JPS58501161A - anaerobic fermentation - Google Patents

anaerobic fermentation

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Publication number
JPS58501161A
JPS58501161A JP57502187A JP50218782A JPS58501161A JP S58501161 A JPS58501161 A JP S58501161A JP 57502187 A JP57502187 A JP 57502187A JP 50218782 A JP50218782 A JP 50218782A JP S58501161 A JPS58501161 A JP S58501161A
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waste liquid
fermentation
flow
filling
organic waste
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マクケオウン・ケビン・ジヨゼフ
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/10Packings; Fillings; Grids
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/28Anaerobic digestion processes
    • C02F3/2806Anaerobic processes using solid supports for microorganisms
    • 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
    • Y02W10/10Biological treatment of water, waste water, or sewage

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  • Life Sciences & Earth Sciences (AREA)
  • Microbiology (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Apparatus Associated With Microorganisms And Enzymes (AREA)
  • Treatment Of Sludge (AREA)

Abstract

(57)【要約】本公報は電子出願前の出願データであるため要約のデータは記録されません。 (57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.

Description

【発明の詳細な説明】 嫌気性発酵 この発明は有機液体の嫌気性発酵法の改善及びそれに使用する発酵装置の改善に 関する。[Detailed description of the invention] anaerobic fermentation This invention is aimed at improving the anaerobic fermentation method for organic liquids and the fermentation equipment used therein. related.

有機廃液を精製する〔例えば有機廃液の生化学的酸素要求量(B、O,DJを減 らす〕ために有機廃液を嫌気性発酵(消化)することは周知である。このような 嫌気性発酵によシガス、特にメタンが生成する。既知の消化法では廃液の滞留期 間は一般に長く、例えばio〜10日間程度である。発酵廃液を環境温度以上の 温度に保つことが屡々必要であるから従来の嫌気性発酵は熱エネルギーを加える ことが必要であり、従って発酵操作からの全体のエネルギー効率は低い。Purify the organic waste liquid [e.g. reduce the biochemical oxygen demand (B, O, DJ) of the organic waste liquid. It is well known that organic waste liquids are subjected to anaerobic fermentation (digestion) in order to reduce waste water. like this Anaerobic fermentation produces gases, especially methane. In known digestion methods, the waste liquid retention period The period is generally long, for example about io to 10 days. The fermentation waste liquid is heated to a temperature higher than the environmental temperature. Traditional anaerobic fermentation adds heat energy because it is often necessary to maintain the temperature The overall energy efficiency from the fermentation operation is therefore low.

この発明の目的は有機廃液の嫌気性発酵を何日とは言わずに何時間といった程度 の比較的短い平均滞留期間で連続式に行う有機廃液の嫌気性発酵法を提供するに ある。The purpose of this invention is to carry out anaerobic fermentation of organic waste liquid in a matter of hours, not days. To provide an anaerobic fermentation method for organic waste liquid that can be carried out continuously with a relatively short average residence period of be.

この発明によれば、有機廃液は充填発酵容器、すなわち充填要素を配列し九発酵 容器中で嫌気性条件下に発酵され、一方、有機廃液は充填要素の配列を通して( 1) 有機廃液の流れの方向に垂直な平面を通る単位面積当りの流速が実質上均 一である: (―)有機廃液は充填要素配列表面上を円滑に流れて流速の急激な変化が比較的 少い; 条件下で通されるう 有機廃液は一般に充填要素配列を上方に向けて昇流させることが好ましい。従っ て以下の記載においてはこの操作態様についてのみ述べる。もつとも、他の操作 態様、例えば有機廃液を充填要素配列を下方に向けて降流させる態様が適してい る場合にはそれについても記載する。According to this invention, the organic waste liquid is stored in a packed fermentation vessel, that is, by arranging the packing elements and carrying out nine fermentations. The organic effluent is fermented under anaerobic conditions in the vessel, while the organic effluent is passed through an array of packing elements ( 1) The flow rate per unit area passing through a plane perpendicular to the direction of flow of organic waste liquid is substantially uniform. is one: (-) The organic waste fluid flows smoothly on the surface of the packing element array, and rapid changes in flow velocity are relatively less likely to occur. Few; be allowed under certain conditions It is generally preferred that the organic waste liquid flow upwardly through the packing element arrangement. follow In the following description, only this mode of operation will be described. However, other operations For example, an embodiment in which the organic waste liquid flows down the packing element arrangement is suitable. If applicable, this should also be stated.

下記の説明において、この発明で使用する発酵装置の策略縦断面図である図につ いて述べる。In the following description, reference will be made to the figure, which is a schematic vertical cross-sectional view of the fermentation apparatus used in this invention. I will explain it.

図に示す発酵装置は封止され喪発酵容器11発酵容器lの上端部に備えられた弁 3付きガス排出−導入導管コ、発酵容器lの下端部に設けられた弁S付きスラッ ジ排出導管fを備える。容器l内には一般に6で示す充填要素配列が取付けられ 、穿孔支持部材7上に配設される。廃液導入管tは弁デを備え、この廃液導入管 tは支持部材りの下方において容器l内に取付けられた多数の穿孔管または樋1 0からなる液体分配装置に連結する。管tと支持部材7との間に拡散装置すなわ ち流れ矯正装置//が配設される。内側周縁せきlコが充填要素配列6の上に置 かれ、処理ずみ液排出管/41と接続し、この処理ずみ液排出管/41は液封上 13と接続することによってガスを容器l内に保持する(或はまた、容器l内に ガスを保持するために例えば封泥方式tl!用できる)。The fermentation apparatus shown in the figure is sealed and has a valve provided at the upper end of the fermentation vessel 11. Gas discharge-intake conduit with 3, slot with valve S provided at the lower end of the fermentation vessel and a discharge conduit f. A filling element array generally designated 6 is installed within the container l. , are arranged on the perforation support member 7. The waste liquid introduction pipe t is equipped with a valve de, and this waste liquid introduction pipe t is a number of perforated pipes or troughs 1 installed in the container l below the support member. Connected to a liquid dispensing device consisting of 0. Between the tube t and the support member 7 there is a diffusion device or A flow correction device// is provided. The inner peripheral weir is placed on top of the filling element array 6. This is connected to the treated liquid discharge pipe/41, and this treated liquid discharge pipe/41 is connected to the liquid seal top. 13 to keep the gas in the vessel l (or alternatively, to keep the gas in the vessel l For example, a sludge system is used to retain the gas! ).

上記第1の期準、すなわち有機廃液の流れの方向に垂直な平面を通る有機廃液の 流速が実質上一定であるという基準を満足するためには、すなわち該有機廃液が 発酵器内を押出し流れに近似の流れとして流れるためKは有機廃液を充填要素配 列の下面を通って実質上均一に充填要素配列中に導入することが必要である。The first criterion mentioned above, i.e., the flow of organic waste through a plane perpendicular to the direction of flow of organic waste. In order to satisfy the criterion that the flow rate is substantially constant, i.e. the organic waste liquid must be K flows through the fermenter as a flow similar to the extrusion flow, so the organic waste liquid is arranged in a filling element. It is necessary to introduce the packing elements into the array substantially uniformly through the lower surface of the row.

これを達成するためには、図に示す実施態様では有機廃液を組をなす複数穿孔管 により発酵容器中に導入し、更に均一性を高めるためには流れ矯正装置//すな わち拡散装置llが廃液導入管tと充填要素配列6との間に配設される。この拡 散装置は例えば穿孔板、格子またはガラス繊維からなる絹織物のような絹織物の 形態を取る。こうして、上記説明から理解されるようK、穿孔支持体7を通る有 機廃液の流速は実質上均一となる。To achieve this, the embodiment shown in the figure requires a set of multi-perforated tubes for directing the organic effluent. to the fermentation vessel, and to further improve the uniformity, a flow straightener// That is, the diffusion device 11 is arranged between the waste liquid inlet pipe t and the filling element array 6. This expansion The scattering device can be used for example on silk fabrics such as perforated plates, grids or silk fabrics made of glass fibres. take form. Thus, as can be seen from the above description, K, the hole passing through the perforated support 7. The flow rate of the machine waste liquid becomes substantially uniform.

充填要素配列6は充填要素配列の表面と接触する有機廃液の急激な変化を減少さ せるようにすべきである。The packing element array 6 reduces rapid changes in the organic waste liquid that comes into contact with the surface of the packing element array. should be made possible.

これは充填要素配列を、配列の頂部から底部へ延びる垂直な管の多数の配列とし て形成することによって理論的に最も良く達成され、このような管の配列はこの 発明によシ使用できる。、しかし、このような管の配列はそれ自体は流れを矯正 する性質はもっていないから、ひとたび有機廃液の押出し流れがある特定の管に 入るとそれは導管の頂部から出るまでその管の中に含まれるから、有機廃液が最 初に非常によく分配されることが必要であることに留意されたい。同様な効果は 垂直なシートの配列によっても達成されるが、しかしこれもある程度同じ欠点を もつ。。This makes the packing element array a number of arrays of vertical tubes running from the top of the array to the bottom. Theoretically, this arrangement of tubes is best achieved by forming Can be used for invention. , but such a tube arrangement itself does not straighten the flow. Because it does not have the property of Once in, it is contained within the conduit until it exits at the top of the conduit, so that the organic waste is Note that it is necessary to be very well distributed at the beginning. A similar effect is This can also be achieved by a vertical sheet arrangement, but this also suffers from some of the same drawbacks. Motsu. .

組をなす管に近似した充填要素の配列を与える他の仕方はラツシツピリング、レ ーシングリングまたは交さ画壁リングのような充填要、素を積重ねた配列である 。Other ways of providing an arrangement of packing elements that approximate a set of tubes are by means of rasppilling, – An array of stacked filling elements, such as single rings or intersecting wall rings. .

このようなリング<fil)を相互にくい違った列に充填するとある程度流れを 矯正できるが、このような環(リング)を大型の発酵容器に積重ねて充填するこ とは非常に時間がかかることに注意すべきである。If such rings <fil) are packed in different rows that are not close to each other, the flow will be improved to some extent. Although it can be straightened, it is difficult to stack such rings in a large fermentation container. It should be noted that this is very time consuming.

いわゆる「投込み」充填配列は充填要素を単に反応容器中に投込むだけによって 反応容器に充填要素を入れればよく、従って容器を投込んだ充填要素で充填する のは極めて簡単、であるという利点がある。しかし、この場合充填要素の入れ方 によって投込まれた充填要素は幾分無秩序配列に1なる傾向がある。一般的に言 って、このような無秩序配列は多くの場合に充填要素配列を流通する液体が充填 要素の表面を流れ渡る時に流速がたびたび急激に変化する。このことは従来使用 されてきたラツシツピリングまたは密実円筒体で形成された投込み充填要素配列 の場合に特にあてはまることである。事情は前記場合より若干よくなるが、同じ ことがボール(poll)型充填要素の場合及び鞍型充填要素の場合にも同じこ とが起る。従来のラツシツピリング及びボールリング祉約lの縦横比(長さ:直 径比)金もつからそれらの充填要素を投込むと充填g累は無秩序に或は縦に配向 する。他方、1未満(例えば0.66、好適にはO,S−O,コS)の縦横比を もつ光*要素はそれらの充填要素が水平になる、すなわち単純なリングの場合、 リングの壁は水平になるのでなく垂直になる傾向をもつ充填要素配列を形成する 。このような充填要素はこの発明により使用するのに特に適し、容器中に入れる のが比較的容易で、流れを矯正でき、同時に充填要素の表面上を流れる液体の流 速が過度にたび九び変化するといったことがないという利点をもつことが判明し 友。The so-called "throw" packing arrangement consists of simply dumping the packing elements into the reaction vessel. It is only necessary to put a filling element into the reaction vessel, so the container is filled with the thrown filling element. It has the advantage of being extremely simple. However, in this case how to put the filling element Filler elements populated by 1 tend to be somewhat chaotic arrays of 1's. generally speaking Therefore, such a disordered array is often filled with liquid flowing through the packed element array. The velocity of the flow often changes rapidly as it flows across the surface of the element. This is traditionally used Throw-filling element arrays formed from solid pillars or solid cylinders This is especially true in the case of The situation is slightly better than in the previous case, but the same The same holds true for poll-type and saddle-type filling elements. happens. Aspect ratio (length: straight) of conventional straight pilling and ball ring Diameter ratio) When the filling elements are inserted into the metal, the filling elements are oriented randomly or vertically. do. On the other hand, an aspect ratio of less than 1 (e.g. 0.66, preferably O, S-O, co-S) Light* elements with their filling elements are horizontal, i.e. in the case of a simple ring, The walls of the ring form an array of filling elements that tend to be vertical rather than horizontal. . Such a filling element is particularly suitable for use according to the invention and is placed in a container. It is relatively easy to It has been found that this has the advantage that the speed does not change excessively. friend.

この発明による発酵器用の投込み充填要素として使用するための充填要素の適性 に対する有用且つ実際的尺度は空気を充填要素配列に通した時の圧力降下である 。知られているように充填要素の形状による圧力降下は、とりわけ、その大きさ によシ決定され、小さい充填要素(リングツの方が大きい充填要素(リング)よ り大きい圧力降下すなわち空気流に対する大きな抵抗を生ずる。またこの逆も真 である。Suitability of the filling element for use as a charge filling element for fermenters according to the invention A useful and practical measure for is the pressure drop when air is passed through an array of packing elements. . As is known, the pressure drop due to the shape of the filling element depends, among other things, on its size The smaller filling elements (rings) are larger than the larger filling elements (rings). This results in a large pressure drop and therefore a large resistance to air flow. The reverse is also true It is.

第1表にこの発明によ#)f用する種々の大きさの充填要素についての好適な蛾 大圧力降下を、掲げる:第1表 空気流速: /!00ポンド/時間/平方フィート水流速: 5ootyytυ ト/時間/平方フィート40 /J /j 、7 o z t、z −〇 6 j 上述の基準を満足する適当な充填要素には側面に穿孔及び内部の半径肋材または 直径肋材を備えまたは備えない環(リング]及びテラレットリング(ツル巻き状 ら線に形成された充填要素)が含まれる。Table 1 lists suitable moths for filling elements of various sizes for use according to the invention. Listing large pressure drop: Table 1 Air flow velocity: /! 00 pounds/hour/square foot Water flow rate: 5ootyytυ / hour / square foot 40 / J / j ,7 oz t,z −〇 6 j Suitable filling elements that meet the above criteria include side perforations and internal radius ribs or Rings with or without diameter ribs and terraret rings (filling elements formed in parallel lines) are included.

我々はどのような理論的理由によシ限定されることを欲するものではないが、こ の発明による発酵方法の効能は充填要素配列の表面上に被処理有機廃液の嫌気性 分解を行う嫌気性微生物を含む物質のフィルムの形成にあると考えられる。更に また、充填要素の表面に有機廃液を比較的円滑に流れさせることによって該フィ ルムの一層均一で且つ広く拡がった被膜を生ずるだけでなく、一層有効なフィル ムを生ずるためと考えられる。Although we do not wish to be limited by any theoretical reason, we The effectiveness of the fermentation method invented by This is thought to be due to the formation of a film of material containing anaerobic microorganisms that perform decomposition. Furthermore Additionally, by allowing the organic waste to flow relatively smoothly over the surface of the packing element, Not only does this result in a more uniform and wider coverage of the film, but it also provides a more effective film. This is thought to be because it causes a problem.

こうして、フィルムの厚さはフィルム上を流れる液体の液圧による剪断速度によ り制限され、従ってフィルム上に液体の比較的均一で且つ円滑な流れをつくるこ とによって実質上均一なフィルム厚を与えることが可能である。すなわち充填要 素の表面上に有効な拡がつ九フィルム(これは比較的「デッドスポット」がない )を与えるから単位表面積当りの活性は充填要素配列の水平面にわたって一層均 一となると考えられる。Thus, the thickness of the film depends on the hydraulic shear rate of the liquid flowing over the film. is limited, thus creating a relatively uniform and smooth flow of liquid over the film. It is possible to provide a substantially uniform film thickness. In other words, filling is required. Effective spreading film on bare surfaces (relatively free of "dead spots") ), the activity per unit surface area becomes more uniform over the horizontal plane of the packing element array. It is thought that it will be one.

従って、この発明により使用する充填要素の形状の適性の他の尺度はフィルムで 覆われる充填要素配列の自由表面積のチであシ、好適には使用に際して少くとも *0%、更に好適には少くともり3sがフィルムで覆われるべきである。Therefore, another measure of the suitability of the shape of the filling element used according to the invention is the film. The free surface area of the packing element array to be covered is preferably at least *0%, more preferably at least 3s should be covered with the film.

再び、どのような理論的理由によっても制限されることを欲しないが、多くの場 合に嫌気性分解は段階的に起ると考えられる。すなわち一つの微生物が有機廃液 中の有機廃物をある程度分解し、次いで他の微生物がその分解工程を更に進める と考えられる。Again, without wishing to be limited by any theoretical reasons, in many cases In this case, anaerobic decomposition is thought to occur in stages. In other words, one microorganism is an organic waste liquid. The organic waste inside is decomposed to some extent, and then other microorganisms further advance the decomposition process. it is conceivable that.

発酵器を通る液体の流れは押出し流れに近似しているから、このことは例えば、 酸生成性微生物は発酵器の下端部の成層層(成層フィルム)に分布し、メタン生 成性微生物に発酵器の上部に同様に分布するようにするのを可能となす。更に、 このような異なるフィルム上での最適流速は異なるから、こうして単位体積当シ 異なる表面積をもつ充填要素の層で形成された充填配列を使用することが可能で あり、或は充填要素配列の一つの面を通る流速(これはその面では実質上均一で あるが]が他の面を通る流速とは異るようにテーパー付き発酵器を使用すること も可能である。Since the flow of liquid through the fermenter is similar to the extrusion flow, this means that e.g. Acid-producing microorganisms are distributed in the stratified layer (stratified film) at the bottom of the fermenter and produce methane. This allows the adult microorganisms to be similarly distributed in the upper part of the fermenter. Furthermore, Since the optimum flow rate on such different films is different, the unit volume ratio is thus It is possible to use packing arrays formed by layers of packing elements with different surface areas. or the flow velocity through one face of the packing element array (which is substantially uniform on that face) Use a tapered fermenter so that the flow rate is different than the flow rate through the other surface. is also possible.

一般に、この発明による発酵器を通る液流速(廃液の流れの方向に対し垂直な平 面を通る流速として考えた) U O,2〜j0ψ程度、史に詳しくはコル弘O w7’日といった比較的低流速である。たとえこのように低流速でも、このよう な低流速が先行技術による滞留時間に比べて低滞留時間、例えばコク時間或はそ れ以下、特に3〜10時間の低滞留時間を与える。In general, the liquid flow rate through the fermenter according to the invention (in the plane perpendicular to the direction of waste flow) (Considered as the flow velocity passing through the surface) U O, about 2~j0ψ. For details on the history, see Col. The flow rate is relatively low, such as w7' days. Even at such low flow rates, The low flow rate results in a low residence time compared to prior art residence times, e.g. body time or the like. It provides a low residence time of less than 3 hours, especially 3 to 10 hours.

被処理廃物の性質に応じて、発酵を行うのに液の加熱が必要であつ九シ、なかっ たりするが、いずれにせよ、発酵はダO℃〜go℃、好適にFi二〇℃〜&j’ Cで行うのが適当である。Depending on the nature of the waste to be treated, heating of the liquid may or may not be necessary for fermentation. However, in any case, fermentation is carried out at temperatures between 0°C and 20°C, preferably between 20°C and 20°C. It is appropriate to use C.

発酵器中の充填要素配列を通って昇流する物質は充填要素配列の少くとも上部で は嫌気性発酵により発生したガス、例えばメタンをも含む。充填要素はその表面 からカスを効率よく放出できることが望ましく、表面上での流速に急激な変化を 生じない充填要素は充填要素上の嫌気性微生物のフィルムの生成を妨害しないで ガスを効率よく放出させ、且つ充填要素配列をガスが流通するのを容易にするこ とが望ましい。発酵器の上部では流体(液体及びガス]の全流速が大きくなるか ら、その大きくなり九流速に順応するために、充填要素配列の下部を形成する充 填要素の単位体積当りの表面積より低い単位体積当りの表面積をもつ充填要素が 上部全形成することが望ましい。The material flowing up through the packing element array in the fermenter must be at least at the top of the packing element array. also includes gases generated by anaerobic fermentation, such as methane. The filling element is its surface It is desirable to be able to efficiently release debris from the surface, and it is desirable to Packing elements that do not interfere with the formation of anaerobic microbial films on the packing elements To efficiently release gas and facilitate gas flow through the packing element arrangement. is desirable. Is the total flow rate of fluids (liquids and gases) higher at the top of the fermenter? In order to accommodate its increasing flow velocity, the filling element forming the lower part of the filling element array is The filling element has a surface area per unit volume lower than the surface area per unit volume of the filling element. It is desirable to form the entire upper part.

この発明の方法及び装置は種々の有機廃液(この有機廃液とはM機廃棄物の水性 液及び/または懸濁液を意味するλ、例えば家庭下水、食品及び飲料製造工場か らの廃水、及び精油工場からの廃水を処理するのに使用できる。この発酵はコク の主要な機能すなわち(a)廃液のB、0.D、 (生化学的酸素要求量)を減 少させ、同時に(b)廃物からメタンのような有用な物質を製造する機能をもつ 。所望により処理ずみ廃液を例えば従来の好気性発酵法によシ更に精製できる。The method and apparatus of this invention can be applied to various organic waste liquids (this organic waste liquid is an aqueous waste of M-machine waste). λ meaning liquid and/or suspension, e.g. domestic sewage, food and beverage manufacturing plants; It can be used to treat wastewater from plants and oil refineries. This fermentation is rich The main functions of (a) waste liquid B, 0. D. Reduce (biochemical oxygen demand) (b) At the same time, it has the function of producing useful substances such as methane from waste. . If desired, the treated effluent can be further purified, for example, by conventional aerobic fermentation methods.

上述のように嫌気性発酵は段階的に起る(と思われる)から、この発明による発 酵法は多数の連続発酵器(これらの各々においては発酵の一段階ずつが行われる ]中で行われるっ この発明による発酵法及び発酵装置は廃液以外に液状、有機物含有基体、例えば 付加的物質または栄養物が添加しである廃液または他の基体の嫌気性発酵に使用 できる。換言すれば、この発明による方法及び装置は人魚また。i遺伝的に変成 した微生物であってもよい微生物例えば細菌または酵素の作用によって種々の基 体の嫌気性発酵全行うのに使用できる。As mentioned above, anaerobic fermentation occurs (it seems) in stages, so the fermentation process according to this invention The fermentation process consists of a number of continuous fermenters, each of which carries out one stage of fermentation. ] It will be held inside The fermentation method and fermentation apparatus according to the present invention can be applied to liquid, organic matter-containing substrates other than waste liquid, e.g. Used for anaerobic fermentation of waste liquids or other substrates to which additional substances or nutrients have been added can. In other words, the method and apparatus according to the present invention can also be used as a mermaid. igenetically altered microorganisms such as bacteria or enzymes, which may be microorganisms that have been It can be used to carry out all anaerobic fermentation in the body.

浄書(内容に変更なし) 手続補正書 昭和5C3年4用 日 特許庁長官殿 ■、 事件の表示 = PCT/GB tコ100:1:1g 2、 発明の名称 嫌気性発d 3、 補正をする者 ゛ 事件との関係 特許出願人 名称 氏名 マクケオウン、ケビン・ジョゼフ5、補正の対象 ム補正の内容 (1) 別紙委任状の通り (2) 図面の翻訳文の浄書(内容に変更なし)コ 国際調査報告Engraving (no changes to the content) Procedural amendment Showa 5C 3rd year 4th day Commissioner of the Patent Office ■, Incident display = PCT/GB tco100:1:1g 2. Name of the invention anaerobic development 3. Person who makes corrections゛ Relationship to the incident: Patent applicant name Name: McKeown, Kevin Joseph 5, subject to correction Contents of correction (1) As per attached power of attorney (2) Engraving of the translation of the drawing (no changes to the content) international search report

Claims (1)

【特許請求の範囲】 l 充填要素配列(A) を備えた充填発酵容器(1)中で嫌気条件下で有機廃 液の発酵を行う方法において、該廃液を充填要素配列(6)に下記の条件:(1 )廃液の流れの方向に垂直な平面を通る廃液の単位面積当シの流速が実質上均一 であること、(−)有機廃液が急激な流速変化が比較的少なく充填要素配列の表 面上に円滑に流れる; という条件下で流すととによって発酵を行うことを特徴とする有機廃液の嫌気性 発酵方法。 3 有機廃液を拡散装置すなわち流れ矯正装置(II) t−経て充填要素配列 (6)に導入する請求の範囲第1項または第2項記載の方法。 嘔 充填要素配列())が1未満の縦横比をもつ投込み充填要素の配列からなる 請求の範囲第1項ないし第3項のいずれかに記載の方法。 S 充填要素の縦横比が0.66以下、好ましくはθ、S〜0.2、特許請求の 範囲第ダ項記載の方法。[Claims] l organic waste under anaerobic conditions in a packed fermentation vessel (1) with a packing element arrangement (A) In the method of fermenting the liquid, the waste liquid is placed in the packing element array (6) under the following conditions: (1 ) The flow rate per unit area of the waste liquid through a plane perpendicular to the direction of the flow of the waste liquid is substantially uniform. (−) The organic waste liquid has relatively few rapid changes in flow rate and the packing element arrangement table Flows smoothly over the surface; Anaerobic treatment of organic wastewater characterized by fermentation by flowing it under the conditions of Fermentation method. 3 Diffusion device for organic waste liquid, i.e. flow straightening device (II) T-through filling element arrangement (6) The method according to claim 1 or 2, which is introduced in (6). The filling element array ()) consists of an array of input filling elements with an aspect ratio of less than 1. A method according to any one of claims 1 to 3. S The aspect ratio of the filling element is 0.66 or less, preferably θ, S ~ 0.2, as claimed in the patent The method described in Scope No. D.
JP57502187A 1981-07-24 1982-07-26 anaerobic fermentation Pending JPS58501161A (en)

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US4613433A (en) * 1982-12-24 1986-09-23 Biomass Limited Anaerobic fermentor
GB2149815A (en) * 1983-09-21 1985-06-19 Biomass International Anaerobic fermenter
GB2149390A (en) * 1983-09-21 1985-06-12 Biomass International Anaerobic fermentation process
US4530762A (en) * 1984-03-28 1985-07-23 Love Leonard S Anaerobic reactor

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GB1385672A (en) * 1970-12-18 1975-02-26 Mass Transfer Ltd Fluid-fluid contact apparatus

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