JP2529804B2 - Sewage treatment device using packed bed - Google Patents
Sewage treatment device using packed bedInfo
- Publication number
- JP2529804B2 JP2529804B2 JP23023592A JP23023592A JP2529804B2 JP 2529804 B2 JP2529804 B2 JP 2529804B2 JP 23023592 A JP23023592 A JP 23023592A JP 23023592 A JP23023592 A JP 23023592A JP 2529804 B2 JP2529804 B2 JP 2529804B2
- Authority
- JP
- Japan
- Prior art keywords
- packed bed
- tank
- water
- sewage treatment
- treated
- 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 - Fee Related
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)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は、限られたスペースを利
用して下水の高度処理を行うことができる充填層を用い
た下水処理装置に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a sewage treatment apparatus using a packed bed capable of performing advanced treatment of sewage using a limited space.
【0002】[0002]
【従来の技術】下水の高度処理に対する社会的要請は益
々高くなっている。この高度処理の当面の対象として
は、水域の富栄養化を防止するための窒素、リンがあ
り、その他にBOD、COD、SS等がある。これらの
うち、BODとSSは好気性の充填層の上部から被処理
水を下向流で流す「生物膜濾過」によってかなりの程度
まで除去することができるが、被処理水中のケルダール
性窒素の硝化脱窒を行うためには嫌気充填層と好気充填
層とを使用することが好ましく、このためのプロセスも
研究されている。2. Description of the Related Art The social demand for advanced treatment of sewage is increasing. The immediate targets of this advanced treatment are nitrogen and phosphorus for preventing eutrophication of water bodies, and also BOD, COD, SS and the like. Of these, BOD and SS can be removed to a large extent by "biofilm filtration" in which the water to be treated flows downward from the top of the aerobic packed bed. It is preferable to use an anaerobic packed bed and an aerobic packed bed for performing nitrification denitrification, and the process for this is also researched.
【0003】図2はこのような硝化脱窒を行わせるため
に研究されている装置の代表例を示したもので、比重が
1よりも大きい粒子を充填した好気槽21と嫌気槽22とを
独立に設け、まず被処理水を好気槽21に下向流で流し、
ポンプ23により好気槽21の下部から被処理水を嫌気槽22
の上部まで移送したうえ、嫌気槽22を下向流で流す方式
のものである。ところが、図2のような従来の下水処理
装置は敷地として広い面積が必要であり、都市部の既設
の下水処理場では高度処理のための余分のスペースを確
保することは非常に困難となっているため、容易に採用
することができないという問題があった。またこの下水
処理装置は、大容量のポンプ23が必要となるという問題
もあった。FIG . 2 shows a typical example of an apparatus studied for performing such nitrification denitrification. An aerobic tank 21 and an anaerobic tank 22 filled with particles having a specific gravity of more than 1. Is provided independently, and first, the water to be treated is allowed to flow downward in the aerobic tank 21.
The anaerobic tank 22 is used to remove the water to be treated from below the aerobic tank 21 by the pump 23.
Is a system in which the anaerobic tank 22 is allowed to flow downward in addition to being transferred to the upper part of the. However, the conventional sewage treatment equipment as shown in FIG. 2 requires a large area as a site, and it becomes very difficult to secure an extra space for advanced treatment at an existing sewage treatment plant in an urban area. Therefore, there is a problem that it cannot be easily adopted. Further, this sewage treatment device also has a problem that a large capacity pump 23 is required.
【0004】また、図3に示すように槽体24の内部に比
重が1よりも小さい粒子を充填して下部を嫌気層25、上
部を好気層26とし、被処理水を上向流として流すととも
に、槽体24の上部から流出する処理水の一部をポンプ27
により嫌気層25へ循環させる「硝化液循環方式」と呼ば
れるものも研究されている。この図3の装置は設置スペ
ースが比較的少ない利点があるが、硝化液循環のために
大容量のポンプが必要となるという問題もあった。Further, as shown in FIG. 3 , the inside of the tank 24 is filled with particles having a specific gravity of less than 1, the lower part is an anaerobic layer 25, the upper part is an aerobic layer 26, and the water to be treated is an upward flow. A part of the treated water that flows out from the upper part of the tank 24 is pumped 27
The so-called “nitrifying solution circulation system” for circulating the anaerobic layer 25 has also been studied. The apparatus of FIG. 3 has an advantage that the installation space is relatively small, but there is also a problem that a large capacity pump is required for circulating the nitrifying solution.
【0005】[0005]
【発明が解決しようとする課題】本発明は上記した従来
の問題点を解決し、広いスペースや大容量のポンプを必
要とせずに下水の高度処理を行うことができる充填層を
用いた下水処理装置を提供するために完成されたもので
ある。DISCLOSURE OF THE INVENTION The present invention solves the above-mentioned conventional problems, and treats sewage using a packed bed capable of performing advanced treatment of sewage without requiring a large space or a large capacity pump. It has been completed to provide a device.
【0006】[0006]
【課題を解決するための手段】上記の課題を解決するた
めになされた本発明は、底部に支持層を持つ槽体の内部
を上下両端に流通部を持つ垂直な隔壁により充填層側と
流入水路側とに区画し、充填層側の上段部には比重が比
較的小さい粒子を充填するとともに散気配管を設けて好
気槽を形成し、また充填層側の下段部には比重が比較的
大きい粒子を充填して嫌気槽を形成し、更に垂直な隔壁
の上端の高さを可変式としたことを特徴とするものであ
る。SUMMARY OF THE INVENTION The present invention, which has been made to solve the above-mentioned problems, has a structure in which the inside of a tank having a support layer at the bottom is introduced into the packed bed side by means of vertical partition walls having circulation portions at both upper and lower ends. Divided into water channels, the upper part on the packed bed side is filled with particles with a relatively small specific gravity, and a diffuser pipe is installed to form an aerobic tank. It is characterized in that an anaerobic tank is formed by filling large particles and the height of the upper end of the vertical partition wall is variable.
【0007】[0007]
【実施例】以下に本発明を実施例とともに更に詳細に説
明する。 図1は本発明の実施例を示す図であり、槽体1
の内部が垂直な隔壁2により充填層側と流入水路13側と
に区画されている。この垂直な隔壁2は下端に流通部3
を持つほか、上端にも流通部14を持っている。この垂直
な隔壁2の上端の流通部14の高さhは可変式とし、充填
層側から流入水路13への流入量を制御できるようになっ
ている。槽体1の槽底部には砂利等で構成された支持層
5が形成されており、また充填層側の上段部には、比重
が1〜1.5 と比較的小さく、直径が5〜15mm程度のPVA
ゲル粒子、アンスラサイト等の粒子を充填するととも
に、この充填層の下部に散気配管6を設けて好気槽7と
してある。また充填層側の下段部には、比重が1.5 〜2.
5 と比較的大きく、直径が2〜10mm程度の軽量骨材、
砕石等のような粒子を充填して嫌気槽8としてある。な
お、支持層5の最下部に充填層7、8を洗浄するための
空気+水配管11が設けられている。 EXAMPLES The present invention will be described below in more detail with reference to Examples.
I will tell. FIG. 1 is a diagram showing an embodiment of the present invention.
The inside of the is separated by the vertical partition wall 2 between the packed bed side and the inflow channel 13 side.
It is divided into This vertical partition wall 2 has a circulation part 3 at its lower end.
Besides, it also has a circulation part 14 at the upper end. This vertical
The height h of the flow section 14 at the upper end of the bulkhead 2 is variable and filling
It became possible to control the amount of inflow into the inflow channel 13 from the layer side.
ing. A supporting layer made of gravel or the like on the bottom of the tank 1
5 is formed, and the specific gravity is
Has a relatively small value of 1 to 1.5 and a diameter of 5 to 15 mm.
When filling particles such as gel particles and anthracite
In addition, an aeration pipe 6 is provided below the packed bed to form an aerobic tank 7.
I am doing it. The specific gravity of the lower part on the packed bed side is 1.5-2.
5, a lightweight aggregate with a diameter of 2-10 mm, which is relatively large.
The anaerobic tank 8 is filled with particles such as crushed stone. What
For cleaning the packing layers 7 and 8 at the bottom of the support layer 5,
Air + water piping 11 is provided.
【0008】このように構成された本発明の充填層を用
いた下水処理装置では、散気配管6からの散気によって
好気槽7内の水が浮上し、これが推進力となって充填層
側では被処理水が浮上し、流入水路13側で下降する循環
を生ずる。なお、充填層側から流入水路13側への循環量
は、隔壁2の上端の流通部14の高さhを変えることによ
り調節することができる。被処理水と硝化処理水とが混
合された液の上向流の速度は、500m/ 日が上限である。 The packing layer of the present invention having the above-mentioned structure is used.
In the sewage treatment equipment that was used,
The water in the aerobic tank 7 floats, and this acts as a driving force for the packed bed.
Circulation in which the treated water floats on the side and descends on the inflow channel 13 side
Cause The amount of circulation from the packed bed side to the inflow channel 13 side
By changing the height h of the flow section 14 at the upper end of the partition wall 2.
Can be adjusted. Water to be treated and nitrification treated water are mixed
The upward velocity of the combined liquid is limited to 500 m / day.
【0009】さて、最終沈殿池の上澄水である被処理水
は、脱窒に必要な水素供与体となるメタノールを供給さ
れたうえで槽体1に供給され、好気槽7を通過した水と
ともに流入水路13を下降し、流通部3と支持層5とを通
過してまず嫌気槽8に入る。ここでは充填層に付着して
いる脱窒菌により硝酸性窒素が脱窒され、窒素ガスとし
て除去される。このとき、BODは脱窒のための水素供
与体の一部として用いられて除去され、SSは嫌気槽8
の充填層で捕捉されて除去される。嫌気槽8を通過した
被処理水は次に好気槽7へ入り、好気槽4内を上向流と
して流れる。この間に被処理水中のケルダール窒素は硝
化されて硝酸性窒素となり、一部は最終処理水として外
部へ排出され、一部は硝化処理水として流入水路13から
嫌気槽8に循環される。なお、1日に1回程度の割合で
空気+水配管11から洗浄用の水と空気とを供給して充填
層を逆洗洗浄するが、好気槽7と嫌気槽8とでは充填さ
れている粒子の比重が異なるために、洗浄終了後に自然
に分離して沈降する。 Now, the treated water which is the supernatant water of the final settling tank
Supply methanol, which is the hydrogen donor required for denitrification.
Water supplied to the tank body 1 after passing through the aerobic tank 7,
Both descend the inflow channel 13 and pass through the circulation section 3 and the support layer 5.
First, enter the anaerobic tank 8. Here it is attached to the packed bed
Nitrate nitrogen is denitrified by the existing denitrifying bacteria to produce nitrogen gas.
Be removed. At this time, BOD is a hydrogen supply for denitrification.
Used as a part of the donor and removed, SS is anaerobic tank 8
Trapped and removed by the packed bed. Passed anaerobic tank 8
The water to be treated next enters the aerobic tank 7 and flows upward in the aerobic tank 4.
Then flow. During this time, the Kjeldahl nitrogen in the water to be treated is
Is converted to nitrate nitrogen, and part of it is treated as final treated water.
Part of it is discharged from the inflow channel 13 as nitrification treated water.
It is circulated in the anaerobic tank 8. At a rate of about once a day
Filling by supplying cleaning water and air from the air + water pipe 11
The layers are backwashed and washed, but the aerobic tank 7 and the anaerobic tank 8 are not filled.
Due to the different specific gravities of the
And separate and settle.
【0010】本発明の充填層を用いた下水処理装置は、
設置スペースを減少できる利点があるうえ、80%程度の
脱窒率を達成できること、図2、図3の装置とは異なり
硝化液循環等のためのポンプが不必要なこと、最終処理
水が好気的であるため処理水に酸素を付与するための設
備が不要であること、層洗浄のための空気+水配管11が
一式でよいこと等の利点がある。 The sewage treatment apparatus using the packed bed of the present invention is
There is an advantage that the installation space can be reduced, and about 80%
Achievement of denitrification rate, which is different from the devices in Fig. 2 and Fig. 3.
No need for a pump for circulating nitrifying solution, final treatment
Since water is aerobic, it is necessary to add oxygen to the treated water.
No need for equipment, and air + water piping 11 for layer cleaning
There are advantages such as that one set is enough.
【0011】[0011]
【発明の効果】以上に詳細に説明したように、本発明の
充填層を用いた下水処理装置は従来の装置に比較して設
置スペースを減少できるので、限られたスペースに設置
することができる。また従来のような大容量のポンプを
必要としないうえに、逆洗洗浄時の充填層の安定性が高
い利点がある。更に本発明によれば、80%程度の脱窒率
を達成できるとともに、処理水に酸素を付与するための
設備が不要である利点がある。よって本発明は従来の問
題点を解消した充填層を用いた下水処理装置として、産
業の発展に寄与するところは極めて大きいものがある。 As described in detail above, the present invention
Compared to conventional equipment, sewage treatment equipment using packed beds is installed.
Installation space can be reduced, so installation in a limited space
can do. In addition, a large-capacity pump like the past
It is not necessary and the stability of the packed bed during backwashing is high.
There are advantages. Further, according to the present invention, the denitrification rate of about 80%
And to provide oxygen to the treated water.
It has the advantage that no equipment is required. Therefore, the present invention is a conventional problem.
As a sewage treatment device using a packed bed that solves the problems,
There are extremely large areas that contribute to the development of the industry.
【図1】本発明の実施例を示す断面図である。FIG. 1 is a sectional view showing an embodiment of the present invention.
【図2】従来例を示す断面図である。 FIG. 2 is a sectional view showing a conventional example.
【図3】他の従来例を示す断面図である。 FIG. 3 is a cross-sectional view showing another conventional example.
1 槽体 2 隔壁 3 流通部 5 支持層 6 散気配管 7 好気層 8 嫌気層 11 空気+水配管 13 流入水路 14 流通部 1 Tank Body 2 Partition 3 Flow Section 5 Support Layer 6 Diffusing Pipe 7 Aerobic Layer 8 Anaerobic Layer 11 Air + Water Pipe 13 Inflow Channel 14 Flow Section
Claims (1)
端に流通部を持つ垂直な隔壁により充填層側と流入水路
側とに区画し、充填層側の上段部には比重が比較的小さ
い粒子を充填するとともに散気配管を設けて好気槽を形
成し、また充填層側の下段部には比重が比較的大きい粒
子を充填して嫌気槽を形成し、更に垂直な隔壁の上端の
流通部の高さを可変式としたことを特徴とする充填層を
用いた下水処理装置。 1. The inside of a tank having a support layer at the bottom is placed on both upper and lower sides.
A vertical partition with a circulation section at the end allows the packed bed side and inflow channel
The specific gravity is relatively small in the upper part on the packed bed side.
The aerobic tank is filled with fine particles and provided with a diffuser pipe.
Grains that have a relatively high specific gravity in the lower part on the packed bed side.
The anaerobic tank is formed by filling the child and the upper end of the vertical partition
The packed bed is characterized in that the height of the distribution part is variable.
Sewage treatment equipment used.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP23023592A JP2529804B2 (en) | 1992-08-28 | 1992-08-28 | Sewage treatment device using packed bed |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP23023592A JP2529804B2 (en) | 1992-08-28 | 1992-08-28 | Sewage treatment device using packed bed |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH0671290A JPH0671290A (en) | 1994-03-15 |
JP2529804B2 true JP2529804B2 (en) | 1996-09-04 |
Family
ID=16904653
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP23023592A Expired - Fee Related JP2529804B2 (en) | 1992-08-28 | 1992-08-28 | Sewage treatment device using packed bed |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2529804B2 (en) |
Families Citing this family (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP4581211B2 (en) * | 2000-10-05 | 2010-11-17 | 栗田工業株式会社 | Biological denitrification equipment |
CN104445798B (en) | 2013-12-10 | 2017-09-29 | 中国环境科学研究院 | Rectilinear sewage disposal device and method |
CN105906053A (en) * | 2016-06-13 | 2016-08-31 | 太原昕美蓝波环境科技有限公司 | Vertical aeration and reflux integrated biological sewage treatment device |
Family Cites Families (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS54108458A (en) * | 1978-02-13 | 1979-08-25 | Toshiba Corp | Method of decoloring and purifying night-soil |
JPS5681197A (en) * | 1979-12-06 | 1981-07-02 | Ebara Infilco Co Ltd | Apparatus for nitrificating and denitrificating waste water biologically |
JPH02191594A (en) * | 1989-01-20 | 1990-07-27 | Nkk Corp | Sewage treating device |
-
1992
- 1992-08-28 JP JP23023592A patent/JP2529804B2/en not_active Expired - Fee Related
Also Published As
Publication number | Publication date |
---|---|
JPH0671290A (en) | 1994-03-15 |
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