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JP3577992B2 - Membrane separation method - Google Patents
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JP3577992B2 - Membrane separation method - Google Patents

Membrane separation method Download PDF

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JP3577992B2
JP3577992B2 JP12729599A JP12729599A JP3577992B2 JP 3577992 B2 JP3577992 B2 JP 3577992B2 JP 12729599 A JP12729599 A JP 12729599A JP 12729599 A JP12729599 A JP 12729599A JP 3577992 B2 JP3577992 B2 JP 3577992B2
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membrane
membrane separation
liquid
water
treated
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JP2000317273A (en
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恒康 安達
明和 山本
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Kurita Water Industries Ltd
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Kurita Water Industries Ltd
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Description

【0001】
【発明の属する技術分野】
本発明は、膜濾過により発酵液からの菌体の分離及び目的有価物の回収、或いは、蛋白質溶液の脱塩濃縮に好適な膜分離方法に係り、特に、このような膜分離処理において膜の透過流束を高く維持して膜の薬品洗浄頻度を低減する膜分離方法に関する。
【0002】
【従来の技術】
発酵法によって生産した酵素などの有価物、例えば、リパーゼ、セルラーゼ、キシラーゼ等の酵素や生理活性ペプチド、蛋白質などを製品化する場合、生産菌と発酵生産物とを分離して有価物を回収する必要がある。従来、発酵液からの目的有価物の回収及び菌体分離のための一般的な方法として、珪藻土濾過法がある。珪藻土濾過法では、多量の珪藻土を濾過助剤又はプリコート剤として使用するため、珪藻土の混入した菌体が分離される。この珪藻土の混入した菌体は焼却処理することができず、投棄処分するため、処分場の問題がある。
【0003】
このため、珪藻土を使用しない分離方法として、MF(精密濾過)膜又はUF(限外濾過)膜を用いた膜分離法が検討され、上記発酵液の処理や蛋白質溶液の脱塩濃縮処理への適用が試みられている。
【0004】
なお、膜分離法による発酵液からの菌体分離と目的有価物の回収は、発酵液の濾過、濃縮(有価物の透過と菌体の濃縮)とダイアフィルトレーション(加水処理による、濃縮液側に残った有価物の透過液側への回収)とによって行われる。即ち、まず、発酵液を膜分離処理して有価物を透過液側に回収すると共に菌体を濃縮し(以下、これを「濃縮工程」と称す場合がある。)、菌体の濃縮がある程度進んだ後に、濃縮液側に水を徐々に添加(加水処理)しながら膜分離を続けるダイアフィルトレーションと称される操作を行うことで濃縮液側に残留する有価物の透過液側への回収を促進する(以下、これを「加工程」と称す場合がある。)。
【0005】
しかしながら、発酵液や蛋白質溶液のような生物系の被処理液を膜分離処理する場合、被処理液中に含まれる菌体、蛋白質、脂質等により、膜の汚染が著しく、膜の透過流束が早期に低下するという問題がある。特に、前述の如く、濃縮工程と加水工程を行う場合、濃縮工程において高度に濃縮された液を処理することから、膜の汚染が激しいものとなる。
【0006】
従来、一般的な膜分離処理においては、この膜の汚染対策として、膜の透過液側(二次側)から原水ないし濃縮液側(一次側)へ洗浄水を逆流させる逆洗による膜表面の汚染物の除去、或いは膜の薬品洗浄などが採用されている。また、膜面積を大きくすることで、膜汚染を相対的に低減することもできる。しかし、薬品洗浄は、膜分離装置の稼動効率を著しく低下させる上に、膜の劣化による膜寿命の短縮、薬品洗浄排液の処理等の問題がある。また、膜面積を大きくすることは、膜分離設備が大型化し、コスト的に不利である。従って、膜の薬品洗浄頻度は可能な限り低減し、また、最小の膜面積で、逆洗により効果的に膜の透過流束の低下を防止することが望ましい。
【0007】
なお、一般的に膜の逆洗を行う場合、逆洗用水としては、多くの場合透過液が用いられている。
【0008】
【発明が解決しようとする課題】
しかし、発酵液や蛋白質溶液の膜分離処理では、透過液中に回収目的とする酵素や蛋白質などが含まれているため、これを逆洗用水として用いると、目的物の回収率が低減することとなる上に、これらが逆洗工程で膜面に付着して二次汚染を引き起こす可能性があった。
【0009】
逆洗効果の面からは、逆洗用水として温水を用いるのが好ましく、温水逆洗を行うことにより、逆洗による膜汚染物質の剥離効果を向上させることができるが、発酵液や蛋白質溶液の膜分離処理で得られる透過液を加熱すると、透過液中に含まれる蛋白質等の有価物が変性してしまうため、透過液を加熱することはできない。また、温水を膜分離装置の一次側に逆流させることで、有価物を含む一次側の液中の有価物が変性する恐れもある。
【0010】
本発明は上記従来の問題点を解決し、発酵液や蛋白質溶液等の生物系の被処理液を膜分離処理するに当り、効果的な逆洗を行って、膜の透過流束を高く維持することができる膜分離方法を提供することを目的とする。
【0011】
【課題を解決するための手段】
本発明の膜分離方法は、菌体又は蛋白質等を含む生物系の被処理液の膜分離方法において、該被処理液を膜分離装置に送液して透過液を取り出すと共に濃縮液側を濃縮する濃縮工程と、該濃縮工程後に濃縮液側に水を添加しながら膜分離を行うダイアフィルトレーションとからなる第1の工程と、該第1の工程終了後に該膜分離装置内の被処理液を排出する第2の工程と、該第2の工程後、膜分離装置の透過液側から、透過液以外の逆洗用水からなる温水を供給して逆洗する第3の工程とを有し、該第1の工程、第2の工程及び第3の工程を繰り返し行うことを特徴とする。
【0012】
本発明においては、膜分離装置内の被処理液を排出した後、温水を逆流させる逆洗を周期的に行うため、膜汚染物を効果的に剥離除去して、膜の透過流束を高く維持することができる。
【0013】
【発明の実施の形態】
以下、図面を参照して本発明の実施の形態を詳細に説明する。
【0014】
図1は本発明の膜分離方法の実施の形態を示す系統図である。
【0015】
この方法は発酵液からの菌体の分離と目的有価物の回収を行うものであり、まず、被処理液貯槽1内の被処理液の所定量をポンプPにより調整槽2に送給した後、バルブV開、バルブV,V閉でポンプPを作動させて調整槽2内の被処理液をクロスフローで膜分離装置3に供給し、目的有価物を含む透過液を透過液受槽4に回収する。膜分離装置3から流出する濃縮液は調整槽2に戻して循環処理する。これに伴い、濃縮液側に菌体が濃縮されていく。所定の倍率まで濃縮が進んだ後、ポンプPを作動させて希釈水を導入して濃縮液側に残存する有価物を更に回収するためのダイアフィルトレーションを行う。この場合、ダイアフィルトレーションに必要な加水量や加水形態は、濃縮液中の目的有価物の濃度、膜による目的有価物の阻止率、及び目標とする目的有価物回収率等に応じて適宜選択される。なお、加水形態は連続加水であっても間欠加水であっても良いが、濃縮液量を一定に保ちながら透過液量に見合った水量を徐々に加えていく方法が一般的に用いられる。
【0016】
このようにして目的有価物を所定の回収率で透過液側に回収した後は、上記膜分離処理工程を終了し、ポンプP,Pを停止してバルブVを開き、膜分離装置3の一次側や濃縮液配管及び調整槽2内の濃縮液を系外へ排出する。
【0017】
この排出工程終了後、バルブV閉、バルブV開としてポンプPを作動させ、温水を膜分離装置3の二次側から一次側に逆流させて逆洗を行う。
【0018】
この逆洗に用いる温水の温度には特に制限はなく、膜素材の耐熱性や汚れの性状等に応じて適宜設定されるが、通常の場合、40〜80℃程度の温水が用いられる。
【0019】
また、温水の送液量等の逆洗条件にも特に制限はなく、汚れの程度に応じて適宜決定されるが、一般的には膜面積1mに対して10〜100L程度の温水を膜面積1m当り1〜20L/minの送液量で0.5〜100分程度送液して逆洗するのが好ましい。
【0020】
この逆洗工程終了後は、再び、被処理液貯槽1から調整槽2に所定量の被処理液を送液し、前記膜分離工程、排出工程及び逆洗工程を繰り返し行う。
【0021】
本発明においては温水を用いて逆洗を行うため、膜の汚染物を効果的に洗浄除去することができるが、生物系の被処理液の膜分離処理では膜汚染が特に著しいことから、逆洗は、膜の透過流束が低下する前に行うようにするのが好ましい。この逆洗間隔は、被処理液の性状や膜分離処理条件、膜面積や膜の型式等によっても異なるが、膜面積1m当り50〜1000Lの被処理液を膜分離処理する毎に逆洗を実施するのが好適である。
【0022】
この膜分離装置3の膜としてはMF膜又はUF膜が用いられる。この膜素材には特に制限はなく、ポリオレフィン膜、ポリスルホン膜、テフロン膜、セラミック膜などが用いられる。膜型式にも特に制限はないが、一般的には中空糸、チューブラー、スパイラル、プレート&フレーム型膜モジュールなどが用いられる。MF又はUF膜の選択及び膜素材や膜型式の選択は、使用目的、即ち、目的有価物を透過液側に回収するか、或いは濃縮液中に濃縮するかといった使用目的や、目的有価物の分子量、その他発酵液等の被処理液の性状などを加味して行われる。
【0023】
なお、図1では、ダイアフィルトレーションによる発酵液からの菌体の分離及び目的有価物の回収を行う場合を例示したが、本発明の膜分離方法は何らこの方法に限定されず、一般的に行われる発酵液からの菌体の分離及び、蛋白質やリパーゼ、セルラーゼ、キシラーゼなどの酵素、生理活性ペプチド等の目的有価物の回収や蛋白質溶液の脱塩濃縮処理等の生物系の被処理液の、濃縮工程と加水工程とからなる膜分離処理に極めて有用である。
【0024】
【実施例】
以下に実施例及び比較例を挙げて本発明をより具体的に説明する。
【0025】
実施例1
図1に示す本発明の方法に従って、発酵液(乾燥菌体濃度:1重量%,目的有価物:分子量約1万8000の酵素)の菌体分離を行った。
【0026】
膜分離装置にはMF中空糸膜モジュール(孔径0.1μm,外径5cm,長さ1m,膜面積1m)を用い、処理温度20℃、モジュール入口圧2.0kg/cm,モジュール出口圧1.5kg/cmの条件でクロスフロー濾過を行った。
【0027】
被処理液貯槽から調整槽に移送した発酵液50Lを膜分離装置に送液し、濃縮液を循環処理する菌体の分離濃縮と、目的有価物の透過液側への回収を行い、その後、循環液がある程度濃縮された段階で加水処理によるダイアフィルトレーションを行い、所定の回収率が達成されるまで処理を継続した。この発酵液50Lの処理で濃縮工程において透過液30Lを回収し、加水工程で透過液40Lを回収した。
【0028】
上記膜分離工程の終了後、膜分離ユニットから濃縮液をブローアウトした。排出された濃縮液(菌体含有廃液)量は20Lであった。
【0029】
次いで、逆洗ポンプにより、膜分離ユニットの透過液側から60℃の市水50Lを10L/分で逆流させることにより膜の逆洗を行った。
【0030】
逆洗終了後、再度上記と同様にして発酵液50Lの膜分離工程、排出工程及び洗浄工程を繰り返し行い、10回の膜分離工程を実施することにより、発酵液500Lを処理した。
【0031】
この処理における各回の膜分離工程の膜の透過流束(濃縮工程の透過流束と加水工程の透過流束との平均値)の変化を図2に示した。
【0032】
比較例1
実施例1において、逆洗水として18℃の市水を用いたこと以外は同様にして処理を行い、同様に透過流束の変化を調べ、結果を図2に示した。
【0033】
比較例2
実施例1において、逆洗を行わず、発酵液500Lを一度に処理したこと以外は同様に処理を行った。即ち、700L容量の調整槽を用い、濃縮工程で透過液300Lを回収し、その後加水工程で透過液400Lを回収し、濃縮液(菌体含有廃液)200Lを排出した。
【0034】
この処理において、発酵液を70L処理する毎に透過流束を調べ、結果を図2に示した。
【0035】
図2より、温水による逆洗を行うことにより、膜の透過流束を高く維持できることがわかる。
【0036】
【発明の効果】
以上詳述した通り、本発明の膜分離方法によれば、発酵液や蛋白質溶液等の生物系の被処理液を膜分離処理するに当り、効果的な逆洗を行って、膜の透過流束を高く維持することができる。このため、膜面積の小さい小型の膜分離設備で処理することができ、また、膜の薬品洗浄頻度を抑えて装置の稼動効率を高めると共に、膜の劣化を防止して膜寿命の延長を図ることができる。
【図面の簡単な説明】
【図1】本発明の膜分離方法の実施の形態を示す系統図である。
【図2】実施例1及び比較例1,2における透過流束の経時変化を示すグラフである。
【符号の説明】
1 被処理液貯槽
2 調整槽
3 膜分離装置
4 透過液受槽
[0001]
TECHNICAL FIELD OF THE INVENTION
The present invention relates to a membrane separation method suitable for separating bacterial cells from a fermentation liquor and recovering valuable resources by a membrane filtration, or for desalting and concentrating a protein solution. The present invention relates to a membrane separation method for maintaining a high permeation flux and reducing the frequency of chemical cleaning of a membrane.
[0002]
[Prior art]
When commercializing valuable products such as enzymes produced by a fermentation method, for example, enzymes such as lipase, cellulase, and xylase, bioactive peptides, and proteins, separating the producing bacteria from the fermentation products and recovering valuable products. There is a need. BACKGROUND ART Conventionally, there is a diatomaceous earth filtration method as a general method for recovering a target valuable substance from a fermentation liquid and separating cells. In the diatomaceous earth filtration method, since a large amount of diatomaceous earth is used as a filter aid or a precoating agent, the cells containing diatomaceous earth are separated. The diatomaceous earth-mixed cells cannot be incinerated and are discarded, so there is a problem with the disposal site.
[0003]
For this reason, as a separation method without using diatomaceous earth, a membrane separation method using an MF (microfiltration) membrane or a UF (ultrafiltration) membrane has been studied. Application is being attempted.
[0004]
Separation of the cells from the fermentation solution by the membrane separation method and recovery of the target valuables include filtration and concentration of the fermentation solution (permeation of valuables and concentration of the cells) and diafiltration (concentration of the concentrated solution by water treatment). (Recovery of valuables remaining on the permeate side). That is, first, the fermented liquor is subjected to membrane separation treatment to collect valuable resources on the permeate side, and at the same time, to concentrate the cells (hereinafter, this may be referred to as a “concentration step”), and the concentration of the cells is increased to some extent. After proceeding, by performing an operation called diafiltration in which membrane separation is continued while gradually adding (water-treating) water to the concentrate side, valuable substances remaining in the concentrate side are transferred to the permeate side. to facilitate recovery (hereinafter, sometimes referred to as "pressurized water process".).
[0005]
However, when a biological liquid such as a fermentation liquid or a protein solution is subjected to membrane separation treatment, the membrane is significantly contaminated by bacteria, proteins, lipids, etc. contained in the liquid to be treated, and the permeation flux of the membrane is increased. However, there is a problem in that the rate of decay decreases early. In particular, as described above, when the concentration step and the water addition step are performed, the highly concentrated liquid is treated in the concentration step, so that the membrane becomes heavily contaminated.
[0006]
Conventionally, in a general membrane separation process, as a countermeasure against the contamination of the membrane, the back surface of the membrane is back-washed by backwashing the washing water from a permeated liquid side (secondary side) to raw water or a concentrated liquid side (primary side). Removal of contaminants or chemical cleaning of the film is employed. In addition, by increasing the film area, film contamination can be relatively reduced. However, the chemical cleaning significantly lowers the operation efficiency of the membrane separation device, and also has problems such as shortening of the membrane life due to deterioration of the membrane and treatment of the chemical cleaning wastewater. Enlarging the membrane area is disadvantageous in terms of cost because the size of the membrane separation equipment increases. Accordingly, it is desirable to reduce the frequency of chemical cleaning of the membrane as much as possible, and to effectively prevent a reduction in the permeation flux of the membrane by backwashing with a minimum membrane area.
[0007]
In general, when backwashing a membrane, a permeate is often used as backwash water.
[0008]
[Problems to be solved by the invention]
However, in the case of membrane separation of fermentation liquid or protein solution, since the permeated liquid contains enzymes and proteins to be recovered, the use of this as backwash water may reduce the recovery rate of the target substance. In addition, they may adhere to the film surface in the backwashing step and cause secondary contamination.
[0009]
From the viewpoint of the backwashing effect, it is preferable to use warm water as the backwashing water.By performing the hot water backwashing, the effect of peeling off the membrane contaminants due to the backwashing can be improved. When the permeate obtained by the membrane separation treatment is heated, valuable substances such as proteins contained in the permeate are denatured, so that the permeate cannot be heated. In addition, by causing the hot water to flow back to the primary side of the membrane separation device, valuables in the primary side liquid containing valuables may be denatured.
[0010]
The present invention solves the above-mentioned conventional problems, and performs effective backwashing to maintain a high permeation flux in the membrane separation treatment of a biologically-treated liquid such as a fermentation solution or a protein solution. It is an object of the present invention to provide a membrane separation method that can perform the method.
[0011]
[Means for Solving the Problems]
The membrane separation method of the present invention is a membrane separation method for a biological liquid to be treated containing cells, proteins, or the like, wherein the liquid to be treated is sent to a membrane separation device, a permeate is taken out , and the concentrated liquid is concentrated. A diafiltration step of performing a membrane separation while adding water to the concentrate side after the concentration step, and a process in the membrane separation apparatus after the first step is completed. A second step of discharging the liquid, and after the second step, a third step of backwashing by supplying warm water consisting of backwashing water other than the permeate from the permeate side of the membrane separation device. The first step, the second step, and the third step are repeatedly performed.
[0012]
In the present invention, after the liquid to be treated in the membrane separation device is drained, backwashing is performed periodically to backflow hot water, so that membrane contaminants are effectively peeled and removed, and the permeation flux of the membrane is increased. Can be maintained.
[0013]
BEST MODE FOR CARRYING OUT THE INVENTION
Hereinafter, embodiments of the present invention will be described in detail with reference to the drawings.
[0014]
FIG. 1 is a system diagram showing an embodiment of the membrane separation method of the present invention.
[0015]
This method is to carry out a recovery of the bacterial cell separation and purpose valuables from the fermentation liquor, was first fed to the adjustment tank 2 by a pump P 1 a predetermined amount of the liquid to be treated to be processed solution storage tank 1 after, the valve V 1 opened to supply the liquid to be treated in the adjustment tank 2 by operating the pump P 2 in the valve V 2, V 3 closed in the membrane separation device 3 in crossflow, a permeate containing the desired valuables It is collected in the permeated liquid receiving tank 4. The concentrated liquid flowing out of the membrane separation device 3 is returned to the adjustment tank 2 and circulated. Along with this, the cells are concentrated on the concentrate side. After it progressed concentrated to a predetermined magnification, diafiltration to further recover valuable materials remaining in the concentrate side by introducing dilution water by operating the pump P 3. In this case, the amount of water and the form of water required for diafiltration are appropriately determined according to the concentration of the target valuables in the concentrate, the rejection of the target valuables by the membrane, and the target recovery rate of the target valuables. Selected. The form of water addition may be continuous water addition or intermittent water addition, but a method of gradually adding an amount of water corresponding to the amount of the permeated liquid while keeping the amount of the concentrated liquid constant is generally used.
[0016]
After the target valuables are collected on the permeate side at a predetermined recovery rate in this way, the above-mentioned membrane separation processing step is terminated, the pumps P 2 and P 3 are stopped, the valve V 3 is opened, and the membrane separation device is opened. The concentrated liquid in the primary side of 3, the concentrated liquid piping and the adjusting tank 2 is discharged out of the system.
[0017]
After the discharge process is completed, the valve V 1 is closed, by operating the pump P 4 is opened valves V 2, the backwash by flowing back to the primary side of the hot water from the secondary side of the membrane separation device 3 performs.
[0018]
The temperature of the hot water used for the backwashing is not particularly limited, and is appropriately set according to the heat resistance of the membrane material, the nature of the stain, and the like. In a normal case, hot water of about 40 to 80 ° C. is used.
[0019]
The backwashing conditions such as the amount of hot water to be fed are not particularly limited and are appropriately determined depending on the degree of dirt. Generally, about 10 to 100 L of hot water is applied to a membrane area of 1 m2. It is preferable that the liquid is sent for about 0.5 to 100 minutes at a liquid sending rate of 1 to 20 L / min per 1 m 2 of area, and backwashed.
[0020]
After the backwashing step is completed, a predetermined amount of the liquid to be treated is again sent from the liquid to be treated storage tank 1 to the adjusting tank 2, and the membrane separation step, the discharging step, and the backwashing step are repeated.
[0021]
In the present invention, since backwashing is performed using warm water, contaminants on the membrane can be effectively washed and removed.However, membrane contamination is particularly remarkable in membrane separation treatment of a biological liquid to be treated. Washing is preferably performed before the permeation flux of the membrane decreases. The backwash interval, properties and membrane separation processing conditions the liquid to be treated, varies depending or model of membrane area and membrane, backwash every time membrane separation liquid to be treated with a membrane area of 1 m 2 per 50~1000L Is preferably performed.
[0022]
As the membrane of the membrane separation device 3, an MF membrane or a UF membrane is used. The membrane material is not particularly limited, and a polyolefin membrane, a polysulfone membrane, a Teflon membrane, a ceramic membrane, or the like is used. Although there is no particular limitation on the membrane type, a hollow fiber, a tubular, a spiral, a plate & frame type membrane module, or the like is generally used. Selection of the MF or UF membrane and selection of the membrane material and membrane type are intended for use, that is, whether the intended valuable is recovered in the permeate side or concentrated in the concentrated solution, or the intended valuable is used. It is carried out in consideration of the molecular weight and other properties of the liquid to be treated such as a fermentation liquid.
[0023]
Although FIG. 1 illustrates the case where the cells are separated from the fermented liquor and the target valuables are collected by diafiltration, the membrane separation method of the present invention is not limited to this method. Biological liquid to be treated such as separation of bacterial cells from fermentation liquor, recovery of target valuables such as proteins, enzymes such as lipase, cellulase and xylase, and physiologically active peptides, and desalting and concentration of protein solution This is extremely useful for a membrane separation treatment comprising a concentration step and a water addition step .
[0024]
【Example】
Hereinafter, the present invention will be described more specifically with reference to Examples and Comparative Examples.
[0025]
Example 1
According to the method of the present invention shown in FIG. 1, cells of the fermented broth (dry bacterial cell concentration: 1% by weight, target valuable substance: enzyme having a molecular weight of about 18,000) were separated.
[0026]
A MF hollow fiber membrane module (pore diameter: 0.1 μm, outer diameter: 5 cm, length: 1 m, membrane area: 1 m 2 ) was used for the membrane separator, processing temperature: 20 ° C., module inlet pressure: 2.0 kg / cm 2 , module outlet pressure: Cross flow filtration was performed under the condition of 1.5 kg / cm 2 .
[0027]
50 L of the fermented liquid transferred from the liquid storage tank to the adjustment tank is sent to a membrane separation device, and the concentrated liquid is separated and concentrated for circulating the cells, and the target valuables are collected on the permeate side. At the stage where the circulating liquid was concentrated to some extent, diafiltration by water treatment was performed, and the treatment was continued until a predetermined recovery rate was achieved. In the treatment of 50 L of the fermentation liquid, 30 L of the permeate was recovered in the concentration step, and 40 L of the permeate was recovered in the water addition step.
[0028]
After the completion of the membrane separation step, the concentrate was blown out from the membrane separation unit. The amount of the discharged concentrated liquid (cell-containing waste liquid) was 20 L.
[0029]
Then, 50 L of city water at 60 ° C. was flowed back from the permeated liquid side of the membrane separation unit at a rate of 10 L / min with a back washing pump to back wash the membrane.
[0030]
After the backwash was completed, the membrane separation step, discharge step, and washing step of 50 L of the fermentation liquor were repeated in the same manner as described above, and 500 L of the fermentation liquor was treated by performing 10 membrane separation steps.
[0031]
FIG. 2 shows the change in the permeation flux of the membrane in each of the membrane separation steps (the average value of the permeation flux in the concentration step and the permeation flux in the water addition step) in this treatment.
[0032]
Comparative Example 1
In Example 1, the treatment was carried out in the same manner except that city water at 18 ° C. was used as the backwash water, and the change in the permeation flux was examined in the same manner. The results are shown in FIG.
[0033]
Comparative Example 2
In Example 1, the same treatment was performed except that 500 L of the fermented liquor was treated at a time without backwashing. That is, using a 700 L capacity adjusting tank, 300 L of the permeate was recovered in the concentration step, 400 L of the permeate was recovered in the water addition step, and 200 L of the concentrate (cell-containing waste liquid) was discharged.
[0034]
In this process, the permeation flux was checked every time 70 L of the fermentation liquor was processed, and the results are shown in FIG.
[0035]
From FIG. 2, it can be seen that by performing backwashing with warm water, the permeation flux of the membrane can be maintained high.
[0036]
【The invention's effect】
As described in detail above, according to the membrane separation method of the present invention, when performing a membrane separation treatment on a biological target liquid such as a fermentation solution or a protein solution, an effective backwash is performed, and the permeation flow of the membrane is performed. The bundle can be kept high. For this reason, the treatment can be performed with a small-sized membrane separation equipment having a small membrane area. In addition, the frequency of chemical cleaning of the membrane can be reduced to increase the operation efficiency of the apparatus, and the deterioration of the membrane can be prevented to extend the life of the membrane. be able to.
[Brief description of the drawings]
FIG. 1 is a system diagram showing an embodiment of a membrane separation method of the present invention.
FIG. 2 is a graph showing a temporal change of a permeation flux in Example 1 and Comparative Examples 1 and 2.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 Treatment liquid storage tank 2 Adjustment tank 3 Membrane separation device 4 Permeate receiving tank

Claims (3)

菌体又は蛋白質等を含む生物系の被処理液の膜分離方法において、
該被処理液を膜分離装置に送液して透過液を取り出すと共に濃縮液側を濃縮する濃縮工程と、該濃縮工程後に濃縮液側に水を添加しながら膜分離を行うダイアフィルトレーションとからなる第1の工程と、
該第1の工程終了後に該膜分離装置内の被処理液を排出する第2の工程と、
該第2の工程後、膜分離装置の透過液側から、透過液以外の逆洗用水からなる温水を供給して逆洗する第3の工程とを有し、
該第1の工程、第2の工程及び第3の工程を繰り返し行うことを特徴とする膜分離方法。
In a membrane separation method of a biological liquid to be treated containing cells or proteins,
A concentration step in which the liquid to be treated is sent to a membrane separation device to take out a permeate and concentrate the concentrated solution side, and a diafiltration for performing membrane separation while adding water to the concentrated solution side after the concentration step. A first step consisting of :
A second step of discharging the liquid to be treated in the membrane separation device after the first step,
After the second step, a third step of backwashing by supplying hot water comprising backwashing water other than the permeate from the permeate side of the membrane separation device,
A membrane separation method, wherein the first step, the second step, and the third step are repeatedly performed.
該第3の工程において、膜面積1mIn the third step, the film area is 1 m 2 に対して10〜100Lの温水を膜面積1m10 to 100 L of warm water for 1 m of membrane area 2 当り1〜20L/minの送液量で0.5〜100分送液して逆洗することを特徴とする請求項1に記載の膜分離方法。The membrane separation method according to claim 1, wherein the liquid is fed for 0.5 to 100 minutes at a liquid feed rate of 1 to 20 L / min and backwashed. 該第1の工程において、膜面積1mIn the first step, the film area is 1 m 2 当り50〜1000Lの被処理液を膜分離処理する毎に該2の工程及び第3の工程を行うことを特徴とする請求項1又は2に記載の膜分離方法。The membrane separation method according to claim 1 or 2, wherein the second step and the third step are performed each time the liquid to be treated is subjected to membrane separation processing in an amount of 50 to 1000 L.
JP12729599A 1999-05-07 1999-05-07 Membrane separation method Expired - Fee Related JP3577992B2 (en)

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WO2012036003A1 (en) 2010-09-14 2012-03-22 東レ株式会社 Production method for chemicals by continuous fermentation

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