JP2001246283A - Microbe fermenting treatment device using magnetic field floor and filter medium - Google Patents

Microbe fermenting treatment device using magnetic field floor and filter medium

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Publication number
JP2001246283A
JP2001246283A JP2000105713A JP2000105713A JP2001246283A JP 2001246283 A JP2001246283 A JP 2001246283A JP 2000105713 A JP2000105713 A JP 2000105713A JP 2000105713 A JP2000105713 A JP 2000105713A JP 2001246283 A JP2001246283 A JP 2001246283A
Authority
JP
Japan
Prior art keywords
tank
magnetic field
water
liquid
pump
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
JP2000105713A
Other languages
Japanese (ja)
Inventor
Yoshio Nakamura
義雄 中村
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 JP2000105713A priority Critical patent/JP2001246283A/en
Publication of JP2001246283A publication Critical patent/JP2001246283A/en
Pending legal-status Critical Current

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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
    • Y02W10/20Sludge processing

Abstract

PROBLEM TO BE SOLVED: To turn night soils and organic garbage into a bacterial soil conditioning material and reclaimed tap water. SOLUTION: This microbe fermenting treatment device is constituted of (1) an inner-tank using a porous plate, (2) a pump with grinding and circulating functions, (3) a raw water tank with aeration piping, (4) an inner-tank with a grinding device and a magnetic field, (5) a crushing device with a lift pump, (6) a rotary screen with a filter cloth wound outside a cylindrical frame, rotating and separating foreign matters from a filtrate and discharging them, (7) an inner-tank set in a main tank and having a magnetic field, (8) a plurality of fermentation tanks spread over a magnetic field net, set tiltingly and having aeration devices, (9) a recovery tank with a magnetic field and a lift pump and (10) an adsorption tank filled with cokes and having backward washing piping whose pipesare set vertically in parallel with are another and also having a plurality of discharge pipes, provided therein, and all of the above components can be overlapped or bent, and night soils ground by far infrared ray effect and generated on the magnetic field or night soils ground by electromagnetic waves and generated on the magnetic field and also a slurry liquid of organic garbage are turned into a colloid-like bacterial soil conditioning material or reclaimed water in compliance with oxygen, microbes and physical laws.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】当出願は現在社会問題化している
生ゴミ処理、下水道処理場の新増設の至難な問題を同時
に解決出来得るものである。非常に短い時間で土壌改良
液化、更に中水道水化が計れ、有蓋にして脱臭装置を設
ける事で、市街地や村落単位の処理装置として設置する
事においても、酵素、微生物の生活反応において速やか
に完全に処理する事が可能である。当項に於ける原水投
入に於いての発気や、酵素投入後摺潰ポンプで混合され
る間は発臭は感じるが、わずかの時間で酸化が始まり臭
気は感じなくなる。曝気に於ける撹散についても、敷布
された磁場マット上に滞積されている好気性菌の繁殖す
る活性汚泥に吸着され、大気間への臭気の撹散は見られ
ない事が実証されており、大きく貢献出来るものであ
る。
BACKGROUND OF THE INVENTION The present application can simultaneously solve the difficult problems of garbage disposal and the new construction of a new sewage treatment plant, which have become social problems. Soil improvement and liquefaction in a very short time can be measured, and furthermore, the water supply to the tap water can be measured. It can be completely processed. In this section, the odor is generated when the raw water is supplied and the enzyme is mixed with the squeezing pump after the supply of the enzyme. Regarding the dispersion during aeration, it was proved that no activated odor was dissipated into the atmosphere because it was adsorbed by activated sludge in which aerobic bacteria accumulated on the spread magnetic field mat. And can greatly contribute.

【0002】[0002]

【従来の技術】糞尿、汚泥については固液分離の後、液
体は原水、沈降、調整、爆気、脱窒、硝化、薬注して放
流という処理が構造。個体は脱水の後焼却して容量を減
らし焼却灰をケミカル固化等して埋立等により処理して
いる。手法に多少の異なりが見られるが行政に於ける従
来の処理装置であり構造の組み替えが技術の改進と言わ
れている。又屎尿を海洋投棄に依る処理を行っていると
ころもあるが海洋投棄が禁止されるという世界状況の中
上記の施設の設置以外の具体的方法は見あたらない状況
である。生ゴミについては焼却場で焼却の後、処理場に
於いて埋立処理を行っているが処理場不足や環境問題等
が生じてきている。こうした生ゴミを堆肥化する様々な
技術が出てきているが、出来た製品の行き先の問題を含
んでいる。
2. Description of the Related Art For manure and sludge, after solid-liquid separation, the liquid is treated with raw water, sedimentation, adjustment, explosion, denitrification, nitrification, chemical injection and discharge. Individuals are incinerated after dehydration to reduce the capacity, and the incinerated ash is treated by chemical solidification and the like by landfill. Although there are some differences in the method, it is a conventional processing unit in the government, and the reorganization of the structure is said to be a technological improvement. There is also a place where human waste is disposed of by ocean dumping, but in the world situation where ocean dumping is prohibited, there is no concrete method other than the installation of the above facilities. For garbage, after incineration at the incineration plant, landfilling is performed at the treatment plant. However, shortage of the treatment plant and environmental problems are occurring. Various technologies for composting such garbage have emerged, but they involve problems with the destination of the resulting products.

【0003】[0003]

【考案の解決しようとする課題】現在農地で問われてい
る地力の衰退であり急務として地中に有るべき微量要
素、特にアルミ、ミネラル成分と其れを殖生するべき有
機性資質物質の給与が絶対である。旧農法では人糞尿、
家庭から出る生ゴミを肥溜め、便槽で有機質堆肥化し微
量要素の殖生材として活用してきて農作物を生産してき
たものである。現在農家にも合併浄化槽が設置され、家
庭ゴミは行政が回収に回り、厚生省令では糞尿肥料は施
肥しては不可とすとさえ言われているが、行政サービス
は法律によって下水道処理、家庭ゴミは当然とされてい
るが実体として住民感情等で新設増設は至難を極めてい
るのが実情である。当出題は屎尿の海洋投棄が禁止され
ると言う世界状況の中で下水処理場の建設、生ゴミ処理
の焼却場の建設も地域住民等々の事情で進展は全く至難
の状況認識して、離島など行政サービスの行き届かない
村落単位で設置、活用することで酵素発酵による有菌土
壌改良材化し活用すると同時に中水道水化し再利用。農
地用灌漑用水としても有効に活用することを出願提供す
るものである。又、下水処理場から出る活性汚泥や有機
性生ゴミの焼却による環境問題や廃棄物処理、残留ダイ
オキシン等の残留物の問題を後生に残さない為に、環境
に影響を与えない微生物発酵による廃棄物を限りなく抑
えることの出来、有機性生ゴミを同時に処理するとき発
生する難分解繊維質(セルローズ質)に於いても、磁場
マットに未分解蛋白と一緒に滞積され、酵素、微生物の
言うなれば餌として処理され、速やかに液化されるもの
であり、あくまで生物分解処理装置として出願するもの
である。
[Problem to be solved by the invention] The decline of the fertility that is currently being sought in farmland, and urgently the supply of trace elements that should be underground, especially aluminum and mineral components, and the organic qualitative substances that should breed them. Absolute. In the old farming method, human manure,
It collects garbage from homes, converts it into organic compost in the toilet, and uses it as a breeding material for trace elements to produce agricultural products. Currently, farmers also have merged septic tanks, and the household waste is collected by the government.The Ministry of Health and Welfare even says that it is impossible to apply manure and fertilizers. It is considered natural, but it is a fact that it is extremely difficult to add new facilities due to the feelings of the residents. In this question, the construction of a sewage treatment plant and the construction of an incineration plant for garbage disposal are difficult to progress due to the situation of the local residents, etc. It is installed and used in villages where administrative services are not accessible, and is used as a soil-improving material for enzymatic fermentation. An application will be provided for the effective use as irrigation water for agricultural land. In addition, the disposal of activated sludge and organic garbage from the sewage treatment plant does not affect the environment because it does not cause environmental problems, waste treatment, and residual dioxin residues. The material can be kept to a minimum, and even in the case of hard-to-degrade fiber (cellulosic) generated when organic garbage is processed at the same time, it is accumulated together with undegraded protein on the magnetic field mat, and enzymes and microorganisms In other words, it is processed as feed and liquefied quickly, and is applied only as a biodegradation treatment device.

【0004】[0004]

【課題を解決するための手段】高濃度の人糞、生ゴミを
摺潰したスリラー液に微生物を接種して生物分解さす為
に微生物の活性、生殖、着床の最適な繁殖状件を満たし
た環境をかもし出す事によって有効な条件のもとで短い
時間で以下の手段、内容を用いた装置を提供するもので
ある。まず磁石を用いて磁場を設け磁場を通過する液
(物質)に高透磁力に依る除菌、落雷に依る現象のマイ
ナスイオンを発生させて磁場を通過さす事によるミネラ
ル素子の成分を多量に含むスリラー液化し、磁場ネット
に貼着した濾過材の上で未分解蛋白質は下面の磁場から
発生する電磁波に依るマイナスイオン効果で効率良く生
物分解されるものである。槽内部に滴下したスリラー液
は装置に依る間欠爆気に依って液中に細かい気泡として
滞留している微生物の呼吸ガス、微粒未分解物の発生す
るガス等々を間欠爆気に依る気泡と同時に大気中に拡散
し、新鮮な酸素を液中に溶融して嫌気性菌の活性、着
床、増殖を計る。こうした手段を用い有効に屎尿、生ゴ
ミを有菌土壌改良材化し活用を計れる。又不需要期には
中水道水として広い範囲で活用できるものである。
[Means for Solving the Problems] In order to inoculate and biodegrade microorganisms in a chiller solution obtained by crushing high-concentration human dung and garbage, the optimum breeding conditions of the activity, reproduction and implantation of the microorganisms are satisfied. The present invention provides an apparatus using the following means and contents in a short time under effective conditions by creating an environment. First, a magnetic field is set up using a magnet, and the liquid (material) passing through the magnetic field contains a large amount of components of the mineral element due to the passage of the magnetic field by generating negative ions of the phenomenon caused by lightning and the sterilization by high magnetic permeability. The undegraded protein is liquefied into a thriller and undegraded protein is efficiently biodegraded on the filter medium attached to the magnetic field net by a negative ion effect due to electromagnetic waves generated from a magnetic field on the lower surface. The chiller liquid dropped into the tank is used to remove the respiratory gas of microorganisms and fine gaseous undecomposed gas generated as fine bubbles in the liquid due to the intermittent explosion due to the intermittent explosion. It diffuses into the atmosphere and melts fresh oxygen into the liquid to measure the activity, implantation and growth of anaerobic bacteria. By using such means, human waste and garbage can be effectively used as a soil-improving material for soil. It can also be used in a wide range as tap water during periods of low demand.

【0005】[0005]

【作用】摺潰装置を用い糞尿、有機性生ゴミをスリラー
液化し、粒子の表面積を小さくして液の濃度調整する事
に依り、酵素、微生物の生物処理の立ち上がりが速やか
にされ、酵素、微生物接種に依り素早い脱臭効果が得ら
れる。液中に設置する摺潰ポンプの放熱が液中に吸収さ
れ液を加温、又循環に依る回転抵抗で発する摩擦熱や酵
素、微生物の活性化で発する熱を各槽上部に敷布した磁
場マットが吸収し、好気性菌に予暖し、熱の大気への撹
散を防止する事で、液温を保持して酵素の分解、微生物
の活性、着床、増殖に有効に作用している。又槽外に側
に保温材を貼着して外装材(テント生地等)で包むこと
に依り、極寒冷地を除いて加温装置の作動の必要は無
い。
[Function] By using a crushing device to convert manure and organic garbage into a chiller liquid and reducing the surface area of the particles to adjust the concentration of the liquid, the start of biological treatment of enzymes and microorganisms is accelerated. A quick deodorizing effect can be obtained by inoculating microorganisms. Magnetic field mats spread over the top of each tank with heat generated by frictional heat generated by rotation resistance due to circulation and heat generated by the activation of enzymes and microorganisms. Absorbs, preheats to aerobic bacteria, and prevents heat from dispersing into the atmosphere, maintaining the liquid temperature and effectively acting on enzyme decomposition, microbial activity, implantation, and growth . In addition, there is no need to operate the heating device except in extremely cold regions by sticking a heat insulating material to the outside of the tank and wrapping it with an exterior material (such as tent cloth).

【0006】各槽に設けた槽内槽に高低を設けた磁石を
林設した磁場、醗酵槽に於いては磁場マットが発する遠
赤外線、放射線等に依るマイナスイオンに依り薬品処理
で生じる化学反(塩素と水質汚染物質)で生じる不純物
(トリハロメタン等)の発生をしない。
In a fermenter, a magnetic field generated by a magnetic field mat has a chemical reaction generated by chemical treatment due to negative ions due to far-infrared rays, radiation and the like in a fermenter. (Chlorine and water pollutants) do not generate impurities (trihalomethane, etc.).

【0007】磁場から遠赤外線、電磁波を投射する事で
水の結晶と不純物が分解、軟水化して酵素の***、微生
物の活性、着床、増殖が進み活発な生物分解に適した環
境を提供する事が出来る。
[0007] By projecting far-infrared rays and electromagnetic waves from a magnetic field, water crystals and impurities are decomposed and softened, and the enzyme is split, the activity of microorganisms, implantation and propagation are promoted to provide an environment suitable for active biodegradation. I can do things.

【0008】スリラー液を濾過材上に槽内槽の磁場を経
て放流する事で、未分解蛋白質と液状部分が分離され、
未分解蛋白質は濾過材上に滞留し、磁場マットから遠赤
外線効果と磁石による電磁波効果で、除菌、除濁の作用
を受け、特に好気性菌の活性及び増殖が計れる。
[0008] By releasing the chiller solution onto the filter medium through the magnetic field in the tank, the undegraded protein and the liquid portion are separated,
The undegraded protein stays on the filter medium, and is subjected to the action of sterilization and turbidity by the far-infrared ray effect and the electromagnetic wave effect of the magnet from the magnetic field mat, whereby the activity and proliferation of aerobic bacteria can be measured.

【0009】槽内に設けた磁場マットにも嫌気性菌が着
床、傾斜して布設してある為下部から間欠的に爆気する
新鮮な空気(酸素)の吸収、接触も良好で、隙間に滞留
していた嫌気性菌の呼吸ガス、未分解物質が不熟分解時
に発生する汚濁ガスを傾斜に副って浮上拡散させる等、
上述作用との相乗効果に依り速やかにスリラー液は分解
され、ミネラルを含んだコロイド液化(有菌土壌改良
液)する。又中水道水化も可能な循環水として活用でき
るものである。
Anaerobic bacteria are also implanted on the magnetic field mat provided in the tank and laid slopingly, so that it absorbs and contacts fresh air (oxygen) that explodes intermittently from the bottom and has good contact. Respiratory gas of anaerobic bacteria that had stayed in the air, and undegraded substances floated and diffused along the slope with pollutant gas generated during immature decomposition, etc.
The chiller solution is rapidly decomposed by the synergistic effect with the above-mentioned action, and liquefies as a colloid containing minerals (sterile soil improvement solution). It can also be used as circulating water that can be turned into tap water.

【0010】[0010]

【実施例】原水槽(1)〔図1,図2〕 投入する糞尿は槽内槽(2)へ投入。同時に酸素剤を混
入。同時に槽内槽(2)の多孔板に依り混入峡雑物と糞
尿は分離され、屎尿、糞尿はバキューム放水圧に依り原
水槽(1)内に流入される。投入と同時に蛋白性物質に
吸着させた酵素、微生物群を混入し、循環ポンプ(3)
に依り投入原水と摺潰、循環さす事に依り原水の租粒を
微粒化し、混入した酵素、微生物との混合を計り、配管
から放出時には空気との接触を計る事に依り酵素、微生
物の活性化を計る。液中に設けたポンプ(3)の放熱を
加温並びに液温の保温エネルギーとした液温保持に依り
酵素の***、微生物の活性が類を見ない速やかさで投入
した糞尿、屎尿の脱臭効果をもたらし、かつ曝気管
(4)に依る微粒気泡に依る強力な曝気に依り沈降、沈
殿している嫌気性物質の浮上液中に混入させ、摺潰ポン
プ(3)に依る糞尿、屎尿、活性汚泥の均一したスリラ
ー液化を計り(以下スリラー液と記載する)摺潰循環ポ
ンプ(3)のバルブの開閉切り替え操作に依り次槽図3
の調整槽(5)の磁場マット(8)を敷布した槽内槽に
放出されるものである。
[Example] Raw water tank (1) [Figs. 1 and 2] Manure to be charged is charged into the tank (2) in the tank. Oxygen is mixed at the same time. At the same time, mixed impurities and manure are separated by the perforated plate of the inner tank (2), and the excrement is excreted into the raw water tank (1) by the vacuum discharge pressure. Enzymes and microorganisms adsorbed on the proteinaceous substance are mixed at the same time as the introduction, and a circulation pump (3)
The raw water is crushed with the input raw water, and the raw water is crushed and circulated.The mixture of the raw water is atomized and mixed with the mixed enzymes and microorganisms, and the activity of the enzymes and microorganisms is measured by measuring the contact with the air when released from the pipe. Measure Deodorizing effect of excrement and excrement of the excrement and excrement which was injected at an unprecedented rate by the heat of the pump (3) provided in the liquid and the maintenance of the liquid temperature as the heat retaining energy of the liquid temperature. And sedimentation by vigorous aeration by fine air bubbles by the aeration tube (4) and mixing in the floating liquid of the anaerobic substance that has settled out, and excreta, manure and activity by the squashing pump (3) The uniform liquefaction of sludge in the sludge is measured (hereinafter referred to as the chiller solution).
Is released to the tank inside the adjusting tank (5) on which the magnetic field mat (8) is laid.

【0011】[0011]

【実施例 1】摺潰槽 磁石を用いた網と濾過材を貼着した磁場マット(8)
(以下磁場マットと記載)の上に放出されたスリラー液
は、磁場マット濾過材を以って、租粒子と微粒子並びに
液体部分に濾過分離される。濾過されたスリラー液は槽
内槽(6)に林設された磁石に依る磁場床を経て槽内に
流出する。当摺潰槽(5)に分別された有機性生ゴミを
投入する事で摺潰ポンプ(7)に依り微粒子液化され
る。その作動を摺潰槽(5)内で反復実施し槽内槽
(6)の磁場マットに放出する事に依り、濾過材上に滞
留する有機性未濾過蛋白物質は混合されている酵素、微
生物に含まれる好気性菌の活性に依り、一層微粒子化さ
れ、濾過され消滅しうるものである。その酵素、微生物
の***、活性化の要因は磁場マット磁床部分から発射さ
れている電磁波、遠赤外線、等に依るマイナスイオンの
効果である。濾過されたスリラー液は槽内槽(6)の磁
石を林設させた磁場床(9)に滴下し一層強い反応に依
りスリラー液中に含まれている水質に含有する不純分子
の分離が計られ水分子核団が、軟水化し活性化するスリ
ラー液となる。遠赤外線を投射する事と酵素の***、微
生物の速やかに活性化の条件として、好気性菌、嫌気性
菌の生存環境を整えて生存し良い環境をまず調整し、還
流水を用いて水質調整も速やかな処理と同時に酵素の分
裂、微生物の活性化、曝気配管から新鮮な空気(酸素)
を供給し接触さす事で一層良好な環境を整わしめ、スリ
ラー液送水ポンプ(10)に依りスリラー液槽(13)
に送水する。
[Example 1] Crushing tank Magnetic field mat (8) on which a net using magnets and a filter material were stuck.
The chiller liquid discharged on the magnetic field mat (hereinafter referred to as a magnetic field mat) is filtered and separated into coarse particles, fine particles, and a liquid portion by using a magnetic field mat filter material. The filtered thriller liquid flows out into the tank via a magnetic field bed formed by magnets installed in the tank (6) in the tank. By adding the separated organic garbage to the crushing tank (5), fine particles are liquefied by the crushing pump (7). The operation is repeatedly carried out in the crushing tank (5) and released to the magnetic field mat in the tank (6), so that the organic unfiltered protein substance remaining on the filter medium is mixed with the enzyme and microorganisms. It can be further micronized, filtered and extinguished, depending on the activity of the aerobic bacteria contained in the microorganism. The factor of the division and activation of the enzymes and microorganisms is the effect of negative ions due to electromagnetic waves, far-infrared rays, and the like emitted from the magnetic-field mat. The filtered chiller solution is dropped on a magnetic bed (9) in which a magnet is provided in a tank (6) in a tank (6), and the separation of impurity molecules contained in the water quality contained in the chiller solution by a stronger reaction is measured. As a result, the water molecular nucleus becomes a thriller liquid that is softened and activated. As conditions for projecting far-infrared rays, fission of enzymes, and rapid activation of microorganisms, the living environment of aerobic bacteria and anaerobic bacteria is prepared, and a good environment for survival is first adjusted, and water quality is adjusted using reflux water. Also rapid processing and enzyme splitting, microbial activation, fresh air (oxygen) from aeration piping
A more favorable environment is prepared by supplying and contacting the water, and the thriller liquid tank (13) is driven by the thriller liquid water supply pump (10).
Water.

【0012】[0012]

【実施例 2】ロータリスクリーン 送水ポンプ(10)から送られてきた摺潰、調整された
スリラー液はスリラー液槽(13)に受け入れる。円筒
のドラムに濾布を緊張し側面に配管の可能なドーナツ板
で構成し、外周下面をスリラー液面に沈殿し回転さす事
で、スリラー液槽の水圧に依る濾過抵抗で緊張してある
濾布のメッシュ内部に回収する事が出来る。ドーナツ板
側面の空洞(隙間)に配管しスリラー液揚水ポンプ(1
5)で次槽調整槽(18)内に設けた槽内槽(19)に
揚水、放水する。なお順次床面に滞積する峡雑物はスリ
ラー槽内峡雑物掻き揚げコンベア(16)を以って峡雑
物放出孔(17)から放出するものである。排出された
峡雑物は酵素、微生物の作用に依り糞、屎尿、生ゴミの
異臭は発しない。
Embodiment 2 The crushed and adjusted chiller solution sent from the rotary screen water pump (10) is received in the chiller solution tank (13). A filter that is tensioned with a filter resistance that depends on the water pressure of the thriller liquid tank by forming a filter cloth on a cylindrical drum and forming a donut plate that can be piped on the side, and setting the outer lower surface on the thriller liquid surface and rotating it. It can be collected inside the cloth mesh. Pilot the thriller liquid pump (1)
In 5), water is pumped and discharged into a tank (19) provided in the next tank adjusting tank (18). It should be noted that the gorge that accumulates sequentially on the floor surface is discharged from the gorge discharge hole (17) through the gorge conveyer (16) in the thriller tank. The discharged gorgeous substances do not emit off-flavors of feces, human waste and garbage due to the action of enzymes and microorganisms.

【0013】[0013]

【実施例 3】調整槽 スリラー液揚水ポンプ(15)で揚水されたスリラー液
は調整槽の槽内槽(19)に放出させて、林設された磁
石に依る磁場で摺潰槽(5)で述べた電磁波、遠赤外
線、放射能等の照射を受けながら、高低を設けた磁石の
間を小波を打つ形態でV字型流出孔〔図17〕から流出
邪魔板(21)に直流をさえぎられ下部方向に流れ、攪
拌装置(22)に依り攪拌されながら、底部に設けられ
た曝気配管(24)から噴出された空気(酸素)を充分
にスリラー液中に溶解させて調整槽(18)内溜め槽へ
流れ込み、流勢を止める事でスリラー液中の微粒子を沈
殿、沈降させて、同槽内で嫌気性菌に依って更に微粒化
される。なお酵素、微生物の活性化に適したスリラー液
化するため、後述の吸着槽からのスリラー液化した処理
水又は逆洗水を配管し希釈、調整水として給水濃度調整
するものである。
[Embodiment 3] Adjustment tank The thriller liquid pumped by the thriller liquid pump (15) is discharged into the tank (19) of the adjustment tank, and is crushed by a magnetic field generated by a forested magnet (5). While receiving electromagnetic waves, far-infrared rays, radioactivity, etc. as described in the above, the direct current is blocked from the V-shaped outflow hole [FIG. The air (oxygen) blown out from the aeration pipe (24) provided at the bottom is sufficiently dissolved in the chiller liquid while flowing downward and being stirred by the stirring device (22). By flowing into the internal storage tank and stopping the flow, the fine particles in the thriller liquid are settled and settled, and are further atomized by the anaerobic bacteria in the tank. In order to liquefy a chiller suitable for the activation of enzymes and microorganisms, treated water or backwashing water liquefied from a chiller from an adsorption tank described later is connected to a pipe to dilute and adjust the feedwater concentration as adjusted water.

【0014】[0014]

【実施例 4】醗酵槽 調整槽で醗酵に適する濃度に調整されたスリラー液は醗
酵槽(26)内の磁石を用いた磁場床を設けた槽内槽
(27)に流出し、電磁波、遠赤外線、放射能を受け、
設けられた磁石の高低差で波状起しV字型流出孔から磁
場マット(29)上に流出する。流出したスリラー液は
磁場マット上濾過材上で濾過分離され、滞積する有機性
蛋白質微粒は磁場ネットから照射される電磁波、遠赤外
線、放射能を受けて相乗的に好気性菌の活性化を計りそ
の生活反応として更に微粒化する。随時流出して来るス
リラー液と一緒に、順次濾過され槽内に滴下するもので
ある。敷布した磁場マット(29)を濾過滴下したスリ
ラー液は槽内に傾設した磁場マット(31)から発する
電磁波、遠赤外線、放射能に依り微粒子化されている未
分解蛋白粒子、素子等は、在来濾過材と考えていた濾過
材を吸着床となし、濾過材に吸着し、磁場ネットから照
射される前述三項の効果に基づくと同時に、曝気配管
(32)から噴出される細かい気泡が傾設された磁場マ
ットに副って上昇する事で、液中に滞留している嫌気性
菌の呼吸ガス並びに沈降している未分解有機質の分解時
の汚濁ガスを速やかに上部に拡散させ、傾斜して設けた
磁場マットの磁気ネット側に着床した一部好気性菌、マ
ット(濾過材)側に着床した嫌気性菌等の特性を生かし
て、傾斜して設けた磁気マットに於ける環境に依って、
一層着床、繁殖、***の生命活動の活性化が計られる。
順次溢出して来るスリラー液に依り邪魔板(30)を潜
通してV時型流出孔〔水戸〕を設けた溜り槽(33)に
ゆるやかに流れ込み、未分解粒子を沈降させて次槽、複
数に列設した列設した醗酵槽(26)と同一仕様の列設
した醗酵槽(34)に流出する。
Embodiment 4 Fermentation tank The chiller solution adjusted to a concentration suitable for fermentation in the adjustment tank flows out into the tank (27) provided with a magnetic field bed using magnets in the fermentation tank (26), and receives electromagnetic waves and distant water. Receiving infrared, radioactivity,
Waves are generated by the height difference of the provided magnets and flow out from the V-shaped outflow hole onto the magnetic field mat (29). The outflowing chiller solution is filtered and separated on a filter material on a magnetic field mat, and the accumulated organic protein particles are synergistically activated by aerobic bacteria by receiving electromagnetic waves, far infrared rays, and radioactivity irradiated from the magnetic field net. It is further atomized as its life response. This is sequentially filtered and dropped into the tank together with the chiller liquid flowing out as needed. The chiller liquid obtained by filtering and dropping the spread magnetic field mat (29) is used to convert undegraded protein particles, elements, and the like, which are micronized by electromagnetic waves, far infrared rays, and radioactivity emitted from the magnetic field mat (31) inclined in the tank, The filter material, which was conventionally considered to be a filter material, is formed as an adsorbent bed, adsorbed on the filter material, and based on the effect of the above-mentioned three items irradiated from the magnetic field net, and at the same time, fine bubbles ejected from the aeration pipe (32) By rising alongside the inclined magnetic field mat, the respiratory gas of anaerobic bacteria staying in the liquid and the pollutant gas at the time of decomposition of undecomposed organic matter that has settled are quickly diffused to the upper part, Taking advantage of the characteristics of partially aerobic bacteria imbedded on the magnetic net side of an inclined magnetic field mat and anaerobic bacteria imbedded on the mat (filter material) side, etc. Depending on the environment
Activation of vital activities of implantation, reproduction, and division is measured.
The spilled liquid gradually passes through the baffle plate (30) and slowly flows into the storage tank (33) provided with the V-hour type discharge port (Mito) to settle undecomposed particles and to settle in the next tank. It flows out to the fermenter tank (34) of the same specification as the fermenter tank (26) arranged in a row.

【0015】[0015]

【実施例 5】回収槽 回収槽(35)に流れ込んで来るスリラー液は、複数の
醗酵槽を経て酵素、微生物、物、電磁波、遠赤外線、放
射能等の相乗的効果と複数の濾過材(床)で濾過され
て、水分子核団がこまかくなったコロイド液化されてお
り(以下コロイド液と呼ぶ)複数に設けた醗酵槽(2
6)の最終槽の溜り槽(33)を経てコロイド液回収槽
(35)の、高低を設けて林設した磁石(37)に依る
磁場床を設けた槽内槽(36)に流入して来てV字型の
流出孔(水戸)から敷布された磁場マット(38)上に
溢出し貼着した磁気ネットの複合作用を受け、磁場マッ
トから滴下貯留し、下部に設けた曝気配管(39)から
微粒な気泡を供給して、各槽ごとに微妙に繁殖、衰退す
る微生物のコロイド液内で生存し得る微生物を当槽で培
養、繁殖をし、水質の安定化を計る。揚水ポンプ(4
0)とポンプによって次槽微粒子吸着槽(41)に送水
する。
Embodiment 5 Recovery tank The chiller liquid flowing into the recovery tank (35) passes through a plurality of fermentation tanks, and has a synergistic effect of enzymes, microorganisms, materials, electromagnetic waves, far infrared rays, radioactivity, etc., and a plurality of filtration materials ( Bed), and is liquefied into colloids in which water molecular nuclei are dispersed (hereinafter referred to as colloid solution).
After flowing into the colloid liquid recovery tank (35) through the reservoir tank (33) of the final tank of (6), the colloid liquid flows into the tank tank (36) provided with a magnetic field floor formed by the magnets (37) provided with elevations. Coming out of the V-shaped outflow hole (Mito), the magnetic net spilled out onto the magnetic field mat (38) laid out and subjected to the combined action of the magnetic net, and dropped and stored from the magnetic field mat, and the aeration pipe (39 ), Micro-bubbles are supplied, and microorganisms that can survive in the colloid liquid of microorganisms that subtly proliferate and decline in each tank are cultured and propagated in this tank to stabilize water quality. Pumping pump (4
0) and the pump sends water to the next fine particle adsorption tank (41).

【0016】[0016]

【実施例 6】吸着槽 吸着槽底面に逆洗浄給水管として複数の分岐管を吸着材
の逆洗浄給水配管を設けて、方円に噴出孔を設けた複数
の方円方位に噴出孔を設けた噴出管(44)を逆洗浄給
水配管に林設配管する。コークス堆積用多孔板(43)
に依る受板を布設し、回収槽からの送水ポンプ(40)
の配管の中間に回収バルブと送水バルブ(49)を設け
て分岐配管し、一方閉で片方開きでどちら方向にてもバ
ルブの開閉に依り必要な方向に送水を可能とした送水管
(46)は吸着槽(41)中央で受板(43)を貫通さ
せて放流を可能とするものである。多孔板(43)に依
る受板の上に林設されている方円に噴出孔を設けた噴出
管(44)の間に吸着材としてコークスを充填する。吸
着槽(41)本体の一面からバルブを設けた配管〔濾過
水配管〕(48)を取り出して、複数の分岐管(50)
を用いて、例えば調整槽(35)の希釈水として活用す
る等、任意の用途にコロイド液の配水を可能とする。同
じく吸着槽(41)の一方面と復数段に設けた逆洗浄排
水管を取り出し、濾過材(45)の隙間に吸着した極微
粒子を逆洗浄水の水位ごとに、槽内で混濁する事無く速
やかに放流するものである。
Embodiment 6 Adsorption tank A plurality of branch pipes are provided on the bottom surface of the adsorption tank as backwash water supply pipes, and a backwash water supply pipe of an adsorbent is provided. The eruption pipe (44) is connected to the backwash water supply pipe by forest. Perforated plate for coke deposition (43)
Laying a receiving plate according to the above, water pump from the recovery tank (40)
A water supply pipe (46) which is provided with a recovery valve and a water supply valve (49) in the middle of the pipe and is branched and opened in one direction and closed in one direction to enable water to flow in a required direction by opening and closing the valve in either direction. Is to allow the water to be discharged by penetrating the receiving plate (43) at the center of the adsorption tank (41). Coke is filled as an adsorbent between jet pipes (44) provided with jet holes in a square formed on a receiving plate formed by a perforated plate (43). A pipe provided with a valve [filtered water pipe] (48) is taken out from one surface of the main body of the adsorption tank (41) and a plurality of branch pipes (50) are taken out.
With this method, it is possible to distribute the colloid liquid for an arbitrary use, for example, to utilize it as dilution water for the adjustment tank (35). Similarly, take out the backwash drainage pipe provided on one side of the adsorption tank (41) and several stages, and opaque the ultrafine particles adsorbed in the gap between the filter media (45) in the tank for each water level of the backwash water. It is released immediately without any treatment.

【0017】[0017]

【実施例1】のV字型流出孔 側面板に差し渡した各槽の槽内槽の仕切り板並びに槽間
の仕切り板に鋸歯の様に、三角形の切り込みを施した事
をさす。
Example 1 V-shaped outflow hole This means that a triangular cut is made like a saw tooth on a partition plate of a tank in each tank and a partition plate between the tanks which are inserted into the side plates.

【0018】[0018]

【実施例1】の液の流出仕様 原水槽(1)からスリラー液槽(13)並びに吸着槽
(41)を除く摺潰槽(5)、調整槽(18)、醗酵槽
(26)、回収槽(35)の順に液は流出して行くが、
槽毎の槽内槽の流入側を浅く切り込み水位を高く保ち、
流出側は深く切り込み各槽の槽内槽並びに溜め槽に於い
て常に水位は水平に保たれ、原水槽(1)からの送水量
で溢れた水量が順次流出する方法であり、常に回収槽
(35)の水位をレベルスイッチで管理して、原水槽
(1)の摺潰循環ポンプ(3)と連動させる必要が有
る。及び回分式で目視による手動で操作運転も可能であ
る。
[Example 1] Outflow specification of liquid of raw water tank (1), crusher tank (5) except for thriller liquid tank (13) and adsorption tank (41), adjustment tank (18), fermentation tank (26), recovery The liquid flows out in the order of the tank (35),
Cut the inflow side of the tank in each tank shallowly to keep the water level high,
The outflow side is cut deeply so that the water level is always kept horizontal in the tank inside each tank and the storage tank, and the amount of water overflowing from the water supply from the raw water tank (1) flows out sequentially. It is necessary to manage the water level of 35) with a level switch and to link it with the crushing circulation pump (3) of the raw water tank (1). Also, a manual operation can be performed visually by a batch system.

【0019】[0019]

【発明の効果】本出願は前述の様に、磁石と濾過材を組
み合わせ、電磁波、遠赤外線、放射能、コークスに依る
吸着等で液中水分から不純物を取り除く事で、酵素、微
生物の生活環境を常に整える機構で、人糞、屎尿、活性
汚泥、有機性生ゴミを有菌土壌改良液化すると共に、当
機構の後設備に軽便な水処理装置を設けることで、容易
に中水道水化が可能である。又、焼却灰として廃棄処理
されている廃棄物を、微生物に依る当機構の処理に依
り、限りなく消滅せしめる事が可能である。
As described above, the present application combines a magnet and a filtering material to remove impurities from water in a liquid by means of adsorption using electromagnetic waves, far-infrared rays, radioactivity, coke, and the like, thereby improving the living environment of enzymes and microorganisms. A mechanism that constantly prepares liquefied human feces, human waste, activated sludge, and organic garbage in germ-free soil improvement. It is possible. In addition, waste that has been disposed of as incineration ash can be eliminated as much as possible by the treatment of our organization by microorganisms.

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

【図1】 原水槽の断面図Fig. 1 Cross section of raw water tank

【図2】 原水槽の上視図Fig. 2 Top view of raw water tank

【図3】 摺潰槽の断面図FIG. 3 is a sectional view of a crushing tank.

【図4】 摺潰槽の上視図Fig. 4 Top view of the crushing tank

【図5】 ロータリースクリーンの断面図FIG. 5 is a sectional view of a rotary screen.

【図6】 ロータリースクリーンの上視図FIG. 6 is a top view of a rotary screen.

【図7】 調整槽の断面図FIG. 7 is a sectional view of an adjustment tank.

【図8】 調整槽の上視図FIG. 8 is a top view of the adjustment tank.

【図9】 醗酵槽の断面図FIG. 9 is a sectional view of a fermenter.

【図10】 醗酵槽の上視図FIG. 10: Top view of the fermenter

【図11】 列設する複数の醗酵槽の断面図FIG. 11 is a sectional view of a plurality of fermenters arranged in a line.

【図12】 列設する複数の醗酵槽の上視図FIG. 12 is a top view of a plurality of fermenters arranged in a line.

【図13】 回収槽の断面図FIG. 13 is a sectional view of a recovery tank.

【図14】 回収槽の上視図FIG. 14 is a top view of a recovery tank.

【図15】 吸着槽の断面図FIG. 15 is a sectional view of an adsorption tank.

【図16】 吸着槽の上視図FIG. 16 is a top view of the adsorption tank.

【図17】 V字型流出孔(水戸)FIG. 17 V-shaped outflow hole (Mito)

【図18】 装置設置概念図FIG. 18 is a conceptual diagram of device installation.

【図19】 装置設置例FIG. 19: Example of device installation

【符号の説明】[Explanation of symbols]

1 原水槽本体 2 多孔板に依る槽内槽 3 摺潰、混合用循環ポンプ 4 曝気配管 5 摺潰槽本体 6 多孔板を用い磁場ネット並びに磁場を設け
た槽内槽 7 摺潰ポンプ 8 槽内槽に磁場ネットに濾過材を貼着し敷布
した磁場マット 9 槽内槽に高低を設けて林設した磁石 10 スリラー液送水ポンプ 11 摺潰槽内溜め槽 12 曝気配管 13 スリラー液槽 14 濾布をしたロータリースクリーン 15 スリラー濾過液揚水ポンプ 16 スリラー槽内夾雑物掻き揚げコンベアー 17 コンベアー峡雑物放出孔 18 調整槽本体 19 V字型流出水戸を設け磁場を設けた槽内
槽 20 槽内槽に高低を設けて林設した磁石 21 邪魔板 22 スリラー調整液攪拌装置 23 調整槽内溜め槽 24 曝気配管 25 希釈調整水送水配管 26 列設した醗酵槽1号槽 27 V字型流出水戸を設け磁場を設けた槽内
槽 28 槽内槽に高低を設けて林設した磁石 29 敷布した磁場マット 30 邪魔板 31 傾設した複数の磁場マット 32 曝気配管 33 V字型流出水戸を設け溜り槽 34 列説した醗酵槽2号(仕様は1号と共
通) 35 コロイド液回収槽 36 V字型流出水戸を設け磁場を設けた槽内
槽 37 槽内槽に高低を設けて林設した磁石 38 敷布した磁場マット 39 曝気配管 40 揚水配管とポンプ 41 微粒子吸着槽 42 逆洗水給水配管 43 多孔板受板 44 複数の逆洗噴出管 45 受板に堆積したコークス 46 回収槽から送水されてきたコロイド液排
水管末端 47 逆洗浄水排水配管 48 濾過水配水管 49 土壌改良液の回収、吸着槽への送水の分
岐配管 50 濾過水配水管から各再利用する方向への
給水分岐管
DESCRIPTION OF SYMBOLS 1 Raw water tank main body 2 Tank in tank by a perforated plate 3 Circulation pump for crushing and mixing 4 Aeration piping 5 Sliding tank main body 6 Tank in which a magnetic field net and magnetic field were provided using a perforated plate 7 Sliding pump 8 Inside of tank Magnetic field mat in which a filtering material is attached to a magnetic field net and laid in a tank 9 Magnets provided with a height in the tank inside the tank 10 Thriller liquid water pump 11 Reservoir tank in the crushing tank 12 Aeration piping 13 Thriller liquid tank 14 Filter cloth Rotary screen 15 Chiller filtrate pump 16 Contaminant scraper conveyor in chiller tank 17 Conveyor gorge discharge hole 18 Adjustment tank main body 19 Tank in which V-shaped outflow door is provided and magnetic field is provided 20 Tank in tank Magnets provided with elevations 21 Baffle plates 22 Thriller adjusting liquid agitator 23 Reservoir tanks in adjusting tanks 24 Aeration pipes 25 Dilution adjusting water feed pipes 26 Fermentation tank No. 1 tank in a row 27 V-shaped outflow door and a tank in which a magnetic field is provided 28 A magnet that is forested by setting the height of the tank in the tank 29 A spread magnetic field mat 30 A baffle plate 31 A plurality of inclined magnetic field mats 32 Aeration piping 33 V-shaped Fermentation tank No. 2 (specification is the same as No. 1). 35 Colloidal liquid recovery tank. 36 V-shaped outflow door and a tank in the tank provided with a magnetic field. 37 Height of the tank in the tank. Magnets installed and installed 38 Magnetic field mats laid 39 Aeration pipes 40 Pumping pipes and pumps 41 Particle adsorption tanks 42 Backwashing water supply pipes 43 Perforated plate receiving plates 44 Multiple backwashing jet tubes 45 Coke deposited on receiving plates 46 Recovery tank End of colloidal liquid drainage pipe sent from Japan 47 Backwash water drainage pipe 48 Filtration water distribution pipe 49 Collection of soil improvement liquid, branching water supply pipe to adsorption tank 50 From filtration water distribution pipe to each reuse direction Water branch pipe

─────────────────────────────────────────────────────
────────────────────────────────────────────────── ───

【手続補正書】[Procedure amendment]

【提出日】平成12年7月3日(2000.7.3)[Submission date] July 3, 2000 (2007.3)

【手続補正1】[Procedure amendment 1]

【補正対象書類名】明細書[Document name to be amended] Statement

【補正対象項目名】図面の簡単な説明[Correction target item name] Brief description of drawings

【補正方法】変更[Correction method] Change

【補正内容】[Correction contents]

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

【図18】FIG.

【図19】削除FIG. 19 is deleted

【図1】 原水槽の断面図Fig. 1 Cross section of raw water tank

【図2】 原水槽の上視図Fig. 2 Top view of raw water tank

【図3】 摺潰槽の断面図FIG. 3 is a sectional view of a crushing tank.

【図4】 摺潰槽の上視図Fig. 4 Top view of the crushing tank

【図5】 ロータリースクリーンの断面図FIG. 5 is a sectional view of a rotary screen.

【図6】 ロータリースクリーンの上視図FIG. 6 is a top view of a rotary screen.

【図7】 調整槽の断面図FIG. 7 is a sectional view of an adjustment tank.

【図8】 調整槽の上視図FIG. 8 is a top view of the adjustment tank.

【図9】 醗酵槽の断面図FIG. 9 is a sectional view of a fermenter.

【図10】 醗酵槽の上視図FIG. 10: Top view of the fermenter

【図11】 列設する複数の醗酵槽の断面図FIG. 11 is a sectional view of a plurality of fermenters arranged in a line.

【図12】 列設する複数の醗酵槽の上視図FIG. 12 is a top view of a plurality of fermenters arranged in a line.

【図13】 回収槽の断面図FIG. 13 is a sectional view of a recovery tank.

【図14】 回収槽の上視図FIG. 14 is a top view of a recovery tank.

【図15】 吸着槽の断面図FIG. 15 is a sectional view of an adsorption tank.

【図16】 吸着槽の上視図FIG. 16 is a top view of the adsorption tank.

【図17】 V字型流出孔(水戸)FIG. 17 V-shaped outflow hole (Mito)

【符号の説明】 1 原水槽本体 2 多孔板に依る槽内槽 3 摺潰、混合用循環ポンプ 4 曝気配管 5 摺潰槽本体 6 多孔板を用い磁場ネット並びに磁場を
設けた総槽内槽 7 摺潰ポンプ 8 槽内槽に磁場ネットに濾過材を貼着し
敷布した磁場マット 9 槽内槽に高低を設けて林設した磁石 10 スリラー液送水ポンプ 11 摺潰槽内溜め槽 12 曝気配管 13 スリラー液槽 14 濾布をしたロータリースクリーン 15 スリラー濾過液揚水ポンプ 16 スリラー槽内夾雑物掻き揚げコンベ
アー 17 コンベアー峡雑物放出孔 18 調整槽本体 19 V字型流出水戸を設け磁場を設けた
槽内槽 20 槽内槽に高低を設けて林設した磁石 21 邪魔板 22 スリラー調整液攪拌装置 23 調整槽内溜め槽 24 曝気配管 25 希釈調整水送水配管 26 列設した醗酵槽1号槽 27 V字型流出水戸を設け磁場を設けた
槽内槽 28 槽内槽に高低を設けて林設した磁石 29 敷布した磁場マット 30 邪魔板 31 傾設した複数の磁場マット 32 曝気配管 33 V字型流出水戸を設け溜り槽 34 列設した醗酵槽2号槽(仕様は1号
と共通) 35 コロイド液回収槽 36 V字型流出水戸を設け磁場を設けた
槽内槽 37 槽内槽に高低を設けて林設した磁石 38 敷布した磁場マット 39 曝気配管 40 揚水配管とポンプ 41 微粒子吸着槽 42 逆洗水給水配管 43 多孔板受板 44 複数の逆洗噴出管 45 受板に堆積したコークス 46 回収槽から送水されてきたコロイド
液配水管末端 47 逆洗浄水配水配管 48 濾過水配水管 49 土壌改良液の回収、吸着槽への送水
の分岐配管 50 濾過水配水管から各再利用する方向
への給水分岐管
[Description of Signs] 1 Raw water tank main body 2 Tank in tank based on perforated plate 3 Circulating pump for crushing and mixing 4 Aeration pipe 5 Sliding tank main body 6 Magnetic tank using perforated plate and total tank in magnetic field provided with magnetic field 7 Grinding pump 8 Magnetic field mat in which a magnetic material is attached to and laid on a magnetic field net in the tank inside the tank 9 Magnets provided in the tank inside the tank with a height difference 10 Thriller liquid water supply pump 11 Reservoir inside the grinding tank 12 Aeration pipe 13 Chiller liquid tank 14 Rotary screen with filter cloth 15 Thriller filtrate pump 16 Pumping contaminants in the thriller tank Conveyor 17 Conveyor gorge discharge holes 18 Adjustment tank main body 19 Inside tank with V-shaped outflow door provided with magnetic field Vessel 20 Magnets provided with heights in the vats in the vats 21 Baffle plates 22 Thriller adjusting liquid stirrer 23 Reservoir tanks in the adjusting tank 24 Aeration pipes 25 Dilution adjustment water supply pipes 26 rows Fermentation tank No. 1 tank 27 V-shaped outflow unit and a magnetic tank provided in a tank 28 A magnet provided with a height in the tank 29 forested magnetic field mats 30 Baffle plate 31 Baffled magnetic field mats 32 Aeration pipe 33 Reservoir tank provided with V-shaped outflow doors 34 Fermentation tank No. 2 tank arranged in rows (specifications are the same as in No. 1) 35 Colloidal liquid recovery tank 36 Tank inside V-shaped outflow door provided with magnetic field 37 Magnets provided in the tank with heights in the tank 38 Spread magnetic field mats 39 Aeration pipes 40 Pumping pipes and pumps 41 Particle adsorption tanks 42 Backwashing water supply pipes 43 Perforated plate receiving plates 44 Plural backwashing jet tubes 45 Receiving plates Coke deposited in the tank 46 Colloid liquid distribution pipe end sent from the recovery tank 47 Backwash water distribution pipe 48 Filtration water distribution pipe 49 Collection of soil improvement liquid, branch piping of water supply to the adsorption tank 50 Filtration water distribution pipe from each Use water supply branch pipe in the direction of

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C02F 11/02 B09B 3/00 C 11/04 ZABD ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) C02F 11/02 B09B 3/00 C 11/04 ZABD

Claims (3)

【特許請求の範囲】[Claims] 【請求項 1】ア)槽内の一部を仕切り、内部に永久磁
石を林設して液体が接触して通過する磁場を設けた槽内
槽。
1. A tank in which a part of the tank is partitioned, and permanent magnets are provided inside the tank to provide a magnetic field through which the liquid contacts and passes.
【請求項 2】イ)永久磁石網(ネット)と不腐食性の
有隙材を重貼した微生物着床マット
2. A microorganism-implanted mat on which a permanent magnet net and a non-corrosive porous material are overlaid.
【請求項 3】ウ)ア項を設けた槽内に爆気装置を設け
て、イ項を複数連体して設置する事の可能な醗酵装置。
3. A fermentation apparatus in which an explosive device is provided in a tank provided with item a), and a plurality of items a) can be installed in series.
JP2000105713A 2000-02-21 2000-02-21 Microbe fermenting treatment device using magnetic field floor and filter medium Pending JP2001246283A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000105713A JP2001246283A (en) 2000-02-21 2000-02-21 Microbe fermenting treatment device using magnetic field floor and filter medium

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000105713A JP2001246283A (en) 2000-02-21 2000-02-21 Microbe fermenting treatment device using magnetic field floor and filter medium

Publications (1)

Publication Number Publication Date
JP2001246283A true JP2001246283A (en) 2001-09-11

Family

ID=18619005

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2000105713A Pending JP2001246283A (en) 2000-02-21 2000-02-21 Microbe fermenting treatment device using magnetic field floor and filter medium

Country Status (1)

Country Link
JP (1) JP2001246283A (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106007157A (en) * 2016-06-30 2016-10-12 芜湖鸣人热能设备有限公司 Environmental protection equipment capable of purifying water
CN106269244A (en) * 2016-10-13 2017-01-04 无锡市金武助剂厂有限公司 A kind of highly purified abluent filter
CN110072625A (en) * 2016-12-20 2019-07-30 澳大利亚赛科劳玛格私人有限公司 A kind of planar magnetic separator
CN110585788A (en) * 2019-09-25 2019-12-20 安徽万磁电子有限公司 Filtration and recovery device and filtration and recovery method for magnetic material processing waste liquid
CN111748588A (en) * 2020-07-20 2020-10-09 北京工业大学 Method for increasing yield of Halofax mediterranei fermentation polyhydroxyalkanoate
CN111773819A (en) * 2020-06-22 2020-10-16 武汉惠农乐植物营养科技有限公司 Powder slurry device for preparing biological organic liquid fertilizer and preparation method thereof
WO2021256568A1 (en) * 2020-06-19 2021-12-23 グレンカル・テクノロジー株式会社 Molding material, molded article, and production method for molding material
CN114540186A (en) * 2022-02-28 2022-05-27 湖南淳芝宝药业有限责任公司 Temperature stable control chinese-medicinal material fermenting installation

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH04341312A (en) * 1991-05-17 1992-11-27 Toyobo Co Ltd Magnetic filter
JPH0663584A (en) * 1992-06-10 1994-03-08 D K Aqua:Kk Water purifying material and water purifying device for live fish water tank
JP3034388U (en) * 1996-07-06 1997-02-18 株式会社日本微生物 Water treatment device

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH04341312A (en) * 1991-05-17 1992-11-27 Toyobo Co Ltd Magnetic filter
JPH0663584A (en) * 1992-06-10 1994-03-08 D K Aqua:Kk Water purifying material and water purifying device for live fish water tank
JP3034388U (en) * 1996-07-06 1997-02-18 株式会社日本微生物 Water treatment device

Cited By (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106007157A (en) * 2016-06-30 2016-10-12 芜湖鸣人热能设备有限公司 Environmental protection equipment capable of purifying water
CN106269244A (en) * 2016-10-13 2017-01-04 无锡市金武助剂厂有限公司 A kind of highly purified abluent filter
CN110072625A (en) * 2016-12-20 2019-07-30 澳大利亚赛科劳玛格私人有限公司 A kind of planar magnetic separator
CN110585788B (en) * 2019-09-25 2021-07-06 安徽万磁电子有限公司 Filtration and recovery device and filtration and recovery method for magnetic material processing waste liquid
CN110585788A (en) * 2019-09-25 2019-12-20 安徽万磁电子有限公司 Filtration and recovery device and filtration and recovery method for magnetic material processing waste liquid
WO2021256568A1 (en) * 2020-06-19 2021-12-23 グレンカル・テクノロジー株式会社 Molding material, molded article, and production method for molding material
JP2022001344A (en) * 2020-06-19 2022-01-06 グレンカル・テクノロジー株式会社 Molding material, molded article, and manufacturing method of molding material
JP7098176B2 (en) 2020-06-19 2022-07-11 グレンカル・テクノロジー株式会社 Molding material, molded body, and manufacturing method of molding material
CN115667414A (en) * 2020-06-19 2023-01-31 愚连队技术株式会社 Molding material, molded body, and method for producing molding material
CN111773819A (en) * 2020-06-22 2020-10-16 武汉惠农乐植物营养科技有限公司 Powder slurry device for preparing biological organic liquid fertilizer and preparation method thereof
CN111748588A (en) * 2020-07-20 2020-10-09 北京工业大学 Method for increasing yield of Halofax mediterranei fermentation polyhydroxyalkanoate
CN111748588B (en) * 2020-07-20 2022-06-07 北京工业大学 Method for increasing yield of Halofax mediterranei fermentation polyhydroxyalkanoate
CN114540186A (en) * 2022-02-28 2022-05-27 湖南淳芝宝药业有限责任公司 Temperature stable control chinese-medicinal material fermenting installation
CN114540186B (en) * 2022-02-28 2023-09-08 湖南淳芝宝药业有限责任公司 Temperature stabilization control chinese-medicinal material fermenting installation

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