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JPS6359725B2 - - Google Patents
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JPS6359725B2 - - Google Patents

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Publication number
JPS6359725B2
JPS6359725B2 JP59024721A JP2472184A JPS6359725B2 JP S6359725 B2 JPS6359725 B2 JP S6359725B2 JP 59024721 A JP59024721 A JP 59024721A JP 2472184 A JP2472184 A JP 2472184A JP S6359725 B2 JPS6359725 B2 JP S6359725B2
Authority
JP
Japan
Prior art keywords
tank
water
electrodialysis
concentration
intermediate concentration
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
Application number
JP59024721A
Other languages
Japanese (ja)
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JPS60168504A (en
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Filing date
Publication date
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Priority to JP59024721A priority Critical patent/JPS60168504A/en
Publication of JPS60168504A publication Critical patent/JPS60168504A/en
Publication of JPS6359725B2 publication Critical patent/JPS6359725B2/ja
Granted legal-status Critical Current

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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

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  • Separation Using Semi-Permeable Membranes (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Description

【発明の詳細な説明】 〔発明の利用分野〕 本発明は太陽光発電電気透析装置による塩水の
淡水化方法に係り、特に太陽の日射量が変動して
も太陽電池の出力を高効率で塩水の淡水化に使用
するのに好適な太陽光発電電気透析装置による塩
水あるいは海水の淡水化方法に関する。
[Detailed Description of the Invention] [Field of Application of the Invention] The present invention relates to a method for desalinating salt water using a photovoltaic electrodialysis device, and in particular, the output of a solar cell can be used to desalinate salt water with high efficiency even when the amount of solar radiation changes. The present invention relates to a method for desalinating salt water or seawater using a solar-powered electrodialysis device suitable for use in desalinating water.

〔発明の背景〕[Background of the invention]

電気透析法は電解質溶液たとえば海水に対し電
位差を与え、異符号イオンに選択性をもつイオン
交換膜を用い電解質の濃縮および希釈を行う方法
である。この方法は、海水(塩水)の前処理が
簡単であること、イオン交換膜の強度が大きい
こと、運転の操業性が低いことなどの特性を有
することから、中小容量の海水を淡水化するのに
適している。
Electrodialysis is a method in which a potential difference is applied to an electrolyte solution, such as seawater, and an ion exchange membrane that is selective to ions of opposite sign is used to concentrate and dilute the electrolyte. This method has the characteristics of easy pretreatment of seawater (salt water), high strength of the ion exchange membrane, and low operability, so it is suitable for desalinating small and medium volumes of seawater. suitable for

近年、塩水(海水)を淡水化する電気透析装置
においては、高温での運転技術の確立および新構
造の開発などの新技術の出現により著しい性能の
向上が見られる。
In recent years, the performance of electrodialysis equipment for desalinating salt water (seawater) has significantly improved due to the establishment of high-temperature operation technology and the emergence of new technologies such as the development of new structures.

一方、太陽電池は新エネルギーとして有望視さ
れ精力的な研究が進められてその性能向上と製造
コストの低減に目覚ましいものがある。
On the other hand, solar cells are seen as a promising new energy source and are being actively researched, with remarkable improvements in performance and reductions in manufacturing costs.

ところで、中近東地域を始めとし一般に太陽エ
ネルギーに恵まれた地域では水資源に恵まれない
場合が多く、水質源を確保する対策に苦慮してい
るのが現状である。そこで、これらの地域におい
ては太陽エネルギーを利用した海水淡水化に関心
が集つている。特に、太陽電池を電源として海水
を淡水化する電気透析装置は最近の技術革新を反
映して有力視されている。
By the way, regions that are generally blessed with solar energy, such as the Middle East, are often poor in water resources, and are currently struggling to take measures to secure water sources. Therefore, interest in seawater desalination using solar energy is gathering in these regions. In particular, electrodialysis equipment that uses solar cells as a power source to desalinate seawater is considered to be a promising technology, reflecting recent technological innovations.

このような太陽電池と電気透析装置を組合せた
海水淡水化装置においては、電気透析に直流電
源を分離エネルギーとして使用するため、太陽電
池の出力を直接利用することができること、太
陽熱を利用して電気透析装置を高温で運転するこ
とにより消費出力が低減できるという利点を有し
ている。従つて、太陽熱と太陽光とを同時に利用
するプロセスが確立できるという利点がある。
In such seawater desalination equipment that combines solar cells and electrodialysis equipment, DC power is used as separated energy for electrodialysis, so the output of the solar cells can be used directly, and solar heat can be used to generate electricity. Operating the dialysis machine at high temperatures has the advantage of reducing power consumption. Therefore, there is an advantage that a process that utilizes solar heat and sunlight simultaneously can be established.

ところで、太陽電池の出力は太陽の日射量が変
動するのに伴つて大きく変動する。このように変
動する電力を効率よく活用することは、電気透析
装置に限らず、太陽電池の負荷となる種種の装置
に対して課せられた課題である。幸にして、淡水
化装置においては淡水を貯蔵することができるた
め、日中のみ運転する方式を採用することができ
る。特に電気透析法では運転―停止が容易である
と共に、イオン交換膜が海水中の微生物に対して
強いため、夜間の停止中においても、特別な配慮
をする必要がない。したがつて、現状の太陽光発
電電気透析装置による海水淡水化方法の課題とし
ては、日射量の変動に対応して大きく変動する太
陽電池の出力をどのように効率よく活用するかに
ある。
By the way, the output of a solar cell varies greatly as the amount of solar radiation changes. Efficiently utilizing fluctuating power in this way is a challenge not only for electrodialyzers but also for various types of devices that serve as a load for solar cells. Fortunately, desalination plants can store fresh water, so they can be operated only during the day. In particular, the electrodialysis method is easy to start and stop, and the ion exchange membrane is resistant to microorganisms in seawater, so there is no need to take special precautions even when the system is stopped at night. Therefore, the problem with current seawater desalination methods using photovoltaic electrodialysis equipment is how to efficiently utilize the output of the solar cells, which fluctuates widely in response to changes in the amount of solar radiation.

従来、この技術課題を解決する方法としては、
鉛蓄電池を用いて電力変動を平滑化する方法が提
案されている(昭和56年度サンシヤイン計画委託
調査研究成果報告書「太陽エネルギーシステムの
研究」)。
Conventionally, the methods to solve this technical problem were as follows:
A method of smoothing power fluctuations using lead-acid batteries has been proposed (FY 1981 Sunshine Project Commissioned Research Results Report ``Research on Solar Energy Systems'').

しかし、この従来方法では、高価な鉛蓄電池が
多量に必要となると共に、その保守および管理が
容易でないのに加えて、蓄電池における充放電と
もなう電力効率の低下が大きいという問題点を有
していた。
However, this conventional method requires a large amount of expensive lead-acid batteries, is not easy to maintain and manage, and has the problems of a significant drop in power efficiency as the batteries charge and discharge. .

〔発明の目的〕[Purpose of the invention]

本発明の目的は、太陽の日射量に伴つて大きく
変動する太陽電池の出力を高効率で電気透析装置
の運転に利用することができる太陽光発電電気透
析装置による塩水の淡水化方法を提供するにあ
る。
An object of the present invention is to provide a method for desalinating salt water using a solar-powered electrodialysis device, in which the output of a solar cell, which varies greatly depending on the amount of solar radiation, can be used with high efficiency to operate the electrodialysis device. It is in.

〔発明の概要〕[Summary of the invention]

本発明の特徴は、太陽の日射量に応じた太陽電
池の特性を考慮して被脱塩処理水の塩濃度を日射
量に対応して調整させて太陽電池の最大出力で電
気透析装置を運転し海水を淡水化することにあ
る。
The feature of the present invention is to operate the electrodialysis machine at the maximum output of the solar cells by adjusting the salt concentration of the water to be desalinated in accordance with the amount of solar radiation, taking into account the characteristics of the solar cells depending on the amount of solar radiation. The goal is to desalinate seawater.

すなわち、本発明は、太陽電池を電源として塩
水を脱塩する電気透析装置に対して淡水槽と中間
濃度槽の2つの循環槽を設け、前記太陽電池の高
出力時に前記中間濃度槽と前記電気透析装置とを
用いて原水を中間濃度まで脱塩し、該中間濃度槽
から脱塩水を前記淡水化槽に移送し、前記太陽電
池の低出力時に該脱塩水を前記淡水化槽と前記電
気透析装置とを用いて淡水濃度まで脱塩すること
を特徴とするものであり、またこれに加えて、該
中間濃度槽に原水を添加して塩濃度を調整するこ
とを特徴とするものである。
That is, the present invention provides two circulation tanks, a freshwater tank and an intermediate concentration tank, for an electrodialysis device that desalinates salt water using a solar cell as a power source, and when the solar cell has a high output, the intermediate concentration tank and the electricity The desalinated water is desalinated to an intermediate concentration using a dialysis device, and the desalinated water is transferred from the intermediate concentration tank to the desalination tank, and when the output of the solar cell is low, the desalinated water is transferred to the desalination tank and the electrodialysis tank. This method is characterized by desalting to a freshwater concentration using a device, and in addition to this, raw water is added to the intermediate concentration tank to adjust the salt concentration.

第1図は太陽の日射量に対する太陽電池の出力
電圧と出力電流との関係を示す発電特性図、第2
図は電気透析槽(電気抵抗R)を太陽電池の負荷
として供した場合の等価回路図であつて、1は太
陽電池であつて、太陽電池1には広範囲に抵抗R
が変化する電気透析槽2が連設されている。
Figure 1 is a power generation characteristic diagram showing the relationship between the output voltage and output current of a solar cell with respect to the amount of solar radiation.
The figure is an equivalent circuit diagram when an electrodialysis tank (electrical resistance R) is used as a load for a solar cell.
Electrodialyzers 2 with varying values are connected in series.

種々の日射量における電圧Eiと電流Iiの特性は
第1図の実線で示されている。図中の破線は最大
電力が得られる条件であつて、実線と破線の交点
が各々日射量に対する最大出力条件(電圧および
電流値すなわち最適負荷抵抗値)である。
The characteristics of voltage E i and current I i at various amounts of solar radiation are shown by solid lines in FIG. The broken lines in the figure are the conditions under which the maximum power can be obtained, and the intersections of the solid lines and the broken lines are the maximum output conditions (voltage and current values, ie, optimum load resistance values) for each amount of solar radiation.

日射量に対する最大出力条件でのEiは第1図に
示す如く各日射量により略一定であり、日射量の
変動に伴つて出力電流値Iiが大きく変動する。
E i under the maximum output condition with respect to the amount of solar radiation is approximately constant depending on the amount of solar radiation as shown in FIG. 1, and the output current value I i varies greatly as the amount of solar radiation changes.

以上のように、太陽電池を効率よく使用するた
めには、負荷抵抗すなわち電気透析槽の電気抵抗
Rを日射量に応じて変化させて最大効率の電圧―
電流の条件を維持することが必要である。
As mentioned above, in order to use solar cells efficiently, it is necessary to change the load resistance, that is, the electrical resistance R of the electrodialysis tank according to the amount of solar radiation, and to obtain the maximum efficiency voltage -
It is necessary to maintain current conditions.

第3図A,B,C,Dは最大効率を得るための
条件を模式的に説明する線図である。
FIGS. 3A, B, C, and D are diagrams schematically explaining conditions for obtaining maximum efficiency.

A図には時刻の経過に伴う日射量Wの変化の一
般的な一例が示されている。日射量Wの小さい日
の出および日没に近い時刻にはB図に示すように
負荷抵抗(電気透析槽の電気抵抗R)を大きく
し、一方、日射量Wが大きくなる正午近くの時刻
においては負荷抵抗Rを小さくすることにより、
最大出力特性を維持することができる。
Figure A shows a general example of changes in the amount of solar radiation W over time. At times near sunrise and sunset when the amount of solar radiation W is small, the load resistance (electrical resistance R of the electrodialysis tank) is increased as shown in Figure B, while at times near noon when the amount of solar radiation W is large, the load resistance By reducing the resistance R,
Maximum output characteristics can be maintained.

第6図C,Dに最大出力特性時における電圧Ei
および電流Iiの変化を示す。すなわち、最大出力
効率を得るには、各時刻においてRi=Ei/Iiを満
足する電気透析槽の電気抵抗Riを実現する必要が
ある。この電気透析槽の電気抵抗値Riは電気透析
槽に循環させて淡水化する被脱塩処理水の塩濃度
Cに左右される。
Figure 6 C and D show the voltage E i at maximum output characteristics.
and shows the change in current I i . That is, in order to obtain the maximum output efficiency, it is necessary to realize the electrical resistance R i of the electrodialysis tank that satisfies R i =E i /I i at each time. The electrical resistance value R i of this electrodialysis tank depends on the salt concentration C of the water to be desalinated which is circulated through the electrodialysis tank for desalination.

第4図は被処理水の塩濃度Cすなわち電気透析
槽内に流通する液の塩濃度C%と電気透析槽の電
気抵抗Rとの関係を示す線である。ここで被脱塩
処理水の塩濃度C%は、正確には電気透析槽の入
口と出口における塩濃度の対数平均値である。
FIG. 4 is a line showing the relationship between the salt concentration C of the water to be treated, that is, the salt concentration C% of the liquid flowing in the electrodialysis tank, and the electrical resistance R of the electrodialysis tank. Here, the salt concentration C% of the water to be desalted is precisely the logarithmic average value of the salt concentrations at the inlet and outlet of the electrodialyzer.

この関係線図は、電気透析槽の構造がイオン交
換膜の1枚当りの有効面積を0.23m2、イオン交換
膜の対数を200対とし、イオン交換膜の間隔を0.8
mmとして、食塩を主成分とする塩類水溶液を常温
で脱塩処理する場合の一例を示すものである。こ
の塩濃度と電気透析装置の電気抵抗Rとの関係は
電気透析槽の構造により一義的に定まるものであ
る。たとえば、約3.5%塩濃度の海水を0.05%の
淡水に脱塩する過程では電気透析槽の電気抵抗R
は、0.7Ωから14Ωまで双曲線状に大きく変化す
る。
This relationship diagram shows that the structure of the electrodialysis tank is such that the effective area of each ion exchange membrane is 0.23 m 2 , the number of logarithms of ion exchange membranes is 200, and the spacing between the ion exchange membranes is 0.8.
An example is shown in which mm is used to desalinate an aqueous salt solution containing common salt as the main component at room temperature. The relationship between this salt concentration and the electrical resistance R of the electrodialysis device is uniquely determined by the structure of the electrodialysis tank. For example, in the process of desalinating seawater with a salt concentration of about 3.5% to freshwater with a salt concentration of 0.05%, the electrical resistance R of an electrodialysis tank is
changes greatly in a hyperbolic manner from 0.7Ω to 14Ω.

そこで、電気透析装置を最大効率で運転する方
法として、電気透析槽に流通させる被脱塩処理水
の塩濃度を変化させて、第3図Bに示した最大出
力の負荷抵抗Rになるように電気透析槽の電気抵
抗を調整し、太陽電池の最大効率の特性を得る方
法が考えられる。この方法は太陽電池の低出力時
に低塩濃度の被脱塩処理水(すなわち電気透析槽
の電気抵抗の高い領域)を電気透析槽に流通させ
る一方、太陽電池の高出力時に高塩濃度の被脱塩
処理水(すなわち電気透析槽の電気抵抗Rが低い
領域)を電気透析槽に流通させることにより電気
透析槽の運転条件と太陽電池の最大出力の時刻変
動とを一致させるものであ。
Therefore, as a method to operate the electrodialysis apparatus at maximum efficiency, the salt concentration of the water to be desalinated that flows through the electrodialysis tank is changed so that the load resistance R for the maximum output is achieved as shown in Figure 3B. One possible method is to adjust the electrical resistance of the electrodialyzer to obtain the maximum efficiency characteristics of the solar cell. In this method, when the output of the solar cell is low, the demineralized water with a low salt concentration (i.e., the area of high electrical resistance of the electrodialysis tank) is passed through the electrodialysis tank, while when the output of the solar cell is high, the water to be desalinated is passed through the electrodialysis tank. The operating conditions of the electrodialysis tank and the time fluctuations in the maximum output of the solar cell are made to match by flowing desalinated water (ie, the area where the electrical resistance R of the electrodialysis tank is low) through the electrodialysis tank.

ところで、従来の電気透析装置の代表的な運転
方法としては回分すなわち被脱塩処理水を循環槽
を介して電気透析槽に何度も循環させて所定の塩
濃度の淡水を得る方法が知られている。この運転
方法では電気透析槽に流通する被脱塩処理水の塩
濃度が経時的に変化するが、その塩濃度の経時変
化の模様は太陽電池出力の変動と全く無関係であ
る。したがつて、この回分運転方向では、単に太
陽電池の負荷として電気透析槽を直接的に結合し
たのみであり、日射量に伴う太陽電池の出力を効
率よく利用することができない。
By the way, as a typical operating method for conventional electrodialysis equipment, there is a known method in which batchwise, ie, desalinated water is circulated through an electrodialysis tank many times through a circulation tank to obtain fresh water with a predetermined salt concentration. ing. In this operating method, the salt concentration of the water to be desalinated flowing through the electrodialysis tank changes over time, but the pattern of the change in salt concentration over time is completely unrelated to fluctuations in the output of the solar cells. Therefore, in this batch operation direction, the electrodialysis tank is simply connected directly as a load to the solar cell, and the output of the solar cell that depends on the amount of solar radiation cannot be efficiently utilized.

これに対し、本発明は、電気透析槽に対して淡
水槽と中間濃度槽の2つの循環槽を並列に設け、
太陽電池の低出時と高出力時に2つの循環槽を使
い分けて被脱塩水の塩濃度を調整して回分運転す
ることにより、電気透析槽の運転条件と太陽電池
出力の時刻変動とを一致させて最大効率を得るよ
うにしたものである。また、太陽電池の高出力時
に予め前記中間濃度槽を用いて塩水を中間濃度ま
で脱塩すると共に、太陽電池の出力変動に対応し
て電気透析装置の最大効率で脱塩できるように中
間濃度槽に塩水を供給して塩濃度が調整してもよ
い。
In contrast, the present invention provides two circulation tanks, a freshwater tank and an intermediate concentration tank, in parallel to the electrodialysis tank,
By adjusting the salt concentration of the water to be desalinated and performing batch operation by separately using two circulation tanks when the output of the solar cells is low and when the output is high, it is possible to match the operating conditions of the electrodialysis tank with the time fluctuations of the output of the solar cells. It is designed to obtain maximum efficiency. In addition, when the solar cell output is high, the intermediate concentration tank is used to desalinate salt water to an intermediate concentration, and the intermediate concentration tank is also used to desalinate salt water to an intermediate concentration in response to fluctuations in the output of the solar cells. The salt concentration may be adjusted by supplying salt water.

次に、中間濃度槽を用いて脱塩された中間濃度
水を淡水槽に移注し、太陽電池の低出力時(たと
えば翌日の日の出以降)に淡水槽を用いて中間濃
度水を淡水濃度まで脱塩して淡水を得ることがで
きる。
Next, transfer the intermediate concentration water desalinated using the intermediate concentration tank to the fresh water tank, and use the fresh water tank to reduce the intermediate concentration water to fresh water concentration when the solar cell output is low (for example, after sunrise the next day). Fresh water can be obtained by desalination.

第5図は本発明の実施に用いる電気透析装置の
フローチヤートの一例を示す説明図である。
FIG. 5 is an explanatory diagram showing an example of a flowchart of an electrodialysis apparatus used for carrying out the present invention.

2は太陽電池の負荷となる電気透析槽であつ
て、この電気透析槽2の脱塩室に被脱塩処理水を
循環させる流路3,4が設けられ4には中間濃度
槽5と淡水槽6とが並列に連設されている。さら
に、中間濃度槽5および淡水槽6の上下管路には
バルブ7〜10がそれぞれ設けられている。また
中間濃度槽5の上方にバルブ11を介して原水を
供給する供給管12が設けられている。一方、中
間濃度槽5および淡水槽6の共通流路3の途中に
ポンプ13が設けられ、バルブ7〜10の開閉に
より中間濃度槽5又は淡水槽6内の被脱塩処理水
を電気透析槽2に循環できるように構成されてい
る。
Reference numeral 2 denotes an electrodialysis tank that serves as a load for the solar cell.Flow paths 3 and 4 for circulating the water to be desalinated are provided in the demineralization chamber of the electrodialysis tank 2. A water tank 6 is arranged in parallel. Further, valves 7 to 10 are provided in the upper and lower pipes of the intermediate concentration tank 5 and the fresh water tank 6, respectively. Further, a supply pipe 12 for supplying raw water via a valve 11 is provided above the intermediate concentration tank 5 . On the other hand, a pump 13 is provided in the middle of the common flow path 3 of the intermediate concentration tank 5 and the fresh water tank 6, and the water to be desalinated in the intermediate concentration tank 5 or the fresh water tank 6 is transferred to the electrodialysis tank by opening and closing valves 7 to 10. It is configured so that it can be circulated to 2.

また電気透析槽2の出口側の流路4は中間濃度
槽および淡水槽6と連結されていると共に、その
延長端はバルブ14を介して淡水タンク15に連
結されている。なお、電気透析槽2においては濃
縮水および極液に関する部分は省略した。
Further, the flow path 4 on the outlet side of the electrodialysis tank 2 is connected to an intermediate concentration tank and a fresh water tank 6, and its extended end is connected to a fresh water tank 15 via a valve 14. In addition, in the electrodialysis tank 2, the parts related to concentrated water and polar liquid are omitted.

次に、このように構成した装置を用いて本発明
法による塩水淡水化方法を説明する。
Next, a salt water desalination method according to the present invention will be explained using the apparatus configured as described above.

第6図A,B,Cは日の出から日没までの時刻
経過に沿つて本発明を応用した操業方法の一例を
説明する線図である。なお、図中のaは日の出時
刻、bは淡水槽から中間濃度槽に切換え操業する
時刻、cは南中時(12時)およびdは日没時刻で
ある。
FIGS. 6A, B, and C are diagrams illustrating an example of an operating method to which the present invention is applied along the passage of time from sunrise to sunset. Note that in the figure, a is the sunrise time, b is the time when the freshwater tank is switched to the intermediate concentration tank, c is the midday hour (12 o'clock), and d is the sunset time.

図において、先ず日の出(第6図中のa点)か
ら時間を経ない電池の低出力時には、第5図に示
したように前日に中間濃度槽において原水から中
間濃度にまで脱塩された中間濃度水のうち一日の
生成淡水量に相当する量を淡水槽6に移注し、バ
ルブ7,8を閉じると共に、バルブ9,10を開
いてポンプ13の作動により中間濃度水を電気透
析槽に移送し脱塩して、所定の濃度の淡水を得
る。
In the figure, first of all, when the battery output is low and time has not passed since sunrise (point a in Figure 6), the intermediate concentration that has been desalted from raw water to an intermediate concentration in the intermediate concentration tank the previous day, as shown in Figure 5, is Of the concentrated water, an amount equivalent to the amount of fresh water produced per day is transferred to the fresh water tank 6, valves 7 and 8 are closed, valves 9 and 10 are opened, and the pump 13 is activated to transfer the intermediate concentration water to the electrodialysis tank. and desalinate to obtain fresh water with a predetermined concentration.

この日の出から所定時間(a―b)を経過する
までの太陽電池の低出力時には塩濃度の低い中間
濃度水(すなわち電気透析槽の電気抵抗が高い)
を処理するので、第3図に示したように高い電力
利用効率を得ることができる。
When the output of the solar cells is low until a predetermined time (a-b) has elapsed from sunrise, intermediate concentration water with low salt concentration (that is, the electrical resistance of the electrodialysis tank is high)
As shown in FIG. 3, high power usage efficiency can be obtained.

処理により得られた淡水はバルブ10を閉じる
と共にバルブ14を開いてポンプ13の作動によ
り淡水タンク15に排出される。
The fresh water obtained by the treatment is discharged into a fresh water tank 15 by closing the valve 10 and opening the valve 14 and operating the pump 13.

次いでバルブ9,14を閉じ、バルブ7,8を
開いて中間濃度槽5内の中間濃度水をポンプ13
により電気透析槽に循環させて脱塩する。
Next, valves 9 and 14 are closed, valves 7 and 8 are opened, and the intermediate concentration water in the intermediate concentration tank 5 is pumped to the pump 13.
It is circulated to an electrodialysis tank for desalination.

この運転に入る時期は電池出力が大きく塩濃度
の高い水を処理するのに適している。
This period of operation is suitable for treating water with high battery output and high salt concentration.

さらに、太陽の南中時までは電池出力は増加す
る傾向にあるので、バルブ11を開き中間濃度槽
5に原水を供給して塩濃度が高くなるように調整
する。
Further, since the battery output tends to increase until the sun reaches its midpoint, the valve 11 is opened to supply raw water to the intermediate concentration tank 5 to adjust the salt concentration to be high.

すなわち、b―c間では電気透析槽2において
淡水化できる最大能力以上に原水を供給し、塩濃
度を経時的に増加させる。この塩濃度の経時変化
は電池の出力増加に対応させることが好ましい。
したがつて、原水の供給量は電池出力に連動して
バルブ11の開度を変えることによつて最適に調
整される。
That is, between b and c, raw water is supplied in an amount exceeding the maximum desalination capacity in the electrodialysis tank 2, and the salt concentration is increased over time. It is preferable that this change in salt concentration over time corresponds to an increase in the output of the battery.
Therefore, the amount of raw water supplied is optimally adjusted by changing the opening degree of the valve 11 in conjunction with the battery output.

南中時以降(第6図のC―D間)においては、
電池出力の低下に伴つて塩濃度が低下し、電池の
最大出力条件が自動的に成立する。このように日
没まで運転を続ければ、翌日の淡水槽6における
脱塩処理に供する中間濃度水を得ることができ
る。また、この運転においても、原水を必要に応
じて供給し、最適条件を厳密に管理することがで
きる。上記の運転によつて得られた中間濃度水の
一定量はバルブ10を開きバルブ8を閉じてポン
プ13により淡水槽6に送られ、翌日の脱塩処理
に供される。
After the mid-south hour (between C and D in Figure 6),
As the battery output decreases, the salt concentration decreases, and the battery's maximum output condition is automatically established. If the operation is continued until sunset in this manner, intermediate concentration water can be obtained for desalination treatment in the fresh water tank 6 the next day. In addition, in this operation as well, raw water can be supplied as needed and optimal conditions can be strictly controlled. A certain amount of intermediate concentration water obtained by the above operation is sent to the freshwater tank 6 by the pump 13 with the valve 10 opened and the valve 8 closed, and is subjected to desalination treatment on the next day.

以下、本発明を実施例によりさらに詳細に説明
する。
Hereinafter, the present invention will be explained in more detail with reference to Examples.

実施例 1 太陽光電池の出力特性をシミユレートした直流
電源を用いて本発明法を実施し、3.5%食塩水溶
液を塩濃度500ppmまで脱塩した。電気透析槽と
しては第4図に示した電気透析槽の電気抵抗特性
と同じイオン交換膜1枚当たりの通電面積を0.23
m2とし、イオン交換膜の対数を200対としたもの
を使用した。運転開始時には淡水槽に0.35%食塩
水溶液を4.2m3を導入し、中間濃度槽に同濃度の
食塩水溶液1.4m3を供給した。直流電源の出力は
最大出力を10kWとし、周期を16時間の正弦波と
し最初の8時間で電気透析装置を運転した。
Example 1 The method of the present invention was carried out using a DC power supply that simulated the output characteristics of a solar cell, and a 3.5% saline solution was desalted to a salt concentration of 500 ppm. As an electrodialysis tank, the current carrying area per ion exchange membrane is 0.23, which is the same as the electrical resistance characteristic of the electrodialysis tank shown in Figure 4.
m 2 and the number of logarithms of the ion exchange membrane was 200. At the start of operation, 4.2 m 3 of 0.35% saline solution was introduced into the freshwater tank, and 1.4 m 3 of the same concentration saline solution was supplied to the intermediate concentration tank. The maximum output of the DC power supply was 10 kW, the period was a sine wave of 16 hours, and the electrodialysis device was operated for the first 8 hours.

第7図A,B,Cは周期時間に対する電気透析
特性を示す線図であつて、A図は時間と太陽電池
の発電量(kW)および電気透析に消費される電
力との関係、Bは淡水槽および中間濃度槽におけ
る被処理塩水の塩濃度変化、C図は電気透析槽の
電力利用効率を示す線図である。
Figures 7A, B, and C are diagrams showing electrodialysis characteristics with respect to cycle time, where Figure A is the relationship between time, the amount of power generated by the solar cell (kW), and the power consumed for electrodialysis, and Figure B is the relationship between time, the amount of power generated by the solar cell (kW), and the power consumed for electrodialysis. Changes in the salt concentration of the salt water to be treated in the freshwater tank and the intermediate concentration tank, and Figure C is a diagram showing the power utilization efficiency of the electrodialysis tank.

図から明らかなように、運転開始後1時間55分
後に淡水槽中の水の塩濃度は500ppmとなり、続
く中間濃度槽の運転では(運転開始から)4時間
まで3.5%食塩水溶液を直流電源出力に対応して
添加した。8時間後(運転開始から)における中
間濃度槽中の水の塩濃度は運転開始時と同じ0.35
%にまで低下した。運転中の電力利用効率は、C
図に示すように淡水槽運転終了の直前で低下する
以外は高く維持され、平均91%が得られた。
As is clear from the figure, the salt concentration of the water in the fresh water tank reached 500 ppm 1 hour and 55 minutes after the start of operation, and in the subsequent operation of the intermediate concentration tank, a 3.5% saline solution was output from the DC power supply for up to 4 hours (from the start of operation). Added accordingly. After 8 hours (from the start of operation), the salt concentration of the water in the intermediate concentration tank is 0.35, the same as at the start of operation.
%. The power usage efficiency during operation is C
As shown in the figure, it remained high except for a drop just before the end of freshwater tank operation, and an average of 91% was obtained.

実施例 2 実施例1と同じ直流電源出力を用いて電気透析
装置を従来の回分運転法により食塩水溶液を脱塩
した。この回分運転では、脱塩水槽及び濃縮水槽
を設け各水槽からそれぞれ電気透析槽の脱塩室及
び濃縮室に塩類水溶液を循環させて、脱塩水槽中
の水の塩濃度が淡水濃度まで低下すると、その淡
水を抜き出し、新たな被処理水を循環させる一般
的な方法を採用した。原水として3.5%食塩水溶
液を脱塩水槽に0.8m3導入し、淡水濃度が500ppm
になるまで回分運転(6回)を行つた。
Example 2 Using the same DC power output as in Example 1, an electrodialysis apparatus was operated in a conventional batch manner to desalinate a saline solution. In this batch operation, a desalination water tank and a concentration water tank are provided, and an aqueous salt solution is circulated from each tank to the desalination chamber and concentration chamber of the electrodialysis tank, respectively, and when the salt concentration of the water in the desalination tank is reduced to the freshwater concentration, , we adopted a common method of extracting the fresh water and circulating new water to be treated. Introduce 0.8 m3 of 3.5% saline solution as raw water into the desalination water tank, and the freshwater concentration is 500 ppm.
Batch operation (6 times) was carried out until .

その結果は第7図A,Bに示す通りである。 The results are shown in FIGS. 7A and 7B.

各回分運転中において第8図Bに示すように必
ず一度は約100%の電力利用効率を示すが、低い
電力利用効率を示す時間が圧倒的に長いため、8
時間の運転における平均電力利用効率は66%であ
つた。従来の回分方法では本発明法(実施例1)
に比べて著しく電力利用効率が低いことが判明し
た。
During each batch operation, as shown in Figure 8B, the power usage efficiency is always approximately 100% once, but the time when the power usage efficiency is low is overwhelmingly long.
The average power usage efficiency during hourly operation was 66%. In the conventional batch method, the method of the present invention (Example 1)
It was found that the power usage efficiency was significantly lower than that of the conventional method.

〔発明の効果〕〔Effect of the invention〕

本発明によれば、変動する太陽電池の出力を効
率よく用いることができるので、淡水化効率を高
くできると云う優れた効果がある。
According to the present invention, since the fluctuating output of the solar cell can be used efficiently, there is an excellent effect that the desalination efficiency can be increased.

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

第1図は太陽電池の発電特性を示す電圧―電流
特性線図、第2図は太陽電池による電気透析装置
の等価回路図、第3図は太陽電池の最大出力での
使用条件を示す模式図、第4図は電気透析装置を
循環する被処理水の塩濃度と電気透析槽の電気抵
抗との関係を示す線図、第5図は本発明法による
電気透析装置のフローチヤート図、第6図A,
B,Cは本発明による運転内容を示す線図、第7
図A,B,Cは本発明の実施例による運転結果を
示す線図、第8図は従来の回分法による運転結果
を示す線図である。 1…太陽電池、2…電気透析槽、5…中間濃度
槽、6…淡水槽、7〜10…バルブ、13…ポン
プ。
Figure 1 is a voltage-current characteristic diagram showing the power generation characteristics of solar cells, Figure 2 is an equivalent circuit diagram of an electrodialysis device using solar cells, and Figure 3 is a schematic diagram showing the operating conditions of solar cells at their maximum output. , FIG. 4 is a diagram showing the relationship between the salt concentration of the water to be treated circulating through the electrodialysis apparatus and the electrical resistance of the electrodialysis tank, FIG. 5 is a flowchart of the electrodialysis apparatus according to the method of the present invention, and FIG. Figure A,
B and C are diagrams showing operation details according to the present invention, No. 7
Figures A, B, and C are diagrams showing the results of operation according to the embodiment of the present invention, and Fig. 8 is a diagram showing the results of operation according to the conventional batch method. DESCRIPTION OF SYMBOLS 1...Solar cell, 2...Electrodialysis tank, 5...Intermediate concentration tank, 6...Fresh water tank, 7-10...Valve, 13...Pump.

Claims (1)

【特許請求の範囲】 1 太陽電池を電源として塩水を脱塩する電気透
析装置に対して淡水槽と中間濃度槽の2つの循環
槽を設け、前記太陽電池の高出力時に前記中間濃
度槽と前記電気透析装置とを用いて原水を中間濃
度まで脱塩し、該中間濃度槽から脱塩水を前記淡
水化槽に移送し、前記太陽電池の低出力時に該脱
塩水を前記淡水化槽と前記電気透析装置とを用い
て淡水濃度まで脱塩することを特徴とする塩水淡
水化方法。 2 太陽電池を電源として塩水を脱塩する電気透
析装置に対して淡水槽と中間濃度槽の2つの循環
槽を設け、前記太陽電池の高出力時に前記中間濃
度槽と前記電気透析装置とを用いて原水を中間濃
度まで脱塩すると共に該中間濃度槽に原水を添加
して塩濃度を調整し、該中間濃度槽から脱塩水を
前記淡水化槽に移送し、前記太陽電池の低出力時
に該脱塩水を前記淡水化槽と前記電気透析装置と
を用いて淡水濃度まで脱塩することを特徴とする
塩水淡水化方法。
[Scope of Claims] 1. Two circulation tanks, a fresh water tank and an intermediate concentration tank, are provided for an electrodialysis apparatus that desalinates salt water using a solar cell as a power source, and when the solar cell has a high output, the intermediate concentration tank and the The raw water is desalinated to an intermediate concentration using an electrodialysis device, and the desalinated water is transferred from the intermediate concentration tank to the desalination tank, and when the output of the solar cell is low, the desalinated water is connected to the desalination tank and the electricity. A saltwater desalination method characterized by desalting to a freshwater concentration using a dialysis device. 2. Two circulation tanks, a fresh water tank and an intermediate concentration tank, are provided for an electrodialysis device that desalinates salt water using a solar cell as a power source, and the intermediate concentration tank and the electrodialysis device are used when the solar cell has a high output. The raw water is desalinated to an intermediate concentration, and the raw water is added to the intermediate concentration tank to adjust the salt concentration, and the desalted water is transferred from the intermediate concentration tank to the desalination tank. A method for desalinating salt water, characterized in that desalinated water is desalinated to a freshwater concentration using the desalination tank and the electrodialysis device.
JP59024721A 1984-02-13 1984-02-13 Salt water desalination method Granted JPS60168504A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59024721A JPS60168504A (en) 1984-02-13 1984-02-13 Salt water desalination method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59024721A JPS60168504A (en) 1984-02-13 1984-02-13 Salt water desalination method

Publications (2)

Publication Number Publication Date
JPS60168504A JPS60168504A (en) 1985-09-02
JPS6359725B2 true JPS6359725B2 (en) 1988-11-21

Family

ID=12146019

Family Applications (1)

Application Number Title Priority Date Filing Date
JP59024721A Granted JPS60168504A (en) 1984-02-13 1984-02-13 Salt water desalination method

Country Status (1)

Country Link
JP (1) JPS60168504A (en)

Families Citing this family (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6157208A (en) * 1984-08-29 1986-03-24 Hitachi Ltd Salt water desalination method
JPH01288391A (en) * 1988-05-17 1989-11-20 Agency Of Ind Science & Technol Method and apparatus for treatment of waste water
CN113060805A (en) * 2021-04-01 2021-07-02 山东大学 A carbon fiber solar water purifier and a method for treating heavy metal sewage
US11502322B1 (en) 2022-05-09 2022-11-15 Rahul S Nana Reverse electrodialysis cell with heat pump
US11502323B1 (en) 2022-05-09 2022-11-15 Rahul S Nana Reverse electrodialysis cell and methods of use thereof
US12040517B2 (en) 2022-11-15 2024-07-16 Rahul S. Nana Reverse electrodialysis or pressure-retarded osmosis cell and methods of use thereof
US11855324B1 (en) 2022-11-15 2023-12-26 Rahul S. Nana Reverse electrodialysis or pressure-retarded osmosis cell with heat pump
JP2025538227A (en) 2022-11-15 2025-11-26 エス ナナ,ラフル Reverse electrodialysis or pressure retarded osmosis cell and method of use thereof
CN119929991B (en) * 2025-03-17 2025-10-31 中国科学院生态环境研究中心 Electric coupling range-extending solar drive target selective electrodialysis method and device

Also Published As

Publication number Publication date
JPS60168504A (en) 1985-09-02

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