[go: up one dir, main page]

JPS5857567B2 - Rainwater infiltration prevention device at garbage landfill - Google Patents

Rainwater infiltration prevention device at garbage landfill

Info

Publication number
JPS5857567B2
JPS5857567B2 JP53141493A JP14149378A JPS5857567B2 JP S5857567 B2 JPS5857567 B2 JP S5857567B2 JP 53141493 A JP53141493 A JP 53141493A JP 14149378 A JP14149378 A JP 14149378A JP S5857567 B2 JPS5857567 B2 JP S5857567B2
Authority
JP
Japan
Prior art keywords
layer
landfill
soil
garbage
synthetic resin
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
Application number
JP53141493A
Other languages
Japanese (ja)
Other versions
JPS5568934A (en
Inventor
かね子 黒瀬
正 新見
正則 新見
宣親 林
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP53141493A priority Critical patent/JPS5857567B2/en
Publication of JPS5568934A publication Critical patent/JPS5568934A/en
Publication of JPS5857567B2 publication Critical patent/JPS5857567B2/en
Expired legal-status Critical Current

Links

Landscapes

  • Pit Excavations, Shoring, Fill Or Stabilisation Of Slopes (AREA)
  • Revetment (AREA)
  • Processing Of Solid Wastes (AREA)

Description

【発明の詳細な説明】 本発明はゴミ埋立地に於ける雨水浸透防止、特に埋立地
内に発生したガスを抜きながら雨水の下層浸透を防止す
る装置に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a device for preventing rainwater infiltration in a garbage landfill, and in particular, to a device for preventing rainwater from infiltrating into the lower layer while removing gas generated in the landfill.

現在、ゴミは全国で焼残査も含めて約15万tが埋立処
分されている。
Currently, approximately 150,000 tons of garbage, including incineration residue, is disposed of in landfills nationwide.

この埋立されている全国3.000ケ所の埋立地での残
余埋立容量は2億5千万Mしかないので、数年のうちに
埋め尽されてし筐い、新たな埋立地を確保しなければな
らない状態になっている。
The remaining landfill capacity of the 3,000 landfill sites nationwide is only 250 million M, so it will be full within a few years and new landfill sites will have to be secured. is in a state.

中間処理として焼却、固化する方法を増大させてみても
、最終処分地としての埋立地が必要でなくなる訳でもな
く、筐た事業系の廃棄物を含めると大変な処分地を必要
とし、都市部で新たな埋立地を探す事はもう殆んど不可
能であり、地方の農村部や内陸地、海岸地域に用地を求
めねばならなくなった。
Even if we increase the use of incineration and solidification as intermediate treatment, it does not eliminate the need for landfills as final disposal sites, and if business waste is included, a large amount of disposal site will be required, and urban areas It is now almost impossible to find new landfill sites in the region, and land must now be sought in rural areas, inland areas, and coastal areas.

しかしながら、今昔での法律によって義務付けられてい
るゴミと覆土とを交互に重層して行く、いわゆるサンド
インチ方式ではガスの発生、衛生害虫の発生、地下水汚
染、浸出汚水等の第2次公害の心配から、用地確保を一
層困難にしている。
However, with the so-called sand-inch method, which alternately layers garbage and soil as required by law, there are concerns about secondary pollution such as gas generation, sanitary pests, groundwater contamination, and leachate sewage. This makes securing land even more difficult.

上記のうちガスの発生問題は覆土中でのガス抜き工法に
よっである程度の対策が出来てpす、芽た衛生害虫の対
策としては一部分に埋立作業を集中し、可能な限り早期
に覆土したり、天敵や殺虫剤を使用することにより略解
決可能となっており、更に地下水汚染対策については埋
立地の底に不透水層を設けることを義務付けることによ
って解決している。
Among the above problems, the problem of gas generation can be countered to some extent by degassing methods during soil covering.As a countermeasure against sanitary pests that have sprouted, it is necessary to concentrate the landfill work on one area and cover the soil as early as possible. The problem can be almost solved by using natural enemies or insecticides, and groundwater contamination can be countered by requiring the installation of an impermeable layer at the bottom of a landfill.

第1図は陸上谷間に於けるゴミ埋立地の在来技術による
埋立完成の断面図である。
Figure 1 is a cross-sectional view of a completed garbage landfill in an onshore valley using conventional technology.

1は埋立前の谷間の地表面であって、その表面上にコン
クリド張り又は合成樹脂膜張り等の不透水層部分2を敷
設する。
Reference numeral 1 indicates the ground surface of the valley before reclamation, and an impermeable layer portion 2 such as a concrete layer or a synthetic resin layer is laid on the surface.

地表面1が岩盤面である場合には上記不透水層部分2は
1略可能である。
When the ground surface 1 is a bedrock surface, the impermeable layer portion 2 can be approximately 1.

3は最初のゴミ埋立部分であって、2〜4m厚さの第1
ゴミ埋立層であり、その上に山上、砂等を0.5 m程
度の厚さに第1覆土層4を覆設する。
3 is the first landfill part, and the first part is 2 to 4 meters thick.
This is a garbage reclamation layer, and a first soil covering layer 4 of about 0.5 m thick is placed on top of it, such as mountain top, sand, etc.

5は第2ゴミ埋立層、6は第2覆土層、Tは第3ゴミ埋
立層であり、最初の第1層と略同に厚さで成層させ、最
後に1〜3m程度の仕上覆土層8を施工する。
5 is the second landfill layer, 6 is the second soil covering layer, and T is the third landfill layer, which are layered with approximately the same thickness as the first layer, and finally a finishing soil covering layer of about 1 to 3 meters. 8 will be constructed.

9はガス抜き部分でその末端は自刃で燃焼させるように
なっている。
9 is the gas venting part, and the end is designed to burn with its own blade.

10は埋立地内外の雨水を集水して排水する側溝であり
、11は埋立層内を浸透し、不透水層部分2を流下して
来る汚水を集水し排水する集排水管である。
Reference numeral 10 is a side gutter that collects and drains rainwater inside and outside the landfill, and reference numeral 11 is a collection and drainage pipe that collects and drains wastewater that permeates through the landfill layer and flows down the impermeable layer portion 2.

以上のような従来の構造であると、雨水Aは表流水B及
び蒸発散水Cとして埋立地外に消失し、差引いたものが
仕上覆土層3内に浸入し、この量は全国平均500 l
/m2年程にもなる。
With the conventional structure as described above, rainwater A disappears outside the landfill as surface water B and evapotranspiration water C, and the subtracted amount infiltrates into the finishing soil cover layer 3, which is an average of 500 liters nationwide.
/m2 years.

浸入雨水aは埋立層の各層を浸透し、最終的に集排水管
11に集まるのであるが、この浸出汚水ばBODにして
、埋立後数ケ月たって10.000ppm前後と非常に
高濃度で黒褐色のゴ□臭を有する汚染度の高いものであ
るが、1年後は1.000ppm、3年後は1100p
pと次第に低下する。
The infiltrated rainwater a permeates through each layer of the landfill layer and finally collects in the collection and drainage pipe 11, but this leached sewage becomes BOD, and several months after the landfill, it becomes blackish brown with a very high concentration of around 10,000 ppm. It is highly contaminated with a gory odor, but after 1 year it is 1.000ppm and after 3 years it is 1100ppm.
p gradually decreases.

捷た種種の重金属も当初は高濃度に含捷れてお・す、公
害防止の面から上記重金属対策が最重要となっている。
The various types of heavy metals that are separated are initially contained in high concentrations, making countermeasures against the above-mentioned heavy metals the most important from the perspective of pollution prevention.

上記高濃度汚染に対しては従来でもその対策がとられて
いなかった訳でもない。
It is not as if countermeasures have not been taken in the past against the above-mentioned high-concentration pollution.

例えば、仕上覆土層8内への雨水浸入防止方法として仕
上覆土層8を中高として丑わりに下降傾斜するよう勾配
を設け、表流水Bが多くなる様装置されているものもあ
った。
For example, as a method of preventing rainwater from entering the finishing soil covering layer 8, there are devices in which the finishing soil covering layer 8 is set at a medium height and is instead sloped downward to increase surface water B.

これをもつと完壁にするために、仕上覆土層8全体を雨
水が浸透しない舗装構造とする事もなされているが、こ
れでは埋立ゴミから多量に発生するガスの抜道をふさぐ
こととなり、爆発事故の危険性があり、逆にガス抜のた
めに高価な装置を組込筐なければならなくなる等の欠点
があった。
In order to have a complete wall, the entire finishing soil cover layer 8 is made of a paving structure that prevents rainwater from penetrating, but this would block the escape route for the large amount of gas generated from the landfill waste. There is a risk of explosion, and on the other hand, there are drawbacks such as the need to incorporate expensive equipment for gas venting.

上記の様に、浸出汚水の濃度は次第に低下し、いずれは
それほと害のない浸出水になることも考慮すると、その
僅かの期間のために莫大な投資をするのも実用性に欠け
、比較的短時間の利用に対する経済的な新しい技術の開
発が望筐れていた。
As mentioned above, considering that the concentration of leachate sewage will gradually decrease and eventually become leachate that is not harmful, it is impractical to make a huge investment for such a short period of time. It has been desired to develop a new technology that is economical for relatively short-term use.

本発明は、上記要望に応えるためになされたもので、そ
の目的とするところのものはガスは低圧で土壌中を除臭
させながら排気し、雨水は下層のゴミ埋立層に浸透させ
ない装置を提供するにある。
The present invention was made in response to the above-mentioned needs, and its purpose is to provide a device that exhausts gas while deodorizing the soil at low pressure, and prevents rainwater from penetrating into the underlying garbage landfill layer. There is something to do.

上記目的を達成するため、本発明は前記第1図に示す従
来技術に加えて下記の2つの原理を組合わせることにあ
る−即ち、その第1は土壌中を移動する雨水の誘導毛管
水運動に着目し、これを不飽和条件で排水しようとする
ことであり、第2はゴミ埋立層の直上に疎水性の合成樹
脂膜を敷設し、これに多数の小孔を開孔させガスは覆土
中を上昇するが、雨水の浸透は阻止し、横方向に誘導し
て自然に排出させようとすることである。
In order to achieve the above object, the present invention consists in combining the following two principles in addition to the prior art shown in FIG. The second method is to lay a hydrophobic synthetic resin membrane directly above the garbage landfill layer, and drill a large number of small holes in it to drain the gas under unsaturated conditions. The aim is to prevent rainwater from penetrating through the roof, but to guide it laterally and allow it to drain naturally.

以下、本発明の一実施例を第2図以下の図面を参照しな
がら説明する。
Hereinafter, one embodiment of the present invention will be described with reference to the drawings from FIG. 2 onwards.

第2図は多重埋立層の最上層の仕上覆土層8部分を示し
たもので、上記第1図に示す部分と同一のものは同一の
符号を付する。
FIG. 2 shows 8 portions of the topmost finishing soil covering layer of the multiple reclaimed layer, and the same parts as shown in FIG. 1 above are given the same reference numerals.

第2図に於いて、12は合成樹脂膜であって、(第3)
ゴミ埋立層7の上に中央部がわずか低くなる様な勾配を
持たせて敷設されている。
In Fig. 2, 12 is a synthetic resin film, (third)
It is laid on top of the garbage landfill layer 7 with a slope so that the central part is slightly lower.

該合成樹脂膜12には第5図aに示すように多数の小孔
12aが穿設されている。
The synthetic resin membrane 12 is provided with a large number of small holes 12a, as shown in FIG. 5a.

この/J”?L 12 aの大きさはその上層の仕上覆
土層8の土壌の粒径より僅かに小さく、土壌がこの小孔
12aから落下しないようにしである。
The size of /J"?L 12a is slightly smaller than the grain size of the soil in the upper finishing soil cover layer 8, so as to prevent the soil from falling through the small holes 12a.

また、上記合成樹脂膜12は疎水性膜である。Further, the synthetic resin film 12 is a hydrophobic film.

合成樹脂膜12の中央凹部には排水管13が配設されて
いて、その周囲には砂利層14が設けである。
A drainage pipe 13 is provided in the central recess of the synthetic resin membrane 12, and a gravel layer 14 is provided around it.

15は覆土8が砂利層14内に落下して四詰芽りしない
ように覆設されたアミ又は不織布等である。
Reference numeral 15 is a material such as mesh or nonwoven fabric that is covered to prevent the covering soil 8 from falling into the gravel layer 14 and causing budding.

排水管13からの汚水は自然排流でも、又はポンプ等で
強制排出しても良い。
The wastewater from the drain pipe 13 may be drained naturally or may be forcibly discharged using a pump or the like.

本実施例の装置は以上のように構成されているので、雨
水Aの一部は表流水B及び蒸発散水Cとして消失し、残
りは仕上覆土層8内に浸透する。
Since the apparatus of this embodiment is configured as described above, a part of the rainwater A disappears as surface water B and evapotranspiration water C, and the rest permeates into the finishing soil cover layer 8.

浸透した雨水aは第4図すに示すように境界面の合成樹
脂膜12から高く上るにしたがって水分率は減少する。
As shown in FIG. 4, the moisture content of the permeated rainwater a decreases as it rises higher from the synthetic resin film 12 on the boundary surface.

誘導毛管水は不飽和度の高いところに重力差で横方向に
移動する特性があるので、合成樹脂膜12にある程度の
勾配を持たせて釦くと、水分率は土壌が一定であれば一
定の曲線を有した状態で第4図aの矢印a、 、 a2
の如く斜め横方向に不飽和な毛管現象で移動する。
Induced capillary water has the characteristic of moving laterally due to the difference in gravity in areas with a high degree of unsaturation, so if the synthetic resin membrane 12 is pressed with a certain slope, the moisture content will remain constant as long as the soil is constant. Arrows a, , a2 in Figure 4 a with curves of
It moves diagonally and horizontally by unsaturated capillary action.

捷た、合成樹脂膜120表面上を流れる汚水は脂膜12
が疎水性膜のためその1J4L 12 aの所で第5図
aに示す如く凸状となった状況を呈し、重力水であって
も落下し難い特色を有する。
The waste water flowing on the surface of the shredded synthetic resin membrane 120 is a lipid membrane 12.
Because it is a hydrophobic membrane, it exhibits a convex shape at 1J4L 12a as shown in FIG.

これに対して、親水性膜であると、第5図すに示す如く
小孔12a′の所で凹状となって落下してしまうことに
なる。
On the other hand, if the membrane is hydrophilic, it will become concave at the small holes 12a' and fall, as shown in FIG.

尚、上記小孔12aの直径、位置、間隔等は覆土の性質
、ガス量等によって実験に基づいて決定するのが良い。
The diameter, position, spacing, etc. of the small holes 12a are preferably determined based on experiments, depending on the nature of the covering soil, the amount of gas, etc.

一方、ゴミ埋立層7内で発生したガスは上記小孔12a
を通過して上昇排気され、その一部はガス抜き9により
土壌外に排気されることもある。
On the other hand, the gas generated in the garbage landfill layer 7 is absorbed by the small holes 12a.
A part of it may be exhausted to the outside of the soil through a gas vent 9.

上記合成樹脂膜12は最上層だげでなく、中間層例えば
第3図に示すように第2ゴミ埋立層6との間にも敷設し
てもよく、その作用効果は上記第■の実施例とほぼ同様
である。
The synthetic resin film 12 may be provided not only in the uppermost layer but also in an intermediate layer, for example, between the second landfill layer 6 as shown in FIG. It is almost the same as

筐た、浸出汚水を覆土中に再循環させて土壌浄化させる
工法を組合わせることも効果的である。
It is also effective to combine methods of soil purification by recirculating leached wastewater into soil cover.

本発明は、以上のように雨水がゴミ中に浸入する機会を
出来るたけ阻止するようになっているので、浸出汚水の
水質が低濃度となって重金属の溶出を少量に止め得るの
みならず、ゴミ層内を好気的条件に維持し、ゴミ0分解
を早めるとともに、時には排水管を利用して、逆送気し
て上記好気的条件を強制的に作り出すことも可能である
等数多くの利点がある。
As described above, the present invention is designed to prevent rainwater from entering garbage as much as possible, so not only can the quality of the leachate sewage be reduced to a low concentration and the elution of heavy metals can be kept to a small amount. It is possible to maintain aerobic conditions within the garbage layer, speed up garbage decomposition, and sometimes use drainage pipes to force back air to create the aerobic conditions mentioned above. There are advantages.

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

第1図は従来の陸上埋立地の完成断面図、第2図は本発
明の一実施例を示す断面図、第3図は別の実施例の断面
図、第4図aは覆土中の水の流れの説明図、第4図すは
水分率を示すグラフ、第5図aは本発明の疎水性合成樹
脂膜の拡大断面図、第5図すは親水性膜の断面図である
。 1・・・・・・地表面、2・・・・・・不透水層部分、
3,5゜7・・・・・・ゴミ埋立層、4,6.8・・・
・・・覆土層、12・・・・・・合成樹脂膜、12a・
・・・・・小孔。
Fig. 1 is a completed sectional view of a conventional land-based landfill, Fig. 2 is a sectional view showing one embodiment of the present invention, Fig. 3 is a sectional view of another embodiment, and Fig. 4a shows water in the covered soil. FIG. 4 is a graph showing the moisture content, FIG. 5a is an enlarged sectional view of the hydrophobic synthetic resin membrane of the present invention, and FIG. 5 is a sectional view of the hydrophilic membrane. 1... Ground surface, 2... Impermeable layer part,
3,5゜7... Garbage landfill layer, 4,6.8...
...Soil covering layer, 12...Synthetic resin film, 12a.
...Small hole.

Claims (1)

【特許請求の範囲】[Claims] 1 ゴミ埋立層と覆土層とを積層した埋立地に於て、上
記ゴミ埋立層と覆土層との間に、多数の小孔を穿設させ
た疎水性合成樹脂膜を敷設して、ゴミ埋立部分への雨水
の浸透を防止し、且つ小孔よりガス抜きさせることを特
徴とするゴ□埋立地に於ける雨水浸透防止装置。
1. In a landfill where a garbage landfill layer and a soil covering layer are laminated, a hydrophobic synthetic resin membrane with a large number of small holes is laid between the garbage landfill layer and the soil covering layer. A device for preventing rainwater infiltration in a Go□ landfill, which is characterized by preventing rainwater from infiltrating into the area and allowing gas to be released through small holes.
JP53141493A 1978-11-16 1978-11-16 Rainwater infiltration prevention device at garbage landfill Expired JPS5857567B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP53141493A JPS5857567B2 (en) 1978-11-16 1978-11-16 Rainwater infiltration prevention device at garbage landfill

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP53141493A JPS5857567B2 (en) 1978-11-16 1978-11-16 Rainwater infiltration prevention device at garbage landfill

Publications (2)

Publication Number Publication Date
JPS5568934A JPS5568934A (en) 1980-05-24
JPS5857567B2 true JPS5857567B2 (en) 1983-12-21

Family

ID=15293199

Family Applications (1)

Application Number Title Priority Date Filing Date
JP53141493A Expired JPS5857567B2 (en) 1978-11-16 1978-11-16 Rainwater infiltration prevention device at garbage landfill

Country Status (1)

Country Link
JP (1) JPS5857567B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0510959A (en) * 1991-07-04 1993-01-19 Sanuki Kogyo Kk Compound liquid mixture feeding device for physical/ chemical machine

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0510959A (en) * 1991-07-04 1993-01-19 Sanuki Kogyo Kk Compound liquid mixture feeding device for physical/ chemical machine

Also Published As

Publication number Publication date
JPS5568934A (en) 1980-05-24

Similar Documents

Publication Publication Date Title
US5857807A (en) Municipal solid waste landfill system
US5201609A (en) Cellular landfill process and apparatus
US4844813A (en) System and process for treatment of biodegradable waste
JPS6087101A (en) Noxious waste container and method thereof
US5183355A (en) Method of draining water through a solid waste site without leaching
Salvato et al. Sanitary landfill-leaching prevention and control
Rowe From the past to the future of landfill engineering through case histories
JP4066538B2 (en) Waste disposal site
JPS5857567B2 (en) Rainwater infiltration prevention device at garbage landfill
JP3770526B2 (en) Waste burial structure and burial method
JPS5837447B2 (en) Landfill disposal method for city garbage, etc.
JPS61101288A (en) Treatment for converting noxious waste to reclaiming material
JPS6223494A (en) Recirculation type quasi-aerobic reclaiming construction method
JP2500690B2 (en) Waste disposal structure and waste disposal method
JPH0295489A (en) Final garbage disposal method in garbage disposal plant
JP2844975B2 (en) Final cover method at waste disposal site
JP3354920B2 (en) Final earth covering method at the final waste disposal site
JPH04367775A (en) Method and sheet for landfilling treatment of waste
JP4780550B2 (en) Covering method for landfill waste and seepage water capillary barrier layer for landfill waste
JP2842173B2 (en) Deep waste disposal site
JPH0154110B2 (en)
JP3847446B2 (en) Waste disposal site
JP3047377U (en) Final waste disposal facility structure that prevents groundwater contamination and simplifies maintenance after landfill completion
JP2002177917A (en) Waste disposal plant
JPH05138143A (en) Final covering method for waste disposition field