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JP3851385B2 - Wastewater treatment equipment - Google Patents
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JP3851385B2 - Wastewater treatment equipment - Google Patents

Wastewater treatment equipment Download PDF

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Publication number
JP3851385B2
JP3851385B2 JP24769296A JP24769296A JP3851385B2 JP 3851385 B2 JP3851385 B2 JP 3851385B2 JP 24769296 A JP24769296 A JP 24769296A JP 24769296 A JP24769296 A JP 24769296A JP 3851385 B2 JP3851385 B2 JP 3851385B2
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Prior art keywords
filter bed
water
partition plate
aerobic
air
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JP24769296A
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JPH1085786A (en
Inventor
辰彦 鈴木
進 石川
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Maezawa Industries Inc
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Maezawa Industries Inc
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Description

【0001】
【発明の属する技術分野】
本発明は、排水処理装置に関し、詳しくは、嫌気性ろ床の後段に好気性ろ床を組合わせた嫌気・好気ろ床法により排水処理を行う下排水処理施設に適した排水処理装置に関する。
【0002】
【従来の技術】
近年、比較的小規模な下排水処理施設においても、富栄養化防止の上から、窒素,リンの除去を求められる場合が多くなってきている。従来から、小規模な下排水処理施設においては、維持管理が容易なことから、ろ床タイプの生物処理装置が多く用いられており、窒素,リンの除去が求められる場合には、嫌気・好気ろ床法が多く用いられている。
【0003】
図3は、嫌気・好気ろ床法を実施するための従来の排水処理装置の一例を示すもので、嫌気性ろ床1の後段に好気性ろ床2を配置している。流入下水(原水)は、沈砂池設備のみ、あるいは、沈砂池設備と最初沈殿池と組合わせた前処理設備等を介して配管4から嫌気性ろ床1に流入する。この嫌気性ろ床1で嫌気処理された水は、配管5により好気性ろ床2に送られて好気処理され、配管6から処理水槽等に送られるとともに、この処理水の一部は、配管7により循環水(硝化液)として嫌気性ろ床1に戻される。なお、符号8は、好気性ろ床2内に空気(酸素)を導入するための散気装置である。
【0004】
【発明が解決しようとする課題】
上述のように、従来の嫌気・好気ろ床法による排水処理装置は、嫌気性ろ床1と好気性ろ床2とを別々に設けていたため、小規模な下排水処理施設の場合には、小さな処理槽を多数設置することが必要となり、設置面積の増加や施工性の悪化、システムの複雑化等の問題が生じていた。
【0005】
このため、嫌気性ろ床と好気性ろ床とを一つの処理槽内に積層することも提案されているが、この場合は、好気性ろ床の散気や洗浄に対する考慮が不十分で、実用性に難点があった。
【0006】
そこで本発明は、嫌気性ろ床と好気性ろ床とを一つの処理槽に一体化させて設置面積の縮小等を図るとともに、好気性ろ床の散気や洗浄も十分に行うことができる排水処理装置を提供することを目的としている。
【0007】
【課題を解決するための手段】
上記目的を達成するため、本発明の排水処理装置は、嫌気性ろ床と好気性ろ床とを一体構造とした排水処理装置であって、処理槽の下部に嫌気性ろ床部を、上部に好気性ろ床部をそれぞれ配置し、処理槽底部に原水流入部と沈殿汚泥抜取部とを設け、処理槽頂部に処理水排出部と洗浄排水排出部とを設けるとともに、前記嫌気性ろ床部と好気性ろ床部との間を区画板にて区画し、該区画板に集水ノズルを設け、前記区画板の上方に散気手段を、下方に洗浄水導入部と洗浄用空気導入部とをそれぞれ設けた排水処理装置であって、前記集水ノズルは、前記区画板を上下方向に貫通する管体部を有し、該管体部の区画板上面部に、区画板の上方に充填されているろ材が通過しない程度の開口が形成されているストレーナーを設け、区画板の下方の管体部に、上下方向のスリットを設けるととともに該スリットの上方に通孔を設け、該スリットと通孔とにより、前記好気性ろ床部のろ材を空気洗浄する際に各集水ノズルから噴出する空気量を均一にすることを特徴としている。さらに、本発明は、前記原水流入部の前段に加圧浮上分離装置を設けたことを特徴としている。
【0008】
【発明の実施の形態】
以下、本発明を、図面を参照してさらに詳細に説明する。図1は、本発明の排水処理装置を用いた下排水処理施設の一例を示すもので、嫌気・好気ろ床法による排水処理装置11の前段上流に加圧浮上分離装置12を設置した例を示している。
【0009】
排水処理装置11は、処理槽13の下部に嫌気性ろ床部14を、上部に好気性ろ床部15をそれぞれ配置したものであって、処理槽底部には、適当な容積を有する沈殿室13aが形成されるとともに、加圧浮上分離装置12で処理された原水が流入する原水流入管16と沈殿汚泥を抜取るための汚泥抜取管17とが設けられており、処理槽頂部には、処理水を排出する処理水排出管18と、トラフ19を介して洗浄排水を排出する洗浄排水排出管20とが設けられている。また、嫌気性ろ床部14と好気性ろ床部15との間は、集水ノズル21を有する区画板22により区画されており、該区画板22の上部に設けられる支持層23内には散気装置24が設けられ、区画板22の下方には、好気性ろ床部15の洗浄時に洗浄水や空気を導入するための洗浄水導入管25と洗浄用空気導入管26とが設けられている。さらに、処理槽13の頂部と底部との間には、硝化液を循環させるための循環配管27が設けられている。
【0010】
前記区画板22に設けられている集水ノズル21は、図2に示すように、区画板22を上下方向に貫通する管体部21aと、該管体部21aの区画板上面部に設けられたストレーナー21bと、区画板22の下方の管体部21aの下端近傍に設けられた上下方向のスリット21cと、該スリット21cの上方に設けられた通孔21dとを有するものであって、ストレーナー21bには、区画板22の上方に充填されているろ材が通過しない程度の開口が形成されている。この集水ノズル21は、スリット21cと通孔21dとにより、ろ材を空気洗浄する際に各集水ノズル21から噴出する空気量を均一にする機能を備えている。
【0011】
すなわち、好気性ろ床部15の空気洗浄において、洗浄用空気導入管26から区画板22の下方に流入した空気は、集水ノズル21を通って区画板22の上方に噴出する。このとき、空気の大部分は、集水ノズル21の通孔21dから管体部21a内に流入し、残りの空気が、その圧力で区画板22の下方の水面を押し下げ、水面の下降により開口した下部のスリット21cから管体部21a内に流入する。そして、水面の押し下げ量と、スリット21cから管体部21a内に流入する空気量とがバランスした状態となるので、各集水ノズル21のレベルを揃えておくことにより、各集水ノズル21から好気性ろ床部15内に噴出する空気量を一定量にすることができ、均一な空気洗浄を行うことができる。また、僅かにレベル差があっても略均一な噴出量が得られ、さらに、一部にスリット21cに達しないレベル差が生じた場合でも、上部の通孔21dから流入する大部分の空気は、確実に集水ノズル21から好気性ろ床部15内に噴出するので、好気性ろ床部15の全体を十分に空気洗浄することができる。
【0012】
このように、一つの処理槽13内に嫌気性ろ床部14と好気性ろ床部15とを一体的に設けることにより、排水処理装置11における設置面積の縮小や施工性の改善、システムの簡略化等を図ることができる。また、好気性ろ床部の洗浄も効率よく行うことができ、発生する汚泥の処理も簡単に行うことができる。
【0013】
また、前記加圧浮上分離装置12は、周知のように、短時間の処理が可能であること、分離汚泥を高濃度で回収可能であること、原水の汚濁物質濃度の影響を受け難いことなどの特徴を有しているため、排水処理装置11の前段に加圧浮上分離装置12を設けることにより、嫌気性ろ床部14への流入負荷を少なくでき、嫌気性ろ床部14の容量を小さくできるとともに、嫌気性ろ床部14の接触材の閉塞やスカムの発生を少なくできる。さらに、嫌気性ろ床部14で安定した良好な処理を行えるので、好気性ろ床部15における処理性も向上させることができる。
【0014】
流入下水(原水)は、スクリーン28を通って原水槽29に流入した後、水中ポンプ30により配管31を介して加圧浮上分離装置12に送られる。なお、必要に応じて原水槽29に流量調節機能を付加することもできる。加圧浮上分離装置12に送られる原水は、加圧浮上分離装置12への流入部で配管32から供給される加圧空気溶解水と混合され、原水中の懸濁成分は、加圧空気溶解水から発生する微細気泡に付着して見掛けの比重が小さくなり、加圧浮上分離装置12の槽上部に浮上汚泥(フロス)として分離する。この浮上汚泥は、掻取機33により掻取られて経路34から汚泥貯留槽35に送られ、加圧浮上分離装置12の底部に沈殿した汚泥は、経路36から汚泥貯留槽35に送られる。このときの汚泥濃度は3〜5%であり、従来の汚泥濃縮槽における重力濃縮に比較して高濃度である。
【0015】
また、嫌気性ろ床部14及び好気性ろ床部15から発生する汚泥についても、汚泥抜取管17,洗浄排水排出管20により原水槽29に戻し、加圧浮上分離装置12で再び処理することにより、汚泥発生箇所の一本化と高濃度化とを図ることができる。したがって、汚泥発生量がランニングコストに大きく影響する比較的小規模な下排水処理施設では、そのランニングコストを大幅に低減させることができる。
【0016】
また、加圧浮上分離装置12で処理された水の一部は、出口側で配管37に抜取られてポンプ38で加圧され、コンプレッサー39から供給される圧縮空気と混合槽40で混合した後、加圧空気溶解水として前記配管32から原水に供給混合される。
【0017】
このように加圧浮上分離装置12で処理した水は、通常の沈殿処理に比べて懸濁成分の除去率が高いため、嫌気性ろ床部14への流入負荷が少なくなり、その分、嫌気性ろ床部14の容量を小さくすることが可能になる。また、浮上処理では、髪の毛、油分、スカム等の浮上し易い成分を、略完全に除去することができるため、嫌気性ろ床部14での接触材の閉塞やスカムの発生が少なくなる。加えて、嫌気性ろ床部14において安定した良好な処理が可能となることから、嫌気性ろ床部14で処理された水が流入する好気性ろ床部15での処理性も向上する。
【0018】
このように加圧浮上分離装置12で処理されて排水処理装置11に流入する原水は、処理槽13の底部で、循環配管27から流入する硝化液と混合して嫌気性ろ床部14内を上昇し、ここで所定の嫌気処理が行われる。嫌気処理された水は、区画板22の集水ノズル21を通過して好気性ろ床部15内に上昇し、所定の好気処理が行われる。このとき、好気性ろ床部15の下方に設置された散気装置24からは、コンプレッサー41から供給される空気が導入されている。排水処理装置11で嫌気・好気処理された処理水は、処理水排出管18から処理水槽42に送られ、一部の処理水は、循環配管27に抜出されてポンプ43を介して槽底部に循環する。
【0019】
好気性ろ床部15のろ材の洗浄は、洗浄ブロワー44から洗浄用空気導入管26及び集水ノズル21を介して好気性ろ床部15内に空気を導入して空洗を行った後、処理水槽42内の処理水の一部を洗浄水としてポンプ45,洗浄水導入管25を介して導入することにより行われる。この洗浄の際に発生する洗浄排水は、トラフ19から洗浄排水排出管20に流出し、原水槽29に戻される。また、槽底部の汚泥抜取管17から抜取られた汚泥も、洗浄排水と同様に原水槽29に戻されて原水と混合し、再度加圧浮上分離装置12に送られて浮上分離処理される。
【0020】
このように、嫌気性ろ床部14と好気性ろ床部15とを一体化させた排水処理装置11に加圧浮上分離装置12を組合わせることにより、排水処理装置11の効率向上や小型化が図れるとともに、汚泥の回収も効果的に行うことができる。
【0021】
なお、本発明の排水処理装置は、処理槽底部に前述の沈殿室を設けることにより、ある程度の固液分離を行うことができるので、該排水処理装置前段の前記加圧浮上分離装置や通常の重力式沈殿池を省略することも可能である。
【0022】
【発明の効果】
以上説明したように、本発明の排水処理装置によれば、嫌気性ろ床と好気性ろ床とを一つの処理槽に一体化させているので、設置面積の縮小や施工性の改善、システムの簡略化等を図ることができる。また、好気性ろ床部の洗浄も効率よく行うことができ、排水処理効率を大幅に向上させることができる。さらに、前段に加圧浮上分離装置を組合わせることにより、嫌気性ろ床部の流入負荷を少なくでき、処理効率を更に向上させることができる。
【図面の簡単な説明】
【図1】 本発明の排水処理装置を用いた下排水処理施設の一例を示す系統図である。
【図2】 集水ノズルの一例を示す一部断面正面図である。
【図3】 従来の排水処理装置の一例を示す系統図である。
【符号の説明】
11…排水処理装置、12…加圧浮上分離装置、13…処理槽、14…嫌気性ろ床部、15…好気性ろ床部、16…原水流入管、17…汚泥抜取管、18…処理水排出管、19…トラフ、20…洗浄排水排出管、21…集水ノズル、22…区画板、23…支持層、24…散気装置、25…洗浄水導入管、26…洗浄用空気導入管、27…循環配管、29…原水槽、35…汚泥貯留槽、40…混合槽、42…処理水槽
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a wastewater treatment apparatus, and more particularly, to a wastewater treatment apparatus suitable for a sewage treatment facility that performs wastewater treatment by an anaerobic / aerobic filter bed in which an aerobic filter bed is combined with an anaerobic filter bed. .
[0002]
[Prior art]
In recent years, even in a relatively small sewage treatment facility, removal of nitrogen and phosphorus is often demanded for preventing eutrophication. Traditionally, small-scale sewage treatment facilities are easy to maintain, and so filter bed type biological treatment equipment has been used in many cases. The air bed method is often used.
[0003]
FIG. 3 shows an example of a conventional wastewater treatment apparatus for carrying out the anaerobic / aerobic filter bed method, in which an aerobic filter bed 2 is arranged at the subsequent stage of the anaerobic filter bed 1. Inflow sewage (raw water) flows into the anaerobic filter bed 1 from the pipe 4 through only the sedimentation basin equipment or the pretreatment equipment combined with the sedimentation basin equipment and the first sedimentation basin. The water that has been anaerobically treated in the anaerobic filter bed 1 is sent to the aerobic filter bed 2 through the pipe 5 and subjected to aerobic treatment, and is sent from the pipe 6 to a treated water tank or the like. It returns to the anaerobic filter bed 1 as circulating water (nitrification liquid) by the piping 7. Reference numeral 8 denotes an air diffuser for introducing air (oxygen) into the aerobic filter bed 2.
[0004]
[Problems to be solved by the invention]
As described above, the conventional anaerobic / aerobic filter bed wastewater treatment apparatus is provided with the anaerobic filter bed 1 and the aerobic filter bed 2 separately. Therefore, it is necessary to install a large number of small treatment tanks, which causes problems such as an increase in installation area, deterioration in workability, and complexity of the system.
[0005]
For this reason, it has also been proposed to stack anaerobic filter beds and aerobic filter beds in one treatment tank, but in this case, consideration for aeration and cleaning of the aerobic filter bed is insufficient, There was a difficulty in practicality.
[0006]
Therefore, the present invention integrates the anaerobic filter bed and the aerobic filter bed into one treatment tank to reduce the installation area and the like, and can also sufficiently diffuse and wash the aerobic filter bed. It aims to provide a wastewater treatment device.
[0007]
[Means for Solving the Problems]
In order to achieve the above object, the wastewater treatment apparatus of the present invention is a wastewater treatment apparatus in which an anaerobic filter bed and an aerobic filter bed are integrated, and an anaerobic filter bed portion is provided at the lower part of the treatment tank. The aerobic filter bed is disposed at the bottom of the treatment tank, the raw water inflow part and the precipitated sludge extraction part are provided at the bottom of the treatment tank, the treatment water discharge part and the washing drainage discharge part are provided at the top of the treatment tank, and the anaerobic filter bed is provided. between the parts and aerobic basin portion partitioned by Gu drawing board, a water collecting nozzle provided in the compartment drawing board, a diffuser means above the partition plate, the cleaning air introduced washing water introduction portion downwards Each of the water collecting nozzles has a tubular body portion that vertically penetrates the partition plate, and the upper portion of the partition plate is disposed above the partition plate. Provide a strainer with an opening that does not allow the filter medium filled in A vertical slit is provided in the body portion, and a through hole is provided above the slit. When the filter medium of the aerobic filter bed is air-washed by the slit and the through hole, the water is ejected from each water collecting nozzle. It is characterized by uniform air volume . Furthermore, the present invention is characterized in that a pressure levitation separation device is provided in the preceding stage of the raw water inflow portion.
[0008]
DETAILED DESCRIPTION OF THE INVENTION
Hereinafter, the present invention will be described in more detail with reference to the drawings. FIG. 1 shows an example of a sewage treatment facility using the effluent treatment device of the present invention, and an example in which a pressurized flotation separation device 12 is installed upstream from a wastewater treatment device 11 by an anaerobic / aerobic filter bed method. Is shown.
[0009]
The waste water treatment apparatus 11 has an anaerobic filter bed 14 disposed at the lower part of the treatment tank 13 and an aerobic filter bed 15 disposed at the upper part, and a sedimentation chamber having an appropriate volume at the bottom of the treatment tank. 13a is formed, and a raw water inflow pipe 16 into which raw water treated by the pressurized flotation separation apparatus 12 flows and a sludge extraction pipe 17 for extracting the precipitated sludge are provided. A treated water discharge pipe 18 for discharging treated water and a cleaning drainage pipe 20 for discharging cleaning wastewater through a trough 19 are provided. Further, the anaerobic filter bed portion 14 and the aerobic filter bed portion 15 are partitioned by a partition plate 22 having a water collecting nozzle 21, and in the support layer 23 provided on the upper portion of the partition plate 22. A diffuser 24 is provided, and a cleaning water introduction pipe 25 and a cleaning air introduction pipe 26 for introducing cleaning water and air when the aerobic filter bed 15 is cleaned are provided below the partition plate 22. ing. Furthermore, a circulation pipe 27 for circulating the nitrification liquid is provided between the top and bottom of the processing tank 13.
[0010]
As shown in FIG. 2, the water collection nozzle 21 provided in the partition plate 22 is provided on a tubular body portion 21 a penetrating the partition plate 22 in the vertical direction and on an upper surface portion of the partition plate of the tubular body portion 21 a. A strainer 21b, a vertical slit 21c provided in the vicinity of the lower end of the tube portion 21a below the partition plate 22, and a through hole 21d provided above the slit 21c. In 21b, an opening is formed so that the filter medium filled above the partition plate 22 does not pass through. The water collection nozzle 21 has a function of making the amount of air ejected from each water collection nozzle 21 uniform when the filter medium is air-washed by the slit 21c and the through hole 21d.
[0011]
That is, in the air cleaning of the aerobic filter bed 15, the air that has flowed from the cleaning air introduction pipe 26 to the lower side of the partition plate 22 is jetted to the upper side of the partition plate 22 through the water collection nozzle 21. At this time, most of the air flows into the tube body portion 21a from the through hole 21d of the water collecting nozzle 21, and the remaining air pushes down the water surface below the partition plate 22 by the pressure, and opens by lowering the water surface. It flows into the tubular body portion 21a from the lower slit 21c. And since it will be in the state where the amount of pushing down of the water surface and the amount of air which flows in into pipe part 21a from slit 21c are in balance, it is from each water collection nozzle 21 by aligning the level of each water collection nozzle 21. The amount of air ejected into the aerobic filter bed 15 can be made constant, and uniform air cleaning can be performed. Moreover, even if there is a slight level difference, a substantially uniform ejection amount can be obtained, and even if a level difference that does not reach the slit 21c occurs in part, most of the air flowing in from the upper through hole 21d is Since the water collection nozzle 21 surely ejects into the aerobic filter bed 15, the entire aerobic filter bed 15 can be sufficiently washed with air.
[0012]
Thus, by providing the anaerobic filter bed part 14 and the aerobic filter bed part 15 in one processing tank 13, the installation area in the waste water treatment device 11 is reduced, the workability is improved, and the system is improved. Simplification and the like can be achieved. In addition, the aerobic filter bed can be washed efficiently, and the generated sludge can be easily treated.
[0013]
Further, as is well known, the pressurized flotation separation device 12 can be treated in a short time, can collect separated sludge at a high concentration, and is not easily affected by the concentration of pollutants in raw water. Therefore, by providing the pressurized flotation separation device 12 in the previous stage of the waste water treatment device 11, the load flowing into the anaerobic filter bed 14 can be reduced, and the capacity of the anaerobic filter bed 14 can be reduced. While being able to make small, obstruction | occlusion of the contact material of the anaerobic filter bed part 14 and generation | occurrence | production of a scum can be decreased. Furthermore, since the anaerobic filter bed part 14 can perform a stable and good treatment, the processability in the aerobic filter bed part 15 can also be improved.
[0014]
The inflowing sewage (raw water) flows into the raw water tank 29 through the screen 28 and is then sent to the pressurized flotation separation device 12 through the pipe 31 by the submersible pump 30. Note that a flow rate adjusting function can be added to the raw water tank 29 as necessary. The raw water sent to the pressurized flotation separator 12 is mixed with the pressurized air dissolved water supplied from the pipe 32 at the inflow portion to the pressurized flotation separator 12, and the suspended components in the raw water are dissolved in the pressurized air. The apparent specific gravity is reduced by adhering to fine bubbles generated from water, and separated as floating sludge (floss) at the upper part of the tank of the pressurized flotation separation device 12. The levitation sludge is scraped off by the scraper 33 and sent from the path 34 to the sludge storage tank 35, and the sludge precipitated at the bottom of the pressurized levitation separator 12 is sent from the path 36 to the sludge storage tank 35. The sludge density | concentration at this time is 3 to 5%, and is high concentration compared with the gravity concentration in the conventional sludge concentration tank.
[0015]
In addition, sludge generated from the anaerobic filter bed 14 and the aerobic filter bed 15 is returned to the raw water tank 29 through the sludge extraction pipe 17 and the washing drainage discharge pipe 20 and processed again by the pressurized flotation separator 12. Thus, it is possible to achieve a unified sludge generation location and a high concentration. Therefore, in a relatively small sewage treatment facility where the amount of sludge generated greatly affects the running cost, the running cost can be significantly reduced.
[0016]
A part of the water treated by the pressurized flotation separation device 12 is withdrawn into the pipe 37 on the outlet side, pressurized by the pump 38, and mixed with the compressed air supplied from the compressor 39 in the mixing tank 40. Then, it is supplied and mixed into the raw water from the pipe 32 as pressurized air dissolved water.
[0017]
Since the water treated with the pressure flotation separation device 12 in this way has a higher removal rate of suspended components compared to the normal precipitation treatment, the inflow load to the anaerobic filter bed portion 14 is reduced, and anaerobic correspondingly. It is possible to reduce the capacity of the filter bed 14. Further, in the floatation process, components that easily float, such as hair, oil, and scum, can be removed almost completely, so that the contact material blockage and the occurrence of scum in the anaerobic filter bed portion 14 are reduced. In addition, since stable and good treatment is possible in the anaerobic filter bed part 14, the processability in the aerobic filter bed part 15 into which water treated in the anaerobic filter bed part 14 flows is also improved.
[0018]
In this way, the raw water that has been treated by the pressurized flotation separation device 12 and flows into the waste water treatment device 11 is mixed with the nitrating solution flowing from the circulation pipe 27 at the bottom of the treatment tank 13 and flows through the anaerobic filter bed portion 14. It rises and a predetermined anaerobic process is performed here. The water subjected to the anaerobic treatment passes through the water collecting nozzle 21 of the partition plate 22 and rises into the aerobic filter bed portion 15, and a predetermined aerobic treatment is performed. At this time, the air supplied from the compressor 41 is introduced from the air diffuser 24 installed below the aerobic filter bed 15. The treated water that has been subjected to anaerobic / aerobic treatment in the waste water treatment device 11 is sent from the treated water discharge pipe 18 to the treated water tank 42, and a part of the treated water is drawn out to the circulation pipe 27 and passed through the pump 43. Circulate to the bottom.
[0019]
Cleaning of the filter medium of the aerobic filter bed 15 is performed by performing air washing by introducing air from the cleaning blower 44 through the cleaning air introduction pipe 26 and the water collection nozzle 21 into the aerobic filter bed 15. This is performed by introducing a part of the treated water in the treated water tank 42 through the pump 45 and the washing water introduction pipe 25 as washing water. The cleaning wastewater generated during the cleaning flows out from the trough 19 to the cleaning drainage discharge pipe 20 and is returned to the raw water tank 29. Also, the sludge extracted from the sludge extraction pipe 17 at the bottom of the tank is returned to the raw water tank 29 and mixed with the raw water in the same manner as the washing waste water, and is sent again to the pressurized flotation separation device 12 for the flotation separation process.
[0020]
Thus, by combining the wastewater treatment device 11 in which the anaerobic filter bed portion 14 and the aerobic filter bed portion 15 are integrated with the pressurized flotation separation device 12, the efficiency and size reduction of the wastewater treatment device 11 are achieved. In addition, sludge can be collected effectively.
[0021]
In addition, since the wastewater treatment apparatus of the present invention can perform solid-liquid separation to some extent by providing the above-described sedimentation chamber at the bottom of the treatment tank, the pressure flotation separation apparatus in front of the wastewater treatment apparatus or a normal It is also possible to omit the gravity sedimentation basin.
[0022]
【The invention's effect】
As described above, according to the wastewater treatment apparatus of the present invention, the anaerobic filter bed and the aerobic filter bed are integrated into one treatment tank, so that the installation area can be reduced and the workability can be improved. Can be simplified. Moreover, the aerobic filter bed can be washed efficiently, and the wastewater treatment efficiency can be greatly improved. Furthermore, by combining the pressure levitation separator in the previous stage, the inflow load of the anaerobic filter bed can be reduced, and the processing efficiency can be further improved.
[Brief description of the drawings]
FIG. 1 is a system diagram showing an example of a wastewater treatment facility using a wastewater treatment apparatus of the present invention.
FIG. 2 is a partial cross-sectional front view showing an example of a water collection nozzle.
FIG. 3 is a system diagram showing an example of a conventional waste water treatment apparatus.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 11 ... Waste water treatment apparatus, 12 ... Pressure floating separator, 13 ... Treatment tank, 14 ... Anaerobic filter bed part, 15 ... Aerobic filter bed part, 16 ... Raw water inflow pipe, 17 ... Sludge extraction pipe, 18 ... Treatment Water discharge pipe, 19 ... Trough, 20 ... Washing drain discharge pipe, 21 ... Water collecting nozzle, 22 ... Partition plate, 23 ... Support layer, 24 ... Air diffuser, 25 ... Washing water introduction pipe, 26 ... Cleaning air introduction Pipe, 27 ... Circulation piping, 29 ... Raw water tank, 35 ... Sludge storage tank, 40 ... Mixing tank, 42 ... Treated water tank

Claims (2)

嫌気性ろ床と好気性ろ床とを一体構造とした排水処理装置であって、処理槽の下部に嫌気性ろ床部を、上部に好気性ろ床部をそれぞれ配置し、処理槽底部に原水流入部と沈殿汚泥抜取部とを設け、処理槽頂部に処理水排出部と洗浄排水排出部とを設けるとともに、前記嫌気性ろ床部と好気性ろ床部との間を区画板にて区画し、該区画板に集水ノズルを設け、前記区画板の上方に散気手段を、下方に洗浄水導入部と洗浄用空気導入部とをそれぞれ設けた排水処理装置であって、前記集水ノズルは、前記区画板を上下方向に貫通する管体部を有し、該管体部の区画板上面部に、区画板の上方に充填されているろ材が通過しない程度の開口が形成されているストレーナーを設け、区画板の下方の管体部に、上下方向のスリットを設けるととともに該スリットの上方に通孔を設け、該スリットと通孔とにより、前記好気性ろ床部のろ材を空気洗浄する際に各集水ノズルから噴出する空気量を均一にすることを特徴とする排水処理装置。It is a wastewater treatment device that has an anaerobic filter bed and an aerobic filter bed in an integrated structure, with an anaerobic filter bed at the bottom of the treatment tank and an aerobic filter bed at the top, and at the bottom of the treatment tank and a settled sludge draw-off unit water inlet provided, provided with a treated water discharge portion in the processing tank top and detergent drain discharge portion, between said anaerobic filter bed section and aerobic basin unit at ward faceplate A wastewater treatment apparatus having a partition , a water collection nozzle provided on the partition plate, an air diffuser provided above the partition plate, and a cleaning water introduction unit and a cleaning air introduction unit provided below, respectively , The water nozzle has a tube portion that penetrates the partition plate in the vertical direction, and an opening is formed on the top surface of the partition plate of the tube portion so that the filter medium filled above the partition plate does not pass through. And a slit in the vertical direction in the tubular body part below the partition plate and The through hole provided above the slit by the said slit and the through hole, the filter media of the aerobic filter bed section, characterized in that a uniform amount of air ejected from the water collecting nozzle when air washing wastewater Processing equipment. 前記原水流入部の前段に、加圧浮上分離装置を設けたことを特徴とする請求項1記載の排水処理装置。The wastewater treatment apparatus according to claim 1, wherein a pressure levitation separator is provided upstream of the raw water inflow section.
JP24769296A 1996-09-19 1996-09-19 Wastewater treatment equipment Expired - Fee Related JP3851385B2 (en)

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JP24769296A JP3851385B2 (en) 1996-09-19 1996-09-19 Wastewater treatment equipment

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Application Number Priority Date Filing Date Title
JP24769296A JP3851385B2 (en) 1996-09-19 1996-09-19 Wastewater treatment equipment

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JPH1085786A JPH1085786A (en) 1998-04-07
JP3851385B2 true JP3851385B2 (en) 2006-11-29

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