JPH04265129A - Filtration system - Google Patents
Filtration systemInfo
- Publication number
- JPH04265129A JPH04265129A JP2648491A JP2648491A JPH04265129A JP H04265129 A JPH04265129 A JP H04265129A JP 2648491 A JP2648491 A JP 2648491A JP 2648491 A JP2648491 A JP 2648491A JP H04265129 A JPH04265129 A JP H04265129A
- Authority
- JP
- Japan
- Prior art keywords
- filtration
- membrane
- flow
- dead
- backwashing
- 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
- 238000001914 filtration Methods 0.000 title claims abstract description 123
- 239000012528 membrane Substances 0.000 claims abstract description 94
- 239000012530 fluid Substances 0.000 claims abstract description 60
- 238000011001 backwashing Methods 0.000 claims abstract description 36
- 239000007788 liquid Substances 0.000 claims abstract description 36
- 239000012466 permeate Substances 0.000 claims description 14
- 238000004140 cleaning Methods 0.000 claims description 13
- 230000004907 flux Effects 0.000 abstract description 33
- 238000000926 separation method Methods 0.000 abstract description 12
- 238000011084 recovery Methods 0.000 abstract description 10
- 238000005406 washing Methods 0.000 abstract description 6
- 238000000746 purification Methods 0.000 abstract description 4
- 239000000463 material Substances 0.000 abstract 4
- 239000007787 solid Substances 0.000 description 34
- 238000009295 crossflow filtration Methods 0.000 description 12
- 238000000034 method Methods 0.000 description 11
- 230000001580 bacterial effect Effects 0.000 description 10
- 239000000126 substance Substances 0.000 description 10
- 230000000694 effects Effects 0.000 description 8
- 239000010419 fine particle Substances 0.000 description 8
- 239000011148 porous material Substances 0.000 description 8
- 230000007423 decrease Effects 0.000 description 7
- 239000000243 solution Substances 0.000 description 7
- 238000001471 micro-filtration Methods 0.000 description 6
- 238000000108 ultra-filtration Methods 0.000 description 6
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 6
- 102000004190 Enzymes Human genes 0.000 description 5
- 108090000790 Enzymes Proteins 0.000 description 5
- 238000000855 fermentation Methods 0.000 description 5
- 230000004151 fermentation Effects 0.000 description 5
- 241000894006 Bacteria Species 0.000 description 4
- 240000004808 Saccharomyces cerevisiae Species 0.000 description 4
- 244000005700 microbiome Species 0.000 description 4
- 229920000642 polymer Polymers 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 3
- 238000010008 shearing Methods 0.000 description 3
- 239000000725 suspension Substances 0.000 description 3
- 241000588724 Escherichia coli Species 0.000 description 2
- 239000005909 Kieselgur Substances 0.000 description 2
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 2
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 2
- 238000009825 accumulation Methods 0.000 description 2
- 238000013459 approach Methods 0.000 description 2
- 238000005119 centrifugation Methods 0.000 description 2
- 239000012141 concentrate Substances 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 239000004745 nonwoven fabric Substances 0.000 description 2
- 239000000047 product Substances 0.000 description 2
- 238000007670 refining Methods 0.000 description 2
- 239000008223 sterile water Substances 0.000 description 2
- 239000011550 stock solution Substances 0.000 description 2
- WQZGKKKJIJFFOK-GASJEMHNSA-N Glucose Natural products OC[C@H]1OC(O)[C@H](O)[C@@H](O)[C@@H]1O WQZGKKKJIJFFOK-GASJEMHNSA-N 0.000 description 1
- 239000000020 Nitrocellulose Substances 0.000 description 1
- 239000004952 Polyamide Substances 0.000 description 1
- 239000004642 Polyimide Substances 0.000 description 1
- FJWGYAHXMCUOOM-QHOUIDNNSA-N [(2s,3r,4s,5r,6r)-2-[(2r,3r,4s,5r,6s)-4,5-dinitrooxy-2-(nitrooxymethyl)-6-[(2r,3r,4s,5r,6s)-4,5,6-trinitrooxy-2-(nitrooxymethyl)oxan-3-yl]oxyoxan-3-yl]oxy-3,5-dinitrooxy-6-(nitrooxymethyl)oxan-4-yl] nitrate Chemical compound O([C@@H]1O[C@@H]([C@H]([C@H](O[N+]([O-])=O)[C@H]1O[N+]([O-])=O)O[C@H]1[C@@H]([C@@H](O[N+]([O-])=O)[C@H](O[N+]([O-])=O)[C@@H](CO[N+]([O-])=O)O1)O[N+]([O-])=O)CO[N+](=O)[O-])[C@@H]1[C@@H](CO[N+]([O-])=O)O[C@@H](O[N+]([O-])=O)[C@H](O[N+]([O-])=O)[C@H]1O[N+]([O-])=O FJWGYAHXMCUOOM-QHOUIDNNSA-N 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- 238000010923 batch production Methods 0.000 description 1
- 239000011942 biocatalyst Substances 0.000 description 1
- 229940041514 candida albicans extract Drugs 0.000 description 1
- 229920002301 cellulose acetate Polymers 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- 239000000084 colloidal system Substances 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 239000002131 composite material Substances 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 239000012531 culture fluid Substances 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 230000018044 dehydration Effects 0.000 description 1
- 238000006297 dehydration reaction Methods 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000000502 dialysis Methods 0.000 description 1
- 238000009792 diffusion process Methods 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 238000000909 electrodialysis Methods 0.000 description 1
- 238000006911 enzymatic reaction Methods 0.000 description 1
- 239000004744 fabric Substances 0.000 description 1
- 239000000706 filtrate Substances 0.000 description 1
- 239000008394 flocculating agent Substances 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 239000008103 glucose Substances 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 230000002209 hydrophobic effect Effects 0.000 description 1
- 230000003834 intracellular effect Effects 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 239000011859 microparticle Substances 0.000 description 1
- 229920001220 nitrocellulos Polymers 0.000 description 1
- 229920000620 organic polymer Polymers 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 230000000149 penetrating effect Effects 0.000 description 1
- 230000000704 physical effect Effects 0.000 description 1
- 239000000049 pigment Substances 0.000 description 1
- 230000010287 polarization Effects 0.000 description 1
- 229920002492 poly(sulfone) Polymers 0.000 description 1
- 229920002239 polyacrylonitrile Polymers 0.000 description 1
- 229920002647 polyamide Polymers 0.000 description 1
- 229920001721 polyimide Polymers 0.000 description 1
- 229920005597 polymer membrane Polymers 0.000 description 1
- 238000010248 power generation Methods 0.000 description 1
- 238000003825 pressing Methods 0.000 description 1
- 238000011085 pressure filtration Methods 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 239000002683 reaction inhibitor Substances 0.000 description 1
- 239000004627 regenerated cellulose Substances 0.000 description 1
- 238000001223 reverse osmosis Methods 0.000 description 1
- 238000013341 scale-up Methods 0.000 description 1
- 239000011780 sodium chloride Substances 0.000 description 1
- 230000001954 sterilising effect Effects 0.000 description 1
- 238000004659 sterilization and disinfection Methods 0.000 description 1
- 239000013076 target substance Substances 0.000 description 1
- 239000012138 yeast extract Substances 0.000 description 1
Landscapes
- Separation Using Semi-Permeable Membranes (AREA)
Abstract
Description
【0001】0001
【産業上の利用分野】本発明は、デッドエンド型濾過方
法に関するものであり、特に大きい膜透過流束を維持す
るために逆洗を周期的に行う新しいデッドエンド型濾過
方法に関するものである。本発明のデッドエンド型濾過
方法は、種々の高分子、微生物、酵母、微粒子を含有あ
るいは懸濁する流体の分離、精製、回収、濃縮などに適
用され、特に濾過を必要とする微細な微粒子を含有する
流体からその微粒子を分離する必要のあるあらゆる場合
に適用することができ、例えば微粒子を含有する各種の
懸濁液、発酵液あるいは培養液などの他、顔料の懸濁液
などから微粒子を分離する、原子力発電の復水からクラ
ッドを分離除去する場合にも適用される。ところで近年
バイオテクノロジーの急速な発展にともない、培養、発
酵、酵素反応等による生化学物質の生産は、医薬品・食
品・化学製品など多くの分野で盛んに行われるようにな
ってきた。これらの生産物質は精製することによって付
加価値が高まるが、この精製操作に多くのコストがかけ
られるのが現状である。本発明のデッドエンド型濾過方
法はこれらの分野で特に有効であり、例えば培養液中か
ら反応阻害物質を連続的に除去することにより高密度培
養を行う、菌体外酵素生産菌を用いた時に酵素を連続回
収する、菌体内酵素生産菌を破砕した溶液から酵素を回
収する、バッチ式で得られた培養液から生体触媒を除去
する、など多岐にわたって適用される。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a dead-end filtration method, and more particularly to a new dead-end filtration method in which backwashing is carried out periodically to maintain a high membrane permeation flux. The dead-end filtration method of the present invention is applied to the separation, purification, recovery, concentration, etc. of fluids containing or suspending various polymers, microorganisms, yeast, and fine particles, and is particularly applicable to the separation, purification, recovery, and concentration of fluids containing or suspending various polymers, microorganisms, yeast, and fine particles. It can be applied in any case where it is necessary to separate fine particles from a fluid containing them, such as in various suspensions containing fine particles, fermentation liquids or culture liquids, as well as suspensions of pigments, etc. It is also applied when separating and removing crud from condensate in nuclear power generation. However, with the rapid development of biotechnology in recent years, the production of biochemical substances through cultivation, fermentation, enzymatic reactions, etc. has become popular in many fields such as pharmaceuticals, foods, and chemical products. Although the added value of these produced substances increases by refining them, the current situation is that a lot of cost is incurred in this refining operation. The dead-end filtration method of the present invention is particularly effective in these fields, for example, when using exoenzyme-producing bacteria that perform high-density culture by continuously removing reaction inhibitors from the culture solution. It has a wide variety of applications, including continuous recovery of enzymes, recovery of enzymes from a solution obtained by crushing intracellular enzyme-producing bacteria, and removal of biocatalysts from culture solutions obtained in a batch process.
【0002】0002
【従来の技術】従来、膜を用いて懸濁物質を含有する原
流体から懸濁物質を分離する技術としては、例えば圧力
を駆動力とする逆浸透法、限外濾過法、精密濾過法、電
位差を駆動力とする電気透析法、濃度差を駆動力とする
拡散透析法等がある。これらの方法は、連続操作が可能
であり、分離操作中に温度やpHの条件を大きく変化さ
せることなく分離、精製あるいは濃縮ができ、粒子、分
子、イオン等の広範囲にわたって分離が可能であり、小
型プラント処理能力を大きく保つことができるので経済
的であり、分離操作に要するエネルギーが小さく、かつ
他の分離方法では難しい低濃度原流体の処理が可能であ
るなどの理由により広範囲に実施されている。そしてこ
れらの分離技術に用いられる膜としては、酢酸セルロー
ス、硝酸セルロース、再生セルロース、ポリスルホン、
ポリアクリロニトリル、ポリアミド、ポリイミド等の有
機高分子等を主体とした高分子膜や耐熱性、耐薬品性な
どの耐久性に優れている多孔質セラミック膜などがあり
、主としてコロイドの濾過を対象とする場合は限外濾過
膜が使用され、微細な粒子の濾過を対象とする精密濾過
ではそれに適した微孔を有する精密濾過膜が使用されて
いる。前述したようにバイオテクノロジーの進歩に伴い
、高純度化、高性能化、高精密化が要求されるようにな
り、従来から行われている遠心分離やけい藻土濾過に代
わって連続操作が可能で大量処理できる、濾過助剤や凝
集剤の添加が必要ない、分離の効率は菌体と懸濁液の比
重差に無関係であり培養液の物性や菌体の種類に関係な
く清澄な濾液が得られる、高濃度培養ができ生産効率が
向上する、完全密閉系が可能で菌の漏れがない、濃縮後
菌体の洗浄が可能である、スケールアップが容易で経済
性が高い等の理由で、精密濾過あるいは限外濾過技術の
応用分野が拡大しつつある。しかしながら、濾過膜の利
点が多いにもかかわらず精密濾過あるいは限外濾過膜を
用いて微粒子を分離する場合に、濃度分極の影響により
ケーク層が生じて透過流体の流れに抵抗が生じ、また濾
過膜の目詰まりによる抵抗が大きくなって膜透過流束が
急激にかつ著しく低下してしまうという問題があり、こ
れが精密濾過あるいは限外濾過の実用化を妨げる最大の
原因であった。またそれに用いられる膜は汚染されやす
く、その防止対策が必要である。BACKGROUND ART Conventionally, techniques for separating suspended solids from a raw fluid containing suspended solids using a membrane include, for example, reverse osmosis, ultrafiltration, microfiltration, which uses pressure as a driving force, There are electrodialysis methods that use a potential difference as a driving force, and diffusion dialysis methods that use a concentration difference as a driving force. These methods can be operated continuously, can separate, purify, or concentrate without significantly changing temperature or pH conditions during the separation operation, and can separate a wide range of particles, molecules, ions, etc. It is economical because it can maintain a large processing capacity in a small plant, requires little energy for separation operations, and can process low-concentration raw fluids that are difficult to use with other separation methods, so it has been widely implemented. There is. The membranes used in these separation techniques include cellulose acetate, cellulose nitrate, regenerated cellulose, polysulfone,
There are polymer membranes mainly made of organic polymers such as polyacrylonitrile, polyamide, polyimide, etc., and porous ceramic membranes with excellent durability such as heat resistance and chemical resistance, and are mainly used for colloid filtration. For microfiltration, ultrafiltration membranes are used, and microfiltration membranes with suitable pores are used for precision filtration, which targets the filtration of fine particles. As mentioned above, with the advancement of biotechnology, higher purity, higher performance, and higher precision are required, and continuous operation is now possible in place of the conventional centrifugation and diatomaceous earth filtration. There is no need to add filter aids or flocculants.The separation efficiency is independent of the difference in specific gravity between the bacterial cells and the suspension, and a clear filtrate is produced regardless of the physical properties of the culture solution or the type of bacterial cells. It is possible to obtain high concentration culture and improve production efficiency, it is possible to have a completely closed system and there is no leakage of bacteria, it is possible to wash the bacteria after concentration, it is easy to scale up and it is highly economical, etc. , the field of application of microfiltration or ultrafiltration technology is expanding. However, despite the many advantages of filtration membranes, when microparticles are separated using microfiltration or ultrafiltration membranes, a cake layer is generated due to the influence of concentration polarization, which creates resistance to the flow of the permeate fluid. There is a problem in that the resistance due to membrane clogging increases and the membrane permeation flux rapidly and significantly decreases, and this has been the biggest cause of hindering the practical application of precision filtration or ultrafiltration. Furthermore, the membrane used therein is easily contaminated, and measures to prevent this are required.
【0003】濾過方法としては、濾過されるべき全ての
流体が濾材(濾布や膜など)とケーク層を通過して流体
中に含まれている微粒子を分離するいわゆるデッドエン
ド型濾過方式がある。この従来のデッドエンド型濾過方
式では流体が通過して懸濁物質が濾過膜の内部に捕捉さ
れて分離される段階では高い透過流束が得られるが、濾
過膜の表面で捕捉される段階になるとケーク層が形成さ
れ、大量の原流体を処理する場合や形成されるケーク層
の比抵抗が極端に高い場合は大きな濾過抵抗となり、こ
のようなデッドエンド濾過を行うと膜透過流束が小さく
なる。このため、クロスフロー型濾過方式が考えられた
。このクロスフロー型濾過方式は、濾過膜の膜表面に平
行に濾過すべき原流体を流し、流体は濾過膜を通って反
対側へ透過し、この原流体と透過流体の流れが直交して
いるためにこのように称されている。このクロスフロー
型濾過方法は、濾過膜に平行な原流体の流れによって膜
面上に形成されたケーク層がはぎ取られるので従来のデ
ッドエンド型濾過方式に比べて膜透過流束が大きく、大
量の原流体を直接連続的に分離、精製、濃縮が可能であ
る。しかし懸濁物質の濾過比抵抗が極端に高い、すなわ
ち培養液、発酵液から菌体や高分子生成物を除くために
純水透過流束の大きいすなわち分画分子量の大きい限外
濾過膜や精密濾過膜を用いた場合は急激に膜透過流束が
低下して濾過開始初期の高い膜透過流束を保つことは困
難であり、結果としてデッドエンド型濾過方式と総透過
液量を比較すると効果は小さく経済的な透過流束を得る
には不十分であった。[0003] As a filtration method, there is a so-called dead-end filtration method in which all the fluid to be filtered passes through a filter medium (filter cloth, membrane, etc.) and a cake layer to separate fine particles contained in the fluid. . In this conventional dead-end filtration system, a high permeation flux is obtained when the fluid passes through and the suspended solids are trapped inside the filtration membrane and separated, but when the suspended solids are trapped on the surface of the filtration membrane, When a large amount of raw fluid is processed or when the specific resistance of the formed cake layer is extremely high, the filtration resistance becomes large, and when such dead-end filtration is performed, the membrane permeation flux is small. Become. For this reason, a cross-flow type filtration system was considered. In this cross-flow filtration system, the raw fluid to be filtered is passed parallel to the membrane surface of the filtration membrane, the fluid passes through the filtration membrane to the opposite side, and the flow of the raw fluid and the permeated fluid are perpendicular to each other. This is why it is called this way. In this cross-flow filtration method, the cake layer formed on the membrane surface is stripped off by the flow of the raw fluid parallel to the filtration membrane, so the membrane permeation flux is larger than in the conventional dead-end filtration method, and a large amount of It is possible to directly and continuously separate, purify, and concentrate raw fluids. However, in order to remove microbial cells and polymer products from culture fluids and fermentation fluids, which have extremely high filtration specific resistance for suspended solids, ultrafiltration membranes with high pure water permeation flux, or high molecular weight cutoff, and precision filters are used. When using a filtration membrane, the membrane permeation flux decreases rapidly and it is difficult to maintain a high membrane permeation flux at the beginning of filtration.As a result, when comparing the dead-end filtration method and the total permeate volume, was small and insufficient to obtain an economical permeation flux.
【0004】0004
【発明が解決しようとする課題】上述のように、クロス
フロー型濾過方式は原理的には高度な分離技術であるが
、最大の問題である膜透過流束は、従来のデッドエンド
型濾過方式に僅かに大きい程度で、精密濾過方法として
このクロスフロー方式を採用しても十分高い膜透過流束
が得られないという問題があった。また従来から行われ
ている懸濁物質と流体との分離の具体的な例を見ても、
例えば発酵液から菌体を分離する場合には、従来から行
われている遠心分離法、珪藻土濾過法などに代わってク
ロスフロー濾過方式を用いても膜面上に形成されたケー
ク層や目詰まりによって濾過時間の経過と共に膜透過流
束が低下するばかりでなく、原流体を循環する際の剪断
力によって菌体の活性が失われるという問題があった。[Problems to be Solved by the Invention] As mentioned above, the cross-flow filtration system is an advanced separation technology in principle, but the biggest problem, the membrane permeation flux, is lower than that of the conventional dead-end filtration system. However, even if this cross-flow method is adopted as a precision filtration method, a sufficiently high membrane permeation flux cannot be obtained. Also, looking at specific examples of conventional separation of suspended solids and fluids,
For example, when separating bacterial cells from a fermentation liquid, even if a cross-flow filtration method is used instead of the conventional centrifugation method or diatomaceous earth filtration method, a cake layer or clogging may occur on the membrane surface. Therefore, there is a problem that not only the membrane permeation flux decreases as the filtration time passes, but also the activity of the bacterial cells is lost due to the shear force when circulating the raw fluid.
【0005】透過流束を高める方法としては従来より濾
過膜への原流体の流入を断続的に停止したり、濾過膜の
透過流体側の弁を閉止することにより、濾過膜の膜面に
垂直にかかる圧力を断続的になくすあるいは減少させた
り、また濾過膜の透過液側から圧力を加え透過液側から
原流体側へ流体を流すことによって、濾過膜の原流体側
の膜面上に堆積しているケーク層や付着層を断続的に取
り除く「逆洗」と称する試みがなされているが、懸濁物
質の濾過比抵抗が小さい場合は逆洗により濾過膜に堆積
した懸濁物質は容易に脱着できるが、懸濁物質の濾過比
抵抗が高く濾過膜との付着力の強い高分子成分や菌体の
場合は、逆洗を行っても濾過膜から十分取り除くことが
できず膜透過流速が十分回復しないなどの問題点があっ
た。またこれら逆洗を行った際に濾過膜から脱着した懸
濁物質を濾過系内に残しておくと原流体中の懸濁物の濃
度が徐々に増加し、場合によっては原流体の粘度も上昇
するため膜透過流束は徐々に低下して逆洗を行っても透
過流束が十分回復しない等の問題があった。一方菌体の
活性を低下させない方法として、クロスフロー濾過の場
合は循環流速を低下させ剪断力を小さくすることが行わ
れているが、剪断力を小さくするとクロスフロー濾過方
式の効果が小さくなるため、実際に菌体活性を低下させ
ない方策をとると膜透過流束が低下する問題があった。
またポンプでの菌体の破砕を少なくするためダイヤフラ
ムポンプなどの剪断力の小さいポンプを用いるとポンプ
の脈動が大きくクロスフロー濾過方式の効果が小さくな
る等の問題もあった。Conventional methods for increasing permeation flux include intermittently stopping the flow of raw fluid into the filtration membrane, or closing the valve on the permeate side of the filtration membrane. By intermittently eliminating or reducing the pressure applied to the filtration membrane, or by applying pressure from the permeate side of the filtration membrane and flowing fluid from the permeate side to the raw fluid side, deposits can be removed on the membrane surface on the raw fluid side of the filtration membrane. Attempts have been made to intermittently remove the cake layer and adhering layer, but if the filtration specific resistance of suspended solids is small, backwashing can easily remove suspended solids that have accumulated on the filtration membrane. However, in the case of polymeric components and bacterial cells that have a high filtration specific resistance of suspended solids and strong adhesion to the filtration membrane, they cannot be sufficiently removed from the filtration membrane even if backwashing is performed, and the membrane permeation flow rate decreases. There were problems such as insufficient recovery. In addition, if the suspended solids desorbed from the filtration membrane during backwashing are left in the filtration system, the concentration of suspended solids in the raw fluid will gradually increase, and in some cases, the viscosity of the raw fluid will also increase. Therefore, there was a problem that the membrane permeation flux gradually decreased and the permeation flux did not recover sufficiently even if backwashing was performed. On the other hand, in the case of cross-flow filtration, the method of not reducing the activity of bacterial cells is to reduce the circulation flow rate and reduce the shearing force, but since reducing the shearing force reduces the effectiveness of the cross-flow filtration method. However, if measures were taken that did not actually reduce bacterial cell activity, there was a problem that the membrane permeation flux would decrease. Furthermore, when a pump with a small shearing force such as a diaphragm pump is used to reduce the crushing of bacterial cells by the pump, there is a problem that the pump pulsates so much that the effect of the cross-flow filtration system is reduced.
【0006】[0006]
【課題を解決するための手段】本発明は、上述した従来
技術にあった問題点を解決するために為されたものであ
って、実用性のある高い膜透過流束を持ち菌体などの活
性低下を減少させる新規なデッドエンド型濾過方法を提
供することを目的とするものである。すなわち本発明は
、精密濾過膜を用いて、懸濁物質を含む流体からなる原
流体を供給し濾過することにより流体と懸濁物質とを分
離し濾過膜の透過流体側の圧力を原流体側の圧力より大
きくして周期的に逆洗を行い、逆洗液と共に濾過膜から
脱着した懸濁物質を濾過系外へ排出するデッドエンド型
濾過方式において、原流体側にも濾過膜と平行に洗浄液
を流すことを特徴とする。以下、本発明を詳細に説明す
る。本発明のデッドエンド型濾過方法は、種々の高分子
、微生物、酵母、微粒子を含有あるいは懸濁する流体の
分離、精製、回収、濃縮など、濾過を必要とする微細な
微粒子を含有する流体からその微粒子を分離する必要の
あるあらゆる場合に適用することができるが、特に発酵
液、培養液からの酵素、微生物、細胞の分離、濃縮、回
収など懸濁物質の濾過比抵抗が極端に大きい場合に効果
がある。[Means for Solving the Problems] The present invention has been made to solve the problems of the prior art described above, and has a practical high membrane permeation flux, and is capable of transporting bacterial cells, etc. The object of the present invention is to provide a novel dead-end filtration method that reduces activity loss. That is, the present invention uses a precision filtration membrane to supply and filter a raw fluid consisting of a fluid containing suspended matter, thereby separating the fluid and suspended matter, and reducing the pressure on the permeate fluid side of the filtration membrane to the raw fluid side. In the dead-end filtration system, backwashing is carried out periodically at a pressure greater than It is characterized by flowing cleaning liquid. The present invention will be explained in detail below. The dead-end filtration method of the present invention is suitable for separating, purifying, recovering, and concentrating fluids containing or suspending various polymers, microorganisms, yeast, and particulates from fluids containing fine particles that require filtration. It can be applied in any case where it is necessary to separate fine particles, but especially in cases where the specific filtration resistance of suspended substances is extremely high, such as in the separation, concentration, and recovery of enzymes, microorganisms, and cells from fermentation liquids and culture liquids. is effective.
【0007】本発明の濾過方式の特徴は透過液側の圧力
を原流体側の圧力より高くして逆洗を行うと同時に、原
流体側にも洗浄液を濾過膜と平行な方向に流しさらに洗
浄液にはガスを同伴させたことである。逆洗を行った際
に濾過膜に堆積した懸濁物質が十分脱着せず、透過流束
が十分回復しない原因の1つは逆洗で脱着した懸濁物質
と逆洗液が排出口まで達せずに濾過器内に残留してしま
うことである。本発明では脱着した懸濁物質と逆洗液が
容易に排出されるように原流体側にも洗浄液を濾過膜と
平行な方向に排出口に至るまで流し、さらに懸濁物が脱
着しにくい時は洗浄液にガスを同伴させ濾過膜表面を攪
乱すると効果が大きい。原流体側の洗浄液は逆洗で使用
する逆洗液と同様のものが好ましいが、系外からの異物
混入を避ける場合は逆洗液として透過液を原流体側の洗
浄液は原流体そのものを用いることができる。また透過
液を逆流させた分だけ透過量が減少することを避ける場
合は、濾過系外より洗浄液を供給して必要に応じた逆洗
液量で逆洗を行うことが好ましい。濾過系外より供給す
る洗浄液は濾過膜の特性を低下させたり原流体の特性を
変化させなければ基本的には何でも良いが、原流体が水
溶液である場合には一般的には滅菌水を用いることが好
ましい。また、逆洗終了後逆洗液を濾過系内に残したく
ない場合はガスによる脱水を行うことが好ましい。逆洗
は膜透過流束が極端に低くなってから行うと逆洗後の膜
透過流束の回復性は悪くなる。これは懸濁物質が濾過膜
の内部に深く侵入したり堆積した懸濁物質が圧密化した
り、また長時間濾過を行うと懸濁物質が濾過膜に強く結
合するため、逆洗時に堆積した懸濁物質を完全に取り除
くことができなくなるためである。このため定圧濾過を
行う場合は濾過初期の透過流速の1/100に達する前
に逆洗を行うことが好ましく、さらに高い透過流速を得
るためには1/10に達する前に逆洗を行うことが好ま
しい。また、定速濾過を行う場合は濾過膜間差圧が極端
委高くなってから逆洗を行うと逆洗後の濾過膜間差圧の
回復性すなわち濾過膜の洗浄性が悪くなるため、濾過初
期の濾過膜間差圧の100倍に達する前に逆洗を行うこ
とが好ましく、さらに好ましくは10倍に達する前に逆
洗を行う。従って濾過開始から逆洗に至るまでの時間は
短く、懸濁物質の比抵抗が大きい場合は濾過を0.5分
以上3分以内行った後に逆洗を行うことが好ましい。ま
た、逆洗液は高い透過流速で多量に濾過膜内を通過させ
る方が洗浄性は高くなるが、逆洗液の透過流束を高めて
長時間逆洗を行うことは逆洗液量が膨大となるばかりで
なく、濾過時間に対する逆洗時間の比率が高まり事実上
平均透過流束は低くなるため、十分透過流束が回復でき
る範囲で透過流速は1×10−4m3 /m2 /se
c以上であり、時間は1秒以上30秒以内であることが
好ましい。The filtration method of the present invention is characterized by backwashing by making the pressure on the permeate side higher than the pressure on the raw fluid side, and at the same time, flowing the cleaning liquid on the raw fluid side in a direction parallel to the filtration membrane. was accompanied by gas. One of the reasons why the suspended solids deposited on the filtration membrane during backwashing is not sufficiently desorbed and the permeation flux is not sufficiently recovered is that the suspended solids and backwash liquid desorbed during backwashing do not reach the outlet. The problem is that the liquid remains in the filter without being absorbed. In the present invention, in order to easily discharge the desorbed suspended solids and backwash liquid, the cleaning liquid is also flowed on the raw fluid side in a direction parallel to the filtration membrane until it reaches the discharge port, and when the suspended solids are difficult to desorb. This is most effective when gas is entrained in the cleaning liquid to disturb the surface of the filtration membrane. The cleaning liquid on the raw fluid side is preferably the same as the backwashing liquid used for backwashing, but if you want to avoid contamination with foreign matter from outside the system, use the permeate as the backwashing liquid, and use the raw fluid itself as the cleaning liquid on the raw fluid side. be able to. In addition, in order to avoid a decrease in the permeation amount by the amount of backflow of the permeate, it is preferable to supply a cleaning liquid from outside the filtration system and perform backwashing with an amount of backwash liquid as required. Basically, any cleaning liquid supplied from outside the filtration system may be used as long as it does not degrade the properties of the filtration membrane or change the properties of the raw fluid, but if the raw fluid is an aqueous solution, sterile water is generally used. It is preferable. Further, if it is desired not to leave the backwash liquid in the filtration system after the backwash is completed, it is preferable to perform dehydration using gas. If backwashing is performed after the membrane permeation flux becomes extremely low, the recovery of the membrane permeation flux after backwashing will deteriorate. This is due to suspended solids penetrating deeply into the filtration membrane, the accumulated suspended solids becoming compacted, or the suspended solids strongly bonding to the filtration membrane when filtration is performed for a long time. This is because the turbid substances cannot be completely removed. For this reason, when performing constant pressure filtration, it is preferable to perform backwashing before the permeation flow rate reaches 1/100 of the initial filtration flow rate, and to obtain an even higher permeation flow rate, backwashing should be performed before reaching 1/10 of the permeation flow rate at the initial stage of filtration. is preferred. In addition, when performing constant-speed filtration, if backwashing is performed after the pressure difference between the filtration membranes becomes extremely high, the recovery of the pressure difference between the filtration membranes after backwashing, that is, the cleaning performance of the filtration membranes, will deteriorate. It is preferable to perform backwashing before reaching 100 times the initial pressure difference between the filtration membranes, and more preferably perform backwashing before reaching 10 times the initial pressure difference between the filtration membranes. Therefore, the time from the start of filtration to backwashing is short, and if the specific resistance of the suspended solids is large, it is preferable to perform backwashing after filtration is performed for 0.5 minutes or more and up to 3 minutes. In addition, cleaning performance will be higher if a large amount of backwash liquid is passed through the filtration membrane at a high permeation flow rate, but if the permeation flux of backwash liquid is increased and backwash is performed for a long time, Not only will the amount be enormous, but the ratio of backwashing time to filtration time will increase, effectively lowering the average permeation flux, so the permeation flow rate should be 1 x 10-4 m3/m2/se within the range where the permeation flux can be sufficiently recovered.
c or more, and the time is preferably 1 second or more and 30 seconds or less.
【0008】使用される濾過膜は懸濁物質が阻止できる
孔径を持つものが必要であり、精密濾過膜では通常0.
05〜10μmの孔径を有するものが使用される。これ
ら精密濾過膜を0.5分から3分の短い時間で濾過した
場合の総濾過量は、濾過膜の構造に著しく影響を受ける
。すなわち懸濁物質を濾過膜の表面で阻止する場合は阻
止された懸濁物質が非常に大きな濾過抵抗となって透過
流束が急激に低下し結果として総濾過量は低くなるが、
濾過膜が膜厚方向に孔径が連続的または不連続的に変化
し濾過膜の一方の表面の孔径と他方の表面の孔径とが異
なる構造を有するいわゆる異方性膜を表面孔径の大きい
側を原流体側に向けて使用することにより、濾過膜内部
で懸濁物質が阻止できるため大きな総濾過量を得ること
が可能となる。また、濾過膜として多孔質膜と不織布ま
たは網状体を一体化した複合構造を持つ場合も不織布ま
たは網状体側を原液側にすることにより同様の効果が得
られる。The filtration membrane used must have a pore size that can block suspended solids, and precision filtration membranes usually have a pore size of 0.
Those having a pore size of 0.05 to 10 μm are used. The total filtration amount when these microfiltration membranes are used for filtration in a short time of 0.5 to 3 minutes is significantly influenced by the structure of the filtration membrane. In other words, when suspended substances are blocked on the surface of a filtration membrane, the blocked suspended substances create a very large filtration resistance and the permeation flux rapidly decreases, resulting in a low total filtration amount.
A so-called anisotropic membrane has a structure in which the pore size changes continuously or discontinuously in the membrane thickness direction, and the pore size on one surface of the filtration membrane is different from the pore size on the other surface. By using it toward the raw fluid side, suspended matter can be blocked inside the filtration membrane, making it possible to obtain a large total filtration amount. Furthermore, when the filtration membrane has a composite structure in which a porous membrane and a nonwoven fabric or a mesh body are integrated, the same effect can be obtained by making the nonwoven fabric or mesh body side the undiluted solution side.
【0009】次に本発明のデッドエンド型濾過方式を図
面に基づいて説明する。図1は従来のデッドエンド型濾
過を行った際に濾過膜に堆積する懸濁物の様子を示して
おり、経時とともに堆積する懸濁物質量は増加し、最終
的には透過流束はゼロに近づく。 図2はクロスフロ
ー濾過を行った際に濾過膜に堆積する懸濁物質の様子を
示しており、濾過開始初期においては懸濁物質が徐々に
増加するが原流体の剪断力によって堆積する懸濁物質量
は一定値をとり透過流束も最終的には一定値に近づく。
図3は本発明のデッドエンド型濾過方式のフローを示し
ている。濾過を一定時間行った後透過流体側から原流体
側に滅菌水を逆流させ、さらに原流体側にも濾過膜と平
行な方向に滅菌水を流して濾過膜から脱着した懸濁物質
と共に排出すし、再び濾過を行う。このサイクルを繰り
返すことによって原流体の懸濁物質濃度も上昇せずに連
続的に高い透過流束を維持することが可能となる。図4
は本発明の濾過方法で逆洗、洗浄を行っている際の濾過
膜面上での懸濁物質の流動状態を示している。Next, the dead-end filtration system of the present invention will be explained based on the drawings. Figure 1 shows the state of suspended matter that accumulates on the filtration membrane when performing conventional dead-end filtration.The amount of suspended matter that accumulates increases over time, and the permeation flux eventually reaches zero. approach. Figure 2 shows the state of suspended solids deposited on the filtration membrane when cross-flow filtration is performed.At the beginning of filtration, the suspended solids gradually increase, but the suspended solids accumulate due to the shear force of the raw fluid. The amount of substance takes a constant value, and the permeation flux eventually approaches a constant value. FIG. 3 shows the flow of the dead-end filtration method of the present invention. After filtration has been carried out for a certain period of time, sterilized water is flowed back from the permeate side to the raw fluid side, and sterile water is also flowed parallel to the filtration membrane on the raw fluid side to be discharged together with the suspended solids that have been desorbed from the filtration membrane. , perform the filtration again. By repeating this cycle, it becomes possible to continuously maintain a high permeation flux without increasing the concentration of suspended solids in the raw fluid. Figure 4
shows the fluid state of suspended solids on the filter membrane surface during backwashing and washing in the filtration method of the present invention.
【0010】0010
【実施例】以下に具体例をあげて本発明をさらに詳しく
説明するが、発明の主旨を越えない限り本発明は実施例
に限定されるものではない。
実施例1
大腸菌(IFO3301)をグルコース10g/l、ポ
リペプトン5g/l、酵母エキス5g/l、塩化ナトリ
ウム5g/lを含む培養溶液を用いて18時間振とう培
養を行って濾過原液とした。培養条件は温度37℃、p
H7.0であった。この原液を公称孔径0.2μmの精
密濾過膜を用いて本発明の逆洗を周期的に行うデッドエ
ンド型濾過を行った。使用した濾過器は有効膜面積10
0cm2で、実験条件は圧力差0.5×105 Pa、
液温度25℃であり、逆洗流束1×10−3m3 /m
2 /sec、逆洗時間3秒で行い逆洗液は滅菌水で行
った。図5に原流体側に洗浄水を流さない場合の比較例
と共に本発明の結果を示した。本発明の濾過方法では逆
洗により透過流束はよく回復した。[Examples] The present invention will be explained in more detail with reference to specific examples below, but the present invention is not limited to the examples unless it goes beyond the gist of the invention. Example 1 Escherichia coli (IFO3301) was cultured with shaking for 18 hours using a culture solution containing 10 g/l of glucose, 5 g/l of polypeptone, 5 g/l of yeast extract, and 5 g/l of sodium chloride to obtain a filtration stock solution. The culture conditions were a temperature of 37°C, p.
It was H7.0. This stock solution was subjected to dead-end filtration using a precision filtration membrane with a nominal pore size of 0.2 μm, which periodically performs backwashing according to the present invention. The filter used has an effective membrane area of 10
0cm2, the experimental conditions were a pressure difference of 0.5×105 Pa,
The liquid temperature is 25℃, and the backwash flux is 1 x 10-3 m3/m.
2/sec, backwashing time was 3 seconds, and the backwashing liquid was sterilized water. FIG. 5 shows the results of the present invention together with a comparative example in which no cleaning water was flowed to the raw fluid side. In the filtration method of the present invention, the permeation flux was well recovered by backwashing.
【0011】[0011]
【発明の効果】本発明によれば、逆洗を周期的に行うデ
ッドエンド型濾過方式において高い膜透過流束が得られ
、それによって種々の懸濁物質を含有する液体から各懸
濁成分の分離、回収、精製、濃縮などがきわめて効率的
しかも経済的に行われる。そしてさらにプロセスの連続
化及び装置の小型化が可能であり、膜の選択性を利用し
て目的物のみを連続的に選択的に分離することができ、
酵母や菌体などのバイオリアクターへの応用ができ、従
来技術に比べて運転管理が容易であるなど諸々の効果が
奏せられる。Effects of the Invention According to the present invention, a high membrane permeation flux can be obtained in a dead-end filtration system in which backwashing is carried out periodically, thereby removing each suspended component from a liquid containing various suspended substances. Separation, recovery, purification, concentration, etc. are performed extremely efficiently and economically. Furthermore, it is possible to make the process continuous and downsize the equipment, and by utilizing the selectivity of the membrane, it is possible to continuously and selectively separate only the target substance.
It can be applied to bioreactors such as yeast and bacterial cells, and has various effects such as easier operation management than conventional technology.
【図1】従来のデッドエンド型濾過における懸濁物質の
堆積状態を示している。FIG. 1 shows the state of accumulation of suspended solids in conventional dead-end filtration.
【図2】従来のクロスフロー濾過における懸濁物質の堆
積状態を示している。FIG. 2 shows the state of accumulation of suspended solids in conventional cross-flow filtration.
【図3】本発明の逆洗を周期的に行うデッドエンド型濾
過方式のフローを示している。FIG. 3 shows a flowchart of a dead-end filtration system in which backwashing is performed periodically according to the present invention.
【図4】本発明の濾過方法で逆洗を行っている際の懸濁
物質の流動状態を示している。FIG. 4 shows the flow state of suspended solids during backwashing in the filtration method of the present invention.
【図5】本発明の濾過方法を用いて大腸菌培養液を濾過
した際の透過流束の経時変化を示している。FIG. 5 shows changes over time in permeation flux when E. coli culture solution is filtered using the filtration method of the present invention.
1 デッドエンド濾過の原流体の流れ2 デッドエ
ンド濾過の透過液の流れ3 デッドエンド濾過の懸濁
物質の移動方向4 濾過膜上に堆積している懸濁物質
5 濾過膜
6 クロスフロー濾過の原流体の流れ7 クロスフ
ロー濾過の透過液の流れ8 クロスフロー濾過の懸濁
物質の移動方向9 濾過膜上に堆積している懸濁物質
10 濾過膜
11 原流体入口
12 透過液出口
13 逆洗液入口
14 排液出口
15 濾過器
16 濾過膜
17 ガス入口
18 疎水性多孔質膜
19 ポンプ
20 滅菌フィルター
21 電磁弁
22 濾過膜
23 懸濁物質
24 洗浄液1 Flow of raw fluid in dead-end filtration 2 Flow of permeate in dead-end filtration 3 Movement direction of suspended solids in dead-end filtration 4 Suspended solids deposited on the filtration membrane 5 Filter membrane 6 Raw material in cross-flow filtration Fluid flow 7 Flow of permeate in cross-flow filtration 8 Movement direction of suspended solids in cross-flow filtration 9 Suspended solids deposited on the filtration membrane 10 Filtration membrane 11 Raw fluid inlet 12 Permeate outlet 13 Backwash liquid Inlet 14 Drainage outlet 15 Filter 16 Filtration membrane 17 Gas inlet 18 Hydrophobic porous membrane 19 Pump 20 Sterilization filter 21 Solenoid valve 22 Filtration membrane 23 Suspended solids 24 Washing liquid
Claims (2)
流体からなる原流体を供給し濾過することにより流体と
懸濁物質とを分離し濾過膜の透過流体側の圧力を原流体
側の圧力より大きくして周期的に逆洗を行い、逆洗液と
共に濾過膜から脱着した懸濁物質を濾過系外へ排出する
デッドエンド型濾過方式において、原流体側にも濾過膜
と平行に洗浄液を流すことを特徴とするデッドエンド型
濾過方式。Claim 1: Using a precision filtration membrane, a raw fluid consisting of a fluid containing suspended matter is supplied and filtered to separate the fluid and suspended matter, and the pressure on the permeate fluid side of the filtration membrane is reduced to the raw fluid side. In the dead-end filtration system, backwashing is carried out periodically at a pressure greater than A dead-end filtration method characterized by flowing cleaning liquid.
伴されていることを特徴とする請求項1に記載のデッド
エンド型濾過方法。2. The dead-end filtration method according to claim 1, wherein the cleaning liquid flowing to the raw fluid side contains gas.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2648491A JPH04265129A (en) | 1991-02-20 | 1991-02-20 | Filtration system |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2648491A JPH04265129A (en) | 1991-02-20 | 1991-02-20 | Filtration system |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH04265129A true JPH04265129A (en) | 1992-09-21 |
Family
ID=12194776
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2648491A Pending JPH04265129A (en) | 1991-02-20 | 1991-02-20 | Filtration system |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH04265129A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2018212354A1 (en) * | 2017-05-19 | 2018-11-22 | 国立大学法人徳島大学 | Stock solution treatment device, and operation method for stock solution treatment device |
-
1991
- 1991-02-20 JP JP2648491A patent/JPH04265129A/en active Pending
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2018212354A1 (en) * | 2017-05-19 | 2018-11-22 | 国立大学法人徳島大学 | Stock solution treatment device, and operation method for stock solution treatment device |
| CN110636872A (en) * | 2017-05-19 | 2019-12-31 | 国立大学法人德岛大学 | Raw solution processing device and method of operating the raw solution processing device |
| CN110636872B (en) * | 2017-05-19 | 2022-11-25 | 株式会社高鸟 | Stock solution processing apparatus and method for operating stock solution processing apparatus |
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