JP4641271B2 - Fermenter charging method and processing apparatus for organic substance-containing liquid - Google Patents

Fermenter charging method and processing apparatus for organic substance-containing liquid Download PDF

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JP4641271B2
JP4641271B2 JP2006056347A JP2006056347A JP4641271B2 JP 4641271 B2 JP4641271 B2 JP 4641271B2 JP 2006056347 A JP2006056347 A JP 2006056347A JP 2006056347 A JP2006056347 A JP 2006056347A JP 4641271 B2 JP4641271 B2 JP 4641271B2
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芳孝 東郷
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Kajima Corp
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本発明は、有機物含有液の発酵槽投入方法及び処理装置に関し、とくに有機物含有液をメタン発酵微生物群との接触により分解する発酵槽へ被処理有機物含有液を投入する方法及びその方法の実施に使用する有機物含有液の処理装置に関する。
本発明は、有機性廃棄物の粉砕スラリー等をメタン発酵微生物群との接触により分解してバイオガスをエネルギーとして回収する廃棄物再資源化型のメタン発酵施設等に有効に利用することができる。
The present invention relates to a fermenter charging method and a processing apparatus for an organic substance-containing liquid, and in particular, to a method for introducing an organic substance-containing liquid to be processed into a fermenter that decomposes an organic substance-containing liquid by contact with a methane fermentation microorganism group and to the implementation of the method. The present invention relates to an organic substance-containing liquid processing apparatus to be used.
INDUSTRIAL APPLICABILITY The present invention can be effectively used for a waste recycling type methane fermentation facility that decomposes a ground slurry of organic waste by contact with a methane fermentation microorganism group and recovers biogas as energy. .

循環型社会の形成を目指して、従来は焼却・埋立て処分されてきた一般家庭やホテル・レストラン等から排出される生ごみ、食品工場等から排出される食品製造残さ、農業・林業・水産・畜産施設や工場等から排出される動植物性残さ等の有機性廃棄物からメタン発酵処理によりエネルギーを回収する再資源化技術が開発され普及が進められている。例えば特許文献1及び2は、有機性廃棄物をスラリー状に微破砕した上でメタン発酵微生物群(以下、分解微生物という)が付着した担体を配設したバイオリアクター(以下、発酵槽という)に投入し、分解微生物が活性を示す温度で廃棄物スラリーを分解微生物と接触させて分解する有機性廃棄物の処理方法を開示する。また特許文献3は、有機性廃棄物スラリーを発酵槽へ送ってバイオガスと残留有機物とに変換し、バイオガスから燃料電池等により電力エネルギーを回収し、残留有機物から肥料・飼料を回収するシステムを開示する。特許文献1〜3の方法は、下水処理場やし尿処理場等において有機性廃水等からメタン発酵を利用してエネルギーを回収する場合にも適用可能である。   Aiming at the formation of a recycling-oriented society, food waste generated from ordinary households, hotels, restaurants, etc. that have been incinerated or landfilled in the past, food production residues from food factories, agriculture, forestry, fisheries, Recycling technology for recovering energy from organic waste such as animal and plant residues discharged from livestock facilities and factories by methane fermentation treatment has been developed and promoted. For example, Patent Documents 1 and 2 disclose a bioreactor (hereinafter referred to as a fermenter) in which a carrier to which a methane fermentation microorganism group (hereinafter referred to as a decomposing microorganism) is attached after finely pulverizing organic waste in a slurry state. Disclosed is a method for treating organic waste that is charged and decomposed by bringing the waste slurry into contact with the decomposing microorganism at a temperature at which the decomposing microorganism is active. Patent Document 3 discloses a system in which an organic waste slurry is sent to a fermentor to be converted into biogas and residual organic matter, and power energy is recovered from the biogas by a fuel cell, and fertilizer and feed are recovered from the residual organic matter. Is disclosed. The methods of Patent Documents 1 to 3 are also applicable when energy is recovered from organic wastewater or the like using methane fermentation in a sewage treatment plant or a human waste treatment plant.

特許文献1〜3のメタン発酵処理では、有機性廃棄物の粉砕スラリーや有機性廃水等(以下、これらを纏めて有機物含有液Sという)を効率的・安定的にメタン発酵するため、発酵槽内の有機物含有液(発酵液)Sを適当に攪拌して均一にすると共に最適な発酵温度に保持する必要がある。様々な攪拌方法を採用できるが、例えば小型の発酵槽1では、図5(C)に示すように発酵槽1の上部に攪拌翼46付き攪拌機45を設け、発酵槽1内の有機物含有液Sを攪拌翼46の回転により攪拌する方法が採用されている。これに対し大型の発酵槽1や微生物固定床2(図4参照)を設けた発酵槽1では、図5(A)及び(B)に示すように発酵槽1にポンプ6付き外付け循環路5を設け、発酵槽1内の有機物含有液Sを循環路5経由の循環により攪拌する方法(循環型攪拌法)が採用されている。   In the methane fermentation treatment of Patent Documents 1 to 3, a fermenter is used to efficiently and stably perform methane fermentation of pulverized slurry of organic waste, organic waste water, and the like (hereinafter collectively referred to as organic substance-containing liquid S). The organic substance-containing liquid (fermented liquid) S in the inside needs to be properly stirred to be uniform and kept at an optimal fermentation temperature. Various agitation methods can be employed. For example, in the small-sized fermenter 1, as shown in FIG. 5C, an agitator 45 with a stirring blade 46 is provided on the upper part of the fermenter 1, and the organic substance-containing liquid S in the fermenter 1 is provided. A method is used in which the agitator is agitated by the rotation of the agitating blade 46. On the other hand, in the fermenter 1 provided with the large-scale fermenter 1 and the microorganism fixed bed 2 (see FIG. 4), an external circulation path with a pump 6 is provided in the fermenter 1 as shown in FIGS. 5, and a method of stirring the organic substance-containing liquid S in the fermenter 1 by circulation through the circulation path 5 (circulation type stirring method) is employed.

図5(A)は、発酵槽1内の有機物含有液Sを下部から抜き出し上部へ戻すことにより、発酵槽1内に下向流を形成しつつ有機物含有液Sを循環させる(図中の斜線付き矢印参照、下向流式の循環型攪拌法)。これに対し同図(B)は、発酵槽1内の有機物含有液Sを上部から抜き出し下部へ戻すことにより、発酵槽1内に上向流を形成しつつ有機物含有液Sを循環させる(図中の斜線付き矢印参照、上向流式の循環型攪拌法)。同図(A)の下向流式は、有機物含有液Sの表面にできるスカム層を破壊することができ、発酵槽1内に発生したバイオガスの上昇流(図中の白抜き矢印参照)との交差により有機物含有液Sの効果的な攪拌が期待できる等の点で、同図(B)の上向流式よりも優れている。   FIG. 5 (A) shows that the organic substance-containing liquid S in the fermenter 1 is extracted from the lower part and returned to the upper part to circulate the organic substance-containing liquid S while forming a downward flow in the fermenter 1 (hatched line in the figure). (Refer to the attached arrow, downward flow type circulation stirring method). On the other hand, FIG. 5 (B) circulates the organic substance-containing liquid S while forming an upward flow in the fermenter 1 by extracting the organic substance-containing liquid S in the fermenter 1 from the upper part and returning it to the lower part (FIG. (See the shaded arrow in the inside, upward-flow circulation type stirring method). The downward flow type in FIG. 6A can destroy the scum layer formed on the surface of the organic substance-containing liquid S, and the upward flow of biogas generated in the fermenter 1 (see the white arrow in the figure). This is superior to the upward flow type in FIG. 5B in that an effective stirring of the organic substance-containing liquid S can be expected due to the intersection with.

図4(A)は、有機物含有液SからバイオガスGを回収する従来のメタン発酵処理システムの一例を示す。スラリータンク等の貯留タンク30に蓄えた有機物含有液Sを、スラリー専用の回転式ポンプ、スクリュー型ポンプ、チューブポンプ等のポンプ31により、供給路32経由で発酵槽1の頂部の投入口33へ適当な流量で投入する。図示例の発酵槽1は嫌気状態に保持された気密槽であり、内部に分解微生物が付着した固定床2を有し、下部の抜出口3と上部の吐出口8との間に外付け循環路5を設けている。発酵槽1に投入された有機物含有液Sは、下向流式の循環型攪拌法で攪拌されながら発酵槽1内に所要時間滞留し、分解微生物との接触によりバイオガスGと処理液Wとに分解される。処理後の処理液Wは発酵槽1の底部から排出され、必要に応じて二次処理施設で高度処理したのち下水道や河川に放流される。発酵槽1内の有機物含有液Sの滞留時間は、ポンプ31の供給流量と処理液Wの排出流量とにより調節できる。発酵槽1内で生成されたバイオガスGは、必要に応じて脱硫機36で脱硫したのち処理系外へ回収する。   FIG. 4A shows an example of a conventional methane fermentation treatment system that recovers the biogas G from the organic substance-containing liquid S. The organic substance-containing liquid S stored in a storage tank 30 such as a slurry tank is supplied to the inlet 33 at the top of the fermenter 1 via a supply path 32 by a pump 31 such as a rotary pump, a screw pump, or a tube pump dedicated to slurry. Input at an appropriate flow rate. The fermenter 1 in the illustrated example is an airtight tank maintained in an anaerobic state, and has a fixed bed 2 to which decomposed microorganisms are attached, and is externally circulated between a lower outlet 3 and an upper outlet 8. A path 5 is provided. The organic substance-containing liquid S charged in the fermenter 1 stays in the fermenter 1 for a required time while being stirred by the downward flow circulation type stirring method, and comes into contact with the decomposing microorganisms for biogas G and treatment liquid W. Is broken down into The treated liquid W after the treatment is discharged from the bottom of the fermenter 1, and after advanced treatment at a secondary treatment facility as necessary, it is discharged into sewers and rivers. The residence time of the organic substance-containing liquid S in the fermenter 1 can be adjusted by the supply flow rate of the pump 31 and the discharge flow rate of the processing liquid W. The biogas G produced in the fermenter 1 is desulfurized by the desulfurizer 36 as needed, and then recovered outside the processing system.

特許第2708087号公報Japanese Patent No. 270887 特開10−005718号公報JP 10-005718 A 特許第3064272号公報Japanese Patent No. 3064272

しかし、図4(A)のメタン発酵処理システムにおいて、図3(A)のように発酵槽1への有機物含有液Sの投入口33が一箇所であると、投入した有機物含有液Sが投入口33の直下に滞留し、発酵槽1内で安定したメタン発酵処理を維持できない場合がある。有機物含有液S中の有機物が分解されて最終的なガス生成物Gができるまでのメタン発酵処理の反応工程は、大きく三段階に分けることができる。第一段階では、分解微生物中の加水分解菌により有機物が加水分解されて低分子量の有機物に分解される(加水分解反応)。第二段階では、分解微生物中の酸発酵菌により低分子量の有機物が酢酸等の有機酸に分解される(酸発酵反応)。最終段階において、分解微生物中のメタン生成菌により有機酸がメタンと二酸化炭素とに分解される(メタン生成反応)。これらの反応のうち加水分解反応・酸発酵反応は比較的容易に進行するが、メタン生成反応はメタン生成菌の利用する蟻酸や酢酸等の有機酸濃度が高くなり過ぎると阻害を受ける。有機物含有液Sを一箇所の投入口33から発酵槽1へ投入した場合、有機物含有液Sが投入口33の直下の液面Fに集中的に供給されることとなり、そこで微生物反応が局所的に進み有機物含有液S内に局所的な有機酸濃度の上昇やpHの低下を生じるため、微生物が死滅して微生物反応の効率が低下する場合がある。   However, in the methane fermentation treatment system of FIG. 4 (A), when the input port 33 of the organic substance-containing liquid S to the fermenter 1 is one place as shown in FIG. 3 (A), the input organic substance-containing liquid S is input. There is a case where the methane fermentation process stays under the mouth 33 and cannot maintain a stable methane fermentation treatment in the fermenter 1. The reaction process of the methane fermentation treatment until the organic substance in the organic substance-containing liquid S is decomposed to produce the final gas product G can be roughly divided into three stages. In the first stage, an organic substance is hydrolyzed by a hydrolyzing bacterium in the decomposing microorganism to be decomposed into a low molecular weight organic substance (hydrolysis reaction). In the second stage, an organic substance having a low molecular weight is decomposed into an organic acid such as acetic acid (acid fermentation reaction) by the acid-fermenting bacteria in the decomposing microorganism. In the final stage, the organic acid is decomposed into methane and carbon dioxide by the methanogen in the decomposing microorganism (methane production reaction). Among these reactions, hydrolysis reaction and acid fermentation reaction proceed relatively easily, but the methanogenesis reaction is inhibited when the concentration of organic acids such as formic acid and acetic acid used by methanogens becomes too high. When the organic substance-containing liquid S is introduced into the fermenter 1 from a single inlet 33, the organic substance-containing liquid S is intensively supplied to the liquid surface F immediately below the inlet 33, where microbial reactions occur locally. Since the local organic acid concentration rises and the pH falls in the organic substance-containing liquid S, the microorganisms may die and the efficiency of the microbial reaction may be lowered.

図4(A)の発酵槽1内における有機物含有液Sの局所的な滞留を避けるため、図3(B)のように発酵槽1への有機物含有液Sの供給路32に複数の出口8を設け、有機物含有液Sを各出口8に均等に分配して発酵槽1内の液面Fの全体に分散する方法が考えられる。ただしこの方法では、有機物含有液Sが固形分を多量に含み高粘度である場合に、閉塞を避けるため発酵槽1の供給路32及び複数の出口8の配管径をある程度大きくし、大径の供給路32から複数の出口8へ均等に分配するため有機物含有液Sを十分な流量で供給する必要がある。実際のメタン発酵施設では有機物含有液Sの発生量(例えば、有機性廃棄物の回収量)が少なく、複数の出口8へ均等に分配できる程度の供給流量を確保することが難しい場合も多い。有機物含有液Sを大量の水で希釈すれば、粘度を下げると同時に流量を上げて有機物含有液Sを分散し易くすることが可能であるが、水量が増えるためバイオガスGの回収効率が低下し、回収効率を上げるため発酵槽1の容量を大きくする必要が生じる。また、ランニングコスト(例えば、発酵槽1の加熱等に要するエネルギーや循環ポンプ6の容量が大きくなり動力にかかるコスト)の増大を招く。   In order to avoid local residence of the organic substance-containing liquid S in the fermenter 1 of FIG. 4 (A), a plurality of outlets 8 are provided in the supply path 32 of the organic substance-containing liquid S to the fermenter 1 as shown in FIG. 3 (B). The organic substance-containing liquid S can be evenly distributed to the outlets 8 and dispersed over the entire liquid surface F in the fermenter 1. However, in this method, when the organic substance-containing liquid S contains a large amount of solids and has a high viscosity, in order to avoid clogging, the pipe diameters of the supply path 32 and the plurality of outlets 8 of the fermenter 1 are increased to some extent, In order to distribute evenly from the supply path 32 to the plurality of outlets 8, it is necessary to supply the organic substance-containing liquid S at a sufficient flow rate. In an actual methane fermentation facility, the amount of organic substance-containing liquid S generated (for example, the amount of organic waste recovered) is small, and it is often difficult to secure a supply flow rate that can be evenly distributed to the plurality of outlets 8. If the organic substance-containing liquid S is diluted with a large amount of water, it is possible to easily disperse the organic substance-containing liquid S by decreasing the viscosity and simultaneously increasing the flow rate. However, since the amount of water increases, the recovery efficiency of the biogas G decreases. In order to increase the recovery efficiency, the capacity of the fermenter 1 needs to be increased. Moreover, the running cost (for example, the energy required for heating the fermenter 1 or the capacity of the circulation pump 6 increases and the cost for power) increases.

特許文献1は、図4(B)に示すように、有機物含有液Sを発酵槽1の循環路5に供給する方法を開示している。供給路32aの有機物含有液Sを循環路5中の有機物含有液S(以下、循環液Sということがある)と混合した上で発酵槽1に投入すれば、供給路32aの有機物含有液Sの流量が少ない場合でも循環路5中の流量が十分あるため、有機物含有液Sを循環液Sと混合しつつ複数の出口8に均等に分配することが可能である。   Patent Document 1 discloses a method of supplying the organic substance-containing liquid S to the circulation path 5 of the fermenter 1 as shown in FIG. If the organic substance-containing liquid S in the supply path 32a is mixed with the organic substance-containing liquid S in the circulation path 5 (hereinafter also referred to as the circulation liquid S) and then introduced into the fermenter 1, the organic substance-containing liquid S in the supply path 32a. Even when the flow rate is small, the flow rate in the circulation path 5 is sufficient, so that the organic substance-containing liquid S can be evenly distributed to the plurality of outlets 8 while being mixed with the circulating liquid S.

しかし、図4(B)のような下向流式の循環型攪拌法では、循環路5のポンプ上流側に発酵槽1の水圧が加わっており、循環路5のポンプ下流側にも水圧とポンプ圧力とが加わっており、循環路5が常に加圧された状態となっている。このため図示例のように有機物含有液Sの供給路32aを循環路5に直接接続すると、何らかの原因で供給ポンプ31が停止した場合や供給路32aにシール漏れ等が生じた場合に、循環路5内の循環液Sが供給路32a側に逆流して外部に漏れ出す重大事故を起こす危険がある。供給路32aに循環液Sの逆流防止用の逆止弁を設置したとしても、有機物含有液Sに多量に含まれる固形分が逆止弁を閉塞して逆止弁が十分に機能しないおそれがある。また、同図に点線で示すように供給路32bを循環路5との接続点より高く保持したとしても、サイフォン現象により循環液Sが供給路32a側へ逆流する可能性があり、やはり循環液Sの外部漏れを確実に防止することは困難である。   However, in the downward flow circulating stirring method as shown in FIG. 4B, the water pressure of the fermenter 1 is applied to the upstream side of the pump in the circulation path 5, and the water pressure is also applied to the downstream side of the pump in the circulation path 5. The pump pressure is applied, and the circulation path 5 is always pressurized. For this reason, when the supply path 32a of the organic substance-containing liquid S is directly connected to the circulation path 5 as shown in the drawing, the circulation path is used when the supply pump 31 is stopped for some reason or when a seal leak occurs in the supply path 32a. There is a risk of causing a serious accident in which the circulating fluid S in 5 flows back to the supply path 32a and leaks outside. Even if a check valve for preventing the backflow of the circulating fluid S is installed in the supply path 32a, there is a possibility that the solid content contained in the organic substance-containing liquid S may block the check valve and the check valve does not function sufficiently. is there. In addition, even if the supply path 32b is held higher than the connection point with the circulation path 5 as indicated by the dotted line in the figure, the circulating fluid S may flow back to the supply path 32a due to the siphon phenomenon. It is difficult to reliably prevent external leakage of S.

そこで本発明の目的は、有機物含有液の安定した発酵処理を安全に維持できる有機物含有液の発酵槽投入方法及び処理装置を提供することにある。   Then, the objective of this invention is providing the fermenter input method and processing apparatus of the organic substance containing liquid which can maintain the stable fermentation process of the organic substance containing liquid safely.

図1の実施例を参照するに、本発明による有機物含有液の発酵槽投入方法は、分解微生物を保持し微生物との接触により有機物含有液Sを分解する発酵槽1に槽1内の有機物含有液Sを下部から抜き出し頂部に分散配置した複数の吐出口8へ戻すポンプ6付き外付け循環路5を設け、発酵槽1の液面レベルLの高さに底部が循環路5と接続され且つ頂部空間13が発酵槽1内の上部空間4と連通した液溜タンク10を保持し、被処理有機物含有液Sを液溜タンク10の頂部空間13に取り入れ液溜タンク10の底部から循環路5に供給し且つ循環路5の循環液Sと共に複数の吐出口8から発酵槽1内に投入するものである。 Referring to the embodiment of FIG. 1, the fermenter charging method of the organic matter-containing liquid according to the present invention includes the fermenter 1 that holds the decomposed microorganisms and decomposes the organic matter-containing liquid S by contact with the microorganisms. An external circulation path 5 with a pump 6 that returns the liquid S from the lower part and returns to a plurality of discharge ports 8 distributed at the top is provided, the bottom is connected to the circulation path 5 at the level of the liquid level L of the fermenter 1 and The top space 13 holds a liquid tank 10 communicating with the upper space 4 in the fermenter 1, and the organic substance-containing liquid S is taken into the top space 13 of the liquid tank 10 from the bottom of the liquid tank 10 to the circulation path 5. To the fermenter 1 from the plurality of discharge ports 8 together with the circulating fluid S in the circulation path 5.

好ましくは、液溜タンク10の頂部及び底部を循環路5のポンプ下流側5b及び上流側5aに接続し、被処理有機物含有液Sを循環路5のポンプ下流側5bから液溜タンク10内に引き込んだ循環液Sと混合して循環路5のポンプ上流側5aへ供給する。   Preferably, the top and bottom of the liquid storage tank 10 are connected to the pump downstream side 5b and the upstream side 5a of the circulation path 5, and the organic matter-containing liquid S to be treated enters the liquid storage tank 10 from the pump downstream side 5b of the circulation path 5. It mixes with the circulating fluid S drawn in and is supplied to the pump upstream side 5a of the circulation path 5.

また図1の実施例を参照するに、本発明による有機物含有液の処理装置は、分解微生物を保持し微生物との接触により有機物含有液Sを分解する発酵槽1、発酵槽1内の有機物含有液Sを下部から抜き出し頂部に分散配置した複数の吐出口8へ戻すポンプ6付き外付け循環路5、発酵槽1の液面レベルLの高さに保持され且つ底部が循環路5に接続された液溜タンク10、液溜タンク10内の頂部と発酵槽5内の上部空間4とを連通する均圧路18、及び液溜タンク10の頂部に接続された被処理有機物含有液Sの供給路32を備えたものである。 Referring to the embodiment of FIG. 1, the processing apparatus for organic matter-containing liquid according to the present invention includes a fermenter 1 that holds decomposed microorganisms and decomposes the organic matter-containing liquid S by contact with microorganisms, and contains organic matter in the fermenter 1. The liquid S is withdrawn from the bottom and returned to a plurality of discharge ports 8 distributed at the top, and is attached to the external circulation path 5 with a pump 6, maintained at the level of the liquid level L of the fermenter 1, and the bottom is connected to the circulation path 5. The liquid tank 10, the pressure equalization path 18 that connects the top of the liquid tank 10 and the upper space 4 in the fermentation tank 5, and the supply of the organic substance-containing liquid S to be treated connected to the top of the liquid tank 10 A road 32 is provided.

好ましくは、液溜タンク10の底部を循環路5のポンプ上流側5aに接続し、液溜タンク10の頂部に循環路5のポンプ下流側5bから循環液Sを引き込む調節弁16付き引込路15を設ける。   Preferably, the bottom of the liquid reservoir tank 10 is connected to the pump upstream side 5a of the circulation path 5, and the retraction path 15 with the control valve 16 is drawn into the top of the liquid reservoir tank 10 from the pump downstream side 5b of the circulation path 5. Is provided.

本発明による有機物含有液の発酵槽投入方法及び処理装置は、発酵槽1の液面レベルLの高さに底部が循環路5と接続され且つ頂部空間13が発酵槽1内の上部空間4と連通した液溜タンク10を保持し、被処理有機物含有液Sを液溜タンク10の頂部空間13に取り入れ液溜タンク10の底部から発酵槽1の外付け循環路5に供給し、循環路5の循環液Sと共に発酵槽1の頂部に分散配置した複数の吐出口8を介して発酵槽1内に投入するので、次の顕著な効果を奏する。 The fermenter charging method and the processing apparatus of the organic substance-containing liquid according to the present invention are such that the bottom is connected to the circulation path 5 at the liquid level L of the fermenter 1 and the top space 13 is connected to the upper space 4 in the fermenter 1. A liquid reservoir tank 10 is held, and the organic substance-containing liquid S to be treated is taken into the top space 13 of the liquid reservoir tank 10 and supplied from the bottom of the liquid reservoir tank 10 to the external circulation path 5 of the fermenter 1. Since it introduce | transduces in the fermenter 1 via the some discharge port 8 disperse | distributed and arrange | positioned at the top part of the fermenter 1 with the circulating fluid S of this, there exists the following remarkable effect.

(イ)被処理有機物含有液Sを複数の吐出口8から発酵槽1内の液面に分散して投入するので、発酵槽1内における有機物含有液Sの局所的な滞留を避け、発酵槽1内の安定した発酵を維持できる。
(ロ)被処理有機物含有液Sを循環路5内の大量の循環液Sと共に発酵槽1に投入するので、有機物含有液Sが少量であっても、それを複数の吐出口8に均等に分散して発酵槽1内に投入できる。
(ハ)液溜タンク10内に発酵槽1内の上部空間4と連通する頂部空間13を設け、被処理有機物含有液Sの供給路32を液溜タンク10の頂部空間13に接続すると共に液溜タンク10の底部を循環路5と接続することにより、循環路5から供給路32への有機物含有液Sの逆流を頂部空間13によって有効に防止することができる。
(A) Since the organic matter-containing liquid S to be treated is dispersed and introduced from the plurality of discharge ports 8 to the liquid surface in the fermenter 1, avoiding local retention of the organic substance-containing liquid S in the fermenter 1, The stable fermentation within 1 can be maintained.
(B) Since the organic substance-containing liquid S to be treated is introduced into the fermenter 1 together with a large amount of the circulating liquid S in the circulation path 5, even if the organic substance-containing liquid S is small, it is evenly distributed to the plurality of discharge ports 8. It can be dispersed and put into the fermenter 1.
(C) A top space 13 communicating with the upper space 4 in the fermenter 1 is provided in the liquid storage tank 10, and the supply path 32 for the organic substance-containing liquid S to be treated is connected to the top space 13 of the liquid storage tank 10 and the liquid By connecting the bottom of the storage tank 10 to the circulation path 5, the back space of the organic substance-containing liquid S from the circulation path 5 to the supply path 32 can be effectively prevented by the top space 13.

(ニ)液溜タンク10に中和剤等の分解処理添加剤を流入させることにより、被処理有機物含有液Sと共に添加剤を発酵槽1内の液面に均等に分散投入することができる。
(ホ)液溜タンク10の頂部及び底部を循環路5のポンプ下流側5b及び上流側5aと接続することにより、被処理有機物含有液Sを循環路5のポンプ下流側5bから引き込んだ循環液Sとの混合により粘度を十分低下させた上で循環路5のポンプ上流側5aに供給することが可能となる。
(ヘ)また、液溜タンク10と発酵槽1とを液面レベル高さで連結し、循環路5のポンプ下流側5bに切替弁20経由で異物タンク21を接続することにより、発酵槽1内の液面の浮遊異物を液溜タンク10経由で異物タンク21へ排出することが可能となる。
(D) By allowing a decomposition treatment additive such as a neutralizing agent to flow into the liquid storage tank 10, the additive can be evenly distributed and introduced onto the liquid surface in the fermenter 1 together with the organic matter-containing liquid S to be treated.
(E) By connecting the top and bottom of the liquid storage tank 10 with the pump downstream side 5b and the upstream side 5a of the circulation path 5, the circulating liquid containing the organic substance to be treated S drawn from the pump downstream side 5b of the circulation path 5 It becomes possible to supply to the pump upstream side 5a of the circulation path 5 after sufficiently reducing the viscosity by mixing with S.
(F) In addition, the liquid tank 10 and the fermenter 1 are connected at a liquid level, and the fermenter 1 is connected to the pump downstream side 5b of the circulation path 5 via the switching valve 20. It becomes possible to discharge the floating foreign matter inside the liquid level to the foreign matter tank 21 via the liquid reservoir tank 10.

図1は、有機性廃棄物の粉砕スラリーである有機物含有液Sを分解微生物との接触により分解してバイオガスGを回収する本発明の処理装置の一実施例を示す。図示例の処理装置は、分解微生物を保持する発酵槽1と、発酵槽1内の有機物含有液Sを下向流式(図5(A)参照)で循環させるポンプ6付き外付け循環路5と、循環路5に接続された液溜タンク10とを有する。   FIG. 1 shows an embodiment of the treatment apparatus of the present invention that recovers biogas G by decomposing an organic substance-containing liquid S, which is a pulverized slurry of organic waste, by contact with decomposing microorganisms. The processing apparatus of the illustrated example has an external circulation path 5 with a pump 6 that circulates the fermenter 1 holding the decomposing microorganisms and the organic substance-containing liquid S in the fermenter 1 in a downward flow manner (see FIG. 5A). And a liquid storage tank 10 connected to the circulation path 5.

図示例の発酵槽1は、図4に示した従来の発酵槽と同様の気密槽であり、内部に微生物固定床4を有し、固定床4に上述した加水分解菌、酸発酵菌、メタン生成菌等が含まれる分解微生物を保持させる。固定床4は分解微生物が高濃度に付着可能な適当な担体、例えばガラス繊維製又は炭素繊維製の中空筒状担体を規則的に並べたものである。ただし、本発明の適用対象の発酵槽1は分解微生物を保持していれば足り、固定床4を有する発酵槽1に限定されない。   The fermenter 1 in the illustrated example is an airtight tank similar to the conventional fermenter shown in FIG. 4, and has a microorganism fixed bed 4 inside, and the hydrolyzed bacteria, acid fermenting bacteria, and methane described above in the fixed bed 4. Decomposing microorganisms containing bacteria and the like are retained. The fixed bed 4 is formed by regularly arranging an appropriate carrier to which a degrading microorganism can adhere at a high concentration, for example, a hollow cylindrical carrier made of glass fiber or carbon fiber. However, the fermenter 1 to which the present invention is applied is not limited to the fermenter 1 having the fixed bed 4 as long as it holds a decomposing microorganism.

図示例の循環路5は、循環ポンプ6と、循環ポンプ6の一端を発酵槽1の下部抜出口3に接続するポンプ上流路5aと、循環ポンプ6の他端を発酵槽1の頂部に接続するポンプ下流路5bと、ポンプ下流路5bの発酵槽側端に取り付けた分散吐出器7とを有する。分散吐出器7は、図3(B)に示すように、発酵槽1の頂面9に分散配置された複数の吐出口8を有する。発酵槽1内の有機物含有液Sを、循環ポンプ6により抜出口3からポンプ上流路5a経由で抜き出し、ポンプ下流路5b経由で分散吐出器7へ送り、分散吐出器7の複数の吐出口8から発酵槽1内へ戻すことにより循環させる。循環路5内の循環液Sが複数の吐出口8に均等に分配されるように、循環ポンプ6により循環路5内の循環液Sの流量を調整することができる。   The circulation path 5 in the illustrated example has a circulation pump 6, a pump upper flow path 5 a connecting one end of the circulation pump 6 to the lower outlet 3 of the fermenter 1, and the other end of the circulation pump 6 connected to the top of the fermenter 1. And a dispersion discharger 7 attached to the fermenter side end of the pump lower flow path 5b. The dispersion | distribution discharger 7 has the some discharge port 8 distributedly arrange | positioned at the top surface 9 of the fermenter 1, as shown to FIG. 3 (B). The organic substance-containing liquid S in the fermenter 1 is extracted from the outlet 3 by the circulation pump 6 via the pump upper flow path 5a, sent to the dispersion discharger 7 via the pump lower flow path 5b, and a plurality of discharge ports 8 of the dispersion discharger 7 Is circulated by returning to the fermenter 1. The flow rate of the circulating fluid S in the circulation path 5 can be adjusted by the circulation pump 6 so that the circulating fluid S in the circulation path 5 is evenly distributed to the plurality of discharge ports 8.

図示例の液溜タンク10は、発酵槽1の液面レベルLの高さに保持され、被処理有機物含有液Sの供給路32に連なる頂部の流入口11と、循環路5に連なる底部の流出口12とを有する。また液溜タンク10は、流入口11から流入する有機物含有液Sにより充満しない容量とし、タンク内に溜まる有機物含有液Sの液面とタンク頂部の流入口11との間に頂部空間13を設ける。液溜タンク10内に設けた頂部空間13により、供給路32内の有機物含有液Sと循環路5内の循環液Sとを液溜タンク10で一旦切断(縁切り)し、循環路5から供給路32への液漏れ又は液流出を防止することができる。   The liquid storage tank 10 in the illustrated example is maintained at the level of the liquid level L of the fermenter 1, and has a top inlet 11 connected to the supply path 32 for the organic matter-containing liquid S to be treated and a bottom connected to the circulation path 5. And an outlet 12. The liquid storage tank 10 has a capacity not filled with the organic substance-containing liquid S flowing from the inlet 11, and a top space 13 is provided between the liquid surface of the organic substance-containing liquid S stored in the tank and the inlet 11 at the top of the tank. . By the top space 13 provided in the liquid storage tank 10, the organic substance-containing liquid S in the supply path 32 and the circulating liquid S in the circulation path 5 are once cut (edge cut) in the liquid storage tank 10 and supplied from the circulation path 5. Liquid leakage or liquid outflow to the path 32 can be prevented.

好ましくは、液溜タンク10を密閉タンクとし、液溜タンク10内の頂部と発酵槽5内の上部空間4とを連通する均圧路18を設ける。発酵槽5内の上部空間4は発酵時の生成バイオガスGにより高圧となり得るが、液溜タンク10を密閉タンクとして均圧路18により液溜タンク10の頂部空間13と発酵槽1の上部空間4とを同圧とすれば、液溜タンク10内の液面レベルを常に発酵槽1内の液面レベルLと一致させることができる。ただし、液溜タンク10の密閉は本発明に必須ではなく、液溜タンク10は上述した頂部空間13を形成できるものであれば足り、例えば頂部開放タンクとしてもよい。   Preferably, the liquid storage tank 10 is a sealed tank, and a pressure equalizing path 18 is provided to communicate the top of the liquid storage tank 10 with the upper space 4 in the fermentation tank 5. The upper space 4 in the fermenter 5 can become high pressure due to the biogas G produced during fermentation. If the pressure is equal to 4, the liquid level in the liquid storage tank 10 can always coincide with the liquid level L in the fermenter 1. However, the sealing of the liquid storage tank 10 is not essential to the present invention, and the liquid storage tank 10 may be sufficient if it can form the top space 13 described above, and may be a top open tank, for example.

また図示例では、液溜タンク10の底部を循環路5のポンプ上流側5aより上方レベルに保持し、液溜タンク10の底部の流出口12を流出路17経由で循環路5のポンプ上流側5aに接続し、液溜タンク10内の有機物含有液Sを重力により循環路5のポンプ上流側5aに流下させている。液溜タンク10の配置レベルは図示例に限定されるものではなく、液溜タンク10と循環路5との間に適当なポンプを設けてもよい。ただし、有機物含有液Sが固形分を多量に含み高粘度である場合は、流出路17内を低圧で流下する有機物含有液Sによって流出路17が閉塞するおそれがある。   In the illustrated example, the bottom of the liquid storage tank 10 is held at a level higher than the pump upstream side 5 a of the circulation path 5, and the outlet 12 at the bottom of the liquid storage tank 10 is connected to the upstream side of the circulation path 5 via the outflow path 17. The organic substance-containing liquid S in the liquid storage tank 10 is caused to flow down to the pump upstream side 5a of the circulation path 5 by gravity. The arrangement level of the liquid storage tank 10 is not limited to the illustrated example, and an appropriate pump may be provided between the liquid storage tank 10 and the circulation path 5. However, when the organic substance-containing liquid S contains a large amount of solids and has a high viscosity, the outflow path 17 may be blocked by the organic substance-containing liquid S flowing down in the outflow path 17 at a low pressure.

望ましくは、図示例のように液溜タンク10の頂部を循環路5のポンプ下流側5bの下方レベルに保持し、液溜タンク10の頂部に循環路5のポンプ下流側5bから循環液Sを引き込む調節弁16付き引込路15を設ける。循環路5の循環液Sは発酵が進んでいるため有機物が90%程度分解されており、供給路32の被処理有機物含有液Sに比し粘土が1/10程度となっている。液溜タンク10において、供給路32の有機物含有液Sを循環路5のポンプ下流側5bから引き込んだ循環液Sと混合し、有機物含有液Sの粘度を下げて循環路5のポンプ上流側5aへ流下させることにより、流出路17の閉塞を防止する。流出路17に流下させる有機物含有液Sの粘度は、調節弁16による循環液Sの引き込み量により調整可能である。   Desirably, the top of the liquid storage tank 10 is held at a level below the pump downstream side 5b of the circulation path 5 as shown in the drawing, and the circulating liquid S is supplied to the top of the liquid storage tank 10 from the pump downstream side 5b of the circulation path 5. A service passage 15 with a control valve 16 is provided. Since the circulation liquid S in the circulation path 5 is fermented, the organic matter is decomposed by about 90%, and the clay is about 1/10 of the organic matter-containing liquid S in the supply path 32. In the liquid storage tank 10, the organic substance-containing liquid S in the supply path 32 is mixed with the circulating liquid S drawn from the pump downstream side 5b of the circulation path 5, and the viscosity of the organic substance-containing liquid S is lowered to increase the pump upstream side 5a of the circulation path 5. By flowing down, the outflow passage 17 is prevented from being blocked. The viscosity of the organic substance-containing liquid S flowing down to the outflow path 17 can be adjusted by the amount of the circulating liquid S drawn by the control valve 16.

被処理有機物含有液Sは、貯留タンク30から供給ポンプ31及び供給路32を介して適当な流量で液溜タンク10の頂部の流入口11へ導かれ、液溜タンク10内の頂部空間13に供給される。液溜タンク10において、有機物含有液Sの粘度を引込路15から引き込んだ循環液Sと混合することにより調節する。粘度調節後の有機物含有液Sを、底部の流出口12から流出路17経由で循環路5へ流下させる。例えば供給ポンプ31による供給流量を、流出路17への流下流量と引込路15からの循環液Sの引込量との関係を考慮して、例えば液溜タンク10内の液面がほぼ中間高さ位置となるように調整する。有機物含有液Sを液溜タンク10内の頂部空間13に供給することにより、たとえ供給ポンプ31の故障等が発生した場合等でも、液溜タンク10内の頂部空間13により、循環路5の有機物含有液Sが供給路32aへ逆流したりサイフォン現象により流入したりする事態を確実に防止できる。   The organic substance-containing liquid S to be treated is guided from the storage tank 30 through the supply pump 31 and the supply path 32 to the inlet 11 at the top of the liquid storage tank 10 at an appropriate flow rate, and enters the top space 13 in the liquid storage tank 10. Supplied. In the liquid storage tank 10, the viscosity of the organic substance-containing liquid S is adjusted by mixing with the circulating liquid S drawn from the drawing path 15. After the viscosity adjustment, the organic substance-containing liquid S is caused to flow down from the bottom outlet 12 to the circulation path 5 via the outlet path 17. For example, considering the relationship between the supply flow rate of the supply pump 31 and the flow rate of flow down to the outflow passage 17 and the amount of circulating fluid S drawn from the draw-in passage 15, for example, the liquid level in the liquid storage tank 10 is substantially intermediate Adjust to position. By supplying the organic substance-containing liquid S to the top space 13 in the liquid storage tank 10, even if a failure of the supply pump 31 occurs, the top space 13 in the liquid storage tank 10 causes the organic matter in the circulation path 5. It is possible to reliably prevent the contained liquid S from flowing back into the supply path 32a or flowing in due to a siphon phenomenon.

循環路5に供給された有機物含有液Sは、循環ポンプ6により循環路5内の循環液Sと共に発酵槽1の頂部の分散吐出器7へ送られる。図示例の循環路5にはポンプ下流側5bに熱交換器35が接続されており、循環路5内の循環液Sは熱交換器35において適当な高温流体Hとの熱交換により最適な発酵温度に加熱される。また、循環路5内の循環液Sの流量は複数の吐出口8へ均等に分配されるように調整されている。循環路5に供給された有機物含有液Sは循環液Sと共に熱交換器35において加熱されたのち複数の吐出口8から発酵槽1内の液面Fの全体に分散して投入される。有機物含有液Sを液面全体に分散して投入することにより、発酵槽1内における局所的な有機酸濃度の上昇やpHの低下を防止し、発酵槽1内の発酵処理を安定的に促進できる。   The organic substance-containing liquid S supplied to the circulation path 5 is sent to the dispersion discharger 7 at the top of the fermenter 1 together with the circulation liquid S in the circulation path 5 by the circulation pump 6. A heat exchanger 35 is connected to the downstream side 5b of the pump 5 in the circulation path 5 in the illustrated example, and the circulating liquid S in the circulation path 5 is optimally fermented by heat exchange with an appropriate high-temperature fluid H in the heat exchanger 35. Heated to temperature. Further, the flow rate of the circulating fluid S in the circulation path 5 is adjusted so as to be evenly distributed to the plurality of discharge ports 8. The organic substance-containing liquid S supplied to the circulation path 5 is heated together with the circulation liquid S in the heat exchanger 35, and then dispersed and fed from the plurality of discharge ports 8 to the entire liquid surface F in the fermenter 1. By dispersing and introducing the organic substance-containing liquid S over the entire liquid surface, a local increase in organic acid concentration and pH in the fermenter 1 are prevented, and the fermentation process in the fermenter 1 is stably promoted. it can.

こうして本発明の目的である「有機物含有液の安定した発酵処理を安全に維持できる有機物含有液の発酵槽投入方法及び処理装置」の提供を達成することができる。   Thus, it is possible to achieve the “objective method and apparatus for fermenting an organic substance-containing liquid that can safely maintain a stable fermentation treatment of the organic substance-containing liquid”, which is an object of the present invention.

図2は、本発明による有機物含有液Sの処理装置の他の実施例を示す。同図の液溜タンク10は中和剤や微量栄養剤等の分解処理添加剤の供給口28を有し、供給口28を添加剤輸送路27経由で添加剤タンク26に接続している。必要に応じて添加剤タンク26から液溜タンク10へ添加剤を供給することにより、有機物含有液Sと共に添加剤を発酵槽1の頂部の分散吐出器7へ送り、発酵槽1内の液面Fの全体に分散して投入することができる。添加剤輸送路27に適当な調節弁又はポンプを設けることにより、添加剤の添加量を調節することができる。   FIG. 2 shows another embodiment of the processing apparatus for the organic substance-containing liquid S according to the present invention. The liquid reservoir tank 10 in the figure has a supply port 28 for a decomposition treatment additive such as a neutralizing agent and a micronutrient, and the supply port 28 is connected to the additive tank 26 via an additive transport path 27. By supplying the additive from the additive tank 26 to the liquid storage tank 10 as necessary, the additive is sent to the dispersion discharge device 7 at the top of the fermenter 1 together with the organic substance-containing liquid S, and the liquid level in the fermenter 1 It is possible to disperse and put in the whole of F. By providing an appropriate control valve or pump in the additive transport path 27, the amount of additive added can be adjusted.

また図2の実施例では、発酵槽1と液溜タンク10とを開閉弁23付き異物排出路24により液面レベルLの高さで連結し、循環路5のポンプ下流側5bに切替弁20経由で異物タンク21を接続し、開閉弁23の開放と切替弁20の切り替えとにより発酵槽1の液面Fの浮遊異物(例えば、微細なプラスチック・発酵が困難な繊維類等)を液溜タンク10経由で異物タンク21に排出可能としている。この場合、均圧路18により液溜タンク10内の頂部空間13と発酵槽5内の上部空間4とを連通することにより、液溜タンク10内の液面レベルを発酵槽1内の液面レベルLと一致させることができる。異物排出路24は、様々な異物を排出できるように適当な管径とすることができ、好ましくは異物により閉塞しにくい十分大きな管径とする。通常の処理運転時は、開閉弁23を閉鎖すると共に切替弁20により循環ポンプ6と分散吐出器7とを接続する。必要に応じて適宜に開閉弁23を開放すると共に切替弁20により循環ポンプ6と異物タンク21とを接続し、発酵槽1の液面Fの浮遊異物を液溜タンク10、流出路17、循環路5のポンプ上流側5a、循環ポンプ6、循環路5のポンプ下流側5b、切替弁20及び異物搬送路22を介して異物タンク21へ搬送する。   In the embodiment of FIG. 2, the fermenter 1 and the liquid storage tank 10 are connected at a liquid level L by a foreign matter discharge passage 24 with an opening / closing valve 23, and the switching valve 20 is connected to the pump downstream side 5 b of the circulation passage 5. A foreign matter tank 21 is connected via the open valve 23 and the changeover valve 20 is switched to collect floating foreign matter (for example, fine plastics or fibers that are difficult to ferment) on the liquid surface F of the fermenter 1. It can be discharged to the foreign matter tank 21 via the tank 10. In this case, by connecting the top space 13 in the liquid storage tank 10 and the upper space 4 in the fermentation tank 5 through the pressure equalizing path 18, the liquid level in the liquid storage tank 10 is adjusted to the liquid level in the fermentation tank 1. It can be matched with level L. The foreign matter discharge path 24 can have an appropriate tube diameter so that various foreign matters can be discharged, and preferably has a sufficiently large tube diameter that is not easily blocked by foreign matter. During normal processing operation, the on-off valve 23 is closed and the circulation pump 6 and the dispersion discharger 7 are connected by the switching valve 20. The opening / closing valve 23 is opened as necessary, and the switching pump 20 connects the circulation pump 6 and the foreign matter tank 21 so that the floating foreign matter on the liquid surface F of the fermenter 1 can be circulated in the liquid storage tank 10, the outflow passage 17, and the circulation. It is conveyed to the foreign matter tank 21 through the pump upstream side 5 a of the path 5, the circulation pump 6, the pump downstream side 5 b of the circulation path 5, the switching valve 20 and the foreign matter conveyance path 22.

本発明の一実施例の説明図である。It is explanatory drawing of one Example of this invention. 本発明の他の実施例の説明図である。It is explanatory drawing of the other Example of this invention. 本発明で用いる分散配置の複数の吐出口の説明図である。It is explanatory drawing of the several discharge outlet of the dispersion | distribution arrangement | positioning used by this invention. 従来の有機物含有液の発酵槽投入方法の説明図である。It is explanatory drawing of the fermenter injection | throwing-in method of the conventional organic substance containing liquid. 発酵槽内の有機物含有液の攪拌方法の説明図である。It is explanatory drawing of the stirring method of the organic substance containing liquid in a fermenter.

符号の説明Explanation of symbols

1…発酵槽 2…微生物担体
3…抜出口 4…上部空間
5…循環路 5a…ポンプ上流側
5b…ポンプ下流側 6…循環ポンプ
7…分散吐出器 8…吐出口
9…頂壁 10…液溜タンク
11…流入口 12…流出口
13…頂部空間 14…取入口
15…引込路 16…調節弁
17…流出路 18…均圧路
20…切替弁 21…異物タンク
22…異物搬送路 23…開閉弁
24…異物排出路 26…添加剤タンク
27…添加剤輸送路 28…添加剤供給口
30…貯留タンク 31…供給ポンプ
32…供給路 33…投入口
35…熱交換器 36…脱硫機
45…攪拌機 46…攪拌翼
F…液面 G…バイオガス
H…高温流体 L…水位レベル
S…有機物含有液 W…処理水
DESCRIPTION OF SYMBOLS 1 ... Fermenter 2 ... Microorganism carrier 3 ... Outlet 4 ... Upper space 5 ... Circulation path 5a ... Pump upstream side
5b ... Downstream side of pump 6 ... Circulating pump 7 ... Dispersion discharger 8 ... Discharge port 9 ... Top wall 10 ... Liquid reservoir tank
11 ... Inlet 12 ... Outlet
13… Top space 14… Inlet
15 ... Retract 16 ... Control valve
17 ... Outflow 18 ... Pressure equalization
20 ... Switch valve 21 ... Foreign matter tank
22 ... Foreign matter transfer path 23 ... Open / close valve
24 ... Foreign matter discharge passage 26 ... Additive tank
27 ... Additive transport route 28 ... Additive supply port
30 ... Storage tank 31 ... Supply pump
32 ... Supply path 33 ... Inlet
35 ... Heat exchanger 36 ... Desulfurizer
45 ... Stirrer 46 ... Stirring blade F ... Liquid level G ... Biogas H ... High temperature fluid L ... Water level S ... Organic substance-containing liquid W ... Treated water

Claims (8)

分解微生物を保持し微生物との接触により有機物含有液を分解する発酵槽に槽内の有機物含有液を下部から抜き出し頂部に分散配置した複数の吐出口へ戻すポンプ付き外付け循環路を設け、発酵槽の液面レベル高さに底部が循環路と接続され且つ頂部空間が発酵槽内の上部空間と連通した液溜タンクを保持し、被処理有機物含有液を液溜タンクの頂部空間に取り入れ液溜タンクの底部から循環路に供給し且つ循環路の循環液と共に前記複数の吐出口から発酵槽内に投入してなる有機物含有液の発酵槽投入方法。 A fermenter that holds decomposed microorganisms and decomposes the organic matter-containing liquid by contact with the microorganisms is provided with an external circulation path with a pump that draws the organic matter-containing liquid in the tank from the bottom and returns it to a plurality of outlets that are dispersedly arranged at the top. Hold the liquid tank where the bottom is connected to the circulation path at the liquid level of the tank and the top space communicates with the upper space in the fermentation tank, and the liquid containing organic matter to be treated is taken into the top space of the liquid tank. A fermenter charging method of an organic substance-containing liquid, which is supplied to the circulation path from the bottom of the storage tank and is charged into the fermentation tank from the plurality of discharge ports together with the circulation liquid of the circulation path. 請求項の方法において、前記液溜タンクに分解処理添加剤を供給し、被処理有機物含有液を添加剤と共に発酵槽内に投入してなる有機物含有液の発酵槽投入方法。 The method according to claim 1 , wherein a decomposition treatment additive is supplied to the liquid storage tank, and the organic matter-containing liquid is added to the fermenter along with the additive to be treated together with the additive. 請求項1又は2の方法において、前記液溜タンクの頂部及び底部を循環路のポンプ下流側及び上流側に接続し、被処理有機物含有液を循環路のポンプ下流側から液溜タンク内に引き込んだ循環液と混合して循環路のポンプ上流側へ供給してなる有機物含有液の発酵槽投入方法。 3. The method according to claim 1 or 2 , wherein the top and bottom of the liquid storage tank are connected to the pump downstream side and upstream side of the circulation path, and the organic substance-containing liquid to be treated is drawn into the liquid storage tank from the pump downstream side of the circulation path. A fermenter charging method of an organic substance-containing liquid, which is mixed with a circulating liquid and supplied to the upstream side of the circulation path pump. 請求項の方法において、前記発酵槽と液溜タンクとを液面レベル高さの開閉弁付き異物排出路で連結し、前記循環路のポンプ下流側に切替弁経由で異物タンクを接続し、前記開閉弁の開放と前記切替弁の切り替えとにより発酵槽内の液面の浮遊異物を液溜タンク経由で異物タンクに排出してなる有機物含有液の発酵槽投入方法。 In the method according to claim 3 , the fermenter and the liquid reservoir tank are connected by a foreign matter discharge passage with an on-off valve having a liquid level, and a foreign matter tank is connected to the downstream side of the circulation passage via a switching valve. A method for charging an organic substance-containing liquid into a fermenter, in which floating foreign matter on a liquid surface in a fermenter is discharged to a foreign matter tank via a liquid storage tank by opening the on-off valve and switching the switching valve. 分解微生物を保持し微生物との接触により有機物含有液を分解する発酵槽、発酵槽内の有機物含有液を下部から抜き出し頂部に分散配置した複数の吐出口へ戻すポンプ付き外付け循環路、発酵槽の液面レベル高さに保持され且つ底部が循環路に接続された液溜タンク、液溜タンク内の頂部と発酵槽内の上部空間とを連通する均圧路、及び液溜タンクの頂部に接続された被処理有機物含有液の供給路を備えてなる有機物含有液の処理装置。 Fermenter that retains decomposed microorganisms and decomposes organic matter-containing liquid by contact with microorganisms, external circulation path with a pump that returns the organic matter-containing liquid in the fermentor from the bottom to a plurality of outlets dispersed and arranged at the top, fermenter A liquid tank that is maintained at a liquid level and has a bottom connected to the circulation path, a pressure equalizing path that communicates the top of the liquid tank and the upper space in the fermenter, and the top of the liquid tank A processing apparatus for an organic substance-containing liquid, comprising a connected supply path for an organic substance-containing liquid to be processed. 請求項の装置において、前記液溜タンクに分解処理添加剤の供給口を設けてなる有機物含有液の処理装置。 6. The apparatus for treating an organic substance-containing liquid according to claim 5 , wherein a supply port for a decomposition treatment additive is provided in the liquid storage tank. 請求項5又は6の装置において、前記液溜タンクの底部を循環路のポンプ上流側に接続する流出路、及び前記液溜タンクの頂部に循環路のポンプ下流側から循環液を引き込む調節弁付き引込路を設けてなる有機物含有液の処理装置。 7. The apparatus according to claim 5 or 6 , further comprising an outflow path connecting the bottom of the liquid reservoir tank to the upstream side of the pump of the circulation path, and a control valve for drawing the circulating liquid from the pump downstream side of the circulation path to the top of the liquid tank. The processing apparatus of the organic substance containing liquid which provides a drawing path. 請求項の装置において、前記循環路のポンプ下流側に切替弁経由で接続された異物タンク、及び発酵槽と液溜タンクとを液面レベル高さで連結する開閉弁付き異物排出路を設けてなる有機物含有液の処理装置。 8. The apparatus according to claim 7 , wherein a foreign substance tank connected via a switching valve to the downstream side of the pump of the circulation path, and a foreign substance discharge path with an on-off valve for connecting the fermentation tank and the liquid reservoir tank at a liquid level. An organic substance-containing liquid processing apparatus.
JP2006056347A 2006-03-02 2006-03-02 Fermenter charging method and processing apparatus for organic substance-containing liquid Expired - Fee Related JP4641271B2 (en)

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Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS58223496A (en) * 1982-06-18 1983-12-26 Mitsubishi Heavy Ind Ltd Methane fermentation tank
JPS60235695A (en) * 1984-04-19 1985-11-22 リンデ・アクチエンゲゼルシヤフト Anaerobic decomposition method and device for organic basic substance
JPS62118600U (en) * 1986-01-21 1987-07-28
JPH0312298A (en) * 1989-06-09 1991-01-21 Kajima Corp Aerobic and anaerobic combination type waste water treatment apparatus
JPH06296988A (en) * 1993-04-16 1994-10-25 Meidensha Corp Activated sludge treatment method and intermittent aeration activated sludge treating device
JPH07328387A (en) * 1994-06-15 1995-12-19 Kurita Water Ind Ltd Treatment of exhaust gas from anaerobic treatment apparatus
JP2002263683A (en) * 2001-03-13 2002-09-17 Mitsubishi Kakoki Kaisha Ltd Upward stream anaerobic processor
JP2006055823A (en) * 2004-07-23 2006-03-02 Nisso Engineering Co Ltd Method and apparatus for methane fermentation

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS58223496A (en) * 1982-06-18 1983-12-26 Mitsubishi Heavy Ind Ltd Methane fermentation tank
JPS60235695A (en) * 1984-04-19 1985-11-22 リンデ・アクチエンゲゼルシヤフト Anaerobic decomposition method and device for organic basic substance
JPS62118600U (en) * 1986-01-21 1987-07-28
JPH0312298A (en) * 1989-06-09 1991-01-21 Kajima Corp Aerobic and anaerobic combination type waste water treatment apparatus
JPH06296988A (en) * 1993-04-16 1994-10-25 Meidensha Corp Activated sludge treatment method and intermittent aeration activated sludge treating device
JPH07328387A (en) * 1994-06-15 1995-12-19 Kurita Water Ind Ltd Treatment of exhaust gas from anaerobic treatment apparatus
JP2002263683A (en) * 2001-03-13 2002-09-17 Mitsubishi Kakoki Kaisha Ltd Upward stream anaerobic processor
JP2006055823A (en) * 2004-07-23 2006-03-02 Nisso Engineering Co Ltd Method and apparatus for methane fermentation

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