JP2003080280A - Organic sewage treatment method not requiring flow end treatment and equipment for the same - Google Patents

Organic sewage treatment method not requiring flow end treatment and equipment for the same

Info

Publication number
JP2003080280A
JP2003080280A JP2001273333A JP2001273333A JP2003080280A JP 2003080280 A JP2003080280 A JP 2003080280A JP 2001273333 A JP2001273333 A JP 2001273333A JP 2001273333 A JP2001273333 A JP 2001273333A JP 2003080280 A JP2003080280 A JP 2003080280A
Authority
JP
Japan
Prior art keywords
water
layer
organic
sewage
underground
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.)
Pending
Application number
JP2001273333A
Other languages
Japanese (ja)
Inventor
Kinichi Hara
欣一 原
Takeshi Kato
剛 加藤
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.)
IZUWA KK
Original Assignee
IZUWA 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 IZUWA KK filed Critical IZUWA KK
Priority to JP2001273333A priority Critical patent/JP2003080280A/en
Publication of JP2003080280A publication Critical patent/JP2003080280A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

Abstract

PROBLEM TO BE SOLVED: To provide a sewage treatment method which does not use outer driving power. SOLUTION: The method which does not require a flow end treatment consists of the methods of: separating the organic sewage to a solid content and sewage by a sieve, storing the separated sewage in an underground water tank, subjecting the sewage to an anaerobic fermentation and decomposing the sewage to water and gases; sucking up the water to the vicinity of the ground by utilizing a capillary phenomenon when the water level rises by the successively fed sewage and arrives at the bottom surface of a porous gravel layer covering the underwater water tank; forming a soil layer containing soil microorganisms and organic matter reaching the ground on the upper layer in which the microholes of the gravel acts as a carrier for anaerobic bacteria and the bacteria density is made greater than the bacterium density in the water and, when the water passes this layer, the water comes into contact therewith and undergoes the anaerobic fermentation; and the water to the ground by utilizing capillary phenomenon of the soil layer in which, when the water is abundant and does not contain oxygen, the water undergoes the anaerobic fermentation and, when the water is scarce and contains the oxygen, the water undergoes an aerobic fermentation, thereby creating ridges on its surface, increasing an area, making it possible to easily receive sunbeams, improving ventilation and evaporating the water. The equipment for the same is also provided.

Description

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

【0001】[0001]

【発明の属する技術分野】本発明は有機性汚水の処理方
法に関するが、詳しくは例えば食品工場では紅茶を抽出
するときは搾りすぎると苦味等で風味が悪くなったり濁
りを生じたりするのである程度までで強く搾るのを止め
る場合がある。この搾りかすを積んで置くと床面や箱の
底に水分が沁みだしてきてこれを汚水として下水道に入
れると下水処理設備に負荷がかかり更に設備建設に費用
がかかりるようになる。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating organic sewage. More specifically, for example, when extracting black tea in a food factory, too much squeezing causes bad taste such as bitterness or turbidity. You may stop squeezing hard with. When this squeezed waste is piled up and put on the floor or the bottom of the box, if it is put into the sewer as sewage, the sewage treatment facility will be overloaded and the construction cost will increase.

【0002】[0002]

【従来の技術】従来の汚水及び排水の処理方法として
は、例えば特開平8−170874号で開示されている
化学的な汚泥処理方法や特開平2−268882号で開
示されている排水の浄化処理方法などがある。化学的な
汚泥処理方法は、処理物質を生石灰により化学反応させ
るものであって、下水・排水・河川等から発生する有機
質及び無機質の汚泥を収集搬送する第1処理工程と、前
記処理汚泥を生石灰により化学反応させる第2処理工程
と、前記化学反応させた処理汚泥を熱成させる第3処理
工程とから構成される化学的な汚泥処理方法である。こ
の処理方法によれば、人間・動物・家畜等のし尿及び
ふん尿の汚泥物を浄化処理することができるので、汚泥
物を再生して土壌改良剤や土質改良剤として再利用する
ことができること、家庭・工場等から排出される下水
及び工場排水汚泥物を浄化処理することができるもので
排水汚泥物を再生して土壌改良剤や土質改良剤として再
利用することができること、汚染された河川や湖水等
の一般汚泥を浄化処理することができるので汚泥を再生
して土壌改良剤や土質改良剤として再利用することがで
きること、道路工事や土木工事等により排出された汚
泥物を浄化処理することができるので汚泥物を再生して
土壌改良剤や土質改良剤として再利用することができる
ことなどの効果が得られる。一方、排水の浄化処理方法
は銅・カドミウム・水銀・鉛・亜鉛等の重金属を含有す
る工場廃水や洗剤・食用油・屎尿等を含む下水等の排水
を浄化する方法に関するものであり、その特徴とすると
ころは石灰質や珪酸等からなる各種ネクトン・プランク
トン・藻類・海草類の成分を含有する天然の貝化石を小
粒若しくは荒い砂状の粗鉱に破砕して天然乾燥させると
ともに120℃乃至450℃程度に熱風乾燥させて粉粒
状に精製し、更にエアー分扱させておおむね0.10μ
mから50.00μm位の粒径に精製した処理物質を主
成分とし、該処理物質を銅・カドミウム・水銀・鉛・亜
鉛等の重金属を含有する工場廃水や洗剤・食用油・屎尿
等を含む下水等の排水に混入して排水の物質を有効的に
吸着・疑集せしめ、更にイオン交換及び中和作用により
排水の再利用を可能ならしめたことを特徴とする排水の
浄化処理方法にある。この処理方法によれば、化学薬
品を一切使用することなく工場廃水や下水等の汚水を浄
化することができ、しかも二次公害を未然に防止できる
ばかりか処理後の水は工業用水等に再利用でき、また処
理用物質が天然物であるから処理能力性・経済性・企業
性等あらゆる面からみても従来方法よりもはるかに優れ
ている排水の浄化処理方法といえること、また本発明
は石灰質や珪酸等からなる各種ネクトン・プランクトン
・藻類・海草類の成分を含有する天然の貝化石を小粒若
しくは荒い砂状の粗鉱に破砕して天然乾燥させるととも
120℃乃至450℃程度に熱風乾燥させて粉粒状に精
製し、更にエアー分扱させておおむね0.10μmから
50.00μm位の粒径に精製した構成になっているの
で排水浄化処理用の貝化石としては最適な処理物質が得
られることにある。
2. Description of the Related Art Conventional methods for treating sewage and waste water include, for example, a chemical sludge treatment method disclosed in JP-A-8-170874 and a waste water purification treatment disclosed in JP-A-2-268882. There are ways. The chemical sludge treatment method is a method of chemically reacting a treated substance with quick lime, and a first treatment step of collecting and transporting organic and inorganic sludge generated from sewage, drainage, rivers, etc., and the treated sludge with quick lime. Is a chemical sludge treatment method comprising a second treatment step of chemically reacting with the above, and a third treatment step of thermally forming the chemically treated treatment sludge. According to this treatment method, since sludge of human waste, such as humans, animals and livestock, and excrement can be purified, sludge can be regenerated and reused as a soil improver or a soil improver, It can purify sewage and factory wastewater sludge discharged from homes, factories, etc., that wastewater sludge can be regenerated and reused as a soil conditioner or soil conditioner, polluted rivers and Since general sludge such as lake water can be purified, sludge can be recycled and reused as a soil improver or soil improver, and sludge discharged from road construction or civil engineering work can be purified. As a result, sludge can be regenerated and reused as a soil improver or a soil improver. On the other hand, the purification method of wastewater relates to a method for purifying wastewater of factory wastewater containing heavy metals such as copper, cadmium, mercury, lead and zinc and sewage including detergents, edible oil, human waste, etc. The natural shell fossils containing various components of nectons, plankton, algae, and seaweeds such as calcareous and silicic acid are crushed into small grains or rough sandy coarse ores and naturally dried, and at 120 ° C to 450 ° C. It is dried with hot air and refined into powder and granules.
The main component is a treated substance purified to a particle size of about 50.00 μm from m, and the treated substance includes factory wastewater containing heavy metals such as copper, cadmium, mercury, lead and zinc, detergent, edible oil, and human waste. It is a method for purifying wastewater characterized by being mixed with wastewater such as sewage to effectively adsorb and collect wastewater substances, and further allowing reuse of wastewater by ion exchange and neutralization. . According to this treatment method, wastewater such as factory wastewater and sewage can be purified without using any chemicals, and in addition, secondary pollution can be prevented and the treated water can be reused as industrial water. It can be said that it is a wastewater purification treatment method that can be used and is far superior to conventional methods in all respects such as treatment ability, economic efficiency, and corporate property because the treatment substance is a natural product. Natural shell fossils containing various components of nectons, plankton, algae, seaweeds such as calcareous and silicic acid are crushed into small or coarse sandy coarse ores and dried naturally with hot air drying at 120 to 450 ° C. It is refined into powder and granular form, and further treated with air to be refined to a particle size of about 0.10 μm to 50.00 μm, so it is the optimum treatment as a shell fossil for wastewater purification treatment. The substance is to be obtained.

【0003】更に、最近では家畜の糞尿を密閉容器に入
れて嫌気発酵を行ないメタンガスを発生させ、それを炊
事の燃料に使用したり発電機の燃料にして電力を得る処
理方法も開発されている。本発明は、この嫌気発酵によ
り有機性の汚れを処理する方法を開発したものである。
Furthermore, recently, a treatment method has been developed in which manure of livestock is put in a closed container and anaerobic fermentation is performed to generate methane gas, which is used as fuel for cooking or as fuel for a generator to obtain electric power. . The present invention has developed a method for treating organic soil by this anaerobic fermentation.

【0004】[0004]

【発明が解決しようとする課題】このような従来方法で
は、密閉容器内の発酵後の残り粕は水分を分離してから
固形分は堆肥として田畑に還元するか若しくは焼却して
灰分は埋めたてたりしている。そして、水分は下水道に
流しているので下水処理施設に多くの負荷をかけてい
た。また、固形分を堆肥とするときは水分の含有率が高
いと堆肥とするための発酵が起こらないので、どうして
も水分を分離しなければならない問題点があった。更に
紅茶製造のときでる茶葉の搾り粕も同様の問題点があっ
た。一方、この水は有機物に富み下水処理施設は定めら
れた濃度以下に有機物を除去しなけらば河川等に水を放
流できないので、既存の活性汚泥による下水処理施設に
はそれを処理するのに負担をかけていた。このように有
機物を定められた濃度以下に除去しなければならないこ
とと、近くに流末を放流できる河川がなければならない
という場所的な制約を受けることになる。かかる問題点
に鑑みて既存の活性汚泥による下水処理施設に負担をか
けずに汚水を処理し、しかも水分は空気中に蒸発させて
全く流末を河川等に放流することがなく設備の設置場所
も河川に近くなくてはならないという制約もなくして流
末処理不要の有機性汚水処理方法にしようとするところ
に、本発明が解決しようとする課題を有している。
According to such a conventional method, the residual lees after fermentation in the closed container are separated from water, and then the solid content is reduced to the fields as compost or incinerated to bury the ash content. I'm afraid. And since the water flows into the sewer, it put a lot of load on the sewage treatment facility. Further, when the solid content is compost, if the water content is high, the fermentation for compost does not occur, so there is a problem that the water must be separated. Further, the squeezed lees of tea leaves produced during the production of black tea also had the same problem. On the other hand, this water is rich in organic matter, and the sewage treatment facility cannot discharge the water to rivers etc. unless the organic matter is removed to below the specified concentration. I was burdened. In this way, the organic matter must be removed to below the specified concentration, and there is a locational constraint that there must be a river that can discharge the end of the stream. In consideration of such problems, wastewater is treated without burdening the existing sewage treatment facility with activated sludge, and moreover, moisture is evaporated into the air and the end of the facility is never discharged to rivers, etc. However, there is a problem to be solved by the present invention in an attempt to provide an organic wastewater treatment method that does not require end-of-stream treatment without the restriction that it must be close to a river.

【0005】[0005]

【課題を解決するための手段】本発明は上記の如き課題
を解決するために開発したものであって、流未処理を不
要とする有機性汚水を篩により固形分と汚水とに分離し
かつ分離された汚水を地下水槽に貯留して嫌気発酵させ
て水とガス体とに分解する方法と、順次送流されてきた
汚水により水位が上がり地下水槽を覆う多孔質礫層の底
面に達したときに毛細管現象により水が地表近くに吸い
上げられる方法と、前記礫の細孔が嫌気性菌の担体とな
り細菌密度が水中よりも大きくかつ水がこの層を通過す
るときに接触して嫌気発酵を受け該上層に地表面に達す
る土壌微生物及び有機物を含む土壌層を形成する方法
と、前記土壌層の毛細管現象により水が地表へ吸い上げ
られて水が多くて酸素の無いときには嫌気発酵を受けか
つ水が少なくて酸素があるときには好気発酵を受け、そ
の表面にうねを作り面積を増加させて太陽光線を受け易
くするとともに通風を良くして水を蒸発させる方法と、
からなることを特徴とする流未処理不要の有機性汚水処
理方法の提供にあり、また前記の有機性汚水処理方法に
おいて蒸発面に降水及び積雪の無いように太陽光線を良
く通すように透明の屋根を設けることと、冬期の強風で
うねの変形を防止しかつ土壌の飛散がないように防壁を
設ける方法と、地下水槽のガス体が水と同じように多孔
質・礫層・土壌層・うね等から空気中へ発散させる方法
と、からなる流未処理不要の有機性汚水処理方法の提供
にある。
The present invention was developed in order to solve the above-mentioned problems, and separates organic wastewater that does not require stream untreatment into a solid content and wastewater by a sieve, and The separated sewage is stored in a groundwater tank and anaerobically fermented to decompose it into water and gas, and the sewage that has been sent sequentially raises the water level and reaches the bottom of the porous gravel layer that covers the groundwater tank. Sometimes a method in which water is sucked up to the surface of the earth by capillary action, and the pores of the gravel serve as a carrier for anaerobic bacteria and the bacterial density is higher than that in water and when water passes through this layer, anaerobic fermentation is performed. A method of forming a soil layer containing soil microorganisms and organic matter reaching the ground surface in the upper layer, and when the water is sucked up to the ground surface by the capillary phenomenon of the soil layer and the amount of water is large and there is no oxygen, it undergoes anaerobic fermentation and water. Less oxygen Undergoing aerobic fermentation in some case, a method of ventilation may to evaporate water while susceptible to sunlight increases the area making ridges on the surface thereof,
The present invention provides a method for treating organic sewage that does not require untreated flow, and in the above-mentioned organic sewage treatment method, it is transparent to allow sunlight to pass well so that there is no precipitation or snow on the evaporation surface. A roof is provided, a method is used to prevent deformation of the ridge due to strong winds in the winter, and a barrier is provided to prevent the soil from scattering, and the gas body of the ground water tank is porous, gravel layer, and soil layer like water. -Providing a method for releasing organic sewage from a ridge, etc. into the air and a method for treating organic sewage that does not require stream treatment.

【0006】更に、本発明は有機性汚水中に含まれる固
形分を除去する篩を有する投入口と固形物を沈殿させて
除去する地下第1室と長期間のうちに生ずる沈殿物を除
去する地下第2室と、前記地下第1室及び地下第2室を
通過した有機性汚水を貯留して嫌気発酵を行なわせかつ
水とガス体に分解させる地下第3室とよりなる一連の地
下槽群と、前記地下第3室の上部を覆う網と該網より広
い面積を有しかつ地下第3室の水位が上がりこの層の底
面に着いたときに毛細管現象で水を地表近くに吸い上げ
る多孔質の礫層を載せ、更に該礫の細孔が嫌気性菌の担
体となりかつ該細孔が地下第3室の水中のそれより細菌
密度を高くして通過する水が更に嫌気発酵を受ける毛細
管層とから構成されることを特徴とする流未処理不要の
有機性汚水処理装置の提供にあり、また有機性汚水を地
下水槽に貯留して嫌気発酵を行ない水とガス体とに分解
する部分Aと、地下水槽上部に設けた多孔質の礫層で水
を毛細管現象で地表近くまで吸い上げるときに礫の細孔
を担体とした地下水槽の水中よりも嫌気性菌の密度の高
い部分と接触させて嫌気発酵を行なう部分Bと、前記B
部分上の土壌微生物及び有機物を含む土壌層にて水を毛
細管現象で地表面まで吸い上げるときに水分が多く酸素
がないときは土壌微生物の中の嫌気性菌により嫌気発酵
を行ない、一方水分が少なく酸素があるときは好気発酵
を行なう部分C、とからなる流未処理不要の有機性汚水
処理装置の提供にあり、また有機性汚水の嫌気発酵を行
なう地下水槽から水を多孔質の礫層の細孔の毛細管現象
を利用して地表近くまで吸い上げる層と、該層上の土壌
微生物及び有機物を含む土壌層の毛細管現象を利用して
地表まで吸い上げて地表にはうねを作り、更に表面積を
大きくしかつ太陽熱を受け易くするとともに通風を良く
して水を蒸発させ、植物が茂るときはその根から水を吸
い上げて葉面から蒸発させて蒸発が多くなる層とから構
成され、この構成により動力を使わず空気中に水を蒸発
させる流未処理不要の有機性汚水処理装置の提供にあ
り、更に有機性汚水が地下水槽で嫌気発酵により水とガ
ス体に分解されるときに、ガス体が地下水槽の上部に多
孔質の礫層と該礫層の上部にある土壌微生物及び有機物
を含む土壌の層を通して空気中に発散させることにより
特別なガス抜き装置を使用しない流未処理不要の有機性
汚水処理装置の提供にある。
[0006] Further, the present invention removes the deposit which occurs in a long period of time with an input port having a sieve for removing solids contained in organic wastewater, the first underground chamber for precipitating and removing solids. A series of underground tanks consisting of an underground second chamber and an underground third chamber that stores the organic wastewater that has passed through the underground first chamber and the underground second chamber to perform anaerobic fermentation and decompose it into water and gas A group, a net that covers the upper part of the third underground chamber, and a porous area that has a larger area than the net and that when the water level in the third underground chamber rises and reaches the bottom of this layer, sucks water near the surface of the ground by capillary action. Capillary tube on which a high quality gravel layer is placed, and the pores of the gravel serve as a carrier for anaerobic bacteria and the pores have a higher bacterial density than that in the water of the third underground chamber and the water passing through is further subjected to anaerobic fermentation. An organic sewage treatment system that does not require stream treatment In addition, the organic wastewater is stored in the groundwater tank and decomposed into water and gas by performing anaerobic fermentation, and the porous gravel layer provided at the upper part of the groundwater tank causes the water to reach the surface by capillary action. A part B for performing anaerobic fermentation by bringing it into contact with a part having a higher density of anaerobic bacteria than that of water in a ground water tank having pores of gravel as a carrier when sucking up to a close vicinity;
When water is sucked up to the ground surface by capillarity in the soil layer containing soil microorganisms and organic matter above the part, when there is no oxygen, anaerobic bacteria in the soil microorganisms perform anaerobic fermentation, while there is little water. The present invention provides an organic wastewater treatment apparatus that does not require a flow untreated and comprises a part C that performs aerobic fermentation when oxygen is present. Also, a porous gravel layer is provided for water from an underground water tank that performs anaerobic fermentation of organic wastewater. The layer that sucks up to the surface of the earth using the capillary action of the pores and the capillary of the soil layer that contains soil microorganisms and organic substances on the layer that sucks up to the surface of the ground to create a ridge on the surface, It is made up of a layer that increases the amount of water and makes it easier to receive solar heat and improves ventilation, evaporates water, and when a plant grows, it absorbs water from its roots and evaporates from the leaves to increase evaporation. The purpose is to provide an organic sewage treatment device that does not use power to evaporate water into the air and does not require untreated organic sewage treatment.Furthermore, when organic sewage is decomposed into water and gas by anaerobic fermentation in a groundwater tank, gas The body does not use a special degassing device by venting into the air through a porous gravel layer above the groundwater tank and a layer of soil containing soil microorganisms and organic matter above the gravel layer To provide an organic sewage treatment device.

【0007】すなわち、本発明は有機性汚水を篩により
固形分と汚水とに分離して汚水を地下水槽に貯留して嫌
気発酵を行ない水とガス体に分解し、次々に底部に送ら
れてくる汚水によりその水位が上がり地下水槽を覆う多
孔質礫層の底面に達すると水は毛細管現象により地表近
くに吸い上げられることになり、一方礫の細孔は嫌気性
菌の担体となり細菌密度は水中のそれよりも大きく、水
はこの層を通過する時にここに接触して嫌気発酵を受け
その上層に地表面に達する土壌微生物や有機物を含んだ
土壌層が形成されることになる。更に、水は土壌層の毛
細管現象により地表へと吸い上げられこの層では水が多
く酸素のないときは嫌気発酵を受けるが水が少なく酸素
があるときは好気発酵を受けることになる。そして、地
表面にはうねを作り面積を増やして太陽光線を受け易く
するとともに通風を良くして水の蒸発をさせることにな
る。ここに植物があるときは、根から水を吸い上げ葉面
から蒸散させるので更に蒸発しやすくなるので、この蒸
発面に降水や積雪のないように太陽光線を良く通すよう
に透明の屋根を設けることと冬期の強風でうねの変形を
防止するとともに土壌の飛散がないように障壁を設ける
ことになる。また地下水槽のガス体は水と同じように多
孔質礫層・土壌層・うねから空気中に発散されることに
なる。
That is, according to the present invention, organic sewage is separated by a sieve into solids and sewage, and the sewage is stored in a groundwater tank for anaerobic fermentation to decompose it into water and gas, which are then sent to the bottom. When the water level rises due to incoming sewage and reaches the bottom of the porous gravel layer that covers the groundwater tank, the water is sucked up near the surface by capillary action, while the pores of the gravel serve as a carrier for anaerobic bacteria and the bacterial density is When the water passes through this layer, it comes in contact with it and undergoes anaerobic fermentation to form a soil layer containing soil microorganisms and organic matter reaching the ground surface in the upper layer. Further, water is sucked up to the surface of the earth due to the capillarity of the soil layer, and this layer undergoes anaerobic fermentation when there is much water and no oxygen, but aerobically fermentation when there is little water and oxygen. Then, ridges are formed on the ground surface to increase the area to make it easier to receive sunlight and improve ventilation to evaporate water. When there is a plant here, it absorbs water from the roots and evaporates from the leaves, which makes it easier to evaporate.Therefore, install a transparent roof on this evaporation surface so that the sun's rays can pass well without causing precipitation or snow. In addition, strong winds in winter will prevent deformation of the ridges and barriers will be installed to prevent soil from scattering. Moreover, the gas body in the groundwater tank will be released into the air from the porous gravel layer, soil layer, and ridge like water.

【0008】このように本発明方法によれば、完全に独
立した動力を使わない設置場所も河川に近いところなど
の制限の受けない流末処理不要の有機性汚水処理方法を
提供することができる。
As described above, according to the method of the present invention, it is possible to provide an organic wastewater treatment method that does not require any end-of-stream treatment such as a completely independent power-less installation site or a place near a river. .

【0009】[0009]

【発明の実施の形態】本発明の実施形態は、汚水を投入
口から投入するとき篩を通して固形分と水分とに分離し
て篩上の固形分は別に堆肥とする。また、汚水は投入管
を通り地下第1室に入り静置され沈殿物が除去されて上
ずみは連絡孔から地下の第2室に入り、沈殿物がでれば
除去されるとともに底部の連絡孔から地下の第3室に入
る。一方、嫌気発酵を受けた汚水は水とガス体とに分解
されて水は多孔室の礫層の毛細管現象で地表近くに吸い
上げられるとともに、礫の細孔は嫌気性菌の担体となり
多くの細菌が住みつきその密度は水中のそれより高くな
る。このように水が吸い上げられてここを通るときに接
触されて嫌気発酵を受けることになる。そして、その上
部は土壌微生物や有機物を含む土壌層で地表面に達して
水は毛細管現象で地表面にまで吸い上げられることにな
る。その際、途中水が多く酸素がないときは土壌微生物
中の嫌気性菌により嫌気発酵を受けるが、水が少なく酸
素があるときは好気性菌により好気発酵を受けることに
なる。
BEST MODE FOR CARRYING OUT THE INVENTION In the embodiment of the present invention, when sewage is introduced from an input port, it is separated into a solid content and moisture through a sieve, and the solid content on the sieve is separately composted. In addition, the sewage passes through the input pipe, enters the underground first chamber, is left to stand, and the precipitate is removed, and the upper pits enter the underground second chamber through the communication hole. Enter the third underground room from the hole. On the other hand, sewage that has undergone anaerobic fermentation is decomposed into water and gas, and water is sucked up near the surface by the capillary phenomenon of the gravel layer of the porous chamber, and the pores of the gravel serve as a carrier for anaerobic bacteria and many bacteria. But they are more dense than they are in water. In this way, when water is sucked up and passes through it, it is contacted and undergoes anaerobic fermentation. Then, the upper part thereof is a soil layer containing soil microorganisms and organic matter and reaches the ground surface, and water is sucked up to the ground surface by a capillary phenomenon. At that time, when there is a large amount of water on the way and there is no oxygen, the anaerobic fermentation in the soil microorganisms causes anaerobic fermentation, while when there is little water and oxygen, the aerobic fermentation causes aerobic fermentation.

【0010】すなわち、本発明は有機性汚水を投入口の
蓋を開け篩を通して投入管に入れると汚水は地下の第1
室に入り、更に汚水は上部にある連絡孔から地下の第2
室に入る。その際、マンホールの蓋は常に閉めてあるの
で汚水は下部の連絡孔から地下の第3室に入ることにな
る。そして、汚水は嫌気発酵を受け水とガス体とに分解
されるので汚水の水位が上り網に達して上部には上面よ
り広い面積を待つ多孔質の大きな礫層と、その上部に多
孔質の小さな礫層と、その上部に地表面に達する土壌微
生物や有機物を含む土壌層とを載せてることになるの
で、地表面は地表GLと同じ高さでうねを形成すること
になる。
That is, according to the present invention, when the organic wastewater is put into the charging pipe through the sieve by opening the lid of the charging port, the wastewater is underground first.
After entering the room, sewage will be sent to the second underground via the communication hole at the top.
Enter the room. At that time, since the manhole cover is always closed, sewage will enter the third underground chamber through the lower communication hole. And since sewage undergoes anaerobic fermentation and is decomposed into water and gas, the water level of the sewage reaches the net and the upper part is a large gravel layer of awaiting a larger area than the upper surface, and the upper part is porous. Since a small gravel layer and a soil layer containing soil microorganisms and organic matter reaching the ground surface are placed on top of it, the ground surface forms a ridge at the same height as the ground surface GL.

【0011】[0011]

【実施例】以下、図面によって本発明の実施例について
説明する。本発明からなる流未処理不要の有機性汚水処
理装置は、図1及び図2に示すように紅茶搾り粕からで
る有機性汚水等を投入口蓋3を開け、篩2を通して投入
管4を経て地下第1室6に入れる。その際、篩2の上に
残った固形分は別に堆肥化する。投入管4は地下第1室
6の底部より上部の隙間5が開いているので、汚水はそ
の地下第1室6の底部から入る。また、地下第1室6の
沈殿物は第1室マンホールの第1室マンホール蓋8を開
けてそこから除去する。一方、第1室マンホール蓋8か
らは地下第1室6の水位を監視することができる。更
に、地下第1室6の汚水の水位が上がってくると上部の
第2室連絡孔7から地下第2室9に入るとともに地下第
2室9の沈殿物は第2室マンホール蓋10を開けて除去
する。更に、汚水は底部の第3室連絡孔11を通って地
下水第3室12に入り、地下第3室12は地下水槽で汚
水は嫌気発酵を受けて汚水の中の有機物は水とガス体と
に分解されることになる。また、地下第3室12の水位
が上がり網13に達すると、この網13の上部には地下
第3室12の面積より広くて大多孔質礫層14と、その
上に小多孔質礫層15とが形成される。そして、水は礫
の細孔の毛細管現象により地表へと吸い上げられてゆき
礫の細孔は嫌気性菌の担体となり、そこは地下第3室1
2の水中より細菌密度が高くなり、吸い上げられる水は
ここを通るとき嫌気発酵を受けることになる。一方、小
多孔質礫層15の上部には土壌微生物や有機物を含む土
壌層16が地表面GLまであり、水は毛細管現象により
地表面へと吸い上げられるが土壌微生物や有機物を含む
土壌層16の水が多く酸素がないときは土壌微生物中の
嫌気性菌により吸い上げられる水は嫌気発酵を受け、一
方水が少なく酸素があるときは好気性菌により好気発酵
を受けることになる。また、土壌微生物や有機物を含む
土壌層16の地表面は、うね17が作られ表面積を増し
て太陽熱を受け易くしたり通風を良くしたりして水を空
気中に蒸発させることができる。ここに植物が茂るとき
は、その根が水を吸い上げ葉面から蒸散させるので更に
蒸発が多くなり、また第3室マンホール18は地下第3
室12の水位や底部の観察をしたりして汚水のサンプリ
ングをしたり沈殿を除去したりするときに使用すること
になる。また、地下第3室12のガス体は網13、大多
孔質礫層14、小多孔質礫層15、土壌微生物や有機物
を含む土壌層16を経てうね17から空気中に発散され
る。そして、うね17の蒸発面に降雨や積雪を防ぎ太陽
光線を通すために透明な屋根20を設けるとともに支柱
21には通風を良くするために四方が開放されている。
なお、冬期の強風によりうね17が変形したり土壌が飛
散されないように障壁22が設けられている。
Embodiments of the present invention will be described below with reference to the drawings. As shown in FIGS. 1 and 2, the organic wastewater treatment apparatus according to the present invention, which does not require a flow untreated, opens the inlet port lid 3 for the organic wastewater discharged from the black tea meal, passes through the sieve 2, and passes through the inlet pipe 4 to the underground. Put in the first chamber 6. At that time, the solid content remaining on the sieve 2 is separately composted. Since the gap 5 above the bottom of the first underground chamber 6 is opened in the input pipe 4, the sewage enters from the bottom of the first underground chamber 6. Moreover, the deposit in the first underground chamber 6 is removed from the first chamber manhole by opening the first chamber manhole cover 8 of the first chamber manhole. On the other hand, the water level in the first underground room 6 can be monitored from the first room manhole cover 8. Furthermore, when the water level of the sewage in the first underground chamber 6 rises, it enters the second underground chamber 9 through the upper second chamber communication hole 7, and the sediment in the second underground chamber 9 opens the second chamber manhole cover 10. To remove. Further, the sewage enters the groundwater third chamber 12 through the bottom third chamber communication hole 11, the underground third chamber 12 is a groundwater tank, and the sewage is subjected to anaerobic fermentation, so that the organic substances in the sewage are water and gas. Will be decomposed into. When the water level in the third underground chamber 12 rises and reaches the net 13, a large porous gravel layer 14 having a larger area than that of the third underground chamber 12 is formed on the upper part of the net 13, and a small porous gravel layer is formed thereon. And 15 are formed. Then, the water is sucked up to the ground surface by the capillary phenomenon of the pores of the gravel, and the pores of the gravel serve as a carrier for the anaerobic bacteria.
The bacteria density is higher than that of the water of 2, and the water that is sucked up will undergo anaerobic fermentation as it passes through it. On the other hand, in the upper part of the small porous gravel layer 15, there is a soil layer 16 containing soil microorganisms and organic matter up to the ground surface GL, and water is sucked up to the ground surface by the capillarity phenomenon, but the soil layer 16 containing soil microorganisms and organic matter. When there is a lot of water and no oxygen, the water sucked up by the anaerobic bacteria in the soil microorganisms undergoes anaerobic fermentation, while when there is little water and oxygen, it undergoes aerobic fermentation by the aerobic bacteria. Further, on the ground surface of the soil layer 16 containing soil microorganisms and organic matter, ridges 17 are formed to increase the surface area to make it easier to receive solar heat and improve ventilation, so that water can be evaporated into the air. When a plant grows here, its roots suck up water and evaporate from the leaf surface, further increasing evaporation, and the third chamber manhole 18 is located in the third underground.
It will be used when observing the water level and the bottom of the chamber 12 to sample sewage and remove sediment. Further, the gas body in the third underground chamber 12 is released into the air from the ridge 17 through the net 13, the large porous gravel layer 14, the small porous gravel layer 15, and the soil layer 16 containing soil microorganisms and organic matter. Further, a transparent roof 20 is provided on the evaporation surface of the ridge 17 to prevent rain and snow and to pass the sun's rays, and the columns 21 are open on all sides to improve ventilation.
A barrier 22 is provided to prevent the ridges 17 from being deformed and the soil from scattering due to the strong wind in winter.

【0012】[0012]

【発明の効果】本発明は、流未処理を不要とする有機性
汚水を篩により固形分と汚水とに分離しかつ分離された
汚水を地下水槽に貯留して嫌気発酵させて水とガス体と
に分解する方法と、順次送流されてきた汚水により水位
が上がり地下水槽を覆う多孔質礫層の底面に達したとき
に毛細管現象により水が地表近くに吸い上げられる方法
と、前記礫の細孔が嫌気性菌の担体となり細菌密度が水
中よりも大きくかつ水がこの層を通過するときに接触し
て嫌気発酵を受け該上層に地表面に達する土壌微生物及
び有機物を含む土壌層を形成する方法と、前記土壌層の
毛細管現象により水が地表へ吸い上げられて水が多くて
酸素の無いときには嫌気発酵を受けかつ水が少なくて酸
素があるときには好気発酵を受け、その表面にうねを作
り面積を増加させて太陽光線を受け易くするとともに通
風を良くして水を蒸発させる方法と、からなることを特
徴とする流未処理不要の有機性汚水処理方法であり、ま
た前記の有機性汚水処理方法において、蒸発面に降水及
び積雪の無いように太陽光線を良く通すように透明の屋
根を設けることと冬期の強風ごうねの変形を防止しかつ
土壌の飛散がないように防壁を設ける方法と、地下水槽
のガス体が水と同じように多孔質・礫層・土壌層・うね
等から空気中へ発散させる方法と、からなる流未処理不
要の有機性汚水処理方法である。
INDUSTRIAL APPLICABILITY The present invention separates organic wastewater that does not require untreated flow into a solid content and wastewater by a sieve, and stores the separated wastewater in a groundwater tank for anaerobic fermentation to produce water and gas. And the method of decomposing the gravel by the capillary phenomenon when the water level rises due to the sewage that has been sent in sequence and reaches the bottom of the porous gravel layer that covers the groundwater tank. The pores serve as carriers for anaerobic bacteria and the bacterial density is higher than that in water, and when water passes through this layer, it contacts and undergoes anaerobic fermentation to form a soil layer containing soil microorganisms and organic matter that reaches the ground surface in the upper layer. The method and the capillary action of the soil layer causes water to be sucked up to the surface of the earth and undergoes anaerobic fermentation when there is much water and no oxygen, and aerobically fermentation when there is little water and oxygen, with ridges on its surface. Increase the building area A method of evaporating water by improving the ventilation while making it easier to receive sun rays, and an organic sewage treatment method that does not require a stream untreated, and in the organic sewage treatment method, the evaporation A transparent roof so that sunlight can pass through it well so that there is no precipitation or snow, and how to prevent the deformation of strong wind ridges in the winter and to prevent the soil from scattering, It is a method of discharging organic matter from a porous body, a gravel layer, a soil layer, a ridge, etc., into the air in the same manner as water, and an organic wastewater treatment method that does not require flow treatment.

【0013】更に、本発明は有機性汚水中に含まれる固
形分を除去する篩を有する投入口と固形物を沈殿させて
除去する地下第1室と長期間のうちに生ずる沈殿物を除
去する地下第2室と、前記地下第1室及び地下第2室を
通過した有機性汚水を貯留して嫌気発酵を行なわせかつ
水とガス体に分解させる地下第3室とよりなる一連の地
下槽群と、前記地下第3室の上部を覆う網と該網より広
い面積を有しかつ地下第3室の水位が上がりこの層の底
面に着いたときに毛細管現象で水を地表近くに吸い上げ
る多孔質の礫層を載せ、更に該礫の細孔が嫌気性菌の担
体となりかつ該細孔が地下第3室の水中のそれより細菌
密度を高くして通過する水が更に嫌気発酵を受ける毛細
管層とから構成されることを特徴とする流未処理不要の
有機性汚水処理装置であり、また有機性汚水を地下水槽
に貯留して嫌気発酵を行ない水とガス体とに分解する部
分Aと、地下水槽上部に設けた多孔質の礫層で水を毛細
管現象で地表近くまで吸い上げるときに礫の細孔を担体
とした地下水槽の水中よりも嫌気性菌の密度の高い部分
と接触させて嫌気発酵を行なう部分Bと、前記B部分上
の土壌微生物及び有機物を含む土壌層にて水を毛細管現
象で地表面まで吸い上げるときに水分が多く酸素がない
ときは土壌微生物の中の嫌気性菌により嫌気発酵を行な
い、一方水分が少なく酸素があるときは好気発酵を行な
う部分Cとからなる流未処理不要の有機性汚水処理装置
であり、また有機性汚水の嫌気発酵を行なう地下水槽か
ら水を多孔質の礫層の細孔の毛細管現象を利用して地表
近くまで吸い上げる層と、該層上の土壌微生物及び有機
物を含む土壌層の毛細管現象を利用して地表まで吸い上
げて地表にはうねを作り、更に表面積を大きくしかつ太
陽熱を受け易くするとともに通風を良くして水を蒸発さ
せ、植物が茂るときはその根から水を吸い上げて葉面か
ら蒸発させて蒸発が多くなる層とから構成され、この構
成により動力を使わず空気中に水を蒸発させる流未処理
不要の有機性汚水処理装置であり、また有機性汚水が地
下水槽で嫌気発酵により水とガス体に分解されるときに
ガス体が地下水槽の上部に多孔質の礫層と該礫層の上部
にある土壌微生物及び有機物を含む土壌の層を通して空
気中に発散させることにより特別なガス抜き装置を使わ
ない流未処理不要の有機性汚水処理装置であるから、次
のような多くの効果を有する。 ア、食品製造のときに搾り粕からでる液体などを固形分
と汚水とに分離して固形分は従来どおり堆肥化すること
ができる。 イ、汚水は従来下水道に流し流末は河川に放流していた
が、それを全くせずに地下水槽に導き嫌気発酵して水と
ガス体とに分解することが可能となる。 ウ、地下水槽の上部に多孔質の礫層と、その上に土壌微
生物や有機物を含む土壌層が地表面まであり、水はこれ
らの層の毛細管現象により地表面にまで吸い上げられ空
気中に蒸発されることになる。 エ、地表面に植物があるときは、その根が水を吸い上げ
葉面から蒸散させるので更に蒸発が多くなる。 オ、吸い上げられる途中にこれらの層で嫌気発酵を受け
て土壌層では水が多く酸素がないときは嫌気発酵を受け
るが、水が少なく酸素があるときは好気発酵を受けるこ
とになる。 カ、地下水槽のガス体は同じように各層を通り地表面か
ら空気中に発散される。 キ、このようにして、動力を使わずしかも設置場所は河
川に近くなくてはならないなどの制限を受けないで、独
立した流末処理不要の有機性汚水処理装置で処理するこ
とができる。
Further, according to the present invention, an input port having a sieve for removing solids contained in organic wastewater, an underground first chamber for precipitating and removing solids, and a precipitate generated in a long period of time are removed. A series of underground tanks consisting of an underground second chamber and an underground third chamber that stores the organic wastewater that has passed through the underground first chamber and the underground second chamber to perform anaerobic fermentation and decompose it into water and gas A group, a net that covers the upper part of the third underground chamber, and a porous area that has a larger area than the net and that when the water level in the third underground chamber rises and reaches the bottom of this layer, sucks water near the surface of the ground by capillary action. Capillary tube on which a high quality gravel layer is placed, and the pores of the gravel serve as a carrier for anaerobic bacteria and the pores have a higher bacterial density than that in the water of the third underground chamber and the water passing through is further subjected to anaerobic fermentation. An organic sewage treatment system that does not require stream treatment In addition, the organic wastewater is stored in the groundwater tank and decomposed into water and gas by performing anaerobic fermentation, and the porous gravel layer provided at the top of the groundwater tank causes the water to reach near the surface by capillary action. Part B for performing anaerobic fermentation by contacting with a part of the groundwater tank having pores of gravel as a carrier when wicking and having a higher density of anaerobic bacteria, and a soil layer containing soil microorganisms and organic matter on the part B When water is sucked up to the ground surface by capillarity, anaerobic fermentation is carried out by anaerobic bacteria in soil microorganisms when there is not much oxygen and when there is little water and there is aerobic fermentation. It is an organic sewage treatment device consisting of C and no treatment, and sucks up water from the groundwater tank that performs anaerobic fermentation of organic sewage to the surface of the earth by utilizing the capillary phenomenon of pores in the porous gravel layer. Layer and on the layer Using the capillarity of the soil layer containing soil microorganisms and organic matter, it sucks up to the surface to create ridges on the surface, further increasing the surface area and making it easier to receive solar heat, and improving ventilation to evaporate water When it grows, it absorbs water from its roots and evaporates from the leaf surface to increase evaporation.This structure evaporates water into the air without using power. Untreated organic wastewater treatment. A device, and when organic wastewater is decomposed into water and a gas body by anaerobic fermentation in a groundwater tank, the gas body is a porous gravel layer above the groundwater tank, and soil microorganisms and organic matter above the gravel layer. Since it is an organic wastewater treatment device that does not require a special degassing device and is not treated by flowing it into the air through a layer of soil containing water, it has many effects as follows. (1) Liquids and the like produced from squeezed lees at the time of food production can be separated into solids and sewage, and the solids can be composted as usual. B. Conventionally, sewage was conventionally discharged to the sewer and discharged to the river at the end, but without doing it at all, it can be guided to the ground water tank and anaerobically fermented to decompose it into water and gas. C) Porous gravel layer on top of ground water tank and soil layer containing soil microorganisms and organic matter on the ground surface, and water is sucked up to the ground surface by the capillary action of these layers and evaporated into the air. Will be done. When there is a plant on the ground surface, its roots absorb water and evaporate from the leaf surface, resulting in more evaporation. E, anaerobically fermented in these layers while being sucked up, the soil layer undergoes anaerobic fermentation when there is much water and no oxygen, but when there is little water and oxygen, it undergoes aerobic fermentation. F. Gas bodies in groundwater tanks pass through each layer in the same way and are emitted from the ground surface into the air. G. In this way, it is possible to treat with an independent organic sewage treatment apparatus that does not require end-of-stream treatment, without being restricted by the fact that it does not use power and that the installation site must be near a river.

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

【図1】本発明の流末処理不要の有機性汚水処理装置を
示した平面図。
FIG. 1 is a plan view showing an organic wastewater treatment apparatus of the present invention that does not require end-of-stream treatment.

【図2】図1に示した本発明装置を示した断面図。FIG. 2 is a sectional view showing the device of the present invention shown in FIG.

【符号の説明】[Explanation of symbols]

1 投入口 13 網 2 篩 14 大多孔質礫層 3 投入口蓋 15 小多孔質礫層 4 投入管 16 土壌層 5 隙間 17 うね 6 地下第1室 18 第3室マンホール 7 第2室連絡孔 19 第3室マンホール
蓋 8 第1室マンホール蓋 20 屋根 9 地下第2室 21 支柱 10 第2室マンホール蓋 22 障壁 11 第3室連絡孔 GL 地表面 12 地下第3室
1 input port 13 mesh 2 sieve 14 large porous gravel layer 3 input port lid 15 small porous gravel layer 4 input pipe 16 soil layer 5 gap 17 ridge 6 underground first chamber 18 third chamber manhole 7 second chamber communication hole 19 Third Room Manhole Cover 8 First Room Manhole Cover 20 Roof 9 Second Underground Room 21 Strut 10 Second Room Manhole Cover 22 Barrier 11 Third Room Communication Hole GL Ground Surface 12 Underground Third Room

───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 4D027 AC01 AC02 AC03 AC05 4D040 AA13 AA23 AA31 CC01 CC07 CC09 4D041 AA01 AB03 AD11 CA08 CB04 CC08    ─────────────────────────────────────────────────── ─── Continued front page    F-term (reference) 4D027 AC01 AC02 AC03 AC05                 4D040 AA13 AA23 AA31 CC01 CC07                       CC09                 4D041 AA01 AB03 AD11 CA08 CB04                       CC08

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 流未処理を不要とする有機性汚水を篩に
より固形分と汚水とに分離しかつ分離された汚水を地下
水槽に貯留して嫌気発酵させて水とガス体とに分解する
方法と、順次送流されてきた汚水により水位が上がり地
下水槽を覆う多孔質礫層の底面に達したときに毛細管現
象により水が地表近くに吸い上げられる方法と、前記礫
の細孔が嫌気性菌の担体となり細菌密度が水中よりも大
きくかつ水がこの層を通過するときに接触して嫌気発酵
を受け該上層に地表面に達する土壌微生物及び有機物を
含む土壌層を形成する方法と、前記土壌層の毛細管現象
により水が地表へ吸い上げられて水が多くて酸素の無い
ときには嫌気発酵を受けかつ水が少なくて酸素があると
きには好気発酵を受け、その表面にうねを作り面積を増
加させて太陽光線を受け易くするとともに通風を良くし
て水を蒸発させる方法と、からなることを特徴とする流
未処理不要の有機性汚水処理方法。
1. An organic wastewater that does not require stream untreatment is separated into solids and wastewater by a sieve, and the separated wastewater is stored in a groundwater tank and anaerobically fermented to decompose it into water and gas. Method, the method of sucking water near the surface of the ground by capillary action when the water level rises due to the sewage that is sequentially sent and reaches the bottom of the porous gravel layer that covers the groundwater tank, and the pores of the gravel are anaerobic A method of forming a soil layer containing soil microorganisms and organic matter that reaches the ground surface in the upper layer by anaerobic fermentation by contact when water having a bacterial density higher than that of water and water passing through this layer serves as a carrier for bacteria, and Capillary phenomenon of the soil layer causes water to be sucked up to the surface and undergoes anaerobic fermentation when there is a lot of water and no oxygen, and aerobically fermentation when there is little water and oxygen, creating a ridge on the surface and increasing the area. Let the sun rays A method for treating organic sewage that does not require stream untreatment, which comprises a method for evaporating water by improving ventilation and improving the ventilation.
【請求項2】 前項の有機性汚水処理方法において、蒸
発面に降水及び積雪の無いように太陽光線を良く通すよ
うに透明の屋根を設け冬期の強風でうねの変形を防止し
かつ土壌の飛散がないように防壁を設ける方法と、地下
水槽のガス体が水と同じように多孔質・礫層・土壌層・
うね等から空気中へ発散させる方法と、からなる請求項
1記載の流未処理不要の有機性汚水処理方法。
2. The method for treating organic sewage according to the preceding paragraph, wherein a transparent roof is provided on the evaporation surface so that sunlight can pass well so that there is no precipitation or snow, and the ridge is prevented from being deformed by strong wind in winter and the soil is protected. The method of installing a barrier to prevent scattering, and the gas body of the groundwater tank has the same porosity, gravel layer, and soil layer as water.
The method for discharging organic sewage according to claim 1, wherein the organic sewage treatment does not require flow treatment.
【請求項3】 有機性汚水中に含まれる固形分を除去す
る篩を有する投入口と固形物を沈殿させて除去する地下
第1室と長期間のうちに生ずる沈殿物を除去する地下第
2室と、前記地下第1室及び地下第2室を通過した有機
性汚水を貯留して嫌気発酵を行なわせかつ水とガス体に
分解させる地下第3室とよりなる一連の地下槽群と、前
記地下第3室の上部を覆う網と該網より広い面積を有し
かつ地下第3室の水位が上がりこの層の底面に着いたと
きに毛細管現象で水を地表近くに吸い上げる多孔質の礫
層を載せ、更に該礫の細孔が嫌気性菌の担体となりかつ
該細孔が地下第3室の水中のそれより細菌密度を高くし
て通過する水が更に嫌気発酵を受ける毛細管層と、から
構成されることを特徴とする流未処理不要の有機性汚水
処理装置。
3. An inlet having a sieve for removing solids contained in organic wastewater, an underground first chamber for precipitating and removing solids, and an underground second for removing sediments generated in a long period of time. A series of underground tank groups consisting of a chamber, and an underground third chamber for storing the organic wastewater that has passed through the underground first chamber and the underground second chamber to perform anaerobic fermentation and decompose it into water and gas. A net covering the upper part of the third underground chamber and a porous gravel having a larger area than the net and sucking up water near the surface of the ground by capillary action when the water level of the third underground chamber rises and reaches the bottom of this layer. A capillary layer on which a layer is placed, the pores of the gravel further serve as a carrier for anaerobic bacteria, and the pores further pass anaerobic fermentation of water having a higher bacterial density than that in the water of the third underground chamber; An organic sewage treatment apparatus that does not require untreated flow.
【請求項4】 有機性汚水を地下水槽に貯留して嫌気発
酵を行ない水とガス体とに分解する部分Aと、地下水槽
上部に設けた多孔質の礫層で水を毛細管現象で地表近く
まで吸い上げるときに礫の細孔を担体とした地下水槽の
水中よりも嫌気性菌の密度の高い部分と接触させて嫌気
発酵を行なう部分Bと、前記B部分上の土壌微生物及び
有機物を含む土壌層にて水を毛細管現象で地表面まで吸
い上げるときに水分が多く酸素がないときは土壌微生物
の中の嫌気性菌により嫌気発酵を行ない、一方水分が少
なく酸素があるときは好気発酵を行なう部分C、とから
なる請求項3記載の流未処理不要の有機性汚水処理装
置。
4. A portion A where organic sewage is stored in a groundwater tank and decomposed into water and gas by anaerobic fermentation, and a porous gravel layer provided at the upper part of the groundwater tank causes the water to reach the surface near the surface by capillary action. Part B in which anaerobic fermentation is carried out by contacting with a part of the groundwater tank that has pores of gravel as a carrier when it is sucked up to a higher density than the water, and soil containing soil microorganisms and organic matter on the part B When water is sucked up to the ground surface by capillarity in a layer, anaerobic fermentation is performed by anaerobic bacteria in soil microorganisms when there is much water and no oxygen, while aerobic fermentation is performed when there is little water and oxygen. The organic wastewater treatment apparatus according to claim 3, which is composed of a part C and the flow untreated.
【請求項5】 有機性汚水の嫌気発酵を行なう地下水槽
から水を多孔質の礫層の細孔の毛細管現象を利用して地
表近くまで吸い上げる層と、該層上の土壌微生物及び有
機物を含む土壌層の毛細管現象を利用して地表まで吸い
上げて地表にはうねを作り、更に表面積を大きくしかつ
太陽熱を受け易くするとともに通風を良くして水を蒸発
させ、植物が茂るときはその根から水を吸い上げて葉面
から蒸発させて蒸発が多くなる層とから構成され、この
構成により動力を使わず空気中に水を蒸発させる請求項
3記載の流未処理不要の有機性汚水処理装置。
5. A layer for sucking water from a ground water tank for anaerobic fermentation of organic wastewater to the surface of the earth by utilizing capillary action of pores of a porous gravel layer, and soil microorganisms and organic matter on the layer It sucks up to the surface of the earth using the capillary action of the soil layer to form ridges on the surface, further increases the surface area and makes it easier to receive solar heat, improves ventilation, evaporates water, and when plants grow, its roots. The organic sewage treatment apparatus according to claim 3, wherein the organic sewage treatment apparatus according to claim 3, wherein the organic sewage treatment apparatus does not require power to evaporate the water into the air. .
【請求項6】 有機性汚水が地下水槽で嫌気発酵により
水とガス体に分解されるときに、ガス体が地下水槽の上
部に多孔質の礫層と該礫層の上部にある土壌微生物及び
有機物を含む土壌の層を通して空気中に発散させること
により、特別なガス抜き装置を使用しない請求項3記載
の流未処理不要の有機性汚水処理装置。
6. When an organic wastewater is decomposed into water and a gas body by anaerobic fermentation in a groundwater tank, the gas body has a porous gravel layer above the groundwater tank and soil microorganisms above the gravel layer. The untreated organic wastewater treatment apparatus according to claim 3, wherein a special degassing apparatus is not used by allowing the organic wastewater to diffuse into the air through a layer of soil containing organic matter.
JP2001273333A 2001-09-10 2001-09-10 Organic sewage treatment method not requiring flow end treatment and equipment for the same Pending JP2003080280A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2001273333A JP2003080280A (en) 2001-09-10 2001-09-10 Organic sewage treatment method not requiring flow end treatment and equipment for the same

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2001273333A JP2003080280A (en) 2001-09-10 2001-09-10 Organic sewage treatment method not requiring flow end treatment and equipment for the same

Publications (1)

Publication Number Publication Date
JP2003080280A true JP2003080280A (en) 2003-03-18

Family

ID=19098563

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2001273333A Pending JP2003080280A (en) 2001-09-10 2001-09-10 Organic sewage treatment method not requiring flow end treatment and equipment for the same

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Country Link
JP (1) JP2003080280A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7407577B2 (en) * 2004-09-17 2008-08-05 Curt Kerns Tertiary filter septic system and method
CN102633365A (en) * 2012-04-24 2012-08-15 山东建筑大学 Wind-energy superimposed-negative-pressure ventilation reoxygenation wastewater treatment system for artificial wetland

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7407577B2 (en) * 2004-09-17 2008-08-05 Curt Kerns Tertiary filter septic system and method
US7695620B2 (en) 2004-09-17 2010-04-13 Curt Kerns Tertiary filter septic system and method
CN102633365A (en) * 2012-04-24 2012-08-15 山东建筑大学 Wind-energy superimposed-negative-pressure ventilation reoxygenation wastewater treatment system for artificial wetland

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