JPH03114591A - Dynamic fixed bed bioreactor - Google Patents
Dynamic fixed bed bioreactorInfo
- Publication number
- JPH03114591A JPH03114591A JP1252666A JP25266689A JPH03114591A JP H03114591 A JPH03114591 A JP H03114591A JP 1252666 A JP1252666 A JP 1252666A JP 25266689 A JP25266689 A JP 25266689A JP H03114591 A JPH03114591 A JP H03114591A
- Authority
- JP
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- Prior art keywords
- carrier
- layers
- water
- fixed bed
- group
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 230000000813 microbial effect Effects 0.000 claims abstract description 7
- 239000000969 carrier Substances 0.000 claims description 11
- 238000010030 laminating Methods 0.000 claims description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 46
- 230000001580 bacterial effect Effects 0.000 abstract description 30
- 241000894006 Bacteria Species 0.000 abstract description 15
- 230000000694 effects Effects 0.000 abstract description 10
- 239000012528 membrane Substances 0.000 abstract description 10
- 230000035699 permeability Effects 0.000 abstract description 9
- 239000010802 sludge Substances 0.000 abstract description 8
- 238000000855 fermentation Methods 0.000 abstract description 7
- 230000004151 fermentation Effects 0.000 abstract description 6
- 238000011084 recovery Methods 0.000 abstract description 2
- 230000001629 suppression Effects 0.000 abstract description 2
- 230000000644 propagated effect Effects 0.000 abstract 1
- 210000004027 cell Anatomy 0.000 description 18
- 239000007787 solid Substances 0.000 description 8
- 238000011282 treatment Methods 0.000 description 8
- 238000007667 floating Methods 0.000 description 7
- 238000013019 agitation Methods 0.000 description 6
- 238000000034 method Methods 0.000 description 6
- 239000007788 liquid Substances 0.000 description 5
- 239000000945 filler Substances 0.000 description 4
- 238000011049 filling Methods 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- 239000002245 particle Substances 0.000 description 4
- 230000000717 retained effect Effects 0.000 description 4
- 230000008901 benefit Effects 0.000 description 3
- 238000004132 cross linking Methods 0.000 description 3
- 230000002829 reductive effect Effects 0.000 description 3
- 238000000926 separation method Methods 0.000 description 3
- 238000005406 washing Methods 0.000 description 3
- 239000002699 waste material Substances 0.000 description 3
- 241001465754 Metazoa Species 0.000 description 2
- 210000000170 cell membrane Anatomy 0.000 description 2
- 230000009849 deactivation Effects 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 238000002474 experimental method Methods 0.000 description 2
- 210000004709 eyebrow Anatomy 0.000 description 2
- 239000004744 fabric Substances 0.000 description 2
- 230000005484 gravity Effects 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 239000004745 nonwoven fabric Substances 0.000 description 2
- 238000012856 packing Methods 0.000 description 2
- 230000036961 partial effect Effects 0.000 description 2
- 229920003023 plastic Polymers 0.000 description 2
- 239000004033 plastic Substances 0.000 description 2
- 238000004062 sedimentation Methods 0.000 description 2
- 239000010865 sewage Substances 0.000 description 2
- 241000894007 species Species 0.000 description 2
- 238000003756 stirring Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 239000004743 Polypropylene Substances 0.000 description 1
- 241000700159 Rattus Species 0.000 description 1
- 230000001133 acceleration Effects 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 238000013459 approach Methods 0.000 description 1
- 238000003287 bathing Methods 0.000 description 1
- 230000001364 causal effect Effects 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- 230000005465 channeling Effects 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 230000006378 damage Effects 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000004945 emulsification Methods 0.000 description 1
- 235000011389 fruit/vegetable juice Nutrition 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 239000008103 glucose Substances 0.000 description 1
- 230000003100 immobilizing effect Effects 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 230000002779 inactivation Effects 0.000 description 1
- 239000000077 insect repellent Substances 0.000 description 1
- 230000001788 irregular Effects 0.000 description 1
- 239000010806 kitchen waste Substances 0.000 description 1
- 230000000670 limiting effect Effects 0.000 description 1
- 238000000465 moulding Methods 0.000 description 1
- 238000005498 polishing Methods 0.000 description 1
- 229920000728 polyester Polymers 0.000 description 1
- -1 polypropylene Polymers 0.000 description 1
- 229920001155 polypropylene Polymers 0.000 description 1
- 229920002635 polyurethane Polymers 0.000 description 1
- 239000004814 polyurethane Substances 0.000 description 1
- 229920000915 polyvinyl chloride Polymers 0.000 description 1
- 239000004800 polyvinyl chloride Substances 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 238000010008 shearing Methods 0.000 description 1
- 230000006641 stabilisation Effects 0.000 description 1
- 238000011105 stabilization Methods 0.000 description 1
- 239000004575 stone Substances 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
- 238000009280 upflow anaerobic sludge blanket technology Methods 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Abstract
Description
【発明の詳細な説明】
産業上の利用分野
この発明は、水処理などの多量の液体を流通させる発酵
器の高効率化のために2部分的可動担体を配備した固定
床式発酵器に関する。DETAILED DESCRIPTION OF THE INVENTION Field of the Invention The present invention relates to a fixed bed fermenter equipped with two partially movable carriers for increasing the efficiency of a fermenter that passes a large amount of liquid, such as for water treatment.
従来技術とその問題点
固定床は、発酵菌を多量にバイオリアクター内に保持し
高濃度化することにより、目的の反応を加速することに
役立ち、また菌体の洗脱を防止して汚泥返送なしで菌体
濃度を一層レベルに保ち、バイオリアクターの安定化に
貢献する。さらに濾床として固形物や可溶物の一部を捕
捉・吸着することによる水の浄化促進機能などが評価さ
れ、近時その使用が盛んになって・いる。Conventional technology and its problemsFixed beds help accelerate the desired reaction by retaining a large amount of fermentation bacteria in the bioreactor and increasing their concentration, and they also prevent bacterial cells from being washed out and prevent sludge from being returned. This contributes to the stabilization of the bioreactor by keeping the bacterial cell concentration at a higher level. Furthermore, as a filter bed, it has been highly evaluated for its ability to promote water purification by capturing and adsorbing a portion of solids and soluble substances, and its use has recently become popular.
特に、メタン発酵菌のように生育速度の低い菌種では、
菌増殖量を画法出量が上廻り、洗脱失活の恐れがあり、
それを防ぐためバイオリアクターが巨大化し易い。そこ
で、菌体を固定化することにより水滞留時間(F(RT
)と固形物滞留時間(SRT)とを切り離し、SRTの
みを延長することにより装置の小型化が可能になる。菌
体の担体への付着・繁殖による往物膜の発注と、担体の
間隙における浮遊菌の捕捉・保持により、一般の浮遊床
の10〜100倍の菌体量をバイオリアクター内に保持
できる。In particular, for bacterial species with low growth rates such as methane-fermenting bacteria,
There is a risk that the amount of bacteria produced by the method will exceed the amount of bacterial growth, resulting in washing and deactivation.
To prevent this, bioreactors tend to grow large. Therefore, by immobilizing the bacterial cells, water retention time (F(RT)
) and the solids residence time (SRT), and by extending only the SRT, it is possible to downsize the device. By ordering a waste film through the adhesion and propagation of bacterial cells to the carrier, and by capturing and retaining floating bacteria in the gaps between the carriers, it is possible to retain 10 to 100 times the amount of bacterial cells in the bioreactor compared to a general floating bed.
しかし、固定床方式には、菌体付着量を増大させるため
に担体の付着表面積を拡大し微生物膜を肥厚させるので
、必然的に目詰りを招き易い欠点がある。However, the fixed bed system has the disadvantage that it inevitably tends to cause clogging because the surface area of the carrier to which it adheres is expanded and the microbial film thickens in order to increase the amount of bacteria attached.
局部的な目詰りはバイオリアクター内に死容積をもたら
し、有効反応空間を減少させ目詰り部位の菌体の失活・
死滅を招く。同時に、他の部分に偏流して水路のショー
トバスやチャンネリングを引起し、結果的に未処理液の
流出や局所流速増大による生物膜剥離・菌の洗脱を招く
。古典的な固定床では、しばしば死空間は1/3にも達
し、そこに固形浮遊物が詰まるので、充填床はrSS
(固形浮遊物)の多い水に不適」とされてきた( J、
C。Local clogging causes dead volume within the bioreactor, reducing the effective reaction space and causing inactivation and deactivation of bacterial cells in the clogging area.
cause death. At the same time, the flow is biased to other parts, causing short bathing and channeling of the waterway, resulting in outflow of untreated liquid and increased local flow velocity, resulting in detachment of biofilm and washing out of bacteria. In classical fixed beds, the dead space often reaches as much as 1/3 and is clogged with solid suspended matter, so packed beds are not suitable for rSS.
(J,
C.
Youug、”The Anaerobic Filt
er for Waste Treat−men t″
、 Proc、22nd、lnd、Waste Con
f、Purdne Univ、。Youug, “The Anaerobic Filt”
er for Waste Treat-ment''
, Proc, 22nd, lnd, Waste Con
f, Purdne Univ.
No、129.p、559.1987年)。No, 129. p. 559.1987).
全面的な目詰りはバイオリアクターの通水抵抗を増大し
て運転の圧力損失を招き、遂にはりアクタ−の閉塞をも
たらす。Complete clogging increases the water flow resistance of the bioreactor, leading to pressure loss during operation, and eventually leading to blockage of the bioreactor.
技術的課題
菌体の高濃度化と目詰り・偏流抑制とを両立させること
は、固定床バイオリアクターの最大の基本的な技術課題
である。Technical Issues The most fundamental technical issue for fixed-bed bioreactors is to achieve both high bacterial cell concentration and suppression of clogging and drift.
図1にみられる充填床では、微生物増殖汚泥による架橋
が起き易く、その結果目詰りし易い。その因果関係を連
鎖的に示すと次のようになる。In the packed bed shown in FIG. 1, crosslinking due to microbial growth sludge is likely to occur, resulting in clogging. The causal relationship is shown as follows.
これらの各種対策とその技術的課題を以下に列挙する。These various measures and their technical challenges are listed below.
(イ)充填率による調整、充填率あるいは空隙率による
対策自由度は少ない。通常1石・セラミック充填材では
空隙率50±10%、薄片状あるいは中空成型の容易な
プラスチック充填材では空隙率95%前後の固定床が標
準である。それより疎にすれば浮遊床に近くなり、床固
着の危険性は減少するが菌体膜面積が不足する。逆に、
固定床の長所、菌体密度の向上を強化するため、より密
にすれば閉塞を起こし易くなる。(b) There is little flexibility in adjusting the filling rate and taking measures based on the filling rate or porosity. Normally, a fixed bed with a porosity of 50±10% is standard for single-stone ceramic fillers, and a porosity of around 95% for plastic fillers that are easily formed into flakes or hollow molding. If it is made more sparse than this, it will resemble a floating bed and the risk of sticking to the floor will be reduced, but the bacterial membrane area will be insufficient. vice versa,
In order to enhance the advantage of a fixed bed, which is the improvement in bacterial cell density, if the bed is made denser, it becomes more likely to cause blockage.
どの場合でも担体相互の間隔が、1〜3mm以下に接近
すると菌体膜成長とともに接着、閉塞を起こし易くなる
ので、それが制限要因となり充填密度は決まってしまう
。菌体保持量を増加し、同時に通水性を確保するため、
「目詰り直前の状態で操業する」のが、固定床の処理効
率を最大化するコツであると言える。In any case, if the distance between the carriers approaches 1 to 3 mm or less, adhesion and occlusion are likely to occur as the bacterial cell membrane grows, and this becomes a limiting factor and determines the packing density. In order to increase the amount of bacteria retained and at the same time ensure water permeability,
It can be said that the trick to maximizing the treatment efficiency of fixed beds is to ``operate in a state just before clogging.''
(ロ)充填材の形状による調整、充填材形状は、球状・
浮き玉・ハニカム状・板状・多孔板・網状・布状・ひも
状・貝ガラ状・不定形など多様な試みがあり、固形物捕
捉能にかなりの差があるが、上述の矛盾を打開するに至
っていない。固形物捕捉能としては1重力または水流に
よる慣性力に対して種々の傾斜角を持つ傾斜板を用いて
、固形物分離能を測定した実験(白神直弘ら、化工論集
。(b) Adjustment by the shape of the filler, the shape of the filler may be spherical or
There have been various attempts such as floating balls, honeycomb shapes, plate shapes, perforated plates, net shapes, cloth shapes, string shapes, shell shapes, irregular shapes, etc., and although there are considerable differences in solid matter trapping ability, the above-mentioned contradiction has been overcome. I haven't reached the point where I can. As for the solid matter trapping ability, experiments were carried out to measure the solid matter separation ability using inclined plates having various tilt angles with respect to 1 gravity or inertial force due to water flow (Naohiro Shirakami et al., Kako Ronshuu).
1987.1.p、86)によって傾斜角が0°〈20
°〈30゜〈45°となるにつれて分離が良ぐなること
が知られている。また、傾斜角を変えた充填材を用いた
濾床の水処理実験(T、 Richardsら、 J
W CF、 、58.7゜774、1986年)では、
水流にffして直角材では付着物が増加し、同時に短絡
部が多発し、傾斜角0〜90°に分布しているランダム
充填材では部分渦を生じ、結局SRTが短縮し1両者と
も45°〜60゜傾斜材に比べてBOD除去能力が低下
した。1987.1. p, 86), the inclination angle is 0°〈20
It is known that the separation becomes better as the angle increases from °<30°<45°. In addition, water treatment experiments using filter beds using packing materials with different inclination angles (T, Richards et al., J
W CF, 58.7°774, 1986),
Due to the flow of water, the amount of deposits increases in right-angled materials, and at the same time, short circuits occur frequently, and partial vortices occur in random filling materials distributed at an inclination angle of 0 to 90°, resulting in a shortened SRT and 45% for both. The BOD removal ability was lower than that of the tilted material at 60° to 60°.
これらの結果から見て、通水閉塞と偏流短絡という反対
の現象は同伴して現れ易く、いかにして均一化した通水
条件を作り出し、保持菌体高濃度でも閉塞し難い固定床
を得るかが課題である。From these results, the opposite phenomena of water flow blockage and uneven flow short circuit tend to occur together, so how can we create uniform water flow conditions and obtain a fixed bed that is difficult to block even with a high concentration of retained bacteria? is the issue.
(ハ)並行床、充填床をハニカム状の並行床(図2)と
すれば、目詰り性は減少し、偏流も抑制される。しかし
菌体保留力はいちじるしく減退してワンスルーの浮遊床
に近い性能になり、固定床の良さである菌の高密度化に
よる発酵の安定性や汚泥返送不要などのメリットが失わ
れる。(c) Parallel beds: If the packed bed is a honeycomb-shaped parallel bed (FIG. 2), clogging is reduced and drifting is also suppressed. However, the ability to retain bacteria is significantly reduced, resulting in performance similar to that of a one-through floating bed, and the advantages of a fixed bed, such as fermentation stability due to high bacterial density and no need to return sludge, are lost.
(ニ)通水速度による調整1通水速度により菌体架橋の
破壊、水路再生は可能である。嫌気性固定床では一般に
0.2〜1 m/時の上向流であるが、さらに加速する
と空隙にある菌体のフロックなどが脱出し、次に菌体膜
の剥離が起こる。ちなみに、下水の最初沈澱池のSS沈
降速度は、はぼ10m/時未満である。(d) Adjustment by water flow rate 1. It is possible to destroy bacterial cell bridges and regenerate water channels by changing the water flow rate. In an anaerobic fixed bed, the upward flow is generally 0.2 to 1 m/hour, but if the flow is further accelerated, bacterial flocs in the voids will escape, and then the bacterial membrane will peel off. Incidentally, the SS sedimentation speed of the sewage primary sedimentation tank is approximately less than 10 m/hour.
間欠流、脈動流等による閉塞の打開は、当然試みられる
技術である。しかし、菌体分離膜などの膜流速(表面を
剥離清掃するため)は1m/秒以上で、一般の通水速度
の数桁上になる。そのような高速では、固定床破壊の可
能性が高く、実際、間欠通水加速は、閉塞部を打開する
よりも通水短絡部を選択的に拡大する弊害を免れない。Breaking the blockage using intermittent flow, pulsating flow, etc. is a technique that can naturally be attempted. However, the flow rate of membranes such as bacterial cell separation membranes (for stripping and cleaning the surface) is 1 m/sec or more, which is several orders of magnitude higher than the general water flow rate. At such high speeds, there is a high possibility of fixed bed failure, and in fact, intermittent water flow acceleration inevitably has the disadvantage of selectively expanding water flow short circuits rather than breaking through blockages.
(ホ)流動床化、流動床は担体の密度や粒径を調整する
ことで、流速を15〜30m/時にとることができ、か
なり高濃度でも閉塞を防ぐ条件が可能である。嫌気性流
動床では菌体膜の剥離を避ける限界流速としてほぼ10
m/時をとる(L、 G、M、Gorris、 eta
l、+Biotechno1.Bioeng、+ 33
+ 687+1989年)。また菌体自身を担体とした
流動床の一種であるUASB法(グラニユール型で約1
m/時、フロック型で約0.2m/時の上向流)も菌体
高濃度化でかなりの成功をおさめている。(e) Fluidized bed: By adjusting the density and particle size of the carrier, the flow rate of the fluidized bed can be set to 15 to 30 m/hour, making it possible to create conditions that prevent clogging even at fairly high concentrations. In an anaerobic fluidized bed, the critical flow rate to avoid detachment of bacterial membranes is approximately 10
m/time (L, G, M, Gorris, eta
l, +Biotechno1. Bioeng, +33
+687+1989). In addition, the UASB method, which is a type of fluidized bed using the bacterial cells themselves as carriers (approximately 1
(upward flow of about 0.2 m/hour for floc type) has also been quite successful in increasing bacterial cell concentration.
しかし、流動床はフィルター性能が低く、浮遊菌体の捕
捉・SSの捕捉は期待し難い。さらにメタン発酵では発
生気泡が担体や菌膜に付着して担体総比重が軽くなり、
担体の浮上逸出をも併発し易い。流出抑制のために流速
を下げると、担体粒子が粘着(プラッギング)を起こす
。そこで流速を上げれば塊が解けぬうちに局所的吹き抜
けを起こし易い。処理効率を高めるためには、保持菌体
量が30KgVSS/m3以上にしたいので、この種の
粘着トラブルは頻発し易くなる。However, the fluidized bed has low filter performance and is difficult to expect to capture floating microbial cells and SS. Furthermore, in methane fermentation, the generated air bubbles adhere to the carrier and bacterial membrane, reducing the total specific gravity of the carrier.
This also tends to cause the carrier to float up and escape. When the flow rate is lowered to suppress outflow, carrier particles cause sticking (plugging). Therefore, if the flow velocity is increased, local blow-throughs are likely to occur before the lumps dissolve. In order to increase treatment efficiency, it is desired that the amount of retained bacterial cells be 30 KgVSS/m3 or more, so this type of adhesion problem is likely to occur frequently.
固定床を一部分可動化して閉塞防止を図ることができ、
プラスティック製ストリップを多数、槽内に懸垂して嫌
気発酵を行う方法(狡開304734および狭量372
8031.1989年)も提案されているが、空隙率が
大きく担体付着量は低レベルになる。Part of the fixed bed can be moved to prevent blockages.
A method of performing anaerobic fermentation by suspending a large number of plastic strips in a tank (Shukai 304734 and Nasai 372)
8031.1989) has also been proposed, but the porosity is large and the amount of carrier adhesion is at a low level.
(へ)ガスリフトによる発酵槽の攪拌、架橋の破壊と通
水性の回復に貢献できるが、一般にガス塊は大水路を選
択的に通過し、むしろ短絡・偏流を促進して好ましくな
い。(f) Gas lift can contribute to agitation of the fermenter, destruction of bridges, and restoration of water permeability, but in general, gas masses selectively pass through large waterways, which is undesirable as it rather promotes short circuits and drifting.
(ト)攪拌翼による攪拌、閉塞しかかった固定床部分に
はほとんど影響を与えず、むしろ局部的剪断力が強いた
め、偏流部において菌体フロックの解体・乳化を促進す
るのみで好ましくない。(g) Stirring by stirring blades has little effect on the fixed bed section, which is about to become clogged, and rather has a strong local shearing force, which is undesirable because it only promotes the disintegration and emulsification of bacterial flocs in the drifting section.
以上述べたように、従来技術のままでは問題解決困難で
、部分的に流動床の長所を取り入れた固定床を作り、閉
塞寸前の高負荷のままで閉塞だけを打破することが望ま
れる。As mentioned above, it is difficult to solve the problem using conventional techniques, and it is desirable to create a fixed bed that partially incorporates the advantages of a fluidized bed to break only the blockage while maintaining the high load on the verge of blockage.
本発明の対策技術の特徴
そこで、理想的な発酵器としては、■より多くの菌体を
保持しく菌体付着可能な有効表面積が大きい担体)、■
なるべく多くの可処理物質(SSを含む)をも捕捉しく
通水方向に対して大きな傾斜角を持つ担体)、■閉塞や
通水短絡が起き難く(空隙が多くかつ均一)、■閉塞直
前に付着固形物を自在に除去できる(清掃に適した担体
配置が必要)、■除去手段として架橋部を破壊し通水短
絡部を選択的に拡張しない、という諸要求を満たすもの
・が望まれる。Features of the countermeasure technology of the present invention Therefore, as an ideal fermenter, (1) a carrier that can hold more bacteria and has a large effective surface area to which bacteria can attach;
(carrier with a large inclination angle to the water flow direction to capture as much processable substances as possible (including SS)), ■ hard to cause blockage or water flow short circuit (many and uniform voids), ■ immediately before blockage. What is desired is a method that satisfies the following requirements: 1. The removal means does not destroy the bridge and selectively expand the water flow short-circuit.
本発明では、■と■とに重点的に着目し、これらのニー
ズをより多く満たす手段を考案した。すなわち、微生物
膜付着用の担体を層状あるいは膜状として、この担体を
積層して構成するバイオリアクターにおいて、それらの
担体を一層おきに連結し、この連結層を一体として動揺
させることにより、眉間の架橋部を一斉に破壊し通水性
を回復させるものである。In the present invention, we focused on (1) and (2) and devised means to more fully satisfy these needs. In other words, in a bioreactor constructed by stacking carriers for attaching microbial membranes in layers or membranes, the carriers are connected every other layer and the connected layers are agitated as a unit, so that the area between the eyebrows can be removed. It destroys the crosslinked parts all at once and restores water permeability.
微生物増殖汚泥による架橋が発達した時点で、この交互
連結層を層面に平行に動揺させれば、すべての眉間の架
橋は切断され、水路の閉塞は打開される。通水短絡部を
選択的に拡張しないため偏流も解消される。When the crosslinks caused by the microorganism-proliferated sludge have developed, if this alternating connection layer is shaken parallel to the layer plane, all the crosslinks between the eyebrows will be severed and the blockage of the waterway will be overcome. Unbalanced flow is also eliminated because the water flow short-circuit portion is not selectively expanded.
図3に、その簡単な担体配置を示す。担体層A11.A
2、A3、・・・は固定されており、担体層B8、B2
、B3、・・・は相互に連結されており、菌体やSSが
担体4群やB群の表面に着生・堆積しく発酵槽活動期)
、やがて種間を埋めて通水抵抗が増大してきた時(閉塞
部)、連結担体758群をずらすように動かす(通水性
回復期)。FIG. 3 shows a simple carrier arrangement. Carrier layer A11. A
2, A3, ... are fixed, and the carrier layers B8, B2
, B3, ... are interconnected, and bacterial cells and SS are attached and deposited on the surface of carrier group 4 and B group (fermenter active phase)
When the space between the seeds is eventually filled and the resistance to water passage increases (occlusion area), the group of connecting carriers 758 is moved to shift (water permeability recovery period).
動かす距離はA−B層間隔の1〜3倍でよく、それより
大きくずらしても架橋打開の効果は同程度である。連結
担体層B群を動揺させる方向は、通水方向に平行でも通
水方向に直角でもよいが、動揺で遊離した固形物を速や
かに排出するためには、通水方向にそって動かす方がよ
り好ましい。The moving distance may be 1 to 3 times the A-B layer spacing, and even if the distance is moved larger than that, the effect of breaking the crosslinking will be the same. The direction in which the connected carrier layer group B is agitated may be parallel to the water flow direction or perpendicular to the water flow direction, but in order to quickly discharge the solid matter liberated by the agitation, it is better to move it along the water flow direction. More preferred.
動揺回数は1〜3回で充分で、それより回数を増やして
も架橋打開の効果は同程度である。動揺期間の通水速度
は、0〜10m/時で自由であるが、洗い出し効果を高
めるには通常の固定床運転状況の通水速度に対して1〜
2倍の範囲が好ましい。It is sufficient that the number of agitation is 1 to 3 times, and even if the number of agitation is increased, the effect of breaking the crosslinking will be the same. The water flow rate during the agitation period can be freely set between 0 and 10 m/hour, but to enhance the washing effect, the water flow rate should be set at 1 to 10 m/hour compared to the water flow rate under normal fixed bed operation.
A range of 2 times is preferred.
担体は、層または膜を形成できるものは何でもよい。布
、不織布、網、金網、多孔板、枠に張った糸、格子枠な
ど、菌体の付着可能な表面が充分に確保される担体であ
れば、同様である。ただし機械的動揺に耐える強度は必
要である。The carrier may be anything that can form a layer or film. The same applies to any carrier that can provide a sufficient surface to which microbial cells can adhere, such as cloth, nonwoven fabric, mesh, wire mesh, perforated plate, thread stretched over a frame, and lattice frame. However, it must have the strength to withstand mechanical vibration.
発明の効果
この発明は、担体の集合体を閉塞時に動かすことによっ
て担体間の閉塞を打開し、通水性を回復させるので、安
定に発酵器を運転できる。Effects of the Invention This invention breaks the blockage between the carriers and restores water permeability by moving the aggregate of the carriers at the time of blockage, so that the fermenter can be operated stably.
また、菌体やSS保持量を増強するためには、担体の有
効表面を増大させたい(担体比表面積は通常約60m2
/m3で、表面付着菌と間隙浮遊菌の比はおよそ半々。In addition, in order to increase the amount of bacterial cells and SS retained, it is necessary to increase the effective surface of the carrier (the specific surface area of the carrier is usually about 60 m2).
/m3, and the ratio of surface-attached bacteria to interstitial floating bacteria is approximately 50-50.
担体比表面積は、最高200〜300m2/m3まで可
能で、表面付着菌の比率は圧倒的になる)が、比表面積
の大きいものほど菌体膜の発達により閉塞し易い。従来
、閉塞障害のため担体比表面積を制限してきたが、本発
明によりその制約は解消される。The specific surface area of the carrier can be up to 200 to 300 m2/m3, and the ratio of bacteria adhering to the surface becomes overwhelming); however, the larger the specific surface area, the more likely it is to be blocked by the development of a bacterial cell membrane. Conventionally, the specific surface area of the carrier has been limited due to obstruction, but the present invention eliminates this limitation.
固定床発酵器の運転においては、立上がりで次第に活性
が向上し、菌体膜の発達や処理対象SSの集積とともに
活性は極限に達したのち、通水抵抗の増大・部分的閉塞
と偏流の発達とともに発酵器の活性は低下する。本発明
を適用すれば、常に発酵器を最高活性付近の運転状況に
維持することが可能になる。During operation of a fixed bed fermenter, the activity gradually increases at the start of operation, and after the activity reaches its limit with the development of bacterial membranes and the accumulation of SS to be treated, water flow resistance increases, partial blockage, and uneven flow develop. Along with this, the activity of the fermenter decreases. By applying the present invention, it becomes possible to always maintain the fermenter in an operating state near the maximum activity.
実施例
実施例1
発酵槽として、ポリ塩化ビニルW4(防虫網用)を張っ
た枠を20枚g層し、−枚置きに槽に固定した枠(A層
)と連結して可動化した枠(B層)とを充填した101
00xlOOxlO00(縦x横X高さ)のガラス製角
槽を数個連結して構成した。流入水には、BOD250
ppm、 S S400ppmのモデル下水を使い、嫌
気性種汚泥とともに上向きに約0.3m/時で送入し、
35°Cで一月間馴養した。Examples Example 1 As a fermentation tank, 20 frames covered with polyvinyl chloride W4 (for insect repellent net) were layered, and every other frame was connected to a frame (layer A) fixed to the tank to make it movable. (B layer)
It was constructed by connecting several square glass vessels measuring 00xlOOxlO00 (length x width x height). Inflow water has a BOD of 250
ppm, S S Using model sewage of 400 ppm, it was sent upward at a rate of about 0.3 m/hour along with anaerobic species sludge.
The animals were acclimated for one month at 35°C.
水滞留時間(HRT)12時間での処理水BOD除去率
はしだいに上昇して60χに達したが、閉塞が甚だしく
、通水不能となった。閉塞時の槽内状況を観察すると、
空隙部はおおむね菌体やSSで埋まり、所々に発生ガス
溜まりが現れている。The BOD removal rate of the treated water at a water retention time (HRT) of 12 hours gradually increased and reached 60χ, but the blockage was so severe that water could not be passed. Observing the situation inside the tank at the time of blockage,
The voids are mostly filled with bacterial cells and SS, and gas pockets appear here and there.
この状態で、B層を上下に10mm、 3回動揺させ
ると空隙部の水路が再生しガス溜まりも消失し、通水性
が回復し、処理能力も復活した。処理水質は払出し汚泥
のために一時的に濃厚になるが、すぐ高いBOD除去率
に戻る。払出し汚泥は静置沈降して、固形物を廃棄し、
上澄液は流入水へ戻して処理した。In this state, when Layer B was shaken up and down by 10 mm three times, the water channels in the voids were regenerated, gas pockets disappeared, water permeability was restored, and treatment capacity was restored. The quality of the treated water temporarily becomes thick due to the discharged sludge, but it quickly returns to a high BOD removal rate. The discharged sludge is allowed to settle and solids are disposed of.
The supernatant liquid was returned to the influent water for treatment.
実施例2
発泡ポリウレタンをポリエステル不織布で補強した厚さ
7mmの板を、実施例1と同様に10枚積層−配置して
発酵槽を構成した。流入水には、ペプトン・グルコース
液(B OD900ppm)で調製した無SS性のモデ
ル廃水を使い、実施例1と同様に2週間馴養した。Example 2 A fermentation tank was constructed by laminating and arranging ten 7 mm thick plates made of foamed polyurethane reinforced with polyester nonwoven fabric in the same manner as in Example 1. SS-free model wastewater prepared with a peptone-glucose solution (B OD 900 ppm) was used as the inflow water, and the animals were acclimatized for two weeks in the same manner as in Example 1.
HRT 6時間で、処理水BOD除去率はしだいに上昇
して90χに達したが、閉塞が甚だしく15日後には通
水不能となった。After 6 hours of HRT, the BOD removal rate of the treated water gradually increased and reached 90χ, but the blockage was so severe that it became impossible to pass water after 15 days.
この状態で、B層を上下に7闘、2回動揺させると空隙
部の水路が再生し通水性が回復し、処理能力も復活した
。In this state, when Layer B was shaken up and down seven times and twice, the water channels in the voids were regenerated, water permeability was restored, and treatment capacity was restored.
実施例3
表面を磨き砂で荒らしたポリプロピレン波板に10mm
間隔で直径3mmの穴を一面に開けた多孔板を、実施例
1と同様に25枚積層配置して発酵槽を構成した。流入
液には、台所生ゴミ(B OD4000ppm)を粒径
1mm以下に破砕した高SS液である。最初はSSを除
いた汁液のみを供給して実施例1と同様に3週間馴養し
た。全波をHRT 3日で供給を開始すると、処理水B
OD除去率は60χに達したが、4日後には閉塞して通
水不能となった。Example 3 A 10 mm thick polypropylene corrugated plate whose surface was roughened with polishing sand
A fermenter was constructed by stacking 25 perforated plates with holes of 3 mm in diameter at intervals in the same manner as in Example 1. The inflow liquid is a high SS liquid obtained by crushing kitchen waste (B OD 4000 ppm) into particles with a particle size of 1 mm or less. At first, only the juice without SS was supplied to the rats, and they were acclimatized for 3 weeks in the same manner as in Example 1. When full-wave HRT supply starts in 3 days, treated water B
The OD removal rate reached 60χ, but after 4 days it became clogged and water could not pass through.
この状態で、B層を上下に10mm、 3回動揺させ
ると空隙部の水路が再生し通水性が回復するが、半日後
に閉塞した。そこで半日に一回づつ、動揺処理を繰り返
し、BOD除去率60χの処理能力を維持し続けること
ができた。In this state, when Layer B was shaken up and down by 10 mm three times, the water channels in the voids were regenerated and water permeability was restored, but they were blocked after half a day. Therefore, by repeating the agitation process once every half day, we were able to maintain a processing capacity with a BOD removal rate of 60χ.
図1 従来型固定床である充填床 1:入水管 2:排水管 3:排ガス管図2 並行床。 5:ハニカム管 図3 部分可動化した固定床 A1、A2、A3:固定担体層 BいB2、B3:可動担体層 4:充填物 Figure 1 Packed bed, which is a conventional fixed bed 1: Inlet pipe 2: Drain pipe 3: Exhaust gas pipe Diagram 2 Parallel floor. 5: Honeycomb tube Figure 3 Partially movable fixed floor A1, A2, A3: Fixed carrier layer B2, B3: Movable carrier layer 4: Filling
Claims (1)
クターにおいて、かつ層状の担体を積層して構成するバ
イオリアクターにおいて、それらの担体を一層おきに連
結し、この連結層を一体として動揺させることを特徴と
する固定床バイオリアクター。In a bioreactor that uses a carrier to which a microbial film is attached as a fixed bed, and in a bioreactor that is constructed by laminating layered carriers, the carriers are connected every other layer and the connected layers are agitated as a unit. Fixed bed bioreactor.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP1252666A JPH03114591A (en) | 1989-09-27 | 1989-09-27 | Dynamic fixed bed bioreactor |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP1252666A JPH03114591A (en) | 1989-09-27 | 1989-09-27 | Dynamic fixed bed bioreactor |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH03114591A true JPH03114591A (en) | 1991-05-15 |
Family
ID=17240541
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP1252666A Pending JPH03114591A (en) | 1989-09-27 | 1989-09-27 | Dynamic fixed bed bioreactor |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH03114591A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100511864B1 (en) * | 2002-08-16 | 2005-09-02 | 주식회사 삼경기술용역단 | Humus holder |
Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS53117258A (en) * | 1977-03-23 | 1978-10-13 | Mitsubishi Heavy Ind Ltd | Submerged filter bed apparatus |
-
1989
- 1989-09-27 JP JP1252666A patent/JPH03114591A/en active Pending
Patent Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS53117258A (en) * | 1977-03-23 | 1978-10-13 | Mitsubishi Heavy Ind Ltd | Submerged filter bed apparatus |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100511864B1 (en) * | 2002-08-16 | 2005-09-02 | 주식회사 삼경기술용역단 | Humus holder |
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