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JP5159585B2 - Organic wastewater treatment method and treatment equipment - Google Patents
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JP5159585B2 - Organic wastewater treatment method and treatment equipment - Google Patents

Organic wastewater treatment method and treatment equipment Download PDF

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JP5159585B2
JP5159585B2 JP2008308789A JP2008308789A JP5159585B2 JP 5159585 B2 JP5159585 B2 JP 5159585B2 JP 2008308789 A JP2008308789 A JP 2008308789A JP 2008308789 A JP2008308789 A JP 2008308789A JP 5159585 B2 JP5159585 B2 JP 5159585B2
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信亜 深山
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Sanwa Seisakusho Co Ltd
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    • 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
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Description

本発明は、米の研ぎ汁や豆腐工場の廃液などの有機汚水の処理方法および処理設備に関する。   The present invention relates to a method and equipment for treating organic sewage such as rice sharpening juice and waste liquid from a tofu factory.

学校や病院などの給食施設やレストラン等では、毎日大量の米の研ぎ汁などの有機汚水が発生する。また、豆腐工場でも大量の有機汚水が発生する。これらの有機汚水は、比較的濃度は薄いが汚水の発生量が大きく、大型の処理施設を必要とする。例えば豆腐の製造には大豆1俵に水5トンと言われ、中規模程度の製造業者でも毎日100トン程度の汚水を処理しなければならない。   A large amount of organic sewage such as rice sharpening juice is generated every day at school facilities and hospitals. A large amount of organic sewage is also generated at the tofu factory. These organic sewage has a relatively low concentration but a large amount of sewage is generated, requiring a large treatment facility. For example, for tofu production, it is said that 5 tons of water per 1 ton of soybean, and even a medium-sized manufacturer must treat about 100 tons of sewage every day.

通常、凝集剤などの薬品を使用して有機質を沈殿させ、上澄み液を排水しているのが一般的であるが、対象となる廃液の量が大きいため薬品の使用量も大きく、食品の製造コストに与える影響も少なくない。また、沈殿物は埋め立て用などに使用することもあるが、多くは焼却処理により減量するので、多大なエネルギーコストを必要とする。   Usually, organic substances are precipitated using chemicals such as flocculants and the supernatant liquid is drained, but the amount of chemicals used is large due to the large amount of waste liquid to be produced, and food production There are many impacts on costs. Moreover, although a deposit may be used for a landfill etc., since many are reduced by incineration processing, a huge energy cost is required.

フィルタによってSS(浮遊物質量)を除去する方法もあるが、網目のような機械的なフィルタでは粒子が細かいため濾過できず、布などのエレメントを使用すると液量が大きいために施設が膨大なものとなるという問題点がある。   There is a method of removing SS (floating matter amount) with a filter, but mechanical filters such as mesh cannot be filtered because the particles are fine, and the use of elements such as cloth makes the amount of liquids large, so the amount of facilities is enormous. There is a problem that it becomes a thing.

特許文献1に記載のフィルタは、金属等のコイルばね状の素材の表面に微小な突起を形成して間隙を構成し、素材の表面にケイソウ土などの濾過助剤を塗布し、間隙を通過する液中の微細な懸濁物を濾過するようにしたものであるが、コイルばねの間隙を所定寸法に保持することが困難な上、液流の振動等でばねが共振して性能を発揮できないなどの問題点がある。   The filter described in Patent Document 1 forms a minute projection on the surface of a coil spring-shaped material such as metal to form a gap, applies a filter aid such as diatomaceous earth to the surface of the material, and passes through the gap. It is designed to filter fine suspensions in the liquid that is flowing, but it is difficult to maintain the gap between the coil springs at a predetermined size, and the spring resonates due to vibration of the liquid flow, etc. There are problems such as being unable to do so.

一方、本出願人は、粉砕したざくろ石と無機バインダを混合して型枠内に充填し、焼成して発泡、成形させた断熱材を発明し、その内容は特許文献2により公開されている。この板状の断熱材は、発泡させたざくろ石を成形したものであるから、内部の空隙が大きく通気性にすぐれ、通水性も同様であることから、特許文献2の段落[0016]にはフィルタとして使用することも示唆されている。   On the other hand, the present inventor invented a heat insulating material in which a pulverized garnet and an inorganic binder are mixed and filled in a mold, fired, foamed and molded, and the contents thereof are disclosed in Patent Document 2. . Since this plate-like heat insulating material is formed from foamed garnet, since the internal voids are large and the air permeability is the same, the water permeability is the same. It has also been suggested to be used as a filter.

さらに本出願人は、有機質汚泥を必要に応じて水で希釈し、曝気処理を行った後、マートンチップを充填した濾過反応槽を通過させ、その排出液をさらに循環させることで有機質を二酸化炭素と水に完全分解して残渣を生じない有機質汚泥の処理方法ならびに処理設備を開発し、その内容は特許文献3に記載されているので、図6によりこれを簡単に説明する。   Furthermore, the present applicant dilutes the organic sludge with water as necessary, performs aeration treatment, passes through a filtration reaction tank filled with Merton chips, and further circulates the effluent to convert the organic matter into carbon dioxide. An organic sludge treatment method and treatment equipment that completely decomposes into water and does not produce a residue have been developed, and the contents thereof are described in Patent Document 3, which will be briefly described with reference to FIG.

図6は特許文献3に記載の有機質汚泥の処理施設を示す系統図で、符号91は調整槽、符号92〜94は曝気槽、符号95,97は移送ポンプ、符号96は濾過反応槽、符号961は濾過反応槽96の表面に液を撒水する撒水管、符号962は濾過反応槽96の底部からの流出液を集める流出樋である。   FIG. 6 is a system diagram showing an organic sludge treatment facility described in Patent Document 3. Reference numeral 91 is an adjustment tank, reference numerals 92 to 94 are aeration tanks, reference numerals 95 and 97 are transfer pumps, reference numeral 96 is a filtration reaction tank, reference numeral Reference numeral 961 denotes a submerged pipe for submerging the liquid on the surface of the filtration reaction tank 96, and reference numeral 962 denotes an outflow trough for collecting the effluent from the bottom of the filtration reaction tank 96.

有機質汚泥を必要に応じて水で希釈しながら調整槽91に投入し、ついで曝気槽92〜94に移送して曝気処理を行った後、その処理液をマートンチップを充填した濾過反応槽96の表面にスプレイして槽内を通過させ、その排出液を前記の調整槽91に戻し、このルートを繰り返し循環させると、有機質は二酸化炭素と水に完全分解されて、残渣を生じない。実績によれば、マートンチップに付着した微生物の働きにより循環する液の温度は30℃程度となり、24時間で汚泥の約60%が分解される。   The organic sludge is introduced into the adjustment tank 91 while being diluted with water as necessary, and then transferred to the aeration tanks 92 to 94 for aeration treatment, and then the treatment liquid is added to the filtration reaction tank 96 filled with Merton chips. When sprayed on the surface and passed through the tank, the discharged liquid is returned to the adjusting tank 91 and this route is repeatedly circulated, the organic matter is completely decomposed into carbon dioxide and water, and no residue is produced. According to actual results, the temperature of the circulating liquid is about 30 ° C. due to the action of microorganisms attached to the Merton chip, and about 60% of the sludge is decomposed in 24 hours.

なおマートンチップとは、特許文献3の段落[0008]に記載のとおり、杉材をたたき潰した「バター材」を0.5〜4.0mmの大きさに粉砕したもので、セルロース約65%、ヘミセルロースのペントサン約10%、リグニン約20%で構成される。マートンチップはここでは濾過のためのフィルタとして、また醗酵、分解、消化反応を行う微生物の担体として機能する。保水性、水切り、保温力に富み、脱臭力、醗酵力には特にすぐれ、有機質汚泥の消化のための接触材として最適である。   Merton chips are pulverized “butter material” obtained by crushing cedar wood into a size of 0.5 to 4.0 mm as described in paragraph [0008] of Patent Document 3, and about 65% cellulose. , About 10% hemicellulose pentosan and about 20% lignin. The Merton chip functions here as a filter for filtration and as a carrier for microorganisms that perform fermentation, decomposition and digestion reactions. It is rich in water retention, draining, and heat retention, especially excellent in deodorizing power and fermentation power, and is optimal as a contact material for digestion of organic sludge.

特許第3124901号公報Japanese Patent No. 3124901 特開2004−69060号公報JP 2004-69060 A 特許第4030496号公報Japanese Patent No. 4030496

本発明は、従来の技術における上記の諸問題点を解消し、第1に、薬剤を使用せず、フィルタに関する不安定要素もなく、有機質を含む大量の汚水を放水可能とすること、第2に濾過残液を完全分解して無害化すること、の2点を達成する有機汚水の処理方法および処理設備を提供することを目的とする。   The present invention solves the above-mentioned problems in the prior art, and firstly, it makes it possible to discharge a large amount of sewage containing organic matter without using chemicals and without unstable elements related to the filter. It is an object of the present invention to provide an organic wastewater treatment method and treatment equipment that achieves the following two points: complete decomposition of the filtered residual liquid and detoxification.

請求項1に記載の本発明は、有機汚水を受け入れる受水池内に、粉砕したざくろ石と無機バインダとを混合して型枠内に充填し、焼成して発泡、成型させたボード状の多孔質材、あるいは粉砕したざくろ石を焼成して発泡させたものと無機バインダとを型枠内に充填し加熱して圧縮、成形させたボード状の多孔質材よりなるフィルタを備える濾過ますを沈設し、この濾過ます内から吸引した排水を放流するとともに、前記受水池内の濾過残液を調整槽に投入し、ついで曝気槽に移送して曝気処理を行った後、その処理液をマートンチップを充填した濾過反応槽表面にスプレイして前記濾過反応槽内を通過させ、その排出液を前記調整槽に戻して繰り返し循環させることを特徴とする有機汚水の処理方法である。 The present invention according to claim 1, the water receiving Ikeuchi accept organic sewage, filled in the mold by mixing a powdered grinding the garnet and the inorganic binder, firing the foam, board-like obtained by molding comprising a porous material, or ground that garnet fired by foaming a an inorganic binder filling the mold frame heated compressed, full Note1 made of a porous material like were molded board After draining the drained water sucked from inside the filtration tank, the filtration residual liquid in the receiving pond is put into the adjustment tank, and then transferred to the aeration tank to perform the aeration treatment, and then the treatment by spraying a liquid to the filtration reactor surface filled with Merton tip is passed through the filtration reactor is the method for processing an organic sewage you characterized thereby repeatedly cycled back to the effluent in the adjusting tank .

請求項2に記載の本発明は、有機汚水を受け入れる受水池と、この受水池に沈設した側面、あるいは底面の少なくとも1面を粉砕したざくろ石と無機バインダとを混同して型枠内に充填し、焼成して発泡、成型させたボード状の多孔質材、あるいは粉砕したざくろ石を焼成して発泡させたものと無機バインダとを型枠内に充填し加熱して圧縮、成型させたボード状の多孔質材で構成した濾過ますと、この濾過ます内の液を吸い出して放流する吸引手段と、前記受水池内の濾過残液を汲み出す手段と、前記受水池内から前記手段によって汲み出された前記濾過残液を受け入れる調整槽と、曝気処理を行う複数の曝気槽と、前記複数の曝気槽からの排水液をスプレイする撒水管と、前記撒水管によってスプレイした前記排水液を受け入れるマートンチップを充填した濾過反応槽とを備え、前記調整槽以下前記濾過反応槽までを一巡する閉じた回路でこの順番に直列に接続しかつ前記濾過反応槽で処理した排出液を前記回路で繰り返し循環させるように構成された濾過残液処理手段によりなることを特徴とする有機汚水の処理設備である。 The present invention according to claim 2 mixes a receiving pond that receives organic sewage, a side surface set in the receiving pond, or a garnet crushed on at least one of the bottom surface and an inorganic binder into a formwork. A board-shaped porous material that has been fired, foamed and molded, or a baked and foamed garnet and an inorganic binder filled in a mold, heated, and compressed and molded And a suction means for sucking out and discharging the liquid contained in the filter, a means for pumping the filtrate remaining in the receiving pond, and the means from the receiving pond. An adjustment tank that receives the filtered residual liquid pumped out by a plurality of aeration tanks, a plurality of aeration tanks that perform aeration processing, a submerged pipe that sprays drainage liquid from the plurality of aeration tanks, and the drainage liquid sprayed by the submerged pipe Accept mart A filtration reaction tank filled with chips, and connected in series in this order in a closed circuit that goes round from the adjustment tank to the filtration reaction tank, and the effluent treated in the filtration reaction tank is repeatedly circulated in the circuit organic sewage treatment facility, characterized that you made by configured filtered residual liquid processing means so as to.

発明によれば、薬剤を使用せず、焼却処理も行わずに大量の有機汚水からSS、BOD、CODを安定して除去し、第1の課題である汚水の放流を可能とし、運転コストが大きく削減される。また、濾過残液の有機物を二酸化炭素と水蒸気に完全分解して無害化するという、いずれもすぐれた効果を奏する。 According to the present invention, SS, BOD, and COD can be stably removed from a large amount of organic sewage without using chemicals and without incineration, enabling the discharge of sewage, which is the first problem, and operating costs. Is greatly reduced. Also, as the organic matter of retentate liquid harmless completely decomposed into carbon dioxide and water vapor, it exhibits the both excellent effect.

以下本発明の望ましい実施例を図面により説明する。   Hereinafter, preferred embodiments of the present invention will be described with reference to the drawings.

図1は本発明の原理ともいうべき最も簡単な構成を示す説明図で、符号1は濾過ます、符号11はその底面を構成するフィルタ、符号2は有機汚水が排出されて来る排水管である。   FIG. 1 is an explanatory view showing the simplest configuration which should be called the principle of the present invention. Reference numeral 1 is a filter, reference numeral 11 is a filter constituting the bottom surface, and reference numeral 2 is a drain pipe from which organic sewage is discharged. .

フィルタ11として、前記特許文献2に記載した板状の断熱材を使用する。本発明においては断熱の目的は特にないから、以下「成形ボード」の名称を使用する。繰り返しになるが、これは粉砕したざくろ石と無機バインダとを混合して型枠内に充填し、焼成して発泡、成形させたボード状の多孔質材、あるいは粉砕したざくろ石を焼成して発泡させたものと無機バインダとを型枠内に充填し加熱して圧縮、成形させたボード状の多孔質材である。つまり、ざくろ石を粉砕して素材としてもよいし、粉砕したざくろ石を焼成して発泡させたものも農業用の水はけ材として「パーライト」の名称で市販されているから、これを使用してもよい。成形ボードのフィルタ性能(目の粗さ)は、20μm程度と推定される。   As the filter 11, the plate-shaped heat insulating material described in Patent Document 2 is used. In the present invention, since there is no particular purpose of heat insulation, the name “molded board” will be used hereinafter. Again, this is done by mixing pulverized garnet and an inorganic binder, filling the mold, firing and foaming, molding board-like porous material, or pulverizing garnet This is a board-like porous material in which a foamed product and an inorganic binder are filled in a mold, heated, compressed and molded. In other words, garnet may be crushed and used as a raw material, or baked and foamed crushed garnet is sold under the name of “Perlite” as an agricultural drainage material. Also good. The filter performance (mesh roughness) of the molded board is estimated to be about 20 μm.

このような装置で米の研ぎ汁を処理し、その処理前および処理後の水質を検査した結果を図2にまとめて示してある。なお、この検査は、CODについてはJIS K0102の17項、BODについてはJIS K0101の21項および32.3項により行い、SSについては昭和41年環境庁告示第59号付表8によって行った。この図2に示す結果から、フィルタ11によって、有機汚水のうちのSS、BOD、CODのすべてが下水道に放流できるレベルにまで除去されていることがわかる。なお、バクテリアなどが問題になる場合は、適宜除菌、あるいは殺菌を行った後に放流すればよい。   FIG. 2 shows the results of processing rice sharpening juice with such an apparatus and examining the water quality before and after the treatment. This inspection was conducted according to JIS K0102 item 17 for COD, JIS K0101 items 21 and 32.3 for BOD, and SS according to Annex 8 of the Environmental Agency Notification No. 59 of 1966. From the results shown in FIG. 2, it can be seen that the filter 11 has removed all SS, BOD, and COD of the organic sewage to a level that can be discharged into the sewer. In addition, when bacteria or the like becomes a problem, it may be discharged after appropriately sterilizing or sterilizing.

図3は、図1の装置を具体化したもので、符号12は金網、符号13は枠体、符号14は上板である。この実施例の濾過ます1は4つの側面と、底面とにフィルタ11として成形ボードを使用している。成形ボードは建材用として、例えば610mm×910mm、厚さ20mmのものが多く製造されるが、カッタナイフ等で容易に切断できるから任意の大きさにして使用すればよい。厚みも、枚数を重ねることによりさまざまに変更できる。成形ボードを大きい寸法のまま使用するとき、あるいは厚みが少ないときなど、水圧に対して強度が不足するおそれがあれば、この図3のように金網12を片面、あるいは両面に当てればよい。また耐久性の面で、ステンレス鋼等で枠体13を作り、これに成形ボードを嵌めるようにすることも望ましい。上板14には排水管2が直接取り付けられているが、後に示す例のように、排水管2に代えて吸い出し管3を取り付ける場合もある。   FIG. 3 embodies the apparatus shown in FIG. 1. Reference numeral 12 denotes a wire mesh, reference numeral 13 denotes a frame, and reference numeral 14 denotes an upper plate. The filter 1 of this embodiment uses a molded board as the filter 11 on the four side surfaces and the bottom surface. For example, many molded boards having a size of 610 mm × 910 mm and a thickness of 20 mm are manufactured for building materials. However, since they can be easily cut with a cutter knife or the like, they may be used in any size. The thickness can also be changed in various ways by overlapping the number. If there is a possibility that the strength is insufficient with respect to the water pressure, such as when the molded board is used in a large size or when the thickness is small, the wire mesh 12 may be applied to one side or both sides as shown in FIG. In terms of durability, it is also desirable to make the frame body 13 of stainless steel or the like and fit the molding board on it. Although the drain pipe 2 is directly attached to the upper plate 14, the suction pipe 3 may be attached in place of the drain pipe 2 as in the example shown later.

また、成形ボードを複数枚重ね合わせ、少なくとも1枚の合わせ面を削り、生じた空間内に活性炭、貝殻粉、川砂、前記のパーライトの粉末などの濾過助材を充填するようにすると、フィルタ性能を調整できるばかりでなく、フィルタに殺菌、吸着などの新たな機能を付与することができる。   In addition, when a plurality of molded boards are stacked, at least one mating surface is cut, and the resulting space is filled with filter aids such as activated carbon, shell powder, river sand, and the above pearlite powder, filter performance In addition, the filter can be provided with new functions such as sterilization and adsorption.

図4は実際の有機汚水処理設備における有機汚水の受け入れ部分を示す構成断面図で、符号はこれまでに示したものの他、符号15は濾過ます1を支持する架台、符号3は吸い出し管、符号31は吸い出しポンプ、符号4は有機汚水を受け入れる受水池である。受水池4内には必要に応じて攪拌手段を設けてもよい。   Fig. 4 is a structural cross-sectional view showing an organic sewage receiving portion in an actual organic sewage treatment facility. In addition to what has been shown so far, reference numeral 15 is a frame for supporting filtration 1, reference numeral 3 is a suction pipe, reference numeral Reference numeral 31 denotes a suction pump, and reference numeral 4 denotes a receiving pond for receiving organic sewage. A stirring means may be provided in the receiving reservoir 4 as necessary.

有機汚水は、排水管2から一旦受水池4に受け入れる。有機汚水の発生量を1日100トンとすれば、受水池の容量は300トン程度が必要である。図3に示した濾過ます1を液中に沈め、フィルタ11を通過して内部に流れ込む液を吸い出し管3で吸い出す。つまり図1に示したのとは逆に、濾過ます1の外側から液を濾過して内部に集め、真空ポンプなどの吸い出しポンプ31で濾過ます1内を負圧にしてこれを吸い出すのである。ここまでが放流可能な濾過液を吸引する吸引手段である。   The organic sewage is once received from the drain pipe 2 into the receiving basin 4. If the amount of organic sewage generated is 100 tons per day, the capacity of the receiving pond should be about 300 tons. The filter 1 shown in FIG. 3 is submerged in the liquid, and the liquid flowing through the filter 11 into the inside is sucked out by the suction pipe 3. That is, contrary to that shown in FIG. 1, the liquid is filtered from the outside of the filter 1 and collected inside, and filtered by the suction pump 31 such as a vacuum pump. This is the suction means for sucking the filtrate that can be discharged.

この構成の場合、濾過ます1の全体、特に上板14と吸い出し管3とは気密構造で接続されていなければならない。時間経過によりフィルタ11が目詰まりするから、適当なタイミングで加圧用の配管(図示せず)を接続して濾過ます1の内部を正圧にし、フィルタ11を逆洗する。吸い出し管3から吸い出された濾過液は有害物質が除去されているから、そのまま下水道等へ放流できる。 In this configuration, the entire filter 1, particularly the upper plate 14 and the suction pipe 3 must be connected in an airtight structure. Since the filter 11 is clogged with the passage of time, a pressurizing pipe (not shown) is connected and filtered at an appropriate timing so that the inside of the filter 1 is brought to a positive pressure and the filter 11 is backwashed. Since the filtrate sucked out from the suction pipe 3 has removed harmful substances, it can be discharged into the sewer as it is.

このまま運転を続けていれば受水池4内の液は段々濃縮されてくるから、適宜これを処理しなければならない。図5はその受水池4内の液の処理を含めた有機汚水全体の処理設備を示す構成図で、符号はこれまでの図で示したものの他、符号5は受水池4内の液を汲み出す汲み出し管、符号51は汲み出しポンプである。なお汲み出しポンプ51は常時運転しなくてもよいし、場合によってはポンプを使用せず、バケツ等で人力で汲み出してもよい。   If the operation is continued as it is, the liquid in the receiving basin 4 is gradually concentrated, and this must be appropriately treated. FIG. 5 is a block diagram showing the treatment facility for the whole organic wastewater including the treatment of the liquid in the receiving basin 4, and the reference numeral 5 is the one shown in the previous drawings, and the reference numeral 5 is the pump for the liquid in the receiving pond 4. A pumping pipe 51 is a pumping pump. The pump 51 need not always be operated, and in some cases, the pump may not be used and may be pumped manually with a bucket or the like.

汲み出した濃縮された廃液は、先に図6で示した調整槽91に投入するが、特許文献3で示した有機汚泥の場合と異なり、投入に際して水で希釈する必要はほとんどない。以後の処理工程は特許文献3に記載の場合と全く同様であり、本発明においては汲み出し管5以降の処理設備全体が濾過残液処理手段であるが、以上の構成により、濾過ますの濾過液と濾過残液の双方が無害化され、有機汚水全体が低コストで安定して処理されたことになる。   The concentrated waste liquid pumped out is put into the adjustment tank 91 previously shown in FIG. 6, but unlike the case of organic sludge shown in Patent Document 3, there is almost no need to dilute with water at the time of charging. The subsequent processing steps are exactly the same as those described in Patent Document 3, and in the present invention, the entire processing equipment after the pumping pipe 5 is the filtration residual liquid processing means. Both the filtration residue and the filtration residual liquid are rendered harmless, and the entire organic wastewater is stably treated at low cost.

フィルタとして、長方形のボードのみを例示したが、前記のとおりこの成形ボードはカッタナイフ等で自由に切断できるので、設計によって円、その他任意の形状に切断して使用できる。
また、側面に対して、ボードを縦向きに使用してもよいし、短冊状に切断したボードを縦方向に積み重ねてもよい。
As a filter, only a rectangular board has been illustrated, but as described above, this molded board can be freely cut with a cutter knife or the like, so that it can be cut into a circle or any other shape depending on the design.
Further, the boards may be used vertically with respect to the side surfaces, or the boards cut into strips may be stacked vertically.

本発明の最も簡単な実施例を示す説明図である。It is explanatory drawing which shows the simplest Example of this invention. 本発明による浄化効果を確認するために行った試験結果をまとめて示す図表である。It is a table | surface which shows collectively the test result performed in order to confirm the purification effect by this invention. 本発明の実施例のひとつを示す説明図である。It is explanatory drawing which shows one of the Examples of this invention. 本発明の実施例の有機汚水受け入れ部分を示す構成断面図である。It is a composition sectional view showing the organic sewage acceptance part of the example of the present invention. 本発明の実施例の有機汚水全体の処理設備を示す構成図である。It is a block diagram which shows the processing equipment of the whole organic waste water of the Example of this invention. 特許文献3に記載の有機質汚泥の処理施設を示す系統図である。It is a systematic diagram showing the treatment facility for organic sludge described in Patent Document 3.

符号の説明Explanation of symbols

1…濾過ます、 2…排水管、 3…吸い出し管、 4…受水池、 5…汲み出し管、 11…フィルタ、12…金網、 13…枠体、 14…上板、 15…架台、 31…吸い出しポンプ、 51…汲み出しポンプ、 91…調整槽、 92,93,94…曝気槽、 95,97…移送ポンプ、 96…濾過反応槽、 961…撒水管、 962…流出樋。   DESCRIPTION OF SYMBOLS 1 ... Filtration, 2 ... Drain pipe, 3 ... Drain pipe, 4 ... Receiving pond, 5 ... Drain pipe, 11 ... Filter, 12 ... Wire mesh, 13 ... Frame body, 14 ... Upper plate, 15 ... Base, 31 ... Dump Pump, 51 ... Pumping pump, 91 ... Adjusting tank, 92, 93, 94 ... Aeration tank, 95, 97 ... Transfer pump, 96 ... Filtration reaction tank, 961 ... Submerged pipe, 962 ... Outflow tank.

Claims (2)

有機汚水を受け入れる受水池内に、粉砕したざくろ石と無機バインダとを混合して型枠内に充填し、焼成して発泡、成型させたボード状の多孔質材、あるいは粉砕したざくろ石を焼成して発泡させたものと無機バインダとを型枠内に充填し加熱して圧縮、成形させたボード状の多孔質材よりなるフィルタを備える濾過ますを沈設し、この濾過ます内から吸引した排水を放流するとともに、前記受水池内の濾過残液を調整槽に投入し、ついで曝気槽に移送して曝気処理を行った後、その処理液をマートンチップを充填した濾過反応槽表面にスプレイして前記濾過反応槽内を通過させ、その排出液を前記調整槽に戻して繰り返し循環させることを特徴とする有機汚水の処理方法。 A water receiving Ikeuchi accept organic sewage, filled in the mold by mixing the garnet and inorganic binder were pulverizng, foamed and sintered, shaped was molded board porous material, or ground garnet an and firing the inorganic binder that is foamed and filled heating the mold frame compression, filtering masses which include the full Note1 made of a porous material like board was formed was sinking, in the filtration masu The waste water sucked from the tank is discharged, and the filtration residual liquid in the receiving pond is put into the adjustment tank, and then transferred to the aeration tank for aeration treatment, and then the treatment liquid is filled with the Merton chip. and spray is passed through the filtration reactor in the surface treatment method of organic wastewater you characterized thereby repeatedly cycled back to the effluent in the adjustment tank. 有機汚水を受け入れる受水池と、この受水池に沈設した側面、あるいは底面の少なくとも1面を粉砕したざくろ石と無機バインダとを混同して型枠内に充填し、焼成して発泡、成型させたボード状の多孔質材、あるいは粉砕したざくろ石を焼成して発泡させたものと無機バインダとを型枠内に充填し加熱して圧縮、成型させたボード状の多孔質材で構成した濾過ますと、この濾過ます内の液を吸い出して放流する吸引手段と、前記受水池内の濾過残液を汲み出す手段と、前記受水池内から前記手段によって汲み出された前記濾過残液を受け入れる調整槽と、曝気処理を行う複数の曝気槽と、前記複数の曝気槽からの排水液をスプレイする撒水管と、前記撒水管によってスプレイした前記排水液を受け入れるマートンチップを充填した濾過反応槽とを備え、前記調整槽以下前記濾過反応槽までを一巡する閉じた回路でこの順番に直列に接続しかつ前記濾過反応槽で処理した排出液を前記回路で繰り返し循環させるように構成された濾過残液処理手段によりなることを特徴とする有機汚水の処理設備。 A receiving pond that receives organic sewage, a side surface set in the receiving pond, or a garnet that has been crushed on at least one side of the bottom and an inorganic binder are mixed together and filled into a mold, fired, foamed, and molded. board-shaped porous material, or ground garnet was filled with calcined to the one obtained by foaming an inorganic binder in a mold frame heated compressed, and a porous material of board-like obtained by molding When filtered, the suction means for sucking out and discharging the liquid in the filtered mass, the means for pumping the filtered residual liquid in the receiving pond, and the filtered residual liquid pumped by the means from the receiving pond Filtration reaction filled with an adjustment tank for receiving, a plurality of aeration tanks for performing aeration treatment, a submerged pipe for spraying drainage liquid from the plurality of aeration tanks, and a Merton chip for receiving the drainage liquid sprayed by the submerged pipe A filtration circuit configured to repeatedly circulate the waste liquid treated in the filtration reaction tank and connected in series in this order in a closed circuit that goes around the adjustment tank and the filtration reaction tank. organic sewage treatment facilities it characterized by comprising the residual liquid treatment unit.
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