JPH05293484A - Sewage treatment apparatus - Google Patents
Sewage treatment apparatusInfo
- Publication number
- JPH05293484A JPH05293484A JP10337192A JP10337192A JPH05293484A JP H05293484 A JPH05293484 A JP H05293484A JP 10337192 A JP10337192 A JP 10337192A JP 10337192 A JP10337192 A JP 10337192A JP H05293484 A JPH05293484 A JP H05293484A
- Authority
- JP
- Japan
- Prior art keywords
- anaerobic chamber
- sewage
- load
- chamber
- low
- 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.)
- Withdrawn
Links
- 239000010865 sewage Substances 0.000 title claims abstract description 72
- 239000007787 solid Substances 0.000 claims abstract description 25
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 19
- 239000000126 substance Substances 0.000 abstract description 5
- 239000007788 liquid Substances 0.000 abstract 1
- 239000002351 wastewater Substances 0.000 description 18
- 238000004891 communication Methods 0.000 description 5
- 238000004065 wastewater treatment Methods 0.000 description 3
- 238000005273 aeration Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000004659 sterilization and disinfection Methods 0.000 description 2
- 238000003287 bathing Methods 0.000 description 1
- 235000021152 breakfast Nutrition 0.000 description 1
- 238000000034 method Methods 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 230000000087 stabilizing effect Effects 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
Classifications
-
- Y02W10/12—
Landscapes
- Treatment Of Biological Wastes In General (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は、家庭の汚水を処理する
汚水処理装置に関し、詳しくは家庭の汚水を効率的に処
理し、放流水の水質の安定化を図ろうとする技術に係る
ものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a sewage treatment apparatus for treating domestic sewage, and more particularly to a technique for efficiently treating domestic sewage and stabilizing the quality of discharged water. is there.
【0002】[0002]
【従来の技術】従来、家庭に設置される汚水処理槽Aa
は図10に示すように、浴室、洗面所、台所、トイレな
どから共通の配管aを使用して一次嫌気室bに導入させ
ていた。そして、図10において、共通の配管aをから
汚水は一次嫌気室b、二次嫌気室5、ばっ気室7、消毒
室8をへて放流されるものである。2. Description of the Related Art Conventionally, a sewage treatment tank Aa installed in a home
As shown in FIG. 10, it was introduced from the bathroom, washroom, kitchen, toilet, etc. into the primary anaerobic chamber b using the common pipe a. Then, in FIG. 10, sewage is discharged from the common pipe a to the primary anaerobic chamber b, the secondary anaerobic chamber 5, the aeration chamber 7, and the disinfection chamber 8.
【0003】[0003]
【発明が解決しようとする課題】ところが、汚水処理槽
Aaの構造設計及び指針は、全ての箇所からの汚水の最
大流入を設定していないため、一挙に最大汚水が流入す
ると処理能力を越えて、未処理のまま放流され、放流水
が悪化し、環境を悪くするという問題があった。つま
り、図11に示すように、朝食時間帯、昼食・洗濯時間
帯及び夕食・入浴時間帯に汚水の流入が多くなり、図1
2に示すように、基準BODを越えて放流されることが
多くなるものである。However, the structural design and guidelines of the sewage treatment tank Aa do not set the maximum inflow of sewage from all locations, so if the maximum inflow of sewage all at once, the treatment capacity will be exceeded. However, there is a problem that the untreated water is discharged, the discharged water is deteriorated, and the environment is deteriorated. That is, as shown in FIG. 11, the inflow of sewage increases during the breakfast time, the lunch / washing time, and the dinner / bathing time, as shown in FIG.
As shown in 2, the water is often released beyond the standard BOD.
【0004】本発明はこのような問題に鑑みてなされた
ものであり、その目的とするところは、家庭における汚
水において、台所及びトイレからの汚水のように固形物
を含んでいて処理負荷が高く(BODが高い)処理に時
間を要するが一挙に多量の汚水が流入することが少ない
汚水系と、浴室や洗面所のように固形物を含まなくて処
理低負の少ない(BODが少ない)が一挙に多量の汚水
が流入する汚水系とに着目し、これらを別系にて処理
し、結果として、家庭の汚水を効率的に処理し、放流水
の水質の安定化を図ることができる汚水処理槽を提供し
ようとするにある。The present invention has been made in view of the above problems, and an object of the present invention is to increase the treatment load in domestic sewage, which contains solid substances like sewage from kitchen and toilet. (BOD is high) It takes a long time for treatment, but a large amount of sewage does not flow in all at once, and there is little treatment loss (less BOD) because solid substances are not included like in bathrooms and washrooms. Focusing on the sewage system into which a large amount of sewage flows at once, treating these with another system, as a result, it is possible to efficiently treat domestic sewage and stabilize the quality of discharged water. There is an attempt to provide a processing tank.
【0005】[0005]
【課題を解決するための手段】本発明は、家庭の汚水を
処理する汚水処理装置であって、台所及びトイレのよう
に固形物を含んでいて処理負荷の高い高負荷汚水経路1
が連通される第1嫌気室2と、浴室や洗面所のように固
形物を含まなくて低負荷汚水経路3が連通される第2嫌
気室4とを備え、第1嫌気室2と第2嫌気室4とが二次
嫌気室5に連通され、第1嫌気室2から二次嫌気室5へ
の移流は水位差によるオーバーフロー形態にておこなう
ようになし、第2嫌気室4から二次嫌気室5への移流は
定量ポンプ6にて定量移流すべく構成して成ることを特
徴とするものである。The present invention is a sewage treatment apparatus for treating domestic sewage, which is a high-load sewage path 1 that contains solids and has a high treatment load, such as a kitchen and a toilet.
The first anaerobic chamber 2 and the second anaerobic chamber 4 which communicate with the low-load sewage passage 3 that does not contain solids and communicates with each other, such as a bathroom or a washroom. The anaerobic chamber 4 is communicated with the secondary anaerobic chamber 5, and the advection from the first anaerobic chamber 2 to the secondary anaerobic chamber 5 is performed in the form of overflow due to the water level difference. The advection to the chamber 5 is characterized by being configured so as to admit a fixed amount by the constant amount pump 6.
【0006】[0006]
【作用】台所及びトイレのように固形物を含んでいて処
理負荷の高い高負荷汚水は高負荷汚水経路1から第1嫌
気室2に流入する。浴室や洗面所のように固形物を含ま
なくて低負荷汚水は低負荷汚水経路3から第2嫌気室4
に流入する。このようにして一挙に多量の汚水が流入さ
れる低負荷汚水に高負荷汚水が混じるのを回避する。そ
して、高負荷汚水は第1嫌気室2において時間をかけて
充分に処理してオーバーフローにて二次嫌気室5へと移
流させる。そして、低負荷汚水は定量ポンプ6にて定量
を二次嫌気室5へと移流させる。しかして、高負荷汚水
及び低負荷汚水を効果的に嫌気処理をし、放流水の安定
化を図る。かかる場合、定量ポンプ6は固形物が少ない
低負荷汚水を定量移流させて、定量ポンプ6の固形物の
詰まりによるトラブルを回避する。The high-load sewage containing solids and having a high processing load, such as in kitchens and toilets, flows into the first anaerobic chamber 2 from the high-load sewage path 1. Low-load sewage that does not contain solids, such as bathrooms and washrooms, is transferred from the low-load sewage route 3 to the second anaerobic chamber 4.
Flow into. In this way, it is possible to prevent the high load wastewater from being mixed with the low load wastewater into which a large amount of wastewater flows at once. Then, the high-load sewage is sufficiently treated in the first anaerobic chamber 2 over a period of time to be transferred to the secondary anaerobic chamber 5 by overflow. Then, a fixed amount of the low load sewage is transferred to the secondary anaerobic chamber 5 by the fixed amount pump 6. Then, the high load wastewater and the low load wastewater are effectively anaerobically treated to stabilize the discharged water. In such a case, the metering pump 6 allows the low-load sewage containing a small amount of solid matter to be advected in a fixed quantity to avoid troubles due to clogging of the solid matter in the metering pump 6.
【0007】[0007]
【実施例】以下本発明の実施例を図面に基づいて詳述す
る。図1に示すように、台所及びトイレのように固形物
を含んでいて、BODが高くて処理負荷の高い高負荷汚
水は高負荷汚水経路1をへて汚水処理槽Aへと移流され
るようにしてある。そして、浴室や洗面所のように固形
物を含まなくて、BODが低くて処理負荷が低い低負荷
汚水は低負荷汚水経路3をへて汚水処理槽Aへと移流さ
れるようにしてある。汚水処理槽Aにおいては、高負荷
汚水経路1に連通して第1嫌気室2が構成され、低負荷
汚水経路3に連通して第2嫌気室4が構成されている。
第1嫌気室2と第2嫌気室4とが二次嫌気室5に連通さ
れている。二次嫌気室5の下流側にはばっ気室7、沈澱
分離室9及び消毒室8が形成され、処理水が放流口11
から放流することができるようにしてある。Embodiments of the present invention will be described in detail below with reference to the drawings. As shown in FIG. 1, high-load sewage that contains solids such as kitchen and toilet and has a high BOD and a high treatment load is transferred to the sewage treatment tank A through the high-load sewage route 1. I am doing it. The low-load sewage, which does not contain solids and has a low BOD and a low treatment load, is transferred to the sewage treatment tank A through the low-load sewage path 3 unlike in a bathroom or a washroom. In the sewage treatment tank A, the first anaerobic chamber 2 is formed in communication with the high-load sewage passage 1, and the second anaerobic chamber 4 is formed in communication with the low-load sewage passage 3.
The first anaerobic chamber 2 and the second anaerobic chamber 4 are in communication with the secondary anaerobic chamber 5. An aeration chamber 7, a precipitation separation chamber 9 and a disinfection chamber 8 are formed on the downstream side of the secondary anaerobic chamber 5, and the treated water is discharged through an outlet 11
It is designed to be released from.
【0008】第1嫌気室2から二次嫌気室5への移流は
水位差によるオーバーフロー形態にておこなうようにし
てある。第2嫌気室4から二次嫌気室5への移流は定量
ポンプ6にて定量移流するようにしてある。しかして、
台所及びトイレのように固形物を含んでいて処理負荷の
高い高負荷汚は高負荷汚水経路1から第1嫌気室2に流
入するのであり、そして、浴室や洗面所のように固形物
を含まなくて低負荷汚水は低負荷汚水経路3から第2嫌
気室4に流入するのである。このようにして一挙に多量
の汚水が流入される低負荷汚水に高負荷汚水が混じるの
を回避するのである。そして、高負荷汚水は第1嫌気室
2において時間をかけて充分に処理してオーバーフロー
にて二次嫌気室5へと移流させるのである。そして、低
負荷汚水は定量ポンプ6にて定量を二次嫌気室5へと移
流させるのである。しかして、高負荷汚水及び低負荷汚
水を効果的に嫌気処理をし、放流水の安定化を図るので
ある。かかる場合、定量ポンプ6は固形物が少ない低負
荷汚水を定量移流させて、定量ポンプ6の固形物の詰ま
りによるトラブルを回避するものである。The advection from the first anaerobic chamber 2 to the secondary anaerobic chamber 5 is carried out in the form of overflow due to the water level difference. The advection from the second anaerobic chamber 4 to the secondary anaerobic chamber 5 is carried out by the metering pump 6 in a constant quantity. Then,
High-load sewage that contains solids and has a high processing load, such as in kitchens and toilets, flows into the first anaerobic chamber 2 from the high-load sewage path 1, and contains solids such as in bathrooms and washrooms. Instead, the low-load wastewater flows into the second anaerobic chamber 4 from the low-load wastewater path 3. In this way, it is possible to prevent the high-load wastewater from being mixed with the low-load wastewater into which a large amount of wastewater flows at once. Then, the high-load sewage is sufficiently treated in the first anaerobic chamber 2 over a period of time to be transferred to the secondary anaerobic chamber 5 by overflow. Then, the low load sewage is admitted to the secondary anaerobic chamber 5 in a fixed amount by the constant amount pump 6. Therefore, the high load wastewater and the low load wastewater are effectively anaerobically treated to stabilize the discharged water. In such a case, the metering pump 6 allows the low-load sewage containing a small amount of solid matter to be advected in a fixed quantity to avoid troubles due to clogging of the solid matter in the metering pump 6.
【0009】図3は全体の汚水排出量を示している。図
4は浴室、洗面所から第2嫌気室4への汚水の流入状況
を示している。図5は第2嫌気室4から二次嫌気室5へ
の移流状況を示している。かかる場合、定量ポンプ6に
て24時間にわたって定量が移流される。図6は台所、
トイレから第1嫌気室2への汚水の流入状況を示してい
る。図7は第1嫌気室2から二次嫌気室5へのオーバー
フローによる移流状況を示している。図8は第1嫌気室
2及び第2嫌気室4から二次嫌気室5への汚水の流入状
況を示している。図9は汚水処理槽Aからの放流水のB
OD排出量を示していて、汚水流入量の平準化による排
出BODを安定化させることが判る。FIG. 3 shows the total amount of discharged wastewater. FIG. 4 shows an inflow situation of sewage from the bathroom or washroom to the second anaerobic chamber 4. FIG. 5 shows the state of advection from the second anaerobic chamber 4 to the secondary anaerobic chamber 5. In such a case, the fixed amount is admitted by the fixed amount pump 6 for 24 hours. Figure 6 shows the kitchen
The situation of inflow of dirty water from the toilet to the first anaerobic chamber 2 is shown. FIG. 7 shows a state of advection due to overflow from the first anaerobic chamber 2 to the secondary anaerobic chamber 5. FIG. 8 shows an inflow situation of sewage from the first anaerobic chamber 2 and the second anaerobic chamber 4 to the secondary anaerobic chamber 5. Figure 9 shows B of the water discharged from the sewage treatment tank A
It shows the OD emission amount, and it can be seen that the BOD emission is stabilized by leveling the inflow amount of sewage.
【0010】[0010]
【発明の効果】本発明は上述のように、台所及びトイレ
のように固形物を含んでいて処理負荷の高い高負荷汚水
経路が連通される第1嫌気室と、浴室や洗面所のように
固形物を含まなくて低負荷汚水経路が連通される第2嫌
気室とを備え、第1嫌気室と第2嫌気室とが二次嫌気室
に連通され、第1嫌気室から二次嫌気室への移流は水位
差によるオーバーフロー形態にておこなうようになし、
第2嫌気室から二次嫌気室への移流は定量ポンプにて定
量移流すべく構成してあるから、台所及びトイレのよう
に固形物を含んでいて処理負荷の高い高負荷汚は高負荷
汚水経路から第1嫌気室に流入され、また、浴室や洗面
所のように固形物を含まなくて低負荷汚水は低負荷汚水
経路から第2嫌気室に流入され、一挙に多量の汚水が流
入される低負荷汚水に高負荷汚水が混じるのを回避し、
高負荷汚水は第1嫌気室において時間をかけて充分に処
理してオーバーフローにて二次嫌気室へと移流し、そし
て、低負荷汚水は定量ポンプにて定量を二次嫌気室へと
移流し、しかして、高負荷汚水及び低負荷汚水を効果的
に嫌気処理をし、放流水の安定化を図ることができると
いう利点がある。しかも、定量ポンプは固形物を含まな
い汚水を定量移流するから、固形物の詰まりによる定量
ポンプの損壊を回避でき、併せて低負荷汚水経路の配管
系にも固形物の詰まりを回避でき、かかる配管系を小型
化、簡略化ができるという利点がある。Industrial Applicability As described above, the present invention can be applied to the first anaerobic chamber, which is connected to the high-load sewage path containing a solid substance and having a high processing load, such as a kitchen and a toilet, and a bathroom or a washroom. A second anaerobic chamber, which does not include solid matter and is in communication with the low-load sewage path, wherein the first anaerobic chamber and the second anaerobic chamber are in communication with the secondary anaerobic chamber, and the first anaerobic chamber to the secondary anaerobic chamber The advection to the river should be carried out in the form of overflow due to the water level difference.
Since the advection from the second anaerobic chamber to the secondary anaerobic chamber is configured to quantitatively advect with a metering pump, high-load sewage that contains solids and has a high processing load, such as kitchen and toilet, is high-load sewage. The low-load sewage that flows into the first anaerobic chamber from the route, and does not contain solids such as in bathrooms and washrooms, flows into the second anaerobic chamber from the low-load sewage route, and a large amount of sewage flows in at once. Avoid mixing high load wastewater with low load wastewater
High-load sewage is sufficiently treated in the first anaerobic chamber over time and is transferred to the secondary anaerobic chamber by overflow, and low-load sewage is quantitatively transferred to the secondary anaerobic chamber by a metering pump. However, there is an advantage that the high load wastewater and the low load wastewater can be effectively anaerobically treated to stabilize the discharged water. Moreover, since the metering pump quantitatively adsorbs sewage that does not contain solids, it is possible to avoid damage to the metering pump due to clogging of solids, and also to avoid clogging of solids in the piping system of the low-load sewage path. There is an advantage that the piping system can be downsized and simplified.
【図1】本発明の一実施例の汚水処理の系統図である。FIG. 1 is a system diagram of wastewater treatment according to an embodiment of the present invention.
【図2】同上の汚水処理槽の概略斜視図である。FIG. 2 is a schematic perspective view of the above wastewater treatment tank.
【図3】同上の全体の汚水排出量を示すグラフである。FIG. 3 is a graph showing the total amount of discharged wastewater in the above.
【図4】同上の浴室、洗面所から第2嫌気室への汚水の
流入状況を示すグラフである。FIG. 4 is a graph showing an inflow situation of sewage from the bathroom and washroom to the second anaerobic chamber in the above.
【図5】同上の第2嫌気室から二次嫌気室への移流状況
を示すグラフである。FIG. 5 is a graph showing a state of advection from the second anaerobic chamber to the secondary anaerobic chamber of the above.
【図6】同上の台所、トイレから第1嫌気室への汚水の
流入状況を示すグラフである。FIG. 6 is a graph showing an inflow situation of sewage from the kitchen and the toilet in the same as above to the first anaerobic chamber.
【図7】同上の第1嫌気室2から二次嫌気室へのオーバ
ーフローによる移流状況を示すグラフである。FIG. 7 is a graph showing a state of advection due to overflow from the first anaerobic chamber 2 to the secondary anaerobic chamber of the above.
【図8】同上の第1嫌気室2及び第2嫌気室から二次嫌
気室への汚水の流入状況を示すグラフである。FIG. 8 is a graph showing an inflow situation of sewage from the first anaerobic chamber 2 and the second anaerobic chamber to the secondary anaerobic chamber of the above.
【図9】同上のBOD排出状況を示すグラフである。FIG. 9 is a graph showing the BOD emission status of the same as above.
【図10】従来例の汚水処理の系統図である。FIG. 10 is a system diagram of conventional wastewater treatment.
【図11】同上の汚水処理槽への汚水流入状況を示すグ
ラフである。FIG. 11 is a graph showing a situation of inflow of sewage into the sewage treatment tank of the above.
【図12】同上の処理水の放流状況を示すグラフであ
る。FIG. 12 is a graph showing the situation of discharge of treated water in the above.
1 高負荷汚水経路 2 第1嫌気室 3 低負荷汚水経路 4 第2嫌気室 5 二次嫌気室 6 定量ポンプ 1 High load sewage route 2 1st anaerobic chamber 3 Low load sewage route 4 2nd anaerobic chamber 5 Secondary anaerobic chamber 6 Metering pump
Claims (1)
って、台所及びトイレのように固形物を含んでいて処理
負荷の高い高負荷汚水経路が連通される第1嫌気室と、
浴室や洗面所のように固形物を含まなくて低負荷汚水経
路が連通される第2嫌気室とを備え、第1嫌気室と第2
嫌気室とが二次嫌気室に連通され、第1嫌気室から二次
嫌気室への移流は水位差によるオーバーフロー形態にて
おこなうようになし、第2嫌気室から二次嫌気室への移
流は定量ポンプにて定量移流すべく構成して成ることを
特徴とする汚水処理装置。1. A sewage treatment apparatus for treating domestic sewage, comprising: a first anaerobic chamber, such as a kitchen and a toilet, which communicates with a high-load sewage path containing a solid matter and having a high treatment load.
A second anaerobic chamber, which does not contain solids and communicates with a low-load sewage path such as a bathroom or a washroom, is provided with a first anaerobic chamber and a second anaerobic chamber.
The anaerobic chamber is communicated with the secondary anaerobic chamber, and the advection from the first anaerobic chamber to the secondary anaerobic chamber does not occur in the form of overflow due to the water level difference. A sewage treatment apparatus characterized in that it is configured to transfer a fixed amount by a constant pump.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP10337192A JPH05293484A (en) | 1992-04-23 | 1992-04-23 | Sewage treatment apparatus |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP10337192A JPH05293484A (en) | 1992-04-23 | 1992-04-23 | Sewage treatment apparatus |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH05293484A true JPH05293484A (en) | 1993-11-09 |
Family
ID=14352255
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP10337192A Withdrawn JPH05293484A (en) | 1992-04-23 | 1992-04-23 | Sewage treatment apparatus |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH05293484A (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2002336883A (en) * | 2001-05-11 | 2002-11-26 | Fuji Clean Kogyo Kk | Hybrid treatment tank capable of treating wastewater from disposer |
| JP2007090154A (en) * | 2005-09-27 | 2007-04-12 | Hitachi Housetec Co Ltd | Wastewater treatment apparatus |
| JP2008253929A (en) * | 2007-04-06 | 2008-10-23 | Hitachi Housetec Co Ltd | Water treatment apparatus |
-
1992
- 1992-04-23 JP JP10337192A patent/JPH05293484A/en not_active Withdrawn
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2002336883A (en) * | 2001-05-11 | 2002-11-26 | Fuji Clean Kogyo Kk | Hybrid treatment tank capable of treating wastewater from disposer |
| JP2007090154A (en) * | 2005-09-27 | 2007-04-12 | Hitachi Housetec Co Ltd | Wastewater treatment apparatus |
| JP2008253929A (en) * | 2007-04-06 | 2008-10-23 | Hitachi Housetec Co Ltd | Water treatment apparatus |
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Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| A300 | Withdrawal of application because of no request for examination |
Free format text: JAPANESE INTERMEDIATE CODE: A300 Effective date: 19990706 |