Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JP6414528B2 - Water desalination method and apparatus - Google Patents
[go: Go Back, main page]

JP6414528B2 - Water desalination method and apparatus - Google Patents

Water desalination method and apparatus Download PDF

Info

Publication number
JP6414528B2
JP6414528B2 JP2015184887A JP2015184887A JP6414528B2 JP 6414528 B2 JP6414528 B2 JP 6414528B2 JP 2015184887 A JP2015184887 A JP 2015184887A JP 2015184887 A JP2015184887 A JP 2015184887A JP 6414528 B2 JP6414528 B2 JP 6414528B2
Authority
JP
Japan
Prior art keywords
solution
temperature
water
flow rate
attracting
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
JP2015184887A
Other languages
Japanese (ja)
Other versions
JP2017056424A (en
Inventor
渕上 浩司
浩司 渕上
戸村 啓二
啓二 戸村
藤原 茂樹
茂樹 藤原
亮 功刀
亮 功刀
彩 加藤
彩 加藤
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.)
JFE Engineering Corp
Original Assignee
JFE Engineering Corp
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 JFE Engineering Corp filed Critical JFE Engineering Corp
Priority to JP2015184887A priority Critical patent/JP6414528B2/en
Publication of JP2017056424A publication Critical patent/JP2017056424A/en
Application granted granted Critical
Publication of JP6414528B2 publication Critical patent/JP6414528B2/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

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
    • Y02A20/131Reverse-osmosis

Landscapes

  • Separation Using Semi-Permeable Membranes (AREA)

Description

この発明は、例えば海水を半透膜を用い淡水を製造する方法と装置に関するものである。   The present invention relates to a method and apparatus for producing fresh water, for example, seawater using a semipermeable membrane.

海水を半透膜を用いて淡水化する方法は種々知られているが、海水に浸透圧以上の圧力を加えて水を強制的に半透膜を透過させる逆浸透法が主に開発されてきた。この方法は高圧に加圧する必要があるため、設備費および運転費にコストがかかるという問題点がある。一方、半透膜を介して海水より高濃度の塩溶液を存在させれば、加圧せずとも浸透圧で水をこの塩溶液に移動させることができる。そして、この塩溶液として揮発性ガスを溶解させた溶液を用いれば、この塩溶液を蒸留することにより揮発性ガスを蒸発、分離させて淡水を得ることができる。この揮発性ガスとしてアンモニアと二酸化炭素の組合せを用いた方法が既に開発されている(特許文献1)。   Various methods for desalinating seawater using a semipermeable membrane are known, but the reverse osmosis method that forcibly permeates water through a semipermeable membrane by applying a pressure higher than the osmotic pressure to seawater has been mainly developed. It was. Since this method requires pressurization to a high pressure, there is a problem that the equipment cost and operation cost are high. On the other hand, if a salt solution having a higher concentration than seawater is present through the semipermeable membrane, water can be transferred to the salt solution by osmotic pressure without applying pressure. If a solution in which a volatile gas is dissolved is used as the salt solution, fresh water can be obtained by evaporating and separating the volatile gas by distilling the salt solution. A method using a combination of ammonia and carbon dioxide as the volatile gas has already been developed (Patent Document 1).

特許文献1の方法は、半透膜を介して海水と反対側にアンモニアと二酸化炭素を溶解して得られる塩溶液を流して、海水中の水を半透膜を通過させて該塩溶液に移動させ、得られた希釈塩溶液を蒸留塔に送って淡水を得るとともにアンモニアと二酸化炭素と水を含む混合ガスを分離し、この混合ガスを冷却し、塩溶液に再生した後、半透膜の元の部屋に返送する方法である。   In the method of Patent Document 1, a salt solution obtained by dissolving ammonia and carbon dioxide is passed through a semipermeable membrane on the side opposite to seawater, and water in the seawater is passed through the semipermeable membrane into the salt solution. The resulting diluted salt solution is sent to a distillation tower to obtain fresh water, and a mixed gas containing ammonia, carbon dioxide and water is separated, the mixed gas is cooled and regenerated into a salt solution, and then a semipermeable membrane. It is a method of returning to the original room.

この方法に用いられる装置は、図3に示すように、海水供給ポンプ22、正浸透(FO)膜モジュール24、ポンプ28、誘引溶液分離手段32、淡水分離手段36、コンプレッサー42、誘引溶液再生手段44からなっている。海水供給ポンプ22によって供給された海水は、FO膜モジュール24に入り、FO膜を介して誘引溶液と向流接触する。そして、その間に浸透圧によって海水中の水分がFO膜を通過して誘引溶液に移動し、それによって濃縮された濃縮海水は流路26からFO膜モジュール24を出る。一方、海水からの水分の移動によって希釈された希釈誘引溶液はFO膜モジュール24を出て誘引溶液分離手段32に入る。誘引溶液分離手段32では、誘引溶液が加熱されて炭酸アンモニウムがアンモニアと二酸化炭素に分解され、発生したアンモニアと二酸化炭素は、ガス流路40を通ってコンプレッサー42で圧縮されて誘引溶液再生手段44に入る。一方、誘引溶液分離手段32でアンモニアと二酸化炭素が分解されて残った水は、流路34を通って淡水分離手段36に送られ、その一部は流路46を通り、誘引溶液再生手段44で再生される誘引溶液の水分として利用される。残りの水は淡水として流路38から取り出される。誘引溶液再生手段44で再生された誘引溶液は、ポンプ28により流路30を通ってFO膜モジュール24に返送される。   As shown in FIG. 3, the apparatus used in this method includes a seawater supply pump 22, a forward osmosis (FO) membrane module 24, a pump 28, an attraction solution separation means 32, a fresh water separation means 36, a compressor 42, an attraction solution regeneration means. 44. Seawater supplied by the seawater supply pump 22 enters the FO membrane module 24 and makes countercurrent contact with the attracting solution through the FO membrane. In the meantime, due to osmotic pressure, water in the seawater passes through the FO membrane and moves to the attracting solution, and the concentrated seawater concentrated thereby exits the FO membrane module 24 from the flow path 26. On the other hand, the diluted attraction solution diluted by the movement of water from the seawater leaves the FO membrane module 24 and enters the attraction solution separating means 32. In the attracting solution separating means 32, the attracting solution is heated to decompose ammonium carbonate into ammonia and carbon dioxide, and the generated ammonia and carbon dioxide are compressed by the compressor 42 through the gas flow path 40 and attracted solution regenerating means 44. to go into. On the other hand, the water remaining after the ammonia and carbon dioxide are decomposed by the attracting solution separating means 32 is sent to the fresh water separating means 36 through the flow path 34, and part of the water passes through the flow path 46 and is attracted solution regenerating means 44. It is used as the moisture of the attracting solution regenerated in The remaining water is taken out from the flow path 38 as fresh water. The attraction solution regenerated by the attraction solution regeneration means 44 is returned to the FO membrane module 24 through the flow path 30 by the pump 28.

一方、この誘引溶液に、温度感応性薬剤である下限臨界温度を有する感応性物質を用いたものも知られている(特許文献2)。この温度感応性物質は、アルコールまたは脂肪酸とエチレンオキサイドの化合物などである。   On the other hand, what uses the sensitive substance which has the lower critical temperature which is a temperature sensitive chemical | medical agent for this attraction solution is also known (patent document 2). This temperature sensitive substance is a compound of alcohol or fatty acid and ethylene oxide.

さらに、誘引溶液に硫酸マグネシウム等の無機塩を浸透圧を高めるための浸透圧剤として用い、これにポリエチレンオキサイドとポリプロピレンオキサイドの共重合体などの温度感応性薬剤を組み合わせた方法も開発されている(特許文献3)。この方法に用いられる装置は、図4に示すように、正浸透膜ユニット230、第1分離槽250、熱交換器256、第2分離槽253、精製装置261からなっている。海水210は、正浸透膜ユニット230に入って、FO膜212を介して浸透圧剤溶液240と向流接触する。そして、その間に浸透圧によって海水中の水分211がFO膜を通過して浸透圧剤溶液内に移動し、それによって濃縮された濃縮海水220が正浸透膜ユニット230から出る。一方、海水からの水分の移動によって希釈された希釈浸透圧剤溶液245は正浸透膜ユニット230を出て、第2分離槽253等から返送される温度感応性薬剤溶液260と混合され、希釈浸透圧剤245中の水が温度感応性薬剤溶液260に移動する。この混合液246が第1分離槽250に送られる。第1分離槽250では重力沈降により、浸透圧剤溶液240の相と温度感応性薬剤溶液252の相に分かれ、浸透圧剤溶液240は正浸透膜ユニット230に返送される。一方、希釈温度感応性薬剤溶液252は、熱交換器256に送られて温度感応性薬剤の曇点以上に加温され、第2分離槽253に送られる。第2分離槽253では重力沈降により粗製淡水257の相と温度感応性薬剤凝集液255の相に分かれ、粗製淡水257は、逆浸透膜262を備えた精製装置261で処理されて淡水258となる。一方、精製装置261で分離された温度感応性薬剤濃厚液259は、第2分離槽253で分離された温度感応性薬剤凝集液255と合流、冷却され、温度感応性薬剤溶液260に再生された後、正浸透膜ユニット230から流出した希釈浸透圧剤溶液245とともに第1分離槽250に返送される。   Furthermore, a method has been developed in which an inorganic salt such as magnesium sulfate is used as an osmotic pressure agent for increasing the osmotic pressure in the attracting solution, and a temperature sensitive agent such as a copolymer of polyethylene oxide and polypropylene oxide is combined with this. (Patent Document 3). As shown in FIG. 4, the apparatus used in this method includes a forward osmosis membrane unit 230, a first separation tank 250, a heat exchanger 256, a second separation tank 253, and a purification apparatus 261. The seawater 210 enters the forward osmosis membrane unit 230 and makes countercurrent contact with the osmotic agent solution 240 via the FO membrane 212. In the meantime, due to osmotic pressure, the moisture 211 in the seawater passes through the FO membrane and moves into the osmotic agent solution, and the concentrated seawater 220 concentrated thereby exits from the forward osmosis membrane unit 230. On the other hand, the diluted osmotic pressure agent solution 245 diluted by the movement of water from the seawater exits the forward osmosis membrane unit 230 and is mixed with the temperature sensitive drug solution 260 returned from the second separation tank 253 and the like, and diluted osmotic solution. The water in the pressure agent 245 moves to the temperature sensitive drug solution 260. This mixed liquid 246 is sent to the first separation tank 250. The first separation tank 250 is divided into a phase of the osmotic agent solution 240 and a phase of the temperature sensitive drug solution 252 by gravity sedimentation, and the osmotic agent solution 240 is returned to the forward osmosis membrane unit 230. On the other hand, the dilution temperature sensitive drug solution 252 is sent to the heat exchanger 256, heated above the cloud point of the temperature sensitive drug, and sent to the second separation tank 253. The second separation tank 253 is separated into a phase of crude fresh water 257 and a phase of a temperature-sensitive drug aggregation liquid 255 by gravity sedimentation, and the crude fresh water 257 is processed by a purification device 261 equipped with a reverse osmosis membrane 262 to become fresh water 258. . On the other hand, the temperature-sensitive drug concentrated liquid 259 separated by the purification device 261 is merged with the temperature-sensitive drug aggregation liquid 255 separated by the second separation tank 253, cooled, and regenerated into the temperature-sensitive drug solution 260. Then, the diluted osmotic pressure agent solution 245 flowing out from the forward osmosis membrane unit 230 is returned to the first separation tank 250.

米国特許第8,021,549B2号明細書US Patent No. 8,021,549B2 特開2014−100692号公報JP 2014-1000069 A2 米国特許第8,852,436B2号明細書US Pat. No. 8,852,436B2

ところが、このような装置の性能(水の膜透過速度:ろ過速度)は、FO膜モジュールに供給される被処理水、誘引溶液の濃度、流量、膜の状態(目詰まり等)によって変化するため、運転条件を最適に調整しないと、所望の造水量を得ることができない。   However, the performance of such an apparatus (water membrane permeation rate: filtration rate) varies depending on the water to be treated supplied to the FO membrane module, the concentration of the attracting solution, the flow rate, and the state of the membrane (clogging, etc.). Unless the operating conditions are adjusted optimally, a desired amount of fresh water cannot be obtained.

例えば、水質変動により被処理水の塩濃度が上昇すると、FO膜モジュール内で被処理水側の平均浸透圧が上昇し、誘引溶液供給量が一定の場合には膜ろ過の駆動力となる浸透圧差が低下して、水の膜透過速度(ろ過速度)が低下する。このような場合は、造水量は設定値より少なくなる。   For example, when the salt concentration of treated water increases due to water quality fluctuations, the average osmotic pressure on the treated water side increases in the FO membrane module, and the permeation serving as the driving force for membrane filtration when the amount of attracted solution supplied is constant. The pressure difference decreases, and the water membrane permeation rate (filtration rate) decreases. In such a case, the amount of fresh water is less than the set value.

本発明の目的は、このような課題を解決することにあり、FO膜モジュールに供給される被処理水、誘引溶液の濃度、流量、膜の状態(目詰まり等)の変化に応じて誘引溶液の流量を最適に調整する手段を提供することにある。   An object of the present invention is to solve such a problem, and an attracting solution according to changes in the water to be treated supplied to the FO membrane module, the concentration, flow rate, and membrane state (clogging, etc.) of the attracting solution. It is intended to provide a means for optimally adjusting the flow rate.

本発明者は、上記課題を解決するべく鋭意検討の結果、次のように考えた。   As a result of intensive studies to solve the above problems, the present inventor has considered as follows.

正浸透(FO)膜への誘引溶液(DS)供給量を流入量上昇によって増加させると、膜透過水によるDS希釈の抑制効果によって膜透過速度が即時に上昇する。しかし、この場合システムを循環するDS流量が増加するため、FO膜透過水によって希釈された希釈DSを相分離する沈殿槽滞留時間の縮小および浸透圧剤として使用される温度感応性薬剤を曇点以上に加温する熱交換器圧力損失の上昇といった現象が生じ、それぞれ分離効率の低下およびポンプ動力の増大といった問題が生ずる。そこでDS流入量による制御は滞留時間や圧力損失の変動が性能やコストに及ぼす影響の小さな偏差、例えば10%以内に制御し、それを越える場合にDS分離温度を変化させる。分離温度を上昇させるとFO膜に流入するDS濃度が上昇するため、DS流入量を増大させる場合と同様に膜透過速度が上昇する。但し、この効果は、分離温度の制御変更後、沈殿池内のDS温度が制御値に到達し、さらに分離後のDS濃度が定常値に達するまでの時間遅れが生じる。   When the amount of the attracting solution (DS) supplied to the forward osmosis (FO) membrane is increased by increasing the inflow rate, the membrane permeation rate immediately increases due to the effect of suppressing the DS dilution by the membrane permeated water. However, since the DS flow rate circulating in the system increases in this case, the sedimentation tank residence time for phase-separating the diluted DS diluted with FO membrane permeated water is reduced, and the temperature sensitive agent used as the osmotic agent is a cloud point. A phenomenon such as an increase in pressure loss of the heat exchanger that heats occurs as described above, causing problems such as a decrease in separation efficiency and an increase in pump power. Therefore, the control based on the DS inflow rate is controlled within a small deviation, for example, 10%, of the influence of the residence time and pressure loss on the performance and cost, and the DS separation temperature is changed when exceeding the deviation. When the separation temperature is increased, the DS concentration flowing into the FO membrane is increased, so that the membrane permeation rate is increased as in the case where the DS inflow amount is increased. However, this effect causes a time delay until the DS temperature in the sedimentation basin reaches the control value after the change in control of the separation temperature and the DS concentration after separation reaches a steady value.

そこで、造水量を膜前後のDS流量差により検知し、造水量低下時にはDS流入量を増加、上昇時には低減させる。DS流入量の設定値との偏差が、例えば10%以内である場合は前記操作を行い、10%を越える場合はDS流入量と併せてDS分離温度を変化させる方法および装置を案出した。   Therefore, the amount of water produced is detected by the difference in the DS flow rate before and after the membrane, and the amount of DS inflow is increased when the amount of fresh water is lowered, and is decreased when the amount of fresh water is raised. For example, when the deviation from the set value of the DS inflow amount is within 10%, the above operation is performed. When the deviation exceeds 10%, a method and apparatus for changing the DS separation temperature together with the DS inflow amount have been devised.

本発明は、このような知見に基づいてなされたものであり、
塩類を含有する被処理水と、浸透圧剤を水に溶解し前記被処理水よりも浸透圧の高い誘引溶液とを半透膜を介して接触させ、前記被処理水中の水を前記半透膜を通して前記誘引溶液に移動させ、水で希釈された希釈誘引溶液と膜濃縮水を得る正浸透工程と、
前記希釈誘引溶液を浸透圧剤を主体とする濃厚溶液相と、少量の浸透圧剤を含有する希薄溶液相とに相分離する相分離工程と、
前記相分離工程で分離された濃厚溶液を前記正浸透工程へ循環し、誘引溶液として再使用する循環工程と、
前記相分離工程で分離された希薄溶液から淡水を得る淡水回収工程を有する水の脱塩処理方法であって、
前記希釈誘引溶液と前記誘引溶液各々の流量を測定し、それらの流量差が予め設定された設定値よりも低い場合は、前記誘引溶液の流量を増加し、また、前記流量差が予め設定された設定値よりも高い場合は、前記誘引溶液の流量を減少させることを特徴とする水の脱塩処理方法と、
前記浸透圧剤が下限臨界温度を有する温度感応性薬剤であり、前記相分離工程が前記希釈誘引溶液を前記誘引溶液の曇点以上の温度まで加温する加温工程を有しており、かつ
前記希釈誘引溶液と前記誘引溶液の流量差が予め設定された設定値よりも低い場合に、前記誘引溶液の流量を増加するとともに、前記加温工程での加温温度を上昇させる、また、前記流量差が予め設定された設定値よりも高い場合に、前記誘引溶液の流量を減少させるとともに、前記加温工程での加温温度を低下させることを特徴とする上記の水の脱塩処理方法と、
前記浸透圧剤が無機塩であり、前記相分離工程の前段で前記希釈誘引溶液に下限臨界温度を有する温度感応性薬剤を混合する温度感応性薬剤混合工程を有するとともに、前記相分離工程で分離された希薄溶液から淡水を得る淡水回収工程が、前記希薄溶液を前記誘引溶液の曇点以上の温度まで加温する加温工程と、前記加温工程に続き温度感応性薬剤を主体とする温度感応性薬剤溶液相と、淡水を主体とし少量の温度感応性薬剤を含有する淡水相とに相分離する第2相分離工程を有しており、
かつ、前記希釈誘引溶液と前記誘引溶液の流量差が予め設定された設定値よりも低い場合に、前記誘引溶液の流量を増加するとともに、前記加温工程での加温温度を上昇させる、また、前記流量差が予め設定された設定値よりも高い場合に、前記誘引溶液の流量を減少させるとともに、前記加温工程での加温温度を低下させることを特徴とする上記の水の脱塩処理方法と、
これらの方法に係る装置を提供するものである。
The present invention has been made based on such knowledge,
A treated water containing salts and an attracting solution having an osmotic agent dissolved in water and having a higher osmotic pressure than the treated water are brought into contact with each other through a semipermeable membrane, and the water in the treated water is brought into contact with the semipermeable material. Forward osmosis step of transferring to the attraction solution through a membrane to obtain a diluted attraction solution diluted with water and membrane concentrated water;
A phase separation step of phase-separating the diluted attraction solution into a concentrated solution phase mainly composed of an osmotic agent and a dilute solution phase containing a small amount of an osmotic agent;
Circulating the concentrated solution separated in the phase separation step to the forward osmosis step and reusing it as an attracting solution;
A method for desalinating water having a fresh water recovery step for obtaining fresh water from the dilute solution separated in the phase separation step,
When the flow rate of each of the diluted attractant solution and the attractant solution is measured and the flow rate difference between them is lower than a preset value, the flow rate of the attractant solution is increased, and the flow rate difference is preset. If higher than the set value, the water desalting method characterized by reducing the flow rate of the attracting solution;
The osmotic agent is a temperature sensitive agent having a lower critical temperature, and the phase separation step has a heating step of heating the dilution attraction solution to a temperature above the cloud point of the attraction solution; and When the flow rate difference between the diluted attracting solution and the attracting solution is lower than a preset value, the flow rate of the attracting solution is increased and the heating temperature in the warming step is increased. When the flow rate difference is higher than a preset set value, the flow rate of the attracting solution is decreased, and the heating temperature in the heating step is decreased. When,
The osmotic agent is an inorganic salt, and has a temperature sensitive drug mixing step in which a temperature sensitive drug having a lower critical temperature is mixed with the dilution attraction solution before the phase separation step, and is separated in the phase separation step. A fresh water recovery step for obtaining fresh water from the diluted solution is a heating step for heating the diluted solution to a temperature equal to or higher than the cloud point of the attracting solution, and a temperature mainly comprising a temperature-sensitive drug following the heating step. Having a second phase separation step of phase separation into a sensitive drug solution phase and a fresh water phase mainly containing fresh water and containing a small amount of temperature sensitive drug;
And when the flow rate difference between the diluted attracting solution and the attracting solution is lower than a preset value, the flow rate of the attracting solution is increased and the heating temperature in the warming step is increased. When the flow rate difference is higher than a preset value, the water desalting is characterized in that the flow rate of the attracting solution is decreased and the heating temperature in the heating step is decreased. Processing method,
An apparatus according to these methods is provided.

本発明により、FO膜モジュールに供給される被処理水や誘引溶液の濃度、流量、膜の状態等応じて誘引溶液の流量、さらには相分離工程における加温温度を調整して、水の脱塩処理装置の安定した運転を行うことができる。   According to the present invention, the concentration of the water to be treated and the attracting solution supplied to the FO membrane module, the flow rate, the flow rate of the attracting solution, and the heating temperature in the phase separation step are adjusted according to the state of the membrane. A stable operation of the salt treatment apparatus can be performed.

本発明の装置の構成の一例を示すブロック図である。It is a block diagram which shows an example of a structure of the apparatus of this invention. 本発明の別の装置の構成の一例を示すブロック図である。It is a block diagram which shows an example of a structure of another apparatus of this invention. 従来の装置の構成の一例を示すブロック図である。It is a block diagram which shows an example of a structure of the conventional apparatus. 従来の別の装置の構成の一例を示すブロック図である。It is a block diagram which shows an example of a structure of another conventional apparatus.

本発明の水の脱塩処理方法は、正浸透工程と相分離工程と循環工程と淡水回収工程よりなっている。   The water desalination method of the present invention comprises a forward osmosis step, a phase separation step, a circulation step, and a fresh water recovery step.

正浸透工程
正浸透工程では、塩類を含有する被処理水と、浸透圧剤を水に溶解し前記被処理水よりも浸透圧の高い誘引溶液とを半透膜を介して接触させ、前記被処理水中の水を前記半透膜を通して前記誘引溶液に移動させ、水で希釈された希釈誘引溶液と膜濃縮水を得る。
Forward osmosis step In the forward osmosis step, the water to be treated containing salts is brought into contact with an attracting solution having an osmotic agent dissolved in water and having a higher osmotic pressure than the water to be treated through a semipermeable membrane. Water in the treated water is transferred to the attraction solution through the semipermeable membrane to obtain a diluted attraction solution and membrane concentrated water diluted with water.

被処理水は塩類を含有する水であればよいが、例示すれば、海水、湖沼水、河川水、工場廃水などである。   The water to be treated may be water containing salts, but for example, seawater, lake water, river water, factory wastewater, and the like.

誘引溶液は、浸透圧剤を水に溶解したものであり、浸透圧剤には、温度感応性薬剤と無機塩を用いることができる。   The attracting solution is obtained by dissolving an osmotic agent in water, and a temperature-sensitive drug and an inorganic salt can be used as the osmotic agent.

温度感応性薬剤は、低温では親水性で水によく溶けるが、ある温度以上になると疎水性化し溶解度が低下する物質であり、親水性〜疎水性に変化する温度が下限臨界温度あるいは曇点と呼ばれる。この温度に達すると疎水性化した温度感応性薬剤が析出して白濁あるいは相分離が起こる。徐々に加温する際に、薬剤によって白濁するが相分離しないもの、白濁した後更に加温すると相分離するもの、白濁状態を経ずに相分離するものがあるが、本発明に用いられる薬剤は相分離するものであって、ここでいう下限臨界温度とは相分離する温度を意味する。   A temperature-sensitive drug is hydrophilic and well soluble in water at low temperatures. be called. When this temperature is reached, a hydrophobized temperature-sensitive drug is precipitated, resulting in white turbidity or phase separation. When gradually warming, there are those that become cloudy by the drug but not phase-separated, those that become cloudy and then further heated and phase-separated, and those that phase-separate without passing through the cloudy state, the drug used in the present invention Means that the phases are separated, and the lower critical temperature here means the temperature at which the phases are separated.

この温度感応性薬剤は、各種界面活性剤、分散剤、乳化剤などとして利用されており、例示すれば、アルコール、アルキル基、グリコール類、または脂肪酸とエチレングリコールの化合物(水溶性ポリアルキレングリコール誘導体、ポリオキシエチレンポリオキシプロピレンアルキルエーテル、ポリオキシテトラメチレンポリオキシエチレングリコール、ポリオキシエチレンポリオキシプロピレントリメチロールプロパン,ポリオキシエチレンポリオキシプロピレングリセリルエーテル,ポリオキシエチレンポリオキシプロピレンペンタエリスリトールエーテルなど)アルキル基または脂肪酸とプロピレンオキサイドの化合物、アクリルアミドとアルキル基の化合物、エチレングリコール脂肪酸エステル、グリセリン脂肪酸エステル、ソルビタン脂肪酸エステルエチレンオキサイド付加物、アミノ酸およびその誘導体、ブチルグリコールやヘキシルグリコールなどのグリコールなどであり、好ましくは、ポリエチレングリコールとポリプロピレン/ポリブチレングリコールのブロックまたはランダム共重合体、グリセロールエトキシレートブトキシレート、トリメチロールプロパンエトキシブトキシレート等である。本発明において使用する温度感応性薬剤としては、下限臨界温度が30℃〜80℃の範囲、特に40℃〜60℃の範囲のものが好ましい。そのために、HLB値が10以上の非イオン性界面活性剤とそれよりHLB値が低い非イオン性界面活性剤、脂肪酸あるいはアルコールを組み合わせて下限臨界温度を上記の範囲に調節するといった方法を取ることもできる。   This temperature-sensitive agent is used as various surfactants, dispersants, emulsifiers, and the like. For example, alcohols, alkyl groups, glycols, or fatty acid and ethylene glycol compounds (water-soluble polyalkylene glycol derivatives, Polyoxyethylene polyoxypropylene alkyl ether, polyoxytetramethylene polyoxyethylene glycol, polyoxyethylene polyoxypropylene trimethylolpropane, polyoxyethylene polyoxypropylene glyceryl ether, polyoxyethylene polyoxypropylene pentaerythritol ether, etc.) alkyl group Or fatty acid and propylene oxide compound, acrylamide and alkyl group compound, ethylene glycol fatty acid ester, glycerin fatty acid ester, sorbi Fatty acid ester ethylene oxide adduct, amino acids and derivatives thereof, glycols such as butyl glycol and hexyl glycol, preferably a block or random copolymer of polyethylene glycol and polypropylene / polybutylene glycol, glycerol ethoxylate butoxylate, And trimethylolpropane ethoxybutoxylate. As the temperature-sensitive drug used in the present invention, those having a lower critical temperature in the range of 30 ° C to 80 ° C, particularly in the range of 40 ° C to 60 ° C are preferable. Therefore, a method is adopted in which the lower critical temperature is adjusted to the above range by combining a nonionic surfactant having an HLB value of 10 or more and a nonionic surfactant having a lower HLB value, a fatty acid or an alcohol. You can also.

温度感応性薬剤の濃度は、誘引溶液の浸透圧が、被処理水の浸透圧より十分高くなるように調整しなければならない。   The concentration of the temperature-sensitive drug must be adjusted so that the osmotic pressure of the attracting solution is sufficiently higher than the osmotic pressure of the water to be treated.

無機塩は浸透圧を被処理水よりも高くできる溶解度があればよく、炭酸ナトリウム、ケイ酸ナトリウム、硫酸ナトリウム、リン酸ナトリウム、硫酸リチウム、硫酸アンモニウム、炭酸アンモニウム、アンモニウムカルバメート、硫酸亜鉛、硫酸銅、硫酸鉄、硫酸マグネシウム、硫酸アルミニウム、リン酸水素2ナトリウム、リン酸2水素ナトリウム、リン酸カリウム、炭酸カリウム、硫酸マンガンなど多種のものを用いることができる。好ましいものは硫酸マグネシウム、リン酸水素2ナトリウム、リン酸2水素ナトリウムである。無機塩の濃度も誘引溶液の浸透圧が、被処理水の浸透圧より十分高くなるように調整しなければならない。   The inorganic salt only needs to have a solubility capable of making the osmotic pressure higher than that of the water to be treated. Sodium carbonate, sodium silicate, sodium sulfate, sodium phosphate, lithium sulfate, ammonium sulfate, ammonium carbonate, ammonium carbamate, zinc sulfate, copper sulfate, Various materials such as iron sulfate, magnesium sulfate, aluminum sulfate, disodium hydrogen phosphate, sodium dihydrogen phosphate, potassium phosphate, potassium carbonate, and manganese sulfate can be used. Preferred are magnesium sulfate, disodium hydrogen phosphate, and sodium dihydrogen phosphate. The concentration of the inorganic salt must also be adjusted so that the osmotic pressure of the attracting solution is sufficiently higher than the osmotic pressure of the water to be treated.

無機塩を浸透圧剤に用いた場合には、希釈誘引溶液から水を分離する手段が必要であり、その手段として温度感応性薬剤を併用するのがよい。これによって相分離が2段になるのでこれをダブルループ法と称する。   When an inorganic salt is used as the osmotic pressure agent, a means for separating water from the dilution attraction solution is necessary, and a temperature sensitive drug is preferably used as the means. Since this results in two stages of phase separation, this is called a double loop method.

正浸透工程を行う正浸透膜処理装置に用いられる半透膜は水を選択的に透過できるものがよく、正浸透(Forward Osmosis)膜が好ましいが、逆浸透膜も使用できる。材質は特に制限されないが、例示すれば、酢酸セルロース系、ポリアミド系、ポリエチレンイミン系、ポリスルホン系、ポリベンゾイミダゾール系のものなどを挙げることができる。半透膜の形態も特に制限されず、平膜、管状膜、中空糸などいずれであってもよい。   The semipermeable membrane used in the forward osmosis membrane treatment apparatus that performs the forward osmosis step is preferably one that can selectively permeate water, and is preferably a forward osmosis membrane, but a reverse osmosis membrane can also be used. The material is not particularly limited, and examples thereof include cellulose acetate-based, polyamide-based, polyethyleneimine-based, polysulfone-based, and polybenzimidazole-based materials. The form of the semipermeable membrane is not particularly limited and may be any of a flat membrane, a tubular membrane, a hollow fiber, and the like.

この半透膜を装着する装置は通常は円筒形あるいは箱形の容器内に半透膜を設置して、この半透膜で仕切られた一方の室に被処理水を流し、他方の室に誘引溶液を流せるものであり、公知の半透膜装置を用いることができ、市販品を用いることもできる。   A device for mounting this semipermeable membrane is usually a semi-permeable membrane installed in a cylindrical or box-shaped container, and water to be treated flows into one chamber partitioned by this semipermeable membrane, and the other chamber is filled with water. An attracting solution can be flowed, and a known semipermeable membrane device can be used, and a commercially available product can also be used.

被処理水を流す室の入口は被処理水溜(これは海や河川そのものであってもよく、タンク等であってもよい。)に配管接続される。出口側は通常は膜濃縮液溜に配管接続される。両配管を結ぶ循環ラインを設けて、循環させることもできる。   The entrance of the chamber through which the water to be treated flows is connected by piping to a water reservoir to be treated (this may be the sea or river itself, or a tank or the like). The outlet side is usually connected by piping to a membrane concentrate reservoir. A circulation line connecting both pipes can be provided for circulation.

誘引溶液を流す室の入口は淡水分離装置の誘引溶液再生側に配管接続され、出口は淡水分離装置の入口に配管接続され、これによって誘引溶液の循環ラインが形成される。   The inlet of the chamber through which the attracting solution flows is connected to the fresh water separator's attracting solution regeneration side, and the outlet is connected to the fresh water separator's inlet, thereby forming a circulation line of the attracting solution.

正浸透工程で被処理水を半透膜を介して誘引溶液と接触させると浸透圧の差によって被処理水中の水が半透膜を通って誘引溶液に移動し、被処理水が流入した室からは膜濃縮水が、そして誘引溶液が流入した室からは希釈誘引溶液が流出する。   A chamber where treated water flows into the attracting solution through the semipermeable membrane due to the difference in osmotic pressure when the treated water is brought into contact with the attracting solution through the semipermeable membrane in the forward osmosis process. From the membrane concentrate and from the chamber into which the attraction solution flows, the dilute attraction solution flows out.

流出する希釈誘引溶液は、相分離工程で浸透圧剤を主体とする濃厚溶液相と、少量の浸透圧剤を含有する希薄溶液相とに相分離する。以下、浸透圧剤に温度感応性薬剤を用いた場合と無機塩を用いた場合に分けて説明する。   The diluted attraction solution that flows out is phase-separated into a concentrated solution phase mainly composed of an osmotic agent and a dilute solution phase containing a small amount of osmotic agent in a phase separation step. Hereinafter, the case where a temperature-sensitive drug is used as the osmotic agent and the case where an inorganic salt is used will be described separately.

A.浸透圧剤に温度感応性薬剤を用いた場合
加温工程
正浸透工程で被処理水から水が移動して温度感応性薬剤が希釈された希釈誘引溶液を下限臨界温度以上の温度まで加温して、温度感応性薬剤の少なくとも一部を凝集させる。この凝集は、温度感応性薬剤の濃厚溶液が分相したものである。
A. When a temperature-sensitive drug is used as an osmotic pressure agent Heating process In the forward osmosis process, water is transferred from the water to be treated, and the dilution-induced solution diluted with the temperature-sensitive drug is heated to a temperature above the lower critical temperature. Agglomerate at least a portion of the temperature sensitive drug. This aggregation is a phase separation of a concentrated solution of the temperature sensitive drug.

加温工程における加温手段は問わないが、加熱器を備えた加温槽や熱交換器などを利用することができる。   The heating means in the heating step is not limited, but a heating tank equipped with a heater or a heat exchanger can be used.

加温工程における加温温度は、例えば熱交換器へ導入する熱媒体の流量の調整で制御できる。   The heating temperature in the heating step can be controlled, for example, by adjusting the flow rate of the heat medium introduced into the heat exchanger.

この加温工程の熱源には、次の相分離工程で分離された濃厚溶液の顕熱を使用することが好ましい。   It is preferable to use the sensible heat of the concentrated solution separated in the next phase separation step as the heat source for this heating step.

相分離工程
加温工程で分相した温度感応性薬剤を主体とする濃厚溶液相と水を主体とし少量の温度感応性薬剤を含有する希薄溶液相に重力沈降により分離する。この重力分離は下限臨界温度以上の液温で相分離槽内で静置することによって行うことができる。
Phase separation step The solution is separated by gravity sedimentation into a concentrated solution phase mainly composed of a temperature-sensitive drug separated in the heating step and a dilute solution phase mainly composed of water and containing a small amount of the temperature-sensitive drug. This gravitational separation can be performed by standing in a phase separation tank at a liquid temperature equal to or higher than the lower critical temperature.

加温した希釈誘引溶液が相分離槽に投入されると、温度感応性薬剤の比重が水より重い場合は、濃厚溶液の微細液滴は速やかに沈降し、液滴同士が合一して下に濃厚溶液相が形成される。一方、温度感応性薬剤の比重が水より軽い場合、例えば、ブチルグリコールやヘキシルグリコールを温度感応性薬剤に用いた場合は、濃厚溶液相が上相になり希薄溶液相が下相になる。   When the heated dilution-inducing solution is put into the phase separation tank, if the specific gravity of the temperature sensitive drug is heavier than water, the fine droplets of the concentrated solution will settle quickly and the droplets will coalesce. A concentrated solution phase is formed. On the other hand, when the specific gravity of the temperature sensitive drug is lighter than water, for example, when butyl glycol or hexyl glycol is used as the temperature sensitive drug, the concentrated solution phase becomes the upper phase and the diluted solution phase becomes the lower phase.

循環工程
循環工程は、相分離工程で分離された濃厚溶液を正浸透工程へ循環し、誘引溶液として再使用する工程である。この循環手段にはポンプや配管が用いられる。相分離工程で分離された濃厚溶液は、まず、これを誘引溶液の下限臨界温度より低い温度に冷却することで水に溶解させて誘引溶液に再生する。この温度は広い範囲で採用可能であるが、経済性を考慮すると常温かそれより高い温度が好ましい。この冷却熱源としては、被処理水あるいは正浸透工程において得られた希釈誘引溶液を用いることがエネルギーの効率利用の点で好ましい。この冷却が不充分な場合には、正浸透工程で被処理水から移動してくる水によって濃度が下がるので下限臨界温度を発現して相分離し、浸透圧が失われてしまう。
Circulation step The circulation step is a step in which the concentrated solution separated in the phase separation step is circulated to the forward osmosis step and reused as an attraction solution. A pump and piping are used for this circulation means. The concentrated solution separated in the phase separation step is first cooled to a temperature lower than the lower critical temperature of the attracting solution to be dissolved in water and regenerated into the attracting solution. Although this temperature can be employed in a wide range, considering the economy, a temperature of room temperature or higher is preferable. As this cooling heat source, it is preferable from the viewpoint of efficient use of energy to use the water to be treated or the dilution attraction solution obtained in the forward osmosis step. If this cooling is insufficient, the concentration is lowered by the water moving from the water to be treated in the forward osmosis process, so that the lower critical temperature is developed and phase separation occurs, and the osmotic pressure is lost.

再生した誘引溶液はそのまま正浸透工程へ循環して再利用する。   The regenerated attractant solution is directly recycled to the forward osmosis process.

淡水回収工程
一方、相分離工程で分離された希薄溶液は、ナノろ過膜や逆浸透膜などで膜ろ過して、そこに残存している温度感応性薬剤を除去する。膜ろ過水は淡水であり、飲料水などに利用できる。膜ろ過されないで残った膜濃縮水は、温度感応性薬剤が含まれているので、相分離工程に循環するのがよい。あるいは、濃縮して誘引溶液として正浸透工程に直接返送することもできる。
Fresh Water Recovery Step On the other hand, the dilute solution separated in the phase separation step is subjected to membrane filtration with a nanofiltration membrane or a reverse osmosis membrane to remove the temperature sensitive drug remaining there. Membrane filtrate is fresh water and can be used for drinking water and the like. Since the membrane-concentrated water remaining without being membrane-filtered contains a temperature-sensitive drug, it should be circulated in the phase separation step. Alternatively, it can be concentrated and returned directly to the forward osmosis process as an attractant solution.

一方、正浸透工程で得られた膜濃縮水は塩分を高濃度で含んでいるので、これを濃縮して塩分を析出させて分離し、有効利用することもできる。   On the other hand, since the membrane concentrated water obtained in the forward osmosis process contains a high concentration of salt, it can be concentrated by precipitating the salt and separating it for effective use.

B.浸透圧剤に無機塩を用いた場合
一方、浸透圧剤に無機塩を用いた場合には、希釈誘引溶液を加温しても分相しないので、相分離工程の前段で前記希釈誘引溶液に下限臨界温度を有する温度感応性薬剤を混合する温度感応性薬剤混合工程を設ける。
B. When an inorganic salt is used as the osmotic agent On the other hand, when an inorganic salt is used as the osmotic agent, phase separation does not occur even when the dilution attraction solution is heated. A temperature sensitive drug mixing step is provided for mixing a temperature sensitive drug having a lower critical temperature.

温度感応性薬剤混合工程
温度感応性薬剤は前述のもののなかから選択して用いればよい。混合工程においては、温度感応性薬剤が淡水を希釈誘引溶液から吸水して希釈誘引溶液を濃縮する必要がある。そのため、吸水後における温度感応性薬剤の浸透圧が濃縮された誘引溶液の浸透圧を上回るように、温度感応性薬剤の濃度・量を設定する必要がある。
この工程で混合される温度感応性薬剤は、通常は、浸透圧剤に無機塩を用いた場合の淡水回収工程における第2相分離工程で分離された温度感応性薬剤溶液が循環使用される。
Temperature-sensitive drug mixing step The temperature-sensitive drug may be selected from those described above. In the mixing step, it is necessary for the temperature-sensitive drug to absorb fresh water from the dilution attraction solution and concentrate the dilution attraction solution. Therefore, it is necessary to set the concentration and amount of the temperature sensitive drug so that the osmotic pressure of the temperature sensitive drug after water absorption exceeds the osmotic pressure of the concentrated attractant solution.
As the temperature-sensitive drug mixed in this step, the temperature-sensitive drug solution separated in the second phase separation step in the fresh water recovery step when an inorganic salt is used as the osmotic agent is usually circulated.

相分離工程
希釈誘引溶液に温度感応性薬剤を混合した液は、無機塩を主体とする濃厚溶液相と温度感応性薬剤を主体とする希薄溶液相に重力沈降によって分離する。一般に温度感応性薬剤は塩分の共存下で曇点が低下するため、この相分離工程においては加温せずとも温度感応性薬剤が凝集する。但し、無機塩と温度感応性薬剤の組合せによっては常温で明確な相分離が行われないことがある。無機塩として硫酸マグネシウム、リン酸2水素ナトリウムやリン酸水素2ナトリウムを用いた場合には多くの場合に常温で層分離するが、その他の場合には層分離のために加温が必要な場合もある。この温度は無機塩の温度感応性薬剤の種類や濃度によって異なるため,別途実験的に求める必要がある。
この重力分離は相分離槽内で静置することによって行うことができる。
Phase Separation Step A liquid in which a temperature-sensitive drug is mixed with a dilution attraction solution is separated into a concentrated solution phase mainly composed of an inorganic salt and a dilute solution phase mainly composed of a temperature-sensitive drug by gravity sedimentation. In general, a temperature-sensitive drug has a cloud point lowering in the presence of salt, and therefore, in this phase separation step, the temperature-sensitive drug aggregates without heating. However, depending on the combination of the inorganic salt and the temperature sensitive agent, a clear phase separation may not be performed at room temperature. When magnesium sulfate, sodium dihydrogen phosphate, or disodium hydrogen phosphate is used as the inorganic salt, the layers are separated at room temperature in many cases. In other cases, heating is required for layer separation. There is also. Since this temperature varies depending on the type and concentration of the temperature-sensitive agent of the inorganic salt, it must be determined experimentally separately.
This gravitational separation can be performed by standing in a phase separation tank.

淡水回収工程
浸透圧剤に無機塩を用いた場合には、相分離工程で分離される希薄溶液が温度感応性薬剤を主体とする液であるので、まず、加温工程で温度感応性薬剤を分相させて、これを第2相分離工程で相分離する。
Fresh water recovery process When an inorganic salt is used for the osmotic pressure agent, the diluted solution separated in the phase separation process is a liquid mainly composed of a temperature sensitive drug. The phases are separated and the phases are separated in the second phase separation step.

加温工程
相分離工程で分離された、温度感応性薬剤を主体とする希薄溶液を温度感応性薬剤の下限臨界温度以上の温度まで加温して、温度感応性薬剤の少なくとも一部を凝集させる。加温温度は、例えば熱交換器へ導入する熱媒体の流量の調整で制御される。
Heating process The dilute solution mainly composed of a temperature-sensitive drug separated in the phase separation process is heated to a temperature equal to or higher than the lower critical temperature of the temperature-sensitive drug to agglomerate at least a part of the temperature-sensitive drug. . The heating temperature is controlled, for example, by adjusting the flow rate of the heat medium introduced into the heat exchanger.

第2相分離工程
加温工程で分相した温度感応性薬剤を主体とする温度感応性薬剤溶液相と水を主体とし少量の温度感応性薬剤を含有する淡水相に重力沈降により分離する。この重力分離は下限臨界温度以上の液温で相分離槽内で静置することができる。
Second phase separation step A temperature-sensitive drug solution phase mainly composed of the temperature-sensitive drug phase-separated in the heating step and a fresh water phase mainly composed of water and containing a small amount of the temperature-sensitive drug are separated by gravity sedimentation. This gravity separation can be left in the phase separation tank at a liquid temperature equal to or higher than the lower critical temperature.

第2相分離工程で分離された少量の温度感応性薬剤を含有する淡水は、ナノろ過膜や逆浸透膜などで膜ろ過して、そこに残存している温度感応性薬剤を除去する。膜ろ過水は淡水であり、飲料水などに利用できる。膜ろ過されないで残った膜濃縮水は、温度感応性薬剤が含まれているので、第2相分離工程に循環するのがよい。   The fresh water containing a small amount of the temperature-sensitive drug separated in the second phase separation step is subjected to membrane filtration with a nanofiltration membrane or a reverse osmosis membrane to remove the temperature-sensitive drug remaining there. Membrane filtrate is fresh water and can be used for drinking water and the like. Since the membrane-concentrated water remaining without being membrane-filtered contains a temperature-sensitive drug, it is preferable to circulate it in the second phase separation step.

循環工程
循環工程は、相分離工程で分離された濃厚溶液を正浸透工程へ循環し、誘引溶液として再使用する工程である。この循環手段にはポンプや配管が用いられる。
Circulation step The circulation step is a step in which the concentrated solution separated in the phase separation step is circulated to the forward osmosis step and reused as an attraction solution. A pump and piping are used for this circulation means.

C.誘引溶液流量と加温温度の制御操作
本発明は、このような水の脱塩処理方法において、前記希釈誘引溶液と前記誘引溶液各々の流量を測定し、それらの流量差が予め設定された設定値よりも低い場合は、前記誘引溶液の流量を増量し、また、前記流量差が予め設定された設定値よりも高い場合は、前記誘引溶液の流量を減少させることを特徴としている。
C. The present invention relates to a method for controlling the flow rate of the attracting solution and the heating temperature. In such a method for desalinating water, the flow rate of each of the diluted attracting solution and the attracting solution is measured and the difference between the flow rates is set in advance When it is lower than the value, the flow rate of the attracting solution is increased, and when the flow rate difference is higher than a preset value, the flow rate of the attracting solution is decreased.

そして、前記相分離工程あるいは第2相分離工程が前記希釈誘引溶液を前記希釈誘引溶液の曇点以上の温度まで加温する加温工程を有している場合には、前記希釈誘引溶液と前記誘引溶液の流量差が予め設定された設定値よりも低い場合に、前記誘引溶液の流量を増加するとともに、前記加温工程での加温温度を上昇させる、また、前記流量差が予め設定された設定値よりも高い場合に、前記誘引溶液の流量を減少させるとともに、前記加温工程での加温温度を低下させることを特徴としている。   And when the phase separation step or the second phase separation step has a heating step of heating the dilution attraction solution to a temperature above the cloud point of the dilution attraction solution, the dilution attraction solution and the When the flow rate difference of the attracting solution is lower than a preset set value, the flow rate of the attracting solution is increased and the heating temperature in the heating step is increased, and the flow rate difference is preset. When the temperature is higher than the set value, the flow rate of the attracting solution is decreased and the heating temperature in the heating step is decreased.

誘引溶液は、正浸透工程において、半透膜を介して被処理水と接触している間に被処理水中の水が移動して希釈される。半透膜を離れた希釈誘引溶液は、その間に移動した水量だけ増量している。そして、単位時間当りの希釈誘引溶液の流量と誘引溶液の流量の差がこの移動水量になる。そこで、この流量差が設定値よりも低い場合は、造水量が設定値より低くなっているので誘引溶液の流量を増加し、高い場合は誘引溶液の流量を減少させるのである。ただ、誘引溶液の流量をあまり増加させると相分離槽内での滞留時間減少による分離効率の低下やポンプ動力の増加、加温工程の熱交換器圧損の増大という問題を生じる。そこで、流量差が一定値を超えたときは、誘引溶液の流量の増加に加えて、加温工程の加温温度を上昇させて半透膜に流入する誘引溶液の濃度を上昇させるのである。   In the forward osmosis step, the attraction solution is diluted by the water in the for-treatment water moving while in contact with the for-treatment water through the semipermeable membrane. The dilution attraction solution leaving the semipermeable membrane is increased by the amount of water transferred during that time. And the difference of the flow volume of the dilution attraction solution per unit time and the flow volume of the attraction solution becomes this moving water amount. Therefore, when the flow rate difference is lower than the set value, the amount of fresh water is lower than the set value, so that the flow rate of the attracting solution is increased, and when it is higher, the flow rate of the attracting solution is decreased. However, if the flow rate of the attracting solution is increased too much, problems such as a decrease in separation efficiency due to a decrease in residence time in the phase separation tank, an increase in pump power, and an increase in heat exchanger pressure loss in the heating process occur. Therefore, when the flow rate difference exceeds a certain value, in addition to the increase in the flow rate of the attracting solution, the concentration of the attracting solution flowing into the semipermeable membrane is increased by increasing the heating temperature in the heating step.

希釈誘引溶液と誘引溶液の流量差の設定値は、原則として造水量と一致させるが,膜ろ過等の後段プロセスで水量が減少する場合にはそれを考慮して設定する。   The flow rate difference between the dilute attracting solution and the attracting solution should be consistent with the amount of water produced in principle. However, if the amount of water decreases in a subsequent process such as membrane filtration, it is set in consideration of it.

流量差が設定値よりも低い場合は誘引溶液の流量を増加し、高い場合は誘引溶液の流量を減少させるが、その増加量や減少量は、各脱塩処理装置によって異なるので各装置に応じて定めるが、要は流量差が設定値に戻るように制御すればよい。   When the flow rate difference is lower than the set value, the flow rate of the attracting solution is increased. When the flow rate difference is high, the flow rate of the attracting solution is decreased. However, the amount of increase or decrease differs depending on each desalting treatment device. In short, what is necessary is to control the flow rate difference to return to the set value.

そして、流量差が設定値からかなりかい離した場合には誘引溶液の流量の制御に加えて、加温工程の加温温度の制御も行うが、この加温温度の制御の併用を開始する時点は、相分離槽、送液ポンプ、熱交換器等の設計許容値などによって異なる。一般的には、誘引溶液の流量制御開始は、流量差の設定値からのかい離が5〜30%程度、通常10〜20%程度とするのがよい。そして、誘引溶液の流量の変化は上限を1.05〜1.3倍とし、流量差の設定値からのかい離が5%の範囲まで、好ましくは設定値まで戻るようにする。この誘引溶液の流量の制御だけでは、上記設定値に戻らない場合は加温温度の制御を開始する。加温温度の変化は上限を2〜10℃程度上昇とするのがよい。   And when the flow rate difference is far from the set value, in addition to controlling the flow rate of the attracting solution, the heating temperature is also controlled in the heating process, but when the combined use of this heating temperature control is started, It depends on the design tolerance of the phase separation tank, liquid feed pump, heat exchanger, etc. In general, the flow control of the attracting solution is preferably controlled so that the deviation from the set value of the flow rate difference is about 5 to 30%, usually about 10 to 20%. The upper limit of the change in the flow rate of the attracting solution is 1.05 to 1.3 times, and the deviation of the flow rate difference from the set value is returned to the range of 5%, preferably to the set value. If control does not return to the set value only by controlling the flow rate of the attracting solution, control of the heating temperature is started. It is preferable that the upper limit of the change in the heating temperature is increased by about 2 to 10 ° C.

かい離度を10%とした場合の制御操作の例を表1に示す。   Table 1 shows an example of the control operation when the separation degree is 10%.

Figure 0006414528
Figure 0006414528

本発明の実施態様1Embodiment 1 of the present invention

本発明の実施態様1を図1に示す。同図に示すように、この装置は、正浸透膜処理装置10、熱交換器7、加熱器12、相分離槽11および冷却器13からなっている。 Embodiment 1 of the present invention is shown in FIG. As shown in the figure, this apparatus includes a forward osmosis membrane treatment apparatus 10, a heat exchanger 7, a heater 12, a phase separation tank 11 and a cooler 13.

被処理水1は、正浸透膜処理装置10の左側の室に下部から入り、半透膜3を通って被処理水中の水が右側の室に移動して、濃縮された膜濃縮水3が左側の室の上部から排出される。誘引溶液4は、正浸透膜処理装置10の右側の室に上部から入り、半透膜3を介して被処理水1と向流接触して希釈誘引溶液5が右側の室の下部から排出される。この希釈誘引溶液5は、希釈誘引溶液流量計9で流量が測定されて、熱交換器7で加温され、加熱器12でさらに温度感応性薬剤の曇点以上まで加温され、相分離槽11に入る。相分離槽11では、温度感応性薬剤を主体とする濃厚溶液相と少量の温度感応性薬剤を含有する希薄溶液相に相分離され、希薄溶液6は上部から取り出され、残存する温度感応性薬剤が除去されて淡水を得る。一方、濃厚溶液は下部から取り出されて熱交換器7で冷却され、冷却器13でさらに冷却されて誘引溶液4として誘引溶液流量計8で流量が測定された後、正浸透膜処理装置10に返送される。   The treated water 1 enters the left chamber of the forward osmosis membrane treatment apparatus 10 from below, the water in the treated water moves to the right chamber through the semipermeable membrane 3, and the concentrated membrane concentrated water 3 is formed. It is discharged from the upper part of the left chamber. The attraction solution 4 enters the right chamber of the forward osmosis membrane treatment apparatus 10 from the upper part, contacts the water to be treated 1 through the semipermeable membrane 3, and the diluted attraction solution 5 is discharged from the lower part of the right chamber. The The dilution attraction solution 5 is measured for flow rate by the dilution attraction solution flow meter 9, heated by the heat exchanger 7, further heated to the cloud point of the temperature sensitive drug by the heater 12, and phase separation tank Enter 11. In the phase separation tank 11, the phase is separated into a concentrated solution phase mainly composed of a temperature-sensitive drug and a dilute solution phase containing a small amount of the temperature-sensitive drug, and the diluted solution 6 is taken out from the upper part, and the remaining temperature-sensitive drug. Is removed to obtain fresh water. On the other hand, the concentrated solution is taken out from the lower part, cooled by the heat exchanger 7, further cooled by the cooler 13, and the flow rate is measured by the attracting solution flow meter 8 as the attracting solution 4. Will be returned.

1.実験装置
図1の実験装置を用いた。
1. Experimental apparatus The experimental apparatus of FIG. 1 was used.

被処理水(FS):NaCl水溶液
誘引溶液(DS):温度感応性薬剤(ポリエチレングリコールとポリプロピレンのランダム共重合体)水溶液
正浸透(FO)膜:CTA製、膜面積60m、設計造水量2.5m/day
加熱器:プレート型熱交換器(熱交換面積7.2m)、熱媒体:100℃シリコンオイル
冷却器:プレート型熱交換器(熱交換面積4.0m)、熱媒体:5℃冷水
相分離槽:横流式沈殿槽(容積40L)
2.運転条件および運転結果
(1)RUN1(通常運転)
Water to be treated (FS): NaCl aqueous solution Attracting solution (DS): Temperature sensitive agent (random copolymer of polyethylene glycol and polypropylene) Aqueous forward osmosis (FO) membrane: CTA, membrane area 60 m 2 , designed water production 2 .5m 3 / day
Heater: plate type heat exchanger (heat exchange area 7.2 m 2 ), heat medium: 100 ° C. silicone oil Cooler: plate type heat exchanger (heat exchange area 4.0 m 2 ), heat medium: 5 ° C. cold water phase Separation tank: Cross-flow type precipitation tank (volume 40L)
2. Operating conditions and results (1) RUN1 (normal operation)

Figure 0006414528
表2に通常運転時の運転条件と運転結果を示す。
FS濃度は一般的な海水塩濃度を模擬した。希釈DS分離温度は、工場の冷却器排気等の低温廃熱利用を想定して80℃に設定した。DS濃度は分離温度によって一義的に決まる値であり、本実験に用いたDSの濃度80.2%は海水より充分高い浸透圧を有する。
FSとDSの流量は、予め予備実験を実施し、FSからの淡水の回収率が33%となるように設定した。
Figure 0006414528
Table 2 shows the operation conditions and operation results during normal operation.
FS concentration simulated general sea salt concentration. The dilution DS separation temperature was set at 80 ° C, assuming low-temperature waste heat utilization such as factory cooler exhaust. The DS concentration is a value uniquely determined by the separation temperature, and the DS concentration of 80.2% used in this experiment has a sufficiently higher osmotic pressure than seawater.
Preliminary experiments were conducted in advance to set the flow rate of FS and DS so that the recovery rate of fresh water from FS was 33%.

通常時の造水量として2.5m/dayと設定値通りの値が得られている。このとき、希釈DSを80℃に加温して沈殿槽にて滞留時間6.5分で分離することにより80.2%の濃度のDSが得られた。DS供給量は造水量の約2.5倍である。
(2)RUN2(高濃度FS1)
As a normal amount of fresh water, 2.5 m 3 / day, which is a set value, is obtained. At this time, the diluted DS was heated to 80 ° C. and separated in a sedimentation tank with a residence time of 6.5 minutes, whereby a DS with a concentration of 80.2% was obtained. DS supply is about 2.5 times the amount of fresh water.
(2) RUN2 (high concentration FS1)

Figure 0006414528

表3にFS濃度を3.5wt%から3.7wt%に上昇させた場合の運転条件と運転結果を示す。
FS濃度を3.5wt%から3.7wt%に上昇させた場合、RUN1と同一の運転条件では造水量が2.3m/dayと8%ほど低下した。FSの浸透圧が上昇したことが原因と考えられる。閉鎖性水域の渇水期などにこのような濃度変化の生じることが想定される。
(3)RUN3(DS流量増加)
Figure 0006414528

Table 3 shows operating conditions and results when the FS concentration is increased from 3.5 wt% to 3.7 wt%.
When the FS concentration was increased from 3.5 wt% to 3.7 wt%, the amount of fresh water was reduced to 2.3 m 3 / day and about 8% under the same operating conditions as RUN1. This is considered to be caused by an increase in the osmotic pressure of FS. It is assumed that such a concentration change occurs during a drought period in a closed water area.
(3) RUN3 (DS flow rate increase)

Figure 0006414528
表4にDS流量を6.3m/dayから6.8m/dayに増やした場合の運転条件と運転結果を示す。
Figure 0006414528
Table 4 shows the operating conditions and operating results when increasing the DS rate from 6.3 m 3 / day to 6.8 m 3 / day.

DS流量の6.3m/dayから6.8m/dayの8%の流量増加によって造水量を設定値通りに制御することができた。FSの温度変化によって同程度の造水量低下が生じた場合においても、同様の対応が可能である。この操作はポンプ設定を変更するだけで即座に効果が得られるため、一時的な造水量変動に即座に対応することが可能である。沈殿槽の滞留時間が6.5分から6.2分に減少したが、分離効率への影響は軽微で、分離後のDS濃度は80.1wt%であった。
(4)RUN4(高濃度FS2)
It could be controlled to a value set as the desalination amount by 8% increase in the flow rate of 6.3 m 3 / day from 6.8 m 3 / day in DS flow. A similar measure can be taken even when a similar decrease in the amount of water produced occurs due to the temperature change of the FS. Since this operation can be obtained immediately by simply changing the pump settings, it is possible to immediately respond to temporary fluctuations in the amount of fresh water. Although the residence time of the precipitation tank decreased from 6.5 minutes to 6.2 minutes, the influence on the separation efficiency was slight, and the DS concentration after separation was 80.1 wt%.
(4) RUN4 (high concentration FS2)

Figure 0006414528
表5にFS濃度を3.9wt%に増やした場合の運転条件と運転結果を示す。
Figure 0006414528
Table 5 shows operating conditions and operating results when the FS concentration is increased to 3.9 wt%.

RUN2よりさらにFSの濃度上昇幅を大きくした結果、造水量は設定値の20%減と大幅に低下した。このような場合にDS供給量の増加で対応した場合、沈殿槽の滞留時間減少が顕著となり、分離性能が低下することが考えられる。分離性能の低下を抑制するためには沈殿槽滞留時間に大幅な余裕を取る必要があり、設備費増につながる。
(5)RUN5(希釈DS分離温度上昇)
As a result of increasing the FS concentration increase range further than RUN2, the amount of fresh water was greatly reduced by 20% of the set value. In such a case, if the DS supply amount is increased, the residence time in the settling tank is significantly reduced, and the separation performance may be lowered. In order to suppress the degradation of the separation performance, it is necessary to take a large margin in the sedimentation tank residence time, which leads to an increase in equipment costs.
(5) RUN5 (Dilution DS separation temperature rise)

Figure 0006414528
表6に希釈DS分離温度を80℃から85℃に上昇させた場合の運転条件と運転結果を示す。
Figure 0006414528
Table 6 shows operating conditions and results when the dilution DS separation temperature is increased from 80 ° C to 85 ° C.

希釈DS分離温度を5℃上昇させることにより、DS濃度が2ポイント上昇した。このことにより設計造水量を得るためのDS流量は6.5m/dayとRUN1の標準的な値からわずかに増加するだけであった。 By increasing the dilution DS separation temperature by 5 ° C., the DS concentration increased by 2 points. As a result, the DS flow rate for obtaining the designed water production amount was only slightly increased from the standard values of 6.5 m 3 / day and RUN1.

本発明の実施態様2Embodiment 2 of the present invention

図2に示すダブルループ法の装置を使用した場合の制御動作について説明する。   A control operation when the apparatus of the double loop method shown in FIG. 2 is used will be described.

正浸透膜処理装置10では、被処理水1が浸透圧剤として硫酸マグネシウムを用いた誘引溶液4と半透膜3を介して向流接触し、それによって濃縮され、膜濃縮水2となって排出される。一方、被処理水1からの水の移動によって希釈された希釈誘引溶液5は、混合槽14に入れられ、相分離槽11から循環してきた温度感応性薬剤溶液17と混合されて誘引溶液再生槽15に送られる。誘引溶液再生槽15で分離された硫酸マグネシウムを浸透圧剤とする誘引溶液4はポンプにより正浸透膜処理装置10に返送される。一方、誘引溶液再生槽15で分離された温度感応性薬剤溶液16は熱交換器7で相分離槽11から出る80℃の温度感応性薬剤溶液17で加温され、さらに加熱器12で90℃の減圧蒸気で加温されて相分離槽11に入れられる。相分離槽11で分離された温度感応性薬剤溶液17は熱交換器7で熱交換して冷却され、さらに冷却器13で32℃まで冷却されて混合槽14に投入されて循環している。一方、相分離槽11の希薄溶液6は淡水として取り出される。   In the forward osmosis membrane treatment apparatus 10, the water 1 to be treated is brought into countercurrent contact with the attraction solution 4 using magnesium sulfate as an osmotic pressure agent through the semipermeable membrane 3, thereby being concentrated to become membrane concentrated water 2. Discharged. On the other hand, the diluted attracting solution 5 diluted by the movement of water from the water 1 to be treated is put in the mixing tank 14 and mixed with the temperature sensitive chemical solution 17 circulating from the phase separation tank 11 to be an attracting solution regeneration tank. 15 is sent. The attraction solution 4 using magnesium sulfate separated in the attraction solution regeneration tank 15 as an osmotic pressure agent is returned to the forward osmosis membrane treatment apparatus 10 by a pump. On the other hand, the temperature sensitive drug solution 16 separated in the attracting solution regeneration tank 15 is heated by the 80 ° C. temperature sensitive drug solution 17 coming out of the phase separation tank 11 by the heat exchanger 7 and further heated by the heater 12 at 90 ° C. It is heated by the reduced pressure steam and put into the phase separation tank 11. The temperature sensitive drug solution 17 separated in the phase separation tank 11 is cooled by exchanging heat in the heat exchanger 7, further cooled to 32 ° C. in the cooler 13, put into the mixing tank 14 and circulated. On the other hand, the dilute solution 6 in the phase separation tank 11 is taken out as fresh water.

このようなプロセスにおいて、造水量が低下した場合、まず正浸透膜処理装置10に供給する誘引溶液(MgSO水溶液、15〜25%)4の流量を増大させる。本操作は即効性があるが、温度感応性薬剤溶液17と希釈誘引溶液5との混合時間および誘引溶液再生槽15における分離時間の減少により再生された誘引溶液濃度が所定値から低下する。そこで、次の手段として誘引溶液再生槽15に供給する温度感応性薬剤溶液17の流量を増大させる。この場合は希釈誘引溶液5から温度感応性薬剤溶液17への淡水の移動は促進されるが、混合時間と分離時間の減少が甚だしくなるため限界がある。次の手段として相分離槽11の温度を上昇させることで温度感応性薬剤溶液17を高濃度化する。これにより温度感応性薬剤溶液17と希釈誘引溶液5との混合時間および分離時間に影響を及ぼさずに希釈誘引溶液5から温度感応性薬剤溶液17への淡水の移動を促進できる。 In such a process, when the amount of water produced decreases, the flow rate of the attraction solution (MgSO 4 aqueous solution, 15 to 25%) 4 supplied to the forward osmosis membrane treatment apparatus 10 is first increased. Although this operation is effective immediately, the concentration of the attracted solution regenerated is reduced from a predetermined value due to a decrease in the mixing time of the temperature sensitive drug solution 17 and the diluted attracting solution 5 and the separation time in the attracting solution regeneration tank 15. Therefore, the flow rate of the temperature sensitive chemical solution 17 supplied to the attracting solution regeneration tank 15 is increased as the next means. In this case, the movement of fresh water from the dilution attraction solution 5 to the temperature sensitive drug solution 17 is promoted, but there is a limit because the reduction of the mixing time and separation time becomes significant. As a next means, the temperature of the phase separation tank 11 is raised to increase the concentration of the temperature sensitive drug solution 17. Thereby, the movement of the fresh water from the dilution attraction solution 5 to the temperature sensitive drug solution 17 can be promoted without affecting the mixing time and the separation time of the temperature sensitive drug solution 17 and the dilution attraction solution 5.

本発明により、海水等から淡水を安定して製造できるので、海水等から淡水を製造する装置に広く利用できる。   According to the present invention, since fresh water can be stably produced from seawater or the like, it can be widely used in an apparatus for producing fresh water from seawater or the like.

1 被処理水
2 膜濃縮水
3 半透膜
4 誘引溶液
5 希釈誘引溶液
6 希薄溶液
7 熱交換器
8 誘引溶液流量計
9 希釈誘引溶液流量計
10 正浸透膜処理装置
11 相分離槽
12 加熱器
13 冷却器
14 混合槽
15 誘引溶液再生槽
16 希釈温度感応性薬剤溶液
17 温度感応性薬剤溶液
DESCRIPTION OF SYMBOLS 1 Water to be treated 2 Membrane concentrated water 3 Semipermeable membrane 4 Attraction solution 5 Dilution attraction solution 6 Dilute solution 7 Heat exchanger 8 Attraction solution flow meter 9 Dilution attraction solution flow meter 10 Forward osmosis membrane treatment device 11 Phase separation tank 12 Heater DESCRIPTION OF SYMBOLS 13 Cooler 14 Mixing tank 15 Attraction solution regeneration tank 16 Dilution temperature sensitive chemical solution 17 Temperature sensitive chemical solution

Claims (6)

塩類を含有する被処理水と、浸透圧剤を水に溶解し前記被処理水よりも浸透圧の高い誘引溶液とを半透膜を介して接触させ、前記被処理水中の水を前記半透膜を通して前記誘引溶液に移動させ、水で希釈された希釈誘引溶液と膜濃縮水を得る正浸透工程と、
前記希釈誘引溶液を浸透圧剤を主体とする濃厚溶液相と、少量の浸透圧剤を含有する希薄溶液相とに相分離する相分離工程と、
前記相分離工程で分離された濃厚溶液を前記正浸透工程へ循環し、誘引溶液として再使用する循環工程と、
前記相分離工程で分離された希薄溶液から淡水を得る淡水回収工程を有する水の脱塩処理方法であって、
前記希釈誘引溶液と前記誘引溶液各々の流量を測定し、それらの流量差が予め設定された設定値よりも低い場合は、前記誘引溶液の流量を増加し、また、前記流量差が予め設定された設定値よりも高い場合は、前記誘引溶液の流量を減少させることを特徴とする水の脱塩処理方法。
A treated water containing salts and an attracting solution having an osmotic agent dissolved in water and having a higher osmotic pressure than the treated water are brought into contact with each other through a semipermeable membrane, and the water in the treated water is brought into contact with the semipermeable material. Forward osmosis step of transferring to the attraction solution through a membrane to obtain a diluted attraction solution diluted with water and membrane concentrated water;
A phase separation step of phase-separating the diluted attraction solution into a concentrated solution phase mainly composed of an osmotic agent and a dilute solution phase containing a small amount of an osmotic agent;
Circulating the concentrated solution separated in the phase separation step to the forward osmosis step and reusing it as an attracting solution;
A method for desalinating water having a fresh water recovery step for obtaining fresh water from the dilute solution separated in the phase separation step,
When the flow rate of each of the diluted attractant solution and the attractant solution is measured and the flow rate difference between them is lower than a preset value, the flow rate of the attractant solution is increased, and the flow rate difference is preset. If it is higher than the set value, the water desalting method is characterized in that the flow rate of the attracting solution is decreased.
前記浸透圧剤が下限臨界温度を有する温度感応性薬剤であり、前記相分離工程が前記希釈誘引溶液を前記誘引溶液の曇点以上の温度まで加温する加温工程を有しており、かつ
前記希釈誘引溶液と前記誘引溶液の流量差が予め設定された設定値よりも低い場合に、前記誘引溶液の流量を増加するとともに、前記加温工程での加温温度を上昇させる、また、前記流量差が予め設定された設定値よりも高い場合に、前記誘引溶液の流量を減少させるとともに、前記加温工程での加温温度を低下させることを特徴とする請求項1に記載の水の脱塩処理方法。
The osmotic agent is a temperature sensitive agent having a lower critical temperature, and the phase separation step has a heating step of heating the dilution attraction solution to a temperature above the cloud point of the attraction solution; and When the flow rate difference between the diluted attracting solution and the attracting solution is lower than a preset value, the flow rate of the attracting solution is increased and the heating temperature in the warming step is increased. 2. The water according to claim 1, wherein when the flow rate difference is higher than a preset value, the flow rate of the attracting solution is decreased and the heating temperature in the heating step is decreased. Desalination treatment method.
前記浸透圧剤が無機塩であり、前記相分離工程の前段で前記希釈誘引溶液に下限臨界温度を有する温度感応性薬剤を混合する温度感応性薬剤混合工程を有するとともに、前記相分離工程で分離された希薄溶液から淡水を得る淡水回収工程が、前記希薄溶液を前記誘引溶液の曇点以上の温度まで加温する加温工程と、前記加温工程に続き温度感応性薬剤を主体とする温度感応性薬剤溶液相と、淡水を主体とし少量の温度感応性薬剤を含有する淡水相とに相分離する第2相分離工程を有しており、
かつ、前記希釈誘引溶液と前記誘引溶液の流量差が予め設定された設定値よりも低い場合に、前記誘引溶液の流量を増加するとともに、前記加温工程での加温温度を上昇させる、また、前記流量差が予め設定された設定値よりも高い場合に、前記誘引溶液の流量を減少させるとともに、前記加温工程での加温温度を低下させることを特徴とする請求項1に記載の水の脱塩処理方法。
The osmotic agent is an inorganic salt, and has a temperature sensitive drug mixing step in which a temperature sensitive drug having a lower critical temperature is mixed with the dilution attraction solution before the phase separation step, and is separated in the phase separation step. A fresh water recovery step for obtaining fresh water from the diluted solution is a heating step for heating the diluted solution to a temperature equal to or higher than the cloud point of the attracting solution, and a temperature mainly comprising a temperature-sensitive drug following the heating step. Having a second phase separation step of phase separation into a sensitive drug solution phase and a fresh water phase mainly containing fresh water and containing a small amount of temperature sensitive drug;
And when the flow rate difference between the diluted attracting solution and the attracting solution is lower than a preset value, the flow rate of the attracting solution is increased and the heating temperature in the warming step is increased. 2. The method according to claim 1, wherein when the flow rate difference is higher than a preset value, the flow rate of the attracting solution is decreased and the heating temperature in the heating step is decreased. Water desalination method.
塩類を含有する被処理水と、浸透圧剤を水に溶解し前記被処理水よりも浸透圧の高い誘引溶液とを半透膜を介して接触させ、前記被処理水中の水を前記半透膜を通して前記誘引溶液に移動させ、水で希釈された希釈誘引溶液と膜濃縮水を得る正浸透膜処理装置と、
前記希釈誘引溶液を浸透圧剤を主体とする濃厚溶液相と、少量の浸透圧剤を含有する希薄溶液相とに相分離する相分離槽と、
前記相分離槽で分離された濃厚溶液を前記正浸透膜処理装置へ循環し、誘引溶液として再使用する循環手段と、
前記相分離槽で分離された希薄溶液から淡水を得る淡水回収装置を有する水の脱塩処理装置であって、
前記希釈誘引溶液の流量測定手段と、前記誘引溶液の流量測定手段と、それらの流量測定手段により測定された前記希釈誘引溶液と前記誘引溶液との流量差と予め設定された前記流量差の設定値との較差に応じて、前記誘引溶液の流量を調整する流量調整手段を有することを特徴とする水の脱塩処理装置。
A treated water containing salts and an attracting solution having an osmotic agent dissolved in water and having a higher osmotic pressure than the treated water are brought into contact with each other through a semipermeable membrane, and the water in the treated water is brought into contact with the semipermeable material. A forward osmosis membrane treatment device that moves to the attraction solution through a membrane to obtain a diluted attraction solution diluted with water and membrane concentrated water;
A phase separation tank for phase-separating the diluted attraction solution into a concentrated solution phase mainly composed of an osmotic agent and a dilute solution phase containing a small amount of an osmotic agent;
A circulating means for circulating the concentrated solution separated in the phase separation tank to the forward osmosis membrane treatment apparatus and reusing it as an attraction solution;
A water desalination apparatus having a fresh water recovery device for obtaining fresh water from a dilute solution separated in the phase separation tank,
The flow rate measuring means for the diluted attracting solution, the flow rate measuring means for the attracting solution, the flow rate difference between the diluted attracting solution and the attracting solution measured by the flow rate measuring means, and the preset flow rate difference setting. An apparatus for desalinating water, comprising flow rate adjusting means for adjusting the flow rate of the attracting solution according to a difference from the value.
前記浸透圧剤が下限臨界温度を有する温度感応性薬剤であり、前記相分離槽の前段に前記希釈誘引溶液を前記誘引溶液の曇点以上の温度まで加温する加温手段を有しており、かつ前記較差に応じて、前記加温手段による加温温度を調整する加温温度調整手段も有することを特徴とする請求項4に記載の水の脱塩処理装置。   The osmotic agent is a temperature-sensitive agent having a lower critical temperature, and has a heating means for heating the dilution attraction solution to a temperature equal to or higher than the cloud point of the attraction solution at the front stage of the phase separation tank. The water desalination apparatus according to claim 4, further comprising a heating temperature adjusting unit that adjusts a heating temperature of the heating unit according to the difference. 前記浸透圧剤が無機塩であり、前記相分離槽の前段で前記希釈誘引溶液に下限臨界温度を有する温度感応性薬剤を混合する温度感応性薬剤混合手段を有するとともに、前記相分離槽で分離された希薄溶液から淡水を得る淡水回収装置が、前記希薄溶液を前記誘引溶液の曇点以上の温度まで加温する加温手段と、前記加温手段の後段に温度感応性薬剤を主体とする温度感応性薬剤溶液相と、淡水を主体とし少量の温度感応性薬剤を含有する淡水相とに相分離する第2相分離槽を有しており、
かつ、前記較差に応じて、前記加温手段による加温温度を調整する加温温度調整手段も有することを特徴とする請求項4に記載の水の脱塩処理装置。
The osmotic agent is an inorganic salt, and has a temperature-sensitive drug mixing means for mixing a temperature-sensitive drug having a lower critical temperature to the dilution-attracting solution in the previous stage of the phase separation tank, and is separated in the phase separation tank. A fresh water recovery device for obtaining fresh water from the diluted solution, comprising a heating means for heating the diluted solution to a temperature equal to or higher than a cloud point of the attracting solution, and a temperature-sensitive drug in the subsequent stage of the heating means. Having a second phase separation tank for phase separation into a temperature sensitive drug solution phase and a fresh water phase mainly containing fresh water and containing a small amount of temperature sensitive drug;
5. The water desalination apparatus according to claim 4, further comprising a heating temperature adjusting means for adjusting a heating temperature by the heating means in accordance with the difference.
JP2015184887A 2015-09-18 2015-09-18 Water desalination method and apparatus Expired - Fee Related JP6414528B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2015184887A JP6414528B2 (en) 2015-09-18 2015-09-18 Water desalination method and apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2015184887A JP6414528B2 (en) 2015-09-18 2015-09-18 Water desalination method and apparatus

Publications (2)

Publication Number Publication Date
JP2017056424A JP2017056424A (en) 2017-03-23
JP6414528B2 true JP6414528B2 (en) 2018-10-31

Family

ID=58389563

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2015184887A Expired - Fee Related JP6414528B2 (en) 2015-09-18 2015-09-18 Water desalination method and apparatus

Country Status (1)

Country Link
JP (1) JP6414528B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US11612860B2 (en) * 2016-08-22 2023-03-28 Trevi Systems Inc. Osmotic fluid purification and draw compounds thereof
JP6973229B2 (en) * 2018-03-27 2021-11-24 Jfeエンジニアリング株式会社 Water treatment equipment and how to start it
JP7575965B2 (en) * 2021-02-25 2024-10-30 三菱重工業株式会社 Water treatment equipment

Family Cites Families (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5433633B2 (en) * 2011-06-06 2014-03-05 株式会社日立製作所 Seawater desalination system using forward osmosis membrane
JP5975821B2 (en) * 2012-09-27 2016-08-23 シャープ株式会社 Desalination system
JP6149626B2 (en) * 2013-09-12 2017-06-21 Jfeエンジニアリング株式会社 Water treatment method with semipermeable membrane
JP6149627B2 (en) * 2013-09-12 2017-06-21 Jfeエンジニアリング株式会社 Water treatment method with semipermeable membrane
JP6465301B2 (en) * 2015-08-12 2019-02-06 Jfeエンジニアリング株式会社 Water desalination equipment

Also Published As

Publication number Publication date
JP2017056424A (en) 2017-03-23

Similar Documents

Publication Publication Date Title
JP6495207B2 (en) Recovery of retrograde solubility solutes for forward osmosis water treatment
JP2014512951A5 (en)
JP6376926B2 (en) Forward osmosis membrane separation method, water treatment facility and power generation facility
JP6149627B2 (en) Water treatment method with semipermeable membrane
JP6149626B2 (en) Water treatment method with semipermeable membrane
JP6414528B2 (en) Water desalination method and apparatus
JP6028645B2 (en) Water treatment equipment
JP6210033B2 (en) Water desalination method and apparatus
JP2015192979A (en) Water treatment equipment with semipermeable membrane
CN107108278A (en) The method and system of water purifying is permeated for Driven by Solar Energy
JP6465301B2 (en) Water desalination equipment
JP6463620B2 (en) Desalination system and desalination method
JP6210034B2 (en) Water desalination method and apparatus
JP2014100692A (en) Water treatment method
JP6210008B2 (en) Water treatment equipment
JP7106465B2 (en) Water treatment system and water treatment method
JP6974797B2 (en) Forward osmosis water treatment method and equipment
JP2015037771A (en) Water treatment method
JP2022129708A (en) Forward osmosis water treatment apparatus and method
JP2021035656A (en) Forward osmosis water treatment method and apparatus
JP2020142162A (en) Forward osmosis water treatment method and equipment
JP6447477B2 (en) Water desalination equipment
JP6210011B2 (en) Water treatment method and apparatus
JP2022129707A (en) Method and apparatus for purifying temperature-sensing agent aqueous solution used in forward osmosis water treatment
JP2016010767A (en) Water treatment apparatus

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20180124

TRDD Decision of grant or rejection written
A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20180829

A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20180905

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20180918

R150 Certificate of patent or registration of utility model

Ref document number: 6414528

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150

S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

LAPS Cancellation because of no payment of annual fees