JP4688595B2 - Waste disposal site - Google Patents

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JP4688595B2
JP4688595B2 JP2005204634A JP2005204634A JP4688595B2 JP 4688595 B2 JP4688595 B2 JP 4688595B2 JP 2005204634 A JP2005204634 A JP 2005204634A JP 2005204634 A JP2005204634 A JP 2005204634A JP 4688595 B2 JP4688595 B2 JP 4688595B2
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water
landfill
oxygen
waste
landfill tank
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JP2007021310A (en
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押方利郎
海老原正明
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Taisei Corp
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Taisei Corp
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Description

本発明は、廃棄物処分場に関するものである。   The present invention relates to a waste disposal site.

例えば図5に示すように周囲に構築した周壁aの内部空間を複数の仕切壁bで仕切って複数の埋立槽cを構築し、各埋立槽c内に順次廃棄物を投入して処理してゆく廃棄物処分場が知られている。
特開2003−136032
For example, as shown in FIG. 5, a plurality of landfill tanks c are constructed by dividing the internal space of the peripheral wall a constructed around by a plurality of partition walls b, and waste is sequentially put into each landfill tank c and processed. A long-term waste disposal site is known.
JP 2003-136032 A

前記した従来の廃棄物処分場にあっては、次のような問題点がある。
<1> 各埋立槽cを仕切る仕切壁bは、片方の埋立槽が満杯で、他方が空であっても倒壊しないだけの強度を持たせる必要があり、大きい強度の擁壁を構築する必要があった。
<2> 埋立て中に雨水の浸入を避けるために埋立槽aは屋根dで覆う必要があり、屋根dの長さが長くなると高価になる。そこで埋て立る容量を増やし、かつ屋根dのスパンを短くすることで屋根dのコストを抑えようとすると、埋立槽cの分割数が増加し、仕切壁bの数も増えるから結局は廃棄物処分場全体のコストが下がらない、という問題があった。
<3> すべての埋立槽cに水を張ると仕切壁bの応力を小さく設計することができる。しかし水中へ廃棄物を投入すると嫌気性状態になって水質が悪化するとともに、廃棄物の安定化に弊害が生じる。さらに硫化水素ガスなどの有毒ガスの発生、メタンガスなどの可燃ガスの発生などの問題が生じる可能性があった。
The conventional waste disposal site described above has the following problems.
<1> The partition wall b that separates each landfill tank c needs to be strong enough not to collapse even if one of the landfill tanks is full and the other is empty, and it is necessary to construct a retaining wall with high strength. was there.
<2> The landfill tank a needs to be covered with the roof d in order to avoid the intrusion of rainwater during the landfill, and becomes expensive as the length of the roof d increases. Therefore, if the capacity of the landfill is increased and the cost of the roof d is reduced by shortening the span of the roof d, the number of divisions of the landfill tank c is increased and the number of partition walls b is also increased. There was a problem that the cost of the entire landfill site could not be reduced.
<3> When all the landfill tanks c are filled with water, the stress of the partition wall b can be designed to be small. However, when waste is thrown into water, it becomes anaerobic and the water quality deteriorates, and the waste is adversely affected. Furthermore, problems such as generation of toxic gases such as hydrogen sulfide gas and generation of flammable gases such as methane gas may occur.

上記のような課題を解決するために、本件出願にかかる第一の発明の廃棄物処理場は、廃棄物の投入前に水の充填してある埋立槽と、埋立槽の水中に廃棄物を投入する投入装置と、埋立槽に供給した水を取り出す、埋立槽の底部に敷設した排水用の集排水管と、取り出した水に酸素富化する酸素富化装置と、酸素富化した水を再度、埋立槽に供給する給水装置とより構成した廃棄物処分場を特徴としたものである。 In order to solve the above-described problems, the waste treatment plant of the first invention according to the present application includes a landfill tank filled with water before the waste is charged, and waste in the water of the landfill tank. A charging device, a drainage pipe for drainage laid on the bottom of the landfill tank, an oxygen enrichment device that enriches the extracted water with oxygen, and an oxygen enriched water. Again, it is characterized by a waste disposal site composed of a water supply device that supplies the landfill tank.

また、本件出願にかかる第二の発明の廃棄物処理場は、廃棄物の投入前に水の充填してある複数の埋立槽と、埋立槽の水中に廃棄物を投入する投入装置と、埋立槽に供給した水を取り出す、埋立槽の底部に敷設した排水用の集排水管と、取り出した水に酸素富化する酸素富化装置と、酸素富化した水を再度、埋立槽に供給する給水装置とより構成した廃棄物処分場を特徴としたものである。
Further, the waste treatment plant of the second invention according to the present application includes a plurality of landfill tanks filled with water before the introduction of the waste, an input device for introducing the waste into the water of the landfill tank, and a landfill Drainage drainage pipes laid at the bottom of the landfill tank that take out the water supplied to the tank, an oxygen enrichment device that enriches the extracted water with oxygen, and oxygen-enriched water is supplied again to the landfill tank It is characterized by a waste disposal site composed of a water supply device.

また本件出願にかかる第三の発明の廃棄物処理方法は、廃棄物の投入前に水の充填してある埋立槽と、埋立槽の水中に廃棄物を投入する投入装置と、埋立槽に供給した水を取り出す、埋立槽の底部に敷設した排水用の集排水管と、取り出した水に酸素富化する酸素富化装置と、酸素富化した水を再度、埋立槽に供給する給水装置とより構成した廃棄物処分場を使用し、埋立槽内に投入装置によって廃棄物を水中投入し、かつ埋立槽内の水を循環して酸素富化状態を維持し、埋立槽内への廃棄物の水中投入が終了したら、内部の水を排水する、廃棄物処分方法を特徴としたものである。 The waste treatment method of the third invention according to the present application is a landfill tank filled with water before the waste is charged, a charging device for charging waste into the water of the landfill tank, and a supply to the landfill tank Drainage drainage pipes laid at the bottom of the landfill tank, an oxygen enrichment device that enriches the extracted water with oxygen, and a water supply device that supplies the oxygen-enriched water to the landfill tank again Using a waste disposal site composed of wastewater, the waste is put into the landfill tank with the input device, and the water in the landfill tank is circulated to maintain the oxygen-enriched state. This is characterized by a waste disposal method that drains the internal water when the water is poured into the water.

また本件出願にかかる第四の発明の廃棄物処理方法は、廃棄物の投入前に水の充填してある複数の埋立槽と、埋立槽の水中に廃棄物を投入する投入装置と、埋立槽に供給した水を取り出す、埋立槽の底部に敷設した排水用の集排水管と、取り出した水に酸素富化する酸素富化装置と、酸素富化した水を再度、埋立槽に供給する給水装置とより構成した廃棄物処分場を使用し、ひとつの埋立槽内に投入装置によって廃棄物を水中投入し、かつその埋立槽内の水を循環して酸素富化状態を維持し、隣接する埋立槽内には水を充填しておき、ひとつの埋立槽内への廃棄物の水中投入が終了したら、内部の水を排水し、次に隣接する埋立槽の水を酸素富化水に置き換え、その埋立槽内に投入装置によって廃棄物を水中投入するという行為を繰り返して行う廃棄物処分方法を特徴としたものである。 Further, the waste treatment method of the fourth invention according to the present application includes a plurality of landfill tanks filled with water before the waste is charged, an input device for introducing the waste into the water of the landfill tank, and a landfill tank Drainage drainage pipes laid at the bottom of the landfill tank that take out the water supplied to the water, oxygen enrichment equipment that enriches the extracted water with oxygen, and water supply that supplies oxygen-enriched water to the landfill tank again Using a waste disposal site composed of equipment and equipment, injecting waste into water in one landfill tank with an input device, and circulating the water in the landfill tank to maintain an oxygen-enriched state, adjacent The landfill tank is filled with water, and when the waste water into one landfill tank is finished, the internal water is drained, and then the water in the adjacent landfill tank is replaced with oxygen-enriched water. , Repeated the act of throwing waste into the landfill tank with a charging device Cormorant waste disposal methods in which was characterized by.

本発明の廃棄物処分場は以上説明したようになるから次のような効果を得ることができる。
<1> 埋立槽内に水を供給して、水中に廃棄物を埋め立てるために粉塵の発生を抑制することができる。
<2> 廃棄物を水中へ埋め立てるために、ラダーやクレーンなどの鉛直方向に廃棄物を移動させる手段を特別に設置する必要がない。
<3> 埋立槽への廃棄物の投入が終了したら内部の水を排水して行う方法を採用すれば、廃棄物の埋立中には嫌気状態にならず、埋立が終了したら内部の水を排水して通常に準好気性状態に戻すことができるから廃棄物の安定化を促進することができる。
<4> 複数の埋立槽を設ける構成、方法を採用すれば、隣接する埋立槽に水を充填しておくことができるから、仕切壁に一方からの土圧が作用することがなく、仕切壁の厚さを薄くすることができて経済的である。
<5> 複数の埋立槽を設ける構成、方法を採用すれば、仕切壁の厚さが薄くてすむから、埋立槽の分割を増やしても経済的に成立し、その結果、埋立槽を被覆する蓋の幅、長さを小さい物とすることができる。
<6> 廃棄物の内部の水を排水する方法を採用すれば、廃棄物に水締め効果を与えることができ、特別な締固め工程を採用する必要がない。
<7> 循環する水に酸素以外の安定化促進剤を混入する方法を採用すれば、有機物以外の安定化を促進することができる。
<8> 定期的に埋立地内の酸素濃度を下げる方法を採用すれば、廃棄物を嫌気性にして脱窒を行うことも可能である。
Since the waste disposal site of the present invention is as described above, the following effects can be obtained.
<1> It is possible to suppress the generation of dust in order to supply water into a landfill tank and landfill waste in water.
<2> In order to reclaim waste into the water, there is no need to specially install a means for moving the waste in the vertical direction, such as a ladder or a crane.
<3> If the method of draining the internal water to the landfill tank and draining the internal water is adopted, the wastewater is not anaerobic during the landfill, and the internal water is drained after the landfill is completed. Then, since it can be returned to a semi-aerobic state normally, stabilization of waste can be promoted.
<4> If a configuration and method for providing a plurality of landfill tanks are adopted, water can be filled in adjacent landfill tanks, so that the earth pressure from one side does not act on the partition walls, and the partition walls It is economical that the thickness can be reduced.
<5> By adopting a configuration and method for providing a plurality of landfill tanks, the partition wall can be made thin, so even if the number of landfill tanks is increased, it is economically established, and as a result, the landfill tanks are covered. The width and length of the lid can be made small.
<6> If a method of draining the water inside the waste is adopted, a water-tightening effect can be given to the waste, and there is no need to adopt a special compaction process.
<7> Stabilization other than organic matter can be promoted by adopting a method in which a stabilizing promoter other than oxygen is mixed into the circulating water.
<8> If a method of periodically reducing the oxygen concentration in the landfill is adopted, it is possible to denitrify the waste by making it anaerobic.

以下図面を参照にしながら本発明の好適な実施の形態を詳細に説明する。   DESCRIPTION OF EMBODIMENTS Hereinafter, preferred embodiments of the present invention will be described in detail with reference to the drawings.

<1>全体の構成。(図1)(単一の埋立槽)
廃棄物を投入する埋立槽1と、埋立槽1に廃棄物を投入する投入装置2と、埋立槽1に供給した水を取り出して酸素富化する酸素富化装置3と、酸素富化した水を再度、埋立槽1に供給する給水装置4とより構成する。
<1> Overall configuration. (Figure 1) (Single landfill tank)
Landfill tank 1 for introducing waste, input device 2 for introducing waste into landfill tank 1, oxygen enrichment apparatus 3 for taking out the water supplied to landfill tank 1 and enriching it with oxygen, and water enriched with oxygen Is constituted again with a water supply device 4 for supplying to the landfill tank 1.

<1−1>埋立槽1。
埋立槽1は周囲の壁をコンクリート製の板体で構成し、底板を設け、上部は開放した箱状体で構成した構造体が一般的である。
埋立槽1は一般に地中に設置するが、地上、半地下状態に設置することも可能である。
<1-1> Landfill tank 1.
The landfill tank 1 is generally a structure in which the surrounding wall is made of a plate made of concrete, a bottom plate is provided, and the upper part is made of an open box.
The landfill tank 1 is generally installed in the ground, but can also be installed on the ground or semi-underground.

<1−2>給水、排水のシステム。
給水装置4は、後述する酸素富化水製造3で製造した酸素富化状態になった水を送水管41を通して埋立槽1内に供給する装置である。
一方、埋立槽1の底部には、排水用の集排水管42を敷設して、この集配水管42で集水した水を集水ピット43に集め酸素富化水製造装置3を通して循環させる。
ただし水の供給位置、排水位置は、埋立槽1の上下に限定されるものではなく、下方から水を供給し、上方から排水する構造、あるいは両者を混在させた構造などを採用することができる。
酸素富化水の循環は必ずしもポンプを使用せず、地形によっては自然流下させて酸素富化装置3を通して循環させる方法を採用することができる。
<1-2> Water supply and drainage system.
The water supply device 4 is a device that supplies the oxygen-enriched water produced in the oxygen-enriched water production 3 described later into the landfill tank 1 through the water supply pipe 41.
On the other hand, a drainage drainage pipe 42 is laid at the bottom of the landfill tank 1, and the water collected by the drainage pipe 42 is collected in the water collection pit 43 and circulated through the oxygen-enriched water production apparatus 3.
However, the water supply position and the drainage position are not limited to the top and bottom of the landfill tank 1, and a structure in which water is supplied from below and drained from above, or a structure in which both are mixed can be employed. .
Circulation of oxygen-enriched water does not necessarily use a pump, and depending on the terrain, it is possible to adopt a method in which the oxygen-enriched water is circulated through the oxygen-enriching device 3 by flowing down naturally.

<1−3>投入装置2。
廃棄物を埋立槽1に投入する投入装置2は、ホッパーやベルコンなどが一般的である。
しかしダンプトラックやショベルカーから直接、埋立槽1内へ廃棄物を投入する場合にはそのトラックやショベルカーを投入装置2とみなすことができる。
ダンプカーなどが埋立槽1の上部空間へ移動できるようにステージを組み立てる構成を採用することができる。
なお、この実施例は埋立槽1が単数の場合であるが、後述するような埋立槽1が複数の構造では、図3に示すように埋め立て対象の埋立槽1だけにステージ12を組み立てる構成、あらかじめすべての埋立槽1にステージ12を設置しておく構成、あるいはステージ12を上下に分けて、下部だけを各埋立槽1に設置しておき、上部をそのつど投入する埋立槽1に付け替えて転用する構成を採用することもできる。
またラダー方式の投入装置2や、天井クレーンのような公知の装置を使用することもできる。
<1-3> Input device 2.
As the charging device 2 for charging the waste into the landfill tank 1, a hopper, a velcon or the like is generally used.
However, when throwing waste into the landfill tank 1 directly from the dump truck or shovel car, the truck or shovel car can be regarded as the loading device 2.
The structure which assembles a stage so that a dump truck etc. can move to the upper space of the landfill tank 1 is employable.
In addition, although this Example is a case where the number of the landfill tank 1 is single, when the landfill tank 1 as described later has a plurality of structures, a configuration in which the stage 12 is assembled only in the landfill tank 1 to be landfilled as shown in FIG. A configuration in which the stages 12 are installed in advance in all landfill tanks 1 or the stage 12 is divided into upper and lower parts, only the lower part is installed in each landfill tank 1, and the upper part is replaced with the landfill tank 1 to be charged each time. A diverted configuration can also be employed.
Also, a ladder-type charging device 2 or a known device such as an overhead crane can be used.

<1−4>酸素富化装置3。
酸素富化装置3は、埋立槽1から引き出した水に酸素を供給して酸素富化水を製造する装置であり、例えば酸素富化膜などを使用して作成した酸素濃度の高い空気を曝気して酸素富化水を作るような構成である。
あるいは、図3の実施例のように、酸素ボンベから高濃度の酸素と水道水をばっき装置31へ供給して曝気する装置、マイクロバブルやノナバブル発生装置などを使用して酸素富化水を製造する公知の装置、方法などを採用することができる。
<1-4> Oxygen enrichment device 3.
The oxygen enrichment apparatus 3 is an apparatus that supplies oxygen to the water drawn from the landfill tank 1 to produce oxygen enriched water. For example, the oxygen enrichment apparatus 3 aerated high oxygen concentration air created using an oxygen enriched film or the like. Thus, it is configured to make oxygen-enriched water.
Alternatively, as in the embodiment of FIG. 3, oxygen-enriched water is supplied using a device that supplies aeration by supplying high-concentration oxygen and tap water from an oxygen cylinder to the flash device 31, a microbubble or a nona bubble generator, and the like. Known apparatuses and methods for manufacturing can be employed.

<1−5>水量の制御。
埋立槽1から引き出した水は、埋め立ての量だけ増加して上昇し、蒸発分だけ減少して下降するから、その差の量を外部へ排出して埋立槽1内の水位を一定に保つように制御する。
つまり、廃棄物の投入により水位が上昇しそうな場合には水位調整バルブ61の操作によって、その量に比例した分だけ水処理装置6へ送り、処理をした後に外部へ排水する。
水位調整バルブ61は、埋立槽1から引き出した水を酸素富化製造装置3か、あるいは水処理装置6に送水する切り替えの弁である。
一方、水位が下降しそうな場合にはその量に比例した分だけ外部から水道水などを導入することによって水位を一定に保つことが必要である。
<1-5> Control of the amount of water.
The water drawn from the landfill tank 1 increases by the amount of landfill, rises, decreases by the amount of evaporation, and falls, so that the amount of the difference is discharged to the outside so as to keep the water level in the landfill tank 1 constant. To control.
That is, when the water level is likely to rise due to the input of waste, the water level adjusting valve 61 is operated to send it to the water treatment device 6 by an amount proportional to the amount, and after processing, the water is discharged to the outside.
The water level adjustment valve 61 is a switching valve for supplying water drawn from the landfill tank 1 to the oxygen enrichment production apparatus 3 or the water treatment apparatus 6.
On the other hand, when the water level is likely to fall, it is necessary to keep the water level constant by introducing tap water or the like from the outside in proportion to the amount.

<1−6>屋根。
埋立槽1の上部には埋立槽1を覆う移動式、あるいは固定式の屋根5を設けて、降雨による水量の変化を阻止する。
<1-6> Roof.
A movable or fixed roof 5 that covers the landfill tank 1 is provided above the landfill tank 1 to prevent a change in the amount of water due to rain.

<2>他の実施例(図2、3)(複数の埋立槽の場合)。
上記の実施例は埋立槽1が単数の構成であったが、廃棄物を投入する埋立槽1を複数の埋立槽1として構成することもできる。
複数の埋立槽1は、周囲の外壁の内部を仕切壁11で区切って構成したものである。
仕切壁11としてはコンクリート製の壁が一般的であるが、その他の利用できる公知の材料、形式、方法を採用することができ、例えば補強盛土工法を適用することもできる。
すなわち補強盛土を積み上げた壁を仕切壁11として採用するような構造である。
複数の埋立槽1を平面的に一列に並べる構成、「田」の字型に配置する構成(図4)など自由な組み合わせを採用することができる。
その他の、給水装置4、投入装置2、酸素富化水製造装置3などの構成は上記の実施例と同様である。
<2> Other examples (FIGS. 2 and 3) (in the case of a plurality of landfill tanks).
In the above-described embodiment, the landfill tank 1 has a single configuration, but the landfill tanks 1 into which the waste is introduced can be configured as a plurality of landfill tanks 1.
The plurality of landfill tanks 1 are configured by dividing the inside of the surrounding outer wall by a partition wall 11.
Although the concrete wall is generally used as the partition wall 11, other known materials, types, and methods that can be used can be employed. For example, a reinforced embankment method can also be applied.
That is, it is a structure which employ | adopts the wall which piled up the reinforcement embankment as the partition wall 11. FIG.
A free combination such as a configuration in which a plurality of landfill tanks 1 are arranged in a row in a plane, or a configuration in which a plurality of landfill tanks 1 are arranged in a “rice” shape (FIG. 4) can be employed.
Other configurations of the water supply device 4, the charging device 2, the oxygen-enriched water production device 3 and the like are the same as those in the above embodiment.

<3>処分方法1(埋立槽1が単槽の場合)
埋立槽1が単数の場合の廃棄物の処分方法について説明する。
上記の埋立槽1が単数の構成の廃棄物処分場を使用し、水の充填してある埋立槽1内に投入装置2によって廃棄物を投入する。
すなわち水中投棄を行う。
水中に廃棄物をそのまま投入すると、前記で指摘したように、水中に溶存している酸素は廃棄物の微生物分解ですぐに消費されてしまい、嫌気性になって水質が悪化する問題がある。
そのような廃棄物の嫌気性分解の阻止と、有機物の早期安定化を図るために、埋立槽1内の水は酸素富化水を採用する。
そのために埋立槽1内の水を例えば底部に配置した集排水管42から引き出し、酸素富化水製造装置3へ供給する。
そこで酸素富化した水は給水装置4によって埋立槽1内へ循環して供給し、埋立槽1内が嫌気状態にならないように維持する。
その際に、廃棄物の投入によって生じた余剰水は水処理装置6において一定の水処理を行って外部へ排水する。
埋立槽1内へ投入した廃棄物が水面から露出するようになったら投入を終了する。
その後、底部に配置した集排水管42から内部の水を排水して、通常の準好気状態に戻し、上部には最終覆土を行い、あるいはキャッピングシートで覆い、雨水の影響を排除する。
埋立槽1の内部の水を排水することによって廃棄物を締め固めるという効果も期待できる。
埋立槽1内の水は、廃棄物の投棄の進行と平行して、すなわち埋立槽1内の酸素消費量にあわせて徐々に酸素富化水に置き換えても、あるいは埋立槽1内の水を酸素富化水に置き換えてから廃棄物の投入を行うことができる。
廃棄物の投入の終了後に表面を被覆したシートの下には散水管を配置して散水を施す場合もある。
その際に有機物の安定化がさらに必要である場合には、酸素富化水の散水を継続する。
有機物以外の物質の安定化が必要である場合には、対象とする非安定化物質を早期に安定化させるための薬剤などを散布する。
このような作業によって、埋め戻し後に散水施設やシートを速やかに撤去することが可能であり、迅速に埋立後の跡地の転用を図ることができる。
<3> Disposal method 1 (when landfill tank 1 is a single tank)
A method for disposing of waste when there is a single landfill tank 1 will be described.
The landfill tank 1 uses a waste disposal site having a single structure, and the throwing device 2 puts waste into the landfill tank 1 filled with water.
That is, dumping in water.
When waste is put into water as it is, as pointed out above, oxygen dissolved in water is consumed immediately by microbial decomposition of the waste, resulting in anaerobic and water quality deterioration.
In order to prevent such anaerobic decomposition of waste and to stabilize organic matter at an early stage, oxygen-enriched water is used as the water in the landfill tank 1.
For this purpose, the water in the landfill tank 1 is drawn from, for example, a collecting / draining pipe 42 arranged at the bottom and supplied to the oxygen-enriched water production apparatus 3.
Therefore, the oxygen-enriched water is circulated and supplied into the landfill tank 1 by the water supply device 4 and is maintained so that the inside of the landfill tank 1 does not become anaerobic.
At that time, surplus water generated by the input of the waste is subjected to a certain water treatment in the water treatment device 6 and discharged to the outside.
When the waste thrown into the landfill tank 1 is exposed from the water surface, the charging is finished.
Thereafter, the internal water is drained from the drainage pipe 42 disposed at the bottom to return to a normal semi-aerobic state, and the top is covered with a final soil or covered with a capping sheet to eliminate the influence of rainwater.
The effect of compacting the waste by draining the water inside the landfill tank 1 can also be expected.
The water in the landfill tank 1 may be replaced with oxygen-enriched water in parallel with the progress of the dumping of the waste, that is, according to the oxygen consumption in the landfill tank 1, or the water in the landfill tank 1 may be replaced. Waste can be input after replacing with oxygen-enriched water.
In some cases, water spraying may be performed by placing a sprinkler tube under the sheet whose surface is covered after the end of the introduction of the waste.
At that time, if further stabilization of the organic matter is necessary, watering of the oxygen-enriched water is continued.
When it is necessary to stabilize substances other than organic substances, a drug for stabilizing the target non-stabilized substance at an early stage is sprayed.
By such an operation, it is possible to quickly remove the watering facility and the sheet after the backfilling, and it is possible to quickly divert the site after the landfill.

<4>処分方法2(埋立槽が複数槽の場合)。
埋立槽1が複数の場合の廃棄物の処分方法について説明する。
ひとつの埋立槽1内に投入装置2によって廃棄物を投入し、その埋立槽1内の水を循環して酸素富化状態を維持する点は上記の実施例と同様である。
その場合に、投入を行っていないすべての埋立槽1内には水を充填しておく。
この水の充填によって仕切壁には一面から廃棄物による圧力が、他面からは水による水圧が作用する。
そのために仕切壁11の厚さはきわめて薄いものとして構成することができる。
埋立槽1内へ投入した廃棄物が水面から露出するようになったらバックホウなどの重機を使って搬入車両が通れるように整地、転圧する。
そして次に埋め立て予定の埋立槽1の内部の水を酸素富化水に置き換え、廃棄物の投入と酸素富化水の循環という同様の作業を行う。
作業中の埋立槽1の上部には屋根5を移動して雨水の影響を遮断する。
こうして順次、投入する埋立槽1を奥の方へ移してゆき、複数の埋立槽1全体の埋め立てを完了する。
<4> Disposal method 2 (when there are multiple landfill tanks).
A method for disposing of waste when there are a plurality of landfill tanks 1 will be described.
The point that waste is thrown into one landfill tank 1 by the charging device 2 and the water in the landfill tank 1 is circulated to maintain the oxygen-enriched state is the same as in the above embodiment.
In that case, all the landfill tanks 1 that have not been charged are filled with water.
Due to this filling of water, pressure from waste is applied to the partition wall from one side and water pressure from the other side.
Therefore, the partition wall 11 can be configured to be extremely thin.
When the waste thrown into the landfill tank 1 is exposed from the surface of the water, the ground leveling and rolling are performed so that the incoming vehicle can pass through using a heavy machine such as a backhoe.
Then, the water inside the landfill tank 1 scheduled to be landfilled is replaced with oxygen-enriched water, and the same operation of charging waste and circulating the oxygen-enriched water is performed.
The roof 5 is moved to the upper part of the landfill tank 1 during work to block the influence of rainwater.
In this way, the landfill tanks 1 to be introduced are sequentially moved to the back, and the landfill of the entire plurality of landfill tanks 1 is completed.

<5>処分方法3(酸素濃度を下げる処分方法)。
埋立槽1が単数であっても、複数であってもよいが、上記のような工程で廃棄物の処分がいったん終了したら、その後に定期的に、あるいは随時に、埋立槽1内の水の酸素濃度を下げる。
水の酸素濃度を下げるためには、水の循環を止める方法を採用できる。
あるいは、循環水への酸素供給を止める方法を採用することができる。
この方法では槽内の微生物が槽内の酸素を消費し、嫌気性となるので、その状態で槽内にアルコールなどの有機物を供給して廃棄物の脱窒を行うことができる。
<5> Disposal method 3 (disposal method for reducing the oxygen concentration).
Although the landfill tank 1 may be singular or plural, once the disposal of the waste is completed in the above-described process, the water in the landfill tank 1 is periodically or occasionally thereafter. Reduce oxygen concentration.
In order to reduce the oxygen concentration of water, a method of stopping water circulation can be employed.
Or the method of stopping the oxygen supply to circulating water is employable.
In this method, since microorganisms in the tank consume oxygen in the tank and become anaerobic, in this state, organic matter such as alcohol can be supplied into the tank to denitrify waste.

<6>処分方法4(安定化促進剤を混入する処分方法)。
埋立槽1が単数であっても、複数であってもよいが、埋立槽1内の水を循環して酸素富化状態を維持する場合に、さらにこの循環水に安定化促進剤を混合する。
安定化促進剤としては、オゾン水、過酸化水素水、キレート剤水溶液、ランタン水溶液、などを使用できる。
それらの安定化促進剤のうちで、オゾン水と過酸化水素水は、特にCODやBODの低減に効果がある。
またキレート剤水溶液は、特に重金属の不溶化に効果がある。
またランタン水溶液は、特にホウ素の低減に効果がある。
その他の工程は上記の実施例と同様である。
<6> Disposal method 4 (disposal method in which a stabilizing accelerator is mixed).
A single landfill tank 1 or a plurality of landfill tanks 1 may be used. However, when the water in the landfill tank 1 is circulated to maintain an oxygen-enriched state, a stabilization promoter is further mixed into the circulating water. .
As the stabilization promoter, ozone water, hydrogen peroxide solution, chelating agent aqueous solution, lanthanum aqueous solution, or the like can be used.
Of these stabilization promoters, ozone water and hydrogen peroxide water are particularly effective in reducing COD and BOD.
The aqueous chelating agent solution is particularly effective for insolubilizing heavy metals.
A lanthanum aqueous solution is particularly effective in reducing boron.
Other steps are the same as those in the above embodiment.

単数の埋立槽を配置した本発明の廃棄物処分場の実施例の説明図。Explanatory drawing of the Example of the waste disposal site of this invention which has arrange | positioned the single landfill tank. 複数の埋立槽を配置した廃棄物処分場の実施例の説明図。Explanatory drawing of the Example of the waste disposal site which has arrange | positioned the several landfill tank. 複数の埋立槽を配置した廃棄物処分場の実施例の説明図。Explanatory drawing of the Example of the waste disposal site which has arrange | positioned the several landfill tank. 複数の埋立槽を配置した廃棄物処分場の実施例の平面図。The top view of the Example of the waste disposal site which has arrange | positioned several landfill tanks. 従来の廃棄物処分場の実施例の説明図。Explanatory drawing of the Example of the conventional waste disposal site.

符号の説明Explanation of symbols

1:埋立槽
2:投入装置
3:酸素富化水製造装置
4:給水装置
5:屋根
6:水処理装置
1: Landfill tank 2: Input device 3: Oxygen-enriched water production device 4: Water supply device 5: Roof 6: Water treatment device

Claims (5)

廃棄物の投入前に水の充填してある埋立槽と、
埋立槽の水中に廃棄物を投入する投入装置と、
埋立槽に供給した水を取り出す、埋立槽の底部に敷設した排水用の集排水管と、
取り出した水に酸素富化する酸素富化装置と、
酸素富化した水を再度、埋立槽に供給する給水装置とより構成した、
廃棄物処分場。
A landfill tank filled with water before waste input,
An input device for injecting waste into the water of the landfill tank;
A drainage pipe for drainage laid at the bottom of the landfill tank, which takes out the water supplied to the landfill tank;
An oxygen enrichment device that enriches the extracted water with oxygen;
A water supply device that supplies oxygen-enriched water to the landfill tank again,
Waste disposal site.
廃棄物の投入前に水の充填してある複数の埋立槽と、
埋立槽の水中に廃棄物を投入する投入装置と、
埋立槽に供給した水を取り出す、埋立槽の底部に敷設した排水用の集排水管と、
取り出した水に酸素富化する酸素富化装置と、
酸素富化した水を再度、埋立槽に供給する給水装置とより構成した、
廃棄物処分場。
A number of landfill tanks filled with water before waste input,
An input device for injecting waste into the water of the landfill tank;
A drainage pipe for drainage laid at the bottom of the landfill tank, which takes out the water supplied to the landfill tank;
An oxygen enrichment device that enriches the extracted water with oxygen;
A water supply device that supplies oxygen-enriched water to the landfill tank again,
Waste disposal site.
廃棄物の投入前に水の充填してある埋立槽と、
埋立槽の水中に廃棄物を投入する投入装置と、
埋立槽に供給した水を取り出す、埋立槽の底部に敷設した排水用の集排水管と、
取り出した水に酸素富化する酸素富化装置と、
酸素富化した水を再度、埋立槽に供給する給水装置とより構成した廃棄物処分場を使用し、
埋立槽内に投入装置によって廃棄物を水中投入し、
かつ埋立槽内の水を循環して酸素富化状態を維持し、
埋立槽内への廃棄物の水中投入が終了したら、
内部の水を排水する、
廃棄物処分方法。
A landfill tank filled with water before waste input,
An input device for injecting waste into the water of the landfill tank;
A drainage pipe for drainage laid at the bottom of the landfill tank, which takes out the water supplied to the landfill tank;
An oxygen enrichment device that enriches the extracted water with oxygen;
Using a waste disposal site consisting of a water supply device that supplies oxygen-enriched water to the landfill tank again,
Waste is thrown into the landfill tank with a charging device,
And keep the oxygen-enriched state by circulating the water in the landfill tank,
After the wastewater is put into the landfill tank,
Drain the water inside,
Waste disposal method.
廃棄物の投入前に水の充填してある複数の埋立槽と、
埋立槽の水中に廃棄物を投入する投入装置と、
埋立槽に供給した水を取り出す、埋立槽の底部に敷設した排水用の集排水管と、
取り出した水に酸素富化する酸素富化装置と、
酸素富化した水を再度、埋立槽に供給する給水装置とより構成した廃棄物処分場を使用し、
ひとつの埋立槽内に投入装置によって廃棄物を水中投入し、
かつその埋立槽内の水を循環して酸素富化状態を維持し、
隣接する埋立槽内には水を充填しておき、
ひとつの埋立槽内への廃棄物の水中投入が終了したら、
内部の水を排水し、
次に隣接する埋立槽の水を酸素富化水に置き換え、
その埋立槽内に投入装置によって廃棄物を水中投入するという行為を繰り返して行う、
廃棄物処分方法。
A number of landfill tanks filled with water before waste input,
An input device for injecting waste into the water of the landfill tank;
A drainage pipe for drainage laid at the bottom of the landfill tank, which takes out the water supplied to the landfill tank;
An oxygen enrichment device that enriches the extracted water with oxygen;
Using a waste disposal site consisting of a water supply device that supplies oxygen-enriched water to the landfill tank again,
Waste is thrown into water in one landfill tank with a loading device,
And keep the oxygen-enriched state by circulating the water in the landfill tank,
Fill the adjacent landfill tank with water,
Once you have finished putting the wastewater into one landfill tank,
Drain the water inside,
Next, replace the water in the adjacent landfill tank with oxygen-enriched water,
Repeat the act of throwing waste water into the landfill tank with a charging device,
Waste disposal method.
廃棄物の投入前に水の充填してある埋立槽と、
埋立槽の水中に廃棄物を投入する投入装置と、
埋立槽に供給した水を取り出す、埋立槽の底部に敷設した排水用の集排水管と、
取り出した水に酸素富化する酸素富化装置と、
酸素富化した水を再度、埋立槽に供給する給水装置とより構成した廃棄物処分場を使用し、
埋立槽内に投入装置によって廃棄物を水中投入し、
かつ埋立槽内の水を循環して酸素富化状態を維持し、
埋立槽内への廃棄物の水中投入が終了したら、
内部の水を排水し、
その後、埋立てられた廃棄物の上面に散水管を配置して酸素富化水を循環させ、定期的に、あるいは随時、水の循環を停止し又は循環水への酸素供給を停止して埋立槽内の水の酸素濃度を下げて、廃棄物の脱窒を行う、
廃棄物処分方法。
A landfill tank filled with water before waste input,
An input device for injecting waste into the water of the landfill tank;
A drainage pipe for drainage laid at the bottom of the landfill tank, which takes out the water supplied to the landfill tank;
An oxygen enrichment device that enriches the extracted water with oxygen;
Using a waste disposal site consisting of a water supply device that supplies oxygen-enriched water to the landfill tank again,
Waste is thrown into the landfill tank with a charging device,
And keep the oxygen-enriched state by circulating the water in the landfill tank,
After the wastewater is put into the landfill tank,
Drain the water inside,
After that, a water sprinkling pipe is placed on the upper surface of the landfilled waste to circulate the oxygen-enriched water, and periodically or whenever necessary, the circulation of the water is stopped or the supply of oxygen to the circulating water is stopped. Reduce the oxygen concentration in the tank to denitrify waste.
Waste disposal method.
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JP2001327947A (en) * 2000-05-19 2001-11-27 Kankyo Eng Co Ltd Quick stabilization and malodor suppression method in waste landfill disposal site and chemical agent to be used therefor
JP2004351242A (en) * 2003-05-27 2004-12-16 Kubota Corp Semi-aerobic reclaimed site and landfill method
JP2005095801A (en) * 2003-09-25 2005-04-14 Sumitomo Heavy Ind Ltd Purification method of land-filled waste

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JP2005095801A (en) * 2003-09-25 2005-04-14 Sumitomo Heavy Ind Ltd Purification method of land-filled waste

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