid separation cylinder and removes excess biofilm accumulated on the surface of the carrier by causing turbulence due to concentration and disappearance of the bubbles in this small area. Is.
また、本発明は、少なくとも前記越流溝に対応する反応
槽位置から出力するラインに常開用開閉弁および第1の
常閉用開閉弁を設け、また懸濁物の沈澱する前記沈澱部
に対応する前記反応槽位置から出力するラインに第2の
常閉用開閉弁を設け、前記担体からの過剰生物膜除去時
および排泥時,常開用開閉弁を閉とし、第1および第2
の常閉用開閉弁を必要な時間開とし、これら常閉用開閉
弁から流出する液体等を同一ラインまたは懸濁状態に応
じて異なるラインに放出する構成である。Further, according to the present invention, at least a normally-opening on-off valve and a first normally-closing on-off valve are provided in a line which outputs from a reaction tank position corresponding to the overflow groove, and the suspension is settled at the settling section. A second normally-closed on-off valve is provided in the line that outputs from the corresponding reaction tank position, and the normally-opened on-off valve is closed when excess biofilm is removed from the carrier and when sludge is discharged.
The normally closed on-off valves are opened for a required time, and the liquid and the like flowing out from these normally closed on-off valves are discharged to the same line or different lines depending on the suspension state.
(作用) 従って、本発明は以上のような手段を講じたことによ
り、請求項第1項においては、外部から反応槽底部に空
気を送給すると、その気泡がエアリフト管の内部を通っ
て上昇するが、このとき気泡によって担体が上昇流動し
ながら担体表面の好気性微生物により被処理水を処理す
る。そのうち、処理水は開状態にある開閉弁を通って外
部に放出され、一方、懸濁物は沈澱部に沈澱する。そし
て、廃水処理に伴って担体に過剰に生物膜が形成された
とき、開閉弁を閉じて反応槽内の液面を気泡分離筒の下
部大面積部から上部小面積部まで上昇させる。そうする
と、その小面積部で気泡の集中,消失等によりその下部
側で乱流が発生し、これにより担体表面から生物膜が容
易に剥離する。(Operation) Therefore, according to the present invention, by taking the means as described above, in the first aspect of the invention, when air is supplied from the outside to the bottom of the reaction tank, the bubbles rise through the inside of the air lift pipe. However, at this time, the water to be treated is treated by the aerobic microorganisms on the surface of the carrier while the carrier moves upward due to the bubbles. Among them, the treated water is discharged to the outside through the open / close valve, while the suspension is settled in the settling section. Then, when the biofilm is excessively formed on the carrier due to the wastewater treatment, the on-off valve is closed to raise the liquid level in the reaction tank from the large area at the lower part to the small area at the upper part of the bubble separation tube. Then, turbulence is generated on the lower side of the small area due to concentration and disappearance of air bubbles, which easily separates the biofilm from the surface of the carrier.
次に、請求項第2項では、担体表面の過剰な生物膜の除
去時および排泥時、越流溝に対応する反応槽位置からの
出力ラインの常開用開閉弁を閉とすると、反応槽内の液
面が気泡分離筒の下部大面積部から上部小面積部まで上
昇し、ここで気泡の集中および消失によって乱流が発生
し、担体表面から生物膜が剥離する。その後、前記越流
溝および沈澱部に対応する反応槽位置の出力ラインの常
閉用開閉弁を時間を異ならせて開とすると、生物膜を含
む懸濁液と懸濁物を分けて常閉用開閉弁を通すと懸濁状
態に応じて異なるラインに放出することができる。Next, according to claim 2, when the excessive biofilm on the surface of the carrier is removed and the sludge is discharged, when the normally open on-off valve of the output line from the reaction tank position corresponding to the overflow groove is closed, The liquid level in the tank rises from the large area in the lower part to the small area in the upper part of the bubble separation cylinder, where turbulent flow occurs due to the concentration and disappearance of the bubbles, and the biofilm separates from the carrier surface. After that, when the normally-closed on-off valve of the output line at the reaction tank position corresponding to the overflow groove and the sedimentation part is opened at different times, the suspension containing the biofilm and the suspension are normally closed separately. It can be discharged to different lines depending on the suspended state through the on-off valve.
(実施例) 以下、本発明の実施例について図面を参照して説明す
る。第1図は本発明の一実施例を示す構成図であって、
この装置は管路20を通ってくる廃水21を一時貯留して汚
泥22を沈降分離する調整槽23と、この調整槽23の底部に
沈降された汚泥22を開閉弁24を介して取込んだ後同様に
一時貯留して汚泥25aと上澄液25bとに分離し、上澄液25
bをポンプ26にて前記管路20へ返送し、かつ、汚泥25aを
開閉弁27を通して外部に排出する濃縮槽28と、ポンプ29
より送られてくる前記調整槽23内の上澄液,つまり廃水
を好気性微生物により処理する反応系30と、この反応系
30による処理によって得られた処理水および懸濁物等を
排出制御する排出制御手段50とによって構成されてい
る。(Example) Hereinafter, the Example of this invention is described with reference to drawings. FIG. 1 is a block diagram showing an embodiment of the present invention,
This device took in via an on-off valve 24 an adjusting tank 23 for temporarily storing the wastewater 21 coming through the pipeline 20 and settling and separating the sludge 22, and the sludge 22 settling at the bottom of the adjusting tank 23. After that, it is temporarily stored and separated into sludge 25a and supernatant 25b.
The boil is returned to the pipe 20 by the pump 26, and the sludge 25a is discharged to the outside through the opening / closing valve 27, and the pump 29.
The reaction system 30 for treating the supernatant liquid in the adjusting tank 23, that is, the waste water, which is sent from the aerobic microorganisms, and the reaction system
The discharge control means 50 controls the discharge of the treated water and the suspension obtained by the treatment of 30.
前記反応系30は、中間部分に上側方向に広角となるロー
ト部31aを持ち、そのロート部31aを挟んで下側および上
側に筒状部31b,31cを形成する有底筒状の反応槽31が設
けられ、この反応槽31の内底部には円板状の散気具32が
設置され、また反応槽31内部で下側筒状部31bからロー
ト部31aにかけてエアリフト管33およびこのエアリフト
管33の上部外側から所定の隙間をもって覆うように上方
に伸びる気液分離筒34が設けられている。この気液分離
筒34は下部側が大断面積の筒状部34aに形成され、この
筒状部34aの上端部より逆ロート部34bおよび小断面積の
筒状部34cが形成され、いわゆる異径部の気液分離筒34
を構成している。The reaction system 30 has a bottomed cylindrical reaction tank 31 having a funnel portion 31a having a wide angle in an upper direction in an intermediate portion and forming tubular portions 31b and 31c on the lower side and the upper side with the funnel portion 31a interposed therebetween. A disk-shaped air diffuser 32 is installed at the inner bottom of the reaction tank 31, and the air lift pipe 33 and the air lift pipe 33 are provided inside the reaction tank 31 from the lower tubular portion 31b to the funnel portion 31a. A gas-liquid separation cylinder 34 extending upward is provided so as to cover the outside of the upper part with a predetermined gap. The gas-liquid separating cylinder 34 has a lower portion formed into a cylindrical portion 34a having a large cross-sectional area, and an upper end portion of the cylindrical portion 34a is provided with an inverted funnel portion 34b and a cylindrical portion 34c having a small cross-sectional area. Part gas-liquid separation cylinder 34
Are configured.
そして、エアリフト管33内部を含む反応槽31の下側筒状
部31b内部をもって反応部を構成し、一方、ロート部31
a,上側筒状部31c内側から気液分離筒34外側にかけて沈
澱部を構成する。さらに、反応槽31内には砂,活性炭,
アンスラサイト等の比重が1よりも大きい担体35が例え
ば反応部の容積の1〜10%程度投入され、外部の加圧空
気源36から送られてくる空気によって散気具32から発生
する気泡37によって担体35をエアリフト管33内部下側か
ら上側へ流動させ、このとき担体35表面の好気性微生物
によりポンプ29から供給される廃水中に含む有機物を処
理除去し、前記上側筒状部31c下部内側に設けた越流溝3
8から外部へ処理水39を放出する構成となっている。The inside of the lower tubular portion 31b of the reaction tank 31 including the inside of the air lift pipe 33 constitutes the reaction portion, while the funnel portion 31
a, a precipitation part is formed from the inside of the upper tubular part 31c to the outside of the gas-liquid separation tube 34. Furthermore, sand, activated carbon,
A carrier 35 such as anthracite having a specific gravity of more than 1 is charged, for example, about 1 to 10% of the volume of the reaction section, and bubbles 37 generated from the air diffuser 32 by the air sent from the external pressurized air source 36. The carrier 35 is made to flow from the lower side to the upper side inside the air lift pipe 33 by this treatment, and the organic matter contained in the wastewater supplied from the pump 29 is treated and removed by the aerobic microorganisms on the surface of the carrier 35, and the inside of the lower portion of the upper tubular portion 31c Overflow groove 3 provided in
It is configured to release treated water 39 from 8 to the outside.
前記排出制御手段50では、沈澱部に第1のレベルセンサ
51,その上側に第2のレベルセンサ52が配置され、反応
槽31の上側筒状部31cから前記管路20へ管路53が接続さ
れ、また越流溝38に対応する反応槽31の外側位置よりパ
ラレルに常開用開閉弁54および常閉用開閉弁55を介して
それぞれ処理水排出ライン56および前記管路20へ接続さ
れ、さらに沈澱部に対応する反応槽31の外側位置つまり
ロート部31aより常閉用開閉弁57を介して前記管路20ま
たは図示点線の如き濃縮槽28へ接続されている。前記レ
ベルセンサ51,52および各開閉弁54,55,57は制御部58に
接続されている。この制御部58は、通常運転時,担体か
らの生物膜除去時等に応じてレベルセンサ51,52の出力
を受けながら各開閉弁54,5,57等を所定時間開閉制御す
る機能をもっている。In the discharge control means 50, the first level sensor is provided at the precipitation portion.
51, a second level sensor 52 is arranged on the upper side thereof, a pipe 53 is connected from the upper cylindrical portion 31c of the reaction tank 31 to the pipe 20, and the outside of the reaction tank 31 corresponding to the overflow groove 38. Parallel to the position via the normally open on-off valve 54 and the normally-closed on-off valve 55, respectively connected to the treated water discharge line 56 and the pipe line 20, and further outside the reaction tank 31 corresponding to the precipitation part, that is, the funnel part. 31a is connected to the conduit 20 or the concentration tank 28 as shown by the dotted line in the drawing through a normally-closed on-off valve 57. The level sensors 51, 52 and the open / close valves 54, 55, 57 are connected to a control unit 58. The control unit 58 has a function of controlling the opening / closing valves 54,5, 57, etc. for a predetermined time while receiving the outputs of the level sensors 51, 52 according to the normal operation, the removal of the biofilm from the carrier, and the like.
次に、以上のように構成された装置の動作について、第
2図を参照しながら通常運転工程、生物膜除去工程、排
泥工程および復帰工程等に分けて説明する。Next, the operation of the apparatus configured as described above will be described separately with reference to FIG. 2 in the normal operation step, the biofilm removal step, the sludge removal step, the restoration step, and the like.
(1) 通常運転工程 この工程は、廃水21中の有機物を除去する工程であっ
て、担体3表面に生物膜40が成長する工程である。先
ず、調整槽23からポンプ29によって廃水である上澄液が
反応槽31に送られてくるが、このとき外部の加圧空気源
36から散気具32を通ってエアリフト管33内側下部に気泡
37を発生させる。そうすると、この気泡37により担体35
がエアリフト管33内部を流動しながら担体表面の好気性
微生物によって廃水中の有機物を処理除去するが、同時
にこの処理中に担体35表面で生物膜40が成長する。この
とき、制御部58からの指令により開閉弁54が開となって
いるので、前記処理によて得られた処理水39は越流溝38
から開閉弁54を通って処理水排出ライン56から排出され
る。従って、この通常運転時,反応槽31の液面は異径型
気液分離筒34の大面積筒状部34aに位置する越流溝38で
規制される越流面となっている。(1) Normal operation step This step is a step of removing organic matter in the wastewater 21, and is a step of growing the biofilm 40 on the surface of the carrier 3. First, the supernatant liquid, which is waste water, is sent from the adjusting tank 23 to the reaction tank 31 by the pump 29. At this time, an external pressurized air source is used.
Air bubbles from 36 through the air diffuser 32 to the inside lower part of the air lift pipe 33
Raise 37. Then, the bubbles 37 cause the carrier 35
The organic substances in the wastewater are treated and removed by the aerobic microorganisms on the surface of the carrier while flowing inside the air lift pipe 33, and at the same time, the biofilm 40 grows on the surface of the carrier 35 during this treatment. At this time, since the on-off valve 54 is opened by the command from the control unit 58, the treated water 39 obtained by the above-mentioned treatment is the overflow groove 38.
Is discharged from the treated water discharge line 56 through the on-off valve 54. Therefore, during this normal operation, the liquid surface of the reaction tank 31 is an overflow surface regulated by the overflow groove 38 located in the large area tubular portion 34a of the different-diameter type gas-liquid separation tube 34.
一方、この通常運転時,反応槽31内部ではエアリフト管
33内部で気泡37が上向方向に移動し、それに伴って担体
35も上昇流動する。そして、気泡37は気液分離筒34の大
面積筒状部34aで消失する。その結果、担体35はエアリ
フト管33の上端を越えてエアリフト管外側に下降してい
く。このように反応槽31では充分な攪拌と酸素の供給が
行われ、廃水中の有機物を食物とする好気性微生物が増
殖し、担体表面にはこれら好気性微生物による生物膜40
が徐々に成長する。また、沈澱部では、反応部内から上
昇する懸濁液を含む生物膜40,浮遊微生物などの懸濁物4
1が分離浮遊し、そのうち上澄液が越流溝38から処理水3
0として排出される。On the other hand, during this normal operation, the air lift pipe is installed inside the reaction tank 31.
33 Bubbles 37 move upwards inside 33
35 also rises. Then, the bubbles 37 disappear in the large area tubular portion 34a of the gas-liquid separation tube 34. As a result, the carrier 35 goes over the upper end of the air lift pipe 33 and descends to the outside of the air lift pipe. Thus, in the reaction tank 31, sufficient agitation and oxygen supply are performed, aerobic microorganisms that feed on the organic matter in the waste water grow, and the biofilm formed by these aerobic microorganisms on the carrier surface.
Grows gradually. In the settling section, the biofilm 40 containing the suspension rising from the reaction section, the suspended solids such as suspended microorganisms 4
1 separates and floats, and the supernatant liquid from the overflow groove 38 is treated water 3
Emitted as 0.
(2) 生物膜除去工程 この工程は、担体35の表面に過剰に成長した生物膜40を
定期的に剥離する工程であって、制御部58では所定の日
時例えばステップS1に示す如く毎日23時00分に達したが
否かを判断し、23時00分に達したとき開閉弁54を閉じる
(ステップS2)。この開閉弁54を閉じてもポンプ29が稼
働しているので、反応槽31内の液面は上昇し、その液面
がレベルセンサ52に達したとき制御部58内のタイマ(図
示せず)が起動する(ステップS3,S4)。このタイマが
起動して所定時間t1を経過するまで液面が徐々に上昇し
ていく。このとき、反応槽31内の液体は管路53を通って
調整槽23に送られる。(2) Biofilm removal step This step is a step of periodically peeling off the biofilm 40 excessively grown on the surface of the carrier 35, and the control section 58 sets a predetermined date and time, for example, every day at 23:00 as shown in step S1. It is determined whether or not the time has reached 00, and when it reaches 23:00, the on-off valve 54 is closed (step S2). Since the pump 29 is operating even when the on-off valve 54 is closed, the liquid level in the reaction tank 31 rises, and when the liquid level reaches the level sensor 52, a timer (not shown) in the control unit 58. Is activated (steps S3, S4). The liquid level gradually rises until this timer is activated and a predetermined time t1 elapses. At this time, the liquid in the reaction tank 31 is sent to the adjustment tank 23 through the conduit 53.
しかして、反応槽31の液面の上昇に伴い、その液面が気
液分離筒34の大面積筒状部34aから逆ロート部34bを通っ
て小面積筒状部34cへ移行する。その結果、エアリフト
管33内部の下側から上昇する気泡37が小面積筒状部34c
で集中しながら気泡37の消失を繰返し、逆ロート部34b
およびその下側で激しく乱流が発生する。その結果、担
体35表面の生物膜40には気泡38の集中および乱流を受け
て大きな剪断力が作用し、担体35から生物膜40が容易に
剥離する。この剥離した生物膜40は沈澱部の下部に懸濁
物40と共に堆積し、一方、再生された担体35は反応部内
に自動回収される。沈澱部では懸濁物41の増加と同時に
上澄液の濁度の上昇(懸濁化)が生ずる。Then, as the liquid level in the reaction tank 31 rises, the liquid level moves from the large-area tubular portion 34a of the gas-liquid separation tube 34 to the small-area tubular portion 34c through the reverse funnel portion 34b. As a result, the bubbles 37 rising from the lower side inside the air lift pipe 33 are generated in the small area tubular portion 34c.
Repeatedly disappearing bubbles 37 while concentrating with the reverse funnel 34b
And violent turbulence is generated underneath. As a result, the biofilm 40 on the surface of the carrier 35 is subjected to a large shearing force due to the concentration and turbulence of the bubbles 38, and the biofilm 40 is easily separated from the carrier 35. The separated biofilm 40 is deposited with the suspension 40 in the lower part of the precipitation part, while the regenerated carrier 35 is automatically collected in the reaction part. At the settling point, the suspension 41 increases and the turbidity of the supernatant increases (suspends).
(3) 排泥工程 この工程は、上記(2)の工程で生じた沈澱部の上層懸
濁液と低層懸濁物41を廃液として排出する工程である。
具体的には、ステップS5に示す如くタイマが所定時間t1
を経過したか否かを判断し、所定時間t1を経過したと
き、制御部58からの指令により開閉弁54を閉じた状態で
先ず開閉弁55を開くと共にタイマを起動する(ステップ
S6)。ここで、開閉弁55を開くと、沈澱部の上層懸濁液
が開閉弁55を通って調整槽23に送られる。そして、この
懸濁液の排出により、液面は越流溝38まで,つまり気液
分離筒34の小面積筒状部34cから大面積筒状部34aまで下
降するので、乱流がなくなって生物膜40の剥離作用が停
止する。しかる後、前記タイマがステップS7の如く所定
時間t2を経過すると、開閉弁55を閉じ、開閉弁57を開と
する(ステップS8)。そうすると、沈澱部の下層懸濁物
41が開閉弁57を通って調整槽23または濃縮槽28に送られ
る。通常,この懸濁物41は汚泥が濃縮状態にあるので、
濃縮槽28へ送るのが望ましい。このようにして懸濁物41
を排出すると、反応槽31内の液面が更に下降するが、こ
のとき制御部58が前記レベルセンサ51の出力を監視して
いる。(3) Sludge discharge step This step is a step of discharging the upper layer suspension and the lower layer suspension 41 of the precipitation portion generated in the above step (2) as waste liquid.
Specifically, as shown in step S5, the timer is set to the predetermined time t1.
When a predetermined time t1 has elapsed, the open / close valve 55 is first opened while the open / close valve 54 is closed by a command from the control unit 58, and a timer is started (step
S6). Here, when the opening / closing valve 55 is opened, the upper layer suspension of the precipitation portion is sent to the adjusting tank 23 through the opening / closing valve 55. Then, due to the discharge of the suspension, the liquid surface descends to the overflow groove 38, that is, from the small area tubular portion 34c of the gas-liquid separation tube 34 to the large area tubular portion 34a, so that the turbulent flow is eliminated and the organism The peeling action of the film 40 stops. Thereafter, when the timer elapses a predetermined time t2 as in step S7, the opening / closing valve 55 is closed and the opening / closing valve 57 is opened (step S8). Then, the lower suspension of the precipitation part
41 is sent to the adjustment tank 23 or the concentration tank 28 through the opening / closing valve 57. Usually, this suspension 41 has sludge in a concentrated state,
It is desirable to send it to the concentration tank 28. In this way suspension 41
When is discharged, the liquid level in the reaction tank 31 is further lowered, but at this time, the control unit 58 monitors the output of the level sensor 51.
(4) 復帰工程 ここで、制御部58は反応槽31の液面がレベルセンサ51の
出力から所定レベルに達したと判断すると(ステップS
9)、前記開閉弁57を閉じると同時に開閉弁54を開く
(ステップS10)。このとき、ポンプ29が稼働している
ので、反応槽31の液面が徐々に上昇して越流溝38に達す
ると上記通常運転工程に移行する。従って、この工程は
沈澱部の上層を清澄化する工程である。(4) Returning Step Here, the control unit 58 determines that the liquid level of the reaction tank 31 has reached a predetermined level from the output of the level sensor 51 (step S
9), the opening / closing valve 57 is closed and at the same time the opening / closing valve 54 is opened (step S10). At this time, since the pump 29 is operating, when the liquid level of the reaction tank 31 gradually rises and reaches the overflow groove 38, the above-mentioned normal operation process is started. Therefore, this step is a step of clarifying the upper layer of the precipitation part.
従って、以上のような実施例の構成によれば、下部側を
大面積筒状部34a,上部側を小面積筒状部34cとし、担体3
5表面の過剰生物膜の除去時,反応槽31の液面を上記大
面積筒状部34aから小面積筒状部34cに移行させることに
より、散気具32からの気泡37が小面積筒状部34cで集中
化しつつ消泡動作を繰返し、かつ、その下部側で乱流が
発生し、これら気泡37の集中,消泡および乱流等によっ
て担体35表面より生物膜40を容易に剥離できる。しか
も、気液分離筒34は単に異径型とする形態であるので、
非常に簡単で、かつ、コスト的に安価な構成にして生物
膜40を剥離することが可能である。また、生物膜40の剥
離された担体35はそのまま反応部内に回収されるので、
従来のように輸送手段14や再生機構15によって担体35が
くだかれて損傷したり、担体35により管路が閉塞すると
いったトラブルがなくなり、全く元の大きさの状態で担
体35を再生できる。Therefore, according to the configuration of the above embodiment, the lower side is the large area tubular portion 34a, the upper side is the small area tubular portion 34c, the carrier 3
5 When removing the excess biofilm on the surface, by moving the liquid surface of the reaction tank 31 from the large-area tubular portion 34a to the small-area tubular portion 34c, the bubbles 37 from the air diffuser 32 have a small-area tubular shape. The defoaming operation is repeated while concentrating at the portion 34c, and turbulent flow is generated on the lower side thereof, and the biofilm 40 can be easily separated from the surface of the carrier 35 by the concentration, defoaming, turbulent flow, etc. of the bubbles 37. Moreover, since the gas-liquid separation cylinder 34 is simply a different diameter type,
The biofilm 40 can be peeled off in a very simple and inexpensive structure. Further, since the carrier 35 from which the biofilm 40 has been peeled off is directly recovered in the reaction section,
The carrier 35 can be regenerated in a completely original size without the trouble that the carrier 35 is broken and damaged by the transportation means 14 and the regenerating mechanism 15 and the pipeline is blocked by the carrier 35 unlike the conventional case.
さらに、反応槽31の液面を上昇させた後、各開閉弁55,5
7を所定の順序で開きながら外部に排出するので、沈澱
部の上層懸濁液と下層懸濁物とを分けて排出することが
でき、しかも調整槽23および濃縮槽28に各別に送出すれ
ば廃水処理の能率率向上に寄与し、また復帰時には清澄
液の状態で通常運転を再開できる。Furthermore, after raising the liquid level in the reaction tank 31, each on-off valve 55, 5
Since 7 is discharged to the outside while opening in a predetermined order, the upper layer suspension and the lower layer suspension of the precipitation part can be separately discharged, and if they are separately sent to the adjusting tank 23 and the concentration tank 28, It contributes to the improvement of the efficiency of wastewater treatment, and normal operation can be resumed in the clear liquid state when returning.
なお、上記実施例では円筒形の反応槽31を用いたが、特
に断面形状を限定するものではない。また、気液分離筒
34は中間部に逆ロート部34bを設けたが、大面積筒状部3
4aと小面積筒状部34cだけの形状でもよく、あるいは上
部を小面積筒状部34cとし、その下端部に逆ロート部34b
だけを設けた構成でもよい。その他、本発明はその要旨
を逸脱しない範囲で種々変形して実施できる。Although the cylindrical reaction tank 31 is used in the above embodiment, the sectional shape is not particularly limited. Also, a gas-liquid separation cylinder
The reverse funnel 34b is provided in the middle of the 34, but the large area tubular portion 3
4a and the small area tubular portion 34c may be formed alone, or the upper portion may be the small area tubular portion 34c and the reverse funnel portion 34b may be provided at the lower end thereof.
It is also possible to use only the structure. In addition, the present invention can be modified in various ways without departing from the scope of the invention.
[発明の効果] 以上説明したように本発明によれば次のような種々の効
果を奏する。[Effects of the Invention] As described above, according to the present invention, the following various effects are achieved.
先ず、請求項1においては、簡単な構成で担体表面から
生物膜を除去でき、しかも反応槽内で生物膜を除去する
ことが可能であり、その再生された担体はそのまま反応
部で回収できるので従来のように担体を損傷させずに再
生できる。First, in claim 1, the biofilm can be removed from the surface of the carrier with a simple structure, and further, the biofilm can be removed in the reaction tank, and the regenerated carrier can be directly recovered in the reaction section. It can be regenerated as before without damaging the carrier.
次に、請求項2では、担体から剥離され生物膜および懸
濁物等を適切に排出でき、かつ、懸濁状態に応じて適切
に仕分けして排出できることから廃水処理の能率向上に
も大きく貢献させることができる。Next, according to claim 2, the biofilm and the suspended matter, which are separated from the carrier, can be appropriately discharged, and can be appropriately sorted and discharged according to the suspended state, which greatly contributes to the improvement of the efficiency of wastewater treatment. Can be made.
第1図は本発明に係わる廃水処理装置の一実施例を示す
構成図、第2図は第1図の装置の全体動作を説明する流
れ図、第3図は従来装置の構成図である。 21……廃水、23……調整槽、28……濃縮槽、30……反応
系、31……反応槽、32……散気具、33……エアリフト
管、34……気液分離筒、34a……大面積筒状部、34b……
逆ロート部、34c……小面積筒状部、35……担体、37…
…気泡、38……越流溝、39……処理液、40……生物膜、
41……懸濁物、50……排出制御手段、51,52……レベル
センサ、54,55,57……開閉弁、58……制御部。FIG. 1 is a block diagram showing an embodiment of a wastewater treatment apparatus according to the present invention, FIG. 2 is a flow chart for explaining the overall operation of the apparatus of FIG. 1, and FIG. 3 is a block diagram of a conventional apparatus. 21 …… waste water, 23 …… adjustment tank, 28 …… concentration tank, 30 …… reaction system, 31 …… reaction tank, 32 …… air diffuser, 33 …… air lift pipe, 34 …… gas-liquid separation cylinder, 34a …… Large area tubular part, 34b ……
Reverse funnel part, 34c ... Small area tubular part, 35 ... Carrier, 37 ...
… Bubbles, 38 …… Overflow groove, 39 …… Treatment liquid, 40 …… Biofilm,
41 …… Suspended matter, 50 …… Discharge control means, 51, 52 …… Level sensor, 54, 55, 57 …… Open / close valve, 58 …… Control section.
Claims (2)
アリフト管およびこのエアリフト管上部外側から上側に
伸びる気液分離筒の順序で配置された反応槽を有し、外
部より前記反応槽のエアリフト管内側へ送り込んだ気泡
で比重が1よりも大きい担体を流動させながら担体表面
の好気性微生物で被処理水を処理し、その処理水を気液
分離筒の外側に設けた越流溝から反応槽外部へ放出し、
かつ、処理結果の懸濁物を越流溝下部の前記沈澱部に沈
澱させて前記反応槽外部へ放出する廃水処理装置におい
て、 上部断面積が下部断面積よりも小さい異径型の前記気液
分離筒を用い、かつ、前記処理水の放出ラインを開閉す
る開閉弁を設け、この開閉弁を閉じて反応槽内部の液面
を前記気液分離筒上部の小面積部まで上げ、この小面積
部で前記気泡の集中,消泡等による乱流を起こして前記
担体表面に堆積する過剰な生物膜を除去することを特徴
とする廃水処理装置。1. A reaction vessel having an air lift pipe and a gas-liquid separation cylinder extending from the upper outer side to the upper side of the air lift pipe from the lower side reaction section to the upper side precipitation section, and the air lift of the reaction tank from the outside. The treated water is treated with aerobic microorganisms on the surface of the carrier while flowing the carrier with a specific gravity of more than 1 by the bubbles sent to the inside of the pipe, and the treated water reacts from the overflow groove provided outside the gas-liquid separation cylinder. Released to the outside of the tank,
Further, in the wastewater treatment device for precipitating the suspension of the treatment result in the precipitation part in the lower part of the overflow groove and discharging it to the outside of the reaction tank, the gas-liquid of different diameter type in which the upper cross-sectional area is smaller than the lower cross-sectional area. A separation cylinder is used and an on-off valve for opening and closing the treated water discharge line is provided, and the on-off valve is closed to raise the liquid level inside the reaction tank to a small area above the gas-liquid separation cylinder. A wastewater treatment device, characterized in that a turbulent flow due to concentration, defoaming, etc. of the bubbles is caused in a portion to remove an excessive biofilm deposited on the surface of the carrier.
アリフト管およびこのエアリフト管上部外側から上側に
伸びる気液分離筒の順序で配置された反応槽を有し、外
部より前記反応槽のエアリフト管内側へ送り込んだ気泡
で比重が1よりも大きい担体を流動させながら担体表面
の好気性微生物で被処理水を処理し、その処理水を気液
分離筒の外側に設けた越流溝から反応槽外部へ放出し、
かつ、処理結果の懸濁物を越流溝下部の前記沈澱部に沈
澱させて前記反応槽外部に放出する廃水処理装置におい
て、 少なくとも前記越流溝に対応する反応槽位置から出力す
るラインに常開用開閉弁および第1の常閉用開閉弁を設
け、また懸濁物の沈澱する前記沈澱部に対応する前記反
応槽位置から出力するラインに第2の常閉用開閉弁を設
け、前記担体表面の過剰生物膜除去時および排泥時,常
開用開閉弁を閉とし、第1および第2の常閉用開閉弁を
必要な時間開とし、これら常閉用開閉弁から流出する液
体等を同一ラインまたは懸濁状態に応じて異なるライン
に放出することを特徴とする廃水処理装置。2. An air lift pipe having an air lift pipe and a gas-liquid separating cylinder extending from the upper outside of the air lift pipe to the upper side in this order from the lower side reaction part to the upper side precipitation part, and the air lift of the reaction tank from the outside. The treated water is treated with aerobic microorganisms on the surface of the carrier while flowing the carrier with a specific gravity of more than 1 by the bubbles sent to the inside of the pipe, and the treated water reacts from the overflow groove provided outside the gas-liquid separation cylinder. Released to the outside of the tank,
In addition, in the wastewater treatment device that precipitates the suspension of the treatment result in the settling section at the lower part of the overflow groove and discharges it to the outside of the reaction tank, at least in the line that outputs from the reaction tank position corresponding to the overflow groove. An opening and closing valve for opening and a first closing valve for normally closing are provided, and a second opening and closing valve for normally closing is provided in a line which outputs from the reaction tank position corresponding to the sedimentation portion where the suspension precipitates. Liquid that flows out from these normally closed on-off valves by closing the normally-opening on-off valves and removing the first and second normally-closing on-off valves for the required time when removing excess biofilm on the carrier surface and during sludge discharge And the like are discharged to the same line or different lines depending on the state of suspension.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP27304588A JPH0745039B2 (en) | 1988-10-31 | 1988-10-31 | Wastewater treatment equipment |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP27304588A JPH0745039B2 (en) | 1988-10-31 | 1988-10-31 | Wastewater treatment equipment |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH02122892A JPH02122892A (en) | 1990-05-10 |
| JPH0745039B2 true JPH0745039B2 (en) | 1995-05-17 |
Family
ID=17522396
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP27304588A Expired - Lifetime JPH0745039B2 (en) | 1988-10-31 | 1988-10-31 | Wastewater treatment equipment |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0745039B2 (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2005074357A (en) * | 2003-09-02 | 2005-03-24 | Ngk Insulators Ltd | Membrane washing method in membrane separation activated sludge method |
| EP1852175A4 (en) | 2005-02-25 | 2009-08-05 | Ngk Insulators Ltd | Method of cleaning membrane in membrane separation activated-sludge process |
| CN100406398C (en) * | 2006-08-29 | 2008-07-30 | 华南理工大学 | Sequencing Batch Airlift Circulation Wastewater Biological Treatment Process |
-
1988
- 1988-10-31 JP JP27304588A patent/JPH0745039B2/en not_active Expired - Lifetime
Also Published As
| Publication number | Publication date |
|---|---|
| JPH02122892A (en) | 1990-05-10 |
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