JPS6068093A - Water treating system - Google Patents

Water treating system

Info

Publication number
JPS6068093A
JPS6068093A JP17470583A JP17470583A JPS6068093A JP S6068093 A JPS6068093 A JP S6068093A JP 17470583 A JP17470583 A JP 17470583A JP 17470583 A JP17470583 A JP 17470583A JP S6068093 A JPS6068093 A JP S6068093A
Authority
JP
Japan
Prior art keywords
water
hollow fiber
porous hollow
micropores
activated carbon
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
JP17470583A
Other languages
Japanese (ja)
Inventor
Atsushi Kawai
厚 河合
Michio Inoue
井上 通生
Hisao Tanaka
久雄 田中
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 Rayon Co Ltd
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 JP17470583A priority Critical patent/JPS6068093A/en
Publication of JPS6068093A publication Critical patent/JPS6068093A/en
Pending legal-status Critical Current

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Abstract

PURPOSE:To obtain inexpensively the purified water without using a special water feed pump by filtering the water to be treated with a porous hollow yarn membrane impermeable to bacteria, allowing to pass through an activated carbon layer, and then filtering with another porous hollow yarn membrane. CONSTITUTION:The bacteria, pyrogens, colloidal substances, low molecular organic compds. contained in the water are almost completely removed in a filtration part A by a filter medium consisting of a porous hollw yarn membrane wherein a multitude of slit micropores are present. The water, after passing through the filtration part A, is sent to an activated carbon type water treating part B wherein the stinky substances, etc. are collected, and then sent to a filtration part C wherein the purified water is obtained. A porous hollow yarn made of polyolefins having 300-5,000Angstrom mean width, 8-50 ratio of length to width and contg. a multitude of slit micropores distributed in the longitudinal direction of the fiber is suitably used as the membrane for the filtration part A.

Description

【発明の詳細な説明】 この発明は水の浄化を目的とする水処理システムに関す
る。更に具体的には、井戸水や水道水等巾に合まれる細
菌類、パイロジエン(発熱物質)コロイド状物質、低分
子有機化合物等の物質や塩素その他の悪臭物質を除去す
る水処理システムに関し、特に医療用、精密理化学実験
用、食品工業用、飲料水用等において要求される純度の
高い水を簡易に得ることのできる低コストのシステムに
関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a water treatment system for purifying water. More specifically, it concerns water treatment systems that remove bacteria, pyrogens, colloidal substances, low-molecular organic compounds, chlorine, and other malodorous substances that are contained in well water, tap water, etc. The present invention relates to a low-cost system that can easily obtain high-purity water required for medical use, precision physical and chemical experiments, food industry use, drinking water use, etc.

水浄化システムについては、従来から種々の形式のシス
テムが考えられ市販されているが、前述の如ぎ物質を完
全に除去することは非常に困難である。かかる物質を完
全に除去するためには、蒸溜法や逆浸透膜等の高度の水
処理技術が必要であるが、これ等のシステムはエネルギ
ー費や設備費が高く、安価に水を浄化することができな
いという欠点を有している。
Regarding water purification systems, various types of systems have been considered and are commercially available, but it is extremely difficult to completely remove the above-mentioned substances. In order to completely remove such substances, advanced water treatment technologies such as distillation and reverse osmosis membranes are required, but these systems have high energy and equipment costs, and are difficult to purify water at low cost. It has the disadvantage that it cannot be used.

活性炭水処理装置にプレフィルタ−を設置したものが知
られているが、このプレフィルタ−は水中の大きなごみ
等を除去するのみで、低分子有機化合物、コロイド状物
質、パイロジエン(発熱性物質)、細菌等を充分に除去
することはできない。
It is known that activated carbon water treatment equipment is equipped with a pre-filter, but this pre-filter only removes large particles in the water, such as low-molecular organic compounds, colloidal substances, and pyrogens (pyrogenic substances). , bacteria, etc. cannot be removed sufficiently.

その上、活性炭の劣化による微細粒子の流出を防ぐ手段
はとられていないために、低コストではあるが、高純度
の水を得ることはできない。また細菌や微細粒子を除去
するため、孔径の小さい市販ストレートボアタイプの微
細孔を有する膜モジュールを活性炭層部の前後に設置す
る方式も知られているが、この場合には大きな濾過流量
を得ることができず、流量を大きくしようとすると高圧
力が必要となり、また短期間での目づまりによる処理用
の低下が大きく、実用的でない。
Moreover, since no measures are taken to prevent the outflow of fine particles due to deterioration of activated carbon, it is not possible to obtain high purity water, although it is low cost. In addition, in order to remove bacteria and fine particles, a method is known in which membrane modules with commercially available straight-bore micropores with small pore diameters are installed before and after the activated carbon layer, but in this case, it is difficult to obtain a large filtration flow rate. If you try to increase the flow rate, you will need a high pressure, and the processing efficiency will be significantly reduced due to clogging in a short period of time, making it impractical.

また悪臭の原因となる物質の除去も必要であるが、この
悪臭の原因は地域開発や生活汚水等による水道水の水源
の著しい水質汚濁にある。特に水源が湖沼水の場合この
傾向が著しい。特に湖沼水の富栄養化により植物性プラ
ンクトンの大量増殖に併う赤潮の発生や水通水の異臭川
縁等が認められている。この異臭はらん藻類等が分泌す
る物質や、湖底に沈澱した有機物に付着する放線菌等の
微生物から分泌される物質によることが多い。これ等の
悪臭物質を取り除く目的で最近活性炭層に被処理水を通
じる方式の家虹用浄水器等が市販されている。また食品
工業の分野においても、製品に箕奥がイ1かないJ:う
に活性炭吸着方式の水浄化システムが広く用いられてい
る。しかしこれ等の活性炭を使用した水浄化システムの
場合、長期間の使用により活性炭層が細菌の繁殖源とな
り、衛生」二問題がある。
It is also necessary to remove substances that cause bad odors, but the cause of these bad odors is significant water pollution of tap water sources due to regional development and domestic sewage. This tendency is particularly remarkable when the water source is lake water. In particular, due to eutrophication of lake water, the occurrence of red tide due to the mass proliferation of phytoplankton and the occurrence of foul-smelling river edges have been observed. This odor is often caused by substances secreted by cyanobacteria or microorganisms such as actinomycetes that adhere to organic matter deposited on the lake bottom. In order to remove these malodorous substances, water purifiers for household use that pass treated water through an activated carbon layer have recently been commercially available. In addition, in the food industry, water purification systems based on sea urchin activated carbon adsorption are widely used, as they do not have a negative impact on products. However, in the case of water purification systems using activated carbon, the activated carbon layer becomes a breeding ground for bacteria due to long-term use, resulting in two hygiene problems.

従って、本発明の目的は上記欠点がなくかつ安価な水処
理システムを提供することである。
It is therefore an object of the present invention to provide a water treatment system that does not have the above-mentioned drawbacks and is inexpensive.

本発明者等はかかる目的に鑑み鋭意研究の結果、本発明
の水処理システムを完成した。
In view of this objective, the present inventors have completed the water treatment system of the present invention as a result of intensive research.

本発明の水処理システムは、微小空孔を有する多孔質中
空糸膜を有するm退部を複数個所設けるとともに、濾過
部と濾過部の間のいずれかに少くとも1つの活性炭層を
設けてなるものであって、該活1g炭層の前段の濾過部
の少くとも1つは細菌を通過せしめないものである。
The water treatment system of the present invention includes a plurality of m-recess sections each having a porous hollow fiber membrane having micropores, and at least one activated carbon layer between the filtration sections. At least one of the filtration sections in front of the 1g activated carbon bed does not allow bacteria to pass through.

本発明に用いられる中空糸膜としては、細菌を通過ぜし
めないもの、あるいは更に、活性体微粉末等を通過せし
めないものとの組み合せであればどのJ:うな中空糸膜
も用いることができるが、パイロジエンも閉止できるも
ののほうが好ましく、特にポリエチレンやポリプロピレ
ン等のポリオレフィン類が好ましい。更に中空糸膜は細
長い円筒形状であり、その壁部は多数の短冊状の微小空
孔が存在し、多孔質であるものが好ましい。壁部の膜厚
は5〜150μ、中空間口部の直径は100〜300μ
、空孔率は30〜70体積%程度が好ましい。微小空孔
はII Ilt長方向に配向しており、平均的な幅は3
00〜5000Aであり、その長さと幅の比は8〜50
であることが好ましい。長さと幅の比が8より小さいと
より微小なものの捕捉が可能であるが流量が低下する。
As the hollow fiber membrane used in the present invention, any hollow fiber membrane can be used as long as it is combined with a membrane that does not allow bacteria to pass through or, furthermore, that does not allow active substance fine powder to pass through. However, it is preferable to use one that can also block pyrodiene, and polyolefins such as polyethylene and polypropylene are particularly preferable. Furthermore, the hollow fiber membrane has an elongated cylindrical shape, and the wall thereof is preferably porous, with many strip-shaped micropores present therein. The thickness of the wall is 5 to 150μ, and the diameter of the opening of the hollow space is 100 to 300μ.
The porosity is preferably about 30 to 70% by volume. The micropores are oriented in the II Ilt length direction, and the average width is 3
00~5000A, and its length to width ratio is 8~50
It is preferable that When the length to width ratio is smaller than 8, it is possible to capture even smaller objects, but the flow rate is reduced.

一方この比が50 、I:り大きくなると膜が弱くなり
、耐圧性が低下する。
On the other hand, when this ratio becomes larger than 50, I: the film becomes weaker and the pressure resistance decreases.

微小空孔は中空糸膜の内壁面から外壁面まで連通してい
る。水はこの孔を通過するが、細菌等の物質はこれに捕
捉される。このような短冊状の微小空孔を有する多孔質
中空糸膜は従来のストレートボアタイプの膜に比較して
より小さい物質を阻止し、目つ濾過性能の高い濾過部を
形成できる。
The micropores communicate from the inner wall surface to the outer wall surface of the hollow fiber membrane. Water passes through the pores, but substances such as bacteria are trapped. Such a porous hollow fiber membrane having strip-shaped micropores can block smaller substances than a conventional straight-bore type membrane, and can form a filtration section with high filtration performance.

またストレートボアタイプ膜に較べ低分子有機化合物の
除去性能に優れている。
It also has superior performance in removing low-molecular organic compounds compared to straight bore type membranes.

濾過部の中間に設けられる活性炭層では、被処理水の水
質に応じて種々の活性炭を使用することができるが、例
えば粒状ヤシガラ活性炭が好ましい。活(/l炭層はそ
の前段に少くとも1つの細菌を通過させない濾過部があ
るために、常に無菌状態に保つことができ、水処理シス
テムを衛生的にすることができる。
In the activated carbon layer provided in the middle of the filtration section, various activated carbons can be used depending on the quality of the water to be treated, and for example, granular coconut shell activated carbon is preferable. Since the live carbon bed has at least one filtration section in front of it that does not allow bacteria to pass through, it can always be kept in a sterile state, making the water treatment system sanitary.

更に多孔質中空糸膜の濾過部を活性炭層の後段にも設け
ることにより、活性炭の劣化により生ずる微11T1 
’J粉末の流出を防ぐことができる。
Furthermore, by providing a porous hollow fiber membrane filtration section downstream of the activated carbon layer, fine 11T1 generated due to deterioration of activated carbon can be removed.
'J powder can be prevented from flowing out.

次に、本発明の水処理システムを図面にしたがって更に
詳細に説明ジる。
Next, the water treatment system of the present invention will be explained in more detail according to the drawings.

第1図は本発明の水処理システムの一実施例を示す。第
1図の水処理システムはAとCで示される多孔質中空糸
膜からなる濾過部と、その中間に設りられた活性炭式水
処理部Bとから構成される。
FIG. 1 shows an embodiment of the water treatment system of the present invention. The water treatment system shown in FIG. 1 is composed of a filtration section made of porous hollow fiber membranes indicated by A and C, and an activated carbon type water treatment section B installed between the filtration sections.

なお、AとC(′f)i11過部に使用される多孔質中
空糸膜としては、具体的には、ポリプロピレン、ポリエ
チレン等からなるポリオレフィン系のものが好ましい。
Specifically, the porous hollow fiber membrane used for A and C('f)i11 is preferably a polyolefin membrane made of polypropylene, polyethylene, or the like.

そしてこの多孔質中空糸膜は例えば平均幅300〜50
00A、長さと幅の比が8〜50でIJi Iff長方
向に配向したスリット状微小空孔を多数有し、空孔串が
30〜70体積%程度、中空間口部の直径が100〜3
00μ、壁膜層の厚さ5〜150μ程度のものが好まし
い。
This porous hollow fiber membrane has an average width of 300 to 50, for example.
00A, the length to width ratio is 8 to 50, IJi Iff has many slit-like micro holes oriented in the longitudinal direction, the hole skewer is about 30 to 70% by volume, and the diameter of the opening of the hollow space is 100 to 3
00μ, and the thickness of the wall film layer is preferably about 5 to 150μ.

濾過部において、多孔質中空糸膜(1)は束状にして例
えば第1図に示すようにU字形に曲げられ、その両端部
付近は中空間口部を密閉することなく、例えばポリウレ
タン系樹脂接着剤等により固定部拐(2〉に接着固定化
されている。このように作成した中空糸膜モジュールは
取水口と排水口を有する容器に収納される。
In the filtration section, the porous hollow fiber membrane (1) is bent into a bundle and bent, for example, into a U-shape as shown in Fig. 1, and the vicinity of both ends is filled with, for example, polyurethane resin without sealing the opening of the hollow space. It is adhesively fixed to the fixing part (2) using an adhesive or the like. The hollow fiber membrane module thus produced is housed in a container having a water intake port and a drainage port.

活性炭式水処理部は、被処理水の水質に応じて種々の活
性炭を用いjqるが、−例として容器の中に粒状ヤシガ
ラ活性炭を充填せしめたものがある。
Activated carbon type water treatment units use various types of activated carbon depending on the quality of the water to be treated. For example, there is one in which a container is filled with granular coconut shell activated carbon.

つぎに第1図の水処J!1′!システムの作用について
説明する。Aの濾過部において水中に含まれる細菌m、
パイロジエン、コロイド状物質、低分子有機化合物等は
スリット状微小空孔が多数存在する多孔質中空糸膜J:
りなる濾過材によってほぼ完全に除去される。そして濾
過部Δを経た水は、活性炭式水処理部Bにおいて水中の
異臭物質等が捕捉され、続いて濾過部Cを経て浄化水が
得られる。
Next, the water place J in Figure 1! 1′! Explain how the system works. Bacteria m contained in the water in the filtration part of A,
Pyrodiene, colloidal substances, low-molecular organic compounds, etc. are used in porous hollow fiber membranes with many slit-like micropores:
It is almost completely removed by a separate filter medium. The water that has passed through the filtration section Δ is subjected to an activated carbon type water treatment section B in which odor substances and the like in the water are captured, and then passes through the filtration section C to obtain purified water.

濾過部△には、前述したような特VA、な微細拷造を有
する多孔質中空糸膜が用いられているために上述の如き
物質の除去はほぼ完全である。しかし水中の異臭の原因
である殺菌剤としての塩素や前述した如さら/υ藻類か
らの分泌物としての臭気成分は除去されないので、Bの
部分において除去することになる。またBの部分の活性
炭の劣化に併うful1粒状物はCの部分によって除去
することができる。またBの前段の濾過部Aにより細菌
類を完全に除去できるので、Bの部分無菌状態に保たれ
る。
Since the filtration section Δ uses a porous hollow fiber membrane having a special VA fine structure as described above, the above-mentioned substances can be almost completely removed. However, since chlorine as a disinfectant and the above-mentioned odor components as secretions from algae are not removed, they are removed in part B. In addition, the ful1 particulate matter accompanying the deterioration of the activated carbon in the B part can be removed by the C part. Furthermore, since bacteria can be completely removed by the filtration section A before B, B can be kept partially sterile.

本発明の水処理システムは例えば水道の蛇口に接続づ゛
るだけで充分な水出が得られる。これはへ部と0部の濾
過材に有効−過面積の大きい多孔質中空糸膜が使用され
ており、濾過抵抗が小さいことによる。従って、特別な
送水ポンプ等を使用する必要がなく、安価に浄化水がえ
られる。
The water treatment system of the present invention can provide sufficient water output simply by connecting it to a water faucet, for example. This is because porous hollow fiber membranes with a large effective filtration area are used for the filtration media in the hem part and the 0 part, and the filtration resistance is small. Therefore, there is no need to use a special water pump or the like, and purified water can be obtained at low cost.

第2図乃至第5図は本発明の水処理システムの別の実施
態様を示す。第2図のシステムはA、B。
2-5 show another embodiment of the water treatment system of the present invention. The systems in Figure 2 are A and B.

Cの3箇の多孔質中空糸膜J:す4rる濾過部と活性炭
式水処理部Bを有する。第3図のシステl\においては
、A及びCの2個の該濾過部の間に種類の異なる活+1
炭の活性炭式水処理部[及びFが設けられている。第4
図のシステムでは、各2つの活性i3’J水処理部は、
それぞれ濾過部にはさまれている。また、第5図のよう
に1個のハウジングを3空に区切りり、2個の濾過部Δ
及びCの間に活性炭式水処理部Bを設ける形式どするこ
ともできる。
Three porous hollow fiber membranes J: C have a filtration section and an activated carbon type water treatment section B. In the system I\ shown in Fig. 3, different types of active +1
An activated carbon type water treatment section [and F] are provided. Fourth
In the system shown, each of the two active i3'J water treatment units is
Each is sandwiched between filter sections. Also, as shown in Fig. 5, one housing is divided into three spaces, and two filter parts Δ
It is also possible to provide an activated carbon type water treatment section B between and C.

このように本発明においては、複数個の多孔質中空糸膜
からなる濾過部と該濾過部と濾過部の間のいずれかに少
なくとも一つの活性炭式処理部が設けられ、該活性炭式
処理部の前段の濾過部の少なくと・し1つが細菌を透過
せしめないものであれば、秤々の形式のものとすること
ができる。次に本発明の水処理システムを使用した水処
理の実施例を示す。
In this way, in the present invention, at least one activated carbon treatment section is provided between the filtration section made of a plurality of porous hollow fiber membranes and between the filtration sections. As long as at least one of the preceding filtration parts does not allow bacteria to pass through, it can be of the scale type. Next, an example of water treatment using the water treatment system of the present invention will be shown.

実施例1 第1図に示したシステムにおいて、濾過部A及びCに空
孔率が63体積%、膜W60μ、中空間口部の孔径(内
径)270μのポリエチレン多孔質中空孔膜からなる痘
過拐を使用し活性炭式水処 4理部Bに粒状Vシガラ活
性炭を充填した。この水処理システムにより、ポンプを
使用して1Kg/Cdの水圧をか()て池の水を濾過し
た。濾過前後の水について水質試験をおこなった。結果
を次表に示す。
Example 1 In the system shown in FIG. 1, the filtration parts A and C were made of a polyethylene porous hollow membrane with a porosity of 63% by volume, a membrane width of 60μ, and a pore diameter (inner diameter) of 270μ at the mouth of the hollow space. Activated carbon type water treatment 4 Part B was filled with granular V-cigara activated carbon. This water treatment system filtered pond water by applying a water pressure of 1 Kg/Cd using a pump. Water quality tests were conducted on the water before and after filtration. The results are shown in the table below.

比較例 ■シガラ活竹炭式水処理部の前段に市販のストレートボ
アタイプの孔径0.2μ、濾過面積0゜5cm’の平膜
型モジュールを用いて、ポンプで水圧I K Q’/ 
ct?にして、池の水を濾過した。初期流最は1 、2
t/minであったが、3時間濾過後流量は015j/
minに低下した。流量低下を防止するためにストレー
トボアタイプの孔径0.6μ、濾過面積0.5m”の平
膜型モジュールを使用して濾過を行なった。この場合濾
過水中の細菌テストの結果、33個/ ml の一般細
菌が検出された。
Comparative example - Using a commercially available straight bore type flat membrane module with a pore diameter of 0.2μ and a filtration area of 0°5cm' in the front stage of the Shigara activated bamboo charcoal water treatment section, the water pressure I K Q'/
ct? and filtered the pond water. The initial flow is 1, 2
t/min, but the flow rate after 3 hours of filtration was 015j/min.
It decreased to min. In order to prevent a decrease in flow rate, filtration was performed using a straight-bore type flat membrane module with a pore diameter of 0.6 μ and a filtration area of 0.5 m. In this case, a bacterial test in the filtrated water showed that 33 bacteria/ml. General bacteria were detected.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図乃至第5図は本発明の中空糸膜モジュールの濾過
部と活性炭層部とを有する水処理システ11のそれぞれ
の実施態様を示す。 A、C,D+ スリット状微小空孔を多数有する多孔質
中空糸膜からなる濾過部。 B、E、F: 活性炭層部 1: 中空糸膜 2: 接着固定部 3.4: 粒状ヤシガラ活性炭 特許出願代理人 弁理土山 崎 行 造
1 to 5 show respective embodiments of a water treatment system 11 having a filtration section and an activated carbon layer section of the hollow fiber membrane module of the present invention. A, C, D+ A filtration section made of a porous hollow fiber membrane having a large number of slit-like micropores. B, E, F: Activated carbon layer part 1: Hollow fiber membrane 2: Adhesive fixing part 3.4: Granular coconut shell activated carbon Patent application agent Yukizo Tsuchiyama Saki

Claims (1)

【特許請求の範囲】 (1) 水処理方法であって、被処理水を細菌を通過せ
しめない多孔質中空糸膜からなる濾過部により濾過し、
次に活性炭層を通し、しかる後多孔質中空糸膜からなる
別の濾過部により濾過することを含む方法。 (2、特許請求の範囲第1項に記載の方法において、前
記多孔質中空糸膜がポリオレフィンからなることを特徴
とする方法。 (3) 特許請求の範囲第1項又は第2項に記載の方法
において、前記多孔質中空糸膜は5〜150μの膜厚を
有する中空円筒状であって、多数のm組長方向に配向し
た短冊状微小空孔を有し、前記微小空孔は平均300〜
5000△の幅を有し、その良さと幅の比は平均8〜5
0であり、かつ前記微小空孔は前記中空糸膜の内壁面か
ら外壁面まで連通していることを特徴とする方法。 (4) 多孔質中空糸膜からなる複数の濾過部と該複数
の濾過部の中間に設けらねた少くとも1つの活性炭層を
有し、前記活性炭層の前段の濾過部の少くとも1つは細
菌を通過せしめないものであることを特徴とする水処理
装置。 (5) 特許請求の範囲第4項に記載の装置において、
前記多孔質中空糸膜がポリオレフィンからなることを特
徴とする装置。 (6) 特許請求の範囲第4項又は第5項に記載の装置
において、前記多孔質中空糸膜は5〜150μの膜厚を
有する中空円筒状であって、多数のIN長方向に配向し
た短冊状微小空孔を有し、前記微小空孔は平均300〜
booo人の幅を有し、その長さと幅の比は平均8〜5
oであり、かつ前記微小空孔は前記中空糸膜の内壁面か
ら外壁面まで連通していることを特徴とする装置。
[Claims] (1) A water treatment method, which comprises filtering the water to be treated through a filtration section made of a porous hollow fiber membrane that does not allow bacteria to pass through;
A method comprising then filtering through a layer of activated carbon and then through another filtration section consisting of a porous hollow fiber membrane. (2. The method according to claim 1, wherein the porous hollow fiber membrane is made of polyolefin. (3) The method according to claim 1 or 2. In the method, the porous hollow fiber membrane has a hollow cylindrical shape with a thickness of 5 to 150 μm, and has a large number of strip-shaped micropores oriented in the m length direction, and the micropores have an average of 300 to 150 micropores.
It has a width of 5000△, and the ratio of width to goodness is 8 to 5 on average
0, and the micropores are in communication from the inner wall surface to the outer wall surface of the hollow fiber membrane. (4) It has a plurality of filtration sections made of porous hollow fiber membranes and at least one activated carbon layer provided between the plurality of filtration sections, and at least one of the filtration sections before the activated carbon layer. A water treatment device characterized in that it does not allow bacteria to pass through. (5) In the device according to claim 4,
An apparatus characterized in that the porous hollow fiber membrane is made of polyolefin. (6) In the device according to claim 4 or 5, the porous hollow fiber membrane has a hollow cylindrical shape with a thickness of 5 to 150μ, and has a plurality of INs oriented in the longitudinal direction. It has strip-shaped micropores, and the micropores have an average of 300 to 300 micropores.
boooo human width, with an average length-to-width ratio of 8 to 5
o, and the micropores are in communication from the inner wall surface to the outer wall surface of the hollow fiber membrane.
JP17470583A 1983-09-21 1983-09-21 Water treating system Pending JPS6068093A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP17470583A JPS6068093A (en) 1983-09-21 1983-09-21 Water treating system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP17470583A JPS6068093A (en) 1983-09-21 1983-09-21 Water treating system

Publications (1)

Publication Number Publication Date
JPS6068093A true JPS6068093A (en) 1985-04-18

Family

ID=15983215

Family Applications (1)

Application Number Title Priority Date Filing Date
JP17470583A Pending JPS6068093A (en) 1983-09-21 1983-09-21 Water treating system

Country Status (1)

Country Link
JP (1) JPS6068093A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2692153A1 (en) * 1992-06-11 1993-12-17 Pall Corp Heat and humidity exchanger filter.
JPH08243366A (en) * 1995-03-13 1996-09-24 Nikkiso Co Ltd Removing method of endotoxin, endotoxin adsorbing apparatus, endotoxin adsorption membrane and endotoxin removing device
NL1017681C2 (en) * 2001-03-23 2002-10-10 Prime Water Systems Gmbh Filter system.

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2692153A1 (en) * 1992-06-11 1993-12-17 Pall Corp Heat and humidity exchanger filter.
JPH08243366A (en) * 1995-03-13 1996-09-24 Nikkiso Co Ltd Removing method of endotoxin, endotoxin adsorbing apparatus, endotoxin adsorption membrane and endotoxin removing device
NL1017681C2 (en) * 2001-03-23 2002-10-10 Prime Water Systems Gmbh Filter system.
WO2002076590A3 (en) * 2001-03-23 2002-12-12 Prime Water Systems Gmbh Filtering system
US7422690B2 (en) 2001-03-23 2008-09-09 Prime Water Systems Gmbh Filtering system

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