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JPH0225672B2 - - Google Patents
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JPH0225672B2 - - Google Patents

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Publication number
JPH0225672B2
JPH0225672B2 JP58085681A JP8568183A JPH0225672B2 JP H0225672 B2 JPH0225672 B2 JP H0225672B2 JP 58085681 A JP58085681 A JP 58085681A JP 8568183 A JP8568183 A JP 8568183A JP H0225672 B2 JPH0225672 B2 JP H0225672B2
Authority
JP
Japan
Prior art keywords
seawater
make
final stage
temperature
evaporator
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Lifetime
Application number
JP58085681A
Other languages
Japanese (ja)
Other versions
JPS59213488A (en
Inventor
Tadatsugu Hamada
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP58085681A priority Critical patent/JPS59213488A/en
Publication of JPS59213488A publication Critical patent/JPS59213488A/en
Publication of JPH0225672B2 publication Critical patent/JPH0225672B2/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

Landscapes

  • Degasification And Air Bubble Elimination (AREA)
  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

〔本発明の技術分野〕 本発明は、最終段脱気方式によるフラツシユ蒸
発型海水淡水化装置の脱気方法に関する。 〔背景技術〕 蒸発型海水淡水化装置(以下MSFという。)に
おいて、補給海水の脱酸素は装置の腐食防止の観
点から非常に重要である。脱酸素(以下脱気とい
う)プロセスには、(1)充填塔を用いた真空脱気方
式と、(2)最終段フラツシユ室(以下“最終段蒸発
缶”という。)で同時に脱気も行わせる最終段脱
気方式とがある。 両方式の性能を比較すると、一般に(2)の方式が
(1)の方式に比べて劣るといわれる。それは(2)の方
式の律速因子の理論的根拠が十分把握されていな
いため、現状では、両方式ともその脱ガス理論を
二重境膜説に立脚せざるを得ない。 〔従来の最終段脱気方式〕 ここで従来法による最終段脱気方式を第1図に
基づいて説明する。蒸発缶に流入する補給海水は
蒸発室1の熱放出部コンデンサー5を貫流する冷
却海水ライン4の熱回収部コンデンサー5の出口
4′から分岐して補給海水ライン6に流入する。
この補給海水は脱気用ノズル7により、蒸発缶最
終段蒸発缶内にスプレーされ、前段蒸発室から流
入した循環ブライン10と混合される。なお、図
中2はフラツシユ蒸発装置の熱回収部コンデンサ
ー5に給水する循環ポンプであり、3は或る一定
の濃度を保つための排出ポンプである。二重境膜
説による脱気の律速因子はO2分圧以外に気液接
触面積、膜厚および帯溜時間であるが、このフロ
ーでも流入する海水より最終段蒸発室内の温度が
高いため、補給海水の温度上昇によるO2濃度の
減少と、スプレー化による放散速度の増大があ
る。しかし滞溜時間が短かいため、別置きの真空
脱気塔方式の塔内均一噴霧と充填物による気液接
触面積および滞溜時間の増大を計つた場合に比べ
て最終段脱気方式の性能が劣るのはやむを得な
い。 以上のように最終段脱気方式を採用すると、確
かに別置きの真空脱気塔を必要とせず、大きなコ
ストダウンの要因にはなるが、反面性能が劣るた
め、蒸発缶体の構成材料の高級化は避け難くした
がつて、大きなコストアツプにつながることにな
る。 最近のMSF構成材料は一部を除いて銅合金、
ステンレス鋼、チタン等高級材料が選定されてい
るが、全て腐食防止のためである。MSFに発生
する腐食トラブルには炭素鋼の全面腐食、アルミ
青銅/チタン、ステンレス鋼/炭素鋼の電食、ス
テンレス鋼の応力腐食、孔食、伝熱管入口部のイ
ンレツトアタツク等があるが、これらは大部分溶
存酸素の除去によつて実用上防止可能である。こ
のため、安価でかつ十分な性能を発揮する脱気シ
ステムを開発することはMSFのコストダウンの
ため必須の要求である。 〔本発明の目的〕 本発明者は、従来の最終段脱気方式が二重境膜
説に基づくのではなく、フラツシユ蒸発環境では
水の蒸発が主要な律速因子になることに着目し、
その結果本発明を完成したものである。すなわ
ち、本発明は最終段脱気方式における脱気効率を
向上させたフラツシユ蒸発型海水淡水化装置の脱
気方法を提供することを目的とする。 〔本発明の構成〕 そして、本発明は上記目的を達成する手段とし
て、補給海水が最終段蒸発室に流入する前にこれ
を予熱するにある。すなわち、本発明は熱放出部
冷却海水の一部を補給海水として使用するフラツ
シユ蒸発型海水淡水化装置において、最終段蒸発
室に補給海水を流入するための補給海水ラインに
補給海水予熱器を設置し、補給海水温度を当該蒸
発缶内温度以上に上昇させた後蒸発缶内で脱気さ
せることを特徴とするフラツシユ蒸発型海水淡水
化装置の脱気方法である。 本発明においては、補給海水が最終段蒸発缶に
流入する前に、補給水予熱器を設け、当該最終段
蒸発缶でフラツシユ蒸発可能な温度だけ上昇させ
ることにより(例えば1〜2℃)、脱気の律速因
子を気液接触面積、帯溜時間からフラツシユ蒸発
に変更することにある。 本発明を第2図に基づいて詳細に説明する。第
2図は本発明のフローを示す。熱放出部は第1図
に示す従来法と同一であるが、補給海水ライン6
を通過する補給海水は、補給水予熱器8にて加熱
流体(蒸気又は熱水)と熱交換を行い、最終段蒸
発缶内温度より1〜2℃高い温度まで加熱され
る。 この加熱補給水が蒸発缶に流入してフラツシユ
蒸発しながら脱気され、前段から流入したブライ
ン温度まで低下する。 (1) 補給水予熱器 この予熱器8は熱回収部コンデンサー5を通
過した海水温度を最終段の蒸発室1で補給水が
フラツシユ蒸発するに十分高い温度まで上昇さ
せる作用をし、ここではマスバランスの変化、
相変化はない。 (2) 最終段フラツシユ室 予熱された海水は、ここでフラツシユ蒸発し
て温度が低下すると共に溶存酸素濃度も減少す
る。これらの関係式を(1)〜(13)に示す。 A マスバランス FT=FB+FE (1) FTCT=FBCB+FECE (2) ただし、FT:補給水入口流量〔Kg/h〕 FB:ブラインと混合する直前の流量
〔Kg/h〕 FE:補給水からの蒸発量〔Kg/h〕 CT:補給水脱気前の酸素濃度〔mol/Kg〕 CB:補給水脱気後の酸素濃度〔mol/Kg〕 CE:気相に放散した酸素濃度〔mol/Kg〕 B 平衡関係 CB *=Pgas・H (3) Pgas/π=Xgas=CE/C (4) PH2O/π=XH2O=CH2O/C=103/18/C(5) (4)、(5)式から Pgas/PH2O=Xgas/XH2O=CE/55.5 (6) 故に m=CE/CB *=55.5/PH2O・H (7) ただしCB *:補給海水脱気後の平衡酸素濃
度〔mol/Kg〕 C:ガス成分全てのモル濃度〔mol/Kg〕 CH2O:水1Kgのモル濃度=103/18=55.5
〔mol/Kg〕 Xgas:酸素のモル分率〔−〕 XH2O:水のモル分率〔−〕 Pgas:酸素の分圧〔atm〕 PH2O:水の分圧〔atm〕 π:気相中の全圧〔atm〕 m:分配率〔−〕 H:ヘンリー常数〔mol/Kg・atm〕 C 蒸発率(R)、非平衡条件(NECR)およ
び温度降下(△T) R=FE/FT (8) (NECR)=CB */CB (9) 以上より R=CT−CB */CB *(m−1)= CT−CB(NECR)/CB(NECR)(m−1) (10) FE=〔CT−CB(NECR)〕/CB(NECR)〔(55.5/PH2O
・H)−1〕 (11) 一方FEの蒸発による温度降下△Tは、 △T=FEHV/FTCP (12) ただしHV:水の蒸発潜熱〔Kcal/Kg〕 CP:水の比熱〔Kcal/Kg・C〕 (10)、(11)式において、分配率mはヘンリー常数と
温度のみによつて一義的に決まる。また、温度:
40〜50℃圧力:飽和圧、ノズル噴霧時の
(NECR)を実機規模の装置データから求めた結
果(NECR)=0.5であつた。 これらの結果をふまえると、(10)、(11)式は、蒸発
率Rと脱気後の濃度CBとは次の関係があること
になる。 R∝CT/CB すなわち、入口O2温度が一定の場合最終段脱
気方式の場合の脱気率はフラツシユ蒸発率に支配
される。 さて、フラツシユ蒸発させるためには、最終段
のバルクの温度より必要なフラツシユ蒸発量に見
合うだけ高温にしておく必要がある。このため、
補給海水が最終段フラツシユ室に供給される前に
予熱することを特徴とする最終段脱気プロセスが
本発明のポイントである。第2図中の8が当該予
熱器で加熱用熱源ライン9を流れる加熱用熱源と
しては、蒸発缶初段ブライン、中間段ブライン、
高温製造淡水を用いる。(加熱器蒸発を用いると、
造水比が低下する。)なお、11は加熱用流体出
口である。 実施例 造水量24m3/d、最高ブライン温度120℃の蒸
発型海水淡水化装置において、本発明を適用した
実施例を第1表に示す。
[Technical Field of the Invention] The present invention relates to a deaeration method for a flash evaporation type seawater desalination apparatus using a final stage deaeration method. [Background Art] In evaporative seawater desalination equipment (hereinafter referred to as MSF), deoxygenation of make-up seawater is very important from the perspective of preventing corrosion of the equipment. The deoxygenation (hereinafter referred to as deaeration) process includes (1) a vacuum deaeration method using a packed column, and (2) deaeration is simultaneously performed in the final stage flash chamber (hereinafter referred to as the "final stage evaporator"). There is a final stage degassing method. Comparing the performance of both methods, method (2) is generally superior.
This method is said to be inferior to method (1). This is because the theoretical basis of the rate-determining factor in method (2) is not fully understood, so at present both methods have no choice but to base their degassing theory on the double-layer theory. [Conventional Final Stage Degassing System] Here, a conventional final stage degassing system will be explained based on FIG. 1. The make-up seawater flowing into the evaporator is branched from the outlet 4' of the heat recovery part condenser 5 of the cooling seawater line 4 passing through the heat release part condenser 5 of the evaporation chamber 1, and flows into the make-up seawater line 6.
This make-up seawater is sprayed into the final stage of the evaporator by the deaeration nozzle 7, and mixed with the circulating brine 10 that has flowed in from the previous stage evaporation chamber. In the figure, 2 is a circulation pump that supplies water to the condenser 5 of the heat recovery section of the flash evaporator, and 3 is a discharge pump for maintaining a certain concentration. The rate-limiting factors for degassing according to the double boundary film theory are the gas-liquid contact area, film thickness, and zonation time in addition to the O 2 partial pressure, but even with this flow, the temperature inside the final stage evaporation chamber is higher than the inflowing seawater, so There is a decrease in O 2 concentration due to the increase in the temperature of the supplementary seawater, and an increase in the dissipation rate due to the formation of a spray. However, because the residence time is short, the performance of the final stage deaeration method is higher than that of a separate vacuum deaeration tower method, which increases the gas-liquid contact area and residence time due to the uniform spray inside the tower and the packing material. It is unavoidable that it is inferior. Adopting the final stage degassing method as described above does not require a separate vacuum degassing tower, which is a major cost reduction factor, but on the other hand, performance is inferior, and the material of the evaporator body is Upgrading becomes difficult to avoid, leading to a significant increase in costs. Recent MSF constituent materials are copper alloys, with some exceptions.
High-grade materials such as stainless steel and titanium have been selected to prevent corrosion. Corrosion problems that occur in MSF include general corrosion of carbon steel, electrolytic corrosion of aluminum bronze/titanium, stainless steel/carbon steel, stress corrosion and pitting corrosion of stainless steel, and inlet attack at the inlet of heat transfer tubes. , these can be practically prevented to a large extent by removing dissolved oxygen. Therefore, it is essential to develop a degassing system that is inexpensive and has sufficient performance in order to reduce the cost of MSF. [Objective of the present invention] The present inventor focused on the fact that the conventional final stage degassing method is not based on the double film theory, but that water evaporation is the main rate-determining factor in a flash evaporation environment.
As a result, the present invention has been completed. That is, an object of the present invention is to provide a deaeration method for a flash evaporation type seawater desalination apparatus in which the deaeration efficiency in the final stage deaeration method is improved. [Structure of the Present Invention] As a means for achieving the above object, the present invention consists in preheating the make-up seawater before it flows into the final stage evaporation chamber. That is, the present invention provides a flash evaporation type seawater desalination device that uses part of the heat release section cooling seawater as make-up seawater, and a make-up seawater preheater is installed in the make-up seawater line for flowing make-up seawater into the final stage evaporation chamber. This is a deaeration method for a flash evaporation type seawater desalination apparatus, which is characterized in that the temperature of the make-up seawater is raised to a temperature higher than the temperature inside the evaporator, and then the air is degassed within the evaporator. In the present invention, before the make-up seawater flows into the final stage evaporator, a make-up water preheater is provided, and the temperature is raised by the temperature at which flash evaporation is possible in the final stage evaporator (for example, 1 to 2°C). The goal is to change the rate-determining factors of gas from the gas-liquid contact area and residence time to flash evaporation. The present invention will be explained in detail based on FIG. FIG. 2 shows the flow of the present invention. The heat release part is the same as the conventional method shown in Figure 1, but the supply seawater line 6
The make-up seawater passing through exchanges heat with the heating fluid (steam or hot water) in the make-up water preheater 8, and is heated to a temperature 1 to 2 degrees Celsius higher than the temperature inside the final stage evaporator. This heated make-up water flows into the evaporator and is degassed while flashing and evaporating, and is lowered to the temperature of the brine that has flowed in from the previous stage. (1) Make-up water preheater This preheater 8 serves to raise the temperature of the seawater that has passed through the heat recovery section condenser 5 to a temperature high enough for make-up water to flash evaporate in the final stage evaporation chamber 1. change in balance,
There is no phase change. (2) Final stage flash chamber The preheated seawater flash evaporates here, lowering the temperature and reducing the dissolved oxygen concentration. These relational expressions are shown in (1) to (13). A Mass balance F T =F B +F E (1) F T C T =F B C B +F E C E (2) However, F T : Makeup water inlet flow rate [Kg/h] F B : Mixed with brine Immediate flow rate [Kg/h] F E : Evaporation amount from makeup water [Kg/h] C T : Oxygen concentration before makeup water degassing [mol/Kg] C B : Oxygen concentration after makeup water degassing [ mol/Kg] C E : Oxygen concentration dissipated into the gas phase [mol/Kg] B Equilibrium relationship C B * =P gas・H (3) P gas /π=X gas =C E /C (4) P H2O /π=X H2O =C H2O /C=10 3 /18/C(5) From equations (4) and (5), P gas /P H2O =X gas /X H2O =C E /55.5 (6) Therefore, m =C E /C B * =55.5/P H2O・H (7) However, C B * : Equilibrium oxygen concentration after degassing of supplementary seawater [mol/Kg] C: Molar concentration of all gas components [mol/Kg] C H2O : Molar concentration of 1 kg of water = 10 3 / 18 = 55.5
[mol/Kg] X gas : Mole fraction of oxygen [ ] Total pressure in the phase [atm] m: Partition ratio [-] H: Henry constant [mol/Kg・atm] C Evaporation rate (R), non-equilibrium condition (NECR) and temperature drop (△T) R=F E /F T (8) (NECR)=C B * /C B (9) From the above, R=C T −C B * /C B * (m−1)= C T −C B (NECR)/C B (NECR) (m-1) (10) F E = [C T −C B (NECR)]/C B (NECR) [(55.5/P H2O
・H)-1〕 (11) On the other hand, the temperature drop △T due to evaporation of F E is △T=F E H V /F T C P (12) where H V : Latent heat of vaporization of water [Kcal/Kg] C P : Specific heat of water [Kcal/Kg・C] In equations (10) and (11), the partition ratio m is uniquely determined only by Henry's constant and temperature. Also, temperature:
40-50°C Pressure: saturation pressure, (NECR) during nozzle spraying was determined from actual scale equipment data (NECR) = 0.5. Based on these results, equations (10) and (11) show that the evaporation rate R and the concentration C B after degassing have the following relationship. R∝C T /C B That is, when the inlet O 2 temperature is constant, the deaeration rate in the case of the final stage deaeration method is controlled by the flash evaporation rate. Now, in order to evaporate the flash, it is necessary to make the temperature higher than the temperature of the final stage bulk by an amount corresponding to the required amount of flash evaporation. For this reason,
The key point of the present invention is the final stage degassing process, which is characterized by preheating the make-up seawater before it is supplied to the final flush chamber. 8 in FIG. 2 is the preheater, and the heating heat sources flowing through the heating heat source line 9 include an evaporator first stage brine, an intermediate stage brine,
Uses high temperature produced fresh water. (If heater evaporation is used,
Water production ratio decreases. ) Note that 11 is a heating fluid outlet. Examples Table 1 shows examples in which the present invention was applied to an evaporative seawater desalination apparatus with a water production capacity of 24 m 3 /d and a maximum brine temperature of 120°C.

【表】【table】

〔本発明の効果〕[Effects of the present invention]

本発明は、以上詳記したように、補給海水が最
終段蒸発室に流入する前にこの補給海水を予熱
し、次いて最終段蒸発室に導入するようにしたの
で、補給海水中の溶存酸素が効率よく脱気され、
その結果、該装置の腐蝕防止の面で顕著な効果が
生ずるものである。
As detailed above, the present invention preheats the makeup seawater before it flows into the final stage evaporation chamber and then introduces it into the final stage evaporation chamber, so dissolved oxygen in the makeup seawater is reduced. is efficiently degassed,
As a result, a remarkable effect is produced in terms of preventing corrosion of the device.

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

第1図は従来の最終段脱気方式を説明するため
のフロー図であり、第2図は本発明のフロー図で
ある。
FIG. 1 is a flow diagram for explaining a conventional final stage degassing system, and FIG. 2 is a flow diagram of the present invention.

Claims (1)

【特許請求の範囲】[Claims] 1 熱放出部冷却海水の一部を補給海水として使
用するフラツシユ蒸発型海水淡水化装置におい
て、最終段蒸発室に補給海水を流入するための補
給海水ラインに補給海水予熱器を設置し、補給海
水温度を当該蒸発缶内温度以上に上昇させた後蒸
発缶内で脱気させることを特徴とするフラツシユ
蒸発型海水淡水化装置の脱気方法。
1. In a flash evaporative seawater desalination system that uses part of the cooling seawater as make-up seawater, a make-up seawater preheater is installed in the make-up seawater line for flowing make-up seawater into the final stage evaporation chamber, and the make-up seawater is 1. A deaeration method for a flash evaporation type seawater desalination apparatus, characterized in that the temperature is raised to a temperature higher than the temperature inside the evaporator, and then the evaporator is degassed.
JP58085681A 1983-05-18 1983-05-18 Deaerating method of flash evaporation type sea water desalting device Granted JPS59213488A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58085681A JPS59213488A (en) 1983-05-18 1983-05-18 Deaerating method of flash evaporation type sea water desalting device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58085681A JPS59213488A (en) 1983-05-18 1983-05-18 Deaerating method of flash evaporation type sea water desalting device

Publications (2)

Publication Number Publication Date
JPS59213488A JPS59213488A (en) 1984-12-03
JPH0225672B2 true JPH0225672B2 (en) 1990-06-05

Family

ID=13865580

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58085681A Granted JPS59213488A (en) 1983-05-18 1983-05-18 Deaerating method of flash evaporation type sea water desalting device

Country Status (1)

Country Link
JP (1) JPS59213488A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0272774U (en) * 1988-11-25 1990-06-04

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0272774U (en) * 1988-11-25 1990-06-04

Also Published As

Publication number Publication date
JPS59213488A (en) 1984-12-03

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