JPS61101298A - Trench shaped rainwater treatment apparatus - Google Patents

Trench shaped rainwater treatment apparatus

Info

Publication number
JPS61101298A
JPS61101298A JP22459484A JP22459484A JPS61101298A JP S61101298 A JPS61101298 A JP S61101298A JP 22459484 A JP22459484 A JP 22459484A JP 22459484 A JP22459484 A JP 22459484A JP S61101298 A JPS61101298 A JP S61101298A
Authority
JP
Japan
Prior art keywords
rainwater
layer
trench
chamber
duct
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
JP22459484A
Other languages
Japanese (ja)
Other versions
JPS6363040B2 (en
Inventor
Shigekazu Kurata
倉田 繁和
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.)
NAGANO EKIKA KK
Original Assignee
NAGANO EKIKA KK
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 NAGANO EKIKA KK filed Critical NAGANO EKIKA KK
Priority to JP22459484A priority Critical patent/JPS61101298A/en
Publication of JPS61101298A publication Critical patent/JPS61101298A/en
Publication of JPS6363040B2 publication Critical patent/JPS6363040B2/ja
Granted legal-status Critical Current

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Abstract

PURPOSE:To enhance oxidation capacity of an org. substance and to attain to reduce cost, by arranging a purification treatment apparatus equipped with both of an aerobic chamber and an anaerobic chamber to a flow channel capable of stably flowing rainwater largely varying in a flow amount. CONSTITUTION:Rain water flows through the flow channel formed by a U-shaped trench 3 to be penetrated into the circumference from a crushed stone layer 2 through a gravel layer 6. Rainwater contains a large quantity of foreign matter or contaminant but aerobic bacteria in soil can be actively propagated in the aerobic chamber 10 of a duct 4 and almost all of org. substances or suspended matters in rainwater can be removed by decompositional treatment. Denitrifying bacteria are actively propagated in the anaerobic chamber of the duct 4 by using carbon C of charcoal 9 as an energy source and decompose ammoniacal nitrogen in rainwater to nitrogen gas.

Description

【発明の詳細な説明】 [発明の技術分野] 本発明は、雨水中の異物や汚染物質を除去して浄化した
雨水を地中に浸透できるようにしたトレンチ溝型雨水処
理装置に関する。
DETAILED DESCRIPTION OF THE INVENTION [Technical Field of the Invention] The present invention relates to a trench-type rainwater treatment device that allows purified rainwater to penetrate underground by removing foreign matter and pollutants from the rainwater.

[発明の技術的背景とその問題点] 周知の如く、降雨水の殆んどは湖用や下水道を経て流れ
たり、地中に吸い込まれるが、このうち地中に浸入した
雨水は地下水として貯溜状態となる。
[Technical background of the invention and its problems] As is well known, most of the rainwater flows through lakes and sewers, or is sucked into the ground, but the rainwater that seeps into the ground is stored as groundwater. state.

従って、多量の雨水は極力地下へ導入することが望まし
いことであり、その手段としては例えば平面拡散方式、
深井戸方式等がある。平面拡散方式とは水田、池等によ
るものであって、上部利用が不可能な広い面積を占有す
るという問題がある。
Therefore, it is desirable to introduce a large amount of rainwater underground as much as possible.
There are deep well methods, etc. The planar diffusion method uses rice fields, ponds, etc., and has the problem of occupying a large area that cannot be used above.

又、そこに流入して来た水流により土砂が巻上げられ、
粒子の大きい重たいものから順次沈降し最後にコロイド
状の細い粒子が沈降する結果、池等の底面が膜で覆われ
たようになり水を捌けさせない所謂る目詰り状態となっ
て、水溜りが生じ、地下への浸透機能が低下する。一方
探井戸方式も上記目詰り状態を避けることができない。
In addition, the water flow that flowed into the area stirred up earth and sand,
As a result, the large and heavy particles settle in order, and the colloidal thin particles settle at the end.As a result, the bottom of the pond, etc. becomes covered with a membrane, creating a so-called clogged state that prevents water from draining. This results in a decline in the ability to penetrate underground. On the other hand, the well exploration method cannot avoid the above-mentioned clogging condition.

その上、地表面を流下して、ゴミや汚染物質を拾って来
た雨水は、もはや汚水であって、それを地下に直接入れ
ることは地下水汚染を進める結果となる。このようなこ
とから、浅い溝の中にパイプや砂利等を充填し、その中
に上記汚水を流し、土中へ散水するようにした毛管浸潤
トレンチが周知である。
Moreover, rainwater that flows down the ground surface and picks up trash and pollutants is no longer sewage, and allowing it directly into the ground will result in further groundwater contamination. For this reason, capillary infiltration trenches are well known in which a shallow trench is filled with pipes, gravel, etc., into which the wastewater is poured and water is sprinkled into the soil.

これは、汚水等が底面鉛直方向の浸透を期待するもので
はなく、トレンチ溝からの側面浸透を期するものであり
、且つ土中で繁殖している微生物により汚水中の汚染物
質を分解処理させ浄化水として地下に貯水させるように
するものである。この具体的な公知例としては、例えば
特公昭57−54193号公報のトレンチ溝型汚水処理
装置が提供されている。即ち、不透水材で形成された槽
をトレンチ溝の底部に設け、該槽を越える高さに進抄を
充填し、更に砂層の上に礫層と被覆土壌層を順次配置し
1、礫層と被覆土壌層に夫々汚水管と多孔排水管を設け
たトレンチ溝型汚水処理装置に於いて、礫層と被覆土壌
層との境界を凹状としたものである。
This does not expect sewage to permeate vertically to the bottom, but to permeate from the side from the trench, and also allows the microorganisms growing in the soil to decompose and process pollutants in the sewage. The purpose is to store water underground as purified water. As a specific known example, a trench-type sewage treatment device is provided, for example, in Japanese Patent Publication No. 57-54193. That is, a tank made of impermeable material is provided at the bottom of the trench, and the gravel is filled to a height beyond the tank, and a gravel layer and a covering soil layer are sequentially placed on top of the sand layer. In a trench-type sewage treatment system in which a wastewater pipe and a porous drainage pipe are provided in the soil covering layer and the soil covering layer, respectively, the boundary between the gravel layer and the covering soil layer is made concave.

これにより、通常の場合は、汚水管を経て供給された汚
水が礫層から砂層に重力浸透し、更に砂層からトレンチ
溝周囲の土壌へ毛管サイホン作用により浸透して、その
一部は地表面から蒸発敗し、残りは地下水へ浸透補給さ
れる。又、汚水が一時的に多聞供給されると、汚水管か
ら供給された汚水は、礫層の上面から排水管迄浸透上昇
する際に略同じ厚さの被覆土壌層によって均一に逆濾過
される。
As a result, in normal cases, sewage supplied through the sewage pipes permeates by gravity from the gravel layer into the sand layer, and then from the sand layer into the soil around the trench by capillary siphon action, with some of the water coming from the ground surface. It evaporates and the rest is replenished by seepage into groundwater. Furthermore, when sewage is temporarily supplied for a long time, the sewage supplied from the sewage pipe is evenly reverse-filtered through the covering soil layer of approximately the same thickness as it percolates up from the top of the gravel layer to the drainage pipe. .

上記公知例のようなトレンチ溝型汚水処理装置の場合は
、汚水中の異物や一般汚染物を濾過除去乃至分解処理が
できるが、この汚染物質を分解する微生物の繁殖を活発
化するため濾材の好気性が重要である。然し乍ら、汚染
物質中のアンモニア性窒素は、上記好気性の微生物では
分解せず、逆にこれを酸化して亜硝酸性窒素に変化させ
てしまうことになり、それがそのまま地下に浸透し地下
水を汚染してしまう問題があった。
In the case of trench-type sewage treatment equipment such as the above-mentioned known example, foreign matter and general pollutants in wastewater can be filtered out or decomposed, but in order to activate the growth of microorganisms that decompose these pollutants, the filter media is Aerobicity is important. However, ammonia nitrogen in pollutants is not decomposed by the aerobic microorganisms mentioned above, but instead oxidizes and changes into nitrite nitrogen, which permeates underground and drains groundwater. There was a problem with contamination.

特に表土を流下して来た雨水の場合は、実に多種多様な
汚染物を拾って来るため、上記アンモニア性窒素物の存
在は無視できないものであり、一方好気性微生物の繁殖
の活性化も不可欠であるという相反する状態が求められ
るものである。
In particular, in the case of rainwater flowing down from the topsoil, it picks up a wide variety of pollutants, so the presence of ammonia nitrogen cannot be ignored, while activating the reproduction of aerobic microorganisms is also essential. A contradictory state is required.

又、雨水は流量の変動が多大であるから、多口の雨水が
流入して来た場合、公知例のような管路では対応できず
、その上連通しだ長尺の排水管を必要とし且つ排水管と
汚水管を夫々要する為設備コストが嵩むという問題があ
った。
In addition, since the flow rate of rainwater fluctuates greatly, when a large amount of rainwater flows in, it is not possible to deal with the inflow of rainwater using conventional pipes, and in addition, long drainage pipes are required to communicate with the system. In addition, there was a problem in that the equipment cost increased because a drain pipe and a sewage pipe were each required.

[発明の目的] 本発明は叙上の問題に鑑み成されたもので、流量変動が
多大な雨水を安定して流すことが出来る流路に、好気室
と嫌気室が兼備された浄化処理装置を付設して、好気性
の微生物の繁殖をより活発化させ雨水中の有機物(BO
D)(COD)の酸化能力を非常に高くすると共に、嫌
気性の脱窒菌による亜硝酸性窒素や硝酸性窒素の殆んど
を窒素ガスに迄分解するようにし、且つ、簡素な構成に
よる廉価性を具備させたトレンチ溝型雨水処理装置の提
供を目的とするものである。
[Purpose of the Invention] The present invention has been made in view of the above-mentioned problems, and is a purification process that has both an aerobic chamber and an anaerobic chamber in a flow path that can stably flow rainwater that has a large flow rate fluctuation. A device is attached to make the reproduction of aerobic microorganisms more active and reduce organic matter (BO) in rainwater.
D) The oxidizing ability of (COD) is extremely high, and most of the nitrite nitrogen and nitrate nitrogen are decomposed into nitrogen gas by anaerobic denitrifying bacteria, and the cost is low due to the simple structure. The purpose of the present invention is to provide a trench-type rainwater treatment device that is equipped with the following features.

[発明の概要コ 上記目的を達成するため本発明に係るトレンチ溝型雨水
処理装置は、トレンチ溝の底部に砕石を敷設し、その表
層にU字溝を伏せた状態で配置し、且つ該U字溝の上に
は、炭等有橢物が充填された嫌気室と空胴状の好気室を
具備する浄化処理装置を配設し、更に該U字溝乃至砕石
層の上にPJ層と通気土壌層を順次積層形成した構成と
しである。
[Summary of the Invention] In order to achieve the above object, a trench type rainwater treatment device according to the present invention is provided by laying crushed stone at the bottom of a trench, placing a U-shaped groove face down on the surface layer thereof, and Above the U-shaped groove, a purification treatment device comprising an anaerobic chamber filled with charcoal and other sludge and a hollow aerobic chamber is installed, and a PJ layer is installed above the U-shaped groove or the crushed stone layer. It has a structure in which layers of soil and aerated soil are laminated in sequence.

[発明の構成] 以下に本発明の実施例を図面に基づき説明する。[Structure of the invention] Embodiments of the present invention will be described below based on the drawings.

地中に形成したトレンチ溝1は、周知のものと同様に細
く浅く長い構造のものであって、幅員や深さは600〜
800mm程度である。これはトレンチ溝1が深すぎる
と、側面積が増えて、側面浸透機能が増加する反面、有
機物を分解する微生物や植物根が少ない為浄化機能が低
下し、又、幅員を広げすぎても貯溜能力を増加させ得る
が、側面浸透機能は変らず、占積効率が悪いものとなる
The trench groove 1 formed underground has a narrow, shallow and long structure similar to well-known ones, and has a width and depth of 600 mm to 60 mm.
It is about 800mm. This is because if the trench groove 1 is too deep, the lateral area increases and the lateral infiltration function increases, but on the other hand, the purification function decreases because there are few microorganisms and plant roots that decompose organic matter, and if the trench groove 1 is made too wide, it will not accumulate water. Although the capacity can be increased, the side penetration function remains unchanged and the space efficiency becomes poor.

而して、該トレンチ溝1内には、その底部に砕石2を1
00〜200mm程度の厚さに敷詰め濾床を形成しであ
る。該砕石2の表層には、断面U字形で長さ1,000
mm程度のコントリート類、又は陶器製のU字溝3を、
多数人々伏せた状態で配列し一本の流路を形成してあり
、且つ各々のU字溝3の間に所定の距離Aを残しである
In the trench groove 1, one piece of crushed stone 2 is placed at the bottom of the trench groove 1.
A filter bed is formed with a thickness of about 00 to 200 mm. The surface layer of the crushed stone 2 has a U-shaped cross section and a length of 1,000 mm.
Contour type or ceramic U-shaped groove 3 of about mm,
A large number of people are arranged face down to form one flow path, and a predetermined distance A is left between each U-shaped groove 3.

又、一定の間隔でU字溝3の間に通気パイプ4を立設し
てあって、該通気バイブ4の上端開口部を地表面(GL
)に臨ませである。上記U字溝3の上には、強化プラス
チック(FRO)等によりU字溝3と同長で断面逆U字
形に成形されたダクト5が配設され、該ダクト5及びU
字溝3の上面乃至砕石2の上面に、礫層6を所定の厚さ
で敷きつめてあり、その表層に張設した網7を介し地表
面(GL)の逃逸通気土壌8を充填しである。
In addition, ventilation pipes 4 are installed between the U-shaped grooves 3 at regular intervals, and the upper end opening of the ventilation vibe 4 is connected to the ground surface (GL
). A duct 5 made of reinforced plastic (FRO) or the like is disposed above the U-shaped groove 3 and is formed to have the same length as the U-shaped groove 3 and an inverted U-shaped cross section.
A gravel layer 6 is laid down to a predetermined thickness on the upper surface of the groove 3 or the upper surface of the crushed stones 2, and the escape aeration soil 8 from the ground surface (GL) is filled through a net 7 stretched over the surface layer. .

上記ダクト5の内部は、その上段室内に脱窒菌が活性化
する有撮材、例えば木炭や石炭等の炭9を充填して嫌気
室を形成すると共に、その下段室内は空胴状として通気
性を保持せしめた好気室10にしである。更にダクト4
の上部即ち嫌気室の頂部には、複数のスリット11を穿
設して外部と連通させてあり、又、ダクト4の下部即ち
好気室10の側面には多数の角孔12を連設して外部と
連通させである。
Inside the duct 5, an anaerobic chamber is formed by filling the upper chamber with a material that activates denitrifying bacteria, such as charcoal 9 such as charcoal or coal, and the lower chamber is hollow to provide ventilation. This is in the aerobic chamber 10 which is held. Furthermore, duct 4
In the upper part of the duct 4, that is, the top of the anaerobic chamber, a plurality of slits 11 are bored to communicate with the outside, and in the lower part of the duct 4, that is, the side of the aerobic chamber 10, a number of square holes 12 are formed in series. and communicate with the outside.

以上の構成に於いて、雨水はU字溝3で形成された流路
を流れ砕石層2乃至礫層6を介し周囲に浸透する。この
雨水は前記した如く多量の異物や汚染物質を含有するも
のであるが、ダクト4の好気室10によって土壌中の好
気性微生物の繁殖を極めて活発にさせることができるか
ら、該雨水中の有機物質(BOD)(COD)や浮遊物
質(SS)等の殆んどを分解処理して除去できる。一方
、ダクト4の嫌気室では、そこに充填されている炭9の
炭素Cをエネルギー源にして脱窒菌が繁殖し、且つより
活発化させることができるので、雨水中に残存するアン
モニア性窒素(NH3−N)が酸化されて亜硝酸性窒素
(NO2−N>や硝酸性窒素(NO3−N)も、その殆
んどを窒素ガスに迄分解させることができる。
In the above configuration, rainwater flows through the channel formed by the U-shaped groove 3 and penetrates into the surrounding area through the crushed stone layer 2 to the gravel layer 6. This rainwater contains a large amount of foreign matter and pollutants as described above, but since the aerobic chamber 10 of the duct 4 can make the reproduction of aerobic microorganisms in the soil extremely active, the rainwater contains a large amount of foreign matter and pollutants. Most organic substances (BOD) (COD) and suspended solids (SS) can be decomposed and removed. On the other hand, in the anaerobic chamber of duct 4, denitrifying bacteria can propagate and become more active using the carbon C of the charcoal 9 filled there as an energy source, so that the ammonia nitrogen ( By oxidizing NH3-N), most of nitrite nitrogen (NO2-N> and nitrate nitrogen (NO3-N)) can be decomposed into nitrogen gas.

このようにU字溝3近傍で微生物により分解処理されて
気化した排気物(ガス)は、PJ層6や通気土壌8を介
して拡散蒸発したり、通気バイブ4から地表面(GL)
の外に排出除去させ1qるので、地下水には浄化処理水
のみが浸透する。このように、従来のトレンチ溝型処理
装置と比較しても大巾に処理効率が向上し、又、雨水の
流量が急増してもその流路が密閉された管路でないため
、礫層6乃至砕石2内に浸透貯溜されることになり、支
障をきたす虞れは無い。
In this way, the exhaust gas (gas) decomposed and vaporized by microorganisms in the vicinity of the U-shaped groove 3 is diffused and evaporated via the PJ layer 6 and the aerated soil 8, or is transferred from the aeration vibrator 4 to the ground surface (GL).
Since the water is discharged and removed outside the water, only purified water permeates into the groundwater. In this way, the treatment efficiency is greatly improved compared to the conventional trench type treatment equipment, and even if the flow rate of rainwater increases rapidly, the flow path is not a sealed pipe, so the gravel layer 6 Since it will percolate and be stored in the crushed stone 2, there is no risk of causing any trouble.

又、施工に際してもトレンチ溝1内にダクト4が付設さ
れているU字溝3を配列するだけであるから、資材コス
トと相俟って@価に処理できる。
Moreover, since the U-shaped grooves 3 to which the ducts 4 are attached are simply arranged in the trench groove 1 during construction, the cost of materials can be reduced as well.

[発明の効果] 以上説明したように本発明によれば、好気室と嫌気室を
夫々具備せしめたダクト状の浄化処理装置をU字溝に添
設し、且つこれ等を所定間隔で以ってトレンチ溝内に連
設しであるから、流量の変動が多大な雨水を処理するの
にも適しており、又、汚水化した雨水中の有機物質や浮
遊物質等は、そその殆んどを好気性の微生物により分解
処理され、更に、亜硝酸性窒素や硝酸性窒素等も嫌気性
の脱窒菌により窒素ガスに迄分解処理せしめ、地下水の
汚染を確実に防止できる上、施工に際してのコストも廉
価であるという効果がある。
[Effects of the Invention] As explained above, according to the present invention, a duct-shaped purification device equipped with an aerobic chamber and an anaerobic chamber is attached to a U-shaped groove, and these are connected at predetermined intervals. Since the trenches are connected in series within the trench, they are suitable for treating rainwater with large fluctuations in flow rate, and most of the organic substances and suspended substances in the rainwater that has become sewage are removed. In addition, nitrite nitrogen, nitrate nitrogen, etc. are decomposed into nitrogen gas by anaerobic denitrifying bacteria, which not only reliably prevents groundwater contamination, but also makes it easy to use during construction. It also has the effect of being inexpensive.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は本発明の実施例に係るトレンチ溝型雨水処理装
置の部分断面図であり、第2図は同上装置の施工状態を
示す縦断面図である。 1・・・トレンチ溝  2・・・砕石(層)3・・・U
字溝    4・・・ダクト5・・・通気バイブ  6
・・・礫層 8・・・通気土壌   9・・・炭 10・・・好気室
FIG. 1 is a partial sectional view of a trench type rainwater treatment device according to an embodiment of the present invention, and FIG. 2 is a longitudinal sectional view showing the construction state of the same device. 1...Trench groove 2...Crushed stone (layer) 3...U
Groove 4...Duct 5...Ventilation vibe 6
...Gravel layer 8...Aerated soil 9...Charcoal 10...Aerobic chamber

Claims (1)

【特許請求の範囲】[Claims] トレンチ溝の底部に砕石を敷設し、その表層にU字形に
成形された多数のU字溝を伏せた状態で且つ所定の間隙
を残して連設し、又、炭等が充填された嫌気室と空胴状
の好気室とを上下2層に区割形成させ夫々を外部と連通
させたダクト状の浄化処理装置を、該U字溝の頂部に添
設し、この周囲乃至前記砕石層上面に所定厚さの礫層と
通気土壌層を順次積層してなるトレンチ溝型雨水処理装
置。
Crushed stone is laid at the bottom of the trench groove, and a number of U-shaped grooves formed in a U-shape are placed face down on the surface layer, leaving a predetermined gap, and an anaerobic chamber filled with charcoal, etc. A duct-like purification device is attached to the top of the U-shaped groove, in which a hollow aerobic chamber is divided into two layers, upper and lower, and each layer is communicated with the outside. A trench-type rainwater treatment device consisting of a gravel layer of a predetermined thickness and an aerated soil layer layered in sequence on the upper surface.
JP22459484A 1984-10-24 1984-10-24 Trench shaped rainwater treatment apparatus Granted JPS61101298A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP22459484A JPS61101298A (en) 1984-10-24 1984-10-24 Trench shaped rainwater treatment apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP22459484A JPS61101298A (en) 1984-10-24 1984-10-24 Trench shaped rainwater treatment apparatus

Publications (2)

Publication Number Publication Date
JPS61101298A true JPS61101298A (en) 1986-05-20
JPS6363040B2 JPS6363040B2 (en) 1988-12-06

Family

ID=16816171

Family Applications (1)

Application Number Title Priority Date Filing Date
JP22459484A Granted JPS61101298A (en) 1984-10-24 1984-10-24 Trench shaped rainwater treatment apparatus

Country Status (1)

Country Link
JP (1) JPS61101298A (en)

Also Published As

Publication number Publication date
JPS6363040B2 (en) 1988-12-06

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