JPH10314552A - Hollow fiber membrane cartridge for capturing protozoa and method for capturing and recovering protozoa - Google Patents

Hollow fiber membrane cartridge for capturing protozoa and method for capturing and recovering protozoa

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Publication number
JPH10314552A
JPH10314552A JP12595297A JP12595297A JPH10314552A JP H10314552 A JPH10314552 A JP H10314552A JP 12595297 A JP12595297 A JP 12595297A JP 12595297 A JP12595297 A JP 12595297A JP H10314552 A JPH10314552 A JP H10314552A
Authority
JP
Japan
Prior art keywords
hollow fiber
fiber membrane
protozoa
water
capturing
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
Application number
JP12595297A
Other languages
Japanese (ja)
Inventor
Ikuo Igami
生雄 伊神
Akihiro Sakimae
明宏 崎前
Yoshie Tanizaki
美江 谷崎
Masanao Kobuke
正直 小泓
Hiroshi Tasaka
広 田阪
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Mitsubishi Chemical Corp
Original Assignee
Mitsubishi Rayon Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Mitsubishi Rayon Co Ltd filed Critical Mitsubishi Rayon Co Ltd
Priority to JP12595297A priority Critical patent/JPH10314552A/en
Publication of JPH10314552A publication Critical patent/JPH10314552A/en
Pending legal-status Critical Current

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Abstract

(57)【要約】 【課題】 短時間かつ高効率で、試水中に含まれる原虫
の捕捉回収を行うための、中空糸膜モジュール及び原虫
の捕捉回収方法を提供する。 【解決手段】 試水中に含まれる原虫の捕捉回収を行う
に際し、最大孔径2.0μm以下の微細孔を有する多孔
質中空糸膜が配設された中空糸膜カートリッジに試水を
通水し濾過することにより、多孔質中空糸膜の一次側で
試水の濃縮を行った後、原虫を含む濃縮水及び/又は多
孔質中空糸膜の表面に堆積した原虫を含む濁度成分を回
収する。
PROBLEM TO BE SOLVED: To provide a hollow fiber membrane module and a method for capturing and collecting protozoa contained in a test water in a short time and with high efficiency. SOLUTION: When capturing and recovering protozoa contained in a sample water, the sample water is passed through a hollow fiber membrane cartridge provided with a porous hollow fiber membrane having micropores having a maximum pore diameter of 2.0 μm or less, and filtered. After concentrating the test water on the primary side of the porous hollow fiber membrane, concentrated water containing protozoa and / or turbidity components containing protozoa deposited on the surface of the porous hollow fiber membrane are recovered.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、試水に含まれる原
虫を捕捉回収するための原虫捕捉用中空糸膜カートリッ
ジ及び原虫の捕捉回収方法に関するものである。
The present invention relates to a hollow fiber membrane cartridge for capturing protozoa for capturing and recovering protozoa contained in a test water, and a method for capturing and recovering protozoa.

【0002】[0002]

【従来の技術】近年、牛、豚等に寄生する原虫であるク
リプトスポリジウムが水道水中に混入し、大量の感染者
を出す事態がしばしば起こっている。クリプトスポリジ
ウムが水道水中に混入する原因は、畜産農家の汚水が表
流水に流れ込むことにより、水道水の水源が汚染される
ためといわれているがはっきりしたことは分かっていな
い。
2. Description of the Related Art In recent years, cryptosporidium, which is a protozoan parasite in cattle, pigs, and the like, is often mixed in tap water to cause a large number of infected persons. The reason that Cryptosporidium is mixed into tap water is said to be due to the contamination of tap water sources by the flow of sewage from livestock farmers into surface water, but it has not been clarified yet.

【0003】クリプトスポリジウムはコクシジウム目の
病原性原虫であり、河川、湖沼等の自然環境中ではオー
シスト(同じくコクシジウム目の病原性原虫であるジア
ルジアの場合はシスト)と呼ばれる長径7〜8μm、短
径5〜6μmの俵型の膜に包まれているため、薬剤に強
く通常の塩素消毒では効果が無く、又凝集沈澱等の濾過
を行っても浄水場で完全に除去することは非常に困難で
ある。
[0003] Cryptosporidium is a pathogenic protozoan of the order Coccidiomycetes, and in the natural environment such as rivers and lakes, is called an oocyst (cyst in the case of Giardia, which is also a pathogenic protozoan of the order Coccidia), having a long diameter of 7 to 8 µm and a short diameter. Because it is wrapped in a 5-6 μm bale-shaped membrane, it is strong against chemicals and has no effect with ordinary chlorine disinfection, and it is very difficult to completely remove it in a water purification plant even if filtration such as coagulation and sedimentation is performed. is there.

【0004】オーシストは内部に4個のスポロゾイドを
内蔵しており、体内に摂取されたオーシストは腸内でス
ポロゾイドが脱嚢し腸内壁に寄生する。感染者の主な症
状は水様下痢であり、免疫力の弱い人は死に至ることも
ある。水道水中に含まれる原虫を検出する方法として
は、1996年9月30日、厚生省より公表された「水
道におけるクリプトスポリジウム暫定対策指針−別添3
−水道水に関するクリプトスポリジウムのオーシストの
検出のための暫定的な試験方法」に、オーシストの捕捉
回収方法が記載がなされている。
[0004] The oocyst contains four sporozoids therein, and in the oocyst ingested into the body, the sporozoid is excysted in the intestine and parasitises the inner wall of the intestine. The main symptom of infected people is watery diarrhea, and people with weak immunity may die. A method for detecting protozoa contained in tap water is described in “Temporary Guideline for Cryptosporidium in Water Supply-Appendix 3” published by the Ministry of Health and Welfare on September 30, 1996.
"Temporary test method for detection of Cryptosporidium oocysts in tap water" describes a method for capturing and recovering oocysts.

【0005】これらの内、試水中の濁質の捕捉回収に関
する部分の概略を以下に記す。 1.試水の採取…給水栓、配水池及び浄水池の水は40
L以上、河川水等水道原水は概ね10L採取する。 2.膜面捕捉…セルロースアセテートのディスクフィル
ター(フィルター径47又は90mm、孔径1.2μm
以下)を濾過器にセットし、試水を濾過する。 3.捕捉物の誘出…濁質を捕捉したディスクフィルター
を沈澱管(15又は50ml)に挿入し、99.5%の
アセトンを加えフィルターを溶解する。 4.精製液置換…2500〜3000rpmで10分間
遠心沈澱し、上清のアセトン液を吸引除去する。得られ
た沈渣に再度アセトンを加え、再懸濁させた後遠心沈澱
を1〜2回繰り返す。得られた沈渣に精製液(二段蒸留
水を孔径0.45μm以下のフィルターで濾過した液)
を加えて、再懸濁させた後同様に遠心沈澱を行う。 5.PBS液置換…精製液での遠心沈澱後、上清液を吸
引除去し、PBS液(リン酸緩衝生理食塩水)を加え、
再懸濁させた後同様に遠心沈澱する。上清液を吸引除去
し、適当量のPBS液を添加し再懸濁させ試料とする。
[0005] Among them, an outline of a portion relating to capture and recovery of turbid matter in a test water is described below. 1. Collection of test water: 40 tap water, water distribution reservoir and clean water reservoir
About 10L of raw water such as river water should be collected. 2. Membrane surface capture: cellulose acetate disc filter (filter diameter 47 or 90 mm, pore diameter 1.2 μm
) Is set in a filter, and the sample water is filtered. 3. Extraction of captured matter: Insert the disk filter capturing the suspended matter into a precipitation tube (15 or 50 ml), add 99.5% acetone, and dissolve the filter. 4. Purification liquid replacement: Centrifugation is performed at 2500 to 3000 rpm for 10 minutes, and the acetone solution of the supernatant is removed by suction. Acetone is added again to the obtained sediment to re-suspend, and centrifugal sedimentation is repeated once or twice. Purified liquid (liquid obtained by filtering double-distilled water with a filter having a pore size of 0.45 μm or less) on the obtained sediment
And resuspended, followed by centrifugation in the same manner. 5. Replacement of PBS solution: After centrifugal precipitation with the purified solution, the supernatant was removed by suction, and PBS solution (phosphate buffered saline) was added.
After resuspension, centrifuge in the same manner. The supernatant is removed by suction, an appropriate amount of a PBS solution is added, and the suspension is resuspended to prepare a sample.

【0006】この様な方法で試水中に含まれる原虫の捕
捉回収を行おうとすると、濾過開始からPBS液置換ま
でで、水道水を使用しても2〜3時間を要することとな
る。その後捕捉物をフィルター上に再度捕捉し、間接蛍
光抗体法により蛍光染色し、プレパラートを作製し、落
射蛍光顕微鏡により観察、計数する。又、懸濁物質の多
い試料は、染色工程にはいる前に、ショ糖液を用いた密
度勾配法により捕捉物を精製する。
[0006] In order to capture and recover the parasites contained in the test water by such a method, it takes two to three hours from the start of filtration to the replacement of the PBS solution even if tap water is used. Thereafter, the captured matter is captured again on the filter, fluorescently stained by an indirect fluorescent antibody method, a preparation is prepared, and observed and counted by an epifluorescence microscope. In the case of a sample having a large amount of suspended substances, the captured matter is purified by a density gradient method using a sucrose solution before entering the staining step.

【0007】[0007]

【発明が解決しようとする課題】しかしながら、前述し
た方法で原虫の捕捉回収を行うと、 1.フィルターの目詰まりが発生するため早期に濾過速
度が低下する、 2.フィルターの膜面積が小さいため、大量の試水を効
率よく通水することができない、 といった不都合が発生する。
However, when the protozoa are captured and recovered by the method described above, 1. The filtration speed is reduced early due to clogging of the filter. Since the membrane area of the filter is small, a large amount of test water cannot be passed efficiently.

【0008】[0008]

【課題を解決するための手段】本発明は、これらの不都
合に鑑みてなされたものであり、短時間かつ高効率で、
試水中に含まれる原虫の捕捉回収を行うための、原虫捕
捉用中空糸膜カートリッジ及び原虫の捕捉回収方法の開
発を目的としてなされたものである。
SUMMARY OF THE INVENTION The present invention has been made in view of these inconveniences, and has been developed in a short time and with high efficiency.
The purpose of the present invention is to develop a hollow fiber membrane cartridge for capturing protozoa and a method for capturing and recovering protozoa for capturing and recovering protozoa contained in the test water.

【0009】即ち、本発明の要旨は、外筒内部に多孔質
中空糸膜の両端が開口してポッティングされ、前記外筒
には、多孔質中空糸膜の外表面側に試水を供給する給水
口と、多孔質中空糸膜の開口端に連通して透過水を取り
出す出水口が配設されたことを特徴とする原虫捕捉用中
空糸膜カートリッジにある。
That is, the gist of the present invention is that both ends of a porous hollow fiber membrane are opened and potted inside an outer cylinder, and a water sample is supplied to the outer cylinder on the outer surface side of the porous hollow fiber membrane. A protozoan-trapping hollow fiber membrane cartridge is provided with a water supply port and a water outlet for taking out permeated water by communicating with an open end of the porous hollow fiber membrane.

【0010】また、本発明の要旨は、外筒内部に多孔質
中空糸膜の両端が別々に開口してポッティングされ、前
記外筒には、多孔質中空糸膜の一方の開口端に試水を供
給する給水口と、多孔質中空糸膜の外表面側に連通して
透過水を取り出す出水口とが配設され、多孔質中空糸膜
の他の開口端から濃縮水を取り出すことを特徴とする原
虫捕捉用中空糸膜カートリッジにある。
The gist of the present invention is that the both ends of the porous hollow fiber membrane are separately opened and potted inside the outer cylinder, and the outer cylinder is provided with a sample at one open end of the porous hollow fiber membrane. And a water outlet for taking out permeated water by communicating with the outer surface side of the porous hollow fiber membrane, and extracting concentrated water from another open end of the porous hollow fiber membrane. And a hollow fiber membrane cartridge for capturing protozoa.

【0011】更に、本発明の要旨は、試水中に含まれる
原虫の捕捉回収を行うに際し、最大孔径2.0μm以下
の微細孔を有する多孔質中空糸膜が配設された中空糸膜
カートリッジに試水を通水し濾過することにより、多孔
質中空糸膜の一次側で試水の濃縮を行った後、原虫を含
む濃縮水及び/又は多孔質中空糸膜の表面に堆積した原
虫を含む濁度成分を回収することを特徴とする原虫の捕
捉回収方法にある。
Further, the gist of the present invention is to provide a hollow fiber membrane cartridge provided with a porous hollow fiber membrane having fine pores having a maximum pore diameter of 2.0 μm or less when capturing and recovering protozoa contained in test water. After passing the test water and filtering, the test water is concentrated on the primary side of the porous hollow fiber membrane, and then the concentrated water containing the protozoa and / or the protozoa deposited on the surface of the porous hollow fiber membrane are contained. A method for capturing and recovering protozoa, comprising recovering a turbidity component.

【0012】中空糸膜カートリッジを、試験管攪拌機等
により振動させながら試水を通水し、濾過を行うと、膜
表面に補足された濁度成分が振り落とされ、膜表面に固
着しにくくなり好ましい。
When the hollow fiber membrane cartridge is vibrated by a test tube stirrer or the like while passing test water through and filtering is performed, the turbidity component trapped on the membrane surface is shaken off, making it difficult to adhere to the membrane surface. preferable.

【0013】また、中空糸膜カートリッジに試水を通水
するに際して、試水を一定時間(或いは一定量)通水し
た後、一定時間停止する間欠通水すると、中空糸膜表面
に濁度成分が固着しにくくなるため好ましい。
When the sample water is passed through the hollow fiber membrane cartridge, the sample water is passed for a certain time (or a fixed amount) and then stopped for a certain time. Are preferred because they are less likely to stick.

【0014】また、中空糸膜カートリッジ内の一次側の
空間で液相を攪拌又は循環させながら試水を通水し、濾
過すると、膜表面に濁度成分が固着しにくくなり好まし
い。
Further, it is preferable that the turbidity component hardly adheres to the membrane surface when the sample water is passed through while stirring or circulating the liquid phase in the primary space in the hollow fiber membrane cartridge and then filtered.

【0015】また、多孔質中空糸膜の二次側を吸引する
ことにより試水の濾過を行うと、特に濁度の高い河川水
等を試水として用いて原虫の回収を行う際に、中空糸膜
の目詰まりが発生しにくく好ましい。
[0015] In addition, when the sample water is filtered by suctioning the secondary side of the porous hollow fiber membrane, especially when the protozoa is collected using river water or the like having high turbidity as the test water, the hollow sample is filtered. It is preferable that clogging of the yarn membrane does not easily occur.

【0016】また、2kg/cm2以下の膜間差圧で試
水の濾過を行うと、多孔質中空糸膜表面の目詰まりが発
生しにくく好ましい。
It is preferable that the filtration of the sample water be performed at a transmembrane pressure difference of 2 kg / cm 2 or less, since the clogging of the surface of the porous hollow fiber membrane does not easily occur.

【0017】多孔質中空糸膜表面に堆積した原虫を含む
濁度成分を回収するに際して、洗浄液中に多孔質中空糸
膜を浸漬し、中空糸膜部をもみ洗いすることにより膜表
面の濁度成分を洗浄液中に誘出させると、膜面に固着し
た濁度成分や、膜間に入り込んだ濁度成分を誘出させる
ことができ、好ましい。
In recovering the turbidity component containing protozoa deposited on the surface of the porous hollow fiber membrane, the porous hollow fiber membrane is immersed in a washing solution, and the hollow fiber membrane portion is rinsed to remove the turbidity of the membrane surface. It is preferable to induce the components into the cleaning liquid, because the turbidity components fixed to the membrane surface and the turbidity components that have entered between the membranes can be induced.

【0018】また、多孔質中空糸膜表面に堆積した原虫
を含む濁度成分を回収するに際して、洗浄液槽内の洗浄
液中に多孔質中空糸膜を浸漬し、多孔質中空糸膜を振動
させることにより、膜表面の濁度成分を洗浄液中に誘出
させると、原虫の破壊等が少なくなる。
Further, when recovering the turbidity component containing protozoa deposited on the surface of the porous hollow fiber membrane, the porous hollow fiber membrane is immersed in a cleaning solution in a cleaning solution tank, and the porous hollow fiber membrane is vibrated. Thus, when the turbidity component on the membrane surface is induced into the washing solution, the destruction of the protozoa and the like are reduced.

【0019】更に好ましくは、多孔質中空糸膜表面に堆
積した原虫を含む濁度成分を回収するに際して、超音波
洗浄機内の洗浄液中に該多孔質中空糸膜を浸漬し、超音
波洗浄により膜表面の濁度成分を洗浄液中に誘出させる
と、洗浄効率が向上する。
More preferably, in recovering the turbid components including protozoa deposited on the surface of the porous hollow fiber membrane, the porous hollow fiber membrane is immersed in a cleaning solution in an ultrasonic cleaner, and the membrane is subjected to ultrasonic cleaning. When the turbidity component on the surface is introduced into the cleaning solution, the cleaning efficiency is improved.

【0020】また、多孔質中空糸膜表面に堆積した原虫
を含む濁度成分を回収するに際して、多孔質中空糸膜部
を中空糸膜カートリッジから切断し、切断した多孔質中
空糸膜のみを洗浄液中で洗浄することにより、膜表面の
濁度成分を洗浄液中に誘出させると、中空糸膜間の距離
が広がり、洗浄効率が向上するので好ましい。
In collecting turbidity components including protozoa deposited on the surface of the porous hollow fiber membrane, the porous hollow fiber membrane is cut from the hollow fiber membrane cartridge, and only the cut porous hollow fiber membrane is washed. It is preferable to induce the turbidity component on the membrane surface into the washing solution by washing in the inside, since the distance between the hollow fiber membranes is increased and the washing efficiency is improved.

【0021】また、多孔質中空糸膜表面に堆積した原虫
を含む濁度成分を回収するに際して、試水濾過時の逆方
向に洗浄液を通水することにより、膜表面の濁度成分を
洗浄液中に誘出させること、微細孔に入り込んだ濁度成
分をも回収することができる。
When the turbidity component including protozoa deposited on the surface of the porous hollow fiber membrane is collected, the turbidity component on the membrane surface is passed through the washing solution by passing the washing solution in the reverse direction of the sample filtration. And the turbidity component that has entered the micropores can also be recovered.

【0022】また、多孔質中空糸膜表面に堆積した原虫
を含む濁度成分を回収するに際して、洗浄液を多孔質中
空糸膜の一次側に循環通水することにより濁度成分を洗
浄液中に誘出させると、膜表面を水流により洗浄するこ
とにより、原虫への衝撃が少なくなる。
In recovering the turbid component including protozoa deposited on the surface of the porous hollow fiber membrane, the washing solution is circulated through the primary side of the porous hollow fiber membrane to induce the turbid component into the washing solution. When released, the impact on the protozoa is reduced by washing the membrane surface with a stream of water.

【0023】好ましくは、洗浄液中に界面活性剤が添加
されていると、濁度成分の回収率が向上する。更に好ま
しくは、洗浄液中に消泡剤が添加されていると、泡の発
生による回収率の低下を防止することができる。
Preferably, when a surfactant is added to the washing solution, the recovery of the turbidity component is improved. More preferably, if an antifoaming agent is added to the cleaning liquid, it is possible to prevent a reduction in the recovery rate due to the generation of foam.

【0024】[0024]

【発明の実施の形態】以下、本発明の実施形態を図面に
より説明する。図1は、本発明の原虫捕捉用中空糸膜カ
ートリッジの一例を模式的に示す断面図である。U字状
に折り曲げられた最大孔径が2.0μm以下の多孔質中
空糸膜11の片端が、ポッティング材12により、中空
部を開口した状態で、キャップ16内に支持固定されて
おり、開口端は、多孔質中空糸膜11を透過した透過水
を外部に送水する出水口13に連通する。外筒17は、
その下方に、試水の給水口14を有しており、キャップ
16と脱着可能に係合されてなる。また、キャップ16
と外筒17との間の係合部にはO−リング15が配置さ
れる。
Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 is a cross-sectional view schematically showing an example of the hollow fiber membrane cartridge for capturing protozoa of the present invention. One end of a U-shaped porous hollow fiber membrane 11 having a maximum pore diameter of 2.0 μm or less is supported and fixed in a cap 16 with a hollow portion opened by a potting material 12. Is connected to a water outlet 13 for sending permeated water that has passed through the porous hollow fiber membrane 11 to the outside. The outer cylinder 17 is
A water supply port 14 for the sample water is provided below it, and is detachably engaged with the cap 16. Also, the cap 16
An O-ring 15 is disposed at an engagement portion between the outer cylinder 17 and the outer cylinder 17.

【0025】この中空糸膜カートリッジに、原虫を含む
試水を給水口14より外筒17に通水し、吸引濾過、或
いは加圧濾過により試水の濾過を行う。濾過方式を吸引
濾過とすると、濁度の高い河川水等を試水として用いて
原虫の回収を行う際に、多孔質中空糸膜の目詰まりが発
生しにくく、好ましい。
A sample water containing protozoa is passed through the hollow fiber membrane cartridge from the water supply port 14 to the outer cylinder 17, and the sample water is filtered by suction filtration or pressure filtration. When the filtration method is suction filtration, the clogging of the porous hollow fiber membrane does not easily occur when the protozoa is recovered using river water having high turbidity as a test water, which is preferable.

【0026】原虫は多孔質中空糸膜の一次側で濃縮され
るので、これを所定量まで濾過した後に濃縮水として原
虫を回収するか、或いは試水の全量濾過を行った後、多
孔質膜表面に堆積した原虫を含む濁度成分の回収を行
う。なお、濃縮水として原虫の回収を行う場合において
も、濾過終了後に膜表面に堆積した原虫を含む濁度成分
を更に回収することが、原虫の回収効率を上げる観点か
ら好ましい。
Since the protozoa are concentrated on the primary side of the porous hollow fiber membrane, the protozoa can be filtered to a predetermined amount and then recovered as concentrated water, or the whole sample can be filtered and the porous membrane can be filtered. The turbidity components including protozoa deposited on the surface are collected. In addition, even when the protozoa is collected as concentrated water, it is preferable to further collect the turbidity components including the protozoa deposited on the membrane surface after the filtration, from the viewpoint of improving the collection efficiency of the protozoa.

【0027】その最大孔径が2.0μm以下である多孔
質中空糸膜を用いて原虫を含む試水の濾過を行うことに
より、従来の回収方法に比較して、膜面積を多くとるこ
とができ、容積効率が向上するとともに、大量の試水の
濾過を短時間かつ高回収効率で濾過することができる。
この際、2kg/cm2以下の膜間差圧で試水の濾過を
行うと、多孔質中空糸膜表面の目詰まりが発生しにくく
好ましい。
[0027] Filtration of a sample containing protozoa using a porous hollow fiber membrane having a maximum pore diameter of 2.0 µm or less can increase the membrane area as compared with a conventional recovery method. In addition, the volumetric efficiency can be improved, and a large amount of sample water can be filtered in a short time and with high recovery efficiency.
At this time, it is preferable that the sample water be filtered at a transmembrane pressure difference of 2 kg / cm 2 or less, since clogging of the surface of the porous hollow fiber membrane does not easily occur.

【0028】試水を中空糸膜カートリッジに通水するに
際しては、中空糸膜カートリッジを、試験管撹拌機等に
より振動させながら通水を行うと、膜表面に捕捉された
濁度成分が振り落とされ、膜表面に固着しにくくなるた
め好ましい。
When the sample water is passed through the hollow fiber membrane cartridge while the hollow fiber membrane cartridge is vibrated with a test tube stirrer or the like, the turbidity component trapped on the membrane surface is shaken off. This is preferable because it is difficult to adhere to the film surface.

【0029】また、中空糸膜カートリッジに試水を通水
するに際して、試水を一定時間(或いは一定量)通水し
た後、一定時間停止する間欠通水を行うと、中空糸膜表
面に濁度成分が固着しにくくなるため好ましい。
When the sample water is passed through the hollow fiber membrane cartridge, the sample water is passed for a certain time (or a fixed amount), and then intermittent water flow is stopped for a certain time. It is preferable because the temperature component hardly adheres.

【0030】中空糸膜表面に堆積した原虫を含む濁度成
分を回収するに際しては、多孔質中空糸膜を洗浄液中に
浸漬し、もみ洗いすると、膜面に固着した濁度成分や、
膜間に入り込んだ濁度成分を誘出させることができ、好
ましい。或いは、多孔質中空糸膜を洗浄液中に浸漬し、
多孔質中空糸膜を振動させることにより濁度成分を洗浄
液中の誘出させると、もみ洗いに使用する器具等による
物理的な衝撃が少なく、原虫の破壊等の危険性が少なく
なる。
When recovering the turbidity component containing protozoa deposited on the surface of the hollow fiber membrane, the porous hollow fiber membrane is immersed in a washing solution and washed with a fibrous material.
The turbidity component that has entered between the membranes can be induced, which is preferable. Alternatively, immerse the porous hollow fiber membrane in the cleaning solution,
When the turbidity component is induced in the cleaning liquid by vibrating the porous hollow fiber membrane, physical shock due to utensils and the like used for fir washing is reduced, and the risk of destruction of the parasite is reduced.

【0031】更に好ましくは、多孔質中空糸膜を超音波
洗浄機内に浸漬し、超音波洗浄による洗浄を行うと、微
多孔質中空糸膜に微細な振動が与えられ、洗浄効率が向
上するため好ましいが、濁度成分が、超音波により破壊
される可能性がある場合には、振とう機のような振動攪
拌機で振動を与えるのがよい。
More preferably, when the porous hollow fiber membrane is immersed in an ultrasonic cleaner and cleaned by ultrasonic cleaning, fine vibrations are given to the microporous hollow fiber membrane, and the cleaning efficiency is improved. Although it is preferable, when there is a possibility that the turbidity component is destroyed by ultrasonic waves, it is preferable to apply vibration with a vibration stirrer such as a shaker.

【0032】尚、これらの方法で多孔質中空糸膜表面の
濁度成分の回収を行うに際しては、中空糸膜カートリッ
ジから中空糸膜を切断し、中空糸膜のみを洗浄液中で洗
浄すると、中空糸膜間の間隔が広がり、洗浄効率が向上
するので好ましい。
When the turbidity component on the surface of the porous hollow fiber membrane is recovered by these methods, the hollow fiber membrane is cut from the hollow fiber membrane cartridge, and only the hollow fiber membrane is washed in a washing solution. This is preferable because the interval between the yarn membranes is increased and the washing efficiency is improved.

【0033】また、多孔質中空糸膜表面に堆積した濁度
成分の回収を行うに際しては、洗浄液を、試水の濾過時
とは逆方向に通水することにより、膜表面の濁度成分を
誘出させても良い。この様な方法を用いると、微細孔に
入り込んだ濁度成分をも回収することができる。或い
は、洗浄液を、中空糸膜の一次側で循環通水することに
より、膜表面の濁度成分を誘出させてもよい。この様な
方法を用いると、膜表面を水流により洗浄することにな
り、原虫への衝撃が少なくなる。
When the turbidity component deposited on the surface of the porous hollow fiber membrane is recovered, the washing solution is passed through in the opposite direction to the filtration of the sample water to remove the turbidity component on the membrane surface. You may be invited. By using such a method, the turbidity component that has entered the micropores can also be recovered. Alternatively, the turbidity component on the membrane surface may be induced by circulating the washing liquid on the primary side of the hollow fiber membrane. When such a method is used, the membrane surface is washed with a water flow, and the impact on the protozoa is reduced.

【0034】膜表面の洗浄に用いる洗浄液には、界面活
性剤を添加すると、濁度成分の回収効率が向上し、好ま
しい。また、洗浄液に消泡剤を添加すると、泡の発生に
より外筒壁面に付着する原虫が減少するので、回収率が
上がり好ましい。得られた回収液は遠沈管に移し、遠心
分離器により原虫を固液分離させる。
It is preferable to add a surfactant to the cleaning solution used for cleaning the membrane surface, because the efficiency of recovering the turbidity component is improved. In addition, when an antifoaming agent is added to the cleaning solution, the number of protozoa attached to the outer cylinder wall surface due to the generation of bubbles is reduced, and the recovery rate is preferably increased. The obtained recovered liquid is transferred to a centrifuge tube, and the protozoa are separated into solid and liquid by a centrifuge.

【0035】図2は、本発明の原虫捕捉用中空糸膜カー
トリッジの他の形態例を模式的に示す断面図である。キ
ャップ21はその上方に給水口22及び出水口23を有
している。出水口23はホルダー部26に連通してお
り、該ホルダー部には、U字状に折り曲げられた複数本
の多孔質中空糸膜24の中空部が開口状態を保つよう支
持固定されたポッティング材25が配設される。また、
濃縮水を収容する外筒27は、キャップ21に着脱可能
に係合される。外筒27として遠心分離器の遠沈管とし
て共用することがでるものを用いると、遠心分離器のロ
ーターにそのまま挿入して遠心分離を行うことができる
ので、作業時間を短縮することが可能である。
FIG. 2 is a sectional view schematically showing another embodiment of the hollow fiber membrane cartridge for capturing protozoa of the present invention. The cap 21 has a water supply port 22 and a water outlet 23 above it. The water outlet 23 communicates with a holder 26, in which a hollow portion of a plurality of U-shaped porous hollow fiber membranes 24 is supported and fixed so as to maintain an open state. 25 are provided. Also,
The outer cylinder 27 containing the concentrated water is detachably engaged with the cap 21. If a tube that can be commonly used as a centrifuge centrifuge is used as the outer cylinder 27, centrifugation can be performed by directly inserting the centrifuge into the rotor of the centrifuge, so that the operation time can be reduced. .

【0036】図3は、本発明の原虫捕捉用中空糸膜カー
トリッジの他の形態例を模式的に示す断面図である。外
筒33はその側方に、多孔質中空糸膜を透過した透過水
を取り出す出水口32が配設されるとともに、その内部
に複数本の多孔質中空糸膜34がその両端で開口状態を
保ちながらポッティング材35により支持固定される。
FIG. 3 is a sectional view schematically showing another embodiment of the hollow fiber membrane cartridge for capturing protozoa of the present invention. A water outlet 32 for taking out permeated water that has passed through the porous hollow fiber membrane is provided on the side of the outer cylinder 33, and a plurality of porous hollow fiber membranes 34 are opened inside at both ends thereof. It is supported and fixed by the potting material 35 while keeping it.

【0037】中空糸膜の一方の開口端部は中空糸膜34
の中空部に試水を通水するための給水口36に連通して
おり、他方の端部には、濃縮水を収容するための集水筒
37の内部に連通する。外筒と集水筒とは、外筒の下方
に取り付けられたキャップ38と、集水筒とを係合させ
ることにより結合される。
One open end of the hollow fiber membrane is
Is connected to a water supply port 36 for passing a test water through the hollow portion, and the other end thereof is connected to an inside of a water collecting cylinder 37 for storing concentrated water. The outer cylinder and the water collecting cylinder are connected by engaging a cap 38 attached below the outer cylinder with the water collecting cylinder.

【0038】また、キャップ38には集水筒37内の空
間と、集水筒37外の空間を連通させる疎水性の多孔質
材39が設けられてなる。この疎水性の多孔質材39は
外筒37内部の空間に開口する中空糸膜カートリッジ3
1の開口端面よりも上方に取り付けることが好ましい。
The cap 38 is provided with a hydrophobic porous material 39 for communicating the space inside the water collecting tube 37 with the space outside the water collecting tube 37. The hollow fiber membrane cartridge 3 that opens into the space inside the outer cylinder 37 is made of the hydrophobic porous material 39.
It is preferable to attach the opening above the opening end face of the first opening.

【0039】図4は、本発明の原虫捕捉用原虫捕捉用中
空糸膜カートリッジの他の形態例を模式的に示す断面図
である。外筒41は給水口42及び循環水出口43を有
する容器であり、容器内にはU字状に折り曲げられた複
数本の多孔質中空糸膜44の中空部が開口状態を保つよ
うポッティング材45で支持固定された中空糸膜が配置
されてなる。ポッティング部45の開口端面は多孔質中
空糸膜を透過した透過水の出水口46が連通する。
FIG. 4 is a cross-sectional view schematically showing another embodiment of the hollow fiber membrane cartridge for capturing a parasite according to the present invention. The outer cylinder 41 is a container having a water supply port 42 and a circulating water outlet 43, and a potting material 45 is provided in the container so that the hollow portions of the plurality of porous hollow fiber membranes 44 bent in a U-shape maintain an open state. And a hollow fiber membrane supported and fixed by the above. An outlet end face of the opening of the potting portion 45 communicates with an outlet 46 of permeated water that has passed through the porous hollow fiber membrane.

【0040】給水口42に送液ポンプを接続して、試水
を加圧通水することにより、出水口46より透過水が取
り出されるとともに濃縮水が循環水出口よりカートリッ
ジ外部へ送水される。
By connecting a liquid feed pump to the water supply port 42 and passing the test water under pressure, permeated water is taken out from the water outlet 46 and concentrated water is sent from the circulating water outlet to the outside of the cartridge.

【0041】本形態例の中空糸カートリッジでは試水を
中空糸膜カートリッジによりクロスフロー濾過するの
で、カートリッジ内の中空糸膜の一次側の液相で試水が
循環され、中空糸膜表面は常に水が流れている状態にな
るので、濁度成分が中空糸膜表面に堆積、固着すること
がなく、膜表面の濁度成分の回収工程を省くことが出来
る。或いは、中空糸膜の一次側で、液相を攪拌させる構
成としても、同様の効果を得ることができる。
In the hollow fiber cartridge of this embodiment, the sample water is subjected to cross-flow filtration by the hollow fiber membrane cartridge. Therefore, the sample water is circulated in the liquid phase on the primary side of the hollow fiber membrane in the cartridge, and the surface of the hollow fiber membrane is always kept. Since the water is flowing, the turbidity component does not accumulate and adhere to the surface of the hollow fiber membrane, and the step of recovering the turbidity component on the membrane surface can be omitted. Alternatively, the same effect can be obtained even when the liquid phase is stirred on the primary side of the hollow fiber membrane.

【0042】図5は、本発明の原虫捕捉用原虫捕捉用中
空糸膜カートリッジの他の形態例を模式的に示す断面図
である。外筒51は多孔質中空糸膜を透過した透過水の
出水口52を有する容器であり、容器内には複数本の多
孔質中空糸膜53の中空部の両端が開口状態を保つよう
ポッティング材54で支持固定される。又、中空糸膜の
開口部の一端は、中空糸膜の中空部に水を供給する給水
口55に連通しており、他端は、循環水出口56に連通
する。給水口から通水された試水はその一部が透過水と
して出水口から取り出されるとともに、濃縮水が循環水
出口よりカートリッジ外部へと送水される。
FIG. 5 is a cross-sectional view schematically showing another embodiment of the hollow fiber membrane cartridge for capturing protozoa according to the present invention. The outer cylinder 51 is a container having a water outlet 52 for permeated water that has passed through the porous hollow fiber membrane, and a potting material is provided in the container so that both ends of the hollow portions of the plurality of porous hollow fiber membranes 53 are kept open. It is supported and fixed at 54. One end of the opening of the hollow fiber membrane is connected to a water supply port 55 for supplying water to the hollow part of the hollow fiber membrane, and the other end is connected to a circulating water outlet 56. A part of the test water passed through the water supply port is taken out from the water outlet as permeated water, and the concentrated water is sent from the circulating water outlet to the outside of the cartridge.

【0043】[0043]

【実施例】以下、本発明を実施例により詳細に説明す
る。なお、本実施例ではオーシストとほぼ同径のサイズ
(4〜10μm)を有する微生物であるクロレラを用
い、クロレラ濃度100個/Lとなるよう名古屋市水に
クロレラを溶解した溶液を試水として用いた。
DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described below in detail with reference to embodiments. In this example, chlorella, which is a microorganism having a size (4 to 10 μm) having substantially the same diameter as the oocyst, was used, and a solution obtained by dissolving chlorella in Nagoya city water so as to have a chlorella concentration of 100 / L was used as a sample. Was.

【0044】また、実施例において用いた原虫捕捉用中
空糸膜カートリッジには、多孔質中空糸膜として三菱レ
イヨン社製ポリエチレン製多孔質中空糸膜(最大孔径
1.0μm、内径270μm、外径380μm)を用
い、中空糸膜の有効糸長が80mm、中空糸膜の充填率
40%、膜面積は1650cm2(中空糸膜外径ベー
ス)となるよう中空糸膜カートリッジを設計した。
The hollow fiber membrane cartridge for capturing protozoa used in the examples includes a porous hollow fiber membrane made of polyethylene manufactured by Mitsubishi Rayon Co., Ltd. (maximum pore diameter: 1.0 μm, inner diameter: 270 μm, outer diameter: 380 μm). ), The hollow fiber membrane cartridge was designed such that the effective fiber length of the hollow fiber membrane was 80 mm, the filling rate of the hollow fiber membrane was 40%, and the membrane area was 1650 cm 2 (hollow fiber membrane outer diameter base).

【0045】<実施例1>図1に示す原虫捕捉用中空糸
膜カートリッジの出水口13にアスピレーターを接続す
るとともに、試水40Lを給水口14より外筒17に通
水し、膜間差圧0.7kg/cm2で、外筒内の滞留水
が無くなるまで吸引濾過した。次に、キャップを外筒か
ら取り外し、中空糸膜部を200mlの洗浄液中でもみ
洗いし、200mlの回収液を得た。得られた回収液の
濃縮倍率は200倍であり、回収液を得るまでに要した
時間は約60分であった。
<Example 1> An aspirator was connected to the water outlet 13 of the hollow fiber membrane cartridge for trapping protozoa shown in FIG. 1, and 40 L of test water was passed through the water supply port 14 to the outer cylinder 17. Suction filtration was performed at 0.7 kg / cm 2 until water remaining in the outer cylinder disappeared. Next, the cap was removed from the outer cylinder, and the hollow fiber membrane portion was washed with 200 ml of a washing solution to obtain 200 ml of a recovered solution. The concentration ratio of the obtained recovered liquid was 200 times, and the time required to obtain the recovered liquid was about 60 minutes.

【0046】なお、洗浄液は界面活性剤としてドデシル
硫酸ナトリウム(SDS)、Tween80(名古屋片
山化学社製)をそれぞれ0.1%、消泡剤としてSig
maAntifoam A(シグマケミカルカンパニー
社製)0.01%を含む調製液を使用した。
The washing solution was 0.1% each of sodium dodecyl sulfate (SDS) as a surfactant and Tween 80 (manufactured by Nagoya Katayama Chemical Co., Ltd.), and Sig as a defoaming agent.
A preparation solution containing 0.01% maAntifoam A (manufactured by Sigma Chemical Company) was used.

【0047】得られた回収液を、50mlの遠沈管に分
配し、遠心分離器(クボタ社製KR−20000S)に
セットし、3000rpm×10分の遠心沈澱を行い、
上清液を吸引除去した後、PBS液を加え再懸濁させ同
様に遠心沈澱を行い、上清液を吸引除去した後、再度P
BS液を加え再懸濁させPBS試料とした。
The obtained recovered solution was distributed into a 50 ml centrifuge tube, set in a centrifuge (KR-20,000S manufactured by Kubota), and centrifuged at 3000 rpm for 10 minutes.
After the supernatant was removed by suction, the PBS solution was added and resuspended, and centrifugation was performed in the same manner.
The PBS solution was added and resuspended to obtain a PBS sample.

【0048】得られたPBS試料を1Lに希釈し、希釈
液100mlをオムニポアメンブレン(ミリポア社製P
TFEメンブレン:孔径1μm 直径47mm)により
濾過し、膜面に捕捉されたクロレラを計数したところ、
292個確認された。
The obtained PBS sample was diluted to 1 L, and 100 ml of the diluted solution was diluted with an omnipore membrane (Pill made by Millipore).
When filtered through a TFE membrane (pore size: 1 μm, diameter: 47 mm) and chlorella trapped on the membrane surface was counted,
292 were confirmed.

【0049】これより、クロレラの回収率は約73%で
あった。又、中空糸膜カートリッジにより濾過された濾
過液1Lをオムニポアメンブレンにより濾過し、膜面を
観察したところ、クロレラは全く確認されなかった。本
実施例において、通水開始からPBS試料を得るまでの
所要時間は約90分であった。
From this, the recovery rate of Chlorella was about 73%. Further, 1 L of the filtrate filtered through the hollow fiber membrane cartridge was filtered through an omnipore membrane, and the membrane surface was observed. As a result, no chlorella was confirmed. In this example, the time required from the start of water flow to the time when the PBS sample was obtained was about 90 minutes.

【0050】<実施例2>図2に示す、外筒27が、容
量50mlの遠沈管として共用することができる原虫捕
捉用中空糸膜カートリッジの出水口23にアスピレータ
ーを接続するとともに、給水口より試水40Lを通水
し、膜間差圧0.7kg/cm2で吸引濾過を行った。
次に、中空糸膜カートリッジの外筒を取り外し、外筒内
の濃縮水を回収した。このときの回収液量は35mlで
あった。
<Embodiment 2> The aspirator is connected to the water outlet 23 of the hollow fiber membrane cartridge for trapping protozoa, in which the outer cylinder 27 shown in FIG. 40 L of test water was passed, and suction filtration was performed at a transmembrane pressure difference of 0.7 kg / cm 2 .
Next, the outer cylinder of the hollow fiber membrane cartridge was removed, and the concentrated water in the outer cylinder was recovered. At this time, the recovered liquid volume was 35 ml.

【0051】次いで、別の外筒を、キャップにセット
し、キャップの出水口から50mlのシリンジを用いて
35mlの洗浄水を注入することにより、逆通水洗浄を
行い、中空糸膜表面の濁度成分を誘出させた洗浄液を、
外筒内に収容した。
Next, another outer cylinder was set on the cap, and 35 ml of washing water was injected from a water outlet of the cap with a 50 ml syringe to perform back-flow washing, whereby the surface of the hollow fiber membrane was turbid. The cleaning solution that has induced the components
Housed in an outer cylinder.

【0052】この逆通水洗浄を計3回行い、前述の濃縮
水と合わせて140mlの回収液を得た。得られた回収
液の濃縮倍率は286倍であり、回収液を得るまでに要
した時間は約60分であった。なお、洗浄液には、界面
活性剤としてドデシル硫酸ナトリウム(SDS)、Tw
een80それぞれ0.1%、消泡剤としてSigma
Antifoam A 0.01%を含む調製液を使
用した。
This back water washing was performed three times in total, and 140 ml of a recovered liquid was obtained in combination with the above-mentioned concentrated water. The concentration ratio of the obtained recovered solution was 286 times, and the time required to obtain the recovered solution was about 60 minutes. The washing solution contains sodium dodecyl sulfate (SDS) as a surfactant and Tw
een80 0.1% each, Sigma as defoamer
A preparation solution containing 0.01% Antifoam A was used.

【0053】外筒4本に収容した回収液を、そのまま遠
心分離器にセットし、3000rpm×10分の遠心沈
澱を行い、上清液を吸引除去した後PBS液を加え再懸
濁させ同様に遠心沈澱を行い、上清液を吸引除去した後
再度PBS液を加え再懸濁させPBS試料とした。
The collected solution contained in the four outer cylinders was set in a centrifuge as it was, centrifuged at 3000 rpm for 10 minutes, and the supernatant was removed by suction. After performing centrifugal sedimentation and removing the supernatant liquid by suction, a PBS solution was added again to resuspend, thereby obtaining a PBS sample.

【0054】得られたPBS試料を1Lに希釈し、希釈
液100mlをオムニポアメンブレンにより濾過し、膜
面に捕捉されたクロレラを計数したところ312個確認
できた。これより、クロレラの回収率は約78%であっ
た。又、中空糸膜カートリッジにより濾過された濾過液
1Lをオムニポアメンブレンにより濾過し、膜面を観察
したところクロレラは確認されなかった。通水開始から
PBS試料を得るまでの所要時間は約90分であった。
The obtained PBS sample was diluted to 1 L, and 100 ml of the diluted solution was filtered through an omnipore membrane. Chlorella captured on the membrane surface was counted, and 312 cells were confirmed. Thus, the recovery rate of Chlorella was about 78%. Further, 1 L of the filtrate filtered through the hollow fiber membrane cartridge was filtered through an omnipore membrane, and the membrane surface was observed. Chlorella was not confirmed. The time required from the start of water passage to obtaining the PBS sample was about 90 minutes.

【0055】<実施例3>図3に示される、遠沈管と共
用できる集水筒37(容量50ml)が配設された原虫
捕捉用中空糸膜カートリッジの給水口36に送液ポンプ
を接続し、更に中空糸膜カートリッジを振動攪拌器(商
品名ボルテックス)にセットし中空糸膜カートリッジを
振動させながら試水40Lを加圧送水し、濾過した。こ
の時膜間差圧は1.0kg/cm2であった。
<Embodiment 3> A liquid feeding pump is connected to a water supply port 36 of a hollow fiber membrane cartridge for capturing parasites, which is provided with a water collecting tube 37 (capacity 50 ml) shown in FIG. Further, the hollow fiber membrane cartridge was set on a vibration stirrer (trade name: Vortex), and while the hollow fiber membrane cartridge was vibrated, 40 L of test water was supplied under pressure and filtered. At this time, the transmembrane pressure was 1.0 kg / cm 2 .

【0056】次に、濃縮水が溜まった集水筒を取り外し
た。このときの回収液量は50mlであった。次いで、
新たな集水筒を中空糸膜カートリッジにセットし、給水
口から50mlのシリンジを用いて50mlの洗浄水を
注入し、中空糸膜の中空部の洗浄を行い、膜面の濁度成
分を含んだ洗浄液を集水筒内に収容した。
Next, the water collecting cylinder in which the concentrated water was stored was removed. At this time, the amount of the recovered liquid was 50 ml. Then
A new water collecting cylinder was set in the hollow fiber membrane cartridge, and 50 ml of washing water was injected from a water supply port using a 50 ml syringe to wash the hollow portion of the hollow fiber membrane, and contained a turbidity component on the membrane surface. The washing liquid was stored in a water collecting cylinder.

【0057】この洗浄操作を計3回行い、濃縮水と合わ
せ200mlの回収液を得た。得られた回収液の濃縮倍
率は200倍であり、回収液を得るまでに要した時間は
約60分であった。なお、洗浄液には、界面活性剤とし
てドデシル硫酸ナトリウム(SDS)、Tween80
それぞれ0.1%、消泡剤としてSigma Anti
foam A 0.01%を含む調製液を使用した。
This washing operation was performed three times in total, and 200 ml of a recovered liquid was obtained by combining the concentrated water. The concentration ratio of the obtained recovered liquid was 200 times, and the time required to obtain the recovered liquid was about 60 minutes. The washing solution contains sodium dodecyl sulfate (SDS) as a surfactant and Tween80.
0.1% each, Sigma Anti as defoamer
A preparation solution containing 0.01% of foam A was used.

【0058】集水筒に回収された計4本の回収液を、そ
のまま遠心分離器にセットし、3000rpm×10分
の遠心沈澱を行い、上清液を吸引除去した後PBS液を
加え再懸濁させ同様に遠心沈澱を行い、上清液を吸引除
去した後再度PBS液を加え再懸濁させPBS試料とし
た。
The total of four collected liquids collected in the water collecting tube were set in a centrifuge as they were, centrifuged at 3000 rpm for 10 minutes, and the supernatant was removed by suction. Then, the mixture was centrifuged and precipitated, and the supernatant was removed by suction. Then, a PBS solution was added again to resuspend the suspension to obtain a PBS sample.

【0059】得られたPBS試料を1Lに希釈し、希釈
液100mlをオムニポアメンブレンにより濾過し膜面
に捕捉されたクロレラを計数したところ336個確認で
きた。これより、クロレラの回収率は約84%であっ
た。又、中空糸膜カートリッジの濾過液1Lをオムニポ
アメンブレンにより濾過し、膜面を観察したところクロ
レラは確認されなかった。通水開始からPBS試料を得
るまでの所要時間は約90分であった。
The obtained PBS sample was diluted to 1 L, and 100 ml of the diluted solution was filtered through an omnipore membrane, and chlorella captured on the membrane surface was counted. Thus, the recovery of Chlorella was about 84%. When 1 L of the filtrate from the hollow fiber membrane cartridge was filtered through an omnipore membrane, and the membrane surface was observed, no chlorella was confirmed. The time required from the start of water passage to obtaining the PBS sample was about 90 minutes.

【0060】<実施例4>図4に示される原虫捕捉用中
空糸膜カートリッジの給水口42に送液ポンプを接続
し、試水40Lを加圧通水し、膜間差圧1.0kg/c
2で濾過を行った。この時、中空糸膜カートリッジに
は10L/minの流量で試水を供給し、出水口46か
ら透過水流量が5L/min、循環水出口から流出する
試水の循環流量が5L/minとなるようクロスフロー
濾過を行った。試水の液量が400mlになるまでクロ
スフロー濾過を行った後、濃縮水を回収した。得られた
回収液の濃縮倍率は100倍であり、回収液を得るまで
に要した時間は約30分であった。
<Embodiment 4> A liquid feed pump was connected to the water supply port 42 of the hollow fiber membrane cartridge for capturing protozoa shown in FIG. 4, and 40 L of test water was pressurized and passed therethrough. c
Filtration was performed at m 2 . At this time, the sample water is supplied to the hollow fiber membrane cartridge at a flow rate of 10 L / min, the flow rate of the permeated water from the water outlet 46 is 5 L / min, and the circulation flow rate of the test water flowing out from the circulating water outlet is 5 L / min. Cross-flow filtration was performed as follows. After performing cross-flow filtration until the amount of the test water reached 400 ml, concentrated water was recovered. The concentration ratio of the obtained recovered liquid was 100 times, and the time required to obtain the recovered liquid was about 30 minutes.

【0061】得られた回収液を、50mlの遠沈管に分
配し、遠心分離器にセットし、3000rpm×10分
の遠心沈澱を行い、上清液を吸引除去した後PBS液を
加え再懸濁させ同様に遠心沈澱を行い、上清液を吸引除
去した後再度PBS液を加え再懸濁させPBS試料とし
た。
The obtained recovered solution was distributed to a 50 ml centrifuge tube, set in a centrifuge, centrifuged at 3000 rpm for 10 minutes, and the supernatant was removed by suction. Then, the mixture was centrifuged and precipitated, and the supernatant was removed by suction. Then, a PBS solution was added again to resuspend the suspension to obtain a PBS sample.

【0062】得られたPBS試料を1Lに希釈し、希釈
液100mlをオムニポアメンブレンにより濾過し膜面
に捕捉されたクロレラを計数したところ308個確認で
きた。これより、クロレラの回収率は約77%であっ
た。又、中空糸膜カートリッジの濾過液1Lをオムニポ
アメンブレンにより濾過し、膜面を観察したところクロ
レラは確認されなかった。通水開始からPBS試料を得
るまでの所要時間は約60分であった。
The obtained PBS sample was diluted to 1 L, and 100 ml of the diluted solution was filtered through an omnipore membrane, and chlorella captured on the membrane surface was counted. As a result, 308 cells were confirmed. Thus, the recovery rate of Chlorella was about 77%. When 1 L of the filtrate from the hollow fiber membrane cartridge was filtered through an omnipore membrane, and the membrane surface was observed, no chlorella was confirmed. The time required from the start of water passage to obtaining the PBS sample was about 60 minutes.

【0063】<実施例5>図5に示される原虫捕捉用中
空糸膜カートリッジの給水口55に送液ポンプを接続
し、試水40Lを膜間差圧1.0kg/cm2で加圧濾
過した。この時、中空糸膜カートリッジには10L/m
inの流量で試水を供給し、出水口52からの透過水の
流量が5L/min、循環水出口からの、循環水の流量
が5L/minとなるようクロスフロー濾過を行った。
Example 5 A liquid feed pump was connected to the water supply port 55 of the hollow fiber membrane cartridge for capturing protozoa shown in FIG. 5, and 40 L of test water was subjected to pressure filtration at a transmembrane pressure difference of 1.0 kg / cm 2. did. At this time, the hollow fiber membrane cartridge has 10 L / m
The sample water was supplied at a flow rate of “in”, and the cross flow filtration was performed such that the flow rate of the permeated water from the water outlet 52 was 5 L / min and the flow rate of the circulating water from the circulating water outlet was 5 L / min.

【0064】試水の液量が400mlになるまでクロス
フロー濾過を行い、濃縮水を回収した。得られた回収液
の濃縮倍率は100倍であり、回収液を得るまでに要し
た時間は約30分であった。得られた回収液を、50m
l遠沈管に分配し、遠心分離器にセットし、3000r
pm×10分の遠心沈澱を行い、上清液を吸引除去した
後PBS液を加え再懸濁させ同様に遠心沈澱を行い、上
清液を吸引除去した後再度PBS液を加え再懸濁させP
BS試料とした。
The cross-flow filtration was performed until the amount of the test water reached 400 ml, and the concentrated water was recovered. The concentration ratio of the obtained recovered liquid was 100 times, and the time required to obtain the recovered liquid was about 30 minutes. The obtained recovered liquid is 50 m
l Dispense into a centrifuge tube, set in a centrifuge, and
After performing centrifugal sedimentation at pm × 10 minutes, removing the supernatant liquid by suction, adding a PBS liquid and resuspending the mixture, similarly performing centrifugal sedimentation, removing the supernatant liquid by suction and adding a PBS liquid again to resuspend. P
A BS sample was used.

【0065】得られたPBS試料を1Lに希釈し、希釈
液100mlをオムニポアメンブレンにより濾過し膜面
に捕捉されたクロレラを計数したところ352個確認で
きた。これより、クロレラの回収率は約88%であっ
た。又、中空糸膜カートリッジの濾過液1Lをオムニポ
アメンブレンにより濾過し、膜面を観察したところクロ
レラは確認されなかった。又、通水開始からPBS試料
を得るまでの所要時間は約60分であった。
The obtained PBS sample was diluted to 1 L, and 100 ml of the diluted solution was filtered through an omnipore membrane, and chlorella captured on the membrane surface was counted. Thus, the recovery of Chlorella was about 88%. When 1 L of the filtrate from the hollow fiber membrane cartridge was filtered through an omnipore membrane, and the membrane surface was observed, no chlorella was confirmed. The time required from the start of water flow to the time when the PBS sample was obtained was about 60 minutes.

【0066】<実施例6>実施例1で使用したものと同
様の原虫捕捉用中空糸膜カートリッジの出水口にアスピ
レーターを接続し、試水40Lを外筒内に滞留水が無く
なるまで、吸引濾過30秒、停止30秒の間隔で間欠通
水した。なお、吸引濾過時の膜間差圧は0.7kg/c
2であった。
<Example 6> An aspirator was connected to the water outlet of the hollow fiber membrane cartridge for capturing protozoa similar to that used in Example 1, and 40 L of sample water was subjected to suction filtration until no water remained in the outer cylinder. Water was supplied intermittently at intervals of 30 seconds and 30 seconds after stopping. The transmembrane pressure during suction filtration is 0.7 kg / c.
m 2 .

【0067】次に、中空糸膜カートリッジの外筒とキャ
ップを分割し、更にキャップの中空糸膜部とポッティン
グ部を切り離し、200mlの洗浄液を入れた超音波洗
浄機内で中空糸膜部を洗浄し、200mlの回収液を得
た。得られた回収液の濃縮倍率は200倍であり、回収
液を得るまでに要した時間は約60分であった。
Next, the outer cylinder and the cap of the hollow fiber membrane cartridge are divided, the hollow fiber membrane part and the potting part of the cap are cut off, and the hollow fiber membrane part is washed in an ultrasonic cleaner containing 200 ml of a washing liquid. , 200 ml of a recovered liquid were obtained. The concentration ratio of the obtained recovered liquid was 200 times, and the time required to obtain the recovered liquid was about 60 minutes.

【0068】洗浄液は、界面活性剤としてドデシル硫酸
ナトリウム(SDS)、Tween80それぞれ0.1
%、消泡剤としてSigma Antifoam A
0.01%を含む調製液を使用した。
The washing solution was prepared by adding 0.1% each of sodium dodecyl sulfate (SDS) and Tween 80 as a surfactant.
%, Sigma Antifoam A as antifoaming agent
A preparation solution containing 0.01% was used.

【0069】得られた回収液を、50ml遠沈管に分配
し、遠心分離器にセットし、3000rpm×10分の
遠心沈澱を行い、上清液を吸引除去した後PBS液を加
え再懸濁させ同様に遠心沈澱を行い、上清液を吸引除去
した後再度PBS液を加え再懸濁させPBS試料とし
た。
The obtained recovered solution was distributed to a 50 ml centrifuge tube, set in a centrifuge, centrifuged at 3000 rpm for 10 minutes, and the supernatant was removed by suction. Similarly, centrifugal sedimentation was performed, and the supernatant was removed by suction. Then, a PBS solution was added again to resuspend, thereby obtaining a PBS sample.

【0070】得られたPBS試料を1Lに希釈し、希釈
液100mlをオムニポアメンブレンにより濾過し膜面
に捕捉されたクロレラを計数したところ368個確認で
きた。これより、クロレラの回収率は約92%であっ
た。中空糸膜カートリッジの濾過液1Lをオムニポアメ
ンブレンにより濾過し、膜面を観察したところクロレラ
は確認されなかった。通水開始からPBS試料を得るま
での所要時間は約90分であった。
The obtained PBS sample was diluted to 1 L, and 100 ml of the diluted solution was filtered through an omnipore membrane, and chlorella captured on the membrane surface was counted. As a result, 368 were confirmed. Thus, the recovery rate of Chlorella was about 92%. 1 L of the filtrate from the hollow fiber membrane cartridge was filtered through an omnipore membrane, and the membrane surface was observed. Chlorella was not confirmed. The time required from the start of water passage to obtaining the PBS sample was about 90 minutes.

【0071】<実施例7>実施例1で用いたものと同一
の仕様の原虫捕捉用中空糸膜カートリッジの給水口にア
スピレーターを接続し、試水40Lを外筒17内に滞留
水が無くなるまで吸引濾過した。この時膜間差圧は0.
7kg/cm2であった。
<Example 7> An aspirator was connected to the water supply port of the hollow fiber membrane cartridge for capturing parasites having the same specifications as those used in Example 1, and 40 L of the test water was used until no water remained in the outer cylinder 17. Suction filtration was performed. At this time, the transmembrane pressure was 0.1.
It was 7 kg / cm 2 .

【0072】次に、中空糸膜カートリッジのキャップと
外筒を分割し、更にキャップの多孔質中空糸膜とポッテ
ィング部を切り離した。その後200mlの洗浄液を入
れた振動攪拌機で、切断した多孔質中空糸膜を洗浄し、
200mlの回収液を得た。回収液を得るまでに要した
時間は約60分であった。
Next, the cap and the outer cylinder of the hollow fiber membrane cartridge were divided, and the porous hollow fiber membrane and the potting portion of the cap were cut off. Thereafter, the cut porous hollow fiber membrane was washed with a vibration stirrer containing 200 ml of a washing solution,
200 ml of recovered liquid was obtained. The time required to obtain the recovered liquid was about 60 minutes.

【0073】得られた回収液の濃縮倍率は200倍であ
った。洗浄液は、界面活性剤としてドデシル硫酸ナトリ
ウム(SDS)、Tween80それぞれ0.1%、消
泡剤としてSigma Antifoam A 0.0
1%を含む調製液を使用した。
The concentration of the obtained recovered liquid was 200 times. The washing liquid was 0.1% each of sodium dodecyl sulfate (SDS) and Tween 80 as surfactants, and Sigma Antifoam A 0.0 as antifoaming agent.
A preparation solution containing 1% was used.

【0074】得られた回収液を、50ml遠沈管に分配
し、遠心分離器にセットし、3000rpm×10分の
遠心沈澱を行い、上清液を吸引除去した後PBS液を加
え再懸濁させ同様に遠心沈澱を行い、上清液を吸引除去
した後再度PBS液を加え再懸濁させPBS試料とし
た。
The obtained recovered solution was distributed to a 50 ml centrifuge tube, set in a centrifuge, centrifuged at 3000 rpm for 10 minutes, and the supernatant was removed by suction. Similarly, centrifugal sedimentation was performed, and the supernatant was removed by suction. Then, a PBS solution was added again to resuspend, thereby obtaining a PBS sample.

【0075】得られたPBS試料を1Lに希釈し、希釈
液100mlをオムニポアメンブレンにより濾過し膜面
に捕捉されたクロレラを計数したところ348個確認で
きた。これより、クロレラの回収率は約87%であっ
た。中空糸膜カートリッジの濾過液1Lをオムニポアメ
ンブレンにより濾過し、膜面を観察したところクロレラ
は確認されなかった。また、通水開始からPBS試料を
得るまでの所要時間は約90分であった。
The obtained PBS sample was diluted to 1 L, and 100 ml of the diluted solution was filtered through an omnipore membrane, and chlorella captured on the membrane surface was counted. As a result, 348 cells could be confirmed. Thus, the recovery rate of Chlorella was about 87%. 1 L of the filtrate from the hollow fiber membrane cartridge was filtered through an omnipore membrane, and the membrane surface was observed. Chlorella was not confirmed. The time required from the start of water flow to the time when the PBS sample was obtained was about 90 minutes.

【0076】<比較例1>1996年9月30日付けで
厚生省より公表された「水道におけるクリプトスポリジ
ウム暫定対策指針−別添3−水道水に関するクリプトス
ポリジウムのオーシストの検出のための暫定的な試験方
法」によるオーシストの分析方法を参考に以下の実験を
行った。
<Comparative Example 1>"Temporary Guideline for Cryptosporidium in Water Supply-Appendix 3 Provisional test for detection of Cryptosporidium oocysts in tap water" published by the Ministry of Health on September 30, 1996. The following experiment was conducted with reference to the oocyst analysis method by "Method".

【0077】東洋濾紙(株)製セルロースアセテートメ
ンブレンフィルター(寸法47mm,孔径0.8μm)
をフィルターホルダーにセットし、クロレラを100個
/Lに調製した試水40Lをアスピレータにより吸引濾
過した。メンブレンフィルター1枚で7〜8Lの試水が
濾過でき、40L通水するのに6枚のメンブレンフィル
ターを使用した。得られた6枚のメンブレンフィルター
を、アセトン20mlに溶解したところ完全に溶解し、
アセトン20mlを回収液とした。得られた回収液の濃
縮倍率は2000倍であり、回収液を得るまでに要した
時間は約180分であった。
A cellulose acetate membrane filter manufactured by Toyo Roshi Kaisha Co., Ltd. (size: 47 mm, pore size: 0.8 μm)
Was set in a filter holder, and 40 L of test water prepared with 100 chlorella / L was suction-filtered with an aspirator. One membrane filter can filter 7 to 8 L of test water, and six membrane filters were used to pass 40 L of water. When the obtained six membrane filters were dissolved in 20 ml of acetone, they were completely dissolved.
20 ml of acetone was used as a recovery liquid. The concentration ratio of the obtained recovered liquid was 2000 times, and the time required to obtain the recovered liquid was about 180 minutes.

【0078】得られた回収液を遠心分離器にセットし、
3000rpm×10分の遠心沈澱を行い上清液を吸引
除去し、再度アセトンを加え再懸濁させ遠心沈澱を行っ
た。アセトンでの遠沈操作を3回行った後、得られた沈
渣に精製液(二段蒸留水を孔径0.45μm以下のフィ
ルターで濾過した液)を加えて、再懸濁させ同様に遠心
沈澱を行い、更に上清液を吸引除去した後PBS液を加
え再懸濁させ同様に遠心沈澱を行い、上清液を吸引除去
した後再度PBS液を加え再懸濁させPBS試料とし
た。
The obtained recovered solution was set in a centrifuge,
The suspension was centrifuged at 3000 rpm for 10 minutes, the supernatant was removed by suction, acetone was added again, and the suspension was resuspended to perform centrifugal precipitation. After performing a centrifugation operation with acetone three times, a purified solution (a solution obtained by filtering double-distilled water through a filter having a pore size of 0.45 μm or less) was added to the obtained sediment, followed by resuspension and centrifugation similarly. After the supernatant was removed by suction, a PBS solution was added thereto to resuspend the suspension, and the mixture was centrifuged in the same manner. After the supernatant was removed by suction, the PBS solution was added again and resuspended to obtain a PBS sample.

【0079】得られたPBS試料を1Lに希釈し、希釈
液100mlをオムニポアメンブレンにより濾過し膜面
に捕捉されたクロレラを計数したところ252個確認で
きた。これより、クロレラの回収率は約63%であっ
た。濾過液1Lをオムニポアメンブレンにより濾過し、
膜面を観察したところクロレラは確認されなかった。遠
心沈澱回数は5回で、通水開始からPBS試料を得るま
での所要時間は約300分であった。この時40Lを濾
過するのに要した時間は約3時間であり、この間フィル
ターの交換やフィルターホルダーに試水を給水する必要
があるため実験者はその場を離れることが出来なかっ
た。
The obtained PBS sample was diluted to 1 L, and 100 ml of the diluted solution was filtered through an omnipore membrane, and chlorella captured on the membrane surface was counted. As a result, 252 cells were confirmed. Thus, the recovery rate of Chlorella was about 63%. 1 L of the filtrate is filtered through an omnipore membrane,
Chlorella was not observed when the film surface was observed. The number of times of centrifugal sedimentation was 5, and the time required from the start of water passage to obtaining the PBS sample was about 300 minutes. At this time, the time required to filter 40 L was about 3 hours. During this time, the experimenter could not leave the place because the filter had to be replaced and the sample water had to be supplied to the filter holder.

【0080】<実施例8>実施例5で用いた原虫捕捉用
中空糸膜カートリッジと同一の仕様の中空糸膜カートリ
ッジの給水口に送液ポンプを接続し、試水800Lを膜
間差圧1.0kg/cm2で加圧濾過した。この時、中
空糸膜カートリッジには10L/minの流量で供給
し、透過水出口からの流量を5L/min、循環水出口
からの流量を5L/minとしてクロスフロー濾過を行
った。
<Embodiment 8> A liquid feeding pump was connected to the water supply port of a hollow fiber membrane cartridge having the same specifications as the hollow fiber membrane cartridge for capturing protozoa used in Example 5, and 800 L of test water was applied to the membrane with a transmembrane pressure of 1. Pressure filtration was performed at 0.0 kg / cm 2 . At this time, the flow was supplied to the hollow fiber membrane cartridge at a flow rate of 10 L / min, and the cross flow filtration was performed at a flow rate of 5 L / min from the permeated water outlet and a flow rate of 5 L / min from the circulating water outlet.

【0081】試水の液量が400mlになるまでクロス
フロー濾過を行い、濃縮水を回収した。得られた回収液
の濃縮倍率は2000倍であり、回収液を得るまでに要
した時間は約180分であった。
Cross-flow filtration was carried out until the amount of the test water reached 400 ml, and concentrated water was recovered. The concentration ratio of the obtained recovered liquid was 2000 times, and the time required to obtain the recovered liquid was about 180 minutes.

【0082】得られた回収液を、50ml遠沈管に分配
し、遠心分離器にセットし、3000rpm×10分の
遠心沈澱を行い、上清液を吸引除去した後PBS液を加
え再懸濁させ同様に遠心沈澱を行い、上清液を吸引除去
した後再度PBS液を加え再懸濁させPBS試料とし
た。
The obtained recovered solution was distributed to a 50 ml centrifuge tube, set in a centrifuge, centrifuged at 3000 rpm for 10 minutes, and the supernatant was removed by suction. Similarly, centrifugal sedimentation was performed, and the supernatant was removed by suction. Then, a PBS solution was added again to resuspend, thereby obtaining a PBS sample.

【0083】得られたPBS試料を20Lに希釈し、希
釈液100mlをオムニポアメンブレンにより濾過し膜
面に捕捉されたクロレラを計数したところ312個確認
できた。これより、クロレラの回収率は約78%であっ
た。中空糸膜カートリッジの濾過液1Lをオムニポアメ
ンブレンにより濾過し、膜面を観察したところクロレラ
は確認されなかった。又、通水開始からPBS試料を得
るまでの所要時間は約220分であった。
The obtained PBS sample was diluted to 20 L, and 100 ml of the diluted solution was filtered through an omnipore membrane, and the number of chlorella captured on the membrane surface was counted. As a result, 312 chlorella were confirmed. Thus, the recovery rate of Chlorella was about 78%. 1 L of the filtrate from the hollow fiber membrane cartridge was filtered through an omnipore membrane, and the membrane surface was observed. Chlorella was not confirmed. The time required from the start of water flow to obtaining the PBS sample was about 220 minutes.

【0084】本実施例においては、濃縮倍率を比較例1
と同等の2000倍にし実験ているが、比較例1よりも
高い回収率で原虫の捕捉回収を行うことができた。ま
た、比較例1とほぼ同等の時間で20倍の試水を処理す
ることができた。
In this example, the concentration ratio was compared with that of Comparative Example 1.
Although the experiment was performed at 2000 times as high as that of Example 1, the protozoa could be captured and recovered at a higher recovery rate than Comparative Example 1. In addition, it was possible to treat the sample water 20 times in approximately the same time as Comparative Example 1.

【0085】[0085]

【発明の効果】本発明の原虫の捕捉回収方法によれば、
試水中に含まれる原虫の捕捉回収を行うに際し、最大孔
径2.0μm以下の微細孔を有する多孔質中空糸膜が配
設された中空糸膜カートリッジに試水を通水し濾過する
ことにより、多孔質中空糸膜の一次側で試水の濃縮を行
った後、原虫を含む濃縮水及び/又は多孔質中空糸膜の
表面に堆積した原虫を含む濁度成分を回収するので、従
来の回収方法に比較して、膜面積を多くとることがで
き、容積効率が向上し、短時間かつ高回収効率で原虫を
捕捉回収することができる。
According to the method for capturing and recovering protozoa of the present invention,
Upon capturing and recovering the protozoa contained in the test water, by passing the test water through a hollow fiber membrane cartridge provided with a porous hollow fiber membrane having fine pores having a maximum pore diameter of 2.0 μm or less, and filtering the water, After concentrating the test water on the primary side of the porous hollow fiber membrane, the concentrated water containing the protozoa and / or the turbidity component containing the protozoa deposited on the surface of the porous hollow fiber membrane are recovered. Compared with the method, the membrane area can be increased, the volumetric efficiency can be improved, and the protozoa can be captured and recovered in a short time and with high recovery efficiency.

【図面の簡単な説明】[Brief description of the drawings]

【図1】図1は本発明の原虫捕捉用中空糸膜カートリッ
ジの一形態を示す断面図である。
FIG. 1 is a cross-sectional view showing one embodiment of a hollow fiber membrane cartridge for capturing protozoa of the present invention.

【図2】図2は本発明の原虫捕捉用中空糸膜カートリッ
ジの他の形態を示す断面図である。
FIG. 2 is a cross-sectional view showing another embodiment of the hollow fiber membrane cartridge for capturing protozoa of the present invention.

【図3】図3は本発明の原虫捕捉用中空糸膜カートリッ
ジの他の形態を示す断面図である。
FIG. 3 is a sectional view showing another embodiment of the hollow fiber membrane cartridge for capturing protozoa of the present invention.

【図4】図4は本発明の原虫捕捉用中空糸膜カートリッ
ジの他の形態を示す断面図である。
FIG. 4 is a sectional view showing another embodiment of the hollow fiber membrane cartridge for capturing protozoa of the present invention.

【図5】図5は本発明の原虫捕捉用中空糸膜カートリッ
ジの他の形態を示す断面図である。
FIG. 5 is a cross-sectional view showing another embodiment of the hollow fiber membrane cartridge for capturing protozoa of the present invention.

【符号の説明】[Explanation of symbols]

17、27、34、41、51 外筒 11、24、34、44、53 多孔質中空糸膜 12、25、35、45、54 ポッティング材 14、22、36、42、55 給水口 13、23、32、46、52 出水口 16、21、38 キャップ 15 Oリング 26 ホルダー部 37 集水筒 39 疎水性多孔質材 43、56 循環水出口 17, 27, 34, 41, 51 Outer cylinder 11, 24, 34, 44, 53 Porous hollow fiber membrane 12, 25, 35, 45, 54 Potting material 14, 22, 36, 42, 55 Water supply port 13, 23 , 32, 46, 52 Outlet 16, 21, 38 Cap 15 O-ring 26 Holder 37 Water collecting cylinder 39 Hydrophobic porous material 43, 56 Circulating water outlet

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI B01D 65/06 B01D 65/06 (72)発明者 小泓 正直 愛知県名古屋市東区砂田橋四丁目1番60号 三菱レイヨン株式会社商品開発研究所内 (72)発明者 田阪 広 愛知県名古屋市東区砂田橋四丁目1番60号 三菱レイヨン株式会社商品開発研究所内────────────────────────────────────────────────── ─── Continuing on the front page (51) Int.Cl. 6 Identification symbol FI B01D 65/06 B01D 65/06 (72) Inventor Masanao Koho 4-60 Sunadabashi, Higashi-ku, Nagoya-shi, Aichi Mitsubishi Rayon Co., Ltd. Inside the Product Development Laboratory (72) Inventor Hiroshi Tasaka 4-1-1-60 Sunadabashi, Higashi-ku, Nagoya City, Aichi Prefecture Mitsubishi Rayon Co., Ltd. Product Development Laboratory

Claims (16)

【特許請求の範囲】[Claims] 【請求項1】 外筒内部に多孔質中空糸膜の両端が開口
してポッティングされ、前記外筒には、多孔質中空糸膜
の外表面側に試水を供給する給水口と、多孔質中空糸膜
の開口端に連通して透過水を取り出す出水口が配設され
たことを特徴とする原虫捕捉用中空糸膜カートリッジ。
1. A porous hollow fiber membrane having two ends open and potted inside an outer cylinder, wherein the outer cylinder has a water supply port for supplying sample water to the outer surface of the porous hollow fiber membrane; A hollow fiber membrane cartridge for capturing protozoa, wherein a water outlet for extracting permeated water is provided so as to communicate with an open end of the hollow fiber membrane.
【請求項2】 外筒内部に多孔質中空糸膜の両端が別々
に開口してポッティングされ、前記外筒には、多孔質中
空糸膜の一方の開口端に試水を供給する給水口と、多孔
質中空糸膜の外表面側に連通して透過水を取り出す出水
口とが配設され、多孔質中空糸膜の他の開口端から濃縮
水を取り出すことを特徴とする原虫捕捉用中空糸膜カー
トリッジ。
2. The porous hollow fiber membrane has two ends separately open and potted inside the outer cylinder, and the outer cylinder has a water supply port for supplying test water to one open end of the porous hollow fiber membrane. An outlet for communicating with the outer surface side of the porous hollow fiber membrane to take out permeated water, and extracting concentrated water from another open end of the porous hollow fiber membrane; Thread membrane cartridge.
【請求項3】 試水中に含まれる原虫の捕捉回収を行う
に際し、最大孔径2.0μm以下の微細孔を有する多孔
質中空糸膜が配設された中空糸膜カートリッジに試水を
通水し濾過することにより、多孔質中空糸膜の一次側で
試水の濃縮を行った後、原虫を含む濃縮水及び/又は多
孔質中空糸膜の表面に堆積した原虫を含む濁度成分を回
収することを特徴とする原虫の捕捉回収方法。
3. When capturing and recovering protozoa contained in the sample water, the sample water is passed through a hollow fiber membrane cartridge provided with a porous hollow fiber membrane having fine pores having a maximum pore diameter of 2.0 μm or less. After the sample is concentrated on the primary side of the porous hollow fiber membrane by filtration, concentrated water containing the protozoa and / or turbidity components containing the protozoa deposited on the surface of the porous hollow fiber membrane are recovered. A method for capturing and recovering protozoa.
【請求項4】 中空糸膜カートリッジを振動させながら
試水を通水し、濾過することを特徴とする請求項3に記
載の原虫の捕捉回収方法。
4. The method for capturing and recovering protozoa according to claim 3, wherein the sample water is passed while the hollow fiber membrane cartridge is vibrated and filtered.
【請求項5】 中空糸膜カートリッジに試水を間欠通水
することを特徴とする請求項3に記載の原虫の捕捉回収
方法。
5. The method for capturing and recovering protozoa according to claim 3, wherein a test water is intermittently passed through the hollow fiber membrane cartridge.
【請求項6】 中空糸膜カートリッジ内の一次側の空間
で液相を攪拌又は循環させながら試水を通水し、濾過す
ることを特徴とする請求項3に記載の原虫の捕捉回収方
法。
6. The method for capturing and recovering protozoa according to claim 3, wherein a test water is passed through while stirring or circulating the liquid phase in a space on the primary side in the hollow fiber membrane cartridge, and filtration is performed.
【請求項7】 多孔質中空糸膜の二次側を吸引すること
により試水の濾過を行うことを特徴とする請求項3に記
載の原虫の捕捉回収方法。
7. The method for capturing and recovering parasites according to claim 3, wherein the sample water is filtered by sucking the secondary side of the porous hollow fiber membrane.
【請求項8】 2kg/cm2以下の膜間差圧で試水の
濾過を行うことを特徴とする請求項3に記載の原虫の捕
捉回収方法。
8. The method for capturing and recovering protozoa according to claim 3, wherein the filtration of the sample water is performed at a transmembrane pressure difference of 2 kg / cm 2 or less.
【請求項9】 多孔質中空糸膜表面に堆積した原虫を含
む濁度成分を回収するに際して、多孔質中空糸膜を洗浄
液中に浸漬してもみ洗いすることにより膜表面の濁度成
分を洗浄液中に誘出させることを特徴とする請求項3に
記載の原虫の捕捉回収方法。
9. A turbidity component containing protozoa deposited on the surface of a porous hollow fiber membrane is recovered by immersing the porous hollow fiber membrane in a cleaning solution and rinsing to remove the turbidity component on the membrane surface. The method for capturing and recovering protozoa according to claim 3, wherein the protozoa are induced into the inside.
【請求項10】 多孔質中空糸膜表面に堆積した原虫を
含む濁度成分を回収するに際して、洗浄液槽内の洗浄液
中に多孔質中空糸膜を浸漬し、多孔質中空糸膜を振動さ
せることにより、膜表面の濁度成分を洗浄液中に誘出さ
せることを特徴とする請求項3に記載の原虫の捕捉回収
方法。
10. A method for recovering turbidity components including protozoa deposited on the surface of a porous hollow fiber membrane, by immersing the porous hollow fiber membrane in a cleaning solution in a cleaning solution tank and vibrating the porous hollow fiber membrane. 4. The method for capturing and recovering protozoa according to claim 3, wherein the turbid component on the membrane surface is induced into the washing solution by the method.
【請求項11】 多孔質中空糸膜表面に堆積した原虫を
含む濁度成分を回収するに際して、超音波洗浄機内の洗
浄液中に該多孔質中空糸膜を浸漬し、超音波洗浄により
膜表面の濁度成分を洗浄液中に誘出させることを特徴と
する請求項10記載の原虫の捕捉回収方法。
11. When recovering a turbid component containing protozoa deposited on the surface of a porous hollow fiber membrane, the porous hollow fiber membrane is immersed in a cleaning solution in an ultrasonic cleaner, and the surface of the membrane is cleaned by ultrasonic cleaning. The method for capturing and recovering protozoa according to claim 10, wherein the turbidity component is induced into the washing solution.
【請求項12】 多孔質中空糸膜表面に堆積した原虫を
含む濁度成分を回収するに際して、多孔質中空糸膜部を
中空糸膜カートリッジから切断し、切断した多孔質中空
糸膜のみを洗浄液中で洗浄することにより、膜表面の濁
度成分を洗浄液中に誘出させることを特徴とする請求項
3に記載の原虫の捕捉回収方法。
12. When recovering a turbid component containing protozoa deposited on the surface of the porous hollow fiber membrane, the porous hollow fiber membrane is cut from the hollow fiber membrane cartridge, and only the cut porous hollow fiber membrane is washed. The method for capturing and recovering protozoa according to claim 3, wherein the turbidity component on the membrane surface is induced into the cleaning solution by washing in the inside.
【請求項13】 多孔質中空糸膜表面に堆積した原虫を
含む濁度成分を回収するに際して、試水濾過時の逆方向
に洗浄液を通水することにより、膜表面の濁度成分を洗
浄液中に誘出させることを特徴とする請求項3に記載の
原虫の捕捉回収方法。
13. When the turbidity component containing protozoa deposited on the surface of the porous hollow fiber membrane is recovered, the turbidity component on the membrane surface is passed through the washing solution by passing the washing solution in the reverse direction of the sample filtration. The method for capturing and recovering protozoa according to claim 3, wherein the parasite is induced.
【請求項14】 多孔質中空糸膜表面に堆積した原虫を
含む濁度成分を回収するに際して、洗浄液を多孔質中空
糸膜の一次側に循環通水することにより濁度成分を洗浄
液中に誘出させることを特徴とする請求項3に記載の原
虫の捕捉回収方法。
14. When the turbidity component containing protozoa deposited on the surface of the porous hollow fiber membrane is recovered, the turbidity component is introduced into the cleaning solution by circulating the washing solution through the primary side of the porous hollow fiber membrane. The method for capturing and recovering protozoa according to claim 3, wherein the protozoa are collected.
【請求項15】 洗浄液中に界面活性剤が添加されてな
ることを特徴とする請求項12〜14のいずれか1項に
記載の原虫の捕捉回収方法。
15. The method for capturing and recovering protozoa according to any one of claims 12 to 14, wherein a surfactant is added to the washing solution.
【請求項16】 洗浄液中に消泡剤が添加されてなるこ
とを特徴とする請求項15記載の原虫の捕捉回収方法。
16. The method for capturing and recovering protozoa according to claim 15, wherein an antifoaming agent is added to the cleaning liquid.
JP12595297A 1997-05-15 1997-05-15 Hollow fiber membrane cartridge for capturing protozoa and method for capturing and recovering protozoa Pending JPH10314552A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP12595297A JPH10314552A (en) 1997-05-15 1997-05-15 Hollow fiber membrane cartridge for capturing protozoa and method for capturing and recovering protozoa

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP12595297A JPH10314552A (en) 1997-05-15 1997-05-15 Hollow fiber membrane cartridge for capturing protozoa and method for capturing and recovering protozoa

Publications (1)

Publication Number Publication Date
JPH10314552A true JPH10314552A (en) 1998-12-02

Family

ID=14923042

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
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