JPS5987090A - Filtering desalinator - Google Patents

Filtering desalinator

Info

Publication number
JPS5987090A
JPS5987090A JP57197567A JP19756782A JPS5987090A JP S5987090 A JPS5987090 A JP S5987090A JP 57197567 A JP57197567 A JP 57197567A JP 19756782 A JP19756782 A JP 19756782A JP S5987090 A JPS5987090 A JP S5987090A
Authority
JP
Japan
Prior art keywords
water
elements
filtration
filter
filtering
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.)
Granted
Application number
JP57197567A
Other languages
Japanese (ja)
Other versions
JPH0212635B2 (en
Inventor
Toshio Ogawa
敏雄 小川
Tetsuro Adachi
安達 哲朗
Katsuya Ebara
江原 勝也
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.)
Hitachi Ltd
Original Assignee
Hitachi 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 Hitachi Ltd filed Critical Hitachi Ltd
Priority to JP57197567A priority Critical patent/JPS5987090A/en
Publication of JPS5987090A publication Critical patent/JPS5987090A/en
Publication of JPH0212635B2 publication Critical patent/JPH0212635B2/ja
Granted legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E30/00Energy generation of nuclear origin
    • Y02E30/30Nuclear fission reactors

Landscapes

  • Treatment Of Water By Ion Exchange (AREA)
  • Filtration Of Liquid (AREA)

Abstract

PURPOSE:To improve the filtering life and the filtering desalination power of the titled desalinator, by supplying water to a space between the group of filter elements from the upper and lower end bounds of the filter elements vertically provided, and precoating the filter elements with an assistant along a vertical direction. CONSTITUTION:The upper end of a filter element is provided at a ceiling plate 22 forming a filtering desalination chamber, while its lower end is equipped with a pipe part for withdrawal of a desalinated filtrate in a manner such that said pipe part extends through a bottom plate 21 to seal introduced water and the desalinated filtrate from each other. Guide plates 23, 24 for introducing streams of water to a space between the group of the elements from the lower position of the elements are provided at a water supply pipe 15 in correspondense to the elements. In precoating the elements with a filtering assistant, slurry of predetermined concentration is introduced in a predetermined flow rate through the pipe 15. A part of the introduced slurry is diffused along a horizontal direction by the guide plates 23, 24. The slurry from the guide plate 23 is spread to a far area while that from the guide plate 24 is spread to near area. Both of them rise through the space between the group of the elements.

Description

【発明の詳細な説明】 〔発明の利用分野〕 本発明は濾過助剤をプリコートする0ゴ過脱塩装置に係
り、特に、原子力発電所の復水等の浄化に使用する多管
式濾過脱塩装置に関する。
Detailed Description of the Invention [Field of Application of the Invention] The present invention relates to a zero-go filtration desalination device that precoats a filter aid, and particularly relates to a multi-tube filtration desalination device used for purifying condensate in nuclear power plants. Regarding salt equipment.

〔従来技術〕[Prior art]

原子力発電所(BWE口の復水鹸化系及び炉水浄化系の
水処理系統を第1図に示す。図において原子炉1で発生
した蒸気(286°C170k g/cm” )は蒸気
管2を経てタービン3を回転駆動し発電を行ない、その
後復水器4に流入し、凝縮して水に復水する。復水器4
からの水は復水浄化系配管15によって導びかれポンプ
5によりp過脱塩器6に送られる。p過脱塩器6では、
復水浄化系内で発生するクラッド(クラッドとは復水浄
化系内の腐食生成物が主体で通常0.45μ!nのシリ
ボアフィルターを通過しない微細な懸濁物の総称で主成
分はFe、 03 + peso、等である。、)及び
核種イオンを円筒形い過エレメントに陽イオン及び陰イ
オンの粉末イオン交換樹脂を特定割合で混合した樹脂を
均等に数節厚みに外径面にプリコートした樹脂層で濾過
脱塩して水の浄化を行なう。濾過脱塩器6で浄化された
水は、次に脱塩器、7に送られ、脱塩器内に陰及び陽イ
オンの粒状イオン交換樹脂を積んだ積層によって、濾過
脱塩器6で除去されなかった残留クラッド及び核種イオ
ンが補足脱塩される。脱塩器7を経た浄化水は、低圧給
水加熱1(凌8で加熱されてポンプ9により高圧給水加
熱器lOへ送られ、再び高圧で加熱されて原子炉1へ戻
るように構成されている。このように、原子炉で発生し
た蒸気はタービンを駆動した後、復水浄化して、原子炉
に戻すので復水浄化系を常時循環していることになる。
Figure 1 shows the water treatment systems of the nuclear power plant (condensate saponification system and reactor water purification system at the BWE port. In the figure, the steam generated in reactor 1 (286°C, 170 kg/cm") is passed through steam pipe 2. The water then rotates the turbine 3 to generate electricity, and then flows into the condenser 4 where it is condensed and condensed into water.Condenser 4
The water is led by a condensate purification system piping 15 and sent to a p-super desalination device 6 by a pump 5. In the p over-demineralizer 6,
Crud generated in the condensate purification system (Crud is a general term for fine suspended matter that is mainly composed of corrosion products in the condensate purification system and does not pass through the 0.45μ!n Silibore filter, and the main component is Fe. , 03 + peso, etc.) and nuclide ions are pre-coated on the outer diameter surface of the cylindrical element with resin prepared by mixing cation and anion powder ion exchange resin in a specific ratio to a thickness of several sections. Water is purified by filtration and desalination through the resin layer. The water purified by the filtration demineralizer 6 is then sent to the demineralizer 7, and is removed by the filtration demineralizer 6 by stacking anion and cation granular ion exchange resins in the demineralizer. Residual cladding and nuclide ions that were not removed are supplementally desalted. The purified water that has passed through the demineralizer 7 is heated by a low-pressure feedwater heater 1 (heater 8), sent to a high-pressure feedwater heater IO by a pump 9, heated again at high pressure, and returned to the reactor 1. In this way, the steam generated in the nuclear reactor drives the turbine, then is purified as condensate and returned to the reactor, so it is constantly circulated through the condensate purification system.

一方、原子炉の炉水は炉水浄化系配管16を経て一部は
ポンプ11により原子炉へ戻され他は冷却器12へ送ら
れる。冷却器12で冷却された炉水はポンプ13によシ
炉水浄化器14へ送られて、浄化された後、再び原子炉
へ戻るように構成されている。炉水浄化器14の構造は
復水p通説塩器と同一で、炉水を循環させて濾過脱塩し
浄化するようになっている。
On the other hand, some of the reactor water is returned to the reactor by the pump 11 through the reactor water purification system piping 16, and the rest is sent to the cooler 12. The reactor water cooled by the cooler 12 is sent to the reactor water purifier 14 by the pump 13, and after being purified, it is returned to the reactor. The structure of the reactor water purifier 14 is the same as that of a condensate salter, and is designed to circulate reactor water, filter it, desalt it, and purify it.

第2図は従動濾過脱塩器の内部構造の概殻を示しだ立断
面図である。濾過脱塩器内には、外径50φ、全長1.
5m程の円筒状ろ過エレメント30が約80園の間隔で
200数本設置されている多管弐沖過器である。濾過エ
レメントは上端が吊シ金具によって、天井板22に装着
、下端はν過水の抜き出し管が底板21を貫通して、設
置されており、各濾過エレメントからの濾過脱塩水18
は室25に集合する。p通説塩器内への給水管15の吐
出部には、傘形状案内板23.24が設けてあり、導入
水をエレメント群間に平均して流入するようにしである
FIG. 2 is an elevational cross-sectional view showing the general outline of the internal structure of the driven filtration demineralizer. The inside of the filtration demineralizer has an outer diameter of 50φ and a total length of 1.
It is a multi-tube filtration device in which more than 200 cylindrical filtration elements 30 of about 5 m are installed at intervals of about 80 gardens. The upper end of the filtration element is attached to the ceiling plate 22 by a hanging fitting, and the lower end is installed with a filtration water extraction pipe passing through the bottom plate 21, and the filtration demineralized water 18 from each filtration element is installed.
will gather in room 25. General theory Umbrella-shaped guide plates 23 and 24 are provided at the outlet of the water supply pipe 15 into the salt chamber, so that the introduced water flows evenly between the element groups.

第3図は濾過エレメント構造の概要とp通説塩層の状態
を示しだものである。濾過エレメントは極細繊維糸を束
ねて撚り合せたものを膜孔円筒支持材32に巻装して1
0数問厚みのp過支持層31を形成してなり、それ自体
でミクロンオーダ粒径の濾過除去が出来る。表11+1
には平均粒径数十μmの粉状イオン交換樹脂をプリコー
トしだ助剤p渦層33が形成されているう導入水17は
エレメントに沿って、上昇し、濾過層を透過することに
よシ、濾過脱塩され、p通説塩水1日を内部から抜き出
す方式である。
Figure 3 shows an outline of the filter element structure and the state of the p-salt layer. The filtration element is made by bundling and twisting ultrafine fiber threads and wrapping them around a membrane-hole cylindrical support material 32.
A p-supersupporting layer 31 having a thickness of several 0.0 mm is formed, and by itself can filter and remove particles with a particle size on the order of microns. Table 11+1
is pre-coated with a powdered ion exchange resin with an average particle size of several tens of micrometers, forming an auxiliary vortex layer 33.The introduced water 17 rises along the element and passes through the filter layer. It is filtered and desalinated, and the commonly known salt water is extracted from the inside.

濾過助剤のエレメントへのプリコートは、水のp過層と
同一給水管から導入して行なう。スラリー(樹脂混合水
で樹脂濃度0.5〜Iwt%)をエレメント表面積に対
する線速度(L、V)、通常3〜4 m / hで導入
してプリコートする方式がとられるが、助剤のプリコー
ト形成層がエレメント全体に対し、平均しておらず、第
4図に示すようにL V 4 m / hでは、位置1
000以上になると極端に薄くなる。またLV、6.5
.10m/h(7)場合のプリコート状態は上位置のプ
リコート形成は改良されるが、0位置近傍の流速が大と
なるだめ、下位置の濾過助剤の形成が悪く、剥離しやす
い。
The filter aid is precoated onto the element by introducing it from the same water supply pipe as the p-filter layer of water. Precoating is done by introducing a slurry (resin mixed water with resin concentration of 0.5 to Iwt%) at a linear velocity (L, V) relative to the element surface area, usually 3 to 4 m/h. The formation layer is not averaged over the entire element, and as shown in FIG.
000 or more, it becomes extremely thin. Also LV, 6.5
.. In the case of 10 m/h (7), the precoat formation at the upper position is improved, but because the flow velocity near the 0 position is high, the formation of the filter aid at the lower position is poor and it is easy to peel off.

このような助剤の形成層厚が不均一の状態で、p逸脱塩
処理をすると、層厚が薄い部分では処理水の濾過脱塩率
が低く、また、濾過機構に於ける体積濾過の状態が悪い
ので、プリコート層形成が均一状態ではその濾過差圧が
徐々に上昇するのに比べ急激に上昇するため、濾過寿命
が短縮する6濾過差圧が設定圧以上に達すとプリコート
しである助剤を剥離して新しい助剤と交換する。従がっ
て、交換回数が多くなり、使用済の廃樹脂駿すなわち放
射性廃棄物の量が増大する。
If p-deviation salt treatment is performed in a state where the layer thickness of the auxiliary agent is uneven, the filtration and desalination rate of the treated water will be low in areas where the layer thickness is thin, and the state of volumetric filtration in the filtration mechanism will be affected. When the precoat layer is formed uniformly, the filtration differential pressure rises rapidly rather than gradually, which shortens the filtration life. 6. When the filtration differential pressure reaches the set pressure or higher, the precoat pressure increases rapidly. Peel off the agent and replace with new auxiliary agent. Therefore, the number of replacements increases, and the amount of used waste resin, that is, radioactive waste increases.

〔発明の概要〕[Summary of the invention]

本発明は濾過エレメントへの助剤プリコート形成層厚を
全体に均一化するためのものである。第5図はエレメン
トにL V 4 m / bで助剤をプリコートシた後
、エレメントの各位置からグリコート助剤を採取し、そ
の助剤の静水中の沈降速度を測定した結果である。エレ
メント位置により、その付着助剤の沈降速度は位置10
00以上から急激に減少する。これは比重の軽いものが
上部位置に薄くプリコートされていることを意味し、重
いものは上部位置まで到達出来ない結果から起るととと
考えられる。そこで、エレメント群間における水流動の
上昇速度を各LVに対して示したのが第6図である。、
Ly4m/hでは、位置1000以上になるとエレメン
ト群間の上昇速度が樹脂の沈降速度36m/h以下とな
ってしまうので、それ以上の位置では、スラリー水の到
達がゆるやかとなるので樹脂の到達歇が少ないだめにプ
リコート形成層厚が薄くなる。まだ、LVを6、I Q
 m / hと上昇させると沈降速度線図上となるエレ
メントの位置も上方へ移動するが完全でないことがわか
った。従がって、プリコート形成層厚を全体的に均 ・
−化するためには、エレメント全域において、上昇速度
が樹脂沈降速度より大であることが必要条件である。本
発明は上記のことがらを考慮して、なされたものである
The present invention is intended to make the thickness of the auxiliary agent precoat layer formed on the filter element uniform throughout. FIG. 5 shows the results of pre-coating the element with the auxiliary agent at L V 4 m/b, collecting the glycolyte auxiliary agent from each position of the element, and measuring the sedimentation rate of the auxiliary agent in still water. Depending on the element position, the sedimentation rate of the adhesion aid is at position 10.
It rapidly decreases from 00 or above. This means that materials with light specific gravity are thinly pre-coated at the upper position, and it is thought that this is caused by the fact that materials with heavy specific gravity cannot reach the upper position. Therefore, FIG. 6 shows the rising speed of water flow between element groups for each LV. ,
At Ly4m/h, when the position is 1000 or more, the rising speed between the element groups becomes less than the sedimentation speed of the resin, 36m/h, so at positions above that, the slurry water reaches slowly, so the arrival time of the resin is The smaller the amount, the thinner the precoat forming layer becomes. Still LV 6, IQ
It was found that when increasing the velocity by m/h, the position of the element on the sedimentation velocity diagram also moved upward, but not completely. Therefore, the thickness of the precoat forming layer is uniform throughout.
In order to achieve this, it is necessary that the rate of rise is greater than the rate of resin sedimentation over the entire area of the element. The present invention has been made in consideration of the above matters.

〔発明の実施例〕[Embodiments of the invention]

第7図は本発明の濾過脱塩器の内部構造を示しだ置所面
図である。、濾過エレメントの上端はD5過脱塩室を形
成する天井板22に装着、下端はろ通説塩水抜き出し部
管が底板21を貫通し、導入水と濾過脱塩水をシールす
るように具備しである。
FIG. 7 is a plan view showing the internal structure of the filtration demineralizer of the present invention. The upper end of the filtration element is attached to the ceiling plate 22 forming the D5 demineralization chamber, and the lower end is provided with a brine extraction pipe passing through the bottom plate 21 to seal the introduced water and the filtered demineralized water.

給水管15には、エレメントと対応して、エレメント下
部位置からエレメント群間に水流を導びく案内板23.
24を設けてあり、案内板23は水流が器側壁部まで達
するように、案内板24は近傍域を対象にして設けであ
る。案内板24上には上部まで達する管26を設けて導
入水の一部が上昇して上端から流出するようにしてちゃ
、管上端には、エレメント上端部と対応して、案内板2
7゜28が設けである。案内27は近傍域にあるエレメ
ント群を、案内板28は、違例域のエレメント群を対象
にして設けである。ろ過膜塩水は下端部から抜き出す構
造である。次にp過助剤をエレメントにグリコートする
場合は、所定濃度スラリーを管15よシ所定流量にて導
入する。導入スラリーの1部は案内板23.24によっ
て、水平方向に拡散し、案内板23からのスラリーは遠
方へ、案内板24からのスラリーは近傍に拡がり、エレ
メント群間を上昇する。
The water supply pipe 15 has guide plates 23.corresponding to the elements that guide the water flow between the element groups from the lower part of the element.
The guide plate 23 is provided so that the water flow reaches the side wall of the vessel, and the guide plate 24 is provided so that the water flow reaches the side wall of the vessel. A pipe 26 reaching the upper part of the guide plate 24 is provided so that a part of the introduced water rises and flows out from the upper end.
The setting is 7°28. The guide 27 is provided for a group of elements in a nearby area, and the guide plate 28 is provided for a group of elements in an unusual area. The filter membrane has a structure in which salt water is extracted from the lower end. Next, when glycoating the element with the p-superior agent, a slurry of a predetermined concentration is introduced through the pipe 15 at a predetermined flow rate. A portion of the introduced slurry is spread horizontally by the guide plates 23, 24, the slurry from the guide plate 23 spreads far away, the slurry from the guide plate 24 spreads nearby, and rises between the element groups.

一方、一部スラリーは管26を上昇し、上部に於いて、
案内27.28によって、水平方向に拡散し、案内板2
Bからは違例、案内板27からは近傍に拡散し、これら
スラリーがエレメント群間を流動している間、p過エレ
メント内部からp過水を連続して抜きとることによって
、濾過エレメント表面に助剤29のp渦層を形成する。
On the other hand, some of the slurry rises up the pipe 26, and at the top,
By the guides 27 and 28, it is spread horizontally and the guide plate 2
Unlike B, the slurry diffuses into the vicinity from the guide plate 27, and while the slurry is flowing between the element groups, the P-filtered water is continuously removed from the inside of the P-filtering element, and the slurry is applied to the surface of the filtering element. A p-vortex layer of agent 29 is formed.

形成のp過励剤層は、第8図に示す。エレメント群間の
流動速度によって、変化し、第9図に示すp過励剤層を
形成する。底部から上方への流動速度vb1上部から下
方向への流動速度をV、とすると、図はエレメントに対
するLV 4 m / hの場合であるが、■は流動流
凌をエレメント間の空間面積で除した瞳、単位面積当シ
の線速度LVがa位置でv 、 = 105.5m/h
 、 V4 = l 2m/11.  ■はV、==9
.5m/11.Wb=108.5m/hの条件で助剤を
プリコートした結果である。■は上部位置に達する助剤
量が少ないため、その部分のプリコート形成層は薄い。
The formation of the p-superexciter layer is shown in FIG. The flow rate between the elements changes to form the p-superexciter layer shown in FIG. Flow velocity from the bottom upwards vb1 If the flow velocity from the top downwards is V, the figure is for the case of LV 4 m/h for the element, but ■ is the flow rate divided by the space area between the elements. pupil, the linear velocity LV per unit area is v at position a, = 105.5 m/h
, V4 = l 2m/11. ■ is V, ==9
.. 5m/11. This is the result of precoating the auxiliary agent under the condition of Wb=108.5 m/h. In case (2), the amount of the auxiliary agent reaching the upper position is small, so the precoat forming layer in that area is thin.

■では比較的均一にプリコート層が形成されるが、上部
からの下向流によって、樹脂の沈降速度が加速されるの
で、上部LVが大の場合は上部位のプリコート層が厚く
なる。またエレメントにグリコートされないで沈降する
樹脂量も多い。■は上昇LVに対し、下向流LVを同一
にした場合で、ここでの下向流LVは樹脂沈降速度をV
、に加算した値での結果である。上下方向からの水流動
はエレメント中央位遣で滞留が起るが、プリコート形成
層はエレメント全体に対し均一に形成される。
In case (2), the precoat layer is formed relatively uniformly, but the sedimentation speed of the resin is accelerated by the downward flow from the upper part, so when the upper LV is large, the precoat layer in the upper part becomes thicker. Also, there is a large amount of resin that settles without being glycated onto the element. ■ is a case where the downward flow LV is the same as the upward flow LV, where the downward flow LV is the resin sedimentation velocity V
The result is the value added to . Water flowing from above and below causes stagnation in the center of the element, but the precoat forming layer is formed uniformly over the entire element.

以上、エレメントへ助剤をプリコートするのに、上下方
向からエレメント外周部に導水し行なう場合合、使用助
剤の沈降速度を考慮して行なえば均一なプリコート層を
形成することが出来る。助剤プリコート完了後ろ過説塩
処理の運転に入るが徐々にエレメントに対するl、Vを
上列し、通常8〜I Q m / bで運転される。
As described above, when precoating an auxiliary agent onto an element by introducing water to the outer periphery of the element from above and below, a uniform precoat layer can be formed if the sedimentation rate of the auxiliary agent used is taken into consideration. After the completion of pre-coating of the auxiliary agent, salt treatment operation begins, but the l and V relative to the element are gradually increased, and the operation is normally performed at 8 to IQ m/b.

〔発明の効果〕〔Effect of the invention〕

本方式では、エレメントへの導入水を2方向から行なう
ため、従来1方向からのに比べLVを上昇することによ
って起っていた導入口近傍のエレメントプリコート層が
流速増大による剥離するのを防止出来、均一プリコート
層を形成しているので、本発明は濾過脱塩性能並びに濾
過寿命の向上に効果大である。
In this method, since water is introduced into the element from two directions, it is possible to prevent the element precoat layer near the introduction port from peeling off due to an increase in flow velocity, which would occur due to an increase in LV compared to conventional methods when water is introduced from one direction. Since a uniform precoat layer is formed, the present invention is highly effective in improving filtration and desalting performance and filtration life.

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

第1図は原子力発成所(B W R)の水の浄化系統図
、第2図は従来の濾過脱塩器の置所面構造図、第3図は
p過エレメントの濾過モデル図、第4図はプリコート層
状態図、第5図は樹脂の沈降速度線図、第6図は流動速
度線図、第7図は本発明のp通説塩器の置所面構造図、
第8図はp過エレメント外の流動モデル図、第9図は本
発明によるプリコート形成層状態図である。 6・・・p通説塩器、21・・・底部板、22・・・天
井板、23.24,27.’28・・・案内板、26・
・・管、29・・・(射脂(助剤)、3o・・・P禍エ
レメント、31・・・濾過エレメント繊維層、32・・
・繊維層支持円筒、33・・・濾過助剤プリコート形成
層。 第3圀 感4 口 寮′7 口 第1 1日 ■  ■ 4は町り  η2(紮ダフ ■ I¥)、 (4rLm) −559−
Figure 1 is a water purification system diagram at a nuclear power plant (BWR), Figure 2 is a structural diagram of the location of a conventional filtration demineralizer, Figure 3 is a filtration model diagram of a p-filtration element, Fig. 4 is a state diagram of the precoat layer, Fig. 5 is a sedimentation velocity diagram of the resin, Fig. 6 is a flow velocity diagram, and Fig. 7 is a structural diagram of the location of the p-general salt vessel of the present invention.
FIG. 8 is a flow model diagram outside the p-element, and FIG. 9 is a state diagram of the precoat forming layer according to the present invention. 6...p common salt vessel, 21...bottom plate, 22...ceiling plate, 23.24,27. '28... Information board, 26.
... Pipe, 29 ... (ejaculate oil (auxiliary agent), 3o ... P-damage element, 31 ... filtration element fiber layer, 32 ...
- Fiber layer support cylinder, 33... Filter aid precoat forming layer. 3rd Kankan 4 Kuchiryo'7 Kuchi 1st 1st day ■ ■ 4 is town η2 (Go Duff ■ I ¥), (4rLm) -559-

Claims (1)

【特許請求の範囲】[Claims] 1、表面に濾過助剤をプリコートし、助剤濾過層、フィ
ルタ一層ト水を透過させ、フィルターエレメント内部か
ら濾過水を抜き済過脱塩をするフィルターエレメントを
内部に多数設置した濾過脱塩装置に於いて、立設のフィ
ルターエレメントの上端及び下端部域からフィルターエ
レメント群間へ給水し、上下方向からフィルターエレメ
ントに助剤をプリコートすることを特徴とする濾過脱塩
装置1t02、請求の範囲第1項に於いて、装置中央部
に給水管を位置させ、フィルターエレメントの下端及び
上端位1紅と対応する位置の給水管に水流の案内を設け
た構造を特徴とする濾過脱塩■も
1. A filtration/desalination device with a number of filter elements pre-coated with a filtration aid on the surface to allow water to permeate through the auxiliary filtration layer and filter layer, and to remove filtrated water from the inside of the filter element for desalination. A filtration and demineralization device 1t02 characterized in that water is supplied between the filter element groups from the upper and lower end regions of the upright filter elements, and the filter elements are precoated with an auxiliary agent from above and below. In item 1, there is also a filtration desalination system characterized by a structure in which a water supply pipe is located in the center of the device, and water flow guides are provided in the water supply pipes at positions corresponding to the lower and upper ends of the filter element.
JP57197567A 1982-11-12 1982-11-12 Filtering desalinator Granted JPS5987090A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57197567A JPS5987090A (en) 1982-11-12 1982-11-12 Filtering desalinator

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57197567A JPS5987090A (en) 1982-11-12 1982-11-12 Filtering desalinator

Publications (2)

Publication Number Publication Date
JPS5987090A true JPS5987090A (en) 1984-05-19
JPH0212635B2 JPH0212635B2 (en) 1990-03-22

Family

ID=16376644

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57197567A Granted JPS5987090A (en) 1982-11-12 1982-11-12 Filtering desalinator

Country Status (1)

Country Link
JP (1) JPS5987090A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS607917A (en) * 1983-06-28 1985-01-16 Kurita Water Ind Ltd Precoated filtration apparatus
JPS61268308A (en) * 1985-05-23 1986-11-27 Mitaka Kogyosho:Kk Method for filtering liquid to be treated
JPS6295709U (en) * 1985-10-24 1987-06-18
JPH033416U (en) * 1989-06-01 1991-01-14

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS607917A (en) * 1983-06-28 1985-01-16 Kurita Water Ind Ltd Precoated filtration apparatus
JPH0113889B2 (en) * 1983-06-28 1989-03-08 Kurita Water Ind Ltd
JPS61268308A (en) * 1985-05-23 1986-11-27 Mitaka Kogyosho:Kk Method for filtering liquid to be treated
JPS6295709U (en) * 1985-10-24 1987-06-18
JPH0328887Y2 (en) * 1985-10-24 1991-06-20
JPH033416U (en) * 1989-06-01 1991-01-14

Also Published As

Publication number Publication date
JPH0212635B2 (en) 1990-03-22

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