JPH05104085A - Purifying treatment of waste water - Google Patents

Purifying treatment of waste water

Info

Publication number
JPH05104085A
JPH05104085A JP29949791A JP29949791A JPH05104085A JP H05104085 A JPH05104085 A JP H05104085A JP 29949791 A JP29949791 A JP 29949791A JP 29949791 A JP29949791 A JP 29949791A JP H05104085 A JPH05104085 A JP H05104085A
Authority
JP
Japan
Prior art keywords
soil
wastewater
treated
tank
bed
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.)
Granted
Application number
JP29949791A
Other languages
Japanese (ja)
Other versions
JP2748752B2 (en
Inventor
Daizo Kida
大三 喜田
Hirokazu Tsuji
博和 辻
Yasu Omi
縁 近江
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Obayashi Corp
Original Assignee
Obayashi Corp
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Obayashi Corp filed Critical Obayashi Corp
Priority to JP3299497A priority Critical patent/JP2748752B2/en
Publication of JPH05104085A publication Critical patent/JPH05104085A/en
Application granted granted Critical
Publication of JP2748752B2 publication Critical patent/JP2748752B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Abstract

PURPOSE:To remove not only a phosphorus component or an org. component but also a nitrogen component in the purifying treatment of waste water by simple constitution. CONSTITUTION:A broken stone bed 68, a lower purifying soil bed 66, a sand bed 64 and a surface rhizosphere soil bed 62 are successively formed on a bottom part in a layered form. A supply pipe 52 of waste water to be treated is embedded in the vicinity of the boundary of the surface rhizosphere soil bed 62 and the lower purifying soil bed 66 through the sand bed 64. A virescence plant 60 is planted in the ground surface of the surface rhizosphere soil bed 62 so as to extend the roots 60a of the plant 60 to the periphery of the supply pipe 52. The nitrogen component in waste water to be treated is absorbed by the virescence plant 60 and phosphorus or an org. component is adsorbed on the lower purifying soil bed 66 to be decomposed.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、排水中のリンや有機成
分ばかりでなく窒素をも除去することができる排水の浄
化処理方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a wastewater purification treatment method capable of removing not only phosphorus and organic components in wastewater but also nitrogen.

【0002】[0002]

【従来の技術】近年リゾート地域の開発や都市部の再開
発にともなって、このような地域では各種排水が公共水
域に放流されるケースが多くなっている。このような場
合、排水を受け入れる公共水域としての河川,湖沼等の
水質汚濁、特に富栄養化にともなうアオコ,赤潮等の発
生を防止するため、放流前に排水中の汚濁成分を除去す
ることが不可欠である。
2. Description of the Related Art In recent years, with the development of resort areas and redevelopment of urban areas, there are many cases where various types of wastewater are discharged into public water areas. In such a case, in order to prevent water pollution of rivers, lakes and marshes as public water bodies that receive wastewater, especially the occurrence of water-bloom, red tide, etc. due to eutrophication, it is necessary to remove pollutants from wastewater before discharge. It is essential.

【0003】このような排水中の汚濁成分を除去するた
めの簡易なシステムとして、自然の浄化能力を活用した
土壌浄化法が従来用いられている。これは、土壌中に排
水を通して、土壌中を通過する間に汚濁物質を吸着さ
せ、さらには土壌微生物により汚濁物質を分解させる等
して、排水中の汚濁物質を除去しようとするものであ
る。
As a simple system for removing such pollutant components in waste water, a soil purification method utilizing the natural purification capacity has been conventionally used. This is to remove the pollutants in the wastewater by passing the wastewater through the soil, adsorbing the pollutants while passing through the soil, and further decomposing the pollutants by soil microorganisms.

【0004】[0004]

【発明が解決しようとする課題】しかしながら、このよ
うな従来の土壌浄化法にあっては、排水中のリンや有機
成分は除去することができるが、窒素成分は除去するこ
とができないという問題点があった。
However, in such a conventional soil purification method, phosphorus and organic components in wastewater can be removed, but nitrogen components cannot be removed. was there.

【0005】一方、発明者らは、土壌表面に植栽される
植物がその成長過程で窒素成分を吸収することから、従
来の土壌浄化法と組合せることにより、より高度な排水
処理が可能となるとの見通しを得た。
On the other hand, since the plants planted on the soil surface absorb nitrogen components during the growth process, the inventors of the present invention can perform more advanced wastewater treatment by combining with the conventional soil purification method. I got the prospect of becoming.

【0006】本発明は前記問題点ならびに知見に基づい
てなされたもので、その目的は、簡易な構成をもって、
リンや有機成分ばかりでなく、窒素成分をも除去するこ
とができる排水の浄化処理方法を提供することにある。
The present invention has been made based on the above problems and findings, and its object is to provide a simple structure.
An object of the present invention is to provide a method for purifying wastewater that can remove not only phosphorus and organic components but also nitrogen components.

【0007】[0007]

【課題を解決するための手段】前記目的を達成するため
に本発明は、土壌中に排水を通水して排水の浄化を図る
排水の浄化処理方法において、前記土壌を表層土と下層
土との二層をもって形成し、該表層土の表面には植物を
植栽するとともに、該表層土と前記下層土との境界付近
に被処理排水を供給するための通路を配設したことを特
徴とする。
In order to achieve the above object, the present invention provides a wastewater purification treatment method for purifying wastewater by passing wastewater through the soil, wherein the soil is a surface soil and a subsoil. And a plant is planted on the surface of the surface soil, and a passage is provided near the boundary between the surface soil and the lower layer soil for supplying treated wastewater. To do.

【0008】[0008]

【作用】以上の構成によれば、表層土と下層土との二層
の境界付近に非処理排水を供給するための通路を配設す
るとともに、前記表層土の表面に植物を植栽したので、
排水中に含まれるリンやその他の有機物質は土壌に吸着
され、あるいは土壌微生物に分解されて除去され、さら
に排水中の窒素成分は表層土表面に植栽された植物の根
を通じて植物に吸収される。
With the above structure, a passage for supplying untreated wastewater is arranged near the boundary between the two layers of the surface soil and the lower soil, and plants are planted on the surface of the surface soil. ,
Phosphorus and other organic substances contained in the wastewater are adsorbed to the soil or decomposed by soil microorganisms to be removed, and the nitrogen component in the wastewater is absorbed by the plants through the roots of the plants planted on the surface soil surface. It

【0009】[0009]

【実施例】以下、本発明の一実施例を図面を用いて詳細
に説明する。図1は本発明に係る排水の浄化処理方法の
試験フローを示す系統図、図2は本発明に係る排水の浄
化処理方法の試験に供するモデル土槽の一部破断側断面
図である。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the present invention will be described in detail below with reference to the drawings. FIG. 1 is a system diagram showing a test flow of a wastewater purification treatment method according to the present invention, and FIG. 2 is a partially cutaway side sectional view of a model soil tank used for a test of the wastewater purification treatment method according to the present invention.

【0010】図1に示すように、人工下水作成プラント
10で人工的に作成された生活排水(BOD濃度200
ppm)は、嫌気方式と好気方式とを併用する合併浄化
槽20に流入し、前処理として生物処理が施される。そ
して、合併浄化槽20からのオーバーフロー水がポンプ
ピット30に流入し、ポンプピット30内に据え付けら
れた移送ポンプ32によって分配槽40に送られる。分
配槽40では、5ヶ所に設置されたモデル土槽50の各
々に被処理排水が分配供給される。なお、この被処理排
水の性状は、試験期間中を通じて、BOD1〜5pp
m,COD3.1〜4.2ppm,全窒素(T−N)
9.5〜13.7ppm,全リン(T−P)3.4〜
5.3ppmであった。
As shown in FIG. 1, domestic wastewater artificially produced in an artificial sewage production plant 10 (BOD concentration 200
(ppm) flows into the combined septic tank 20 that uses both the anaerobic method and the aerobic method, and is subjected to biological treatment as a pretreatment. Then, the overflow water from the combined purification tank 20 flows into the pump pit 30, and is sent to the distribution tank 40 by the transfer pump 32 installed in the pump pit 30. In the distribution tank 40, the wastewater to be treated is distributed and supplied to each of the model soil tanks 50 installed at five locations. The properties of this treated wastewater are BOD1-5pp throughout the test period.
m, COD 3.1 to 4.2 ppm, total nitrogen (TN)
9.5 to 13.7 ppm, total phosphorus (TP) 3.4 to
It was 5.3 ppm.

【0011】前記5ヶ所のモデル土槽50には、浄化作
用を比較するために、それぞれ異なった土壌が形成され
るとともに、その表層土の地表面に異なる種類の緑化植
物が植栽されている。
Different soils are formed in each of the five model soil tanks 50 in order to compare their purifying effects, and different kinds of greening plants are planted on the surface of the surface soil. ..

【0012】前記被処理排水は、それぞれのモデル土槽
50に形成された土壌の表層土と下層土との間に配設さ
れた供給管52を介して土壌中に供給され、浄化処理さ
れた後、モデル土槽50内の最下部に設けられた集水管
54を通じてモデル土槽50から導出され、放流枡70
を経由して放流用のU字溝80へ放流される。
The wastewater to be treated is supplied into the soil through a supply pipe 52 arranged between the surface soil and the lower soil of the soil formed in each model soil tank 50, and is purified. After that, it is led out from the model soil tank 50 through the water collecting pipe 54 provided at the bottom in the model soil tank 50, and the discharge box 70
It is discharged to the U-shaped groove 80 for discharge via.

【0013】以上述べた被処理排水の通水経路は、図1
中に矢印を付した太線で示されている。
The water passage for the wastewater to be treated described above is shown in FIG.
It is indicated by a thick line with an arrow inside.

【0014】次に、モデル土槽50の構成について説明
する。モデル土槽50に用いる土槽としては、気温変化
の影響を受けにくいコンクリート製のボックスカルバー
ト50aを使用した。また、その寸法は、各種植栽植物
の生育状況を観察比較し、かつ被処理排水の均等な供給
状況を確認するための最小規模として、長さ,幅各2m
とし、植栽植物の根が生育する表層土である表層根圏土
壌として30〜40cm、下層土である下層浄化土壌と
して同じく30〜40cmを確保するために、高さ1m
とした。さらに、浄化処理後の処理水を採取する必要か
ら、モデル土槽50は地上に設置した。
Next, the structure of the model soil tank 50 will be described. As a soil tank used for the model soil tank 50, a box culvert 50a made of concrete, which is not easily affected by temperature changes, was used. In addition, its size is 2 m each for length and width as the minimum scale for observing and comparing the growth status of various planting plants and confirming the uniform supply status of wastewater to be treated.
In order to secure 30 to 40 cm as the surface rhizosphere soil, which is the surface soil on which the roots of planted plants grow, and also 30 to 40 cm as the lower layer purified soil, which is the lower soil, a height of 1 m
And Further, since it is necessary to collect the treated water after the purification treatment, the model soil tank 50 was installed on the ground.

【0015】ボックスカルバート50aの内部には、図
2に示すように、その底部側から砕石層68、下層浄化
土壌66、砂層64、表層根圏土壌62の順に層状のモ
デル土壌が形成されている。そして、表層根圏土壌62
と下層浄化土壌66との境界付近には、表層根圏土壌6
2との間に砂層64を介して、被処理排水の供給管52
が埋設されている。
Inside the box culvert 50a, as shown in FIG. 2, layered model soils are formed in this order from the bottom side to a crushed stone layer 68, a lower layer purified soil 66, a sand layer 64, and a surface rhizosphere soil 62. .. And surface rhizosphere soil 62
The surface rhizosphere soil 6
2 through the sand layer 64, the supply pipe 52 for the wastewater to be treated
Is buried.

【0016】供給管52は、内部を流通する被処理排水
が、周囲の土壌中に浸透するための透水孔が多数設けら
れた有孔管52aと、有孔管52aを土壌中に安定して
支持するためのベッド52bとから構成されている。ま
た、有孔管52aの周囲には不織布56が捲回され、そ
の両端は有孔管52aの径方向に延在されて、被処理排
水が適度に土壌中に湿潤されるようになっている。
The supply pipe 52 has a perforated pipe 52a provided with a large number of water permeation holes for allowing the treated wastewater flowing therein to permeate into the surrounding soil, and the perforated pipe 52a stably in the soil. It is composed of a bed 52b for supporting. Further, the nonwoven fabric 56 is wound around the perforated pipe 52a, and both ends thereof are extended in the radial direction of the perforated pipe 52a so that the wastewater to be treated is appropriately wet in the soil. ..

【0017】表層根圏土壌62の地表面には、芝等の緑
化植物60が植栽され、その根60aは表層根圏土壌6
2の内部を下方に向かって生育、伸長している。
A green plant 60 such as turf is planted on the surface of the surface rhizosphere soil 62, and its root 60a is the surface rhizosphere soil 6
The inside of No. 2 grows and extends downward.

【0018】最下部の砕石層68には浄化処理された高
度処理水を集めてモデル土槽50の外部に導出する集水
管54が設けられている。
The crushed stone layer 68 at the lowermost portion is provided with a water collecting pipe 54 for collecting the highly-treated water that has been purified and discharging it to the outside of the model soil tank 50.

【0019】次に、本実施例の作用について、1990
年5月〜1990年11月に前記試験設備を使用して実
施した試験の結果を参照して説明する。表1に、各モデ
ル土槽50での緑化植物60,表層根圏土壌62および
下層浄化土壌66の組み合わせをまとめて示す。
Next, the operation of this embodiment will be described in 1990.
A description will be given with reference to the results of the tests conducted from May to November 1990 using the test facility. Table 1 collectively shows combinations of greening plants 60, surface rhizosphere soil 62, and lower layer purified soil 66 in each model soil tank 50.

【0020】 1.窒素(N)の除去能 試験期間中の5月から7月にかけては、表層根圏土壌の
表面にベントグラスを植栽したNo.1槽が、Nの除去
量が多く、除去率は23〜38%であった。これに対し
て、8月から10月中旬にかけては、表層根圏土壌の表
面にコウライシバを植栽したNo.2槽,No.3槽で
のNの除去量が多く、除去率は23〜33%であった。
また、地表にタマリュウ・シバザクラを植栽したNo.
4槽は、全試験期間を通じて1ppm程度の除去量があ
り、除去率は10%程度であった。一方、地表になにも
植栽されていない裸地のNo.5槽では、全試験期間を
通じてNの除去量が0.6ppmと低く、除去率も5%
程度であった。
[0020] 1. Nitrogen (N) removal capacity From May to July during the test period, No. No. in which bentgrass was planted on the surface of the surface rhizosphere soil was used. One tank had a large amount of N removed, and the removal rate was 23 to 38%. On the other hand, from August to mid-October, No. 2 tanks, No. The amount of N removed in three tanks was large, and the removal rate was 23 to 33%.
In addition, No.
The four tanks had a removal amount of about 1 ppm throughout the entire test period, and the removal rate was about 10%. On the other hand, no. In the 5 tanks, the amount of N removed was as low as 0.6 ppm throughout the entire test period, and the removal rate was 5%.
It was about.

【0021】以上の結果から、 (1)Nの除去能は、表層根圏土壌の表面に植栽された
植物の種類に影響される。 (2)芝が植栽されたモデル土槽(No.1〜No.3
槽)では、タマリュウ・シバザクラが植栽されたモデル
土槽(No.4槽)と比較して、Nの除去効果が大き
い。 (3)それぞれの芝の特徴として、ベントグラスは5月
から7月にかけて、コウライシバは8月から10月にか
けてNの除去量が大きい。ということが確認された。 2.リン(P)の除去能 Pの除去能を検討するにあたっては、原水および処理水
ともに、全リン(T−P)中に占めるリン酸リン(PO
4 −P)の比率が95〜98%であったため、原則とし
てPO4 −Pの除去能について検討した。
From the above results, (1) N removal ability is affected by the type of plant planted on the surface of the surface rhizosphere soil. (2) Model soil tank (No. 1 to No. 3) in which turf is planted
In the tank), the effect of removing N is greater than that in the model soil tank (No. 4 tank) in which Tamariu and Shibazakura are planted. (3) As a characteristic of each turf, bentgrass has a large amount of N removal from May to July, and Koroshiiba from August to October. It was confirmed. 2. Phosphorus (P) removal ability When examining the removal ability of P, both the raw water and the treated water account for phosphorus phosphate (PO) in the total phosphorus (TP).
4 -P) for the ratio was 95% to 98% of were examined removal capability of PO 4 -P principle.

【0022】No.2槽では、全試験期間を通じてPO
4 −Pはほとんど除去されていた。No.3槽,No.
4槽,No.5槽では、6月から8月にかけてPO4
Pの吸収率は44〜65%であったが、その後除去率が
悪くなり、5〜22%に減少した。No.1槽では、全
試験期間を通じて30〜40%の除去率であった。
No. In 2 tanks, PO throughout the entire test period
Most of 4- P was removed. No. 3 tanks, No.
4 tanks, No. In the 5 tanks, PO 4 − from June to August
The absorption rate of P was 44 to 65%, but thereafter the removal rate deteriorated and decreased to 5 to 22%. No. In one tank, the removal rate was 30 to 40% throughout the entire test period.

【0023】以上のことから、Pの除去能は、リン酸吸
収係数が高い黒ボク土を下層浄化土壌に使用したモデル
土槽で高いことが確認された。 3.シバの生育量と全窒素(T−N)除去量との関係 前記表1に示した緑化植物60のうち、No.1槽〜N
o.3槽のシバについては、ほぼ定期的に刈り込みを行
ない、その生育量を調査した。この結果、シバの刈り込
み収量とT−N除去量との関係から、シバの生育量の増
大とともに、各モデル土槽でのT−Nの除去量が大きく
なっていることが確認された。モデル土槽で除去された
T−Nがすべてシバに吸収されたものと仮定すると、シ
バのT−N含有量の理論値は2.5〜3.3%程度であ
るが、実際に刈り込んだシバのT−N含有量は2.1〜
4.1%であり、前記理論値にほぼ相当する値であっ
た。
From the above, it was confirmed that the removal ability of P was high in the model soil tank in which the black soil with high phosphoric acid absorption coefficient was used as the lower layer purified soil. 3. Relationship between Growth of Shiva and Total Nitrogen (TN) Removal Amount of the green plant 60 shown in Table 1 above. 1 tank to N
o. The three turf grasses were mowed almost regularly and their growth was investigated. As a result, it was confirmed from the relationship between the pruning yield of turfgrass and the amount of TN removed, that the amount of TN removed in each model soil tank increased as the growth amount of turf increased. Assuming that all the TN removed in the model soil tank was absorbed by the turf, the theoretical TN content of the turf is about 2.5-3.3%, but it was actually trimmed. The TN content of shiba is 2.1-
It was 4.1%, which was a value almost equivalent to the theoretical value.

【0024】以上のことから、No.1槽〜No.3槽
の各モデル土槽で除去されたT−Nのほとんどは、表層
根圏土壌62の地表面に生育しているシバに吸収された
ことが確認された。
From the above, No. 1 tank-No. It was confirmed that most of the TN removed in each of the three model soil tanks was absorbed by the turf growing on the surface of the surface rhizosphere soil 62.

【0025】以上の試験結果に基づいて、本実施例の作
用について述べると、被処理排水は、モデル土槽50の
表層根圏土壌62と下層浄化土壌66との境界付近に埋
設設置された供給管52の有孔管52aの内部を流通
し、有孔管52aに設けられた多数の透水孔を通じて土
壌中に浸透していく。この際、有孔管52aの周囲に
は、透水係数の高い砂層64が形成されているので、被
処理排水は、容易に有孔管52aから外部に滲出するこ
とができる。また、有孔管52aの周囲には不織布56
が捲回され、これが砂層64と下層浄化土壌66との間
に延在されているので、有孔管52aから滲出した被処
理排水は、不織布56に沿って浸透していき、土壌中に
被処理排水を均一に供給することができる。
The operation of this embodiment will be described based on the above test results. The treated wastewater is supplied by being buried in the model soil tank 50 near the boundary between the surface rhizosphere soil 62 and the lower layer purified soil 66. It flows through the inside of the perforated pipe 52a of the pipe 52 and permeates into the soil through a large number of water-permeable holes provided in the perforated pipe 52a. At this time, since the sand layer 64 having a high water permeability is formed around the perforated pipe 52a, the wastewater to be treated can easily exude from the perforated pipe 52a to the outside. Further, a non-woven fabric 56 is formed around the perforated pipe 52a.
Since it is wound and it extends between the sand layer 64 and the lower layer purified soil 66, the wastewater to be treated that has exuded from the perforated pipe 52a permeates along the non-woven fabric 56 and is deposited in the soil. The treated wastewater can be supplied uniformly.

【0026】表層根圏土壌62の地表面に植栽された緑
化植物60の根60aは、土壌中に浸透してきた被処理
排水を求めて砂層64の付近まで伸長し、被処理排水中
に含有される肥料要素、特に窒素を顕著に吸収するの
で、被処理排水中の全窒素(T−N)が効果的に除去さ
れるとともに、緑化植物60には、水分と肥料とが与え
られる。
The root 60a of the greening plant 60 planted on the surface of the surface rhizosphere soil 62 extends to the vicinity of the sand layer 64 in search of the treated wastewater that has penetrated into the soil and is contained in the treated wastewater. Since it significantly absorbs the fertilizer elements used, particularly nitrogen, the total nitrogen (TN) in the wastewater to be treated is effectively removed, and the greening plant 60 is provided with water and fertilizer.

【0027】緑化植物60に吸収されなかった被処理排
水は、下層浄化土壌66を透過して、下方に移動してい
く。この過程で、被処理排水中の全リン(T−P)が土
壌に吸着されて除去されるとともに、被処理排水中の有
機物質等の汚濁物質が土壌微生物によって分解されると
いう作用も同時に得られ、簡単な構成で高度の排水処理
を実施できる。
The wastewater to be treated, which has not been absorbed by the green plant 60, passes through the lower-layer purified soil 66 and moves downward. In this process, the total phosphorus (TP) in the treated wastewater is adsorbed to the soil and removed, and at the same time, the pollutants such as organic substances in the treated wastewater are decomposed by soil microorganisms. Therefore, it is possible to carry out advanced wastewater treatment with a simple structure.

【0028】[0028]

【発明の効果】以上詳細に説明したように、本発明に係
る排水の浄化方法によれば、表層土と下層土との二層の
境界付近に被処理排水を供給するための通路を配設する
とともに、前記表層土の表面に植物を植栽したので、排
水中に含まれるリンやその他の有機物質は土壌に吸着さ
れ、あるいは土壌微生物に分解されて除去され、さらに
排水中の窒素成分は表層土表面に植栽された植物の根を
通じて植物に吸収され、排水中のリンあるいは有機成分
ばかりでなく、窒素成分をも除去することができ、排水
の富栄養化を防止することができる。
As described in detail above, according to the wastewater purification method of the present invention, the passage for supplying the wastewater to be treated is provided near the boundary between the two layers of the surface soil and the lower soil. In addition, since plants were planted on the surface of the surface soil, phosphorus and other organic substances contained in the drainage are adsorbed to the soil or decomposed by soil microorganisms to be removed, and nitrogen components in the drainage are It is absorbed by the plant through the roots of the plant planted on the surface of the surface soil, and it is possible to remove not only phosphorus or organic components but also nitrogen components in the wastewater, and it is possible to prevent eutrophication of the wastewater.

【図面の簡単な説明】[Brief description of drawings]

【図1】本発明に係る排水の浄化処理方法の試験フロー
を示す系統図である。
FIG. 1 is a system diagram showing a test flow of a wastewater purification treatment method according to the present invention.

【図2】本発明に係る排水の浄化処理方法の試験に供す
るモデル土槽の一部破断側断面図である。
FIG. 2 is a partially cutaway side sectional view of a model soil tank used for a test of a wastewater purification treatment method according to the present invention.

【符号の説明】[Explanation of symbols]

10 人工下水作成プラント 20 合併浄化槽 30 ポンプピット 40 分配槽 50 モデル土槽 52 供給管 54 集水管 56 不織布 60 緑化植物 62 表層根圏土壌 64 砂層 66 下層浄化土壌 68 砕石層 10 Artificial sewage production plant 20 Combined septic tank 30 Pump pit 40 Distribution tank 50 Model soil tank 52 Supply pipe 54 Water collection pipe 56 Nonwoven fabric 60 Green plant 62 Surface rhizosphere soil 64 Sand layer 66 Lower layer purification soil 68 Crushed stone layer

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 土壌中に排水を通水して排水の浄化を図
る排水の浄化処理方法において、 前記土壌を表層土と下層土との二層をもって形成し、 該表層土の表面には植物を植栽するとともに、 該表層土と前記下層土との境界付近に被処理排水を供給
するための通路を配設した、 ことを特徴とする排水の浄化処理方法。
1. A method for purifying wastewater, which comprises purifying wastewater by passing wastewater through the soil, wherein the soil is formed with two layers of surface soil and lower soil, and the surface soil has a plant. And a passage for supplying wastewater to be treated is disposed near the boundary between the surface soil and the lower soil.
JP3299497A 1991-10-21 1991-10-21 Wastewater purification treatment structure Expired - Fee Related JP2748752B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3299497A JP2748752B2 (en) 1991-10-21 1991-10-21 Wastewater purification treatment structure

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3299497A JP2748752B2 (en) 1991-10-21 1991-10-21 Wastewater purification treatment structure

Publications (2)

Publication Number Publication Date
JPH05104085A true JPH05104085A (en) 1993-04-27
JP2748752B2 JP2748752B2 (en) 1998-05-13

Family

ID=17873345

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3299497A Expired - Fee Related JP2748752B2 (en) 1991-10-21 1991-10-21 Wastewater purification treatment structure

Country Status (1)

Country Link
JP (1) JP2748752B2 (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100424289B1 (en) * 2001-05-11 2004-03-24 정재수 nature equilibrium vertical flow type artificial swamp facility for purging contaminate matter away contaminated water
KR100457730B1 (en) * 2001-02-06 2004-11-20 (주) 상원이엔씨 Water treatment method with plant
KR100463062B1 (en) * 2001-02-06 2004-12-29 (주) 상원이엔씨 Water treatment method with plant
JP2008080305A (en) * 2006-09-29 2008-04-10 Fujishima Kensetsu:Kk Drainage filtration system
WO2009150720A1 (en) * 2008-06-10 2009-12-17 冨安洋子 Sewage purification system and method of growing plant by using the purification system
JP2017094303A (en) * 2015-11-26 2017-06-01 株式会社竹中工務店 Storage-purification system

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS53108662A (en) * 1977-03-05 1978-09-21 Okuma Kougiyou Kk Device for purifying waste water
JPS5845788A (en) * 1981-09-14 1983-03-17 Mitsubishi Plastics Ind Ltd Means for draining purified water in sewage-purifying plant
JPS59154398U (en) * 1983-03-31 1984-10-16 株式会社明電舎 Sewage treatment equipment
JPS62171791A (en) * 1986-01-23 1987-07-28 Toshiyuki Wakatsuki Soil cleaning up device
JPH02126996A (en) * 1988-11-07 1990-05-15 Onoda Autoclaved Light Weight Concrete Co Ltd Soil trench

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS53108662A (en) * 1977-03-05 1978-09-21 Okuma Kougiyou Kk Device for purifying waste water
JPS5845788A (en) * 1981-09-14 1983-03-17 Mitsubishi Plastics Ind Ltd Means for draining purified water in sewage-purifying plant
JPS59154398U (en) * 1983-03-31 1984-10-16 株式会社明電舎 Sewage treatment equipment
JPS62171791A (en) * 1986-01-23 1987-07-28 Toshiyuki Wakatsuki Soil cleaning up device
JPH02126996A (en) * 1988-11-07 1990-05-15 Onoda Autoclaved Light Weight Concrete Co Ltd Soil trench

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100457730B1 (en) * 2001-02-06 2004-11-20 (주) 상원이엔씨 Water treatment method with plant
KR100463062B1 (en) * 2001-02-06 2004-12-29 (주) 상원이엔씨 Water treatment method with plant
KR100424289B1 (en) * 2001-05-11 2004-03-24 정재수 nature equilibrium vertical flow type artificial swamp facility for purging contaminate matter away contaminated water
JP2008080305A (en) * 2006-09-29 2008-04-10 Fujishima Kensetsu:Kk Drainage filtration system
JP4587401B2 (en) * 2006-09-29 2010-11-24 有限会社藤島建設 Wastewater filtration system
WO2009150720A1 (en) * 2008-06-10 2009-12-17 冨安洋子 Sewage purification system and method of growing plant by using the purification system
JP2017094303A (en) * 2015-11-26 2017-06-01 株式会社竹中工務店 Storage-purification system

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