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JPH0822434B2 - Method and apparatus for treating salt-containing water - Google Patents
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JPH0822434B2 - Method and apparatus for treating salt-containing water - Google Patents

Method and apparatus for treating salt-containing water

Info

Publication number
JPH0822434B2
JPH0822434B2 JP2168097A JP16809790A JPH0822434B2 JP H0822434 B2 JPH0822434 B2 JP H0822434B2 JP 2168097 A JP2168097 A JP 2168097A JP 16809790 A JP16809790 A JP 16809790A JP H0822434 B2 JPH0822434 B2 JP H0822434B2
Authority
JP
Japan
Prior art keywords
water
salt
concentration
reverse osmosis
osmosis membrane
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 - Fee Related
Application number
JP2168097A
Other languages
Japanese (ja)
Other versions
JPH0461983A (en
Inventor
紀宏 川島
健 安国
弘一 田太
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.)
Kawasaki Motors Ltd
Original Assignee
Kawasaki Jukogyo KK
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 Kawasaki Jukogyo KK filed Critical Kawasaki Jukogyo KK
Priority to JP2168097A priority Critical patent/JPH0822434B2/en
Priority to US07/719,507 priority patent/US5238574A/en
Priority to DE69123644T priority patent/DE69123644T2/en
Priority to EP91110447A priority patent/EP0463605B1/en
Priority to PL91290803A priority patent/PL173335B1/en
Publication of JPH0461983A publication Critical patent/JPH0461983A/en
Publication of JPH0822434B2 publication Critical patent/JPH0822434B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A20/00Water conservation; Efficient water supply; Efficient water use
    • Y02A20/124Water desalination
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A20/00Water conservation; Efficient water supply; Efficient water use
    • Y02A20/124Water desalination
    • Y02A20/131Reverse-osmosis

Landscapes

  • Separation Using Semi-Permeable Membranes (AREA)
  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、塩分を多量に含む含塩分水を、複数段の高
圧及び低圧の逆浸透膜モジュールに通して処理する方法
及び装置に関するものである。
TECHNICAL FIELD The present invention relates to a method and an apparatus for treating salt-containing water containing a large amount of salt through a multi-stage high pressure and low pressure reverse osmosis membrane module. is there.

〔従来の技術〕[Conventional technology]

例えば、東欧では炭鉱と水脈とが並存し、水脈が岩塩
層を通るので、炭鉱から排出される水の塩濃度が30,000
〜80,000ppmと非常に高く、この含塩分水が河川、湖沼
等に流入するため、ある地域では深刻な環境汚染の原因
となっている。
For example, in Eastern Europe, a coal mine and a water vein coexist, and the water vein passes through a rock salt layer, so the salt concentration of water discharged from the coal mine is 30,000.
It is as high as ~ 80,000ppm, and this salt water flows into rivers, lakes and marshes, causing serious environmental pollution in some areas.

この問題を、2次汚染を起こさずに解決するために
は、含塩分水を河川、湖沼等に排出することなく、飲用
水又は工業用水と、塩分を高濃度に含む濃縮水又は固形
の塩とになるように完全に処理する必要がある。
In order to solve this problem without causing secondary pollution, drinking water or industrial water and concentrated water or solid salt containing a high concentration of salt without discharging salt-containing water to rivers, lakes, etc. Must be fully processed to be

この目的のために、従来から存在する蒸発法単独の適
用、単段逆浸透膜法と蒸発法との組合せの適用、電気透
析法と蒸発法との組合せの適用が考えられる。
For this purpose, the conventional evaporation method alone, the combination of the single-stage reverse osmosis membrane method and the evaporation method, and the combination of the electrodialysis method and the evaporation method can be considered.

一方、特開昭55−31459号公報には、海水から淡水を
得るために、海水を高圧用逆浸透膜モジュールに通し、
脱塩水を低圧用逆浸透膜モジュールに供給する装置が記
載されている。ちなみに、海水の塩濃度は35,000ppm前
後である。
On the other hand, in JP-A-55-31459, in order to obtain fresh water from seawater, seawater is passed through a high pressure reverse osmosis membrane module,
An apparatus for supplying demineralized water to a low pressure reverse osmosis membrane module is described. By the way, the salt concentration of seawater is around 35,000ppm.

また、実開昭58−108195号公報には、1基のベッセル
内に、脱塩率の小さい逆浸透膜モジュールと、脱塩率の
大きい逆浸透膜モジュールとを、脱塩率の大きいモジュ
ールが後流になるように直列に接続した装置が記載され
ている。
Further, Japanese Utility Model Application Laid-Open No. 58-108195 discloses a reverse osmosis membrane module having a small desalination rate and a reverse osmosis membrane module having a large desalination rate in one vessel. Devices are described which are connected in series in a downstream manner.

〔発明が解決しようとする課題〕[Problems to be Solved by the Invention]

蒸発法のみを適用する場合は、飲料水はすべて蒸発・
凝縮によって得ることになり、エネルギー消費が大とな
る(蒸発法では、相の変化を伴うため、逆浸透膜等によ
る造水法に比べ、エネルギーコストが大である)。
If only the evaporation method is applied, all drinking water will
It will be obtained by condensation, and energy consumption will be large (the evaporation method involves a phase change, so the energy cost is higher than that of the water production method using a reverse osmosis membrane or the like).

単段逆浸透膜法と蒸発法とを組み合わせて適用する場
合は、蒸発法に比べてかなりのエネルギー低減が可能で
あるが、単段の逆浸透膜では濃縮の程度が低く、かなり
の水を蒸発させる必要があるので、エネルギー使用量の
低減は十分ではない。
When the single-stage reverse osmosis membrane method and the evaporation method are applied in combination, a considerable reduction in energy is possible compared to the evaporation method, but the single-stage reverse osmosis membrane has a low degree of concentration and requires a considerable amount of water. The reduction in energy usage is not sufficient as it needs to be evaporated.

また、逆浸透膜への供給水の塩濃度が60,000ppmを越
えると、一般の海水淡水化用逆浸透膜は、浸透圧の関係
で用いることができない(圧力が高くなりすぎるか
ら)。一方、低圧用逆浸透膜では飲料水レベルの脱塩水
を得ることができない。
Further, when the salt concentration of the water supplied to the reverse osmosis membrane exceeds 60,000 ppm, the general reverse osmosis membrane for seawater desalination cannot be used due to the osmotic pressure (because the pressure becomes too high). On the other hand, low-pressure reverse osmosis membranes cannot obtain drinking water-level demineralized water.

電気透析法と蒸発法とを組み合わせて適用する場合に
おいては、電気透析法は一般に塩濃度が高くなると、エ
ネルギー消費が大となる。また、電気透析法を濃縮の目
的で用いることもできるが、この場合、電気透析装置の
脱塩側から大量の中塩濃度の排水が出るので、好ましく
ない。
When the electrodialysis method and the evaporation method are applied in combination, the electrodialysis method generally consumes a large amount of energy when the salt concentration is high. Further, the electrodialysis method can be used for the purpose of concentration, but in this case, a large amount of waste water having a medium salt concentration is discharged from the desalting side of the electrodialysis device, which is not preferable.

また、特開昭55−31459号公報記載の方式は、海水か
ら淡水を得るのが主目的であり、濃縮水の濃縮程度は、
本発明における濃縮程度より低く、しかも、濃縮水は投
棄されている さらに、実開昭58−108195号公報記載の方式は、所定
の圧力に加圧した塩水を順次、複数の膜モジュールに通
過させて行くもので、2段目の低圧用膜モジュールに供
給する中濃度濃縮水を減圧したり、2段目の高圧用膜モ
ジュールに供給する粗脱塩水を昇圧したりする技術的思
想は、何も記載されていない。
In addition, the method described in JP-A-55-31459 has the main purpose of obtaining fresh water from seawater, and the degree of concentration of concentrated water is
The concentration is lower than the concentration in the present invention, and the concentrated water is discarded. Further, in the method described in Japanese Utility Model Publication No. 58-108195, salt water pressurized to a predetermined pressure is sequentially passed through a plurality of membrane modules. What is the technical idea of reducing the pressure of the medium-concentrated concentrated water supplied to the second-stage low-pressure membrane module or increasing the pressure of the crude demineralized water supplied to the second-stage high-pressure membrane module? Is also not listed.

本発明は上記の諸点に鑑みなされたもので、多段の逆
浸透膜モジュールにより含塩分水を処理するか、又は多
段の逆浸透膜モジュールと蒸発装置とを組み合わせるこ
とにより、エネルギー消費を低減し、効率的な処理を可
能にした含塩分水の処理方法及び装置を提供することを
目的とするものである。
The present invention has been made in view of the above points, by treating salt-containing water with a multi-stage reverse osmosis membrane module, or by combining a multi-stage reverse osmosis membrane module and an evaporator, to reduce energy consumption, It is an object of the present invention to provide a method and an apparatus for treating salt-containing water that enables efficient treatment.

〔課題を解決するための手段及び作用〕[Means and Actions for Solving the Problems]

上記の目的を達成するために、請求項1記載の含塩分
水の処理方法は、第1図に示すように、塩濃度50,000〜
80,000ppmの比較的高濃度の含塩分水を30〜70kg/cm2Gで
低圧用逆浸透膜モジュール20に通して、粗脱塩水と塩濃
度80,000〜120,000ppmの高濃度濃縮水とに分離し、つい
で、この粗脱塩水を40〜70kg/cm2に加圧し、高圧用逆浸
透膜モジュール22に通して、飲料水レベルの脱塩水と中
濃度濃縮水とに分離することを特徴としている。
In order to achieve the above object, the method for treating salt-containing water according to claim 1 is, as shown in FIG.
80,000 ppm relatively high concentration salt water is passed through low pressure reverse osmosis membrane module 20 at 30-70 kg / cm 2 G to separate into crude demineralized water and high concentration concentrated water with salt concentration of 80,000-120,000 ppm. Then, this crude demineralized water is pressurized to 40 to 70 kg / cm 2 and passed through a high pressure reverse osmosis membrane module 22 to separate into drinking water level demineralized water and medium concentration concentrated water.

そして、請求項1の方法において、高圧用逆浸透膜モ
ジュール22からの中濃度濃縮水は、低圧用逆浸透膜モジ
ュール20に供給される(請求項2)。
Then, in the method of claim 1, the medium-concentrated concentrated water from the high-pressure reverse osmosis membrane module 22 is supplied to the low-pressure reverse osmosis membrane module 20 (claim 2).

請求項4の含塩分水の処理装置は、第1図に示すよう
に、塩濃度50,000〜80,000ppmの比較的高濃度の含塩分
水を30〜70kg/cm2Gで導入し、粗脱塩水と塩濃度80,000
〜120,000ppmの高濃度濃縮水とに分離する低圧用逆浸透
モジュール20と、 この粗脱塩水を40〜70kg/cm2Gに加圧するための加圧
ポンプ24と、 加圧された含塩分水を導入し、飲料水レベルの脱塩水
と中濃度濃縮水とに分離する高圧用逆浸透膜モジュール
22とを包含することを特徴としている。26は減圧手段で
ある。
As shown in FIG. 1, the apparatus for treating salt-containing water according to claim 4 introduces a relatively high-concentration salt-containing water having a salt concentration of 50,000 to 80,000 ppm at 30 to 70 kg / cm 2 G to obtain crude desalinated water. And salt concentration 80,000
Reverse pressure osmosis module 20 for low pressure that separates to highly concentrated water of ~ 120,000 ppm, pressurizing pump 24 to pressurize this crude demineralized water to 40 to 70 kg / cm 2 G, and pressurized salt-containing water High pressure reverse osmosis membrane module that introduces water and separates it into demineralized water at the level of drinking water and concentrated water
It is characterized by including 22 and. 26 is a decompression means.

前記の請求項1又は2の方法において、低圧用逆浸透
膜モジュール20からの塩濃度80,000〜120,000ppmの高濃
度濃縮水は、蒸発工程に送られ、塩を結晶として得るよ
うに構成するのが望ましい。
The method according to claim 1 or 2, wherein the high-concentration concentrated water having a salt concentration of 80,000 to 120,000 ppm from the low-pressure reverse osmosis membrane module 20 is sent to the evaporation step to obtain the salt as crystals. desirable.

第1図に示す方式において、高圧用逆浸透膜モジュー
ル22からの中濃度濃縮水の塩分は40,000〜70,000ppm
で、この膜モジュール22からの飲料水レベルの脱塩水の
塩分は1,000ppm以下、望ましくは500ppm以下である。
In the system shown in FIG. 1, the salinity of the medium concentration concentrated water from the high pressure reverse osmosis membrane module 22 is 40,000 to 70,000 ppm.
Then, the salinity of the demineralized water at the drinking water level from the membrane module 22 is 1,000 ppm or less, preferably 500 ppm or less.

高圧用逆浸透膜モジュールとは、脱塩率が約99%以上
のもので、一般に、40〜70kg/cm2G、望ましくは50kg/cm
2G以上の高圧下で使用される膜モジュールを指称する。
Reverse osmosis membrane module for high pressure has a desalination rate of about 99% or more, and generally 40 to 70 kg / cm 2 G, preferably 50 kg / cm
Refers to a membrane module used under high pressure of 2 G or more.

一方、低圧用膜モジュールとは、脱塩率が高濃度(5,
000ppm以上)で90%以下のもので、一般に、5,000ppm以
下の塩濃度では、10〜40kg/cm2G、望ましくは30kg/cm2G
以下の低圧下で使用される膜モジュールを指称する。
On the other hand, the low-pressure membrane module has a high desalination ratio (5,
But 90% or less than 000 ppm), generally, in the following salt concentration 5,000ppm, 10~40kg / cm 2 G, preferably 30kg / cm 2 G
The following refers to a membrane module used under low pressure.

両方の膜モジュールとも、中空糸形、スパイラル形、
管形、プリーツ形、平板形等の形式を有し、材質として
は、酢酸セルロース等の高分子材料が用いられる。特
に、低圧膜モジュールでは、合成高分子複合膜が普及し
ている。
Both membrane modules are hollow fiber type, spiral type,
It has a tubular shape, a pleat shape, a flat plate shape, or the like, and as a material thereof, a polymer material such as cellulose acetate is used. In particular, in a low pressure membrane module, a synthetic polymer composite membrane has been widely used.

低圧膜は、一般に、低濃度塩水(5,000ppm以下程度)
の脱塩に用いられる。本発明では、低圧膜の脱塩率が低
いという特性を利用して、塩濃度50,000〜80,000ppm程
度の比較的高濃度の含塩分水を、30〜70kg/cm2程度の圧
力で処理するものである。
Low-pressure membranes are generally low-concentration salt water (about 5,000 ppm or less)
Used for desalting. In the present invention, by utilizing the characteristic that the low-pressure membrane has a low desalination rate, a relatively high concentration of salt-containing water having a salt concentration of about 50,000-80,000 ppm is treated at a pressure of about 30-70 kg / cm 2. Is.

また、減圧手段26としては、減圧弁、制限オリフィス
等が用いられる。
Further, as the pressure reducing means 26 , a pressure reducing valve, a restriction orifice, or the like is used.

〔実施例〕〔Example〕

以下、本発明の実施例について説明する。 Examples of the present invention will be described below.

実施例1 本例は、流量5,000T/D、塩濃度70,000ppmの含塩分水
を、第2図に示すような、2段逆浸透膜法と蒸発法との
組合せ方式により処理する場合を示している。
Example 1 This example shows the case of treating salt-containing water having a flow rate of 5,000 T / D and a salt concentration of 70,000 ppm by a combined method of a two-stage reverse osmosis membrane method and an evaporation method as shown in FIG. ing.

含塩分水は、まず、前処理装置23に導入され、固形
分、及び含塩分水中に微量に含まれる鉄分、マンガン分
が除去され、さらに、Ca分を除去し、pHを約6.5に調整
した後(処理前のpHは約7.5)、約60kg/cm2Gに加圧され
て、第1段目の低圧用逆浸透膜モジュール20に供給され
る。
Salt-containing water is first introduced into the pretreatment device 23, the solid content, and iron contained in a trace amount in the salt-containing water, manganese is removed, further, Ca is removed, the pH was adjusted to about 6.5. After that (pH before treatment is about 7.5), it is pressurized to about 60 kg / cm 2 G and supplied to the first-stage low pressure reverse osmosis membrane module 20.

第1段目の膜モジュール20には、低操作圧、低塩排除
率の特性を持つ合成複合膜が用いられており、供給水の
約50%は低圧膜を透過し、塩濃度27,000ppm程度の脱塩
水となり、残りの約50%は塩濃度110,000ppmまで濃縮さ
れ、次の蒸発装置25(例えば、多重効用蒸発装置)への
供給水となる。
The first-stage membrane module 20 uses a synthetic composite membrane with the characteristics of low operating pressure and low salt rejection. About 50% of the feed water permeates the low-pressure membrane, and the salt concentration is about 27,000 ppm. Demineralized water, and the remaining about 50% is concentrated to a salt concentration of 110,000 ppm, and is supplied to the next evaporator 25 (for example, a multi-effect evaporator).

第1段目の低圧用逆浸透膜モジュール20の脱塩水は、
約65kg/cm2Gに加圧された後、一般的な海水淡水化用逆
浸透膜を用いた第2段目の高圧用逆浸透膜モジュール22
へ供給される。供給水の約50%は高圧膜を透過し、塩濃
度500ppm以下の飲料水レベルの脱塩水1,670T/Dが得られ
る。残りの約50%は、塩濃度54,000ppmまで濃縮され
る。この濃縮水は、第1段目の低圧用逆浸透膜モジュー
ル20の供給側へ返送され、前処理済の含塩分水と合流
し、第1段目の低圧用逆浸透膜モジュール20で処理され
る。27は苦汁(にがり)処理装置、29は生成水貯槽であ
る。
The demineralized water of the first-stage low pressure reverse osmosis membrane module 20 is
After being pressurized to approximately 65 kg / cm 2 G, the second-stage high-pressure reverse osmosis membrane module using a general seawater desalination reverse osmosis membrane 22
Supplied to About 50% of the feed water passes through the high-pressure membrane, and drinking water level demineralized water of 1,670 T / D with a salt concentration of 500 ppm or less is obtained. The remaining about 50% is concentrated to a salt concentration of 54,000 ppm. This concentrated water is returned to the supply side of the first-stage low pressure reverse osmosis membrane module 20, merges with the pretreated salt-containing water, and is treated by the first-stage low pressure reverse osmosis membrane module 20. It 27 is a bitter soup treatment device, and 29 is a produced water storage tank.

〔発明の効果〕〔The invention's effect〕

本発明は上記のように構成されているので、次のよう
な効果を奏する。
Since the present invention is configured as described above, it has the following effects.

(1)含塩分水を処理して、飲料水レベルの脱塩水と、
塩濃度80,000〜120,000ppmの高濃度濃縮水とに分離する
ことができるので、この高濃度濃縮水を蒸発工程で処理
する場合には、塩を結晶として得ることができる。ま
た、エネルギー消費量の低減を図ることができる。
(1) Treatment of salt-containing water to obtain drinking water-level demineralized water,
Since it can be separated into high-concentration concentrated water having a salt concentration of 80,000 to 120,000 ppm, the salt can be obtained as crystals when the high-concentration concentrated water is treated in the evaporation step. In addition, energy consumption can be reduced.

(2)従来の蒸発法、1段逆浸透膜法+蒸発法と、本発
明の方法のうち、塩濃度70,000ppmの比較的高濃度の含
塩分水を透過処理した後、蒸発処理する方法(第2図に
示す方法)との造水比率を比較すると、第1表の如くに
なる。第1表から、本発明の方法(第2図に示す方法)
の造水比率が大きいことがわかる。
(2) Conventional evaporation method, one-step reverse osmosis membrane method + evaporation method, and among the methods of the present invention, a method of permeating a relatively high-concentration salt-containing water having a salt concentration of 70,000 ppm, and then performing an evaporation treatment ( Table 1 shows a comparison of the desalination ratio with the method shown in FIG. From Table 1, the method of the present invention (method shown in FIG. 2)
It can be seen that the water production ratio is high.

(3)造水のためのエネルギーコストを、蒸発法の場合
25kwh/m3、逆浸透膜法の場合7kwh/m3(造水促進センタ
ー資料による)として、前記(2)の第2図に示す本発
明の方法について計算した結果から、2.5割程度のエネ
ルギーコスト低減が可能であることがわかる。
(3) In case of evaporation method, energy cost for water production
25kwh / m 3, as the case of the reverse osmosis membrane method 7 kWh / m 3 (according to desalination Promotion Center article), the results calculated for the method of the present invention shown in FIG. 2 (2), 2.5 percent about energy It can be seen that the cost can be reduced.

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

第1図は本発明の含塩分水の処理方法を実施する装置の
一例を示す系統的説明図、第2図は比較的高濃度(70,0
00ppm)の含塩分水を処理する場合(実施例1)を示す
系統的説明図である。22 ……高圧用逆浸透膜モジュール、20……低圧用逆浸透
膜モジュール、23……前処理装置、24……高圧ポンプ、
25……蒸発装置、26……減圧手段、27……苦汁処理装
置、29……生成水貯槽
FIG. 1 is a systematic explanatory view showing an example of an apparatus for carrying out the method for treating salt-containing water of the present invention, and FIG. 2 is a comparatively high concentration (70,0
It is a systematic explanatory view showing the case (Example 1) of treating salt-containing water of (00 ppm). 22 …… High pressure reverse osmosis membrane module, 20 …… Low pressure reverse osmosis membrane module, 23 …… Pretreatment device, 24 …… High pressure pump,
25 …… Evaporator, 26 …… Decompression means, 27 …… Bitter juice treatment device, 29 …… Generated water storage tank

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】塩濃度50,000〜80,000ppmの比較的高濃度
の含塩分水を30〜70kg/cm2Gで低圧用逆浸透膜モジュー
ル(20)に通して、粗脱塩水と塩濃度80,000〜120,000p
pmの高濃度濃縮水とに分離し、ついで、この粗脱塩水を
40〜70kg/cm2に加圧し、高圧用逆浸透膜モジュール(2
2)に通して、飲料水レベルの脱塩水と中濃度濃縮水と
に分離することを特徴とする含塩分水の処理方法。
1. A relatively high-concentration salt-containing water having a salt concentration of 50,000-80,000 ppm is passed through a reverse pressure osmosis membrane module (20) for low pressure at 30-70 kg / cm 2 G to obtain crude demineralized water and a salt concentration of 80,000- 120,000p
pm high-concentration concentrated water and then separate this crude demineralized water
40~70kg / cm 2 pressurized, the reverse osmosis membrane module for high pressure (2
A method for treating salt-containing water, characterized in that it is separated into demineralized water at a drinking water level and concentrated concentrated water through 2).
【請求項2】高圧用逆浸透膜モジュール(22)からの中
濃度濃縮水を、低圧用逆浸透膜モジュール(20)に供給
することを特徴とする請求項1記載の含塩分水の処理方
法。
2. The method for treating salt-containing split water according to claim 1, wherein the concentrated concentrated water from the high pressure reverse osmosis membrane module (22) is supplied to the low pressure reverse osmosis membrane module (20). .
【請求項3】低圧用逆浸透膜モジュール(20)からの塩
濃度80,000〜120,000ppmの高濃度濃縮水を蒸発工程に送
り、塩を結晶として得ることを特徴とする請求項1又は
2記載の含塩分水の処理方法。
3. The high-concentration concentrated water having a salt concentration of 80,000 to 120,000 ppm from the low-pressure reverse osmosis membrane module (20) is sent to the evaporation step to obtain the salt as crystals. Method of treating salt-containing water.
【請求項4】塩濃度50,000〜80,000ppmの比較的高濃度
の含塩分水を30〜70kg/cm2Gで導入し、粗脱塩水と塩濃
度80,000〜120,000ppmの高濃度濃縮水とに分離する低圧
用逆浸透モジュール(20)と、 この粗脱塩水を40〜70kg/cm2Gに加圧するための加圧ポ
ンプ(24)と、 加圧された含塩分水を導入し、飲料水レベルの脱塩水と
中濃度濃縮水とに分離する高圧用逆浸透膜モジュール
(22)とを包含することを特徴とする含塩分水の処理装
置。
4. A relatively high-concentration salt-containing water having a salt concentration of 50,000-80,000 ppm is introduced at 30-70 kg / cm 2 G and separated into crude demineralized water and high-concentration concentrated water having a salt concentration of 80,000-120,000 ppm. Low pressure reverse osmosis module (20), pressurizing pump (24) to pressurize this crude demineralized water to 40 to 70 kg / cm 2 G, and pressurizing salt water An apparatus for treating salt-containing water, comprising: a high-pressure reverse osmosis membrane module (22) for separating into demineralized water and concentrated water of medium concentration.
JP2168097A 1990-06-25 1990-06-25 Method and apparatus for treating salt-containing water Expired - Fee Related JPH0822434B2 (en)

Priority Applications (5)

Application Number Priority Date Filing Date Title
JP2168097A JPH0822434B2 (en) 1990-06-25 1990-06-25 Method and apparatus for treating salt-containing water
US07/719,507 US5238574A (en) 1990-06-25 1991-06-24 Method and apparatus having reverse osmosis membrane for concentrating solution
DE69123644T DE69123644T2 (en) 1990-06-25 1991-06-25 Method and device with a reverse osmosis membrane for concentrating a solution
EP91110447A EP0463605B1 (en) 1990-06-25 1991-06-25 Method and apparatus having reverse osmosis membrane for concentrating solution
PL91290803A PL173335B1 (en) 1990-06-25 1991-06-25 Method of and apparatus for increasing concentration of solutions

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2168097A JPH0822434B2 (en) 1990-06-25 1990-06-25 Method and apparatus for treating salt-containing water

Publications (2)

Publication Number Publication Date
JPH0461983A JPH0461983A (en) 1992-02-27
JPH0822434B2 true JPH0822434B2 (en) 1996-03-06

Family

ID=15861786

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2168097A Expired - Fee Related JPH0822434B2 (en) 1990-06-25 1990-06-25 Method and apparatus for treating salt-containing water

Country Status (1)

Country Link
JP (1) JPH0822434B2 (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0588693U (en) * 1992-05-19 1993-12-03 三菱重工業株式会社 Waste liquid boric acid processor
JP3593765B2 (en) * 1994-12-02 2004-11-24 東レ株式会社 Reverse osmosis membrane separation apparatus and method for seawater
JP2001269544A (en) * 1994-12-02 2001-10-02 Toray Ind Inc Membrane separation device and method for separating high concentration solution
JP2001269543A (en) * 1994-12-02 2001-10-02 Toray Ind Inc Membrane separation device and method for separating high concentration solution
US7144511B2 (en) * 2002-05-02 2006-12-05 City Of Long Beach Two stage nanofiltration seawater desalination system
TW200420506A (en) * 2003-02-14 2004-10-16 Dainichiseika Color Chem Method of desalting
JP4996068B2 (en) * 2005-06-24 2012-08-08 株式会社ササクラ Waste water concentration method and apparatus
JP2013167156A (en) * 2010-05-28 2013-08-29 Nitto Denko Corp Fluid membrane separation power generation system
AU2010357341B2 (en) * 2010-07-12 2014-06-05 Hitachi, Ltd. Associated-water concentration system and associated-water concentration method
WO2019180789A1 (en) * 2018-03-19 2019-09-26 三菱重工エンジニアリング株式会社 Water treatment device and water treatment method

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS55109406A (en) * 1979-02-14 1980-08-22 Toray Ind Inc Liquid separating system

Also Published As

Publication number Publication date
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