JPH0630793B2 - Water circulation system - Google Patents
Water circulation systemInfo
- Publication number
- JPH0630793B2 JPH0630793B2 JP60158235A JP15823585A JPH0630793B2 JP H0630793 B2 JPH0630793 B2 JP H0630793B2 JP 60158235 A JP60158235 A JP 60158235A JP 15823585 A JP15823585 A JP 15823585A JP H0630793 B2 JPH0630793 B2 JP H0630793B2
- Authority
- JP
- Japan
- Prior art keywords
- water
- wastewater
- membrane
- water circulation
- hydrophobic porous
- 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.)
- Expired - Lifetime
Links
Landscapes
- Separation Using Semi-Permeable Membranes (AREA)
- Water Treatment By Sorption (AREA)
Description
【発明の詳細な説明】 〔発明の利用分野〕 本発明は、排水管を浄化して飲料水等として再利用する
水循環処理システムに係り、特に宇宙ステーシヨンや潜
水艦のような閉鎖系空間での再利用に好適な水循環シス
テムに関する。Description: FIELD OF THE INVENTION The present invention relates to a water circulation treatment system for purifying a drainage pipe and reusing it as drinking water or the like, and particularly to a recycle system in a closed space such as a space station or a submarine. The present invention relates to a water circulation system suitable for use.
従来、排水を処理して再利用するための水処理技術とし
ては、特開昭55-35972号公報、或は技術雑誌「日経メカ
ニカル」1984年5月21日号、p55に“256Kビツ
トささえる超純水製造装置、膜材質、配管、測定技術を
総動員”として内容が紹介されている様に、限外過や
逆浸透などの膜を利用した処理技術があり、これを単独
あるいは組合せたシステムにより水を浄化する。しか
し、宇宙空間のように限られた極めて狭い空間で、しか
も、飲料に供することができるまで排水を高度に浄化す
るには、従来の限外過や逆浸透では有機物の除去が不
充分なこと、高い運転圧力を必要とすること、水の回収
率が低いこと、などいくつかの欠点がある。Conventionally, as a water treatment technology for treating and reusing wastewater, Japanese Patent Laid-Open No. 55-35972, or technical magazine "Nikkei Mechanical" May 21, 1984, p55, "Super 256K Bit Support" As the content is introduced as "total mobilization of pure water production equipment, membrane material, piping, and measurement technology", there are treatment technologies using membranes such as ultrafiltration and reverse osmosis, which can be used individually or in combination. Purify water. However, in extremely limited space such as outer space, and in order to highly purify wastewater until it can be used for beverages, removal of organic substances by conventional ultrafiltration and reverse osmosis is insufficient. There are some drawbacks such as high operating pressure, low water recovery and so on.
本発明の目的は、宇宙ステーシヨンや潜水艦のような閉
鎖系空間で人間あるいは動植物などから排出される排水
(シヤワー水、尿、石けん水、植物栽培排水、培養排
水、など)を浄化して飲料水や生活用水、栽培用水など
に用いる水循環処理システムを提供することにある。An object of the present invention is to purify drinking water (shear water, urine, soap water, plant cultivation drainage, culture drainage, etc.) discharged from humans or animals and plants in a closed space such as a space station or a submarine, and drinking water. The purpose is to provide a water circulation treatment system for water for daily use, water for cultivation, and the like.
本発明の特徴は、疎水性多孔質膜を分離膜として用いる
いわゆるサーモパーベーパレーシヨン法を排水中からの
不純物分離手段として用い、膜の疎水性を維持するため
に、サーモパーベーパレーシヨンの前処理として活性炭
吸着などの有機物除去手段を設けることにある。A feature of the present invention is that the so-called thermopervaporation method using a hydrophobic porous membrane as a separation membrane is used as a means for separating impurities from wastewater, and in order to maintain the hydrophobicity of the membrane, a thermopervaporation As a pretreatment, an organic substance removing means such as activated carbon adsorption is provided.
本発明のもうひとつの特徴はサーモパーベーパレーシヨ
ン法で濃縮された排水を晶析器のような固形物分離装置
に送り、固形物を分離した上澄液は再びサーモパーベー
パレーシヨンで処理して浄化水を100%近くまで高効
率で回収することにある。Another feature of the present invention is to send the wastewater concentrated by the thermopervaporation method to a solid matter separation device such as a crystallizer, and the supernatant liquid from which the solid matter is separated is treated again by the thermopervaporation method. It is to collect purified water up to 100% with high efficiency.
第1図にサーモパーベーパレーシヨン法の原理を示す。
ここで用いる膜はいわゆる疎水性多孔質膜で、膜面に接
している排水は加温され一部が膜面で蒸発する。蒸発し
た蒸気は膜の細孔(0.1〜1.0μm)を通り、膜と
相対して設けられている冷却面まで拡散しここで冷却さ
れ凝縮する。凝縮した水は蒸発および膜透過の2段の分
離操作を経ているので、排水中の不純物の99.99%以上
は除去された極めて高純度の水となる。ここで、排水浄
化のエネルギーは温度差なので排水を加温するためのエ
ネルギーは電気ヒータによることも、排熱系の熱で直接
排水を加温しても良い。宇宙船等では各種の電子機器や
制御機器から多量の排熱が発生するので、これらの排熱
を熱源として有効に利用することも可能である。Fig. 1 shows the principle of the thermo-pervaporation method.
The membrane used here is a so-called hydrophobic porous membrane, and the wastewater in contact with the membrane surface is heated and a part thereof is evaporated on the membrane surface. The vaporized vapor passes through the pores (0.1 to 1.0 μm) of the film, diffuses to the cooling surface provided facing the film, and is cooled and condensed here. Since the condensed water has undergone a two-stage separation operation of evaporation and membrane permeation, 99.99% or more of the impurities in the waste water have been removed, resulting in extremely high purity water. Here, since the energy for purifying the wastewater has a temperature difference, the energy for heating the wastewater may be supplied from an electric heater, or the wastewater may be directly heated by the heat of the exhaust heat system. In a spacecraft or the like, a large amount of exhaust heat is generated from various electronic devices and control devices, and thus it is possible to effectively use the exhaust heat as a heat source.
ここで用いる疎水性多孔質膜の材質としては、通常、PT
FE(ポリテトラフルオロエチレン)ポリプロピレン製等
が用いられ、孔径は0.1〜1.0μmが用いられる。The material of the hydrophobic porous membrane used here is usually PT
FE (polytetrafluoroethylene) polypropylene or the like is used, and the pore size is 0.1 to 1.0 μm.
第2図は不純物として3.4wt%のNaClを含む排水
をサーモパーベーパレーシヨン法で浄化した場合の単位
膜面積あたりの透過水量Qと得られた透過水の電気伝導
度を示した実験結果である。図のように、透過水量Qは
排水(高温度)と冷却水(低温)の蒸気圧差ΔPに一次
的に比例する。また、透過水の電導度はΔPによらない
が、平均して10μs/cmと、排水の電導度約48ms/c
mに比べて4桁以上低くなつており、極めて高純度であ
る。Fig. 2 shows the experimental results showing the permeated water amount Q per unit membrane area and the electric conductivity of the obtained permeated water when the wastewater containing 3.4 wt% NaCl as an impurity was purified by the thermo-pervaporation method. Is. As shown in the figure, the permeated water amount Q is linearly proportional to the vapor pressure difference ΔP between the waste water (high temperature) and the cooling water (low temperature). The conductivity of the permeated water does not depend on ΔP, but on average it is 10 μs / cm, and the conductivity of the drainage is about 48 ms / c.
It is more than 4 orders of magnitude lower than m and is extremely high in purity.
以下、本発明の一実施例を第3図により説明する。 An embodiment of the present invention will be described below with reference to FIG.
宇宙船内の人間生活あるいは動植物の飼育、栽培の結果
排出される排水は、まず、カートリツジフイルターのよ
うなプレフイルター1で微細な固形物を除去した後、活
性炭のような有機物を吸着除去する装置2で排水中の有
機物を除去する。有機物を除去するのは、後段のサーモ
パーベーパレーシヨンで用いている疎水性多孔質膜の疎
水性を維持するためである。排水中の界面活性剤などの
有機物が疎水性膜表面に付着すると、膜の表面が親水性
となり、排水が直接膜の細孔を通過するようになるの
で、疎水性の維持には特に注意せねばならない。Wastewater discharged as a result of human life in the spacecraft or breeding and cultivation of animals and plants is a device that first removes fine solids with a prefilter 1 such as a cartridge filter and then adsorbs and removes organic substances such as activated carbon. At 2, the organic matter in the waste water is removed. The organic matter is removed in order to maintain the hydrophobicity of the hydrophobic porous membrane used in the subsequent thermopervaporation. When organic substances such as surfactants in wastewater adhere to the surface of the hydrophobic membrane, the surface of the membrane becomes hydrophilic and the wastewater directly passes through the pores of the membrane, so be especially careful to maintain hydrophobicity. I have to.
有機物を除去された排水は、次にサーモパーベーパレー
シヨン膜分離装置3に入り、第1図に示したような原理
により膜透過水5が得られる。膜透過水は、第2図に示
したように極めて高純度なので、飲料水やその他の生活
用水に供することができる。The wastewater from which the organic substances have been removed then enters the thermo-pervaporation membrane separation device 3, and the membrane permeated water 5 is obtained according to the principle shown in FIG. Since the membrane-permeated water has an extremely high purity as shown in FIG. 2, it can be used as drinking water or other domestic water.
一方、膜を透過しない排水は徐々に濃縮され、排水中の
溶解性不純物が溶解度以上にすると固形物として析出し
てくるので、析出する前濃縮水管6により晶析器4に送
入しここで析出した固形物7を分離する。固形物分離後
の上澄水戻し管8により再びパーベーパレーシヨン膜分
離装置3に入る。したがつて、排水から透過水は高効率
で回収でき再び使用可能となる。On the other hand, the wastewater that does not pass through the membrane is gradually concentrated, and if the soluble impurities in the wastewater exceed the solubility, they will precipitate as a solid matter. Therefore, they are sent to the crystallizer 4 by the preconcentrated concentrated water pipe 6 where they are deposited. The precipitated solid 7 is separated. After the solids are separated, the supernatant water return pipe 8 enters the pervaporation membrane separator 3 again. Therefore, the permeated water can be recovered from the wastewater with high efficiency and can be used again.
ここでサーモパーベーパレーシヨン装置で排水を加温す
る加温源9としては宇宙船内で使用される電子機器や制
御機器などから発生する排熱を用いている。Here, as the heating source 9 for heating the waste water in the thermo pervaporation device, exhaust heat generated from electronic devices and control devices used in the spacecraft is used.
本発明のもうひとつの実施例を第4図にブロツク線図で
示す。ここでは、排水100はプレフイルター1限外
過11、逆浸透12でまず前処理され大部分の不純物が
除かれる。再利用する水質として飲料水のように高度に
浄化しなくても使用可能なシヤワー水や動植物飼育、栽
培用水110には、逆浸透12までの処理水が用いられ
る。飲料水120のように高度に浄化する必要がある用
水には、逆浸透12での透過水を活性炭処理13し、こ
れをパーベーパレーシヨン3で浄化する。このようにす
れば、パーベーパレーシヨン3での処理量は少なくてす
むので、装置はさらに小形となる。Another embodiment of the present invention is shown in the block diagram of FIG. Here, the wastewater 100 is first pretreated by the prefilter 1 ultrafiltration 11 and reverse osmosis 12 to remove most impurities. As the water quality to be reused, treated water up to reverse osmosis 12 is used as shower water, animal and plant breeding water 110, which can be used without highly purified like drinking water. For water that needs to be highly purified, such as drinking water 120, the permeated water in reverse osmosis 12 is treated with activated carbon 13 and this is purified with pervaporation 3. By doing so, the amount of processing in the pervaporation 3 can be small, and therefore the apparatus can be made more compact.
本発明によれば、疎水性多孔質膜を用いたサーモパーベ
ーパレーシヨン法により排水を処理するので、蒸発と膜
分離の2段操作で排水を浄化でき極めて高純度な水を、
小形の装置で得ることができる。また、前処理として活
性炭のような有機物除去装置を備えているので、膜の疎
水性を維持でき安定した運転が可能となる効果がある。
また、パーベーパレーシヨンの濃縮水を晶析器で処理し
析出固形物を分離できるので、排水から浄化水を高効率
で回収できる効果である。さらに、宇宙船内で本システ
ムを使用する場合は、サーモパーベーパレーシヨンの熱
源として、宇宙船内で発生する排熱を直接排水の加熱源
として用いることができるので、排水の処理コストを低
減できる効果がある。According to the present invention, since the wastewater is treated by the thermopervaporation method using the hydrophobic porous membrane, the wastewater can be purified by the two-step operation of evaporation and membrane separation, and extremely high-purity water can be obtained.
It can be obtained with a small device. Further, since the apparatus for removing organic substances such as activated carbon is provided as the pretreatment, there is an effect that the hydrophobicity of the membrane can be maintained and stable operation can be performed.
Further, the concentrated water of the pervaporation can be treated with a crystallizer to separate the precipitated solid matter, so that the purified water can be recovered from the waste water with high efficiency. Furthermore, when this system is used in a spacecraft, the exhaust heat generated in the spacecraft can be used directly as the heat source of the thermo-pervaporation, and the wastewater treatment cost can be reduced. There is.
第1図はサーモパーベーパレーシヨン膜分離の排水処理
原理モデル、第2図はサーモパーベーパレーシヨン膜分
離法によりモデル排水を処理した実験結果、第3図は本
発明の一実施例である排水処理システム、第4は本発明
の他の実施例である排水処理システムである。 1……プレフイルター、2……有機物除去装置、3……
サーモパーベーパレーシヨン膜分離装置、4……晶析
器、5……膜透過水、6……濃縮水管、7……固形物、
8……戻し管、9……加熱源。FIG. 1 is a model of wastewater treatment for thermopervaporation membrane separation, FIG. 2 is an experimental result of treating model wastewater by the thermopervaporation membrane separation method, and FIG. 3 is one embodiment of the present invention. A wastewater treatment system, the fourth is a wastewater treatment system which is another embodiment of the present invention. 1 ... Prefilter, 2 ... Organic matter removing device, 3 ...
Thermopervaporation membrane separator, 4 ... Crystallizer, 5 ... Membrane permeate, 6 ... Concentrated water pipe, 7 ... Solid matter,
8 ... Return tube, 9 ... Heating source.
───────────────────────────────────────────────────── フロントページの続き (72)発明者 黒川 秀明 茨城県日立市久慈町4026番地 株式会社日 立製作所日立研究所内 (72)発明者 高橋 燦吉 茨城県日立市久慈町4026番地 株式会社日 立製作所日立研究所内 (72)発明者 芦田 章 東京都千代田区神田駿河台4丁目6番地 株式会社日立製作所内 ─────────────────────────────────────────────────── ─── Continuation of front page (72) Hideaki Kurokawa 4026 Kuji Town, Hitachi City, Hitachi City, Ibaraki Prefecture Hitachi Research Laboratory Ltd. Hitachi, Ltd. (72) Inventor Akira Ashida 4-6, Sugawadai Kanda, Chiyoda-ku, Tokyo Hitachi, Ltd.
Claims (3)
活や動植物などの飼育栽培装置から発生する排水を浄化
し飲料水やその他用水に再利用するための水循環処理シ
ステムにおいて、疎水性多孔質膜を用いて排水処理を行
ない、かつ前期疎水性多孔質膜を用いた水処理装置の前
に活性炭などの有機物除去装置を特徴とする水循環シス
テム。1. A water circulation treatment system for purifying wastewater generated from human-life and breeding and cultivating equipment for animals and plants in a closed space such as a spaceship or submarine and reusing it as drinking water or other water. A water circulation system that uses organic matter membranes for wastewater treatment and features an organic matter removal device such as activated carbon in front of a water treatment device that uses a hydrophobic porous membrane.
孔質膜で濃縮された排水を晶析器に導入し濃縮排水中の
固形物を分離した後の上澄液を再び疎水性多孔質膜を用
いた水処理装置に導入することを特徴とする水循環シス
テム。2. The method according to claim 1, wherein the wastewater concentrated by the hydrophobic porous membrane is introduced into a crystallizer to separate the solid matter in the concentrated wastewater, and the supernatant liquid is again made into the hydrophobic porous material. A water circulation system characterized by being introduced into a water treatment device using a membrane.
孔質膜を用いた水処理装置の処理エネルギー源として宇
宙船内等で発生する排熱を利用することを特徴とする水
循環システム。3. The water circulation system according to claim 1, wherein exhaust heat generated in a spacecraft or the like is used as a treatment energy source of the water treatment device using the hydrophobic porous membrane.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP60158235A JPH0630793B2 (en) | 1985-07-19 | 1985-07-19 | Water circulation system |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP60158235A JPH0630793B2 (en) | 1985-07-19 | 1985-07-19 | Water circulation system |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6219299A JPS6219299A (en) | 1987-01-28 |
| JPH0630793B2 true JPH0630793B2 (en) | 1994-04-27 |
Family
ID=15667226
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP60158235A Expired - Lifetime JPH0630793B2 (en) | 1985-07-19 | 1985-07-19 | Water circulation system |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0630793B2 (en) |
Families Citing this family (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH03186800A (en) * | 1989-12-15 | 1991-08-14 | Hitachi Ltd | Radioactive waste liquid treatment facilities |
| JP2007137765A (en) * | 2006-12-22 | 2007-06-07 | Takenaka Komuten Co Ltd | Apparatus for producing concentrated salt water |
| JP5463022B2 (en) * | 2008-11-20 | 2014-04-09 | 三菱重工業株式会社 | Wastewater treatment apparatus and method for space station |
| KR20160123822A (en) * | 2015-04-17 | 2016-10-26 | 한국과학기술연구원 | Apparatus for treatment of a high temperature wastewater by using a membrane distillation process |
| CN109673498A (en) * | 2019-01-22 | 2019-04-26 | 宁夏保利节能科技有限公司 | A kind of water purifier concentration Water warfare reuse means and its method |
| JP7740457B1 (en) * | 2024-04-02 | 2025-09-17 | 栗田工業株式会社 | Apparatus and method for recovering water from wastewater containing organic matter |
-
1985
- 1985-07-19 JP JP60158235A patent/JPH0630793B2/en not_active Expired - Lifetime
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6219299A (en) | 1987-01-28 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| US8753514B2 (en) | Osmotic desalination process | |
| US9822021B2 (en) | Forward osmosis separation processes | |
| US20110180479A1 (en) | Zero liquid discharge water treatment system and method | |
| JPH02293023A (en) | Combination method of membrane separation | |
| JP2013509295A (en) | Forward osmosis separation method | |
| WO2009155596A2 (en) | Forward osmosis separation processes | |
| KR102816674B1 (en) | Apparatus and Method for processing organic waste | |
| JPH0630793B2 (en) | Water circulation system | |
| JP2765032B2 (en) | Method for producing concentrated solution of volatile organic liquid aqueous solution | |
| JPH04290597A (en) | water treatment equipment | |
| JP4966523B2 (en) | Biomass processing system | |
| EA017489B1 (en) | Water purification method and apparatus therefor | |
| JPH01115493A (en) | Method for regenerating water from domestic waste water | |
| JP4709467B2 (en) | Method and apparatus for treating wastewater containing organic chemicals | |
| US3450508A (en) | Extraction of salts from saline water using dimethylsulfoxide | |
| JPH08224572A (en) | Closed system ultrapure water production and wastewater treatment method | |
| JP2981077B2 (en) | Mineral recovery method and mineral recovery device | |
| JP2721694B2 (en) | How to collect pure water from wastewater | |
| JPH08318136A (en) | Seawater desalting and salt manufacturing method | |
| US20240294412A1 (en) | Method and apparatus for desalination of high-salt and high-concentration organic wastewater by coupling three membrane separation technologies | |
| JP2002191941A (en) | Method and apparatus for concentrating solute by reverse osmosis membrane | |
| Nitta et al. | Water recycling system using thermopervaporation method | |
| JPH11244846A (en) | Treatment of diluted liquid to be treated and device therefor | |
| JP2011101883A (en) | Treatment method for organic chemical containing wastewater and apparatus of the same | |
| JPH08155434A (en) | Pure water recovery system from wastewater |